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The <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong> (<strong>IRRI</strong>) was established<br />

in 1960 by the Ford and Rockefeller Foundations with<br />

the help and approval of the Government of the Philippines.<br />

Today <strong>IRRI</strong> is one of the 15 nonprofit international research<br />

centers supported by the Consultative Group on <strong>International</strong><br />

Agricultural <strong>Research</strong> (CGIAR – www.cgiar.org).<br />

<strong>IRRI</strong> receives support from several CGIAR members,<br />

including the World Bank, European Union, Asian Development<br />

Bank, <strong>International</strong> Fund for Agricultural Development,<br />

<strong>International</strong> Development <strong>Research</strong> Centre,<br />

Rockefeller Foundation, Food and Agriculture Organization<br />

of the United Nations, and agencies of the following countries:<br />

Australia, Austria, Belgium, Brazil, Canada, Denmark,<br />

France, Germany, India, Iran, Japan, Malaysia, Netherlands,<br />

Norway, People’s Republic of China, Republic of Korea,<br />

Republic of the Philippines, Spain, Sweden, Switzerland,<br />

Thailand, United Kingdom, United States, and Vietnam.<br />

The responsibility for this publication rests with the<br />

<strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>.<br />

Suggested citation:<br />

Toriyama K, Heong KL, Hardy B, editors. 2005. <strong>Rice</strong> is<br />

life: scientific perspectives for the 21st century. Proceedings<br />

of the World <strong>Rice</strong> <strong>Research</strong> Conference held in Tokyo<br />

and Tsukuba, Japan, 4-7 November 2004. Los Baños (Philippines):<br />

<strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>, and Tsukuba<br />

(Japan): Japan <strong>International</strong> <strong>Research</strong> Center for Agricultural<br />

Sciences. CD-ROM. 590 p.<br />

Copyright <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong> 2005<br />

Mailing address: DAPO Box 7777, Metro Manila,<br />

Philippines<br />

Phone: +63 (2) 580-5600, 845-0563,<br />

844-3351 to 53<br />

Fax: +63 (2) 580-5699, 891-1292,<br />

845-0606<br />

Email: irri@cgiar.org<br />

Home page: www.irri.org<br />

<strong>Rice</strong>web: www.riceweb.org<br />

<strong>Rice</strong> Knowledge Bank:<br />

www.riceknowledgebank.org<br />

Courier address: Suite 1009, Pacific<br />

Bank Building 6776 Ayala<br />

Avenue, Makati City, Philippines<br />

Tel. (63-2) 891-1236, 891-1174,<br />

891-1258, 891-1303<br />

CD-ROM cover design: Juan Lazaro IV<br />

CD-ROM production coordinator: George R. Reyes<br />

Layout and design: Ariel Paelmo<br />

Figures and illustrations: Ariel Paelmo<br />

ISBN 971-22-0204-6


Contents<br />

FOREWORD<br />

ACKNOWLEDGMENTS<br />

xiv<br />

xv<br />

Keynotes<br />

The power of settled life: rice farming as a lifestyle 2<br />

Ken-ichi Matsumoto<br />

The role of rice in the Japanese diet 3<br />

Yoshiko Kagawa<br />

A greeting 4<br />

Yoshinobu Shimamura<br />

Statement by Jacques Diouf 4<br />

Address by Imperial Highness Crown Prince Naruhito 5<br />

New technologies for rice production 6<br />

Gurdev S. Khush<br />

The changing economics and politics of rice: implications for food security, 7<br />

globalization, and environmental sustainability<br />

Joachim von Braun and María Soledad Bos<br />

Feeding the world: How much more rice do we need 21<br />

Vaclav Smil<br />

Development of sustainable agriculture from rice, water, 23<br />

and the living environment<br />

Riota Nakamura<br />

<strong>Research</strong> strategy for rice in the 21st century 26<br />

Ronald P. Cantrell and Gene P. Hettel<br />

SESSION 1<br />

The genus Oryza, its diversity, and its evolution<br />

Molecular phylogeny and divergence of the rice tribe Oryzeae, with special 40<br />

reference to the origin of the genus Oryza<br />

Song Ge, Ya-long Guo, and Qi-hui Zhu<br />

Eco-genetic diversification in the genus Oryza: implications for sustainable 44<br />

rice production<br />

Duncan Vaughan, Koh-ichi Kadowaki, Akito Kaga, and Norihiko Tomooka<br />

Toward a global strategy for the conservation of rice genetic resources 47<br />

Ruaraidh Sackville Hamilton and Ruth Raymond<br />

Genetic architecture and complexity in wild and cultivated rice 49<br />

Y. Sano<br />

Who was the mother of cultivated rice Differentiation of chloroplast genome 52<br />

structure among cultivated rice and ancestral wild species<br />

Koh-ichi Kadowaki<br />

Diverse mechanisms of low-temperature stress response in rice 54<br />

Ryozo Imai, Jiangqi Wen, Kentaro Sasaki, and Kiyoharu Oono<br />

Genetic diversity of Myanmar rice landraces 56<br />

Ye Tint Tun, K. Irie, T. Nagamine, Jhon Ba Maw, F. Kikuchi, and H. Fujimaki<br />

Contents<br />

iii


QTL analysis for eating quality in japonica rice 60<br />

H.G. Hwang, J.P. Suh, Y.C. Cho, S.J. Kwon, I.S. Choi, H.C. Hong, Y.G. Kim,<br />

M.K. Kim, H.C. Choi, and Y.T. Lee<br />

SESSION 2<br />

Structure and function of the rice genome<br />

The complete rice genome sequence and its application to breeding 66<br />

and genetics<br />

Takuji Sasaki<br />

Exploitation and use of naturally occurring allelic variations in rice 69<br />

Masahiro Yano, Yasunori Nonoue, Tsuyu Ando, Ayahiko Shomura,<br />

Takehiko Shimizu, Izumi Kono, Saeko Konishi, Utako Yamanouchi,<br />

Tadamasa Ueda, Shin-ichi Yamamoto, and Takeshi Izawa<br />

Allelic and functional diversity of stress-tolerance genes in rice 73<br />

Hei Leung, Hehe Wang, Jianli Wu, Ma. Elizabeth Naredo,<br />

Marietta Baraoidan, Alicia Bordeos, Suzette Madamba, Gay Carrillo,<br />

Jatinder Sangha, Zenna Negussie, Jill Cairns, Bin Liu, Yolanda Chen,<br />

Darshan Brar, Il Ryong Choi, Cassiana Vera Cruz, Renee Lafitte,<br />

Luca Comai, and Kenneth L. McNally<br />

Functional genomics by reverse genetics 76<br />

Gynheung An<br />

Tissue culture-induced mutations and a new type of activation tagging 78<br />

as tools for functional analysis of rice genes<br />

Hirohiko Hirochika<br />

Toward genome-wide transcriptional analysis in rice using MAS 80<br />

oligonucleotide tiling-path microarrays<br />

Lei Li, Xiangfeng Wang, Xueyong Li, Ning Su, Viktor Stolc, Bin Han,<br />

Jiayang Li, Yongbiao Xue, Jun Wang, and Xing Wang Deng<br />

Candidate gene characterization at the Pup1 locus: a major QTL increasing 83<br />

tolerance of phosphorus deficiency<br />

Matthias Wissuwa, Kristy Gatdula, and Abdelbagi Ismail<br />

Wrap-up of Session 2 85<br />

SESSION 3<br />

Opportunities and challenges of transgenic rice<br />

Overproduction of C 4<br />

enzymes in transgenic rice: an approach for improved 88<br />

photosynthesis and crop yield<br />

Mitsue Miyao-Tokutomi and Hiroshi Fukayama<br />

The uptake and translocation of minerals in rice plants 90<br />

Naoko K. Nishizawa<br />

Improving drought and cold-stress tolerance in transgenic rice 94<br />

Kazuko Yamaguchi-Shinozaki and Kazuo Shinozaki<br />

Broad-spectrum disease resistance in transgenic rice 97<br />

Motoshige Kawata<br />

Golden <strong>Rice</strong> and improvement of human nutrition 99<br />

Swapan Datta, Vilas Parkhi, Mayank Rai, Jing Tan, Niranjan Baisakh,<br />

Lina Torrizo, Editha Abrigo, Norman Oliva, Md. Alamgir Hossain,<br />

Russel Julian, Anindya Bandyopadhyay, and Karabi Datta<br />

Health-promoting transgenic rice suppressing life-related disease 102<br />

and type-I allergy<br />

Fumio Takaiwa<br />

Producing rice plants with a site-specific base change in the acetolactate 105<br />

synthase gene by chimeraplast-directed gene targeting<br />

A. Okuzaki and K. Toriyama<br />

Transgenic rice plants expressing wheat catalase show improved 108<br />

tolerance for chilling-induced damage in membranes<br />

Haruo Saruyama, Hidenori Onodera, and Matsuo Uemura<br />

Wrap-up of Session 3 110<br />

iv<br />

<strong>Rice</strong> is life: scientific perspectives for the 21st century


SESSION 4<br />

Improving the rice yield potential<br />

Photosynthesis improvement in rice: Rubisco as a target for enhancing 114<br />

N-use efficiency<br />

Amane Makino<br />

Carbon metabolism to improve sink and source function 116<br />

R. Ohsugi<br />

Improving radiation-use efficiency: the acclimation of photosynthesis 118<br />

to high irradiance in rice leaves<br />

E.H. Murchie, S. Hubbart, S. Peng, and P. Horton<br />

Sink-source relationship and yield potential of rice: effect of ethylene 120<br />

on grain filling of late-flowering spikelets<br />

P.K. Mohapatra and Rashmi Mohapatra<br />

Impact of increased source capacity on rice yield: a case study 124<br />

with CO 2<br />

enrichment<br />

Toshihiro Hasegawa, Kazuhiko Kobayashi, Mark Lieffering, Han Yong Kim,<br />

Hidemitsu Sakai, Hiroyuki Shimono, Yasuhiro Yamakawa, Mayumi Yoshimoto,<br />

and Masumi Okada<br />

Possibilities for and constraints to improving canopy photosynthesis 127<br />

J.E. Sheehy, A.V. Elmido, P. Pablico, M.J.A. Dionora, and A.B. Ferrer<br />

Progress in breeding the new plant type for yield improvement: 130<br />

a physiological view<br />

Shaobing Peng, Rebecca C. Laza, Romeo M. Visperas,<br />

Gurdev S. Khush, and Parminder Virk<br />

Current status and prospects of rice breeding for increased yield in China 132<br />

Wan Jianmin<br />

A large-grain rice cultivar, Akita 63, exhibits high yield and N-use efficiency 135<br />

for grain production<br />

Tadahiko Mae, Ayako Inaba, Yoshihiro Kaneta, Satoshi Masaki,<br />

Mizuo Sasaki, and Amane Makino<br />

Using heterosis and hybrid rice to increase yield potential in China 138<br />

Xuhua Zhong, Shaobing Peng, Feng Wang, and Nongrong Huang<br />

Breeding and prevalence of japonica hybrid rice variety Mitsuhikari 140<br />

Atsushi Nakamura<br />

Dry-matter production and nitrogen distribution in a female-sterile line of rice 142<br />

Morio Kato, Sachio Maruyama, and Masao Yokoo<br />

Cytokinin as a causal factor of varietal differences in the reduction in leaf level 145<br />

of ribulose-1,5-bisphosphate carboxylase/oxygenase during senescence<br />

in rice plants<br />

Taiichiro Ookawa, Yukiko Naruoka, Ayumi Sayama, and Tadashi Hirasawa<br />

Measurement and evaluation of rice plant type by means of an image 148<br />

analysis method and a 3-D digitizer<br />

Masaaki Oka and Takashi Ogawa<br />

Wrap-up of Session 4 150<br />

SESSION 5<br />

Broadening the gene pool and exploiting heterosis in cultivated rice<br />

Developing aerobic rice in Brazil 154<br />

B. da S. Pinheiro, E. da M. de Castro, O.P. de Moraes, and F. Breseghello<br />

Broadening the gene pool of rice through introgression from wild species 157<br />

D.S. Brar<br />

Mutation in seed reserves and its use for improving grain quality in rice 160<br />

Hikaru Satoh, Ken-ichi Ohtsubo, and Yasunori Nakamura<br />

Heterosis in rice for increasing yield, production efficiency, 162<br />

and rural employment opportunities<br />

Sant S. Virmani<br />

Contents<br />

v


Harnessing molecular markers in hybrid rice commercialization in the Philippines 166<br />

E.D. Redoña, L.M. Perez, L.R. Hipolito, V.E. Elec, I.A. Pacada, L.M. Borines,<br />

R.O. Solis, S.A. Ordoñez, and J. Agarcio<br />

Genetic evolution of Rf1 locus for the fertility restorer gene of BT-type CMS rice 170<br />

Tomohiko Kazama and Kinya Toriyama<br />

A polygenic balance model in yield components as revealed by QTL analysis 172<br />

in rice<br />

Wilhelm E. Hagiwara, Kazumitsu Onishi, Itsuro Takamure, and Yoshio Sano<br />

Wrap-up of Session 5 174<br />

SESSION 6<br />

Trends in crop establishment and management in Asia<br />

Trends in crop establishment methods in Asia and research issues 178<br />

Sushil Pandey and Lourdes Velasco<br />

Direct seeding and weed management in Korea 181<br />

Soon-Chul Kim and Woon-Goo Ha<br />

Direct-seeding cultivation of rice in Japan: stabilization of seedling establishment 184<br />

and improvement of lodging resistance<br />

Satoshi Yoshinaga<br />

Direct seeding of aerobic rice in China 186<br />

Guang Hui Xie, Jun Yu, Jing Yan, Huaqi Wang, and Xiurong Zhu<br />

An overview on direct seeding for rice crop establishment in the Philippines 189<br />

Jovino L. de Dios, Evelyn F. Javier, Myrna D. Malabayabas,<br />

Madonna C. Casimero, Alex J. Espiritu<br />

<strong>Rice</strong> establishment in drought-prone areas of Bangladesh 193<br />

M.A. Mazid, M.A. Mortimer, C.R. Riches, A. Orr, B. Karmaker,<br />

A. Ali, M.A. Jabbar, and L.J. Wade<br />

Emerging issues in weed management of direct-seeded rice in Malaysia, 196<br />

Vietnam, and Thailand<br />

M. Azmi, D. V. Chin, P. Vongsaroj, and D.E. Johnson<br />

Changing from transplanted rice to direct seeding in the rice-wheat 198<br />

cropping system in India<br />

Y. Singh, Govindra Singh, David Johnson, and Martin Mortimer<br />

Seedling recruitment in direct-seeded rice: weed biology and water management 202<br />

A.M. Mortimer, O. Namuco, and D.E. Johnson<br />

The crop protection industry’s view on trends in rice crop establishment 205<br />

in Asia and their impact on weed management techniques<br />

Jean-Louis Allard, Kee Fui Kon, Yasuo Morishima, and Ruediger Kotzian<br />

Improved anchorage and bird protection with iron-coated seeds 209<br />

in wet direct seeding of rice crops<br />

Minoru Yamauchi<br />

Issues for integrated weed management and decision support 211<br />

in direct-seeded rice<br />

D.E. Johnson and A.M. Mortimer<br />

Control of Leptochloa chinensis (L.) Nees in wet-seeded rice fields in Sri Lanka 215<br />

Anuruddhka S.K. Abeysekera and U.B. Wickrama<br />

Village-level modeling of environment-friendly and appropriate 217<br />

technologies and practices for direct seeding<br />

Rowena G. Manalili, Bernard D. Tadeo, Emmanuel R. Tiongco,<br />

Wilfredo B. Collado, Rodolfo V. Bermudez, Constancio A. Asis,<br />

Jovino L. De Dios, Marvin F. Adap, Mario dela Cruz, Ulysses G. Duque,<br />

Leonardo V. Marquez, Cheryll B. Casiwan, Roy F. Tabalno,<br />

Placida C. Lanuza, and Belen C. Tejada<br />

Wrap-up of Session 6 220<br />

vi<br />

<strong>Rice</strong> is life: scientific perspectives for the 21st century


SESSION 7<br />

Improving efficiency through innovations in mechanization<br />

<strong>Rice</strong> as a key resource for saving our planet 224<br />

Nobutaka Ito<br />

Mechanizing paddy rice cultivation in Korea 225<br />

Woo-Pung Park and Sang-Cheol Kim<br />

The status and prospects of rice production mechanization in China 228<br />

Li Yaoming<br />

The Phil<strong>Rice</strong>-JICA rotary rice reaper: redesigning a technology for Filipino 229<br />

farmers and manufacturers<br />

Eulito Bautista, Manuel Jose Regalado, Arnold Juliano, Shuji Ishihara,<br />

Hiroyuki Monobe, Joel Ramos, and Leo Molinawe<br />

Long-mat seedling culture and the transplanting system: an innovative 232<br />

one-person operational technology for mechanical rice transplanting<br />

Hisashi Kitagawa, Akio Ogura, Kouhei Tasaka, Hiroyuki Shiratsuchi,<br />

and Mikio Yashiro<br />

High-precision autonomous operation using an unmanned rice transplanter 235<br />

Yoshisada Nagasaka, Yutaka Kanetani, Naonobu Umeda, and Takuo Kokuryu<br />

Precision-drilling methods for the direct sowing of rice in flooded paddy fields 238<br />

Yoh Nishimura, Kazunobu Hayashi, Takashi Goto, and Mitsuhiro Horio<br />

The rice direct-seeding system using multiple seed pellets in northern Tohoku 241<br />

Hiroyuki Sekiya, Hitoshi Ogiwara, Shoichi Kimura, Ryuji Otani,<br />

Yukio Yaji, Satoshi Morita, Tatsushi Togashi, and Hiroaki Watanabe<br />

Wrap-up of Session 7 243<br />

SESSION 8<br />

Improving rice quality<br />

The chemical basis of rice end-use quality 246<br />

Kshirod R. Bhattacharya<br />

Improving rice grain quality in Thailand 248<br />

Kunya Cheaupun, Sunantha Wongpiyachon, and Ngamchuen Kongseree<br />

New tools for understanding starch synthesis 251<br />

Melissa Fitzgerald, Jeffrey Castro, Rosa Paula Cuevas, and Robert Gilbert<br />

Textural differences between indica and japonica varieties in cooked rice 253<br />

Keiko Hatae, Sonoko Ayabe, and Midori Kasai<br />

Biological efficacy of consuming rice biofortified with iron 256<br />

J. Haas, J. Beard, A. Del Mundo, G. Gregorio, L.M. Kolb, and A. Felix<br />

Radical-scavenging activity of red and black rice 256<br />

Tomoyuki Oki, Mami Masuda, Saki Nagai, Miwako Take’ichi,<br />

Mio Kobayashi, Yoichi Nishiba, Terumi Sugawara, Ikuo Suda,<br />

and Tetsuo Sato<br />

A rice mutant with enhanced amylose content in endosperm derived 260<br />

from low-amylose variety Snow Pearl: isolation and characterization<br />

Yasuhiro Suzuki, Hiro-Yuki Hirano, Yoshio Sano, Kazuo Ise,<br />

Ushio Matsukura, Noriaki Aoki, and Hiroyuki Sato<br />

The role of the water-soluble fraction in rice pasting behavior 261<br />

Tadashi Yoshihashi, Eizo Tatsumi, Vipa Surojanametakul,<br />

Patcharee Tungtrakul, and Warunee Varanyanond<br />

Wrap-up of Session 8 265<br />

SESSION 9<br />

Developing new uses of rice<br />

Overview of rice and rice-based products 268<br />

Bienvenido O. Juliano<br />

Sterilization effect of electrolyzed water on rice food 270<br />

Seiichiro Isobe, Chang-yong Lee, and Kyoichiro Yoshida<br />

Current status of varietal improvement and use of specialty rice in Korea 272<br />

Hae Chune Choi<br />

Contents<br />

vii


Processed novel foodstuffs from pregerminated brown rice 275<br />

by a twin-screw extruder<br />

Ken’ichi Ohtsubo, Tomoya Okunishi, and Keitaro Suzuki<br />

High-pressure food processing of rice and starch foods 278<br />

Rikimaru Hayashi<br />

Developing novel processes for incorporating the unique nutritional 280<br />

and functional properties of rice into value-added products<br />

Elaine T. Champagne, Harmeet S. Guraya, Frederick F. Shih,<br />

and Ranjit S. Kadan<br />

Dehydrin proteins in rice bran 283<br />

Michiko Momma<br />

Physicochemical properties of modified rice flour and its use 285<br />

for processed food<br />

T. Takahashi, M. Miura, N. Ohisa, K. Mori, and S. Kobayashi<br />

Introducing soybean β-conglycinin genes into rice to improve nutritional 288<br />

and physiological value<br />

Takayasu Motoyama, Nobuyuki Maruyama, Takahiko Higasa,<br />

Masaaki Yoshikawa, Fumio Takaiwa, and Shigeru Utsumi<br />

Wrap-up of Session 9 291<br />

SESSION 10<br />

Postharvest technology for efficient processing and distribution of rice<br />

Postharvest technology for rice in India: a changing scenario 294<br />

Pallab Kumar Chattopadhyay<br />

Development of a far-infrared radiation dryer for grain 296<br />

Yasuyuki Hidaka, Kotaro Kubota, and Tomohiko Ichikawa<br />

Status of rice milling and use of by-products 299<br />

Naoto Shimizu, Yuji Katsuragi, and Toshinori Kimura<br />

Advanced application technology of rice bran: preparation of ferulic acid 301<br />

and its applications<br />

Hisaji Taniguchi, Eisaku Nomura, and Asao Hosoda<br />

New movements regarding the safety of rice and residual agrochemical inspection 304<br />

Yukio Hosaka<br />

Impact of infrastructure on profitability and global competitiveness 307<br />

of rice production in the Philippines<br />

Rowena G. Manalili and Leonardo A. Gonzales<br />

Development of an on-farm rice storage technique using fresh chilly air and 310<br />

preservation of high-quality rice<br />

Shuso Kawamura, Kazuhiro Takekura, and Kazuhiko Itoh<br />

Life-cycle inventory analysis of local parboiling processes 313<br />

Poritosh Roy, Naoto Shimizu, Takeo Shiina, and Toshinori Kimura<br />

Using genetics to create changes in rice cooking, processing, storage, 315<br />

and health-beneficial properties<br />

Christine Bergman<br />

The role of proteins in textural changes in aged rice 318<br />

Toshihisa Ohno, Takahiro Kaneko, and Naganori Ohisa<br />

Postharvest technology of rice: the role of farm women in storing grains 320<br />

with different storage practices<br />

P. Sumathi and M.N. Budhar<br />

Wrap-up of Session 10 322<br />

SESSION 11<br />

Enhancing the multifunctionality of rice systems<br />

Multifunctional roles of paddy irrigation in monsoon Asia 324<br />

Takao Masumoto<br />

Accounting for culture in paddy cultivation: toward a broader definition 327<br />

of “livelihood”<br />

David Groenfeldt<br />

viii<br />

<strong>Rice</strong> is life: scientific perspectives for the 21st century


The need to keep irrigated rice culture sustainable 329<br />

Nyoman Sutawan<br />

Multifunctional roles of irrigation water and rice fields in Dujiangyan, China 331<br />

Liu Yulong, Yamaoka Kazumi, and Ren Yonghuai<br />

Decommissioning of paddy lands in the Wet Zone of Sri Lanka: 334<br />

some effects on food security and ecosystems<br />

Kusum Athukorala and Missaka Hettiarachchi<br />

True agro-biodiversity depending on irrigated rice cultivation as a multifunction 337<br />

of paddy fields<br />

Kazumasa Hidaka<br />

Enhancing the multifunctionality of floating-rice farming in the Chao Phraya 340<br />

delta of Thailand<br />

Yuyama Yoshito, Ogawa Shigeo, and Ueda Tatsuki<br />

Demonstration program on multifunctionality of paddy fields 343<br />

in the northeastern region of Thailand<br />

Chatchai Boonlue<br />

Remediation effect of rice terraces for strong acidic and nitrate-rich 346<br />

effluent water from tea bush areas in the Makinohara plateau<br />

of Shizuoka, Japan<br />

Kiyoshi Matsuo, Yuhei Hirono, and Kunihiko Nonaka<br />

W<strong>here</strong> are the hot spots of RDB plants in rice paddy fields A GIS-based 347<br />

analysis using information accumulated at a natural history museum<br />

Takuya Mineta, Kenji Ishida, and Takashi Iijima<br />

Wrap-up of Session 11 349<br />

SESSION 12<br />

Conservation of soil, water, and environment in rice culture<br />

Paddy soils around the world 352<br />

K. Kyuma<br />

Sustainability of paddy soil fertility in Vietnam 354<br />

Ngo Ngoc Hung, Nguyen Bao Ve, Roland J. Buresh, Mark Bayley,<br />

and Takeshi Watanabe<br />

Managing soil fertility for sustainable rice production in northeast Thailand 357<br />

Kunnika Naklang<br />

Site-specific nutrient management and the sustainability of phosphorus 360<br />

and potassium supply in irrigated rice soils of Asia<br />

C. Witt, A. Dobermann, R. Buresh, S. Abdulrachman, H.C. Gines,<br />

R. Nagarajan, S. Ramanathan, P.S. Tan, and G.H. Wang<br />

Ecological engineering for sustainable rice production and the restoration 363<br />

of degraded watersheds in West Africa<br />

Toshiyuki Wakatsuki, Md. Moro Buri, and Oluwarotimi O. Fashola<br />

Nitrogen cycling under the rice-wheat rotation and environmental effects 367<br />

Jian-guo Zhu, Xiaozhi Wang, Zu-cong Cai, Ren Gao, and Yasukazu Hosen<br />

Urea deep placement increases yield and saves nitrogen fertilizer 369<br />

in farmers’ fields in Bangladesh<br />

W.T. Bowen, R.B. Diamond, U. Singh, and T.P. Thompson<br />

New fertilizer management to maximize yield and minimize environmental 372<br />

effects in rice culture<br />

Masahiko Saigusa<br />

Does anaerobic decomposition of crop residues impair soil nitrogen 374<br />

cycling and yield trends in lowland rice<br />

D.C. Olk, K.G. Cassman, M.M. Anders, K. Schmidt-Rohr, and J.-D. Mao<br />

Influence of the paddy-upland rotation on soil physico-chemical properties 377<br />

and crop growth in the Honam Plain of Korea<br />

Lee Deog-Bae, Yang Chang-Hyu, Ryu Chul-Hyun, Lee Kyeong-Bo,<br />

and Kim Jae-Duk<br />

A decrease in soil fertility and crop productivity by succession of 379<br />

the paddy-upland rotation<br />

Hirokazu Sumida<br />

Contents<br />

ix


Promising technologies for reducing cadmium contamination in rice 381<br />

Satoru Ishikawa<br />

N uptake inhibition of the rice plant in flooded soils receiving wheat straw 384<br />

Fukuyo Tanaka<br />

Stable isotope ratios of hydrogen and oxygen in paddy water affected 386<br />

by evaporation<br />

Yohei Hamada, Shiho Yabusaki, Norio Tase, and Ichiro Taniyama<br />

Erosion control by sawah in comparison to other land-use systems 388<br />

Fahmuddin Agus and Irawan<br />

Wrap-up of Session 12 390<br />

SESSION 13<br />

Farmers’ participatory approaches to facilitate adoption of improved technology<br />

How does a farmer accept a new technology 394<br />

Fujihiko Tozawa<br />

Farmer participatory evaluation of nitrogen management technology: the case 395<br />

of the leaf color chart in West Bengal, India<br />

B. Bagchi, M.Z. Abedin, and S.K.T. Nasar<br />

A farmer participatory approach in the adaptation and adoption of controlled 397<br />

irrigation for saving water: a case study in Canarem, Victoria, Tarlac,<br />

Philippines<br />

F.G. Palis, M. Hossain, B.A.M. Bouman, P.A.A. Cenas, R.M. Lampayan,<br />

A.T. Lactaoen, T.M. Norte, V.R. Vicmudo, and G.T. Castillo<br />

Companion modeling and multi-agent systems for collective learning 401<br />

and resource management in Asian rice ecosystems<br />

F. Bousquet and G. Trébuil<br />

Participatory approaches for improving rice breeding in the Mekong Delta 404<br />

of Vietnam<br />

Nguyen Ngoc De and Kotaro Ohara<br />

<strong>IRRI</strong>’s approach to participatory research for development: advances 408<br />

and limitations<br />

Thelma R. Paris and M. Zainul Abedin<br />

A participatory approach for building sustainable rice-farming systems 411<br />

in the reclaimed farmland of Ogata, Japan<br />

Yoshimitsu Taniguchi and Satoru Sato<br />

<strong>Rice</strong> farmers’ participatory research has played a key role 412<br />

in implementing the System of <strong>Rice</strong> Intensification<br />

Dandu Jagannadha Raju<br />

Wrap-up of Session 13 415<br />

SESSION 14<br />

Potentials for diversification in rice-based systems to enhance rural livelihoods<br />

Agricultural diversification in Asia: opportunities and constraints 420<br />

Prabhu Pingali<br />

Consequences of technologies and production diversification for 422<br />

the economic and environmental performance of rice-based farming<br />

systems in East and Southeast Asia<br />

Huib Hengsdijk, Marrit van den Berg, Reimund Roetter, Wang Guanghuo,<br />

Joost Wolf, Lu Changhe, and Herman van Keulen<br />

Rural poverty and agricultural diversification in Thailand 425<br />

Alia Ahmad and Somporn Isvilanonda<br />

Sustaining higher efficiency in rice production 428<br />

Amelia S. delos Reyes, Arelene Julia B. Malabayabas,<br />

and Mercedita A. Sombilla<br />

Determinants of agricultural diversification in Vietnam: changes 432<br />

at the farm level in the Mekong and Red River deltas<br />

Magnus Jirström and Franz-Michael Rundquist<br />

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<strong>Rice</strong> is life: scientific perspectives for the 21st century


Growth of the rural nonfarm economy in Bangladesh: determinants and impact 436<br />

on poverty reduction<br />

Mahabub Hossain<br />

SESSION 15<br />

Challenges to expanding rice production in unfavorable environments<br />

In vitro selection of somaclonal and gametoclonal variants for salt tolerance 442<br />

in rice<br />

Nguyen Thi Lang, Dang Minh Tam, Hiromi Kobayashi, and Bui Chi Buu<br />

Submergence damage in rice and challenges in expanding the crop’s 445<br />

adaptability to submerged conditions in West and Central Africa<br />

Koichi Futakuchi<br />

Ecological, morphological, and physiological aspects of drought adaptation 448<br />

of rice in upland and rainfed lowland systems<br />

Shu Fukai and Akihiko Kamoshita<br />

Managing iron toxicity in lowland rice: the role of tolerant genotypes 452<br />

and plant nutrients<br />

Kanwar L. Sahrawat<br />

Soil acidity and related problems in upland rice in the tropics 454<br />

Kensuke Okada and Matthias Wissuwa<br />

The physiological foundation of crop breeding for stress environments 456<br />

A. Blum<br />

Expression of a serine protease during microsporogenesis in rice 458<br />

Kentaro Kawaguchi, Naoshi Dohmae, Shuichi Matsuba,<br />

Hideyuki Funatsuki, Yutaka Sato, and Masao Ishimoto<br />

Responses to chilling temperature at the early stage of development 460<br />

in rice: geographical clines and genetic bases as revealed by QTL analysis<br />

Kazumitsu Onishi, Noriko Ishigoh-Oka, Mieko Adachi, and Yoshio Sano<br />

QTL analysis on plasticity in lateral root development in response 463<br />

to water stress in the rice plant<br />

Hong Wang, Yoshiaki Inukai, Akihiko Kamoshita, Len Wade,<br />

Joel Siopongco, Henry Nguyen, and Akira Yamauchi<br />

Wrap-up of Session 15 465<br />

SESSION 16<br />

Pest management with minimal environmental stress<br />

Integrated biodiversity management (IBM) in rice fields 468<br />

Keizi Kiritani<br />

Habitat manipulation in sustainable pest management in the rice ecosystem 470<br />

of the Yangtze River Delta<br />

Xiaoping Yu, Jianming Chen, Zhongxian Lu, Xusong Zheng, Hongxin Xu,<br />

Juefeng Zhang<br />

Evaluating augmentative releases of the mirid bug Cyrtorhinus lividipennis 473<br />

to suppress brown planthopper Nilaparvata lugens in open paddy fields<br />

Masaya Matsumura, Satoru Urano, and Yoshito Suzuki<br />

Developing a rice production system for sustainable pest management 475<br />

T.W. Mew<br />

Evaluation of a leaf blast simulation model (BLASTMUL) for rice multilines 477<br />

in different locations and cultivars, and effective blast control using<br />

the model<br />

T. Ashizawa, M. Sasahara, A. Ohba, T. Hori, K. Ishikawa, Y. Sasaki,<br />

T. Kuroda, R. Harasawa, K.S. Zenbayashi, and S. Koizumi<br />

Association of candidate defense genes with quantitative resistance to rice blast 479<br />

and in silico analysis of their characteristics<br />

G. Carrillo, J. Wu, B. Liu, N. Sugiyama, I. Oña, M. Variar, B. Courtois,<br />

J.E. Leach, P.H. Goodwin, H. Leung, and C.M. Vera Cruz<br />

Transferring resistance genes among different cereal species 482<br />

Bingyu Zhao, Shavannor Smith, Jan Leach, and Scot Hulbert<br />

Contents<br />

xi


Screening of allelopathic activity from rice cultivars by bioassay and field test 484<br />

Yoshiharu Fujii, Hiroshi Araya, Syuntarou Hiradate, and Kaoru Ebana<br />

Evaluating near-isogenic lines with QTLs for field resistance to rice blast 487<br />

from upland rice cultivar Sensho through marker-aided selection<br />

Norikuni Saka and Shuichi Fukuoka<br />

Wrap-up of Session 16 490<br />

SESSION 17<br />

<strong>Rice</strong> supply and demand<br />

<strong>International</strong> trade in rice: recent developments and prospects 492<br />

Concepcion Calpe<br />

<strong>Rice</strong> in the world at stake 494<br />

Shoichi Ito<br />

<strong>Rice</strong> consumption in China: Can China change rice consumption 497<br />

from quantity to quality<br />

Chien Hsiaoping<br />

Surplus rice supply in Asia 499<br />

Vichai Sriprasert<br />

Review of existing global rice market models 502<br />

Eric J. Wailes<br />

Household rice consumption in Japan: quantity and price by income 505<br />

while controlling for household types<br />

Kimiko Ishibashi, Yoshinobu Kono, and Yuuji Ooura<br />

Wrap-up of Session 17 507<br />

SESSION 18<br />

Impact of globalization on rice farmers<br />

Impacts of distorted trade policies on rice productivity 510<br />

Manitra A. Rakotoarisoa<br />

A new strategy for group farming in Japan 513<br />

Kyoichi Miyatake<br />

The role of the rice economy after the implementation of agricultural 515<br />

policy reform and trade liberalization from the perspective of farmers:<br />

the case of rice farmers in Java, Indonesia<br />

Roosiana<br />

El Niño sensitivity, resource endowment, and socioeconomic characteristics: 517<br />

the case of wetland rice in Java, Indonesia<br />

Shigeki Yokoyama and Bambang Irawan<br />

Global competitiveness of medium-quality Indian rice: a PAM analysis 520<br />

B.V. Chinnappa Reddy, M.S. Raghavendra, and Lalith Achoth<br />

Behavior and strategies of Japanese rice producers under globalization 523<br />

Masaki Umemoto<br />

The future perspective of upland rice farmers in Indonesia in the era of 525<br />

globalization<br />

Yusman Syaukat and Sushil Pandey<br />

Impact of globalization on rice farmers in Thailand 527<br />

Rangsan Pitipunya<br />

The rice economy and rice policy in China 530<br />

Li Ninghui<br />

Wrap-up of Session 18 532<br />

SESSION 19<br />

Climate change and rice production<br />

Effects of elevated atmospheric CO 2<br />

concentration and increased temperature 536<br />

on rice: implications for Asian rice production<br />

T. Horie, H. Yoshida, S. Kawatsu, K. Katsura, K. Homma, and T. Shiraiwa<br />

Monitoring rice growth and development using a crop model: the case 539<br />

of northern Japan<br />

Masaharu Yajima<br />

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<strong>Rice</strong> is life: scientific perspectives for the 21st century


Coping with climate variability and change in rice production systems 542<br />

in the Philippines<br />

Felino P. Lansigan<br />

Effect of elevated CO 2<br />

on nutrient uptake and nutritional conditions of rice 545<br />

Jianguo Zhu<br />

Effect of soil properties, substrate addition, microbial inoculation, and 546<br />

sonication on methane production from three rice topsoils and subsoils<br />

in the Philippines<br />

Sudip Mitra and Deepanjan Majumdar<br />

Modeling the effects of farming management alternatives on greenhouse 551<br />

gas emissions: a case study for rice agriculture in China<br />

Changsheng Li, Steve Frolking, Xiangming Xiao, Berrien Moore III,<br />

Steve Boles, Yu Zhang, Jianjun Qiu, Yao Huang, William Salas,<br />

and Ronald Sass<br />

Impact of rising atmospheric CO 2<br />

on CH 4<br />

emissions from rice paddies 555<br />

Weiguo Cheng, Kazuyuki Yagi, Kazuyuki Inubushi, Kazuhiko Kobayashi,<br />

Hidemitsu Sakai, Han-Yong Kim, and Masumi Okada<br />

The detrimental effect of tropospheric O 3<br />

on lowland rice is ameliorated 557<br />

by elevated CO 2<br />

T. Ishioh, K. Kobori, and K. Imai<br />

Effects of topdressing on grain shape and grain damage under high temperature 560<br />

during ripening of rice<br />

Satoshi Morita, Osamu Kusuda, Jun-ichi Yonemaru, Akira Fukushima,<br />

and Hiroshi Nakano<br />

Wrap-up of Session 19 562<br />

SESSION 20<br />

Improving rice productivity through IT<br />

Data mining using combined yield and quality maps of paddy fields 566<br />

Tadashi Chosa<br />

A wireless sensor network with Field-Monitoring Servers and MetBroker 568<br />

in paddy fields<br />

Masayuki Hirafuji, Tokihiro Fukatsu, Hu Haoming, Takuji Kiura,<br />

Tominari Watanabe, and Seishi Ninomiya<br />

Prediction of airborne immigration of rice insect pests 571<br />

Akira Otuka, Tomonari Watanabe, Yoshito Suzuki, Masaya Matsumura,<br />

Akiko Furuno, and Masamichi Chino<br />

Distance education and eLearning for sustainable agriculture: 574<br />

lessons learned<br />

Robert T. Raab and Buenafe R. Abdon<br />

The <strong>Rice</strong> Knowledge Bank 576<br />

Mark Bell and David Shires<br />

Integrated information systems for crop research and improvement 579<br />

Graham McLaren, Arllet Portugal, Alexander Cosico, William Eusebio,<br />

Teri Ulat, May Ann Sallan, Victor Jun Ulat, and Richard Bruskiewich<br />

Using APAN for content delivery: possibilities for the CGIAR 583<br />

Paul O’Nolan<br />

A decision support system for site-specific nitrogen management 587<br />

of paddy rice<br />

Ryouji Sasaki, Kazunobu Toriyama, and Yoichi Shibata<br />

Wrap-up of Session 20 589<br />

Contents<br />

xiii


Foreword<br />

Just after World War II, rapid population growth with limited rice production led<br />

experts to predict starvation in Asia. On its own, the Food and Agriculture Organization<br />

(FAO) of the United Nations had declared 1966 the Year of <strong>Rice</strong> and numerous<br />

countries took measures to improve production, marketing, milling, and nutrition.<br />

Conferences were organized and scientific research and technology were stimulated.<br />

<strong>Rice</strong> is now the staple food for over half of the world’s population but its production<br />

faces many constraints under conditions of increasing world population and diminishing<br />

resources of water and land.<br />

The United Nations launched the <strong>International</strong> Year of <strong>Rice</strong> 2004 on 31 October<br />

2003. This is the second time that the United Nations has paid such a special<br />

tribute to rice, the only food crop honored twice. <strong>Rice</strong> is the single most important<br />

employment and income source for the rural poor. <strong>Rice</strong> will play a significant role in<br />

meeting the important UN Millennium Development Goal of poverty reduction in<br />

the world. Besides being an essential food, rice is also an important factor in enriching<br />

culture, lifestyles, and ecosystem functions. It is thus fitting that the United Nations<br />

pronounced 2004 the <strong>International</strong> Year of <strong>Rice</strong> to emphasize the important<br />

roles rice plays in the livelihoods and culture of humankind. <strong>Rice</strong> is a symbol of<br />

cultural identity, global unity, and life.<br />

To mark the Year of <strong>Rice</strong> 2004, the Ministry of Agriculture, Forestry, and Fisheries<br />

(MAFF) of Japan, research organizations affiliated with MAFF, and the <strong>International</strong><br />

<strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong> (<strong>IRRI</strong>) jointly financed and organized the World<br />

<strong>Rice</strong> <strong>Research</strong> Conference (WRRC) that was held in Tokyo and Tsukuba, Japan, 4-7<br />

November 2004. The WRRC had two parts: the Tokyo Opening Ceremony and Symposium<br />

in the Akasaka Prince Hotel graced by His Imperial Highness Crown Prince<br />

Naruhito of Japan on 4 November and the <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> Conference at<br />

the Tsukuba Congress Center on 5-7 November.<br />

The WRRC attracted 1,274 participants from 43 nations, who presented 190<br />

scientific papers and 302 posters in 20 sessions and 6 workshops. Scientific themes<br />

covered genomics to climate change and involved scientists with expertise in genes<br />

to ecosystems. Such a broad range of subjects discussed during the conference makes<br />

the WRRC one of the most significant scientific events of the last few decades. Scientists<br />

presented their latest concepts, research findings, and products, which are<br />

captured in the topics presented in this proceedings. The proceedings contains the<br />

state of the art in rice science and production that we hope will be useful to rice<br />

scientists, extension specialists, development agents, and policymakers who will use<br />

this to better the lives of all humans, but especially those of poor farmers and consumers.<br />

AKINORI NOGUCHI<br />

Vice president of the Japan <strong>International</strong> <strong>Research</strong> Center<br />

for Agricultural Sciences and chairman<br />

of the WRRC 2004 Organizing Committee<br />

xiv<br />

<strong>Rice</strong> is life: scientific perspectives for the 21st century


Acknowledgments<br />

The success of the World <strong>Rice</strong> <strong>Research</strong> Conference (WRRC) was due largely to the<br />

constant endeavor of many individuals and organizations. The framework of this<br />

conference was set up by the executive committee composed of the Division of <strong>International</strong><br />

<strong>Research</strong> in the Secretariat of Agriculture, Forestry, and Fisheries <strong>Research</strong><br />

Council of the Ministry of Agriculture, Forestry, and Fisheries (MAFF) and the presidents<br />

of co-sponsoring research institutes as well as the delegate from the <strong>International</strong><br />

<strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong> (<strong>IRRI</strong>).<br />

The organizing committee consisted of A. Noguchi and Y. Morokoka (Japan<br />

<strong>International</strong> <strong>Research</strong> Center for Agricultural Sciences, JIRCAS) as chairs, with<br />

seven representatives from the co-sponsoring research institutes: T. Imbe (National<br />

Agricultural and Bio-oriented <strong>Research</strong> Organization, NARO), K. Okuno (National<br />

<strong>Institute</strong> of Agrobiological Sciences; NIAS), M. Oka (National <strong>Institute</strong> for Agro-<br />

Environmental Sciences, NIAES), Y. Tsutsui (National <strong>Institute</strong> of Rural Engineering,<br />

NIRE), T. Imai (National Food <strong>Research</strong> <strong>Institute</strong>, NFRI), Y. Yunoki (MAFF),<br />

and K.L. Heong (<strong>IRRI</strong>). Special thanks are due to M. Iwamoto, former president of<br />

JIRCAS, and E. Miwa, president of NARO, for their valuable suggestions and constant<br />

encouragement.<br />

The secretariat was successfully handled by JIRCAS personnel headed by O.<br />

Ito, with R. Ikeda, T. Kumashiro, K. Toriyama, K. Yasunobu, T. Uetani, H. Fujii, S.<br />

Tsuchiya, R. Saito, H. Tanaka, T. Hatta, Y. Hamada, and H. Miura. For Web management,<br />

E. Hettel (<strong>IRRI</strong>) and H. Miura (JIRCAS) contributed significantly. Special<br />

appreciation goes to <strong>IRRI</strong> personnel: K.L. Heong for coordinating with <strong>IRRI</strong> and the<br />

JIRCAS secretariat and giving much useful advice for the success of the WRRC, D.<br />

Macintosh for press releases, and B. Hardy for editorial work on the manuscripts of<br />

this large proceedings.<br />

The conveners of each session organized and provided a first review of the<br />

papers from their respective session contributers. Without their strong efforts, the<br />

WRRC could not have succeeded. These are K. Okuno and R.S. Hamilton for S1; T.<br />

Sasaki, H. Hirochika, and H. Leung for S2; F. Takaiwa, S. Oka, and S. Datta for S3;<br />

M. Kondo, H. Ikehashi, and S. Peng for S4; Y. Fukuta, D. Mackill, and R. Ikeda for<br />

S5; M. Yamauchi and D. Johnson for S6; N. Itokawa and J. Rickman for S7; U.<br />

Matsukura for S8; K. Otsubo for S9; T. Kimura and J. Rickman for S10; Y. Tsutsui<br />

and K. Yamaoka for S11; M. Saito, S. Ito, and T. Nozoe for S12; T. Paris and J.<br />

Caldwell for S13; M. Hossain for S14; S. Tobita and R. Lafitte for S15; C. Vera Cruz<br />

and Y. Suzuki for S16; O. Koyama and D. Dawe for S17; M. Umemoto and D. Dawe<br />

for S18; T. Imagawa, T. Hasegawa, Y. Hayashi, and J. Sheehy for S19; and S. Ninomiya<br />

and M. Bell for S20.<br />

This conference was supported by different academic societies and it attracted<br />

many participants of different disciplines. These were the Japan Society of Breeding,<br />

Crop Science Society of Japan, Japanese Society of Soil Science and Plant Nutrition,<br />

the Japanese Society of Irrigation, Drainage, and Reclamation Engineering, the Japanese<br />

Society of Agricultural Machinery, the Japanese Society of Applied Entomology<br />

and Zoology, the Phytopathological Society of Japan, Pesticide Science Society<br />

of Japan, the Farm Management Society of Japan, the Japanese Society for Food<br />

Contents<br />

xv


Science and Technology, the Society of Agricultural Meteorology of Japan, Japanese<br />

Society for Tropical Agriculture, and Science Council of Japan (National Committee<br />

for Rural Planning).<br />

Financial support was given by the Japan Science Promotion Society. Special<br />

thanks are also due to the Tsuchiura Tsukuba Convention Bureau and the <strong>International</strong><br />

Congress Center (Epochal Tsukuba).<br />

xvi<br />

<strong>Rice</strong> is life: scientific perspectives for the 21st century


Keynotes


The power of settled life: rice farming as a lifestyle<br />

Ken-ichi Matsumoto<br />

Folklorist Yanagida Kunio (1875-1962), known as the father<br />

of Japanese folklore study, once raised the question, “What is<br />

Japan” In his view, insularity and rice cultivation are the two<br />

key factors composing Japanese ethnicity. In other words,<br />

Yanagida sees our Japanese way of life as the result of being<br />

rice farmers on an island.<br />

I would like to add another factor to these two: settled<br />

life, rooted in a community and a plot of land.<br />

Some may argue that rice cultivation, either paddy rice<br />

or dry rice, is naturally coupled with a settled life and is too<br />

obvious to mention as a new factor. However, this is not so.<br />

If you see rice cultivation as a part of life deeply connected<br />

to ethnicity, being a rice farmer means living a settled<br />

life on specific parcels of land. However, if you see rice farming<br />

as an industry that generates profits, farmers may choose<br />

to plant strawberries instead of rice when profits are low, as<br />

happens in California. Furthermore, they may decide to sell<br />

their land to Disneyland and move to other areas. In this case,<br />

rice cultivation is not inevitably linked to a settled lifestyle.<br />

California rice farmers are not the only ones who choose<br />

alternate lifestyles. Another good example is Indonesia. Indonesia<br />

achieved 100% rice self-sufficiency in 1997. Soon, the<br />

farmers recognized that shrimp cultivation would triple their<br />

income and they turned their paddies into shrimp cultivation<br />

ponds. As a result, the self-sufficiency rate of rice dropped to<br />

80%.<br />

Now, let us focus on settled rice farming as an ethnic<br />

lifestyle. The reward of your life as a farmer is to sustain your<br />

paddies and paddy terraces passed down from your ancestors.<br />

Issho-kenmei, a Japanese idiom for “do your best,” literally<br />

means “maintain a piece of land for all your worth.” This idea<br />

has been supported as an ethnic ethos of Japanese. This describes<br />

why Japanese pay more respect to the process of “doing<br />

your best” than to getting good results or high profits.<br />

Sharing the ethos of issho-kenmei, people living in an<br />

area work together to dig drainage ditches, build irrigation systems,<br />

and weed the whole village. The working group unavoidably<br />

encourages the development of a community system.<br />

The Japanese call the community system work kou. Similar<br />

systems developed in Okinawa are called yui, and ke in<br />

Korea and ban in South China.<br />

In these community work systems, innovations and processes<br />

to increase productivity develop to improve ancestral<br />

farming land. In other words, the whole community is encouraged<br />

to exert an effort to breed crops and control the crops’<br />

quality, as well as construct drainage and irrigation systems<br />

for the community and weed the rice paddies.<br />

As another example, to harvest more crops on the same<br />

areas of land that their ancestors reclaimed, farmers must breed<br />

rice stocks more resistant to extreme temperature, drought, and<br />

disease. They also carry out thorough quality control by removing<br />

pests and weeds from the rice field, improving the<br />

rice paddy to create efficient irrigation and drainage conditions,<br />

and figuring out what the most suitable spaces are between<br />

rice plants.<br />

This lifestyle is very different from that of Western countries,<br />

w<strong>here</strong> productivity increased through territorial expansion.<br />

The Western ranchers’ way of adding new pastures outside<br />

the towns, in my opinion, demonstrates the principle of<br />

the “power to expand.” This naturally extends expansion to<br />

products and innovations in fields such as traffic technology,<br />

transportation, communication, and military affairs.<br />

On Earth today, we do not have any new land to expand<br />

onto. The natural environment is worsening, the population is<br />

exploding, and a food crisis is just around the corner.<br />

If we recognize this reality, isn’t this the time for us to<br />

remember “the power of inner accumulation,” traditionally cultivated<br />

by rice farming It is the wisdom of various ethnic<br />

groups to live on the same land for generations, thus increasing<br />

wealth in a village, and in a rice paddy, in a single rice<br />

grain. <strong>Rice</strong> farming will provide the core motive for the settled<br />

lifestyle we now seek.<br />

Notes<br />

Author’s address: Professor, Reitaku University.<br />

2 <strong>Rice</strong> is life: scientific perspectives for the 21st century


The role of rice in the Japanese diet<br />

Yoshiko Kagawa<br />

<strong>Rice</strong> is the starting point of Japanese food culture. In a traditional<br />

Japanese diet, the carbohydrates contained in rice are<br />

the main energy source. The average Japanese eats about 594<br />

kcal of rice and rice products per day, which is 31% of the<br />

average energy intake. <strong>Rice</strong> contains 6.1 g of protein per 100<br />

g, and, though this level is not so high, rice protein is superior<br />

in quality to wheat protein. T<strong>here</strong>fore, rice alone can support a<br />

person if that person eats enough of it. Even today, the Japanese<br />

receive 12% of their daily protein from rice, and decades<br />

ago many sustained their lives by eating only rice. That is why<br />

the Japanese call it shu-shoku, the principal food.<br />

The conventional Japanese diet also contains a variety<br />

of fuku-shoku, the side dishes served along with rice. These<br />

wholesome foods are economical, too. <strong>Rice</strong> at breakfast reduces<br />

the day’s food expense compared to popular Westernstyle<br />

breakfasts. Furthermore, a rice-based diet is healthier in<br />

nutritional balance.<br />

Although rice is an excellent food, a large problem involving<br />

a rice-rich diet exists: beriberi, a thiamine deficiency.<br />

This disease emerged with the grain polishing that produces<br />

white rice, intended to improve the digestion and taste of<br />

cooked rice. The process removes the rice germ that contains<br />

most of the naturally occurring vitamin B 1 . Some 0.42 mg of<br />

vitamin B 1 is required for the metabolism of 1,000 kcal of<br />

carbohydrates. T<strong>here</strong>fore, for people who try to sustain their<br />

diet mainly by rice, the relative shortage in vitamin B 1 develops<br />

into an absolute deficiency and causes beriberi.<br />

An adult male needs 1.1 mg of vitamin B 1 per day, and<br />

an adult female needs 0.7 mg. This is why young men who<br />

consume more food and energy are more likely to develop<br />

beriberi. In the 1920s and ’30s, when the Japanese diet depended<br />

much more on rice, beriberi killed more than 10,000<br />

people and terrified Japanese called it a “nation-ruining disease.”<br />

Beriberi is common to ethnic groups that eat rice as<br />

their principal food, and has often occurred in Southeast Asian<br />

countries, including Indonesia.<br />

It is easy to solve the thiamine problem: just change to<br />

“rice with the embryo,” produced by polishing the grain almost<br />

white but leaving the embryo. If one prefers white rice,<br />

eating vitamin B 1 -enriched rice and/or accompanying dishes<br />

rich in vitamin B 1 prevents beriberi. Getting enough vitamin<br />

B 1 is the first and major issue in a rice-based diet.<br />

The next point we must keep in mind in a rice-based diet<br />

is the imbalance in nutrition when one eats rice too much. White<br />

rice is most appetizing when accompanied by salty dishes.<br />

Because of this, one is more likely to develop unhealthy eating<br />

habits—consuming a small amount of salty food and eating<br />

a lot of white rice, thinking that white rice is the principal<br />

food. This eating pattern results in an overconsumption of salt.<br />

Sodium causes high blood pressure and a higher chance of<br />

stroke. In addition, this diet pattern often lacks food made from<br />

animal products that supply a certain amount of high-quality<br />

protein necessary to avoid a range of diseases.<br />

In the 1930s, physicians Shozo Kagawa and Aya Kagawa<br />

treating beriberi patients found a method to produce “rice with<br />

the embryo.” They promoted “rice with the embryo” to prevent<br />

beriberi, and founded an educational institute that later<br />

became the Kagawa Nutrition University. To help people remember<br />

the benefits of a balanced “rice with the embryo” diet,<br />

they made a campaign slogan: the principal food is “rice with<br />

the embryo,” accompanied by one fish, one bean, and four<br />

vegetables. This reminded people to eat 100 g of fish, 100 g of<br />

bean and bean products, and 400 g of vegetables a day.<br />

The idea of a food guideline based on food groups was<br />

new at the time. This eating method was widely accepted by<br />

the educated homemakers of Japan. After World War II, milk<br />

and milk products were introduced to school lunch programs.<br />

Children’s better health proved its effectiveness and milk was<br />

added to the list. This is how the well-known and popular “four<br />

food groups” method we use today developed.<br />

A rice-based diet has another advantage: rice is eaten as<br />

a form of grain. Grains are digested and taken into the body<br />

more slowly than milled cereals. T<strong>here</strong>fore, in spite of low-fat<br />

and low-calorie meals, one has a long-lasting feeling of satiety<br />

and less insulin is consumed. The key to the lower rate of diabetes<br />

in the Japanese population in the past seems to be rice.<br />

<strong>Rice</strong> is a delicious and handy food. I would like to emphasize<br />

that it is an excellent food if you avoid too much polishing and<br />

pay close attention to good nutritional balance.<br />

Notes<br />

Author’s address: President of Kagawa Nutrition University, Japan.<br />

Keynotes 3


A greeting<br />

Yoshinobu Shimamura<br />

The United Nations has designated 2004 as the <strong>International</strong><br />

Year of <strong>Rice</strong> (IYR) and countries around the world are joining<br />

hands to hold events to raise awareness about rice, which plays<br />

a major role in eliminating hunger and poverty in developing<br />

nations. Japan kicked off this special year with the <strong>International</strong><br />

Symposium to Celebrate IYR, which was sponsored by<br />

the Ministry of Agriculture, Forestry, and Fisheries in January.<br />

A variety of other events, spearheaded by the Japanese Committee<br />

for the <strong>International</strong> Year of <strong>Rice</strong> 2004, are being staged<br />

throughout the nation this year.<br />

<strong>Rice</strong> is not only the staple food of monsoon Asian; it<br />

also plays an important role in regional culture because of the<br />

idyllic agricultural villages that form around the beautiful paddies.<br />

The Japanese people’s lifestyle and society are based on<br />

rice and rice cultivation and have advanced thanks to the tireless<br />

efforts of farmers and researchers. <strong>Rice</strong> research has produced<br />

many technologies and varieties of rice and contributed<br />

greatly to the furtherance of our nation’s agriculture.<br />

<strong>Rice</strong> is the staple food of more than half of the world’s<br />

population, and about 1 billion households depend on rice cultivation<br />

for employment and their main source of livelihood.<br />

At the same time, approximately 800 million people in developing<br />

nations suffer from hunger. Most of the world popula-<br />

tion that suffers from hunger and poverty lives in Asia and<br />

Africa. New research findings related to rice are expected to<br />

help eradicate hunger and poverty among farmers and others<br />

in developing nations.<br />

To address these issues, Japan has provided cooperation<br />

to improve rice varieties and establish cultivation technologies<br />

in Asia. Our nation also plays a leadership role in rice<br />

research. In addition to working alongside ten other regions<br />

and countries to sequence the rice genome, Japan is engaged<br />

in research on New <strong>Rice</strong> for Africa (NERICA) in cooperation<br />

with international research institutes. To achieve the UN Millennium<br />

Development Goals, Japan will continue to promote<br />

research to meet international expectations.<br />

By holding the World <strong>Rice</strong> <strong>Research</strong> Conference during<br />

this memorable year, I am confident that we will strengthen<br />

cooperation among rice researchers throughout the world and<br />

further stimulate research to eradicate world hunger and poverty<br />

and solve environmental problems.<br />

Notes<br />

Author’s address: Minister of Agriculture, Forestry, and Fisheries,<br />

Japan.<br />

Statement by Jacques Diouf<br />

It is a privilege to address the distinguished participants of the<br />

World <strong>Rice</strong> <strong>Research</strong> Conference. I wish to thank the Ministry<br />

of Agriculture, Forestry, and Fisheries in Japan for organizing<br />

this important event and for its efforts to promote the <strong>International</strong><br />

Year of <strong>Rice</strong>, 2004.<br />

It is a pleasure to be with you today as we draw the attention<br />

of the world community to the vital role of rice in food<br />

security and poverty alleviation. I am confident that this opportunity<br />

will be used by the many individuals and representatives<br />

of countries and organizations and all those dedicated to<br />

sustainable rice production <strong>here</strong> today to share their thoughts<br />

and make further commitments toward enhancing sustainable<br />

rice-based production systems.<br />

On 16 December 2002, the United Nations General Assembly<br />

declared the year 2004 the <strong>International</strong> Year of <strong>Rice</strong><br />

(IYR). The dedication of an <strong>International</strong> Year to a single crop<br />

is unprecedented in the history of the UN General Assembly.<br />

This reflects not only the role of rice in food security and poverty<br />

alleviation but also the significance of rice in almost every<br />

culture and indeed in our world’s cultural heritage.<br />

About 842 million people, including millions of children<br />

worldwide, are undernourished. Hunger impedes development<br />

through malnutrition and disease. Hunger and poverty<br />

lead to increased susceptibility to illness and reduced capacity<br />

for work and concentration. The end result is even deeper poverty<br />

and hunger. Food security is essential to sustainable livelihoods<br />

and to maintain a peaceful environment. In this regard,<br />

rice plays a vital role in fighting hunger and promoting<br />

stability. <strong>Rice</strong> is the staple food for over half of the world’s<br />

population. Almost a billion households in Asia, Africa, and<br />

the Americas depend on rice-based systems as their main source<br />

of employment and livelihood. <strong>Rice</strong> is the most rapidly growing<br />

food source in Africa. About four-fifths of the world’s rice<br />

is produced by small-scale farmers in developing countries,<br />

and is consumed locally.<br />

<strong>Rice</strong> systems are hubs for biodiversity, including aquatic<br />

and terrestrial organisms, wildlife, livestock, and other crop<br />

varieties. This biodiversity is crucial for the environment, and<br />

contributes to sustainable livelihoods through increased rural<br />

income and improved human health. <strong>Rice</strong>-based production<br />

4 <strong>Rice</strong> is life: scientific perspectives for the 21st century


systems have been designed to support biodiversity, enabling<br />

intensive rice cultivation systems that include fisheries, livestock,<br />

and other plant species. Diversified agriculture and a<br />

more diversified diet promote improved nutrition, help to improve<br />

sustainable livelihoods, and provide protection for agricultural<br />

genetic resources.<br />

In declaring the <strong>International</strong> Year of <strong>Rice</strong>, the UN General<br />

Assembly reaffirms the need to focus world attention on<br />

the role that rice can play in providing food security and eradicating<br />

poverty in the attainment of the internationally agreedupon<br />

development goals, including those contained in the<br />

Millennium Declaration and the World Food Summit.<br />

A major objective of FAO and the IYR Steering Committee<br />

is to promote sustainable rice production and increased<br />

access to this vital food crop. Through the <strong>International</strong> <strong>Rice</strong><br />

Commission, FAO works closely with member governments,<br />

the international centers of the Consultative Group on <strong>International</strong><br />

Agricultural <strong>Research</strong> (CGIAR), and national agricultural<br />

research and extension systems (such as the Japan <strong>International</strong><br />

<strong>Research</strong> Center for Agricultural Sciences) to promote<br />

the sustainable development of rice-based production<br />

systems in order to alleviate poverty and hunger worldwide.<br />

In addition, FAO actively pursues partnerships with UN agencies,<br />

nongovernmental organizations, civil society, and the<br />

private sector to raise awareness, encourage information generation<br />

and exchange, and promote improved production and<br />

access to food.<br />

FAO recognizes, and appreciates, the role played by Japan<br />

in helping developing countries by promoting sustainable<br />

rice production during the Green Revolution in Asia and more<br />

recently in developing and disseminating NERICA rice in sub-<br />

Saharan Africa. The <strong>International</strong> Year of <strong>Rice</strong> and this World<br />

<strong>Rice</strong> <strong>Research</strong> Conference both recognize the potential for rice<br />

and rice-based production systems to improve human nutrition<br />

and food security around the globe.<br />

As the rice-consuming population continues to grow, and<br />

the land and water resources needed for rice production diminish,<br />

we face a potential crisis. World rice production has<br />

been less than rice consumption since 2000. This insufficiency<br />

has been addressed by drawing on rice from buffer stock. In<br />

this context, advances in science and technology, as well as<br />

rice research, are increasingly critical to enhance rice production<br />

and sustainable agricultural development. The successful<br />

mapping of the rice genome in 2002 has opened the way for<br />

potential scientific breakthroughs, but it has also created new<br />

issues related to biosafety, intellectual property rights, and<br />

access.<br />

Ensuring an increase in sustainable rice production will<br />

require innovation and cooperation within the scientific community,<br />

as well as commitment and shared responsibility among<br />

all stakeholders. The Global Plan of Action for the Conservation<br />

and Sustainable Use of Plant Genetic Resources for Food<br />

and Agriculture and the <strong>International</strong> Treaty on Plant Genetic<br />

Resources for Food and Agriculture provide a framework for<br />

global collaboration in the dissemination and use of rice genetic<br />

resources and protection of biodiversity. Capacity building<br />

within nations is urgently required to ensure that the innovations<br />

benefit local people and do not trigger long-term costs<br />

to the environment.<br />

Collaboration among institutions and stakeholders, from<br />

policymakers to farmers in the field, is imperative in order to<br />

promote scientific understanding and achieve effective, longterm<br />

improvements in rice production. This is the greatest challenge<br />

ahead. We must ensure that the fruits of our research,<br />

and the knowledge t<strong>here</strong>by gained, reach those hardest hit by<br />

hunger and poverty.<br />

In this regard, the World <strong>Rice</strong> <strong>Research</strong> Conference is<br />

very timely. It is an opportunity for those gat<strong>here</strong>d <strong>here</strong> to share<br />

their experience and knowledge, formulate initiatives, and<br />

confirm their commitment toward achieving global food security.<br />

It will address the challenges and opportunities that face<br />

us today.<br />

I would like to thank the government of Japan once again<br />

for hosting this conference, as well as the many leaders,<br />

policymakers, scientists, researchers, and other partners for<br />

their participation and efforts in the fight against hunger and<br />

poverty. I wish you a very successful and fruitful conference.<br />

Notes<br />

Author’s address: Director-General, Food and Agriculture Organization<br />

of the United Nations.<br />

Address by Imperial Highness Crown Prince Naruhito<br />

I am very pleased that the World <strong>Rice</strong> <strong>Research</strong> Conference is<br />

being held with rice researchers and other participants from<br />

Japan and overseas.<br />

<strong>Rice</strong> is an excellent crop that is the staple food for more<br />

than half of the world’s population. <strong>Rice</strong> has been cultivated<br />

in the Japanese archipelago since ancient times and has provided<br />

the Japanese people with the basis for a stable life. Every<br />

Japanese holds dear the idyllic scene of placid rice paddies,<br />

which have worked as dams by storing water, preserved<br />

the soil, and nurtured a great variety of living things. I am told<br />

that both at home and abroad the Japanese-style diet based on<br />

rice has come to be highly regarded in recent years as a very<br />

healthy diet. It is no exaggeration to say that rice cultivation<br />

has been the basis for the development of Japanese society<br />

and culture.<br />

The United Nations designated this year as the <strong>International</strong><br />

Year of <strong>Rice</strong>, and activities are under way throughout<br />

the world to raise awareness of the important role of rice in<br />

Keynotes 5


eliminating hunger and poverty. I believe that this conference<br />

is very significant as an opportunity for experts to discuss the<br />

production and use of rice and the many roles of rice paddies<br />

from the perspective of science and technology, and to consider<br />

the best avenues for future rice research.<br />

By bringing together the wisdom from all over the world<br />

and promoting active discussions from a wide range of perspectives,<br />

I hope that this conference will make a great contribution<br />

to solving the world’s food problems and protecting<br />

the global environment.<br />

New technologies for rice production<br />

Gurdev S. Khush<br />

Major advances have taken place in rice production during the<br />

last four decades because of the adoption of Green Revolution<br />

technology. <strong>Rice</strong> production increased 130% from 257 million<br />

tons in 1966 to 598 million tons in 1999. Average rice<br />

yield increased from 2.1 to 3.9 t ha –1 during the same period.<br />

In 2000, average per capita food availability was 18% higher<br />

than in 1966. W<strong>here</strong>as rice production increased at 3.0% and<br />

2.5% per annum during the 1970s and ’80s, respectively, the<br />

increase was only 1.5% during the 1990s. During the last four<br />

years, production has been stagnant. According to the <strong>International</strong><br />

Food Policy <strong>Research</strong> <strong>Institute</strong>, rice production must<br />

increase 38% by 2025 to feed 4 billion rice consumers.<br />

The area planted to rice is declining because of the pressure<br />

of urbanization and industrialization. Availability of water<br />

for agriculture is declining and labor is moving to industry.<br />

To meet the challenge of producing more rice under those constraints,<br />

we need new technologies. These include rice varieties<br />

with higher yield potential, greater yield stability, and<br />

adapted to changing global climate, as well as more efficient<br />

management practices.<br />

In addition to conventional hybridization and selection<br />

procedures, other strategies for developing rice varieties with<br />

higher yield potential include ideotype breeding, exploitation<br />

of heterosis, wide hybridization, molecular breeding, genetic<br />

engineering, and apomixis. Similarly, marker-aided selection<br />

and genetic engineering approaches are useful for developing<br />

rice varieties with more durable resistance to diseases and insects<br />

and tolerance of abiotic stresses such as drought, submergence,<br />

and salinity.<br />

Precision agriculture should lead to more sustainable increases<br />

in rice production, It is important to improve the efficiency<br />

of all production inputs such as nutrients and water and<br />

fine-tune the strategies for managing natural resources. Fertilizer<br />

is the most important input in crop production. Yet, areaspecific<br />

or regional fertilizer recommendations are based on<br />

short-term trials, which do not reflect the long-term impact of<br />

fertilizer use on the resource base. The chlorophyll meter is an<br />

excellent technique to measure the leaf N status of rice and to<br />

synchronize N application with crop demand. Water efficiency<br />

can be improved through its judicious use and zero tillage.<br />

Vast lands are unsuitable for crop production or have poor<br />

productivity because of soil problems such as salinity and alkalinity.<br />

Gypsum can be used to reclaim acidic and saline soils.<br />

Crop diversification is necessary to improve the productivity<br />

of intensively farmed soils with cereal crops. Crop rotations in<br />

addition to improving the soil structure show allelopathic effects<br />

through the release of chemical compounds directly in<br />

the soil or indirectly through microbial decomposition of residue,<br />

which affect the growth of another species. Integrated<br />

pest management (IPM) approaches have led to a reduction in<br />

the overuse and misuse of pesticides in rice production in a<br />

few countries. Universal adoption of IPM should lead to a reduction<br />

in the cost of rice production and more healthy rice.<br />

Notes<br />

Author’s address: Adjunct Professor, University of California, Davis.<br />

6 <strong>Rice</strong> is life: scientific perspectives for the 21st century


The changing economics and politics of rice:<br />

implications for food security, globalization,<br />

and environmental sustainability<br />

Joachim von Braun and María Soledad Bos<br />

For centuries, rice has been one of the world’s most important<br />

food crops. For the people of Asia in particular, rice has been<br />

the main source of calories and an important source of income<br />

and employment throughout most of their history. Furthermore,<br />

rice has shaped societies and cultures. Today, the cultivation,<br />

marketing, and consumption of rice are changing faster than<br />

ever before, yet t<strong>here</strong> are also strong forces working to stabilize<br />

and conserve rice systems. The economics and politics of<br />

rice are changing because of globalization, technological transformation<br />

of agriculture driven by science, and changing diets<br />

and tastes due to prosperity and urbanization. At the same time,<br />

rice remains the lifeline of many poor producers and consumers.<br />

Deeply embedded in established food systems, rice remains<br />

local and traditional and appears to be partially excluded<br />

from globalization trends. Thus, rice is a most modern food<br />

and a very traditional one at the same time.<br />

As 2004—the <strong>International</strong> Year of <strong>Rice</strong>, as declared by<br />

the United Nations—comes to a close, it is pertinent to address<br />

key issues about the emerging changes in the economics<br />

and politics of rice and to look into the future of rice and the<br />

key role it plays in the livelihood of millions of people.<br />

<strong>Rice</strong> consumption plays a crucial role in assuring food<br />

security to people in Asia, and parts of Africa and<br />

Latin America. However, diets are diversifying and<br />

other crops are emerging as a result of growing urbanization<br />

and rising incomes. Moreover, demand for<br />

rice is shifting from lower-quality rice to higher-quality<br />

rice. What will be the patterns of demand for rice<br />

in the future<br />

<strong>Rice</strong> production and consumption remain closely<br />

linked. Only a small proportion of the rice produced<br />

is traded. Furthermore, production of different qualities<br />

of rice remains tied to the tastes and preferences<br />

of the region w<strong>here</strong> it is produced. What are the rice<br />

production patterns across the world and how will<br />

they change<br />

<strong>Rice</strong> systems are highly sustainable, if well managed.<br />

However, it remains a permanent challenge to maintain<br />

the environmental sustainability of the diverse<br />

rice ecosystems. The environmental externalities related<br />

to rice production are complex. Moreover, rice<br />

is increasingly grown in irrigated ecosystems; thus,<br />

as water becomes increasingly scarce, priority should<br />

be given to research aimed at producing water-saving<br />

rice varieties. What is the future of rice technology<br />

<br />

<br />

<strong>Rice</strong> markets are generally characterized as thin, concentrated,<br />

and volatile. Because most rice is consumed<br />

w<strong>here</strong> it is produced, only a small share of production<br />

is traded internationally. In the fastest globalizing<br />

region of the world, Asia, it is surprising that the<br />

most important crop, rice, is not globalizing—its integration<br />

into the international traded economy remains<br />

limited, lagging far behind other commodities.<br />

What are the reasons behind this phenomenon and<br />

can we expect this situation to change in the future<br />

<strong>Rice</strong> policies are partly shaped by culture, in particular<br />

as they affect consumer and producer behaviors,<br />

but for how much longer will that be the case as societal<br />

transformations progress The political economy<br />

of rice is changing, and that will shape rice production<br />

and consumption in the future. Even though the<br />

long history of state engagement in rice stockholding<br />

and trading is coming to an end, rice remains a strategic<br />

food security crop for policymakers and voters.<br />

What will be the future role of governments and the<br />

private sector in rice systems<br />

We approach these questions with deep respect for rice and<br />

what it means to the people and cultures in Asia and around<br />

the world, and are conscious that our brief review can only<br />

address selected aspects of the above-mentioned issues and<br />

themes. 1<br />

The culture of rice<br />

In many societies, when people consume or produce rice, they<br />

are not just consuming calories or producing grain, they are<br />

also engaging in practices that have an intrinsic cultural value.<br />

While prices and incomes are important drivers of demand,<br />

other factors such as traditions are also significant. For centuries,<br />

rice has shaped Asian societies and their cultures. Asian<br />

cultures are partly cultures of rice, and many Asian societies<br />

relate to rice beyond the satisfaction of basic needs. <strong>Rice</strong> is<br />

mentioned in the scriptures of the ancient civilizations of Asia.<br />

Its cultivation was considered as the basis of the social order<br />

and occupied a major place in Asian religions and customs<br />

1 We gratefully acknowledge comments on an earlier draft by Ron Cantrell,<br />

Susumu Matsuoka, Rajul Pandya-Lorch, and Keijiro Otsuka.<br />

Keynotes 7


(Hossain 1998). Hamilton (2003) describes the integral and<br />

vital role of rice as follows: “A key tenet of rice culture is that<br />

rice is a sacred food divinely given to humans that uniquely<br />

sustains the human body in a way that no other food can.” 2<br />

<strong>Rice</strong> is so embedded in Asian cultures that even the languages<br />

reflect the special nature of rice as the primary food for humans.<br />

In many Asian languages, t<strong>here</strong> is no general word for<br />

“food” other than the word for rice and an invitation to “eat”<br />

implies the eating of rice. Moreover, growing rice used to be<br />

considered an ideal form of human labor and reflective of a<br />

well-ordered moral society (Hamilton 2003). Beyond the cultural<br />

influence of rice, its cultivation defines the landscape in<br />

many Asian countries. In China, Korea, and Japan, t<strong>here</strong> is a<br />

well-established concept of an ideal landscape, consisting of<br />

rice fields spread out over a valley floor at the base of a mountain.<br />

Furthermore, in Japanese art, t<strong>here</strong> is a strong tradition of<br />

depicting rice plants or rice agriculture as part of an idealized<br />

natural environment (Hamilton 2003). Japanese “rice culture”<br />

is based on a social infrastructure accumulated over centuries.<br />

Just half a century ago, Japanese agriculture and rural areas<br />

were not much different from those in present-day Vietnam or<br />

Thailand or southern China (being subsistent to a considerable<br />

degree), and, even today, many Japanese farm families<br />

eat their own rice, a practice unheard of in the U.S. or Europe.<br />

Changing demand for rice<br />

<strong>Rice</strong> is crucial for food security, especially in Asia, w<strong>here</strong> more<br />

than 500 million people are undernourished and w<strong>here</strong> rice<br />

provides on average more than 30% of total calories. The importance<br />

of rice is even starker in countries such as Cambodia,<br />

Vietnam, and Bangladesh, w<strong>here</strong> rice represents more than 70%<br />

of the daily calorie intake (Fig. 1).<br />

Although the average share of total calories originating<br />

from rice has remained fairly constant during the last three<br />

decades for the world as a whole, in Asia this share has fallen<br />

from 38% to 31%, primarily due to diversification of diets<br />

caused by urbanization and increasing incomes. Within Asia,<br />

it is notable that the share of calories from rice has declined in<br />

China and Japan but this trend is not observed in other Asian<br />

countries; instead, the share of rice has remained fairly stable.<br />

In Africa, however, the share of rice in total food consumption<br />

is growing (Table 1).<br />

The world’s biggest consumer of rice is China, followed<br />

by India and Indonesia. While Asia has been and continues to<br />

be the main consumer of rice, consumption in other regions of<br />

the world is increasing. Outside Asia, Nigeria and Brazil are<br />

the most significant consumers; in fact, Nigeria is a leading<br />

rice importer.<br />

2 In some Asian cultures, the traditional understanding goes further: “Since<br />

humans live by eating rice, the human body and soul are regarded as being<br />

made of rice. T<strong>here</strong>fore, it is by eating rice that humans are defined” (Hamilton<br />

2003).<br />

US$ per ton<br />

90<br />

80<br />

70<br />

60<br />

50<br />

40<br />

30<br />

20<br />

10<br />

0<br />

1970 1980 1990 2001<br />

Year<br />

Cambodia Indonesia Japan Brazil<br />

Bangladesh Philippines India Nigeria<br />

Vietnam China Côte d’Ivoire<br />

Fig. 1. Evolution of the share of calories originating from rice, selected<br />

countries, 1970-2001. Source: FAOSTAT (September 2004).<br />

Table 1. Share (%) of calories originating from rice, by region,<br />

1970-2001.<br />

Region 1970 1980 1990 2001<br />

Asia 38 36 35 31<br />

South America 11 11 12 11<br />

Africa 5 7 7 8<br />

United States 1 1 2 2<br />

European Union 1 1 1 2<br />

World 20 19 21 21<br />

Source: World <strong>Rice</strong> Statistics, <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong> (September<br />

2004).<br />

The key factors that affect demand for rice are incomes,<br />

prices, population growth, and urbanization, but they do so in<br />

different ways. As incomes rise, consumers tend to diversify<br />

their diet, with the share of rice declining and with consumption<br />

of wheat initially increasing and of livestock and other<br />

products later increasing (Barker and Dawe 2002). Further,<br />

once calorie needs have been met, people express a preference<br />

for higher-quality rice as their incomes rise. In Japan,<br />

even though overall consumption of rice has declined in the<br />

past few decades, the type of rice demanded by consumers has<br />

changed from standard-quality rice to high-quality rice.<br />

Outside Asia, patterns of rice consumption vary considerably.<br />

In African countries, such as Côte d’Ivoire or Nigeria,<br />

rice consumption is increasing both in quantity as well as share<br />

of total food consumption, partly because of savings in time<br />

8 <strong>Rice</strong> is life: scientific perspectives for the 21st century


for preparation relative to roots and tubers and coarse grains.<br />

European consumers have traditionally chosen to consume<br />

round- to medium-grain japonica rice, but in recent years their<br />

consumption of long-grain indica rice has increased. Furthermore,<br />

their demand for aromatic rice varieties has increased<br />

significantly since the early 1990s. European consumers are<br />

increasingly interested in special rice varieties such as organic<br />

rice, waxy rice, jasmine rice, wild rice, and colored pericarp<br />

(Ferrero and Nguyen 2004). In the United States, rice consumption<br />

has more than doubled in the last 20 years, mainly<br />

because of increased concerns about diet and health but also,<br />

as in Europe, because of increases in Asian and Hispanic populations<br />

who prefer rice. <strong>Rice</strong> imported into the United States<br />

accounts for 11% of direct food consumption, and is mostly<br />

aromatic Thai jasmine and Indian and Pakistani basmati consumed<br />

by ethnic Asians (Maclean et al 2002).<br />

T<strong>here</strong> is tremendous variation in tastes and preferences<br />

for rice across the world. Hence, the market for rice is segmented<br />

by type and quality, with little substitution in consumption.<br />

Geographically, the production of different qualities of<br />

rice follows the tastes and preferences of the region w<strong>here</strong> it is<br />

consumed. Among traded rice varieties, indica rice accounts<br />

for the bulk of global rice trade (75–80%), followed by japonica<br />

(10–12%) and aromatic rice varieties such as basmati and jasmine<br />

(10%), with glutinous rice accounting for the rest (Gulati<br />

and Narayanan 2002). The variation in tastes and preferences<br />

partly depends on historical and socio-cultural factors. Topquality<br />

rice in one region may be considered low-quality in<br />

another (Kaosa-ard and Juliano 1991). For example, in East<br />

Asia, the preferred grain is short and round “sticky rice” that<br />

can be eaten easily with chopsticks. In Southeast Asia, most<br />

consumers prefer medium- to long-grain rice with little aroma.<br />

In South Asia, consumers prefer parboiled long-grain rice with<br />

a strong aroma, with basmati being the most popular rice of<br />

this type. Production patterns tend to follow consumption patterns.<br />

Among the available rice varieties, traditional varieties<br />

are generally considered to be of higher quality and thus get<br />

premium prices in the market. Thailand, for example, still extensively<br />

grows low-yielding traditional varieties, because the<br />

export market is mostly for high-quality rice (Pingali et al<br />

1997). In many traditional rice markets such as India, Pakistan,<br />

and Thailand, fragrant rice—considered a national treasure—fetches<br />

the highest prices and is t<strong>here</strong>fore the most profitable<br />

type of rice to cultivate under rainfed conditions in these<br />

countries.<br />

<strong>Rice</strong> and poverty<br />

<strong>Rice</strong> consumption and production are closely connected to<br />

poverty. <strong>Rice</strong> is the main staple food in Asia and the most important<br />

source of employment and income for rural people<br />

(Hossain 1998). Because of the large size of the rice economy<br />

and the importance of rice in the Asian diet, productivity gains<br />

in rice have a greater impact on poverty reduction than gains<br />

in other agricultural commodities. The impact on poverty<br />

mainly operates through lower prices for consumers, driven<br />

by increased production, which reduces spending on food by<br />

the poor, including the urban poor, rural landless people, and<br />

nonrice farmers. <strong>Rice</strong> farmers also benefit from higher rice<br />

productivity, which helps them to diversify into high-value<br />

agriculture. In a later section, we will describe how rice research<br />

in India and China has increased rice production, which<br />

in turn has decreased the number of rural poor.<br />

<strong>Rice</strong> consumption typically varies among different income<br />

groups. In Bangladesh, expenditure on rice alone accounts<br />

for more than half of the weekly per capita expenditure<br />

for all income groups. For example, in the lowest income<br />

quintile, rice represents 65% of total food expenditure and in<br />

the highest income quintile this share drops to 50%, which is<br />

still high. Moreover, studies indicate that calorie intake in<br />

Bangladesh increases by almost 40% from the lowest to the<br />

highest income group, with increases in rice consumption accounting<br />

for two-thirds of this increase (Bouis and Novenario-<br />

Reese 1997). In low-income countries such as Bangladesh,<br />

rice consumption is not only the main source of energy but<br />

also of essential micronutrients such as iron. Many poor people<br />

consume poor-quality diets that provide insufficient micronutrients.<br />

Fortification of rice is one option for addressing this<br />

situation. The introduction of biofortified crops, that is, varieties<br />

bred for increased mineral and vitamin content, complements<br />

existing nutrition interventions and provides a sustainable<br />

and low-cost way of reaching people who have poor access<br />

to formal markets and health care. The high levels of per<br />

capita consumption of rice in the developing countries of Asia<br />

mean that increasing the nutrient value of rice can have significant<br />

positive health outcomes. For example, food consumption<br />

studies suggest that doubling the iron content of rice could<br />

increase the iron intake of the poor by 50% (HarvestPlus 2004)<br />

and could thus have a positive effect on health.<br />

A study of the two main rice-producing and -consuming<br />

countries, China and India, showed that improvements in rice<br />

yields significantly helped to reduce rural poverty (Fan et al.<br />

2003, Fan and Chan-Kang 2005). Investments in rice research<br />

have increased rice production in both these countries over<br />

the past four decades. From 1961 to 2001, rice production<br />

grew at an average rate of 2.7% per year in India and 2.6% per<br />

year in China. Fan et al (2003) estimated that rice research<br />

reduced poverty in India by about 2% per annum and in China<br />

by about 4.5% per annum in the 1990s (Table 2). Rural poverty<br />

is reduced through three main channels. First, the release<br />

of new and better rice varieties enables farmers to produce<br />

more rice at the same cost, which in turn improves their income<br />

(Kerr and Kolavalli 1999). Second, the diffusion of<br />

modern rice varieties can result in lower food prices, which is<br />

crucial to most poor people, who spend a large proportion of<br />

their income on food (Datt and Ravallion 1997). Third, the<br />

productivity consequences of improved varieties results in<br />

greater demand for labor (David and Otsuka 1994, Hossain<br />

1988).<br />

The growing economic prosperity in Asia is reducing<br />

the incentives of farmers to engage in rice cultivation. The<br />

Keynotes 9


Table 2. Poverty impact of rice research in India and China.<br />

India<br />

China<br />

Year Number of poor Reduction as % Number of poor Reduction as %<br />

reduced by rice of total poor reduced by rice of total poor<br />

research(million)<br />

research(million)<br />

1991 4.95 2.1 5.20 5.5<br />

1995 4.81 1.9 2.85 4.4<br />

1999 3.06 1.9 1.53 4.5<br />

Source: Fan et al (2003).<br />

Table 3. Total rice production, percentage of world production, and percentage increase of production by region, 1970-<br />

2002.<br />

Item World Asia South America North and Africa Europe<br />

Central America<br />

Production (1,000 mt, paddy), 576,280 523,030 19,846 11,880 17,034 3,194<br />

2002<br />

Percentage of world production, 100 91 3 2 3 1<br />

2002<br />

Percentage increase in production, 82 80 90 126 133 79<br />

1970-2002<br />

Source: World <strong>Rice</strong> Statistics, <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong> (September 2004).<br />

expansion of the nonfarm sector and rising labor productivity<br />

have pushed up nonfarm wage rates, which motivates migration<br />

of labor—particularly of the young generation and children—from<br />

rural areas to cities and from farm to nonfarm activities<br />

within rural areas. Since traditional rice farming is a<br />

highly labor-intensive activity, increases in wages have pushed<br />

up the cost of rice production and reduced the incomes and<br />

profits of farmers (Hossain and Narciso 2004). In response,<br />

mechanization of harvesting and threshing has occurred in<br />

Malaysia, Thailand, and, in recent years, China. Direct seeding<br />

has also replaced transplanting to further save on the labor<br />

costs of crop establishment. These labor-saving techniques help<br />

to restore profitability in the face of rising wages.<br />

<strong>Rice</strong> production and technology<br />

Developing countries account for 95% of global rice production.<br />

Asia alone produces 90% of world rice, with China and<br />

India accounting for over half of the world’s output. Worldwide,<br />

rice production has increased by more than 80% in the<br />

last three decades (Table 3). The most striking increase is observed<br />

in Africa, w<strong>here</strong> rice production increased by 133%,<br />

albeit from very low levels, reflecting the growing importance<br />

of rice in this region. Other nontraditional rice-producing areas,<br />

including South, North, and Central America, have increased<br />

rice production at a higher rate than traditional rice<br />

producers.<br />

World rice production increased steadily during the<br />

1990s and started to decline only in the past four years (Fig.<br />

2). The decline in rice prices may be a main factor behind<br />

these recent developments in world rice production. Stocks of<br />

rice followed patterns similar to those of production, increasing<br />

during the 1990s and declining more recently. Dawe (2002)<br />

offers three reasons for the plunge in world prices: the significant<br />

reduction in Indonesia’s imports after 1998, the devaluation<br />

of the Thai baht during the Asian financial crisis, and the<br />

increase in rice production in Bangladesh, Vietnam, Pakistan,<br />

and India.<br />

Productivity and sustainability issues<br />

around rice ecosystems<br />

<strong>Rice</strong> ecosystems vary widely across countries and regions. In<br />

Europe, the United States, and Australia, rice is cultivated solely<br />

under irrigation. In Africa, on the other hand, the majority of<br />

rice is cultivated upland, with less than 20% of rice cultivated<br />

under irrigation. A similar situation is found in Latin America.<br />

In Asia, more than 50% of rice is irrigated, with the majority<br />

of the remaining 50% being cultivated in rainfed lowlands (Fig.<br />

3).<br />

Successful agricultural development requires the diversification<br />

of agriculture away from staple crops, for which<br />

demand gradually declines. In the case of Asia, however, diversification<br />

away from rice production is difficult because<br />

the surface irrigation systems have been designed to provide<br />

an adequate water supply for rice but not for other crops.<br />

Moreover, because of the monsoon climate, other crops are<br />

not easily adopted.<br />

The transformation to irrigated rice production has varied<br />

considerably in Asian countries during the past three decades.<br />

Countries such as Pakistan and Japan have always cul-<br />

10 <strong>Rice</strong> is life: scientific perspectives for the 21st century


US$ per ton<br />

280<br />

260<br />

240<br />

220<br />

200<br />

180<br />

160<br />

140<br />

120<br />

100<br />

1983<br />

White broken rice, Thai A1<br />

Super, f.o.b. Bangkok<br />

Production (milled)<br />

1985 1987 1989 1991 1993 1995 1997 1999 2001 2003<br />

Year<br />

000 tons<br />

420,000<br />

400,000<br />

380,000<br />

360,000<br />

340,000<br />

320,000<br />

300,000<br />

Fig. 2. Milled rice production and world price trends. Source: USDA PS&D Database (2004) and<br />

FAO Commodities and Trade Division (2004).<br />

%<br />

%<br />

100<br />

Deepwater<br />

Upland<br />

Rainfed lowland<br />

Irrigated<br />

100<br />

Bangladesh<br />

China<br />

India<br />

Japan<br />

Pakistan<br />

Philippines<br />

Thailand<br />

80<br />

80<br />

60<br />

60<br />

40<br />

20<br />

0<br />

Asia<br />

Latin America<br />

Africa<br />

Australia<br />

Region<br />

Fig. 3. Distribution of rice ecosystems, by regions and selected<br />

countries, 2001. Source: World <strong>Rice</strong> Statistics, <strong>IRRI</strong> (September<br />

2004).<br />

USA<br />

Europe<br />

World<br />

40<br />

20<br />

0<br />

1970 1980 1990 2001<br />

Year<br />

Fig. 4. Evolution of the share of rice in the irrigated<br />

ecosystem, selected countries, 1970-<br />

2001. Source: World <strong>Rice</strong> Statistics, <strong>IRRI</strong> (September<br />

2004).<br />

tivated rice under the irrigated ecosystem and continue to do<br />

so, largely because of the limited rainfall in these countries.<br />

Another group of countries that includes the Philippines, India,<br />

and Bangladesh has experienced a steady increase in the<br />

use of irrigation for rice cultivation in the last three decades.<br />

Most surprising is the case of Thailand, however, w<strong>here</strong> the<br />

proportion of rice cultivated under irrigation declined from<br />

the 1970s to the 1990s to a low of less than 10% before turning<br />

around, although it has still not returned to the level of the<br />

1970s (Fig. 4).<br />

A move toward irrigated rice cultivation is desirable not<br />

only because it increases rice yields but also because it decreases<br />

the vulnerability of rice cultivation to weather condi-<br />

tions (David and Otsuka 1994). In addition, the main technological<br />

breakthroughs in rice cultivation, which occurred as<br />

part of the Green Revolution, were in the cultivation of irrigated<br />

rice; as a consequence, the yield of rice cultivated under<br />

this ecosystem is now much higher than yields that can be<br />

achieved under other conditions.<br />

Concerns regarding the adverse environmental effects<br />

of irrigation and flood control projects on waterlogging, salinity,<br />

fish production, and the quality of groundwater have been<br />

growing (Hossain and Narciso 2004). Water is becoming increasingly<br />

scarce and t<strong>here</strong> is growing competition for it between<br />

agricultural and nonagricultural uses. The water-use efficiency<br />

of irrigated rice is low. For example, rice production<br />

Keynotes 11


equires about twice as much water as other crops such as maize<br />

and wheat. In Asia, irrigated rice consumes 150 billion m 3 of<br />

water, which corresponds to a water-use efficiency of approximately<br />

20,000 m 3 ha –1 . Assuming an average yield of 5 t ha –1 ,<br />

the water productivity of irrigated rice is only 0.15 kg of milled<br />

rice per m 3 of water. This level of productivity is low compared<br />

with that of other crops and makes rice noncompetitive<br />

compared to other uses of water in the face of growing water<br />

scarcity (Sohl 2002).<br />

To improve the productivity of water use, it is important<br />

to identify sources of water loss and minimize them. For example,<br />

reducing seepage and percolation will increase water<br />

efficiency on farms. 3 Given the growing constraints to water<br />

use for rice, the future of rice production relies on the development<br />

and adoption of water-saving technologies, a research<br />

area currently being pursued at the <strong>International</strong> <strong>Rice</strong> <strong>Research</strong><br />

<strong>Institute</strong> (<strong>IRRI</strong>). 4<br />

Beyond the negative externalities associated with inefficient<br />

use of water in rice cultivation, population increases are<br />

putting increasing pressure on the land to be more productive.<br />

In marginal areas, intensification of land use may lead to degradation<br />

of resources through loss of biodiversity, deforestation,<br />

pest infestations, depletion of natural soil fertility, and<br />

soil erosion. Furthermore, the use of pesticides and fertilizers<br />

to increase the output of a given piece of land will likely result<br />

in degradation, environmental pollution, and adverse effects<br />

on human health (Cantrell and Hettel 2004). The lands that<br />

are most threatened in Asia are the fragile rainfed and upland<br />

environments w<strong>here</strong> the poor are forced to use whatever resources<br />

are available to produce the food they need.<br />

Further, rice ecologies interact with regional and global<br />

ecosystems. A case in point is the interaction among climate<br />

change, land use, and production systems. Some lowland rice<br />

systems in coastal zones and river deltas are potentially threatened<br />

by rising sea levels caused by global warming. At the<br />

same time, irrigated rice contributes to greenhouse gases. These<br />

complex interactions, as well as the appropriate responses in<br />

terms of ecological, technological, and policy measures, need<br />

further study.<br />

3 If this water is recovered for crop consumption at some point downstream,<br />

then t<strong>here</strong> is no loss in the irrigation system and it does not affect water efficiency<br />

at the basin level (Guerra et al 1998).<br />

4 Guerra et al (1998) suggest four strategies to increase farm irrigation productivity:<br />

(1) increasing production per unit of evapotranspiration, which involves<br />

developing new varieties with higher yields and better fertilizer and<br />

weed management; (2) reducing water use in land preparation; (3) adopting a<br />

water-efficient method of rice establishment, mainly by moving from transplanting<br />

to direct seeding to reduce irrigation inflow during land preparation;<br />

and (4) reducing surface runoff, that is, reducing seepage and percolation<br />

during the crop growth period. The authors also suggest some strategies at the<br />

irrigation system level; in brief, they include changing the crop and irrigation<br />

schedule to use rainfall more effectively, improving water distribution strategies<br />

and rehabilitation, and modernizing irrigation infrastructure, among others.<br />

Table 4. <strong>Rice</strong> yields in different countries and ecosystems.<br />

Country Ecosystem Year <strong>Rice</strong> yield<br />

(t ha -1 )<br />

Bangladesh All 2000 3.6<br />

Burkina Faso Rainfed 1987-90 2.5<br />

India Irrigated 1995-96 5.2<br />

Rainfed 1995-97 2.3<br />

United States Irrigated 2001 7.0<br />

Japan Irrigated 1999 6.4<br />

Philippines All 1999-2000 3.1<br />

Thailand Irrigated 2000 4.2<br />

Rainfed 2000 2.2<br />

South Korea Irrigated 1999 6.6<br />

Vietnam Irrigated 2000 4.2<br />

Source: Hossain and Narciso (2004).<br />

Yield patterns and changes<br />

<strong>Rice</strong> yields vary enormously across ecosystems and countries.<br />

Yields of 4–6 t ha –1 are common in irrigated settings, as are<br />

yields of 2–3 t ha –1 in rainfed ecologies (Table 4). The potential<br />

to increase yields in rainfed ecosystems is still high. This<br />

ecosystem is dominant in the low-income countries of South<br />

Asia, Southeast Asia, West Africa, and Central America. <strong>Rice</strong><br />

farming in rainfed ecosystems is subject to natural hazards such<br />

as droughts, floods, and typhoons. W<strong>here</strong> rainfall is unreliable<br />

and drainage is poor, farmers still grow traditional varieties<br />

and use fertilizers in suboptimal amounts because of the uncertainty<br />

of obtaining adequate returns from investment in inputs.<br />

This is one of the main reasons for the low yield and<br />

large yield gap in countries with predominantly rainfed ecosystems<br />

(Hossain and Narciso 2004).<br />

The scope for further conversion of rainfed ecosystems<br />

into irrigated ecosystems is becoming increasingly limited. In<br />

addition, the cost of introducing irrigation to new areas has<br />

increased substantially, partly because areas that are amenable<br />

to irrigation tend already to have irrigation systems in place,<br />

and partly because of drastic declines in investment in the development<br />

and maintenance of large-scale irrigation projects<br />

in many Asian countries (Hossain and Narciso 2002). Moreover,<br />

energy costs for water lifting are rising.<br />

Scientific breakthroughs have enabled less-favored lands<br />

to improve their productivity. For instance, research at <strong>IRRI</strong><br />

has produced rice varieties that are more drought-tolerant, and<br />

the Chinese agricultural research system has produced hybrid<br />

rice strains with higher yields. Another good example is the<br />

development of the “New <strong>Rice</strong> for Africa” (NERICA) variety,<br />

a cross of African and Asian rice cultivars, by the West Africa<br />

<strong>Rice</strong> Development Association (WARDA). NERICA promises<br />

more tolerance of most African stresses, including weeds and<br />

drought, shorter growing cycles, and higher yield potential.<br />

This technological development provides an opportunity for<br />

farmers to stabilize and intensify low-input upland farming<br />

systems. Faster adoption of these varieties may lead to a substantial<br />

increase in production in Nigeria, Guinea, Côte<br />

d’Ivoire, Sierra Leone, Liberia, and Uganda, w<strong>here</strong> upland and<br />

12 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 5. Growing yield differences of rice within countries<br />

in the 1980s and 1990s.<br />

Average annual growth rates (%) in national average cereal<br />

yield and subnational variation.<br />

Country Average growth Standard deviation<br />

per annum (%) (subnational variation)<br />

Bangladesh 1.8 5.1<br />

Brazil 4.6 2.3<br />

China 2.1 1.7<br />

India 2.3 2.4<br />

Source: Schreinemachers (2004).<br />

rainfed lowland ecosystems predominate (Hossain and Narciso<br />

2004).<br />

Recent analyses suggest that growth rates of yields are<br />

increasingly differing between and within countries. In three<br />

out of four major rice-producing countries, the growth in average<br />

yields over the past 20 years is higher than the standard<br />

deviation of yield growth by provinces in the respective countries<br />

(Table 5). Rising inequality in yield growth within countries<br />

is not to be interpreted as a “growing yield gap,” which is<br />

understood as the difference between actual and potential yield.<br />

In fact, rising inequality in growth of rice yields within a country<br />

(e.g., by region or as uplands versus lowlands) would be<br />

expected w<strong>here</strong> rice is cultivated more in line with the respective<br />

ecologies, and w<strong>here</strong> scarcities of production factors determine<br />

the costs and input uses more strongly, as is the case in<br />

countries whose governments limit their interference in input<br />

and output markets. This rising inequality can also be found<br />

w<strong>here</strong> earlier low-yield regions are catching up because of<br />

improved technology.<br />

Closing the actual yield gap will not only increase production<br />

per se but will also improve the efficiency of land and<br />

labor use, reduce production costs, and, most importantly,<br />

improve food security.<br />

In Asian countries, rice is mostly grown on small family<br />

farms. The average size of a rice farm is typically less than<br />

half a hectare in China, Indonesia (Java), and the Red River<br />

Delta in Vietnam; less than 1 ha in Bangladesh, eastern India,<br />

and the Mekong River Delta in Vietnam; and 1 to 2 ha in most<br />

other countries in Asia. Only in Thailand, Myanmar, Cambodia,<br />

and the Punjab in India is the average farm size over 2 ha<br />

(Hossain and Narciso 2004). Hayami and Kikuchi (2000) have<br />

presented an excellent analysis of the dynamics and perspectives<br />

of small-farm rice production in Asia, taking a small village<br />

in the Philippines as an illustrative example. The “saga”<br />

of this rice village demonstrates that improving rice yield is a<br />

necessary but not sufficient condition to increase rice production.<br />

Irrigation, appropriate policies, and investment in infrastructure<br />

are also needed in this process.<br />

Political economy of rice, markets, and trade<br />

<strong>Rice</strong> has played a key role in the historical conception of the<br />

state in many Asian countries. Today, most Asian governments<br />

still view rice as a strategic commodity because of its importance<br />

to the diet of the poor and to the employment and income<br />

of farmers. Given this importance, fluctuations in rice<br />

prices are considered a threat to political stability, and this<br />

may be one reason why governments tend to intervene in their<br />

country’s rice market (Hossain and Narciso 2004). Historically,<br />

governments in the main rice-producing and -consuming<br />

countries have favored policies that maintained stable prices<br />

for consumers in urban centers and provided subsidies to farmers.<br />

Dorosh and Shahabuddin (2002) explain that, in<br />

Bangladesh, policy instruments are designed to minimize both<br />

annual price fluctuations and seasonal price variations. Before<br />

1994, public imports and, to a lesser extent, drawdown of<br />

stocks were the main policy instruments used to achieve<br />

interannual price stability. After trade liberalization in 1994,<br />

however, the private-sector import trade has been the dominant<br />

factor in successfully keeping prices within acceptable<br />

boundaries. In addition, during this period, the main instruments<br />

used to achieve intra-annual price stability were domestic<br />

procurement and open market sales.<br />

In Indonesia, a central strategy for providing affordable<br />

rice to the poor has been a targeted rice subsidy, termed “<strong>Rice</strong><br />

for the Poor” (Raskin). A ration of 20 kg per month per family<br />

is provided as part of the social safety net program initiated<br />

after the crisis in 1997 (Sidik 2004). In addition, the Indonesian<br />

government provides incentives to diversify consumption.<br />

Probably the most notable trend in rice-related policies<br />

over the past years has been the deregulation of postharvest<br />

activities and efforts to shift some functions traditionally carried<br />

out by the public sector, such as stock holding, to the private<br />

sector (FAO 2003a). Governments are less dominant today<br />

in international rice trade than they were in the late 1970s,<br />

although the magnitude of the change is difficult to quantify<br />

precisely. Slayton (1999) calculated that, from 1995 to 1999,<br />

government-to-government contracts, including food aid, averaged<br />

less than 7% of world rice trade, w<strong>here</strong>as, in 1980,<br />

total government-to-government contracts were at least 19%<br />

of world trade.<br />

Indonesia is an example of a country w<strong>here</strong> government<br />

intervention in the rice market and international trade is declining.<br />

BULOG, initially a parastatal organization whose main<br />

function was to stabilize the prices of basic foods in line with<br />

the government’s food policy, has shaped Indonesia’s rice<br />

policy and market for years. In the late 1990s, the Indonesian<br />

government started releasing the right to import to other private<br />

importers and BULOG lost its monopoly. For the past<br />

several years, the private sector has been responsible for about<br />

75% of Indonesia’s imports (Dawe 2004). In early 2003,<br />

BULOG became a state-owned enterprise (SOE) with dual<br />

Keynotes 13


400<br />

350<br />

300<br />

250<br />

200<br />

US$ t –1 1985 1987 1989 1991 1993 1995 1997 1999 2001 2003<br />

150<br />

100<br />

50<br />

White broken rice, Thai A1<br />

Super, f.o.b. Bangkok<br />

White rice, Thai 100% B<br />

second grade, f.o.b. Bangkok<br />

0<br />

1983<br />

Year<br />

Fig. 5. Evolution of Thailand’s (main rice exporter) rice price, 1983-2004. Source: FAO Commodities<br />

and Trade Division (September 2004), World <strong>Rice</strong> Statistics, <strong>IRRI</strong> (2004).<br />

functions, to conduct public-service activities and to conduct<br />

business as a commercial organization. Under the former function,<br />

BULOG still distributes “<strong>Rice</strong> for the Poor” (Raskin) and<br />

maintains national stock reserves to counter food shortages<br />

during emergencies. As a commercial organization, BULOG<br />

can enter into trading activities as a profit-making organization.<br />

The role of governments in the international rice trade<br />

has also diminished, as has the influence of large trading companies.<br />

Today, numerous smaller trading companies are engaged<br />

in the international trade of rice, which has increased<br />

competition and eroded trading margins. However, the degree<br />

and type of policy changes that have occurred in recent years<br />

vary greatly from country to country. We consider two examples:<br />

Vietnam and India.<br />

Vietnam’s rice market is characterized by a high level of<br />

commercialization and a large role of the private sector in the<br />

production and marketing stages. The private sector plays a<br />

key role in procuring rice from farmers, supplying rice to exporters,<br />

and distributing rice within the country. At the same<br />

time, however, the private sector is highly underdeveloped and<br />

regionally imbalanced (Golleti and Minot 1997). Until recently,<br />

all rice exports from Vietnam were conducted by SOEs, but<br />

over the last few years private firms have gradually been allowed<br />

to export rice. Although SOEs buy from farmers, the<br />

importance of these transactions is not sufficient for SOEs to<br />

stabilize producer prices, which is considered one of the main<br />

functions of these organizations. Thus, although SOEs still play<br />

an important role in Vietnam’s international trade, gradual liberalization<br />

is occurring (Tolentino and Bruce 2003, Dawe<br />

2004).<br />

In India, the government still intervenes in trade transactions.<br />

The Food Corporation of India is one of the largest<br />

organizations procuring food grains on behalf of the government<br />

of India. One of the main roles of this organization is to<br />

buy and transport rice from surplus areas to deficit areas, under<br />

the Public Distribution System, to ensure food for the poor<br />

and to stabilize prices (Nigam 2004). Nevertheless, although<br />

the private sector negotiates and handles the export of rice,<br />

the government still makes key decisions that determine the<br />

quantity of rice exported (Dawe 2004).<br />

Developments in and determinants<br />

of the price of rice<br />

The world price for rice has shown a declining trend over the<br />

past 50 years. After adjusting for inflation, world rice prices<br />

today are 77% lower than the average from 1950 to 1981. The<br />

main reason for the decline in prices is the Green Revolution,<br />

which led to an increase in yields and a decrease in unit production<br />

costs, and consequently to an increase in worldwide<br />

supply (Dawe 2004). World prices for other grains have also<br />

declined in real terms, but to a lesser extent than has occurred<br />

for rice. <strong>Rice</strong> prices continue to fluctuate substantially, as can<br />

be seen in the plot of rice prices for Thailand over the period<br />

1983-2004 (Fig. 5).<br />

The price of rice fluctuates significantly and is sensitive<br />

to variations in supply and demand. The main cause for this is<br />

the small amount of rice traded internationally; less than 7%<br />

of the world’s total rice production is traded. Furthermore, six<br />

countries (Thailand, Vietnam, China, the United States, Pakistan,<br />

and India) supply 85% of the rice that is traded. This<br />

concentration in world rice markets implies that changes in<br />

production or consumption in major rice-trading countries have<br />

a strong effect on world prices. In recent years, t<strong>here</strong> has been<br />

a diversification of world importers and exporters that could<br />

further stabilize rice prices. Before the Green Revolution, Asia<br />

(excluding the Middle East) accounted for 64% of world rice<br />

imports, and an identical share of world exports. Today, a more<br />

diversified group of countries accounts for rice imports.<br />

14 <strong>Rice</strong> is life: scientific perspectives for the 21st century


120<br />

110<br />

100<br />

90<br />

80<br />

70<br />

60<br />

1998 1999 2000 2001 2002 2003<br />

Year<br />

Indica high<br />

Indica low<br />

Japonica<br />

Aromatic<br />

Fig. 6. Evolution of rice price indices by quantity (1998-2000 =<br />

100). Source: FAO (2004, 2003b).<br />

Asian countries have been successful at stabilizing domestic<br />

prices relative to those in the world market. This has<br />

been achieved both under centralized (Malaysia and Indonesia)<br />

and less-centralized (Thailand) political systems. <strong>Rice</strong> price<br />

stabilization remains central to protecting poor consumers in<br />

many Asian countries. An interesting case to follow is that of<br />

China, which recently entered the World Trade Organization<br />

and committed to suppress rice price stabilization mechanisms.<br />

This policy shift gave rice producers an incentive to diversify<br />

production to other more profitable crops. <strong>Rice</strong> production in<br />

China has declined over the last three years, and, if this trend<br />

continues, China will become one of the world’s main rice<br />

importers.<br />

Another interesting feature of world rice prices is the<br />

evolution of prices of different qualities of rice. As mentioned<br />

earlier, rising income levels in many countries have been accompanied<br />

by a shift away from low-quality rice (defined as<br />

less than or equal to 20% broken) during the past 25–30 years<br />

(Dawe 2004). Dawe (2004) further observes that in recent years<br />

(1999-2003 versus 1986-95) prices of different qualities of<br />

indica varieties moved closer to each other (this is observed in<br />

Figure 6, w<strong>here</strong> the price indices for low- and high-quality<br />

indica move almost in synchrony). T<strong>here</strong> is still a lot of substitution<br />

between the qualities, as would be expected for a food<br />

item that is predominantly consumed by people with low income.<br />

However, relative price differences between different<br />

types of rice in 2002 and 2003 appear higher than five years<br />

earlier.<br />

<strong>International</strong> trade of rice and trade policies<br />

Global trade in rice expanded on average by 7% a year over<br />

the 1990s. Nevertheless, the international rice market remains<br />

thin, accounting for only 7% of global output compared with<br />

19% for wheat and 13% for maize. Developing countries are<br />

still the main players in the world rice trade, with a share of<br />

83% of world exports and 85% of world imports.<br />

Despite a trend toward governments limiting their interventions<br />

in the rice market, the long tradition of government<br />

intervention in rice markets (Siamwalla and Haykin 1983) continues<br />

across the world. Both developing and developed countries<br />

protect this sector, although the policies differ between<br />

these two groups of countries. Developed countries typically<br />

use a combination of domestic market interventions and border<br />

protection or export subsidies depending on whether they<br />

are net importers or exporters. Border protection through bans,<br />

high tariffs, and state trading enterprises (STEs) is very common<br />

in wealthy rice-importing countries and regions such as<br />

Japan, South Korea, and the European Union. Japan and South<br />

Korea, for example, control imports through monopoly STEs,<br />

with Japan’s Food Agency being one of the world’s largest<br />

importer STEs. Domestically, developed countries support rice<br />

producers with a combination of market price interventions<br />

and direct payments. Developed-country exporters also use<br />

export subsidies and export credit guarantees to promote their<br />

rice exports (Gulati and Narayanan 2002).<br />

Poorer developing countries in South and Southeast Asia<br />

have tended to tax rice producers by imposing support measures<br />

that keep the rice price at levels below international prices.<br />

Public procurement and government stocking are undertaken<br />

in almost all of these countries for public distribution of food<br />

grain (India) or for market interventions (Vietnam, Thailand,<br />

China, and Indonesia). Stocking limits on private traders and<br />

restrictions on the movement of rice are also common practices.<br />

STEs continue to play a dominant role in many of these<br />

countries, particularly those that are net importers (Gulati and<br />

Narayanan 2002).<br />

Given that developing countries protect their producers<br />

mostly by border support and other price-based policy measures,<br />

a measure of the protection of producers in these countries<br />

is given by the gap between domestic and international<br />

prices (Mullen et al 2004a,b). Mullen et al (2004a,b) estimated<br />

the market price support (MPS) and producer support estimates<br />

(PSE) 5 for rice in India, Indonesia, and Vietnam (Table<br />

6).<br />

The general pattern that emerges from these estimates is<br />

that current levels of support of rice by trade and market policies<br />

in Asian developing countries are considerably higher than<br />

the levels in the 1980s or early 1990s. India’s trade policies in<br />

the last decade can be followed by examining the PSEs. Before<br />

1994, India had in place a ban on exports of certain types<br />

of rice. In that year, the ban was lifted and India’s rice exports<br />

increased from less than 1 million tons per year to about 5<br />

5 MPS is calculated comparing the domestic farm-gate price and the adjusted<br />

reference price. The reference price at the border is the “world market” c.i.f.<br />

price for an importer and f.o.b. price for an exporter, adjusted by the costs of<br />

handling, transporting, and marketing and difference in quality. For more details<br />

on the calculations and selection of reference price, see Mullen et al<br />

(2004a,b). The PSE is calculated by adding the budgetary transfers to the<br />

MPS.<br />

Keynotes 15


Table 6. Producer support estimates for India, Indonesia, and Vietnam.<br />

Country 1990 1991 1992 2000 2001 2002<br />

India –10.3 –2.7 –25.1 28.3 11.2 40.1<br />

Indonesia 2.2 1.0 10.9 21.4 19.3 45.6<br />

Vietnam –28.4 –15.8 –10.7 53.0 60.4 32.4<br />

Sources: Mullen et al (2004a), Thomas and Orden (2004).<br />

million tons in 1995-96, making India the second-largest exporter<br />

of rice in that year. Since then, India has become a major<br />

supplier of common and basmati rice. Vietnam’s PSEs for<br />

rice show that rice farmers have tended to be protected, especially<br />

at the end of the 1980s and after 1996, although from<br />

1990 to the mid-1990s they were taxed. This trend was further<br />

accentuated by a dramatic decline in public stockholding and<br />

fertilizer prices. In general, as indicated by the PSEs, the trend<br />

has been toward increasing support for rice (Nguyen and Grote<br />

2004).<br />

We now return to one of the initial questions posed above:<br />

Why is the integration of rice into international trade so limited<br />

Of critical importance to this issue is inelastic supply<br />

and demand, that is, both supply and demand do not respond<br />

quickly and strongly to price changes. An additional factor is<br />

the vulnerability of production to occasional disruptions due<br />

to climatic phenomena. These characteristics lead to large price<br />

fluctuations. Market interventions are then used to stabilize<br />

prices and policies are applied to transfer income from consumers<br />

to producers.<br />

Future scenarios for rice: toward 2050<br />

In view of the close linkages among production, markets, and<br />

consumption of rice, any outlook on rice must take a holistic<br />

perspective, and the future of rice cannot be assessed without<br />

due consideration of the broader economic context and developments<br />

related to other foods. Global and regional rice consumption<br />

and production will be determined by changes in<br />

consumption behavior and policy actions related to technology<br />

(research) and trade. An analysis of the effects of these<br />

variables on rice consumption, production, and market developments<br />

can be useful for identifying appropriate policies that<br />

serve growth, sustainability, and poverty reduction. Below, we<br />

present three policy scenarios using the <strong>International</strong> Model<br />

for Policy Analysis of Agricultural Commodities and Trade<br />

(IMPACT) 6 developed by Mark Rosegrant of the <strong>International</strong><br />

6 IMPACT covers 36 countries and accounts for almost all of the world’s commodities.<br />

The IMPACT model explores the potential implications of policies<br />

in key variables such as prices, demand, yields, production, and net trade.<br />

This model assumes competitive agricultural markets for crops and livestock<br />

(Rosegrant et al 2002).<br />

Food Policy <strong>Research</strong> <strong>Institute</strong> (IFPRI). The key policy assumptions<br />

for each scenario are briefly described below. 7<br />

Progressive policy scenario<br />

This scenario assumes a new focus on agricultural growth and<br />

rural development. Developing countries’ public investments<br />

and government expenditures on agriculture and rural development,<br />

appropriately supported by official development assistance<br />

(ODA), increase between 2005 and 2015 and stabilize<br />

t<strong>here</strong>after. Investments in education, social services, and<br />

health increase. The rate of agricultural technology improvement<br />

is high owing to increased investment in agricultural research<br />

and development. Irrigation efficiency and water-use<br />

efficiency improve in this scenario, and the rate of irrigation<br />

expansion is moderate to high. Furthermore, producer support<br />

to farmers in wealthy countries declines substantially, dropping<br />

to half of current levels by 2010, and to half of the 2010<br />

level by 2020.<br />

Policy failure scenario<br />

This scenario assumes trade and political conflicts, with no<br />

progress on global agricultural trade negotiations and increased<br />

levels of protectionism worldwide. Today, we cannot exclude<br />

political-economic forces from producing such outcomes. The<br />

policy failure scenario assumes decreases in yield growth for<br />

all crops and fish, and decreases in numbers growth for all<br />

livestock. It also shows trade policies that lead to an increase<br />

in protection in many countries, contributing to stagnating<br />

world trade and slow growth in the net imports of developing<br />

countries. This impasse in agricultural trade liberalization further<br />

contributes to the growing food deficit in developing countries.<br />

As a result of political conflicts, investments in social<br />

services and agricultural R&D are low. Producer support to<br />

farmers in wealthy countries triples from current levels by 2020<br />

and remains steady through 2050.<br />

Technology and natural resource management<br />

failure scenario<br />

This scenario is characterized by water mismanagement, declining<br />

irrigation efficiency, lack of adaptation to climate<br />

change, and pest problems in agriculture. Low agricultural in-<br />

7 For further details, see von Braun et al (2004); for a detailed model description,<br />

see Rosegrant et al (2002).<br />

16 <strong>Rice</strong> is life: scientific perspectives for the 21st century


000 t<br />

kg ha –1<br />

590,000<br />

550,000<br />

510,000<br />

Progressive policy actions<br />

Policy failure<br />

Technology and resource<br />

management failure<br />

5,000<br />

4,000<br />

Progressive policy actions<br />

Policy failure<br />

Technology and resource<br />

management failure<br />

470,000<br />

430,000<br />

390,000<br />

3,000<br />

350,000<br />

1997 2015 2030 2050<br />

Year<br />

Fig. 7. World rice demand projections (1,000 mt, milled rice).<br />

Source: IFPRI IMPACT projections (September 2004).<br />

2,000<br />

1997 2015 2030 2050<br />

Year<br />

Fig. 8. World rice yield projections under different policy scenarios.<br />

Source: IFPRI IMPACT projections (September 2004).<br />

vestments undermine the development of new agricultural technology<br />

and contribute to marginal levels of irrigation efficiency<br />

and lack of improvement in water-use efficiency. In addition,<br />

investments in many sectors, including education, social services,<br />

and health, are low in developing countries. The lack of<br />

growth in agricultural yields is the outcome of all of the above,<br />

and also partly a result of weak income growth in developing<br />

countries, and only moderate income growth in industrialized<br />

countries.<br />

Under the progressive policy actions scenario, world<br />

demand for rice is projected to increase by more than 50%<br />

from 1997 to 2050 (Fig. 7). The projected change in demand<br />

varies by region; for example, under this scenario, rice demand<br />

is predicted to rise by almost 200% in sub-Saharan Africa<br />

and by 110% in Latin America. However, if natural resources,<br />

especially water, are mismanaged, and investment in<br />

agriculture is low, as in the technology and natural resource<br />

management failure scenario, demand for rice is projected to<br />

remain flat.<br />

Appropriate policies can boost rice production under sustainable<br />

use of the natural resources on which rice production<br />

largely depends. Future trends in rice yields will be greatly<br />

affected by the degree of investment in research, resource<br />

management, and market and trade policy. In the progressive<br />

policy actions scenario, in which developing countries increase<br />

public investment in agriculture, rural development, and agricultural<br />

research and development, rice yields are projected to<br />

almost double from 1997 to 2050 (Fig. 8). However, if agricultural<br />

investment is low and natural resources are mismanaged,<br />

contributing among other things to marginal levels of<br />

irrigation efficiency, as in the technology and natural resource<br />

management failure scenario, yield growth is predicted to stagnate<br />

over the next 50 years.<br />

Projections under the progressive policy actions scenario<br />

suggest that, with increased public investment and government<br />

expenditure, rice production will increase in the two poorest<br />

regions of the world, South Asia and sub-Saharan Africa (Figs.<br />

000 t<br />

200,000<br />

180,000<br />

160,000<br />

140,000<br />

120,000<br />

100,000<br />

Progressive policy actions<br />

Policy failure<br />

Technology and resource<br />

management failure<br />

1997 2015 2030 2050<br />

Year<br />

Fig. 9. South Asia rice production projections under different policy<br />

scenarios. Source: IFPRI IMPACT projections (September 2004).<br />

9 and 10). On the other hand, if trade and political conflict rise<br />

and the level of protectionism increases, as in the policy failure<br />

scenario, production will not increase sharply. The worst<br />

outcome in terms of rice production stagnation arises when<br />

t<strong>here</strong> is technology and natural resource mismanagement. The<br />

patterns of change differ by world region, as suggested by differences<br />

in the predicted trends for Asia and sub-Saharan Africa.<br />

Projections under the progressive policy actions scenario,<br />

in which producer support to farmers in developed countries<br />

declines substantially, suggest that the international price for<br />

rice will continue to decline in the future. By contrast, under<br />

the policy failure scenario, which assumes strong trade distortions,<br />

the price of rice will remain at 1997 levels (Fig. 11).<br />

In sum, the long-term future of rice is going to be very<br />

much influenced by policies related to technologies, water<br />

management, and trade. In addition, the incomes and tastes of<br />

consumers will remain fundamental drivers of change in the<br />

economics of rice.<br />

Keynotes 17


000 t<br />

US$ t –1<br />

40,000<br />

30,000<br />

20,000<br />

Progressive policy actions<br />

Policy failure<br />

Technology and resource<br />

management failure<br />

600<br />

500<br />

300<br />

200<br />

Progressive policy actions<br />

Policy failure<br />

Technology and resource<br />

management failure<br />

10,000<br />

100<br />

0<br />

1997 2015 2030 2050<br />

Year<br />

0<br />

1997 2015 2030 2050<br />

Year<br />

Fig. 10. Sub-Saharan Africa rice production projections under different<br />

policy scenarios. Source: IFPRI IMPACT projections (September<br />

2004).<br />

Fig. 11. Projections of rice price under different policy scenarios.<br />

Source: IFPRI IMPACT projections (September 2004).<br />

Conclusions<br />

The cultivation and consumption of rice have shaped the lives<br />

of millions of people for centuries. Today, rice is facing new<br />

risks and new opportunities, but, for millions of people, every<br />

year is the Year of <strong>Rice</strong>, not just the year 2004, as declared by<br />

the United Nations.<br />

More than 500 million undernourished people live in<br />

Asia, accounting for 63% of the world’s undernourished people.<br />

The importance of rice in the Asian diet is expected to decline<br />

over time because of increases in migration to urban areas and<br />

increases in incomes to above the level at which people begin<br />

to diversify their diets. This pattern stands in contrast to the<br />

patterns observed in other parts of the world such as Africa<br />

and Latin America, w<strong>here</strong> rice is becoming increasingly important.<br />

However, regardless of these mixed trends, rice will<br />

remain central to the diets of millions of people across the<br />

world.<br />

<strong>Rice</strong> is a “health food” with many characteristics and<br />

diverse flavors, and can be developed further to accentuate its<br />

desirable characteristics. For example, scientific research into<br />

the diet quality aspects of rice, including the contents of micronutrients<br />

such as iron and vitamin A, has the potential to<br />

transform rice into an even more important agent of change,<br />

especially for the poor. At the same time, high-income consumers<br />

are expected to increase their demand for specialty rice<br />

varieties.<br />

Under a scenario that assumed increased investment in<br />

rural development, improved technology, efficient use of natural<br />

resources, and increased trade liberalization—referred to<br />

as the progressive policy actions scenario—the global demand<br />

for rice was predicted to increase by more than 50% over the<br />

next 50 years. Most significant in relative terms is the prediction<br />

that the demand for rice in sub-Saharan Africa and Latin<br />

America will increase by almost 200% and 110%, respectively,<br />

over this period.<br />

Over the last three decades, global rice production has<br />

increased by more than 80%. North and Central America as<br />

well as sub-Saharan Africa increased their production by more<br />

than 120% during this time. This growth can be largely explained<br />

by the increase in yields accomplished with the Green<br />

Revolution. Feeding the ever-increasing world population poses<br />

a challenge that must be tackled by increasing yields. If this is<br />

to be achieved, increased investment in research and development<br />

is needed. Increases in rice yields have strongly contributed<br />

to reducing poverty in Asia, and such increases will continue<br />

to be much needed by the millions of people who live in<br />

poverty across the world.<br />

Efforts to increase rice production must not overlook<br />

the externalities associated with ecological effects. Water is<br />

an increasingly scarce resource, and current rice cultivation<br />

methods use water inefficiently; hence, new methods of cultivation<br />

and new technologies will be needed in the future to<br />

achieve sustainable and efficient use of this resource. Beyond<br />

the adverse externalities associated with the inefficient use of<br />

water in rice cultivation, population increases put pressure on<br />

the land to be more productive. The development of appropriate<br />

improved technologies represents an opportunity to enhance<br />

sustainable rice production. Scientific research aimed at improving<br />

the water-use efficiency of rice and the resistance of<br />

rice to pests and tolerance of drought has the potential to facilitate<br />

environmental sustainability, t<strong>here</strong>by increasing yields<br />

further. These objectives will need to remain high on the agenda<br />

of rice research for decades to come.<br />

Countries with long-standing experience in enhancing<br />

rice productivity and sustainability, such as Japan, may accept<br />

a certain “corporate” responsibility to share their know-how<br />

in research and management with low-income countries. Such<br />

knowledge sharing, which already occurs to a considerable<br />

extent, is probably as important as sharing opportunity through<br />

access to markets.<br />

Among its multiple functions, rice is a strategic commodity<br />

because it is the single most important element in the<br />

diet of the poor and one of the main sources of income and<br />

employment for farmers in Asia. Traditionally, governments<br />

have sought to maintain stable prices for consumers in urban<br />

18 <strong>Rice</strong> is life: scientific perspectives for the 21st century


areas and to provide input subsidies to farmers. Nowadays, a<br />

shift toward increased private intervention in the rice market<br />

is noted, and governments are increasingly delegating functions<br />

to private enterprises. Hence, appropriate policies need<br />

to be developed so that these new players can provide affordable<br />

food to the poor and do not exclude poor farmers from<br />

the transforming food and agricultural system.<br />

As a worldwide trend toward freer trade is observed,<br />

developing countries are likely to become increasingly important<br />

players in the world trade of rice. Developments in policy<br />

at the national, regional, and international levels are a decisive<br />

component of the state of rice in the world today and will also<br />

shape the future role of rice.<br />

Changes in policies may be driven by societal and technological<br />

changes. <strong>Rice</strong> culture has modernized but certainly<br />

not vanished. The roles of rice for improving food security,<br />

reducing poverty, and sustaining the environment will remain<br />

strong. <strong>Rice</strong> cultures show strong resilience against drastic<br />

changes. This aspect of rice may actually be a healthy force in<br />

a rapidly changing and globalizing world, w<strong>here</strong> rice has been<br />

as much an agent of developmental change as it has been a<br />

conserving factor serving sustainability.<br />

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<strong>Institute</strong>.<br />

Hamilton RW. 2003. The art of rice: spirit and sustenance in Asia.<br />

Los Angeles, Calif. (USA): UCLA Fowler Museum of Cultural<br />

History. 552 p.<br />

Harvest Plus. 2004. Breeding crops for better nutrition. Brief. Washington,<br />

D.C. (USA): <strong>International</strong> Food Policy <strong>Research</strong> <strong>Institute</strong>.<br />

Hayami Y, Kikuchi M. 2000. A rice village saga: three decades of<br />

green revolution in the Philippines. Lanham, Md. (USA):<br />

Barnes & Noble.<br />

Hossain M. 1988. Nature and impact of the green revolution in<br />

Bangladesh. <strong>Research</strong> Report No. 67. Washington, D.C.<br />

(USA): <strong>International</strong> Food Policy <strong>Research</strong> <strong>Institute</strong>.<br />

Hossain M. 1998. Sustaining food security in Asia: economic, social,<br />

and political aspects. In: Dowling NG, Greenfield SM,<br />

Fischer KS, editors. Sustainability of rice in the global food<br />

system. Davis, Calif. (USA) and Manila (Philippines): Pacific<br />

Basin Study Center and <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>.<br />

Hossain M, Narciso J. 2002. New rice technologies and challenges<br />

for food security in Asia and the Pacific. In: Sustainable rice<br />

production for food security. Proceedings of the 20th Session<br />

of the <strong>International</strong> <strong>Rice</strong> Commission. Bangkok, Thailand,<br />

23-26 July 2002.<br />

Keynotes 19


Hossain M, Narciso J. 2004. Long-term prospects for the global rice<br />

economy. Rome (Italy): FAO <strong>Rice</strong> Conference.<br />

Huang J, Bouis HE. 1996. Structural changes in the demand for food<br />

in Asia. 2020 Vision Discussion Paper No. 11. Washington,<br />

D.C. (USA): <strong>International</strong> Food Policy <strong>Research</strong> <strong>Institute</strong>.<br />

<strong>IRRI</strong>. World rice statistics, various years. Los Baños (Philippines):<br />

<strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>.<br />

Kaosa-ard M, Juliano BO. 1991. Assessing rice quality characteristics<br />

and prices in selected international markets: rice grain<br />

marketing and quality issues. Selected papers from the <strong>International</strong><br />

<strong>Rice</strong> <strong>Research</strong> Conference, 27-31 August 1990, Seoul,<br />

Korea.<br />

Kerr J, Kolavalli S. 1999. Impact of agricultural research on poverty<br />

alleviation: conceptual framework with illustrations from the<br />

literature. Environmental and Production Technology Division<br />

Discussion Paper No. 56. Washington, D.C. (USA): <strong>International</strong><br />

Food Policy <strong>Research</strong> <strong>Institute</strong>.<br />

Maclean JL, Dawe D, Hardy B, Hettel GP, editors. 2002. <strong>Rice</strong> almanac.<br />

Third edition. Los Baños (Phillipines), Bouaké (Côte<br />

d’Ivoire), Cali (Colombia), and Rome (Italy): <strong>IRRI</strong>, WARDA,<br />

CIAT, and FAO.<br />

Mullen K, Gulati A, Orden D. 2004a. Agricultural policies in India:<br />

producer support estimates 1985-2002. Markets, Trade, and<br />

Institutions Division Discussion Paper. Washington, D.C.<br />

(USA): <strong>International</strong> Food Policy <strong>Research</strong> <strong>Institute</strong>. (Forthcoming.)<br />

Mullen K, Sun D, Thomas M, Orden D, Gulati A. 2004b. Agricultural<br />

policy interventions in developing countries: mapping<br />

the nature, degree and progress in reforms. Selected paper<br />

prepared for presentation at the American Agricultural Economics<br />

Association Annual Meeting, Denver, Colorado, 1-4<br />

August 2004.<br />

Nguyen NV, Grote U. 2004. Agricultural policies in Vietnam: producer<br />

support estimates 1986-2002. Discussion Paper. Washington,<br />

D.C., (USA) and Bonn (Germany): IFPRI and Center<br />

for Development <strong>Research</strong> (ZEF). (Forthcoming.)<br />

Nigam S. 2004. <strong>Rice</strong>: challenges in production and marketing in<br />

India. Paper presented at the FAO <strong>Rice</strong> Conference, 12-13<br />

February 2004.<br />

Pingali PL, Hossain M, Gerpacio RV. 1997. Asian rice bowls: the<br />

returning crisis New York and Manila: CAB <strong>International</strong><br />

and <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>.<br />

Rosegrant M, Meijer S, Cline S. 2002. <strong>International</strong> Model for Policy<br />

Analysis of Agricultural Commodities and Trade (IMPACT):<br />

model description. Washington, D.C. (USA): <strong>International</strong><br />

Food Policy <strong>Research</strong> <strong>Institute</strong>.<br />

Schreinemachers P. 2004. Yield gaps and their determinants. Bonn<br />

(Germany): Center for Development <strong>Research</strong>. (In mimeo.)<br />

Siamwalla A, Haykin S. 1983. The world rice market: structure, conduct,<br />

and performance. IFPRI <strong>Research</strong> Report No. 39. Washington,<br />

D.C. (USA): <strong>International</strong> Food Policy <strong>Research</strong> <strong>Institute</strong>.<br />

Sidik M. 2004. Indonesia rice policy in view of trade liberalization.<br />

Paper presented at the FAO <strong>Rice</strong> Conference, 12-13 February<br />

2004.<br />

Slayton T. 1999. The outlook for the rice trade in the new millennium.<br />

World <strong>Rice</strong> Commerce Conference.<br />

Sohl M. 2002. Issues and challenges in rice technological development<br />

for sustainable food security. Keynote Address at the<br />

20th Session of the <strong>International</strong> <strong>Rice</strong> Commission, Bangkok,<br />

Thailand, 23-26 July 2002. Rome (Italy): FAO.<br />

Thomas M, Orden D. 2004. Agricultural policies in Indonesia: producer<br />

support estimates 1985-2005. Markets, Trade, and Institutions<br />

Division Discussion Paper. Washington, D.C.<br />

(USA): <strong>International</strong> Food Policy <strong>Research</strong> <strong>Institute</strong>. (Forthcoming.)<br />

Tolentino V, Bruce J. 2003. Successful transition to the market<br />

economy: overview of the experience in Vietnam. Yangon<br />

(Myanmar): FAO Seminar on rice sector policy: neighboring<br />

countries’ experiences.<br />

USDA. 2004. Producer, supply and distribution online database.<br />

Washington, D.C.: United States Department of Agriculture.<br />

www.fas.usda.gov/psd/.<br />

von Braun J, Rosegrant MW, Cohen MJ, Cline S, Brown, Bos MS,<br />

Pandya-Lorch R. 2004. New risks and opportunities for food<br />

security. 2020 Discussion Paper. Washington, D.C. (USA):<br />

<strong>International</strong> Food Policy <strong>Research</strong> <strong>Institute</strong>.<br />

Notes<br />

Authors’ address: <strong>International</strong> Food Policy <strong>Research</strong> <strong>Institute</strong><br />

(IFPRI), e-mail: j.vonbraun@cgiar.org.<br />

20 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Feeding the world: How much more rice do we need<br />

Vaclav Smil<br />

The key question that underlies efforts to increase rice yields,<br />

to improve the crop’s nutritional quality, and to cut its<br />

postharvest losses is how much more of the grain will we need<br />

to assure global adequacy of its supply I will look just a generation<br />

(25 years) ahead, but, even then, a precise answer is<br />

impossible as well as unnecessary: what we need is a good<br />

approximation of w<strong>here</strong> we are headed. Key determinants of<br />

future rice consumption are the rates of population growth,<br />

the process of population aging, the increased mechanization<br />

of labor, the need to improve inadequate diets, and the extent<br />

and pace of dietary transitions. The complex interplay of these<br />

factors will determine potential demand, the total that should<br />

give us a better appreciation of how high we should aim our<br />

efforts at future yield increases and agronomic improvement.<br />

Population growth<br />

The global population growth rate has been slowing ever since<br />

it peaked at just over 2.0% in 1967 (Fig. 1). As a result, consecutive<br />

long-range population forecasts issued by the United<br />

Nations have been repeatedly revised downward and the low<br />

variant in the forecast for 2025 is just 7.3 billion people, not<br />

even 20% above the 6.1 billion in 2000 (UN 2002). The medium<br />

variant is 7.8 billion and the high 8.3 billion, but the<br />

recent accelerated decline in fertility indicates that the most<br />

likely outcome will be closer to the low total and that virtually<br />

all of the net increase will take place in Africa, Asia, and Latin<br />

America.<br />

The medium forecast of population growth in the world’s<br />

ten most populous countries w<strong>here</strong> rice is the staple grain and<br />

that consume about 85% of the world crop—Bangladesh, Brazil,<br />

China, Egypt, India, Indonesia, Myanmar, the Philippines,<br />

Thailand, and Vietnam—is for about a 26% increase from 2000<br />

to 2025, an addition of just over 800 million people. Everything<br />

else being equal, demand for rice would rise by about<br />

25% in 25 years compared with the 68% increase from 1975<br />

to 2000. But everything else will not be equal. Rapidly aging<br />

populations will actually require less food per capita because<br />

of the natural decline in metabolic needs (unless we assume<br />

universal obesity), further mechanization of labor will eliminate<br />

most of the hard physical tasks that are still common in<br />

many countries, and rising incomes will improve average diets<br />

and change their composition.<br />

Population aging and activity<br />

The process of population aging will be pronounced not only<br />

in Europe and Japan but also in China (thanks to its one-child<br />

policy) and in many countries in Asia (Fig. 1). In the world’s<br />

ten most populous rice-eating countries, the share of the popu-<br />

Declining population growth rates, annual growth rate (%)<br />

2.5<br />

2.0<br />

1.5<br />

1.0<br />

0.5<br />

0<br />

100<br />

80<br />

60<br />

40<br />

20<br />

World<br />

Asia<br />

Declining annual absolute growth rates, population change<br />

per year (miilions)<br />

Population aged 60+ (%)<br />

16<br />

14<br />

12<br />

10<br />

8<br />

World<br />

Asia<br />

World<br />

6<br />

1950 1975 2000 2025<br />

Year<br />

Fig. 1. Declining population growth rates and population aging:<br />

global and Asian trends, 1950-2025.<br />

Asia<br />

Keynotes 21


lation older than 60 years will increase by roughly 15% to<br />

about two-thirds, or nearly 600 million people, by 2025. Complexities<br />

of human metabolism preclude any accurate calculation<br />

of this aging effect (Smil 2000), but, assuming that, on<br />

average, people above age 60 consume 15–20% less food energy<br />

per day per capita than the mean for the adult population,<br />

then aging would reduce 2025 demand by no more than 2–3%<br />

compared to a population with a stationary age structure.<br />

The continuing mechanization of agricultural and industrial<br />

tasks in modernizing countries may have a similar effect<br />

on overall food demand. Again, complexities of human metabolism<br />

make it impossible to make any accurate estimates,<br />

but, assuming an average difference of at least 10–15% between<br />

moderately and highly active population groups and a<br />

shift of 20–25% of today’s labor force from more demanding<br />

tasks in agriculture and industry to mechanized manufacturing<br />

and services would lower overall food demand and hence presumably<br />

also rice consumption by 2–3% compared to the unchanged<br />

frequency of typical labor exertions. The combined<br />

effect of aging and mechanization could decrease the overall<br />

demand for rice by no more than 5% by 2025.<br />

Eliminating undernutrition<br />

In spite of major gains during the last quarter of the 20th century,<br />

the FAO (Food and Agriculture Organization of the United<br />

Nations) estimated the total number of malnourished people<br />

at about 800 million during the late 1990s (FAO 2002). Nearly<br />

60% of this total, or almost 480 million people, were in the<br />

world’s ten most populous rice-eating countries. India had<br />

about 233 million undernourished people (almost 29% of the<br />

world total) and China 119 million (about 15%). Undernourished<br />

people thus added up to about 15% of the population in<br />

countries w<strong>here</strong> rice is the staple cereal.<br />

When assuming that, to eliminate these nutritional deficiencies,<br />

this disadvantaged segment of the population would<br />

have to increase its average food intake by 25%, the overall<br />

food supply in 2025 would have to rise by 3.75% above the<br />

level needed to provide larger populations merely with today’s<br />

inadequate diets. An excellent confirmation of this additional<br />

amount comes from the FAO’s estimates of the relative inadequacy<br />

of the food supply that was calculated for all of the<br />

world’s countries for the early 1990s and that ranged for the<br />

rice-eating countries from roughly 1% in Brazil and Egypt to<br />

nearly 9% in Bangladesh (FAO 1996). The populationweighted<br />

mean of this relative inadequacy was almost exactly<br />

4% for the ten countries and improvements during the 1990s<br />

would have reduced it by about 10%.<br />

Dietary transitions<br />

Predicting the course of dietary transitions is difficult because<br />

they can be greatly influenced by unexpected changes in a<br />

nation’s economic course: post-Mao China is the best example<br />

of such unpredictable shifts. As gross domestic product (GDP),<br />

and with it average income, rises beyond subsistence levels, it<br />

Annual rice consumption (kg capita –1 )<br />

200<br />

150<br />

100<br />

50<br />

Myanmar<br />

Bangladesh<br />

Vietnam<br />

Indonesia<br />

Philippines<br />

Thailand<br />

India<br />

China<br />

0<br />

1,000 10,000 100,000<br />

PPP GDP capita –1 (2001 US$)<br />

may be accompanied by a temporary increase in demand for<br />

staple grain, followed by a prolonged decrease in consumption<br />

as more varied diets and higher shares of lipids (both plant<br />

oils and animal fats), meat, eggs, and dairy and aquatic products<br />

displace staple grains (Caballero and Popkin 2002). No<br />

other rice-eating country experienced such a precipitous decline<br />

in average intake as did post-World War II Japan: as annual<br />

per capita consumption dropped to less than 60 kg, rice<br />

ceased to be a staple food and became more of a luxury foodstuff<br />

(Chern et al 2003). The South Korean drop was also precipitous,<br />

from nearly 125 kg per capita in 1975 to about 85 kg<br />

in 2000, or more than 30% in 25 years.<br />

Many country-specific scenarios of future dietary trends<br />

are thus possible, but t<strong>here</strong> is no doubt about the general decline<br />

in average per capita rice consumption with rising economic<br />

performance. Every tripling of purchasing power parity-adjusted<br />

per capita GDP appears to be accompanied by a<br />

50-kg decline in average annual per capita rice consumption<br />

(Fig. 2). Consequently, even when assuming a sluggish growth<br />

of average per capita GDPs in the world’s ten most populous<br />

rice-eating countries—on the order of 1.5% per year, or less<br />

than half of the rate they achieved during the 1990s—a nearly<br />

50% increase in that average would correspond to an annual<br />

per capita reduction of about 20 kg of milled rice. By 2025,<br />

this would translate into overall demand about 20% below the<br />

level that would result from unchanged dietary patterns.<br />

Overall demand for rice<br />

Brazil<br />

South Korea<br />

Japan<br />

Fig. 2. Log-normal relationship between per capita GDP (PPP) and<br />

annual per capita rice consumption at the beginning of the 21st<br />

century.<br />

This is not a forecast, merely an exploration of key<br />

countervailing trends that point us in the most likely direction<br />

and that should be useful in guiding our decisions regarding<br />

future agronomic efforts. By 2025, population growth in the<br />

world’s ten most populous rice-eating countries whose con-<br />

22 <strong>Rice</strong> is life: scientific perspectives for the 21st century


sumption dominates the global demand for rice will increase<br />

demand by about 25%; lower intakes because of aging and the<br />

physically less active population would reduce it by about 5%,<br />

and improvements in average diets needed to eliminate the<br />

existing undernutrition would boost it by about the same<br />

amount. The single largest factor determining the eventual<br />

outcome will be the extent and rapidity of dietary change and<br />

even very conservative assumptions point to a decline on the<br />

order of 20%.<br />

This would leave us with the need to produce only about<br />

5% more rice than we do now, or, bracketing the estimate by a<br />

factor of two, the range would be from no net increase at all to<br />

as much as a 10% higher output. Postharvest losses in the ten<br />

most populous rice-eating countries are on the order of 15%<br />

(Smil 2000) and cutting them in half during the next generation<br />

would only reinforce the conclusion that t<strong>here</strong> may be no<br />

need for any net increase in rice production, or that the needed<br />

increase could be only a marginal addition of a few percent<br />

above the current level.<br />

Even in the unlikely case that these estimates err on the<br />

low side by as much as 100%, it is obvious that, during the<br />

first quarter of the 21st century, we will need increases in global<br />

rice production that will not be even remotely comparable<br />

to those of the past 25 years. Consequently, our research and<br />

development should concentrate primarily on the maintenance<br />

of existing yields, on improved nutritional quality, and on lowering<br />

the environmental effects of rice cultivation, particularly<br />

on reducing large (commonly in excess of 60%) losses of nitrogen<br />

from applied urea (Cassman et al 2002).<br />

References<br />

Caballero B, Popkin BM, editors. 2002. The nutrition transition:<br />

diet and disease in the developing world. Amsterdam (Netherlands):<br />

Elsevier. 261 p.<br />

Cassman KG et al. 2002. Agroecosystems, nitrogen-use efficiency,<br />

and nitrogen management. Ambio 31:132-140.<br />

Chern Wen S et al. 2003. Analysis of the food consumption of Japanese<br />

households. Rome (Italy): Food and Agriculture Organization<br />

of the United Nations. 88 p.<br />

FAO (Food and Agriculture Organization of the United Nations).<br />

1996. The sixth world food survey. Rome (Italy): FAO. 153<br />

p.<br />

FAO (Food and Agriculture Organization of the United Nations).<br />

2002. The state of food insecurity in the world 2002. Rome<br />

(Italy): FAO. 36 p.<br />

Smil V. 2000. Feeding the world. Cambridge, Mass. (USA): The<br />

MIT Press. 360 p.<br />

UN (United Nations). 2002. World population prospects: the 2002<br />

revision. New York (USA): UN. http://esa.un.org/unpp.<br />

Notes<br />

Author’s address: Faculty of Environment, University of Manitoba,<br />

Winnipeg R3T 2N2, Canada, e-mail: vsmil@cc.umanitoba.ca.<br />

Development of sustainable agriculture<br />

from rice, water, and the living environment<br />

Riota Nakamura<br />

The Green Revolution based on the development<br />

of irrigated agriculture<br />

Wisdom developed from soil and water has continuously been<br />

the fundamental element of all human activities since ancient<br />

civilization. The tragedies and ruins of the Mesopotamian/<br />

Sumerian civilization remind us of the significance of building<br />

sustainable agriculture and society. The drama of the collapse<br />

of Mesopotamia started with a gradual rising of the saline<br />

groundwater level. The collapse advanced rapidly when<br />

this level exceeded a threshold. It is well known that this problem<br />

was caused by faulty irrigation. Can we be confident that<br />

the current threshold is high enough when we look at the global<br />

expansion of commercialized agriculture and hazardously<br />

exploited water resources, such as in the Aral Sea basin, the<br />

Ogallala aquifer (Nebraska) and Central Valley (California) in<br />

the United States, Punjab and Haryana in India, and Northern<br />

China<br />

A stable water supply was a strong driving force behind<br />

the Green Revolution. Irrigated agriculture provides an essen-<br />

tial environment for high yield, so that improved bred varieties<br />

of crops can be fully used. From 1961 to 2002, global irrigated<br />

agricultural land roughly doubled from 139 million to<br />

277 million ha, while total land for arable and permanent crops<br />

expanded slightly from 1,357 million to 1,534 million ha (Fig.<br />

1). Global population and cereal production have also doubled<br />

from 3.08 billion to 6.23 billion and from 877 million metric<br />

tons to 2.03 billion metric tons. Irrigated land, which accounts<br />

for about 18% of agricultural land area, produces about 40%<br />

of the food for the global population, contributing considerably<br />

to the alleviation of global poverty and starvation.<br />

Sound and sustainable irrigated agriculture is indispensable<br />

for humankind to survive in the future. Now, about 70%,<br />

or 2,504 km 3 , of the world’s annual freshwater usage of 3,572<br />

km 3 is for agriculture, and, of this, about 70% is used mainly<br />

for rice paddy agriculture in Asia.<br />

Our generation is primarily responsible for assuring sustainable<br />

and efficient agriculture through wiser governance and<br />

management of soil and water resources.<br />

Keynotes 23


Index (1961 = 100)<br />

250<br />

240 Total cereal production (1961 = 100)<br />

Population (1961 = 100<br />

230<br />

Irrigation area (1961 = 100)<br />

220 Land for arable and permanent crops (1961 = 100)<br />

210 Rainfed area (1961 = 100)<br />

200<br />

190<br />

180<br />

170<br />

160<br />

150<br />

140<br />

130<br />

120<br />

110<br />

90<br />

1961<br />

1963<br />

1965<br />

1967<br />

1969<br />

1971<br />

1973<br />

1975<br />

1977<br />

1979<br />

1981<br />

1983<br />

1985<br />

1987<br />

1989<br />

1991<br />

1993<br />

1995<br />

1997<br />

1999<br />

2001<br />

2002<br />

Year<br />

Fig. 1. World cereal production, population, and farmland area (1961-2002).<br />

World water issues and conversion of policies<br />

for irrigation—from expansion to increasing efficiency<br />

of existing systems<br />

Fresh water existing on the global land surface in readily usable<br />

forms such as lakes, swamps, and rivers accounts for only<br />

about 0.0075% (104,620 km 3 ) of all the water existing on our<br />

planet. This percentage is equivalent to the ratio of two teaspoonfuls<br />

of water (15 cm 3 ) in a typical household bathtub<br />

full of water. Of the annual global rainfall on land, which supports<br />

the hydrologic cycle of fresh water, only about 40%<br />

(45,000 km 3 ) becomes potential water resources after excluding<br />

evaporation. Humankind has to share this available water<br />

with other water uses such as industry, domestic use, and<br />

biodiversity while producing food for the more than 6 billion<br />

people living on the planet.<br />

In the 20th century, the century of fire and machines, we<br />

strived to develop water resources mostly through construction<br />

technologies such as large reservoirs, until the early 1980s.<br />

Not only drastic growth in the world human population but<br />

also worldwide trends of economic growth and expansion of<br />

cities, especially in developing countries, resulted in sharp increases<br />

in demand for domestic and industrial water use, and<br />

put strong and continuous pressure on the increase in water<br />

supplies. Water resource development by construction of “hardware”<br />

was promoted in many regions around the world.<br />

However, after the 1980s, this type of development met<br />

with certain limitations. Although the most effective way to<br />

increase water resources, speaking from an engineering viewpoint,<br />

was to build large reservoirs, appropriate construction<br />

sites for new reservoirs became limited. Moreover, governments<br />

of developing countries faced financial pressure for the<br />

operation and maintenance of overaged water facilities.<br />

In the 21st century, the century of water and life, another<br />

option has been recognized as a better solution. That is to increase<br />

the efficiency of the use of water in existing systems. In<br />

many countries, attempts to increase this efficiency have been<br />

made through (1) renovating irrigation water facilities such as<br />

lining canals with concrete, (2) introducing/reinforcing volumetric<br />

water pricing, and (3) introducing participatory irrigation<br />

management (PIM).<br />

Efficiency of agricultural water use in different regional<br />

conditions—arid and humid<br />

Improving water-use efficiency in agriculture is a key issue<br />

during international water discussions nowadays. Many experts<br />

have reported case studies and mentioned success stories.<br />

These reports are helpful for improving water-use efficiency<br />

in regions w<strong>here</strong> it is reasonable for farmers to constantly<br />

use a minimum amount of irrigation water to secure<br />

good crop growth. The concept of water-use efficiency in this<br />

definition is typically applicable to agriculture in arid/semiarid<br />

regions. This concept comes from the idea that all water<br />

should be consumed in crop fields in the form of evapotranspiration,<br />

allowing no water to be lost elsew<strong>here</strong>.<br />

However, in humid regions blessed with abundant precipitation,<br />

the shortcomings of this concept have now come to<br />

be widely recognized. These shortcomings are mainly caused<br />

by neglect of the following factors accompanying rice paddy<br />

farming in these regions: (1) the highly substitutable characteristic<br />

of water usage and labor investment, (2) the dynami-<br />

24 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Socioeconomic externalities generated by irrigation<br />

and rice paddy agriculture in the Asian monsoon region<br />

Automatically provided by agricultural activities<br />

Multiple use of water by farmers and residents<br />

Aquaculture, duck raising, washing, cleaning, bathing,<br />

cooling, gardening, fire fighting, etc.<br />

Nonuse-value in cultural-religious activities<br />

Multifaceted socioeconomic benefits to the public<br />

Protect aqua-ecosystem, enhance water-related environment,<br />

form landscape, recharge groundwater aquifer, stabilize<br />

downstream river flow by return flow, etc.<br />

Intentionally provided by special consideration and actions<br />

l<br />

l<br />

l<br />

l<br />

Provide water from agriculture for domestic use during severe<br />

dry spells<br />

Increase performance of paddy fields while protecting reservoirs<br />

during extreme floods<br />

Create winter sanctuaries for migratory birds<br />

Restore groundwater level for downstream city, etc.<br />

Fig. 2. Externalities provided by activities of irrigation and rice paddy agriculture.<br />

cally fluctuating competitiveness among water users over the<br />

short term, and (3) the enormous value of socioeconomic elements<br />

other than food/fiber production; this value is defined<br />

as an “externality.” Factor 1 allows for reduced labor investment<br />

costs w<strong>here</strong> farmers use much more than the minimum<br />

amount of water required for meeting crop water requirements.<br />

Factor 1 also allows for a drastic reduction in water use through<br />

farmers’ collective efforts during severe dry spells that occur<br />

unexpectedly under the conditions of factor 2.<br />

A considerable part of the water irrigated into rice paddy<br />

fields is not consumed but drained into the basin downstream<br />

during the rainy season from vast paddy fields in the Asian<br />

monsoon region. This is because (1) the value of water is quite<br />

low because of abundant precipitation and low competitiveness<br />

among water users, and (2) immersion cultivation with a<br />

larger amount of water than the equivalent to evapotranspiration<br />

reduces labor investment cost.<br />

This behavior seemingly decreases water-use efficiency,<br />

but, on the contrary, the affluent water use provides diverse<br />

and enormous value for socioeconomic externalities. The<br />

drained return flow also helps to preserve nature, resulting in<br />

any negative externality counting for nothing. Note that, in<br />

rice paddy agriculture in humid regions, the irrigation water<br />

automatically serves as an externality, w<strong>here</strong>as, in upland fields<br />

and relatively arid regions, the water has to be set aside and<br />

preserved, especially for externalities.<br />

Socioeconomic externalities in rice paddy agriculture<br />

in humid regions<br />

The enormous external value generated by irrigated rice paddy<br />

agriculture can be grouped in the following categories: (1)<br />

multiple use of water by farmers and residents for aquaculture,<br />

duck raising, washing, cleaning, bathing, cooling, gardening,<br />

and fire fighting; (2) multifaceted socioeconomic benefits<br />

to the public such as protecting the aqua-ecosystem, enhancing<br />

the water-related environment, forming landscape,<br />

recharging the groundwater aquifer, and stabilizing downstream<br />

river flow by return flow; and (3) various other nonuse-values<br />

in cultural-religious activities (Fig. 2).<br />

The socioeconomic situation of countries in the Asian<br />

monsoon region is diversified, including tropical developing<br />

and temperate developed countries. However, predominant rice<br />

paddy agriculture and its enormous external value are common<br />

to them. Note that the external values are not only important<br />

for farmers and the economy in developing countries but<br />

are also very valuable for citizens of developed countries in<br />

providing multifaceted socioeconomic benefits.<br />

Water productivity, often advocated by the catch phrase<br />

“more crop per drop,” is a newly conceptualized term as an<br />

indicator of water-use efficiency in rainfed agriculture, using<br />

about 16,000 km 3 of rainwater annually, as well as in irrigated<br />

agriculture. This concept, however, unjustly underestimates the<br />

water productivity of rice paddy agriculture in the Asian monsoon<br />

region. T<strong>here</strong>fore, it must be reevaluated after incorporating<br />

the high value of socioeconomic externalities.<br />

Traditional participatory irrigation management<br />

and governance (PIM/G) in rice paddy systems<br />

Recent challenges to establish PIM in Asian monsoon countries<br />

show difficulties in transferring the operation and management<br />

(O&M) of irrigation from government agencies to<br />

farmers. Lessons learned from these challenges include how<br />

to establish effective incentives for farmers. Initially, strong<br />

economic incentives superior to disincentives such as labor<br />

Keynotes 25


contributions of O&M and water charge are necessary to launch<br />

modernized operations. Afterward, the diverse values of socioeconomic<br />

externalities for farmers become driving forces<br />

to improve their performance. The diverse values are realized<br />

step by step through various group activities. Well-sustained<br />

traditional PIM shows many examples of built-in incentives<br />

related to externalities as well as agricultural production.<br />

When we look around the world, we find many current<br />

irrigation systems that have been fulfilling both requisites of<br />

food production and externalities, such as the Muang Fai in<br />

Thailand, Kanna in Sri Lanka, and Subak in Indonesia. The<br />

Dujiangyan irrigation system in Sichuan, China, was established<br />

in 250 B.C. and is still working for about 670,000 ha of<br />

farmland. In Japan, many old irrigation systems have lasted<br />

for centuries, with technology advancing in stages. It has to be<br />

noted that these systems always consist of weirs, canals, and<br />

ponds operated and managed by indigenous farmers’ organizations,<br />

namely, Land Improvement Districts (LIDs). Most of<br />

them are historically as old as their weirs and canals. The LIDs<br />

are responsible for O&M of nationwide canals extending a<br />

total length of about 400,000 km (equivalent to ten times around<br />

the globe).<br />

We found it very interesting that irrigation systems that<br />

achieve a good balance between externalities and food production<br />

are observed mostly in old systems. In presenting this<br />

paper at the WRRC, I wanted to mention representative canal<br />

systems that have completed the difficult task of satisfying both<br />

requisites.<br />

Renaissance of efficient and sustainable rice production<br />

with socioeconomic externalities generated by PIM/G<br />

Group activities through PIM/G can generate much more value<br />

for externalities than individually disconnected activities. A<br />

good example is shown by a full cultural and religious performance<br />

in Bali, Indonesia. Such a group activity works as a<br />

platform for consultation in a local community and sometimes<br />

develops new activities such as mutual farming aid, group<br />

composting, and joint ventures for purchasing and shipping.<br />

In Japan, agriculture has lost its substantial position in<br />

the country’s economy. However, farmer group activities<br />

through PIM/G create new values for socioeconomic externalities<br />

as a safety net against natural disasters and as a generator<br />

of resources for other sectors. At the WRRC, I can mention<br />

examples of providing water from agriculture to domestic<br />

use during severe dry spells, increasing the performance of<br />

paddy fields while protecting reservoirs during extreme floods,<br />

creating winter sanctuaries for migratory birds, and restoring<br />

groundwater levels for downstream water use in cities in winter.<br />

The value of socioeconomic externalities cannot be commercially<br />

exchanged, w<strong>here</strong>as agricultural products are widely<br />

traded in the international market. Irrigation systems and water<br />

accompanied by the value of externalities are social overhead<br />

capital and commons. T<strong>here</strong>fore, development programs<br />

for irrigated agriculture should take into account external value<br />

as a benefit vis-à-vis the cost of the investment.<br />

I believe that improving water-use efficiency by fully<br />

taking into account the value of socioeconomic externalities<br />

can create a future with more sustainable agriculture through a<br />

rice-based system. Sustainability of this agriculture will be<br />

strongly supported by interactions between human activities<br />

through PIM/G and broad-banded products, including various<br />

economic values, the living environment, and cultural-religious<br />

activities, as well as the agricultural product rice.<br />

The proposition I have maintained in this paper might<br />

be a claim for the renaissance of old systems because water<br />

management in the 21st century requires a holistic approach<br />

in harmony with various factors, including externalities, as<br />

some old irrigation systems have achieved. These old systems<br />

make a good guide for future sustainable development.<br />

I especially wish to acknowledge the contributions of<br />

Mr. Kazumi Yamaoka of the National <strong>Institute</strong> for Rural Engineering<br />

in co-authoring this document and preparing the presentation<br />

materials.<br />

<strong>Research</strong> strategy for rice in the 21st century<br />

Ronald P. Cantrell and Gene P. Hettel<br />

Thank you for this opportunity to speak<br />

to you as one of the keynoters of this<br />

week’s World <strong>Rice</strong> <strong>Research</strong> Conference,<br />

which—as the culminating scientific<br />

event of the <strong>International</strong> Year<br />

of <strong>Rice</strong> 2004—has brought to Tsukuba<br />

the planet’s leading rice scientists to exchange<br />

the latest research information<br />

on key rice-related issues.<br />

Why rice research must continue<br />

Before we go into the details of what we think should be the<br />

research strategy for rice in the 21st century, I would like to<br />

discuss, briefly, why indeed rice research for developing countries<br />

must continue and be reinvigorated.<br />

Since the dawn of the Green Revolution—which began<br />

in Asia with <strong>IRRI</strong>’s release in 1966 of IR8, the first modern,<br />

high-yielding semidwarf rice variety—the global rice harvest<br />

has more than doubled, racing slightly ahead of population<br />

growth. This increased production and the resulting lower<br />

26 <strong>Rice</strong> is life: scientific perspectives for the 21st century


prices of rice across Asia have been one of the most important<br />

results of the higher yields that rice research and new farming<br />

technologies have made possible. Around 1,000 modern varieties—approximately<br />

half the number released in 12 countries<br />

of South and Southeast Asia over the last 38 years—are linked<br />

to germplasm developed by <strong>IRRI</strong> and its partners alone—a<br />

large impact indeed (Cantrell and Hettel 2004a). These modern<br />

varieties and the resultant increase in production have increased<br />

the overall availability of rice and also helped to reduce<br />

world market rice prices by 80% over the last 20 years.<br />

Poor and well-to-do farmers alike have benefited directly<br />

through more efficient production that has led to lower unit<br />

costs and increased profits. Poor consumers have benefited<br />

indirectly through lower prices. This has brought national food<br />

security to China and India, not to mention Indonesia and other<br />

countries.<br />

So, why is more rice research needed Clearly, t<strong>here</strong> are<br />

two major integral challenges—for now and well into the 21st<br />

century—involving rice—and particularly in Asia (Cantrell and<br />

Hettel 2004a). The first is the ability of nations to meet their<br />

national and household food security needs with an ever-declining<br />

natural resource base, two of the critical resources being<br />

water and land. How the current level of annual rice production<br />

of around 545 million tons can be increased to about<br />

700 million tons to feed an additional 650 million rice eaters<br />

by 2025 (D. Dawe, <strong>IRRI</strong>, 2004, pers. comm.) using less water<br />

and less land is indeed one great challenge in Asia.<br />

The second is—as has been stated so eloquently by the<br />

United Nations as one of its eight Millennium Development<br />

Goals (www.undp.org/mdg)—the eradication of extreme poverty<br />

and hunger. <strong>Rice</strong> is so central to the lives of most Asians<br />

that any solution to global poverty and hunger must include<br />

research that helps poor Asian farmers reduce their risks and<br />

earn a decent profit while growing rice that is still affordable<br />

to poor consumers.<br />

These new challenges that we face today may not be on<br />

the mammoth scale of those at the onset of the Green Revolution<br />

some 38 years ago when large parts of Asia were on the<br />

brink of famine and starvation. But perhaps they are even more<br />

difficult from a technology standpoint. Indeed, the challenges<br />

for rice farmers and researchers in 1966—although daunting—<br />

were fairly straightforward. Renowned economist Prof. Peter<br />

Timmer points out that the task of agricultural development<br />

was much easier back then when the need for greater cereal<br />

output to accomplish national<br />

food security was met by new<br />

seed-fertilizer technologies,<br />

which were already in fairly<br />

advanced stages of development<br />

(Timmer 2003). Today,<br />

it is important to elevate the<br />

awareness of key<br />

policymakers and donors that<br />

rice research must continue<br />

so that we all can face these<br />

new—and much more complicated—challenges<br />

of the<br />

21st century.<br />

<strong>Research</strong> priorities<br />

Bridging the yield gap<br />

So, now that we have made the case that rice research must<br />

continue, what are the priorities Clearly, one area of research<br />

involves the continuing effort to close the quite large rice yield<br />

gap between what is possible and what is actually achieved in<br />

farmers’ fields—especially in the more marginal environments<br />

such as the rainfed lowlands and uplands—across regions,<br />

ecological zones, and crop seasons in all rice-growing countries<br />

in the Asia-Pacific Region (FAO 1999, Pingali 2001).<br />

This yield deficit ranges from 10% to 60% between attainable<br />

and economically exploitable yields depending on the ecosystems<br />

and countries. The various factors currently contributing<br />

to the yield gap in different countries and regions include biophysical,<br />

technical/management, socioeconomic, institutional/<br />

policy, technology transfer, and adoption/linkage problems<br />

(FAO 1999).<br />

Reducing the yield gap can be seen as the local solution<br />

to a global problem. It can lead to increased production with<br />

the additional incentives of cost reduction, poverty alleviation,<br />

social justice, and equity. The FAO suggests that reducing<br />

the yield gap could alone supply as much as 60% of the<br />

increased annual rice demand by 2025 that we mentioned earlier<br />

(FAO 1999).<br />

Annual changes in weather can cause yield variations of<br />

nearly 30% and this can mask gains made by plant breeders.<br />

Currently, we estimate that breeding new elite cultivars and<br />

Keynotes 27


using the best management techniques could lead to yield improvements<br />

of 18% in the coming decades if the negative effects<br />

of climate change can be avoided (Sheehy et al 2005).<br />

The incidence of weather extremes appears to be increasing<br />

and t<strong>here</strong> is a need to breed new rice cultivars that can tolerate<br />

the worst aspects of climate change.<br />

Recent <strong>IRRI</strong> research has brought both good and bad<br />

news. The good news is: It appears that improved crop and<br />

nitrogen management has effectively closed the yield gap between<br />

simulated potential yield and actual yield of existing<br />

elite cultivars in long-term plots at <strong>IRRI</strong> (Kropff et al 2003).<br />

The bad news is: Even when these improved crop and nitrogen<br />

management practices are employed, t<strong>here</strong> can still be yield<br />

fluctuations, which are largely associated with climatic factors<br />

(Dobermann et al 2000). Recent fluctuations in grain yield<br />

trials at <strong>IRRI</strong> have been associated with reduced solar radiation<br />

and increased seasonal mean minimum temperature, and<br />

not related to crop management (Kropff et al 2003, Peng et al<br />

2004b).<br />

In many countries, new technologies are not making the<br />

impact that they should be in closing the yield gap. To make<br />

any major breakthroughs in the immediate future will first require<br />

the bridging of another gap—the knowledge gap<br />

(Schiffrin 2001). Extension specialists and the farmers they<br />

serve are starved for information. They need new management<br />

skills and technical know-how as soon as possible.<br />

To help close this knowledge gap by getting technology<br />

off the shelf and into farmers’ hands, scientists and information<br />

and communication technology (ICT) specialists at <strong>IRRI</strong><br />

have placed a <strong>Rice</strong> Knowledge Bank on the Web<br />

(www.knowledgebank.irri.org) aimed at extension workers and<br />

farmers. At the speed of a keystroke, it can provide the latest<br />

information—from diagnosing field problems via <strong>Rice</strong>Doctor<br />

(www.knowledgebank.irri.org/riceDoctor_MX/default.htm) to<br />

making crop management decisions via Trop<strong>Rice</strong><br />

(www.knowledgebank.irri.org/troprice/default.htm). Usually,<br />

only more prosperous farmers are currently going online. But,<br />

sooner than some might expect, even the poorest farmers will<br />

be going online to access field problem and crop management<br />

information near w<strong>here</strong> they toil in their rice fields. For example,<br />

in the Philippines, the Open Academy of Philippine<br />

Agriculture predicts that within 2 years it will be commonplace<br />

for Filipino farmers—through strategically located<br />

Internet kiosks in farming villages—to be diagnosing crop pests<br />

by accessing the Web and sharing information with peers anyw<strong>here</strong><br />

in the country using electronic mail and cell phone technology<br />

(Marquez 2004).<br />

In addition, continued on-farm research will be needed<br />

to fine-tune new technologies if the yield gap is to be narrowed.<br />

For example, <strong>IRRI</strong> has<br />

a long tradition of listening to<br />

farmers (Hettel and Dedolph<br />

1996) and planning farmer<br />

participatory research (FPR).<br />

FPR is an approach that involves<br />

encouraging farmers to<br />

engage in experiments in their<br />

own fields so that they can<br />

learn, adopt new technologies,<br />

and spread them to other farmers.<br />

With scientists acting as<br />

facilitators, farmers and scientists<br />

work closely together<br />

from initial design of the research<br />

project to data gathering,<br />

analysis, final conclusions,<br />

and follow-up actions.<br />

A great example of this is the ongoing FPR in Bangladesh<br />

w<strong>here</strong> farmers’ livelihoods are being improved by closing rice<br />

yield gaps caused by weeds. Farmers in Bangladesh grow rice<br />

over a wide range of rainfed and irrigated lands and weeds are<br />

a major constraint. In this project of the Irrigated <strong>Rice</strong> <strong>Research</strong><br />

Consortium (www.irri.org/irrc/weeds/closing.asp), researchers<br />

are examining two contrasting farming systems in<br />

Comilla and Rajshahi districts to learn how different rice-cropping<br />

systems affect weed abundance and methods for their<br />

management. This work has shown the benefit of integrated<br />

management involving herbicides in combination with manual<br />

weeding. Application of herbicides or use of a hand-pushed<br />

weeder in transplanted rice results in similar yields—and a<br />

28 <strong>Rice</strong> is life: scientific perspectives for the 21st century


one-third reduction in weeding costs—compared to farmers’<br />

current practice of weeding twice by hand.<br />

In one study, more than 100 farmers in both districts participated<br />

in measuring the yield gaps caused by weeds in their<br />

own fields under their own practices. The results are helping<br />

them to make management decisions about whether or not to<br />

invest in additional weeding and/or fertilizer.<br />

Maintenance research (MR)—exciting<br />

and award-winning and a jumpstart<br />

for a Doubly Green Revolution in rice!<br />

A second area of research that we must continue is maintenance.<br />

The tendency for some researchers is to continually<br />

chase the newest fad—organizations sometimes stop doing one<br />

thing and start doing another because it might be easier to “sell”<br />

the latest research trend that is getting the “buzz.” Indeed, research<br />

with the mundane label of “maintenance” is often difficult<br />

to promote to donors. But, even so, truly successful organizations<br />

will always have that appropriate mix of MR and<br />

new strategic directions.<br />

For example, although <strong>IRRI</strong> is embarking on novel and<br />

exciting strategic research on a number of fronts involving new<br />

tools and directions (mentioned later in this paper), it is still<br />

committed to MR. For example, during our recent external review,<br />

we emphasized to the review panel that our germplasm<br />

improvement work will continue to contribute to both maintaining<br />

yield gains and increasing yield potential—at least 1%<br />

per year (the average of the recent past). In light of what we<br />

are discovering in our long-term yield plots (mentioned above),<br />

our maintenance breeding will be placing particular emphasis<br />

on stress associated with anticipated environmental and climatic<br />

changes.<br />

Dana Dalrymple, senior research adviser and agricultural<br />

economist at USAID, who has been thinking and writing<br />

about MR recently, says we cannot take current yield levels<br />

for granted and that an increasing amount of MR will be needed<br />

to hold on to the current levels. He adds that MR, which is<br />

heavily oriented to plant and animal diseases and insect pests,<br />

tends to be taken for granted until t<strong>here</strong> is a severe outbreak of<br />

some type and to get overlooked in priority setting (Dalrymple<br />

2004).<br />

One great challenge in agricultural MR is the development<br />

of natural resistance to reduce chemical usage in agriculture.<br />

The search for new chemical treatments in agriculture<br />

has gone on for over a century and is never-ending (Dalrymple<br />

2004). In rice, <strong>IRRI</strong> is countering this trend with significant<br />

projects in Asia—showing that MR is not necessarily mundane<br />

and it can even be exciting and award-winning and that,<br />

indeed, a Doubly Green Revolution in rice has already been<br />

jumpstarted (Cantrell and Hettel 2004b).<br />

China. <strong>IRRI</strong> researchers and collaborators achieved notable<br />

success with integrated pest management (IPM) in China’s<br />

southwestern province of Yunnan. T<strong>here</strong>—in what the New<br />

York Times called “one of the largest agricultural experiments<br />

ever” (Yoon 2000)—we found that intercropping rows of different<br />

varieties of rice can almost completely control the devastating<br />

rice blast disease (Zhu et al 2000). Some farmers t<strong>here</strong><br />

were already using this technique, albeit in a haphazard way.<br />

Keynotes 29


We scientifically tested several variations of the concept and<br />

improved it. Now we are disseminating our findings with confidence<br />

that the practice not only reduces farmers’ reliance on<br />

chemical pesticides, t<strong>here</strong>by protecting the environment, but<br />

also improves yield and income to give farmers the options<br />

they need to break out of the poverty trap. Word-of-mouth is<br />

already leading to the technique’s wide adoption on nearly 1<br />

million hectares across 10 provinces in China.<br />

Vietnam. Our Vietnam study offers valuable lessons on<br />

how to reduce pesticide applications. We converted our findings<br />

into one simple rule: “Don’t spray for the first 40 days.”<br />

We launched a media campaign to deliver the message to farmers,<br />

stressing the cost savings and health benefits of reduced<br />

spraying. The result In the test area of 21,000 households,<br />

after an 18-month interval, we recorded a 53% reduction in the<br />

number of insecticide applications—without affecting yield!<br />

Many farmers reduce input costs by US$30–50 per season—<br />

equal to a month’s income in Vietnam. Eventually, this effort<br />

persuaded almost 2 million rice-growing households in the<br />

Mekong Delta to cut back on using harmful and unnecessary<br />

farm chemicals. Underscoring the significance of this work,<br />

the project received the St. Andrews Prize for the Environment<br />

from Scotland’s St. Andrews University in 2002 and the <strong>International</strong><br />

Green Apple Environment Award from the U.K.-based<br />

Green Organization in 2003 (<strong>IRRI</strong> 2003).<br />

SSNM. Our past research has produced awareness of excessive<br />

use of chemical nitrogen fertilizer in farmers’ fields.<br />

So, we are now promoting a technique called site-specific nutrient<br />

management (SSNM) across 20 key sites in eight countries<br />

in tropical and subtropical Asia. The technique enables<br />

farmers to “feed” the rice plant with nutrients only as and when<br />

needed, with optimal use of existing indigenous nutrient<br />

sources, including crop residues and manures, and timely application<br />

of fertilizer (Wang et al 2004).<br />

More efficient use of nitrogen through the principles of<br />

SSNM in ratios to better match plant needs can reduce the<br />

incidence of rice disease and insect pests, which in turn further<br />

reduces the need for pesticides. The benefits from SSNM<br />

multiply when improved management of phosphorus and potassium<br />

is thrown into the mix with improved N management.<br />

Improved management of N, P, and K fertilizers through SSNM<br />

is now increasingly being shown in Asia to reduce disease and<br />

insect damage (Buresh 2004, Jahn 2004, Wang et al 2004)—<br />

yet another avenue on which farmers can reduce their need for<br />

pesticides and usher in the Doubly Green Revolution in rice.<br />

When does MR begin T<strong>here</strong> are some interesting new<br />

twists on the importance of maintenance research and Dr.<br />

Dalrymple has been recently looking at the interface between<br />

MR and what he calls productivity-enhancing research (PER).<br />

He assumes that t<strong>here</strong> is an area of overlap between the two,<br />

and that, in some cases, particularly significant advances in<br />

MR could actually contribute to increasing yield. This is likely<br />

to be true in the case of resistance to plant diseases and insects<br />

(D. Dalrymple, USAID, 2004, pers. comm.). Clearly, the line<br />

between MR and PER is fuzzy and it raises some definitional<br />

questions, such as, When does MR actually begin to kick in<br />

Otsuka et al (1994) concluded that the Green Revolution would<br />

not have been very revolutionary without the development and<br />

the diffusion of second-generation modern rice varieties with<br />

multiple pest and disease resistance. So, depending on w<strong>here</strong><br />

MR is placed on the rice-improvement breeding continuum, it<br />

can be argued that, without it, t<strong>here</strong> might not have been a<br />

Green Revolution.<br />

Exciting strategic research—new directions<br />

and new tools to get us t<strong>here</strong><br />

New tools such as biotechnology are affording us the opportunity<br />

to follow some new strategic research directions. As we<br />

mentioned earlier, any successful agricultural research institution<br />

must have a harmonious mix of maintenance research and<br />

strategic research on its agenda. We believe that our strategic<br />

directions addressing such critical issues as the rice yield barrier,<br />

global warming, the water crisis, and human nutrition are<br />

the right blend for <strong>IRRI</strong>.<br />

Breaking the yield barrier. During the recent 4th <strong>International</strong><br />

Crop Science Congress in Brisbane (26 Sept.-1 Oct.),<br />

<strong>IRRI</strong> researchers provided an update on progress in breaking<br />

the yield barrier using the ideotype—or idealized plant—approach<br />

(Peng et al 2004a). Great progress has been made with<br />

second-generation new plant type (NPT) lines developed by<br />

30 <strong>Rice</strong> is life: scientific perspectives for the 21st century


crossing elite indica plants with improved tropical japonica<br />

plants (Virk et al 2004). Our researchers believe that the recent<br />

success of “super” hybrid rice breeding in China combined<br />

with progress of NPT breeding at <strong>IRRI</strong> will contribute<br />

greatly to the goal of breaking the yield barrier in irrigated<br />

rice-based cropping systems.<br />

However, leaving no stone unturned in the quest for a<br />

higher yield potential in rice, we are also looking at the link<br />

among photosynthesis, yield, and radiation-use efficiency—<br />

or RUE. Some of our scientists have concluded that the upper<br />

yield limit of rice with its conventional photosynthetic pathway<br />

will go only halfway to a target of increasing rice yield<br />

50% by 2050. Improved crop photosynthesis would then seem<br />

essential. One proposal for increasing rice’s RUE is to incorporate<br />

the high C 4 photosynthetic capacity of a crop such as<br />

maize into rice, which is a less photosynthetically efficient C 3<br />

cereal (Sheehy et al 2000). An additional benefit of such a<br />

change would be a doubling in the efficiency with which the<br />

plant uses water for growth.<br />

Making the photosynthetic pathway of rice resemble that<br />

of maize would require a long-term genetic engineering project<br />

(10–15 years) to introduce genes for enzymes of the C 4 pathway<br />

and for leaf anatomy. If this were accomplished, the benefits<br />

would be enormous across the rice ecosystem spectrum.<br />

A C 4 rice plant would yield the same as a C 3 with half the<br />

transpirational water loss. It would also require significantly<br />

less N fertilizer, thus providing for a cleaner environment and<br />

lower input costs for farmers. In irrigated rice, yield potential<br />

would rise significantly. In drought-prone ecosystems (rainfed<br />

lowland and upland rice), yield could be maintained or increased<br />

with less water and less fertilizer, especially when<br />

coupled with the predicted rising atmospheric concentration<br />

of carbon dioxide that is associated with future world climate<br />

change (see below). Farmers living at the margins in these ecosystems<br />

would see improvements in yield and yield stability.<br />

It would be a new revolution in rice farming.<br />

Global warming. The September 2004 issue of National<br />

Geographic (http://magma.nationalgeographic.com/ngm/<br />

0409) devoted 74 pages to a three-part series of stories on<br />

global climate change. Under the umbrella title of Global<br />

Warning: Bulletins from a Warmer World, the editors state that<br />

t<strong>here</strong>’s no question that Earth is getting hotter—and fast. Warning<br />

signs discussed included retreating glaciers, rising seas,<br />

shrinking lakes, damaged coral reefs, and declining penguin<br />

populations in the Antarctic. Another warning sign that could<br />

have also been included comes directly from the irrigated field<br />

experiments at <strong>IRRI</strong>’s headquarters in the Philippines.<br />

<strong>Research</strong> at <strong>IRRI</strong> agrees with predictions from theoretical<br />

studies that global warming will make rice crops much less<br />

productive unless research to ameliorate its worst effects is<br />

undertaken (Sheehy et al 2005). Early work (Satake and<br />

Yoshida 1978) showed that, as day temperatures increased from<br />

34 to 40 °C, floret sterility increased to 100% and yield fell to<br />

zero. Later, Ziska and Manalo (1996) showed that very high<br />

nighttime temperatures could also reduce yield. More recently,<br />

Peng et al (2004b) suggested that increasing mean minimum<br />

nighttime temperatures were already decreasing yield in the<br />

field acting through previously unknown mechanisms. The<br />

Third Assessment Report of the Intergovernmental Panel on<br />

Climate Change (IPCC; www.ipcc.ch) forecasts that by 2100<br />

mean planet-wide surface temperatures will rise by 1.4 to 5.8<br />

°C. Global warming could threaten to erase the hard-won productivity<br />

gains that have kept the rice harvest in step with population<br />

growth.<br />

Our future studies will focus on investigating the differential<br />

effects of global warming on night versus daytime temperatures<br />

and searching for more heat-tolerant rice. We must<br />

also look at the effects of manmade ozone and other gaseous<br />

pollutants that could have serious effects on rice yield as Asia<br />

continues to develop. Climate and weather are becoming more<br />

complex because of these changing gaseous components in<br />

the atmosp<strong>here</strong>. An important tie-in will include the photosynthetic<br />

pathway research we mentioned earlier—a C 4 rice plant<br />

would fare much better in the warmer world of the future. These<br />

are certainly important issues to include on our strategic research<br />

agenda since—as the UK’s Department for <strong>International</strong><br />

Development states—we cannot afford to ignore the impact of<br />

increasing climate risks to particularly the poor in Asia<br />

(www.dfid.gov.uk/pubs/files/climatechange/11asia.pdf).<br />

The water crisis. As put forth by the CGIAR Challenge<br />

Program on Water and Food, increasing water scarcity and<br />

competition for the same water from nonagricultural sectors<br />

point to an urgent need to improve crop water productivity to<br />

ensure adequate food for future generations with the same or<br />

less water than is presently available to agriculture<br />

(www.waterforfood.org). About 70% of the water currently<br />

withdrawn from all freshwater sources worldwide is used for<br />

agriculture and to grow rice requires about twice as much water<br />

as other grain crops such as wheat or maize. In Asia, irrigated<br />

agriculture accounts for 90% of the total diverted fresh<br />

water used, and more than 50% of this is used to irrigate rice.<br />

Keynotes 31


Until recently, this amount of water has been taken for granted,<br />

but this cannot continue.<br />

To meet the water crisis head-on for rice, the <strong>International</strong><br />

Platform for Saving Water in <strong>Rice</strong> (www.irri.org/ipswar/<br />

about_us/ipswar.htm) has been created as a mechanism to increase<br />

the efficiency and enhance the co<strong>here</strong>nce of research<br />

on water savings in rice-based cropping systems in Asia. The<br />

overarching goal is to conserve water resources, which will in<br />

turn safeguard national and household food security and alleviate<br />

poverty.<br />

About 75% of the world’s rice is produced in irrigated<br />

fields, w<strong>here</strong> farmers can control the amount of water applied.<br />

In the tropics, these systems can produce yields up to 9 t ha –1 ,<br />

but they typically use from 1,000 to 2,000 mm of water per<br />

hectare. This means that from 1,000 to more than 3,000 L of<br />

water are used to produce each kg of rice. In contrast, rainfed<br />

rice can produce yields of up to 5 t ha –1 with a water input of<br />

only 800 mm of well-distributed rainfall.<br />

Approaches to improving water productivity in both irrigated<br />

and rainfed rice systems involve decreasing the water<br />

requirement of irrigated systems without affecting yield and<br />

increasing the yield of rainfed systems without increasing their<br />

water use. These approaches are complementary, with spillover<br />

benefits expected across the irrigated and rainfed systems. The<br />

recent advancement of crop sciences, especially in rice<br />

genomics (see below) and linkage of conventional breeding<br />

with molecular tools, has shown some promising possibilities<br />

for making such innovations a reality. We are already aiming<br />

our strategic research to attack the water problem from several<br />

angles, using modern tools of molecular biology, environmental<br />

monitoring, simulations, and database integration.<br />

Two types of water-saving systems can be used to replace<br />

the traditional irrigated rice production schemes that are<br />

now under threat. One is alternate wetting and drying (AWD).<br />

In this system, the field is irrigated with enough water to flood<br />

the paddy for 3 to 5 days, and, as the water soaks into the soil,<br />

the surface is then allowed to dry for a few days (usually from<br />

2 to 4) before getting re-flooded.<br />

Another alternative is dry-field or aerobic rice, w<strong>here</strong><br />

the rice is sown directly into dry soil, like wheat or maize, and<br />

irrigation is applied to keep the soil sufficiently moist for good<br />

plant growth, but the soil is never saturated. Both of these systems<br />

allow for substantial water savings of from 30% to 50%.<br />

Our strategic research on water will be looking closely<br />

at both of these systems. For example, we have already established<br />

an Aerobic <strong>Rice</strong> Working Group, involving breeders,<br />

physiologists, and water and soil scientists, that is striving to<br />

overcome the many difficulties in taking rice out of its natural<br />

aquatic environment. By developing a completely new management<br />

system, the new aerobic rice should be able to yield<br />

up to 6 t ha –1 using only half the water!<br />

Human nutrition. And finally, the world’s poor will<br />

achieve household food security only when—in addition to<br />

being available in sufficient quantity—the food is of ample<br />

quality as well. Although rice supplies adequate energy in the<br />

form of calories and is a good source of thiamine, riboflavin,<br />

and niacin, it is lacking as a source of vitamin A and other<br />

critical vitamins, iron, zinc, and other micronutrients and amino<br />

32 <strong>Rice</strong> is life: scientific perspectives for the 21st century


We are happy to announce some other exciting developments<br />

in our biofortification work to produce iron-enriched<br />

rice. First, <strong>IRRI</strong> and collaborators, including <strong>here</strong> in Japan,<br />

have introduced an iron-enhancing ferritin gene to indica rice<br />

in such a way that it expresses itself in the rice endosperm.<br />

Thus, after polishing, the rice grains contain three times more<br />

iron than usual (Vasconcelos et al 2003). This is indeed the<br />

most significant increase in iron ever achieved in an indica<br />

rice variety and it could have important benefits for the 3.5<br />

billion people in the world who have iron-deficient diets.<br />

Second, <strong>IRRI</strong> is part of a forthcoming, multi-institutional<br />

publication that will detail the results of a 9-month human biological<br />

efficacy study of the consumption of iron-enriched rice<br />

(Studdert 2004). It involved 317 religious sisters from 10 convents<br />

in the Philippines. The results of this large feeding trial<br />

demonstrated that t<strong>here</strong> is indeed a significantly positive effect<br />

for women with iron-poor diets who consume biofortified<br />

rice. The high-iron rice, IR68144-3-3B-2-2-3, used in this ironuptake<br />

study is now a pre-release variety in the Philippines<br />

with the name Maligaya Special #13 (MS-13).<br />

acids that are essential to human health, especially the health<br />

of women and children. We believe the nutrient content of rice<br />

can be improved substantially by using both traditional plant<br />

breeding and new biotechnology approaches.<br />

<strong>IRRI</strong> is a major participant in the CGIAR Challenge Program<br />

called Harvest Plus (www.harvestplus.org), which is seeking<br />

to reduce the effects of micronutrient malnutrition by harnessing<br />

the power of plant breeding to develop staple food<br />

crops that are rich in micronutrients, a process called<br />

biofortification. <strong>IRRI</strong> has been active in research on enhancing<br />

micronutrient levels in rice through genetic engineering<br />

and leading the development at <strong>IRRI</strong> of tropical varieties of<br />

vitamin A-enriched golden rice (Datta et al 2003). It was only<br />

in early 2001 that the first seed samples were delivered to <strong>IRRI</strong><br />

by Professor Ingo Potrykus and Dr. Peter Beyer, the inventors<br />

of this genetically modified rice, which could save half a million<br />

children each year from irreversible blindness.<br />

Our team of scientists has bioengineered several Asian<br />

indica varieties with genes for beta-carotene biosynthesis. Selected<br />

lines—including genotypes of IR64—show expression<br />

of beta-carotene, the precursor of vitamin A (Datta et al 2003).<br />

These IR64 golden rice events are now being evaluated for<br />

agronomic performance. <strong>IRRI</strong> has shown that very little of the<br />

beta-carotene in the golden rice is lost during milling and cooking.<br />

T<strong>here</strong> is still a lot of work to do in this strategic research<br />

that involves bioavailability tests and working with national<br />

partners who will advance the leading materials following local<br />

biosafety regulations. Indica golden rice is still probably<br />

4–6 years away from release to farmers.<br />

<strong>Research</strong> consortia—the way of the future<br />

Significant progress in agricultural research—especially strategic<br />

research—cannot be accomplished in a vacuum. With<br />

today’s rapid accumulation of “mountains” of scientific data,<br />

how we conduct research is<br />

changing rapidly as well.<br />

Back in the 19th century, a<br />

genius such as Gregor<br />

Mendel—the Father of Genetics—could<br />

come up with<br />

brilliant and unprecedented<br />

theories of <strong>here</strong>dity in relative<br />

isolation while tending pea<br />

pod plants in his monastery<br />

garden. But today, researchers<br />

in our various public and<br />

private institutions—the geniuses<br />

of today—can rarely<br />

accomplish much in isolation—even<br />

in their sophisticated<br />

laboratories.<br />

The need for researchers to work together in collaboration<br />

to accomplish a goal is paramount—and the best mechanism<br />

we have seen for this is the concept of a consortium. A<br />

simple definition of “consortium” is a group of individuals or<br />

institutions/companies formed to undertake an enterprise or<br />

activity that would be beyond the capabilities of the individual<br />

members or difficult to perform effectively without partnership.<br />

<strong>International</strong> <strong>Rice</strong> Genome Sequencing Project<br />

The finest example of a consortium we can give is the <strong>International</strong><br />

<strong>Rice</strong> Genome Sequencing Project (http://<br />

Keynotes 33


gp.dna.affrc.go.jp/<br />

IRGSP/index.html), a<br />

leading member of which<br />

is the <strong>Rice</strong> Genome <strong>Research</strong><br />

Program (http://rgp.dna.affrc.go.jp), based right <strong>here</strong><br />

in Tsukuba. The IRGSP, a consortium of publicly funded laboratories<br />

in both developed and developing countries (Japan,<br />

USA, China, Taiwan-China, Korea, India, Thailand, France,<br />

Brazil, and the United Kingdom), was established in 1997 to<br />

obtain a high-quality, map-based sequence of the entire 12-<br />

chromosome rice genome using the cultivar Nipponbare of<br />

Oryza sativa subsp. japonica.<br />

Five years ahead of the original schedule, the IRGSP, in<br />

December 2002, announced the completion of a high-quality<br />

draft sequence of the genome (Feng et al 2002, Sasaki et al<br />

2002). This great achievement could not have been accomplished<br />

in any one country or region. The rice genome sequence,<br />

now freely available on the Internet (see http://<br />

rgp.dna.affrc.go.jp/cgi-bin/statusdb/irgsp-status.cgi) with data<br />

integrated from Monsanto and Syngenta, is already inducing<br />

innovative research worldwide in the new science of functional<br />

genomics. With 50,000 or more genes predicted in the DNA<br />

sequence, the task ahead requires the development of many<br />

genetic resources to unravel the function and interaction of<br />

these genes and their relationship with important traits.<br />

<strong>International</strong> <strong>Rice</strong> Functional Genomics Consortium<br />

Enter the <strong>International</strong> <strong>Rice</strong> Functional Genomics Consortium.<br />

Parallel to the initiation and activities of the IRGSP, <strong>IRRI</strong> recognized<br />

the need to bring together diverse expertise to capitalize<br />

on the wealth of genomic<br />

information for functional<br />

analysis. Informal<br />

meetings were held in 1999<br />

and 2000 that led to the formation<br />

of an <strong>International</strong><br />

<strong>Rice</strong> Functional Genomics<br />

Working Group. This Working<br />

Group brought together<br />

research groups from around<br />

the world to discuss mutual<br />

interests and promoted collaboration<br />

in anticipation of<br />

the completion of the rice<br />

genome sequence. During<br />

this time, members of this research<br />

community developed useful materials to form a base<br />

for collaboration in functional genomics studies in rice involving<br />

the genome sequence itself, gene cloning and arrays, and<br />

mutants (Phillips et al 2004).<br />

After two years of discussion, the idea of creating a more<br />

structured consortium was discussed at a Working Group meeting<br />

in Beijing in September 2002, and at the November 2002<br />

meeting in Canberra, Towards building a global rice gene<br />

machine (www.pi.csiro.au/grgm02/home1.htm), organized by<br />

the Commonwealth Scientific and Industrial <strong>Research</strong> Organization.<br />

An interim steering committee for the consortium was<br />

formed at the Plant and Animal Genome Conference in San<br />

Diego in January 2003, leading to the formal inauguration of<br />

the <strong>International</strong> <strong>Rice</strong> Functional Genomics Consortium<br />

(www.iris.irri.org/IRFGC).<br />

Currently, the <strong>IRRI</strong>-coordinated consortium is guided by<br />

a 21-member steering committee, which includes 17 institutions<br />

from 10 countries—including Japan—and two Future<br />

Harvest Centers—CIAT and <strong>IRRI</strong>. The collective goals are to<br />

share materials, integrate databases, seek bilateral and multilateral<br />

partnerships, implement initiatives for the cooperative<br />

elucidation of gene function, and accelerate delivery of research<br />

results to benefit rice production (Phillips et al 2004). Again,<br />

this is an effort that no one institution, country, or region could<br />

take on in isolation. For example, through the IRFGC, <strong>IRRI</strong> is<br />

investing its USAID Linkage Program funds to support eight<br />

laboratories in the United States to identify genes for stress<br />

tolerance (www.iris.irri.org/irfgc/researchstrength.shtml). This<br />

unique consortium embraces and encourages the role of developing<br />

countries in gene discovery and applications of the<br />

new science (Leung and An 2004). <strong>IRRI</strong> will continue to work<br />

closely with the international community to pursue initiatives<br />

that will accelerate gene discovery and take advantage of the<br />

new knowledge to make a true impact.<br />

To celebrate the completion of the rice genome and learn<br />

about the latest developments in functional as well as structural<br />

and evolutionary genomics research, IRFGC members<br />

will gather during the 2nd Annual Symposium on <strong>Rice</strong> Functional<br />

Genomics (www.rfg2004.org) later this month (15-17<br />

November) in Tucson, Arizona. We’re truly excited about what<br />

the consortium will be coming up with in the years to come.<br />

Other important rice-related consortia<br />

Within the CGIAR, <strong>IRRI</strong> has long taken the lead using the<br />

consortium concept to link research capacity of national agricultural<br />

research and extension systems (NARES) with that of<br />

<strong>IRRI</strong>’s to solve important problems through multi-country collaboration.<br />

We are using consortia to provide ways to conduct<br />

primarily strategic research by sharing research responsibilities<br />

according to each partner’s interests and capabilities. The<br />

key to success <strong>here</strong> is that we have, in consortia, truly peer<br />

relationships among NARES and with <strong>IRRI</strong> for much of the<br />

strategic research we mentioned earlier, with a substantial commitment<br />

of staff and resources. The special feature of collaboration<br />

in these consortia is that <strong>IRRI</strong> scientists put substantive<br />

components of their own strategic research at the consortia<br />

sites with NARES partners.<br />

Some key consortia we would like to mention briefly<br />

are the Irrigated <strong>Rice</strong> <strong>Research</strong> Consortium (IRRC), the new<br />

Consortium for Unfavorable <strong>Rice</strong> Environments (CURE), and<br />

the <strong>Rice</strong>-Wheat Consortium (RWC).<br />

IRRC (www.irri.org/irrc). Some 2.2 billion Asian rice<br />

farmers and consumers depend on the sustainable productivity<br />

of irrigated rice ecosystems. The IRRC, composed of<br />

NARES from Bangladesh, Cambodia, China, India, Indonesia,<br />

Lao PDR, Malaysia, the Philippines, Thailand, and Viet-<br />

34 <strong>Rice</strong> is life: scientific perspectives for the 21st century


nam, is working with <strong>IRRI</strong> to promote research collaboration<br />

and integration of research, strengthen multi-institutional and<br />

interdisciplinary research, and facilitate technology delivery.<br />

Farmers’ knowledge and input are key ingredients as we illustrated<br />

earlier with the example of the ongoing weed research<br />

to close the yield gap in Bangladesh (www.irri.org/irrc/weeds/<br />

closing.asp).<br />

CURE. Some of the greatest challenges facing rice researchers<br />

are found in the fragile rainfed and marginal environments<br />

w<strong>here</strong> few of the modern technologies targeted to<br />

high productivity through high levels of inputs are appropriate.<br />

To make rice research more relevant under rainfed conditions,<br />

it is necessary to conduct the research on-site in a wide<br />

range of environments that present specific constraints to production.<br />

Since 1991, <strong>IRRI</strong> had worked in partnership with<br />

NARES to conduct rice research in these unfavorable environments<br />

through two research consortia—one for the rainfed<br />

lowlands and one for the uplands.<br />

A review in 2001 indicated that the consortium approach<br />

had notable successes in developing new technologies more<br />

suited to these environments. However, we decided to restructure<br />

the two consortia to consolidate the research programs<br />

and focus on increasing impact through wider dissemination<br />

of the research findings—hence, the June 2002 birth of CURE,<br />

the streamlined Consortium for Unfavorable <strong>Rice</strong> Environments<br />

(www.irri.org/cure/cure.htm). Consortium members—<br />

Asian NARES in Bangladesh, Cambodia, India, Indonesia,<br />

Laos, Myanmar, Nepal, the Philippines, Thailand, and Vietnam;<br />

advanced research institutes; and other international agricultural<br />

research centers—have adopted a holistic and systems<br />

approach to achieve a higher degree of integration of the<br />

disciplines in identifying and addressing problems relating to<br />

Keynotes 35


agricultural production and rural livelihoods involving—but<br />

not necessarily confined to—rice. We are confident that the<br />

new consortium will serve as a platform and forum for identifying<br />

and prioritizing the rainfed research needed to generate<br />

impact in farmers’ fields.<br />

RWC. Bangladesh, India, Nepal, and Pakistan have devoted<br />

to agriculture nearly half of their total land area of 402<br />

million hectares to feed and provide livelihoods for 1.8 billion<br />

people. <strong>Rice</strong> and wheat, the staple food crops for these people,<br />

contribute more than 80% of the total cereal production in these<br />

countries.<br />

Celebrating its 10th anniversary this year, the <strong>Rice</strong>-Wheat<br />

Consortium (www.rwc.cgiar.org/rwc), a NARES-driven initiative<br />

of the four countries, has truly emerged as an innovative<br />

model for regional and international collaboration. Operating<br />

as an inter-institutional and intercenter multidisciplinary network<br />

facilitating system-based farmer participatory research<br />

in the rice-wheat ecology of the Indo-Gangetic Plains, it has<br />

successfully addressed the issues of productivity enhancement<br />

of rice and wheat in a sustainable fashion. These issues include<br />

tillage and crop establishment, crop diversification,<br />

postharvest, and environmental benefits. Through the RWC’s<br />

efforts, tens of thousands of resource-poor farmers in South<br />

Asia have been able to increase their income by using practices<br />

that save water, fuel, and other inputs; facilitate timely<br />

planting; reduce tillage needs and crop residue burning; and<br />

allow them to diversify their cropping systems (Ladha et al<br />

2003).<br />

Last year, external reviewers pointed out that “the effectiveness<br />

of partnership among <strong>IRRI</strong> and CIMMYT and their<br />

NARES partners as well as within and between the four national<br />

systems is one of the most important achievements of<br />

the RWC”—and truly this is what consortia are all about and<br />

why they have the potential to achieve so much.<br />

Summary and conclusions<br />

We are happy to have been able to keynote this scientific meeting<br />

of the WRRC—this culminating conference of the <strong>International</strong><br />

Year of <strong>Rice</strong>—to suggest what the strategy should be<br />

for rice research in the 21st century. As we have just outlined,<br />

we feel that strategy must include<br />

Renewing and invigorating efforts to close the yield<br />

gap in rice;<br />

Remembering the critical importance of maintenance<br />

research;<br />

Using cutting-edge tools to enhance strategic thrusts<br />

to (1) break the yield barrier, (2) face head-on the<br />

crises of impending global warming and water shortages,<br />

and (3) improve human nutrition; and<br />

<br />

Employing the consortium model whenever and w<strong>here</strong>ver<br />

possible for researchers to work together to accomplish<br />

the important goals we just discussed.<br />

If you remember anything of what we’ve discussed today,<br />

we hope it is that, for any agricultural research institution<br />

to be successful, it must have a harmonious mix of maintenance<br />

research and strategic research on its agenda. T<strong>here</strong> really<br />

can’t be one without the other in the long term. The dual<br />

challenges are producing new products to solve future problems<br />

caused by diminishing resources and climate change and<br />

maintaining and securing what we have already achieved.<br />

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Notes<br />

Authors’ address: <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong> (<strong>IRRI</strong>), Los<br />

Baños, Laguna, Philippines.<br />

Keynotes 37


SESSION 1<br />

The genus Oryza, its diversity,<br />

and its evolution<br />

CONVENER: R. Okuno (NIAS)<br />

CO-CONVENER: R. Sackville Hamilton (<strong>IRRI</strong>)


Molecular phylogeny and divergence of the rice tribe<br />

Oryzeae, with special reference to the origin<br />

of the genus Oryza<br />

Song Ge, Ya-long Guo, and Qi-hui Zhu<br />

The rice tribe Oryzeae consists of 12 genera and more than 70<br />

species distributed in tropical and temperate regions worldwide<br />

(Tzvelev 1989, Vaughan 1994). Species in the genus<br />

Oryza and other genera closely related to Oryza have been<br />

extensively studied either because of their agronomically useful<br />

traits in rice genetic improvement (wild species in Oryza<br />

and Porteresia) or because of their economic value as part of<br />

cuisine (Zizania) and forage (Leersia) (Vaughan and Morishima<br />

2003). However, phylogenetic relationships among genera in<br />

this tribe have not been well studied, and the circumscription<br />

and taxonomic position of some genera have remained controversial<br />

for decades. In addition, the origin and diversification<br />

of this tribe, in particular the origin of the genus Oryza<br />

and its divergence, remain largely unclear. Recently, sequences<br />

of low-copy nuclear genes have been successfully used for<br />

addressing phylogenetic questions and, in combination with<br />

chloroplast DNA fragments, have provided especially powerful<br />

markers in terms of phylogenetic reconstruction and biogeographic<br />

inference (Sang 2002).<br />

The alcohol dehydrogenase (Adh) gene is the most widely<br />

used low-copy nuclear gene, w<strong>here</strong>as the chloroplast matK<br />

gene, trnL intron, and trnL-trnF spacer, as well as mitochondrial<br />

nad1 intron, are widely used in phylogenetic studies.<br />

Nuclear GPA1 that encodes a G protein α subunit is also a<br />

source of choice because it is a single copy in higher plants<br />

and well characterized in function and structure. To better understand<br />

the evolutionary and biogeographic history of the rice<br />

tribe, we sequenced two chloroplast (matK and trnL-trnF) fragments<br />

and one mitochondrial (nad1 intron) fragment and portions<br />

of two nuclear genes (Adh2 and GPA1) from 35 species<br />

representing 12 genera in the tribe, as well as Ehrharta and<br />

Phyllostachys (subfamily Bambusoideae) as the outgroups. In<br />

addition, to clarify the phylogenetic relationship among the A-<br />

genome species, which include cultivated rice (O. sativa), we<br />

have chosen to sequence introns of three anonymous nuclear<br />

single-copy genes (OsRFCD001283, OsRFCD017357, and<br />

OsRFCD009971 on chromosomes 1, 4, and 2, respectively)<br />

that evolve much faster than commonly used ITS and cpDNA<br />

fragments. Based on sequences of these introns, we reconstructed<br />

the phylogeny and dated the origin and divergence of<br />

the A-genome species.<br />

Molecular phylogeny based on multiple sequences<br />

from three genomes<br />

Phylogenetic analyses of the aligned sequences of the above<br />

fragments from three genomes were conducted using maxi-<br />

mum parsimony (MP), neighbor-joining (NJ), and Bayesian<br />

(BI) approaches. A comparison of the phylogenies inferred<br />

from two nuclear genes shows that they are largely congruent,<br />

with only one area of disagreement involving the placement of<br />

the monotypic genus Hygroryza (see below). The partitionhomogeneity<br />

test (PHT) indicated that two data sets (Adh2<br />

and GPA1) were statistically incongruent (P


2<br />

Oryza sativa<br />

O. glaberrima<br />

O. meridionalis<br />

O. punctata<br />

5<br />

O. officinalis<br />

O. rhizomatis<br />

O. australiensis<br />

8<br />

*Porteresia coarctata-7<br />

*P. coarctata-4<br />

O. brachyantha<br />

O. granulata<br />

14<br />

Leersia oryzoides-1<br />

L. perrieri-2<br />

L. hexandra-2<br />

L. perrieri-6<br />

L. hexandra-3<br />

L. oryzoides-4<br />

L. tisserantti<br />

20<br />

*Hygroryza aristata-Adh2<br />

*Prosphytochloa<br />

*Potamophila parviflora<br />

Chikusichloa aquatica<br />

*Rhynchoryza<br />

35<br />

–10 changes<br />

Zizania aquatica<br />

Z. latifolia<br />

Zizaniopsis villanensis<br />

Luziola leiocarpa<br />

L. fluitans<br />

*Hygroryza aristata-GPA1<br />

Ehrharta erecta<br />

Phyllostachys aurea<br />

Fig. 1. Strict consensus tree of the rice<br />

tribe Oryzeae generated from the combined<br />

Adh2 and GPA1 sequences. The<br />

thick lines indicate the nodes with the<br />

bootstrap support and Bayesian posterior<br />

probability over 95%, while the<br />

thin lines indicate the nodes with the<br />

bootstrap support and Bayesian posterior<br />

probability from 75% to 94%. The<br />

numbers on the node represent divergence<br />

times (approximate) in million<br />

years ago (MYA) as estimated by molecular<br />

clock approaches. Broken<br />

lines indicate the placement of<br />

Hygroryza on Adh2 and GPA1 trees, respectively.<br />

The numbers following the<br />

species name represent the clone sequenced.<br />

The asterisks indicate the<br />

monotypic genera.<br />

Session 1: The genus Oryza, its diversity, and its evolution 41


just “spurious” insufficient data or some other unknown artifact<br />

is unclear and needs to be further explored.<br />

Divergence of the rice tribe and the origin of Oryza<br />

Although the phylogeny and divergence time of Poaceae have<br />

been revealed by molecular approaches and estimated based<br />

on fossil evidence (GPWG 2001, Gaut 2002), little in the fossil<br />

record reflects upon the origin or diversification of the genus<br />

Oryza. A few studies have been made to estimate the divergence<br />

time of Oryza and its related genera (Second 1991,<br />

Vaughan and Morishima 2003). However, estimation of the<br />

possible dates of divergent events related to the evolution of<br />

Oryza was largely based on isozyme studies (Second 1991)<br />

and many contradictions exist regarding the divergence event<br />

proposed (see Vaughan and Morishima 2003). Despite several<br />

limitations to the use of clock-based sequence data (Gaut 2002),<br />

they are useful for estimating divergence time when the clock<br />

can be calibrated with some confidence, in particular when<br />

fossil evidence is not available or is inadequate.<br />

To test the molecular clock hypothesis in Oryzeae, we<br />

performed relative rate tests for all the data sets. Results show<br />

that no rate heterogeneity exists at synonymous sites for both<br />

Adh2 and matK data sets and so the molecular clock hypothesis<br />

cannot be rejected for the synonymous evolution at both<br />

loci. Using the synonymous molecular clocks of matK and Adh2<br />

and assuming that maize and rice diverged 50 million years<br />

ago (MYA) (Gaut 2002), we calculated approximate divergence<br />

times for various lineages within the tribe and within<br />

Oryza (Fig. 1). The estimates suggest that the rice tribe originated<br />

roughly 35 MYA, during approximately the transition<br />

from the Eocene to the Oligocene. Within the tribe, Oryza and<br />

Leersia separated from the rest of the tribe approximately 20<br />

MYA, and from each other 14 MYA. Within Oryza, the age of<br />

the deepest split between the most basal G genome and remaining<br />

genomes was estimated at about 8 MYA.<br />

Phylogeny, origin, and divergence<br />

of A-genome species in Oryza<br />

Evidence showed that the A-genome group that consists of eight<br />

diploid species is one of the most recently diverged lineages<br />

within the genus Oryza (Ge et al 2001). Their evolutionary<br />

relationships have long been controversial and are still not well<br />

studied at the sequence level. This is mainly because the commonly<br />

used sequences such as ITS and cpDNA fragments lack<br />

sufficient resolution in groups that have undergone rapid or<br />

recent radiations. Accordingly, we sequenced introns of three<br />

nuclear genes located on different chromosomes from multiple<br />

accessions of eight A-genome species. As expected, the<br />

intron sequences provide much higher (more than two times<br />

higher) informative characters than those of ITS (data not<br />

shown). Phylogenetic relationships and divergence times of<br />

the main lineages of the A-genome species were inferred based<br />

on these intron sequences using the similar approaches mentioned<br />

above. Figure 2 presents a phylogeny and divergence<br />

times among eight species, along with the B- (O. punctata)<br />

and E-genome (O. australiensis) species as the outgroups. All<br />

the species except O. rufipogon and O. nivara form a monophyletic<br />

group and the Australian endemic O. meridionalis is<br />

the earliest divergent lineage. However, accessions from O.<br />

rufipogon and O. nivara entirely mix together, supporting previous<br />

opinion that the two species should be treated as a single<br />

one. Moreover, two ecogeographic races of O. sativa (indica<br />

and japonica) form monophyletic groups along with some O.<br />

rufipogon and O. nivara accessions.<br />

Sequence divergence is low in all pair-wise comparisons<br />

among A-genome species, suggesting that the group radiated<br />

relatively recently. Using the similar molecular clock approaches<br />

mentioned above, we estimate that the A-genome<br />

species began to diverge roughly 2 MYA. The Asian cultivated<br />

rice (O. sativa) diverged from the African cultivated rice (O.<br />

glaberrima) at about 0.6 MYA, w<strong>here</strong>as two races of O. sativa<br />

(indica and japonica) separated approximately 0.4 MYA<br />

(Fig. 2).<br />

To put the divergence of the rice tribe and rice genus<br />

into a temporal framework raises an interesting question: How<br />

can the present distribution patterns in the rice tribe be reconciled<br />

with the apparent pantropical distribution for the tribe<br />

and many genera such as Oryza and Leersia In particular,<br />

many closely related species (e.g., the A-genome species) are<br />

currently geographically isolated from one another by thousands<br />

of kilometers of open ocean. This implies that oceanic<br />

dispersal would contribute to the evolution and divergence of<br />

the genus Oryza and its tribe.<br />

References<br />

Gaut BS. 2002. Evolutionary dynamics of grass genomes. New Phytol.<br />

154:15-28.<br />

Ge S, Li A, Lu BR, Zhang SZ, Hong DY. 2002. A phylogeny of the<br />

rice tribe Oryzeae (Poaceae) based on matK sequence data.<br />

Am. J. Bot. 89:1967-1972.<br />

Ge S, Sang T, Lu BR, Hong DY. 2001. Phylogeny of the genus Oryza<br />

as revealed by molecular approaches. In: Khush GS, Brar DS,<br />

Hardy B, editors. <strong>Rice</strong> genetics IV. Enfield, N.H. (USA): Science<br />

Publishers, Inc. and Los Baños (Philippines): <strong>International</strong><br />

<strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>. p 89-105.<br />

GPWG (Grass Phylogeny Wording Group). 2001. Phylogeny and<br />

subfamilial classification of the grasses (Poaceae). Ann. Missouri<br />

Bot. Garden 88:373-457.<br />

Pyrah GL. 1969. Taxonomic and distributional studies in Leersia<br />

(Gramineae). Iowa State J. Sci. 44:215-270.<br />

Sang T. 2002. Utility of low-copy nuclear gene sequences in plant<br />

phylogenetics. Crit. Rev. Biochem. Mol. Biol. 37:121-147.<br />

Second G. 1991. Molecular markers in rice systematics and the evaluation<br />

of genetic resources. In: Bajaj YPS, editor. <strong>Rice</strong> biotechnology<br />

in agriculture and forestry. Vol. 14. Berlin (Germany):<br />

Springer-Verlag. p 468-494.<br />

Tzvelev NN. 1989. The system of grasses (Poaceae) and their evolution.<br />

Bot. Rev. 55:141-204.<br />

42 <strong>Rice</strong> is life: scientific perspectives for the 21st century


indica<br />

+<br />

rufipogon<br />

+<br />

nivara<br />

0.4<br />

0.6<br />

japonica<br />

+<br />

rufipogon<br />

+<br />

nivara<br />

glumaepatula<br />

glaberrima<br />

+<br />

barthii<br />

2.0<br />

longistaminata<br />

meridionalis<br />

–5 changes<br />

punctata<br />

australiensis<br />

Fig. 2. Strict consensus tree of the A-genome species in Oryza generated from the<br />

combined intron sequences of three nuclear genes. The thick lines indicate the nodes<br />

with the bootstrap support and Bayesian posterior probability over 95%, while the thin<br />

lines indicate the nodes with the bootstrap support and Bayesian posterior probability<br />

from 75% to 94%. The numbers on the node represent divergence times in million<br />

years ago (MYA) as estimated by molecular clock approaches. Accessions were omitted<br />

from the figures.<br />

Session 1: The genus Oryza, its diversity, and its evolution 43


Vaughan DA, Morishima H. 2003. Biosystematics of the genus Oryza.<br />

In: Smith W, editor. <strong>Rice</strong>: origin, history, technology, and production.<br />

New York, N.Y. (USA): John Wiley & Sons, Inc. p<br />

27-65.<br />

Vaughan DA. 1994. The wild relatives of rice: a genetic resources<br />

handbook. Manila (Philippines): <strong>International</strong> <strong>Rice</strong> <strong>Research</strong><br />

<strong>Institute</strong>.<br />

Eco-genetic diversification in the genus Oryza:<br />

implications for sustainable rice production<br />

Duncan Vaughan, Koh-ichi Kadowaki, Akito Kaga, and Norihiko Tomooka<br />

Notes<br />

Authors’ address: Laboratory of Systematic and Evolutionary Botany,<br />

<strong>Institute</strong> of Botany, Chinese Academy of Sciences, Beijing<br />

100093, China, e-mail: gesong@ibcas.ac.cn.<br />

Acknowledgments: We thank Tao Sang of Michigan State University<br />

(East Lansing, Mich., USA) and Bao-rong Lu of Fudan University<br />

(Shanghai, China) for their encouragement and assistance.<br />

We are also grateful to the <strong>International</strong> <strong>Rice</strong> Genebank<br />

at <strong>IRRI</strong> (Los Baños, Philippines) for providing seed samples.<br />

This study was supported by the Chinese Academy of Sciences<br />

(Kscxz-sw-101A), the National Natural Science Foundation<br />

of China (30025005), and the Program for Key <strong>International</strong><br />

S & T Cooperation Project of China (2001CB711103).<br />

<strong>Rice</strong> is a component of some remarkably productive and sustainable<br />

farming systems. However, many factors threaten sustainable<br />

rice farming, such as economic development leading<br />

to labor, land, and freshwater constraints to rice-farming systems.<br />

In addition, abiotic stresses, including the consequences<br />

of climate change, and ever-changing biotic stresses require<br />

diverse approaches to maintain and improve rice yields. In this<br />

paper, the contributions that diversity in the gene pools of rice<br />

can make to rice improvement are considered.<br />

Primary gene pool<br />

Since Oryza species having the AA genome can hybridize naturally<br />

with one another, they can all be considered part of the<br />

primary gene pool of rice. AA-genome Oryza species have<br />

astonishing eco-genetic diversification in relation to environments<br />

with different hydrological regimes. During domestication,<br />

particular ecotypes of wild rice were selected for increased<br />

yield. Subsequently, because of selection and accompanying<br />

human migrations, diversification of the cultivated rice gene<br />

pool extended the climatic and geographic range of rice to<br />

areas w<strong>here</strong> its wild relatives do not grow (Vaughan et al<br />

2004a,b). The wild relatives of rice in this gene pool have been<br />

the main source of useful genes for rice improvement from<br />

wild Oryza. Recent examples of the use of the wild species in<br />

this gene pool are given below.<br />

Abiotic stress resistance in O. rufipogon<br />

from the Mekong Delta<br />

In December 1990, a collaborative collecting mission for the<br />

wild relatives of rice was undertaken by the Vietnam Agricultural<br />

Sciences <strong>Institute</strong> and the <strong>International</strong> <strong>Rice</strong> <strong>Research</strong><br />

<strong>Institute</strong> (<strong>IRRI</strong>) in the Mekong Delta. During that mission, areas<br />

of adverse soils w<strong>here</strong> the wild rice O. rufipogon Griff.<br />

grows were targeted for collection. Many samples of O.<br />

rufipogon were collected from different parts of the Mekong<br />

Delta, including Phup Hiep and Thap Muoi districts, w<strong>here</strong><br />

the soils were bright red and known to be highly acid sulfate.<br />

Passport data of the collections reported this. Consequently,<br />

germplasm from these locations could be rapidly evaluated in<br />

standardized conditions to determine the type and degree of<br />

abiotic stress resistance it had. Three accessions (106412,<br />

106423, and 106424) 1 were found to be useful sources of resistance<br />

to aluminum toxicity. One accession (106424) was<br />

crossed to rice (cv. IR64) and recombinant inbred lines developed<br />

from this cross were analyzed. Using root length to evaluate<br />

the response to stress, five QTLs from O. rufipogon were<br />

found that explained aluminum tolerance and these were<br />

mapped to rice chromosomes 1, 3, 7, 8, and 9 (Nyugen et al<br />

2003). Since this accession (106424) has useful traits and is<br />

being used in rice improvement programs, it is one of the accessions<br />

chosen for analysis by the Oryza Map Alignment<br />

Project (www.genome.arizona.edu/BAC_special_projects/).<br />

Biotic stress resistance in O. rufipogon<br />

from the Central Plains of Thailand<br />

Tungro is the most serious virus disease of rice in South and<br />

Southeast Asia (Azzam and Chancellor 2002). Sources of resistance<br />

to tungro viruses are found in cultivated rice but some<br />

of these have broken down as new forms of these viruses have<br />

emerged. Generally, field collection notes cannot help guide<br />

1 Accession numbers mentioned are materials in the <strong>International</strong> <strong>Rice</strong><br />

Genebank at <strong>IRRI</strong> and refer to germplasm collected directly by the first author<br />

with collaborating colleagues in national programs while a staff member<br />

at <strong>IRRI</strong>.<br />

44 <strong>Rice</strong> is life: scientific perspectives for the 21st century


evaluators in relation to biotic stress tolerance because biotic<br />

stresses are transient and do not affect germplasm in the field<br />

uniformly. T<strong>here</strong>fore, a logical approach to evaluation is the<br />

core collection approach. To find new sources of tungro resistance<br />

for use in rice breeding, a wild Oryza core collection<br />

was evaluated (Kobayashi et al 1997, Vaughan and Jackson<br />

1995). A few accessions of O. rufipogon from Thailand<br />

(105908, 105909, and 105910) collected by boat in a deeply<br />

flooded area 68 km north of Bangkok were tolerant of both<br />

the spherical and bacilliform virus types that constitute tungro<br />

(Kobayashi et al 1997). These O. rufipogon accessions tolerant<br />

of tungro were used to transfer tungro tolerance to advanced<br />

breeding lines (Brar and Khush 2003) and one variety, called<br />

Matatag 9, was released in the Philippines with tungro tolerance<br />

from accession 105908.<br />

These two examples of germplasm collected, evaluated,<br />

and used in rice improvement and basic research reinforce the<br />

importance of the wild relatives of rice for rice improvement.<br />

However, these examples also illustrate the potential problem<br />

associated with the loss of wild Oryza genetic resources in<br />

situ. The Mekong Delta and Central Plains of Thailand are<br />

developing rapidly and the extinction of populations of wild<br />

rice has been recorded in various parts of Southeast Asia<br />

(Akimoto et al 1999, Kuroda et al 2004). T<strong>here</strong>fore, the chance<br />

for evolutionary change in natural wild rice populations to<br />

enable adaptation to changing biotic and abiotic stresses, such<br />

as climate change, is diminished.<br />

Secondary and tertiary gene pools of rice<br />

It is debatable whether rice has a secondary gene pool since<br />

making crosses between rice and species with other genomes<br />

is very difficult and leads to rapid chromosome elimination in<br />

subsequent generations. However, in Thailand and Costa Rica,<br />

hybrid populations between AA-genome Oryza species and<br />

species having other genomes have been reported and these<br />

populations are reported to be vigorous but sterile. The secondary/tertiary<br />

gene pools of rice can be considered to be composed<br />

of Oryza species with genomes other than the AA genome.<br />

Eco-genetic diversification in non-AA-genome Oryza<br />

species reveals different types of environmental adaptation not<br />

found among AA-genome species. Shade tolerance is a feature<br />

of species with the CC, BBCC, GG, and HHJJ genomes.<br />

Among the three diploid CC-genome species (O. eichingeri<br />

Peter, O. officinalis Wall ex Watt, and O. rhizomatis Vaughan),<br />

t<strong>here</strong> is diversification in relation to the degree of sun their<br />

habitats receive. O. eichingeri is a forest-dwelling species. O.<br />

rhizomatis is adapted to open hot and dry areas in Sri Lanka.<br />

O. officinalis has wide ecological adaptation but is usually<br />

found in open habitats and areas with higher precipitation than<br />

O. rhizomatis. GG diploid species (O. granulata complex) tend<br />

to be confined to upland forested habitats with pronounced<br />

wet and dry seasons. In contrast, the HHJJ-genome species<br />

(O. ridleyi complex) tend to be abundant in wet tropical lowland<br />

forests (Vaughan 2003). T<strong>here</strong> has yet to be a comprehensive<br />

analysis of the photosynthetic and drought-tolerance<br />

systems of Oryza species not having the AA genome. Given<br />

the diverse eco-edaphic habitats of Oryza species, they likely<br />

contain much useful variation in a range of ecological traits.<br />

Beyond Oryza in the tribe Oryzeae<br />

The genus Oryza belongs to a small group of genera in the<br />

tribe Oryzeae in the subfamily Bambusoideae of the Poaceae<br />

(Graminae). The related genera have several characteristics<br />

that are not found in the genus Oryza. Among these, two are<br />

worthy of special mention because of their potential use in<br />

rice improvement.<br />

Separation of male and female florets: Zizania<br />

Several genera in the tribe Oryzeae have unisexual spikelets—<br />

Luziola, Zizania, and Zizaniopsis. In the case of Luziola, staminate<br />

and pistillate spikelets are usually on separate panicles.<br />

In Zizania and Zizaniopsis, they are both on the same panicle.<br />

Of these three genera, Zizania has been the best studied because<br />

of its economic importance in Asia (w<strong>here</strong> Zizania<br />

latifolia [Griseb.] Turcz. ex Stapf is a vegetable) and in North<br />

America (w<strong>here</strong> Zizania palustris Linn., “wild rice,” is a gourmet<br />

food). The genome map of Zizania palustris has been compared<br />

with that of rice (Kennard et al 1999, Hass et al 2003).<br />

This has revealed that the 15 haploid chromosomes of Zizania<br />

represent the 12 haploid chromosomes of Oryza, with duplication<br />

of chromosomes 1, 4, and 9. However, these studies<br />

have not been revealing regarding the genetic control of pistillate<br />

and staminate spikelets. Using protoplast fusion, Chinese<br />

researchers have succeeded in producing two somatic hybrids<br />

between rice and Z. latifolia (Liu et al 1999). These intergeneric<br />

hybrids had Z. latifolia fragments in the rice genome.<br />

Improvement in protoplast culture and fusion conditions may<br />

enable abundant and potentially useful somatic hybrids to be<br />

developed.<br />

Adaptation to saline conditions: Porteresia<br />

In the saline tracts at the mouth of the Ganges Delta, wild<br />

grasses are sometimes harvested for food. Myriostachya<br />

wightiana Hook., locally called Dhanshi, and Porteresia<br />

coarctata (Roxb.) Tateoka, locally called Uri-dhan, are two of<br />

these salt-tolerant grasses that are gat<strong>here</strong>d. Porteresia<br />

coarctata is in the tribe Oryzeae and, because it is the most<br />

salt-tolerant relative of rice, it has been subject to much research<br />

attention. Porteresia is a monospecific genus that exhibits<br />

several unique morphological and anatomical features<br />

of the embryo and leaf (Balakrishna 2003). Porteresia<br />

coarctata has salt hairs on the leaves through which salt is<br />

secreted (Flowers et al 1990). Success has been reported in<br />

crossing Porteresia with rice (Jena 1994, Brar et al 1997) but<br />

transfer of the complex structural mechanism by which<br />

Porteresia has adapted to living in saline conditions has yet to<br />

be achieved.<br />

Session 1: The genus Oryza, its diversity, and its evolution 45


Conclusions<br />

The primary gene pool of rice, AA-genome Oryza species, offers<br />

gene sources from regions to which rice is adapted. The<br />

secondary and tertiary gene pools of rice, consisting of the<br />

other Oryza species, provide gene sources that include adaptation<br />

to areas to which rice is not adapted, such as forest shade.<br />

Beyond the genus Oryza in the tribe Oryzeae, gene sources for<br />

major morphological and structural change such as panicle<br />

structure or leaf anatomy can be found. Global and regional<br />

environmental changes suggest that, in the future, germplasm<br />

naturally exposed and evolving in response to these changes<br />

may be an essential source of genes to address these changes.<br />

Hence, t<strong>here</strong> is a need for innovative approaches to in situ<br />

conservation of rice genetic resources to complement ex situ<br />

conservation efforts.<br />

References<br />

Akimoto M, Shimamoto Y, Morishima H. 1999. The extinction of<br />

genetic resources of Asian wild rice, Oryza rufipogon Griff.:<br />

a case study in Thailand. Genet. Resour. Crop Evol. 46:419-<br />

425.<br />

Azzam O, Chancellor TCB. 2001. The biology, epidemiology, and<br />

management of rice tungro disease in Asia. Plant Dis. 86:88-<br />

100.<br />

Balakrishna P. 2003. Porteresia coarctata: scope and limitations of<br />

utilization in rice improvement. In: Nanda JS, Sharma SD,<br />

editors. Monograph on the genus Oryza. Enfield, N.H. (USA):<br />

Science Publishers, Inc. p 359-373.<br />

Brar DS, Elloran R, Talag JD, Abbasi F, Khush GS. 1997. Cytogenetic<br />

and molecular characterization of an intergenic hybrid<br />

between Oryza sativa L. and Porteresia coarctata (Roxb.)<br />

Tateoka. <strong>Rice</strong> Genet. Newsl. 14:43-44.<br />

Brar DS, Khush GS. 2003. Utilization of wild species of genus Oryza<br />

in rice improvement. In: Nanda JS, Sharma SD, editors. Monograph<br />

on the genus Oryza. Enfield, N.H. (USA): Science Publishers,<br />

Inc. p 283-309.<br />

Flowers TJ, Flowers SA, Hajibagheri MA. 1990. Salt tolerance in<br />

the halophytic wild rice, Porteresia coarctata Tateoka. New<br />

Phytol. 114:675-684.<br />

Hass BL, Pires JC, Porter R, Phillips RL, Jackson SA. 2003. Comparative<br />

genetics at the gene and chromosome levels between<br />

rice (Oryza sativa) and wild rice (Zizania palustris). Theor.<br />

Appl. Genet. 107:773-782.<br />

Jena KK. 1994. Develoment of intergeneric hybrid between O. sativa<br />

and Porteresia coarctata. <strong>Rice</strong> Genet. Newsl. 11:78-79.<br />

Kennard W, Phillips R, Porter R, Grombacher A. 1999. A comparative<br />

map of wild rice (Zizania palustris L. 2n=2x=30). Theor.<br />

Appl. Genet. 99:793-799.<br />

Kobayashi N, Ikeda R, Vaughan DA, Imbe T. 1997. New gene sources<br />

for tungro resistance in wild species of rice (Oryza spp.). In:<br />

Chancellor TCB, Thresh JM, editors. Epidemiology and management<br />

of rice tungro disease. Chatham (UK): Natural Resources<br />

<strong>Institute</strong>. p 60-68.<br />

Kuroda Y, Appa Rao S, Bounphanousay C, Kongphanh K, Iwata A,<br />

Tanaka K, Sato YI. 2004. Diversity of wild and weedy rice in<br />

the Lao PDR. In: Schiller JM, Chanphengxay M, Linquist B,<br />

Appa Rao S, editors. <strong>Rice</strong> in Laos. (In press.)<br />

Liu B, Liu ZL, Li XW. 1999. Production of a highly asymmetric<br />

somatic hybrid between rice and Zizania latifolia (Griseb.):<br />

evidence for inter-genomic exchange. Theor. Appl. Genet.<br />

98:1099-1103.<br />

Nguyen BD, Brar DS, Bui BC, Nguyen TV, Pham LN, Nguyen HT.<br />

2003. Identification and mapping of the QTL for aluminium<br />

tolerance introgressed from the new source, Oryza rufipogon<br />

Griff., into indica rice (Oryza sativa L.). Theor. Appl. Genet.<br />

106:583-593.<br />

Vaughan DA. 2003. Genepools in the genus Oryza. In: Nanda JS,<br />

Sharma SD, editors. Monograph on the genus Oryza. Enfield,<br />

N.H. (USA): Science Publishers, Inc. p 113-138.<br />

Vaughan DA, Jackson MT. 1995. Core collections as a guide to the<br />

whole collection. In: Hodgkin T, Brown AHD, van Hintum<br />

ThJL, Morales EAV, editors. Core collections of plant genetic<br />

resources. Chichester (UK): Wiley and Sons. p 229-239.<br />

Vaughan DA, Miyzaki S, Miyashita K. 2004a. The rice genepool<br />

and human migrations. In: Werner D, editor. Biological resources<br />

and migration. Berlin (Germany): Springer. p 1-13.<br />

Vaughan DA, Sanchez, Ushiki J, Kaga A, Tomooka N. 2004b. Asian<br />

rice and weedy rice: evolutionary perspectives. In: Gressel J,<br />

editor. Crop ferality and volunteerism. Boca Raton, Fla.<br />

(USA): CRC Press. (In press.)<br />

Notes<br />

Authors’ address: National <strong>Institute</strong> of Agrobiological Sciences,<br />

Tsukuba, Japan, e-mail: duncan@affrc.go.jp.<br />

46 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Toward a global strategy for the conservation<br />

of rice genetic resources<br />

Ruaraidh Sackville Hamilton and Ruth Raymond<br />

Twenty-two species of wild rice of the genus Oryza occur as<br />

natives in 81 countries, in all tropical and subtropical regions<br />

of the world. <strong>Rice</strong> is believed to have been first cultivated<br />

around 6,000 to 14,000 years ago, with probably at least two<br />

independent domestication events of O. sativa (with separate<br />

events for indica and japonica rice) in Asia and a third of O.<br />

glaberrima in Africa. <strong>Rice</strong> is now cultivated in 114 countries,<br />

also in all tropical and subtropical regions, with distinctive<br />

forms occurring in different parts of Asia, Africa, Europe, and<br />

Oceania.<br />

The genetic diversity encompassed by the genus is remarkable.<br />

More than 400,000 accessions are conserved ex situ<br />

in genebanks. The task of efficiently conserving and using all<br />

this diversity is formidable, and requires a globally integrated,<br />

multinational effort. Yet, rice genebanks are working largely<br />

independently and ignorant of the achievements of sister<br />

genebanks. The resulting scientific and economic inefficiency,<br />

with uncontrolled duplication and ineffective targeting of conservation<br />

and use, is clear.<br />

In this paper, we present the first steps toward a plan to<br />

rectify the situation, through development of a global strategy<br />

for the efficient conservation and use of rice diversity. We begin<br />

by describing the new Global Crop Diversity Trust, through<br />

which it has become possible to consider an efficient global<br />

strategy. We then consider the required elements of the strategy,<br />

and the process toward implementation of those steps.<br />

The Global Crop Diversity Trust<br />

The Global Crop Diversity Trust (www.startwithaseed.org) has<br />

been set up to establish and support a rational, efficient, and<br />

sustainable global system for the conservation of crop diversity.<br />

In the short term, it will assist in the development of rational<br />

and efficient systems, by providing both expert technical<br />

support and financial support. It will fund the upgrading of<br />

selected national and regional genebanks and the establishment<br />

of infrastructure for coordination. In the longer term, it<br />

seeks to provide a permanent source of funding for the maintenance<br />

of crop diversity collections around the world.<br />

It is developing the global system through two complementary<br />

strategies. It is developing a series of regional strategies,<br />

based on identification of regional priorities building on<br />

the economic efficiencies of multicrop genebanks. At the same<br />

time, it is developing a series of global crop strategies, which<br />

will be implemented within the context of the regional strategies<br />

and which will seek the genetic efficiencies of global coordination.<br />

In <strong>International</strong> Year of <strong>Rice</strong> 2004, we are celebrating<br />

the world’s most important crop for food security. It is highly<br />

appropriate to start developing a global rice conservation strategy<br />

as one of the early initiatives of the Global Crop Diversity<br />

Trust.<br />

The history and diversity of rice<br />

Cultivated rice has at least three centers of origin (Fig. 1). Oryza<br />

sativa spread from its origins in South and East Asia to the<br />

south, north, east, and west, eventually to cover all continents<br />

except Antarctica. The precise time line of the migration of<br />

rice remains obscure in many countries.<br />

Primary centers of diversity are clearly associated with<br />

the centers of origin. An additional primary center of diversity<br />

in the mainland and islands off Southeast Asia appears to be<br />

associated with the intercrossing of the indica and japonica<br />

forms of O. sativa, encompassing a wide range of intermediate<br />

forms and tropical japonica.<br />

On its westward migration, O. sativa reached Europe<br />

more than 2,000 years ago, and secondary centers of diversity<br />

can be recognized with distinctive forms in the Indian Ocean,<br />

western Asia, and Europe. More recent distinctive secondary<br />

centers of diversity are also apparent in Africa and South<br />

America.<br />

For wild rice, the centers of species diversity and genomic<br />

diversity are the islands from Southeast Asia into the<br />

Pacific Ocean. Nine of the 22 wild species occur in Indonesia,<br />

and 7 of the 10 genome types are found in the Asian-Pacific<br />

islands. In addition, distinctive sets of species assemblages are<br />

associated with South Asia, Africa, and the Americas.<br />

Given so much genomic, species, and genetic diversity<br />

within and between regions, a comprehensive strategy for conserving<br />

the diversity of rice must be truly global in extent.<br />

Ex situ conservation of rice<br />

According to the FAO report on the State of the World’s Plant<br />

Genetic Resources, more than 400,000 accessions of rice are<br />

conserved in genebanks around the world. However, the majority<br />

of the accessions are in only a small number of genebanks<br />

(Table 1). Over 25% are held in <strong>IRRI</strong> and more than 60% of<br />

the remaining accessions are held in just five national Asian<br />

genebanks in China, India, Japan, Thailand, and the Republic<br />

of Korea.<br />

This conservation effort is far from coordinated or global.<br />

The extent of duplication across the major genebanks is<br />

unknown. T<strong>here</strong> are strong indications of gaps in coverage<br />

Session 1: The genus Oryza, its diversity, and its evolution 47


Fig. 1. History of the spread of rice agriculture. Each rice-producing country is shaded according<br />

to the date of the first cultivation of rice in the country. Key: dark green > 5,000 years ago<br />

→ yellow 2,000–3,000 years ago → dark red 100–200 years ago; hatched = rice is cultivated,<br />

unclear date of first cultivation; white = rice is not cultivated. The three centers of origin of<br />

cultivated rice are highlighted.<br />

Table 1. Summary of approximate numbers of accessions<br />

of rice held in major rice genebanks around the world.<br />

Genebank a<br />

Approximate number of accessions<br />

<strong>IRRI</strong> 107,000<br />

China-CAAS 64,000<br />

India-NBPGR 54,000<br />

Japan-NIAR 36,000<br />

Thailand-RRI 24,000<br />

Korea-RDA 23,000<br />

WARDA 20,000<br />

USA-NSGC 17,000<br />

Brazil-CENARGEN 14,000<br />

Laos-NARC 12,000<br />

IITA 12,000<br />

Russia-VIR 5,500<br />

Vietnam-PGRC 4,800<br />

Pakistan-PGRI 2,400<br />

Australia 1,400<br />

Indonesia-RIR 1,000<br />

Total 398,100<br />

a <strong>IRRI</strong> = <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>, CAAS = Chinese Academy<br />

of Agricultural Sciences, NBPGR = National Bureau of Plant Genetic<br />

Resources, NIAR = National <strong>Institute</strong> of Agrobiological Resources,<br />

RRI = <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>, RDA = Rural Development Administration,<br />

WARDA = Africa <strong>Rice</strong> Center, NSGC = National Small Grains<br />

Center, CENARGEN = Embrapa Recursos Genéticos e Biotecnologia,<br />

EMBRAPA = Empresa Brasileira de Pesquisa Agropecuária, NARC =<br />

National Agricultural <strong>Research</strong> Center, IITA = <strong>International</strong> <strong>Institute</strong> for<br />

Tropical Agriculture, VIR = Vavilov <strong>Research</strong> <strong>Institute</strong> of Plant Industry,<br />

PGRC = Plant Genetic Resources Center, PGRI = PARC Plant Genetic<br />

Resources <strong>Institute</strong>, PARC = Pakistan Agricultural <strong>Research</strong> Council,<br />

RIR = <strong>Research</strong> <strong>Institute</strong> for <strong>Rice</strong>.<br />

outside South and East Asia, especially in wild species but<br />

also in cultivated rice. The absence of coordinated information<br />

makes it impossible to assess the extent of duplication or<br />

gaps, or to fully and rationally analyze the distribution of diversity<br />

or target the worst gaps.<br />

The global strategy outlined<br />

A major element of the rice conservation strategy must be a<br />

global network, through which to coordinate conservation activities<br />

worldwide. Yet, most existing rice networks are for rice<br />

breeding and research (e.g., INGER, the <strong>International</strong> Network<br />

for the Genetic Evaluation of <strong>Rice</strong>), not for genetic resources.<br />

Through the GCDT, it is planned to develop such a network.<br />

Yet, any such network would be ineffective without an effective<br />

information resource on which to base decisions and strategies.<br />

Indeed, the lack of coordinated information is the major<br />

hindrance to the development of an efficient and rational global<br />

strategy for the conservation of rice genetic resources.<br />

T<strong>here</strong>fore, the heart of the network must contain a global information<br />

system documenting, as far as possible, the relevant<br />

data of all accessions conserved in all participating genebanks.<br />

Next steps<br />

Development of a global information resource will be the first<br />

objective of the global rice conservation strategy.<br />

T<strong>here</strong> is a risk, however, that we are planning to avoid,<br />

associated with assembling these data into a common system.<br />

Early attempts to integrate data from different genebanks were<br />

based on standardizing subsets of diverse data from different<br />

genebanks into a common format and collating them into a<br />

central database. Considerable effort was required to populate<br />

the central database with data. T<strong>here</strong>fore, data in the central<br />

48 <strong>Rice</strong> is life: scientific perspectives for the 21st century


database were updated only infrequently, if at all, so that the<br />

central database quickly became out-of-date. A rational, integrated<br />

decision-making process cannot be efficient or effective<br />

if it is based on outdated data.<br />

For the global rice database, an entirely different approach<br />

is being developed. We are working on developing a<br />

central search engine that will redirect incoming queries directly<br />

to the databases of participating genebanks. The only<br />

information kept in the central search engine will be metadata<br />

describing the data held by participating genebanks; these<br />

metadata are needed to redirect incoming queries correctly.<br />

Security mechanisms will keep the genebanks’ live databases<br />

safe behind firewalls and will ensure that only nonconfidential<br />

data are accessed. For each participating genebank, a map will<br />

be created that describes the relationship between the<br />

genebank’s own internal data structures and the common international<br />

standard. This map will be used to create a dynamic<br />

view of the data that has the appearance of the international<br />

standard but without changing the internal data structures<br />

or values. After creating the initial map and view, the<br />

global information resources will be kept automatically updated,<br />

with no additional investment by the contributing<br />

genebank.<br />

The outlook<br />

Once the test system is in place, we will be seeking additional<br />

partners to add new database nodes to the information network.<br />

The resulting global information resources will guide<br />

the establishment of responsibilities for conservation, identification<br />

of duplicates, and gaps in the global collection, and<br />

the rationalization of procedures for sharing germplasm and<br />

making it available to farmers and other users. The objectives<br />

of the <strong>International</strong> Treaty on Plant Genetic Resources for Food<br />

and Agriculture will be facilitated for rice in a way that will<br />

benefit us all.<br />

Notes<br />

Genetic architecture and complexity<br />

in wild and cultivated rice<br />

Y. Sano<br />

Authors’ addresses: Ruaraidh Sackville Hamilton, <strong>International</strong> <strong>Rice</strong><br />

<strong>Research</strong> <strong>Institute</strong>, DAPO Box 7777, Metro Manila, Philippines;<br />

Ruth Raymond, <strong>International</strong> Plant Genetic Resources<br />

<strong>Institute</strong>, Via dei Tre Denari, 472/a, 00057, Maccarese, Rome,<br />

Italy.<br />

A major challenge to modern geneticists and breeders is to<br />

understand the nature of quantitative trait loci (QTL) and environmental<br />

factors causing variation in quantitative traits, since<br />

adaptive traits are not determined by a single mutation under<br />

changing environments. Genetic complexity results from the<br />

combined effects of multiple genes whose expression is greatly<br />

influenced by the environment. We present <strong>here</strong> our recent studies<br />

on the significance of genetic diversity in wild and cultivated<br />

forms of rice.<br />

Hidden variation in the primary gene pool<br />

The offspring of two plants can contain novel combinations of<br />

alleles that produce more extreme phenotypes than those of<br />

either parent. This phenomenon (transgressive segregation) has<br />

been shown to be common (Rieseberg et al 2003). This indicates<br />

the importance of gene flow for the emergence of novelty<br />

in crops under man-made habitats, possibly showing a rapid<br />

change in their genetic architecture responding to the environment.<br />

Recently, the wild ancestor of maize (teosinte) was shown<br />

to have a high potential to produce phenotypic diversity although<br />

epistasis had tended to conceal the expression of genetic<br />

differences in natural populations (Lauter and Doebley<br />

2002), suggesting that phenotypic diversity has not been sufficiently<br />

exposed to date.<br />

Generally, isolating barriers appear between species but<br />

not within species, raising the question of how such a reproductive<br />

barrier could develop between species. We detected<br />

cross-incompatibility in advanced generations of backcrossing<br />

between wild and cultivated rice strains although no crossing<br />

barrier had been reported within the primary gene pool<br />

(Matsubara et al 2003). Genetic analysis revealed that an alien<br />

segment of chromosome 6 from a wild strain caused a failure<br />

of early endosperm development and that the cross-incompatibility<br />

resulted from the sexual affinity between the cross-incompatibility<br />

reactions in the female and male. Further, the<br />

postfertilization barrier was controlled by at least three linked<br />

genes on chromosome 6, showing a different distribution of<br />

interacting alleles among taxa (Fig. 1). The results suggest that<br />

differences leading to species-specific barriers might be partly<br />

preexisting within the gene pool even though they are not observed<br />

by conventional methods.<br />

A profound isolating barrier tends to be species-specific.<br />

We analyzed a hybrid sterility gene, S1, on chromosome 6 between<br />

Asian and African cultivated rice species. The hybrid<br />

sterility gene has the strongest effect among plant hybrids. The<br />

S1 gene is called a “gamete eliminator” since it induces abor-<br />

Session 1: The genus Oryza, its diversity, and its evolution 49


Short arm of chromosome 6<br />

Centromere<br />

wx<br />

RM204<br />

RZ516 RZ398<br />

S1520 RZ588 OsC1 G200<br />

RG264<br />

Hd1<br />

C235<br />

R111 R32<br />

G2028<br />

6.8<br />

2.6<br />

2.0<br />

7.5<br />

3.5<br />

5.3<br />

7.6<br />

11.9<br />

2.1<br />

7.3<br />

3.0<br />

5.6<br />

cM<br />

Cif<br />

cim<br />

Su-Cif<br />

Female gamete<br />

Male gamete<br />

Gene Reaction Reaction Gene<br />

Cif<br />

Cif<br />

+<br />

Cim<br />

Su-Cif<br />

cif<br />

+<br />

cim<br />

cim<br />

Incompatible cross<br />

Compatible cross<br />

Fig. 1. (A) Three linked genes (Cif, cim, and Su-Cif) responsible for the unidirectional cross-incompatibility<br />

detected between wild and cultivated rice strains. (B) The genetic model proposed by<br />

these genes, all of which act sporophytically. Cross-incompatibility occurs when gametes with the<br />

cross-incompatibility reactions in the female (Cif) and the male (cim) are fertilized. Cim and cim are<br />

predominantly distributed in indica and japonica types, respectively. + indicates the cross-compatibility<br />

reaction. The locations of the three genes are shown by thick solid lines.<br />

tion of both the male and female gametes possessing its allelic<br />

alternative S1-a only in the heterozygote. Surveys in their distribution<br />

showed that the S1 and S1-a alleles were specific to<br />

African and Asian rice species, respectively, although the sensitivity<br />

to distortion in the female differed between indica and<br />

japonica types. In addition, fine mapping revealed that only<br />

the female gametes became viable when the flanking region of<br />

the S1 gene was deleted, showing a preferential transmission<br />

only in pollen grains. Such a meiotic drive (MD) system violating<br />

Mendel’s rules has been detected in natural populations<br />

of a variety of organisms. The results in rice species suggested<br />

that a gamete eliminator could be derived from the male MD<br />

by accumulating responder-like elements affecting the female<br />

gamete and that this system could be involved in reproductive<br />

barriers.<br />

Polygenic balance theory<br />

Phenotypic variation is central to evolutionary adaptation underlying<br />

natural and artificial selection. Polygenes, which are<br />

very sensitive to residual variation and the environment, might<br />

be partly built up on a chromosome by selection, and repulsion<br />

or coupling linkages along a chromosome have been demonstrated<br />

in Drosophila (Mather and Jinks 1982). Stabilizing<br />

or normalizing selection could encourage the development of<br />

hidden variation within and between populations. Such a linked<br />

group of polygenes could be reshuffled through recombination,<br />

resulting in the formation of newly recombined phenotypes<br />

or transgression.<br />

Grain characteristics were examined between the two<br />

subspecific rice strains regarding QTLs on chromosome 6.<br />

Grain characteristics are known to be quantitative traits and to<br />

be diagnostic between them. To enhance the power to detect<br />

QTLs with small effects, recombinant inbred lines (RILs) were<br />

made after introgression of chromosome 6, so the segmented<br />

fragments could be precisely compared, minimizing the residual<br />

variation. The resulting RILs showed a distinct transgressive<br />

segregation in the seed dimension. Multiple linked<br />

QTLs were detected on the segment, showing positive and<br />

negative values in additive effects as well as epistatic interactions<br />

between the detected QTLs, although such QTLs on chromosome<br />

6 were not reported before. The results confirmed<br />

50 <strong>Rice</strong> is life: scientific perspectives for the 21st century


that the transgressive segregation is driven from breakdown<br />

of linkage and that the detection of QTLs highly depends on<br />

the genetic effects of the flanking QTLs, indicating a need for<br />

caution in interpreting data about the detected QTLs.<br />

Implications from genealogy<br />

Analysis of geographic patterns of variation in crops is essential<br />

to understand their evolving populations and to make efficient<br />

use of the available variability in plant breeding, even<br />

though traditional landraces are rapidly replaced by modern<br />

high-yielding varieties worldwide. The nature of crop gene<br />

pools suggests that domestication has been achieved largely at<br />

the intraspecific level although gene flow enables cultivated<br />

forms to keep pace with abiotic and biotic factors. Genetic<br />

diversity could result from the diversification of alleles and<br />

interacting genes (including epistasis) and/or from the diversification<br />

of structural and regulatory genes. Recent work on<br />

DNA sequences shows that genetic diversity is affected both<br />

by current patterns of microevolutionary forces, such as gene<br />

flow and selection, and by phylogenetic history (Schaal et al<br />

2003). Alleles at different loci even on different chromosomes<br />

were not randomly associated with each other, possibly attributable<br />

to selection, drift, and nonrandom mating (Morishima<br />

et al 1992). Genealogy provides insight into these evolutionary<br />

processes.<br />

Divergent phenotypes are often detected in domesticated<br />

plants. An example in rice is apiculus coloration associated<br />

with anthocyanin pigmentation. It has been reported in cultivars<br />

from the northern area of Japan that varying degrees of<br />

coloration are caused by a series of alleles at the C locus<br />

(Takahashi 1982). Based on the synteny map between rice and<br />

maize, the C gene was expected to be the rice homologue<br />

(OsC1) of maize C1, which belongs to the group of R2R3-<br />

Myb regulatory factors. Two different types of deletions causing<br />

a frameshift were detected in the 3rd exon, and both of the<br />

deleted nucleotides corresponded to the positions of putative<br />

base-contacting residues, suggesting that the indica and<br />

japonica types carry mutations with independent origins (Saitoh<br />

et al 2004). In addition, replacement substitutions were frequently<br />

detected in the OsC1 gene of strains carrying the previously<br />

defined C alleles. Molecular evolutionary analysis revealed<br />

that haplotype diversity was higher in wild forms than<br />

in cultivated forms; however, cultivated forms had their specific<br />

haplotypes showing few shared haplotypes with their wild<br />

form (Fig. 2). The genealogy of the OsC1 gene suggested that<br />

allelic diversification causing phenotypic changes might have<br />

resulted from mutations in the coding region of landraces rather<br />

than incorporation from others through hybridization. The neutrality<br />

test also revealed that changes in amino acids might be<br />

associated with selective forces acting on the lineage representing<br />

most Asian cultivated forms. This suggests that<br />

landraces might maintain more agronomically valuable genes<br />

accumulated since the origin of rice than previously believed,<br />

even if a reduction in nucleotide diversity was caused by the<br />

population bottleneck due to domestication. Thus, the allelic<br />

diversity of the OsC1 gene shows the importance of farmers’<br />

efforts; however, it remains to be studied why haplotype diversity<br />

is high in the northern areas of rice cultivation.<br />

It is well known that the semidwarf gene from variety<br />

DGWG greatly contributed to the Green Revolution in rice.<br />

Recent molecular work revealed that the mutation is due to a<br />

deletion at the OsGA20ox2 gene (Ashikari et al 2002), which<br />

made it possible to survey its geographical distribution. It has<br />

been believed that the semidwarf gene arose and was maintained<br />

in a local variety until the development of high-yielding<br />

varieties (Jennings 1966). Recently, we found that wild strains<br />

and landraces from China carry the same allele as that of<br />

DGWG, although it was not distributed in tropical areas, except<br />

for modern high-yielding varieties. The phenotypic expression<br />

of the semidwarf gene was suppressed in the wild<br />

strain, showing that the presence of interacting genes enabled<br />

its wild carriers to maintain it within the population, although<br />

slightly deleterious mutations would be rapidly selected against<br />

because of competition in rice fields. This leads us to consider<br />

that sd1 preexisted in wild forms and was incorporated into<br />

landraces through gene flow. T<strong>here</strong>fore, farmers’ efforts seem<br />

to have greatly contributed to mine the semidwarf gene, excluding<br />

interacting genes under less-competitive fields apart<br />

from tropical areas. These findings confirm that genetic resources<br />

of wild forms and landraces have been equally important,<br />

giving us suggestions for improving rice in the future.<br />

References<br />

Ashikari MA, Sasaki A, Ueguchi-Tanaka M, Itoh H, Nishimura A,<br />

Datta S, Ishiyama K, Saito T, Kobayashi M, Khush GS, Kitano<br />

H, Matsuoka M. 2002. Mutation in a gibberellin biosynthetic<br />

gene, GA20 oxidase, contributed to the rice ‘Green Revolution’.<br />

Breed. Sci. 52:143-150.<br />

Jennings PR. 1966. The evolution of plant type in Oryza sativa.<br />

Econ. Bot. 20:396-402.<br />

Lauter N, Doebley J. 2002. Genetic variation for phenotypically invariant<br />

traits detected in teosinte: implications for the evolution<br />

of novel forms. Genetics 160:333-342.<br />

Mather K, Jinks JL. 1982. Biometrical genetics. 3rd edition. New<br />

York, N.Y. (USA): Chapman and Hall. 396 p.<br />

Matsubara K, Khin-Thidar, Sano Y. 2003. A gene block causing crossincompatibility<br />

hidden in wild and cultivated rice. Genetics<br />

165:343-352.<br />

Morishima H, Sano Y, Oka HI. 1992. Evolutionary studies in cultivated<br />

rice and its wild relatives. Oxford Surv. Evol. Biol.<br />

8:135-184.<br />

Rieseberg LH, Widmer A, Arntz AM, Burke JM. 2003. The genetic<br />

architecture necessary for transgressive segregation is common<br />

in both natural and domesticated populations. Philos.<br />

Trans. R. Soc. Lond. B Biol. Sci. 358:1141-1147.<br />

Saitoh K, Ohnishi K, Mikami I, Khin-Tidar, Sano Y. 2004. Allelic<br />

diversification at the C (OsC1) locus of wild and cultivated<br />

rice: nucleotide changes associated with phenotypes. Genetics<br />

168:(in press).<br />

Schaal BA, Gaskin JF, Caicedo AL. 2003. Phylogeography, haplotype<br />

trees, and invasive plant species. J. Hered. 94:197-204.<br />

Takahashi M-E. 1982. Gene analysis and its related problems. J.<br />

Fac. Agric. Hokkaido Univ. 61:91-142.<br />

Session 1: The genus Oryza, its diversity, and its evolution 51


Haplotype Strain Group<br />

SA1<br />

Jp (T65, A58)<br />

SA2<br />

Jp (A18, A56)<br />

SA3<br />

Jp (A38, A83, A136, 544)<br />

Jv (226, 647) In (133)<br />

SA4<br />

Jp (A5, A55, A108)<br />

87<br />

SA5<br />

Jp (734)<br />

60<br />

SA6<br />

In (108, IR36, 868, 414,<br />

719, Acc6622, Acc35618)<br />

A<br />

63 SA8<br />

In (I47)<br />

65 SA9<br />

In (I32, I45) Ra (W2012)<br />

RU1<br />

Rp (W1944)<br />

80<br />

77<br />

75<br />

78<br />

85<br />

56<br />

SA7<br />

RU4<br />

RU3<br />

RU5<br />

RU2<br />

Rp (W1943)<br />

In (160, 706, N303, C6172)<br />

RP (W120)<br />

Ra (W107) Rin (W1819)<br />

Ra (W1865)<br />

B<br />

95<br />

RU6<br />

96 64<br />

66<br />

RU7<br />

RU8<br />

Rp (W1294)<br />

Rp (W593)<br />

Ra (W2002)<br />

C<br />

AF<br />

GLU<br />

W025, W1468, W1647<br />

W1187<br />

Outgroup<br />

0.001<br />

Substitution/site<br />

Fig. 2. Neighbor-joining (NJ) reconstruction of the genealogical relationships among OsC1 haplotypes<br />

of 43 strains in wild and cultivated rice strains. Oryza glaberrima, O. barthii (AF), and O. glumaepatula<br />

(GLU) were used as outgroups. The maximum-parsimony (MP) method gave the same topology. Bootstrap<br />

values for nodes supported in >50% of 1,000 bootstrap replicates are shown above (for NJ) and<br />

below (for MP) the branches. Jp, Jv, and In represent japonica, javanica, and indica types of O. sativa,<br />

respectively. Ra, Rin, and Rp represent annual, intermediate, and perennial types of O. rufipogon,<br />

respectively. AF includes O. glaberrima (W025) and O. barthii (W1468, W1647).<br />

Notes<br />

Author’s address: Graduate School of Agriculture, Hokkaido University,<br />

Sapporo, Japan, e-mail: rysano@abs.agr.hokudai.ac.jp.<br />

Who was the mother of cultivated rice Differentiation<br />

of chloroplast genome structure among cultivated rice<br />

and ancestral wild species<br />

Koh-ichi Kadowaki<br />

Phylogenetic analysis of Oryza species based<br />

on the mitochondrial and chloroplast genomes<br />

Analysis of variation in the cytoplasmic genome is valuable<br />

for taxonomic analysis (e.g., Ge et al 1999). Simple sequence<br />

repeats (SSR) and their flanking regions in the mitochondrial<br />

and chloroplast genomes were sequenced in order to reveal<br />

DNA sequence variation (Fig. 1). The information was used to<br />

gain new insights into phylogenetic relationships among 22<br />

species in the genus Oryza (Vaughan et al 2003). Five chloroplast<br />

SSR loci (Ishii and McCouch 2000) and seven mitochondrial<br />

SSR loci equal to or longer than ten mononucleotide repeats<br />

were chosen from known rice mitochondrial (Notsu et al<br />

52 <strong>Rice</strong> is life: scientific perspectives for the 21st century


O. granulata complex<br />

O. sativa complex<br />

Related genus<br />

GG<br />

AA<br />

BB<br />

EE<br />

O. officinalis complex<br />

Wheat,<br />

barley,<br />

maize,<br />

etc.<br />

HHJJ<br />

FF<br />

CC<br />

BBCC<br />

CCDD<br />

Genus Oryza<br />

O. ridleyi complex<br />

Fig. 1. A model for evolution of the cytoplasmic genome in Oryza species based on<br />

SSRs and their flanking regions.<br />

2002) and chloroplast genome sequences (Hiratsuka et al<br />

1989). A total of 50 accessions of Oryza that represented six<br />

different genomes of diploid Oryza species and three different<br />

allopolyploid genomes were analyzed. Many base substitutions<br />

and deletions/insertions were identified in the SSR loci and<br />

their flanking regions. Of mononucleotide SSR, G (or C)-repeats<br />

were more variable than A (or T)-repeats. Results obtained<br />

by chloroplast and mitochondrial SSR analyses showed<br />

similar phylogenetic relationships among species, although<br />

chloroplast SSR were more informative because of their higher<br />

sequence diversity. The CC genome is suggested to be the<br />

maternal parent for the two BBCC-genome species (O.<br />

punctata and O. minuta) and the CCDD species (O. latifolia)<br />

based on the high level of sequence conservation between diploid<br />

CC-genome species and these allotetraploid species.<br />

Polyphyletic domestication of indica, temperate japonica,<br />

and tropical japonica from O. rufipogon: evaluation<br />

of genetic diversity by the chloroplast genome<br />

It is believed that Oryza sativa ecospecies indica and japonica<br />

were domesticated in Asia from O. rufipogon and/or O. nivara,<br />

but that domestication process is still not well understood.<br />

Complete chloroplast genome information is available for one<br />

japonica variety (Hiratsuka et al 1989). Recently, we have determined<br />

a whole chloroplast genome of O. nivara, an annual<br />

type of wild rice and possible progenitor to O. sativa (Masood<br />

et al 2004). Several insertion/deletion events were identified<br />

between the two species. To investigate the domestication process<br />

of rice, three polymorphic loci, 8K, 57K, and 67K, were<br />

examined using 303 accessions of Asian cultivated rice and<br />

32 accessions of Oryza species carrying the AA genome. The<br />

8K was originally found as ORF100 by Chen et al (1993) and<br />

Kanno et al (1993). The three regions showed a different extent<br />

of sequence variation. In the 8K region, most indica<br />

(76.1%) had a deletion type of polymorphism, w<strong>here</strong>as most<br />

japonica (98.5%) had a nondeletion type. In contrast, in the<br />

76K region, no length polymorphism was observed at all within<br />

the cultivated rice examined. In the 57K region, various length<br />

polymorphisms, so far six types, were identified by DNA sequencing.<br />

These results showed that the extent of polymorphism<br />

is variable depending on the chloroplast locus and that<br />

occurrence of an insertion/deletion event is independent regarding<br />

the three regions. Sequence variations at the 8K and<br />

57K regions were also present in some of the O. nivara and O.<br />

rufipogon but not in other wild species, suggesting that mutations<br />

at the two regions happened relatively recently and prior<br />

to the domestication of Asian cultivated rice. These results<br />

suggest that indica of type IV and VII were domesticated either<br />

from a local population of O. rufipogon via O. nivara or<br />

directly from a local population of O. rufipogon separately.<br />

Regarding japonica, japonica of type VI and IV (tropical type)<br />

were derived from a different local population of O. rufipogon<br />

without O. nivara, polyphyletically and independently. A previous<br />

study using nuclear element SINEs also showed that O.<br />

sativa has been derived polyphyletically from O. rufipogon<br />

(Ohtsubo et al 2004). Our study strongly suggests that t<strong>here</strong><br />

are at least four major lineages for the domestication process<br />

of Asian cultivated rice (Fig. 2).<br />

Session 1: The genus Oryza, its diversity, and its evolution 53


0<br />

Type IV-AA<br />

1<br />

Type IV-TT<br />

16<br />

2<br />

Hypothetical<br />

ancestor<br />

Type VII-TT<br />

15<br />

17<br />

Type VI <br />

unidentified<br />

O. rufipogon<br />

107<br />

indica<br />

japonica<br />

81<br />

Fig. 2. A model for the domestication process of cultivated rice from wild species.<br />

Numerals in the figure show the number of accessions.<br />

References<br />

Chen WB, Nakamura I, Sato Y, Nakai H. 1993. Distribution of deletion<br />

type in cpDNA of cultivated and wild rice. Jpn. J. Genet.<br />

68:597-603.<br />

Ge S, Sang T, Lu B-R, Hong D-Y. 1999. Phylogeny of rice genomes<br />

with emphasis on origins of allotetraploid species. Proc. Natl.<br />

Acad. Sci. USA 96:14400-14405.<br />

Hiratsuka J, Shimada H, Whittier R, Ishibashi T, Sakamoto M, Mori<br />

M, Kondo C, Honji Y, Sun CR, Meng BY. 1989. The complete<br />

sequence of the rice (Oryza sativa) chloroplast genome:<br />

intermolecular recombination between distinct tRNA genes<br />

accounts for a major plastid DNA inversion during the evolution<br />

of the cereals. Mol. Gen. Genet. 217:185-194.<br />

Ishii T, McCouch SR. 2000. Microsatellites and microsynteny in the<br />

chloroplast genomes of Oryza and eight other Gramineae species.<br />

Theor. Appl. Genet. 100:1257-1266.<br />

Kanno A, Watanabe N, Nakamura I, Hirai A. 1993. Variations in<br />

chloroplast DNA from rice (Oryza sativa): differences between<br />

deletions mediated by short direct-repeat sequences within a<br />

single species. Theor. Appl. Genet. 86:579-584.<br />

Masood S, Kadowaki K, Nishikawa T, Fukuoka S, Njenga PK,<br />

Tsudzuki T, Kadowaki K. 2004. The complete nucleotide sequence<br />

of wild rice (Oryza nivara) chloroplast genome: first<br />

genome-wide comparative sequence analysis of wild and cultivated<br />

rice. Gene. (In press.)<br />

Notsu Y, Masood S, Nishikawa T, Kubo N, Akiduki G, Nakazono M,<br />

Hirai A, Kadowaki K. 2002. The complete sequence of the<br />

rice (Oryza sativa L.) mitochondrial genome: frequent DNA<br />

sequence acquisition and loss during the evolution of flowering<br />

plants. Mol. Genet. Genomics 268:434-445.<br />

Ohtsubo H, Cheng C, Ohsawa I, Tsuchimoto S, Ohtsubo E. 2004.<br />

<strong>Rice</strong> retroposon p-SINE1 and origin of cultivated rice. Breed.<br />

Sci. 54:1-11.<br />

Vaughan DA, Morishima H, Kadowaki K. 2003. Diversity in the<br />

Oryza genus. Curr. Opin. Plant Biol. 6:139-146.<br />

Notes<br />

Author’s address: National <strong>Institute</strong> of Agrobiological Sciences,<br />

Tsukuba, Ibaraki 305-8602, Japan, e-mail:<br />

kadowaki@affrc.go.jp.<br />

Diverse mechanisms of low-temperature stress<br />

response in rice<br />

Ryozo Imai, Jiangqi Wen, Kentaro Sasaki, and Kiyoharu Oono<br />

<strong>Rice</strong> is widely cultivated in a large number of different natural<br />

environments. Compared with other cereal crops such as wheat<br />

and barley, rice is much more sensitive to low temperature,<br />

probably as a result of its subtropical origin. In terms of impact<br />

on rice production, male sterility is the most damaging<br />

impact of chilling. The developmental stages from pollen formation<br />

to fertilization are the most vulnerable to low temperature<br />

throughout the life cycle of rice plants (Nishiyama 1984).<br />

It has been reported that the young microspore stage in pollen<br />

development was the most sensitive to low temperature (Satake<br />

and Hayase 1970). Exposure of rice plants at the tetrad stage<br />

to a moderate low temperature (12 ºC) for 4 days resulted in<br />

male sterility in 80% of the spikelets (Satake and Hayase 1970,<br />

Nishiyama 1984). Microscopic observation of developing rice<br />

anthers suggested that one possible reason for male sterility<br />

after low-temperature treatment was the failure of anther de-<br />

54 <strong>Rice</strong> is life: scientific perspectives for the 21st century


velopment. Observed abnormalities included the cessation of<br />

anther development, arrest of pollen development, anthers remaining<br />

within the flowers after anthesis, and partial or no<br />

dehiscence (Satake 1976).<br />

Cytological observation revealed a dilatation of tapetal<br />

layers in chilling-treated rice anthers (Nishiyama 1976, 1984).<br />

Dilatation of the tapetal layer was accompanied by a vigorous<br />

augmentation of cytoplasmic organelles such as mitochondria,<br />

proplastids, Golgi bodies, and endoplasmic reticula (Nishiyama<br />

1976, 1984). Chilling temperature treatment also affects the<br />

physiological status of anthers. Nonreducing sugar content was<br />

found to increase rapidly, w<strong>here</strong>as acid phosphatase activity<br />

decreased in the moderate temperature-treated rice anthers<br />

(Nishiyama 1984). Possible involvement of phytohormones,<br />

such as GA and auxin in chilling-induced male sterility, has<br />

been reported (Nishiyama 1975, Yoshioka and Suge 1996).<br />

However, it is still largely unknown how chilling temperature<br />

induces molecular events that result in male sterility in rice<br />

plants.<br />

In this paper, we used a large-scale screening of genes<br />

responsive to a moderate chilling temperature (12 ºC) and functional<br />

analysis of the gene products. We report on diverse<br />

molecular responses that occur during chilling stress in rice.<br />

Materials and methods<br />

Plant materials, growth conditions,<br />

and stress treatment<br />

Seeds of Oryza sativa L. cv. Yukihikari (japonica rice) were<br />

grown in a growth chamber at 25 ºC under continuous illumination<br />

(256 mmol m –2 s –1 ). After growing for 7 days, rice seedlings<br />

underwent environmental stress treatments. To collect<br />

the flowers and anthers, Yukihikari plants were grown in pots<br />

with nutrient soil for 2 months in a phytotron room controlled<br />

at 25/19 ºC (day/night). Anthers and panicles at the tetrad stage<br />

of microspore development were collected and frozen immediately<br />

in liquid nitrogen. For the chilling treatment, the pots<br />

with rice plants were transferred to a phytotron room that was<br />

precooled to 12 ºC. Anthers and panicles were collected at 48<br />

h of 12 ºC treatment.<br />

cDNA subtraction<br />

Total RNA was isolated using TRIzol reagent (Invitrogen) and<br />

poly (A) + RNA was purified using Dynabeads Oligo(dT) 25<br />

(Dynal). The PCR-Select cDNA subtraction kit (CLONTECH)<br />

was used to isolate chilling-induced clones. Candidate clones<br />

were arrayed on Hybond-N + membranes (Amersham-<br />

Pharmacia Biotech) and further selected using differential hybridization.<br />

Northern blot analysis<br />

Twenty micrograms of total RNA that was isolated from<br />

stressed or control samples using TRIzol reagent were separated<br />

on 1.0% formaldehyde denaturing agarose gels and transferred<br />

onto Hybond-N + membranes according to standard<br />

methods.<br />

Microarray screening<br />

Total RNA was extracted from seedling roots and used for labeling<br />

with Cy5. Microarray plates containing about 9,000<br />

cDNA clones (provided by STAFF) were screened with target<br />

cDNA from nonstressed (NS) and cold-treated (2 or 24 h) roots<br />

(CS). Cold-induced clones were selected from spots with a 2<br />

or higher CS/NS signal ratio.<br />

Results and discussion<br />

Subtractive screening of cDNA that accumulated in 12 ºCtreated<br />

anthers identified a cDNA clone, OsMEK1, encoding<br />

a protein with features characteristic of an MAP kinase (Wen<br />

et al 2002). The putative OsMEK1 protein shows 92% identity<br />

to the maize MEK homolog, ZmMEK1. OsMEK1 transcript<br />

levels were induced in rice anthers by 12 ºC treatment<br />

for 48 h. Similar OsMEK1 induction was observed in shoots<br />

and roots of seedlings that were treated at 12 ºC for up to 24 h.<br />

Interestingly, no induction of OsMEK1 transcripts was observed<br />

in 4 ºC-treated seedlings. In contrast, rice lip19, encoding a<br />

bZIP protein possibly involved in low-temperature signal transduction,<br />

was not induced by 12 ºC treatment but was induced<br />

by 4 ºC treatment. Among the three MAP kinase homologs<br />

cloned, only OsMAP1 displayed a 12 ºC-specific induction<br />

pattern similar to that of OsMEK1. A yeast two-hybrid system<br />

revealed that OsMEK1 interacts with OsMAP1, but not with<br />

OsMAP2 and OsMAP3, suggesting that OsMEK1 and<br />

OsMAP1 probably function in the same signaling pathway.<br />

An in-gel assay of protein kinase activity revealed that a protein<br />

kinase (approx. 43 kDa), which preferentially uses MBP<br />

as a substrate, was activated by 12 ºC treatment but not by<br />

4 ºC treatment. These results lead us to conclude that at least<br />

two signaling pathways for low-temperature stress exist in rice<br />

and an MAP kinase pathway with OsMEK1 and OsMAP1 components<br />

is possibly involved in the signaling for the higherrange<br />

low-temperature stress.<br />

Microarray slides were screened with target cDNA from<br />

nonstressed and chilling-stressed (2 or 24 h) roots. Forty-nine<br />

spots were selected for cDNA clones that are induced by the<br />

2-h cold treatment. Database searches indicated that 26 clones<br />

have a putative function and contain lip9 (Aguan et al 1991),<br />

OsCDPK7 (Saijo et al 2000), and OsMAP1, which are known<br />

to be cold-inducible. In addition, all of the 12 clones that were<br />

analyzed by Northern blots showed induction within 2 h of<br />

12 ºC treatment. Collectively, these data suggest that the rice<br />

microarray system is highly reliable for identifying stress-related<br />

genes. The newly identified 12 ºC-induced clones include<br />

NAC-family transcription factors, a zinc finger protein, and a<br />

ring finger protein, suggesting that these DNA-binding proteins<br />

may be involved in chilling signal transduction. Genes<br />

for biosynthesis of phospholipids, a disaccharide, polyamines,<br />

and jasmonate were also induced. These data suggest that<br />

metabolic changes occur as early responses to moderate lowtemperature<br />

stress. Exposure to moderate low temperature for<br />

a longer period (24 h) induced different responses in rice roots.<br />

Screening of spots that gave stronger signals in CS (24 h) than<br />

Session 1: The genus Oryza, its diversity, and its evolution 55


in NS identified 94 spots. Functions for 29 clones were assigned<br />

after database searches. Those clones include genes for<br />

protein sorting and vesicle transport, translation, and oxidative<br />

stress protection.<br />

Our data demonstrated that moderate (12 ºC) and severe<br />

(4 ºC) chilling stresses could be recognized as distinctive signals<br />

in rice. We were able to detect a number of responses of<br />

rice to moderate chilling temperature. Identification of functions<br />

for such genes will provide us with a clue to understand<br />

specific molecular events that occur during moderate chilling<br />

stress in rice.<br />

References<br />

Aguan K, Sugawara K, Suzuki N, Kusano T. 1991. Isolation of genes<br />

for low-temperature-induced proteins in rice by a simple subtractive<br />

method. Plant Cell Physiol. 32:1285-1289.<br />

Nishiyama I. 1975. Male sterility caused by cooling treatment at the<br />

young microspore stage in rice plants. XI. Effects of some<br />

substances on sterility. Proc. Crop Sci. Soc. Jpn. 44:397-402.<br />

Nishiyama I. 1976. Male sterility caused by cooling treatment at the<br />

young microspore stage in rice plants. Proc. Crop Sci. Soc.<br />

Jpn. 45:254-262.<br />

Nishiyama I. 1984. Climate influence on pollen formation and fertilization.<br />

In: Tsunoda S, Takahashi N, editors. Biology of rice.<br />

Amsterdam (Netherlands): Elsevier. p 153-171.<br />

Saijo Y, Hata S, Kyozuka J, Shimamoto K, Izui K. 2000. Over-expression<br />

of a single Ca 2+ -dependent protein kinase confers<br />

both cold and salt/drought tolerance on rice plants. Plant J.<br />

23:319-327.<br />

Satake T, Hayase H. 1970. Male sterility caused by cooling treatment<br />

at the young microspore stage in rice plants. V. Estimation<br />

of pollen developmental stage and most sensitive stage<br />

to coolness. Proc. Crop Sci. Soc. Jpn. 39:468-473.<br />

Satake T. 1976. Determination of the most sensitive stage to steriletype<br />

cool injury in rice plants. Res. Bull. Hokkaido Natl. Agric.<br />

Exp. Stn. 113:1-43.<br />

Yoshioka T, Suge H. 1996. Damage of seed fertility by cooling treatment<br />

and endogenous gibberellins in ears of rice plants (Oryza<br />

sativa L.). Breed. Sci. 46:173-178.<br />

Wen JQ, Oono K, Imai R. 2002. Two novel mitogen-activated protein<br />

signaling components, OsMEK1 and OsMAP1, are involved<br />

in a moderate low temperature signaling pathway in<br />

rice. Plant Physiol. 129:1880-1891.<br />

Notes<br />

Authors’ addresses: Ryozo Imai and Kentaro Sasaki, Winter Stress<br />

Laboratory, National Agricultural <strong>Research</strong> Center for<br />

Hokkaido Region, NARO, Sapporo, Japan. Present address:<br />

Jiangqi Wen, Division of Biological Sciences, University of<br />

Missouri-Columbia, MO, USA; Kiyoharu Oono, <strong>Research</strong><br />

Center for Environmental Genomics, Kobe University, Kobe,<br />

Japan, e-mail: rzi@affrc.go.jp.<br />

Genetic diversity of Myanmar rice landraces<br />

Ye Tint Tun, K. Irie, T. Nagamine, Jhon Ba Maw, F. Kikuchi, and H. Fujimaki<br />

Myanmar is a tropical country in monsoon Asia and is included<br />

in the center of diversity of cultivated rice along with Yunnan<br />

Province (China), east Nepal, Bhutan, Assam (India), and northern<br />

Thailand (Nakagahra and Hayashi 1977, Nakagahra et al<br />

1984, Glaszmann 1987). Myanmar has varied natural environments,<br />

various social and cultural customs, different types<br />

of farming and cropping systems, and tribal diversity. Consequently,<br />

various ecotypes such as rainfed, irrigated, deepwater,<br />

floating, and upland rice are cultivated and a number of<br />

landraces are differentiated in each ecotype. A number of<br />

landraces are still cultivated locally but are being rapidly replaced<br />

by improved cultivars. It is thus necessary to collect<br />

landraces for ex situ conservation and to characterize and evaluate<br />

them for future rice breeding.<br />

Our study deals with a thousand or more rice landraces<br />

collected throughout Myanmar in order to investigate their genetic<br />

diversity and characterize them.<br />

Agroecological zoning of rice-growing environments<br />

The characterization of rice-growing areas was first needed<br />

for analyzing the diversity of landraces of Myanmar cultivated<br />

rice. T<strong>here</strong>fore, agroecological zoning was attempted by using<br />

monthly meteorological data accumulated at 34 observatory<br />

sites throughout Myanmar for more than 30 years of rainfall;<br />

maximum, minimum, and mean temperatures; differences<br />

between day and night temperatures; evapotranspiration; and<br />

sunshine, compiled by FAO (1987). Eight agroecological zones<br />

were elaborated by the results of the principal component analysis:<br />

Northern Mountainous (NM), Eastern Plateau (EP), Semiarid<br />

(SA), Western Hilly (WH), Western Coastal (WC), Southern<br />

Coastal (SC), Southern Plain (SP), and Ayeyarwady Delta<br />

(AD) (Fig. 1). The NM, EP, and WH zones had the most complex<br />

topography, with high mountains and deep valleys, but<br />

the others are rather flat and plain zones.<br />

In Myanmar, rainfed rice is the most dominant ecotype<br />

and it is grown extensively in SP and AD zones. In the mountainous<br />

zones, NM, WH, and EP, upland rice is preferentially<br />

grown in the slash-and-burn farming system. Irrigated rice is<br />

predominantly cultivated in the central SA zone and deepwater<br />

and floating rice are grown exclusively in delta areas in AD<br />

and WC zones.<br />

56 <strong>Rice</strong> is life: scientific perspectives for the 21st century


WH<br />

n = 134<br />

NM<br />

n = 232<br />

NM<br />

WC<br />

n = 130<br />

WH<br />

EP<br />

EP<br />

n = 260<br />

WC<br />

SA<br />

SP<br />

SP<br />

n = 144<br />

AD<br />

SC<br />

SA<br />

n = 125<br />

AD<br />

n = 149<br />

SC<br />

n = 217<br />

Low<br />

Medium<br />

High<br />

Myanmar<br />

n = 1,391<br />

Fig. 1. Regional variation in photoperiod sensitivity of landraces of cultivated rice in Myanmar. WH =<br />

Western Hilly, NM = Northern Mountainous, EP = Eastern Plateau, SA = Semiarid, WC = Western Coastal,<br />

SC = Southern Coastal, SP = Southern Plain, and AD = Ayeyarwady Delta.<br />

Session 1: The genus Oryza, its diversity, and its evolution 57


Indica-japonica discrimination<br />

A core collection of 300 samples randomly chosen from the<br />

1,391 landrace collection was used to discriminate between<br />

indica and japonica Myanmar rice landraces. A discriminating<br />

index (Z) was employed, which was composed of a linear function<br />

of degree of phenol color reaction (Ph), tolerance of KClO 3<br />

(K), and apiculus hair length (H). Classification of landraces<br />

was carried out by using those indices calculated by the following<br />

formula (Sato 1991):<br />

Z = Ph + 1.313K – 0.82H – 1.251<br />

Eighty percent of the landraces were found to belong to<br />

indica and 20% to japonica. Indica landraces were distributed<br />

ubiquitously in every zone, w<strong>here</strong>as japonicas were predominant<br />

exclusively in the WH zone. Several techniques have been<br />

proposed by different researchers to discriminate between indica<br />

and japonica. Their results are not always consistent but<br />

the presently employed discriminating index seemed to be the<br />

most useful for identifying subspecific differentiation of<br />

Myanmar cultivated rice.<br />

Photoperiod sensitivity<br />

Some 1,391 landraces were sown at Yezin in Myanmar twice a<br />

year—on 12 March 2001 under long-day conditions and on<br />

25 August 2001 under short-day conditions—to observe heading<br />

responses under different daylength. The photoperiod sensitivity<br />

(PS) of rice landraces was evaluated based on the differences<br />

in days to heading under the two different growing<br />

seasons. The basic vegetative growth (BVG) was estimated<br />

from days to heading of the landraces when they were sown on<br />

25 August.<br />

A great diversity was observed in the BVG and PS of<br />

landraces. The PS of landraces was categorized into three<br />

groups as low (less than 59 days), intermediate (60 to 109 d),<br />

and high (above 110 d). It was disclosed that 15% of Myanmar<br />

landraces were less sensitive to photoperiodism, 13% were<br />

intermediate, and 72% were highly sensitive. Figure 1 shows<br />

the regional variation of PS. A distinctive cline was observed<br />

from the mountainous to the plain zones. This sort of differentiation<br />

among zones was considered to be closely associated<br />

with cultivated ecotypes, the prevailing cropping system, and<br />

the natural conditions of each rice-growing area.<br />

Photoperiod sensitivity is the most important factor in<br />

determining the growth duration of the rice plant and is considered<br />

to be closely associated with local adaptability and<br />

with ecological differentiation of rice landraces as well.<br />

Amylose content of endosperm starch and genotypes<br />

of esterase isozyme<br />

The 1,391 landraces were used for analyzing the amylose content<br />

of endosperm starch and a core collection of 300 samples<br />

randomly chosen from the landrace collection was used to identify<br />

esterase isozyme genotypes. Landraces of Myanmar cultivated<br />

rice were found to have great diversity in amylose content<br />

of endosperm starch, ranging from 0 to 40%. Glutinous<br />

landraces distributed ubiquitously in every zone had less varied<br />

frequencies. However, the amylose content of nonglutinous<br />

landraces varied from zone to zone. In particular, landraces<br />

with very low (3–10%) amylose content appeared more frequently<br />

in the northeastern NM and EP zones, but amylose<br />

content was less or zero in the middle to southwestern zones<br />

such as WC, SA, SP, AD, and SC (Fig. 2). Glutinous landraces<br />

have been grown in every zone and are supposed to be used<br />

especially for making rice snacks or cakes at seasonal festivals.<br />

Those who live in the northeastern zones such as NM<br />

and EP are supposed to have a strong preference for low-amylose<br />

rice and/or any special way of cooking it. In Japan, lowamylose<br />

mutants have been artificially induced to improve the<br />

palatability of cooked rice of japonica cultivars (Okuno et al<br />

1983). However, low-amylose landraces occurred spontaneously<br />

in the northeastern zones of Myanmar. The amylose content<br />

of endosperm starch seems closely associated with the<br />

palatability of cooked rice and is highly influenced by human<br />

selection. We need to clarify whether the low amylose content<br />

of landraces in the northeastern zones is controlled by the du<br />

genes or any other genetic mechanisms.<br />

Isozymes have an identical enzymic function and are supposed<br />

to be less affected by or rather independent of natural<br />

and/or artificial selection. Consequently, polymorphic diversity<br />

in isozymes may reflect the phylogenetic differentiation<br />

of rice landraces. Esterase isozymes have been used repeatedly<br />

for investigating polymorphic diversity reflecting the<br />

phylogenic differentiation of various kinds of cultivated plants.<br />

For rice, three loci of Est1, Est2, and Est3 have been identified<br />

w<strong>here</strong> two, three, and two alleles are located, respectively.<br />

Two alleles in the Est1 locus produce the 1A band and null in<br />

electrophoresis, three alleles in the Est2 do 6A and 7A band<br />

and null, and two alleles in the Est3 do 12A and 13A band. All<br />

combinations of those alleles in the three loci produce 12 genotypes<br />

(Nakagahra and Hayashi 1977). Myanmar landraces are<br />

found to have 11 genotypes among them.<br />

In contrast to the amylose content of endosperm, genotypic<br />

frequencies of esterase isozymes were less varied among<br />

zones and no significant difference in genotypic frequency was<br />

observed among agroecological zones. The contrasting frequency<br />

distributions observed between amylose contents and<br />

esterase isozyme genotypes are considered greatly influenced<br />

by differences in effects of natural and/or artificial selection.<br />

Conclusions<br />

Myanmar has various social and cultural customs, complex<br />

topography, and different ethnic groups in its eight<br />

agroecological zones. The genetic diversity of rice landraces<br />

is thought to have been brought about by natural factors such<br />

as various topographic and climatic conditions and by different<br />

social and agricultural circumstances.<br />

58 <strong>Rice</strong> is life: scientific perspectives for the 21st century


45<br />

45<br />

40<br />

40<br />

WH<br />

35<br />

35<br />

n = 134<br />

30<br />

30<br />

25<br />

25<br />

20<br />

20<br />

15<br />

15<br />

10 10<br />

50 50<br />

NM<br />

n = 232<br />

NM<br />

45<br />

40<br />

35<br />

30<br />

25<br />

20<br />

15<br />

10<br />

5<br />

0<br />

WC<br />

n = 130<br />

WC<br />

WH<br />

SA<br />

EP<br />

45<br />

40<br />

35<br />

30<br />

25<br />

20<br />

15<br />

10<br />

5<br />

0<br />

EP<br />

n = 260<br />

45<br />

40<br />

35<br />

30<br />

25<br />

20<br />

15<br />

10<br />

5<br />

0<br />

SP<br />

n = 144<br />

AD<br />

SP<br />

SC<br />

45<br />

40<br />

35<br />

30<br />

25<br />

20<br />

15<br />

10<br />

5<br />

0<br />

SA<br />

n = 125<br />

45<br />

40<br />

35<br />

30<br />

25<br />

20<br />

15<br />

10<br />

5<br />

0<br />

0<br />

2<br />

AD<br />

n = 149<br />

4 8 12 16 20 24 28 32 36<br />

6 10 14 18 22 26 30 34 38<br />

45<br />

40<br />

35<br />

30<br />

25<br />

20<br />

15<br />

10<br />

5<br />

0<br />

40 0<br />

2<br />

SC<br />

n = 217<br />

4 8 12 16 20 24 28 32 36 40<br />

6 10 14 18 22 26 30 34 38<br />

No. of landraces<br />

180<br />

160<br />

140<br />

120<br />

100<br />

80<br />

60<br />

40<br />

20<br />

Myanmar<br />

n = 1,391<br />

0<br />

0<br />

2<br />

4<br />

6<br />

8<br />

10<br />

12<br />

14<br />

16<br />

18<br />

20<br />

22<br />

24<br />

26<br />

28<br />

30<br />

32<br />

34<br />

36<br />

38<br />

40<br />

Amylose content (%)<br />

Fig. 2. Regional variation in amylose content of endosperm starch in Myanmar rice landraces. WH = Western Hilly, NM = Northern<br />

Mountainous, EP = Eastern Plateau, SA = Semiarid, WC = Western Coastal, SC = Southern Coastal, SP = Southern Plain, and AD<br />

= Ayeyarwady Delta.<br />

Session 1: The genus Oryza, its diversity, and its evolution 59


<strong>Rice</strong> landraces in Myanmar show remarkable diversity<br />

in traits such as grain size and shape, plant type, etc., besides<br />

the characters investigated <strong>here</strong>. Their diversity is considered<br />

to result from adaptation to various natural and agroecological<br />

environments and to be caused by unconscious selection by<br />

farmers for several thousand years and by artificial selection<br />

applied through preference for different qualities and ingredients<br />

of rice grains.<br />

The diversity of genetic resources of Myanmar rice is<br />

expected to be very useful for domestic rice breeding in the<br />

future and an irreplaceable and valuable property for human<br />

beings from the global point of view. These resources are becoming<br />

rapidly eroded because of the extensive diffusion of<br />

improved high-yielding cultivars. We urgently need to collect<br />

and characterize rice landraces. T<strong>here</strong>fore, the Myanmar seed<br />

bank has collected and stored a number of them. These will be<br />

very useful genetic resources for future rice breeding but remain<br />

to be evaluated for useful agronomic traits.<br />

References<br />

FAO. 1987. Agro-climatologic data. FAO Plant Production and Protection<br />

Series, Rome.<br />

Glaszmann JC. 1987. Isozymes and classification of Asian rice varieties.<br />

Theor. Appl. Genet. 74:21-30.<br />

Nakagahra M, Hayashi KI. 1977. Origin of cultivated rice as detected<br />

by isozyme variations. JARQ 11:1-5.<br />

Nakagahra M, Akihama T, Hayashi KI. 1984. Geographical distribution<br />

of esterase genotypes of rice in Asia. <strong>Rice</strong> Genet. Newsl.<br />

1:118-120.<br />

Okuno K, Fuwa H, Yano M. 1983. A new mutant gene lowering<br />

amylase content in endosperm starch of rice. Jpn. J. Breed.<br />

33:387-394.<br />

Sato YI. 1991. Variation in spikelet shape of indica and japonica<br />

rice cultivars of Asian origin. Jpn. J. Breed. 41:121-134.<br />

Notes<br />

Authors’ addresses: Ye Tint Tun, K. Irie, F. Kikuchi, and H. Fujimaki,<br />

Tokyo University of Agriculture, 1-1-1 Sakuragaoka, Setagaya,<br />

Tokyo 156-8502, Japan, e-mail: tint@affrc.go.jp; Ye Tint Tun,<br />

Myanma Agriculture Service, Ministry of Agriculture and Irrigation,<br />

Yangon, Myanmar; T. Nagamine, National Agricultural<br />

<strong>Research</strong> Center for Western Region, Fukuyama,<br />

Hiroshima 721-8514, Japan; Jhon Ba Maw, Department of<br />

Agricultural <strong>Research</strong>, Ministry of Agriculture and Irrigation,<br />

Yezin, Myanmar.<br />

QTL analysis for eating quality in japonica rice<br />

H.G. Hwang, J.P. Suh, Y.C. Cho, S.J. Kwon, I.S. Choi, H.C. Hong, Y.G. Kim, M.K. Kim, H.C. Choi, and Y.T. Lee<br />

In Korea, the most important goal in japonica rice breeding is<br />

to improve the eating quality of cooked rice. The eating quality<br />

of rice is a complex characteristic whose many components<br />

are difficult to evaluate for selection in a rice breeding program.<br />

The quality of cooked rice has been examined by a sensory<br />

test. Recently, we have been using an indirect rapid evaluation<br />

method by detecting the glossiness of cooked rice for<br />

eating quality. However, this is difficult to apply for early-generation<br />

selection in the rice breeding program because of size<br />

constraints.<br />

The use of molecular markers has facilitated the understanding<br />

of quantitative trait loci (QTLs) and marker-assisted<br />

selection (MAS). Many QTL analyses for grain quality of rice<br />

have been reported (Bao et al 2002, Tan et al 1999, Wan et al<br />

2004, Zhou et al 2003). QTLs related to glossiness of cooked<br />

rice were identified at different loci in Ilpumbyeo—a highquality<br />

parent (Cho et al 2004, Lee 2003). In this study, we<br />

report on QTLs associated with physicochemical traits and<br />

eating quality by glossiness of cooked rice using a japonica ×<br />

japonica cross. Also, we evaluated the allelic effect of QTLs<br />

associated with glossiness of cooked rice in BC 3 F 1 and BC 4 F 2<br />

generations developed by MAS.<br />

Materials and methods<br />

Plant materials<br />

Suweon365 possesses medium eating quality and is highly resistant<br />

to blast. On the other hand, Chucheongbyeo is known<br />

for its good eating quality and susceptibility to leaf blast. A<br />

total of 231 recombinant inbred lines (RILs) derived from a<br />

cross between Suweon365 and Chucheongbyeo were developed<br />

using the single-seed descent method. The RIL population<br />

was field-evaluated by the National <strong>Institute</strong> of Crop Science,<br />

Suwon, for three years (1999 to 2001). To develop a<br />

series of QTL-NILs (near-isogenic lines), four desirable RILs<br />

carrying QTL segments for glossiness of cooked rice (GCR)<br />

from a Toyo taste meter value were successively backcrossed<br />

with Suweon365 for selection using linked markers until the<br />

BC 4 F 2 . The allele effect of QTLs related to GCR was evaluated<br />

in BC 3 F 1 and BC 4 F 2 generations.<br />

Chemical properties<br />

The amylose content of milled rice was determined by the relative<br />

absorbency of starch-iodine color in digested solution of<br />

100-mesh rice flour by the modified method of Juliano (1971).<br />

Protein content was calculated by total nitrogen multiplied by<br />

60 <strong>Rice</strong> is life: scientific perspectives for the 21st century


5.95 after determining the nitrogen content of rice material<br />

using the Micro-Kjeldahl method (Foss:2300 Kjeltec Analyzer).<br />

Gelatinization characteristics were evaluated using a<br />

Rapid Visco Analyser (model: RVA-3D) in accordance with<br />

the operation manual (NewPort Sci. Co., Australia).<br />

Glossiness of cooked rice (GCR)<br />

using a Toyo taste meter<br />

The glossiness of cooked rice was determined in two replications<br />

using a Toyo taste meter (model: MA-90A and 90B) in<br />

accordance with the operation manual (TRCM Co.). The whole<br />

rice grains of milled rice were separated from broken rice grains<br />

using a length grain separator of a Satake testing rice grader<br />

(Model: TGR 05A) of mesh size 3.6 mm for 2 min and a 33-g<br />

sample of whole grain was used.<br />

Linkage map construction and QTL analysis<br />

The linkage map was constructed with 236 markers of various<br />

origins such as SSRs, STS, AFLP, and MITE. The Mapmaker<br />

program was used to construct a molecular map at an LOD<br />

value of 3.0 and a maximum recombination fraction q = 0.40<br />

using the “group” command. QTL analysis was performed by<br />

one-way analysis of variance using the qGene v.3.06 program.<br />

An LOD score of 2.0 was used as the threshold for detecting<br />

QTLs.<br />

Results and discussion<br />

The correlation coefficients among seven chemical properties<br />

and GCR (Toyo taste meter value) were computed. T<strong>here</strong> was<br />

a high correlation (r ≥ 0.8) between GCR and the sensory evaluation<br />

for eating quality of cooked rice by panelists (data not<br />

shown, Lee 2003). GCR by the Toyo taste meter value showed<br />

a highly negative correlation with amylose and protein content,<br />

and a positive correlation with alkali digestion value. This<br />

result was similar to those of previous reports in japonica ×<br />

japonica (Lee 2003) and japonica × javanica crosses (Cho et<br />

al 2004). The eating quality of cooked rice can be evaluated<br />

indirectly based on GCR by the Toyo taste meter value instead<br />

of palatability score because the sensory test needs much time<br />

and labor from well-trained panelists.<br />

The polymorphism between Suweon365 and<br />

Chucheongbyeo was 16.3%, 4.8%, and 13.0% for SSR, STS,<br />

and AFLP markers, respectively. This result was similar to that<br />

of the cross between two Korean japonica cultivars (Lee 2003).<br />

The linkage map spanning 1,998 cM with an average interval<br />

size of 8.5 cM was constructed using 236 DNA markers. The<br />

distal region of the long arm on chromosome 2 showed only<br />

polymorphism and a map could be constructed of 8.1 cM by<br />

seven SSR markers. The coverages of chromosomes 1, 5, 6,<br />

and 10 were relatively poor. T<strong>here</strong> were big gaps in many regions<br />

of chromosomes 3, 4, 5, 8, 11, and 12. AFLP markers<br />

were not mapped evenly on all chromosomes, and were combined<br />

only on chromosomes 4, 7, 8, 10, 11, and 12.<br />

For chemical properties, gelatinization characteristics,<br />

and glossiness of cooked rice, 15 putative QTLs were identified.<br />

Three QTLs for alkali digestion value were located on<br />

chromosomes 6, 8, and 11. One QTL, qADV-6, was identified<br />

at the wx locus (RM190). A QTL, qPro-10, for protein content<br />

was identified near RM333 on chromosome 10. It was different<br />

from the one identified on chromosomes 1, 4, 5, 6, and 7<br />

by Hu et al (2004). A QTL, qGIT-11, for gelatinization temperature<br />

was identified in the same region (em2210) as qADV-<br />

11. Three QTLs for high viscosity, breakdown, and consistency<br />

were located in a cluster region (RM213–RM482) at the<br />

distal end of the long arm on chromosome 2. The QTLs for<br />

gelatinization characteristics in a DH population from japonica<br />

× indica were reported on chromosomes 1, 2, 3, 6, and 11 by<br />

Tian et al (2004). Five QTLs for amylose content, gel consistency,<br />

water absorption, cooked rice elongation, and volume<br />

expansion were identified near the wx locus. However, only<br />

one QTL for alkali digestion value in this mapping population<br />

was identified at the wx locus. The QTLs for GCR by the Toyo<br />

taste value were identified on chromosomes 3, 7S, 7L, 8, and<br />

11 (Fig. 1). These QTLs explained 7.1%, 10.6%, 8.8%, 8.9%,<br />

and 7.2% of the total phenotypic variation, respectively. A QTL<br />

for GCR was not detected repeatedly at the same locus in three<br />

years. In addition, QTLs were different from those from<br />

japonica × japonica (Lee 2003), japonica × javanica (Cho et<br />

al 2004), and japonica × indica (Ebitani et al 2002) crosses.<br />

They were also located at loci different from 13 QTLs affecting<br />

six palatability properties in japonica × indica (Wan et al<br />

2004) crosses. Traits related to grain quality appear to be influenced<br />

by ecotypes as well as by environment and cultural<br />

method.<br />

BC 3 F 1 and BC 4 F 2 lines developed by successive backcrossing<br />

with Suweon365 for four desirable RILs carrying four<br />

putative QTL segments for GCR, based on MAS, were evaluated<br />

for allele effect (Table 1). In the BC 3 F 1 generation, the<br />

lines having DNA markers close to the QTL showed an allelic<br />

effect of 2.5 for qGCR-7.1, 1.6 for qGCR-7.2, 2.1 for qGCR-<br />

8, and 4.1 for qGCR-11, contributed by Chucheongbyeo. In<br />

the BC 4 F 2 generation, the lines homozygous for the<br />

Chucheongbyeo allele had an allelic effect of 1.1 for qGCR-<br />

7.1, 2.7 for qGCR-7.2, 1.9 for qGCR-8, and 1.0 for qGCR-11.<br />

Although the allelic effect was not statistically significant, all<br />

lines having QTLs from Chucheongbyeo for GCR from the<br />

Toyo taste meter value increased the value of glossiness of<br />

cooked rice vis-à-vis the lines with the Suweon365 allele. It is<br />

difficult to evaluate the dosage effect for QTLs because the<br />

values of Chucheongbyeo homozygotes were not always as<br />

high as those of the heterozygous lines (Table 1). The allelic<br />

effect of QTLs associated with GCR was lower because the<br />

parents used to develop genetic material had a similar japonica<br />

genetic background. These results will be helpful for developing<br />

effective breeding selection for grain quality of japonica<br />

rice. In the future, we will try to evaluate the effect of QTL<br />

pyramiding associated with the glossiness of cooked rice.<br />

Session 1: The genus Oryza, its diversity, and its evolution 61


Chr. 7<br />

Chr. 8<br />

Chr. 11<br />

qGCR-7-1<br />

3.2 cM<br />

RM481<br />

RM180<br />

RM214<br />

RM500<br />

em623<br />

em723<br />

em724<br />

em127<br />

em225<br />

em525<br />

em524<br />

em425<br />

em424<br />

1031R25<br />

1031R08<br />

RM320<br />

RM560<br />

OSR22<br />

qGCR-8<br />

3.8 cM<br />

qADV-8<br />

qHV-8<br />

em2211<br />

RM547<br />

RM72<br />

em445<br />

em145<br />

RM044<br />

RM404<br />

em5211<br />

em429<br />

em4210<br />

em7210<br />

em123<br />

em522<br />

RM342A<br />

RM342B<br />

qGCR-11<br />

8.6 cM<br />

qGIT-11<br />

qADV-11<br />

1031R37<br />

OSR01<br />

RM20B<br />

RM332<br />

RM552<br />

em1217<br />

em7215<br />

em429<br />

em2210<br />

em4214<br />

RM229<br />

RM021<br />

RM206<br />

em426<br />

qGCR-7-2<br />

4.2 cM<br />

RM342D<br />

em443<br />

em243<br />

em143<br />

RM346<br />

RM182<br />

OSR04<br />

RM336<br />

RM070<br />

em529<br />

em738<br />

em1210<br />

em1211<br />

em428<br />

em229<br />

em627<br />

dasng04<br />

RM505<br />

em864<br />

RM473a<br />

RM234<br />

RM515<br />

1031R28<br />

RM281<br />

RM264<br />

em812<br />

em427<br />

em726<br />

em129<br />

em526<br />

em442<br />

RM144<br />

em242<br />

dasng08<br />

1031R23<br />

RM47<br />

RM478<br />

Fig. 1. Chromosomal location of QTLs associated with glossiness of cooked rice. qGCRs are QTLs for glossiness of cooked rice<br />

from the Toyo taste meter.<br />

References<br />

Bao JS, Wu YR, Hu B, Wu P, Cui HR, Shu QY. 2002. QTL for rice<br />

grain quality based on a DH population derived from parents<br />

with similar apparent amylose content. Euphytica 128:317-<br />

324.<br />

Cho YC, Hong HC, Suh JP, Jeong YP, Choi IS, Kim MK, Kim YG,<br />

Choi HC, Hwang HG. 2004. QTL mapping for grain quality<br />

and shape in japonica × javanica in rice. Korean J. Breed.<br />

36(Suppl. 1):408-409.<br />

Ebitani T, Umemoto T, Yano M. 2002. QTL analysis of “Mido” value,<br />

an inbreed selection index for eating quality of rice, using<br />

progenies from a cross between japonica and indica variety.<br />

Breed. Sci. 52(Suppl. 1):371.<br />

Hu ZL, Li P, Zhou MQ, Zhang ZH, Wang LX, Zhu LH, Zhu YG.<br />

2004. Mapping of quantitative trait loci (QTLs) for rice protein<br />

and fat content using doubled haploid lines. Euphytica<br />

135:47-54.<br />

Juliano BO. 1971. A simplified assay for milled rice amylose. Cereal<br />

Sci. Today 16:334-338, 340, 360.<br />

62 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. Allelic effect of QTLs for glossiness of cooked rice by Toyo taste value in BC 3 F 1 and BC 4 F 2<br />

generations.<br />

Glossiness of cooked rice by Toyo taste value<br />

QTLs Chr. Markers BC 3 F 1 (2003) BC 4 F 2 (2004)<br />

Hetero Homo Allelic Homo Hetero Homo Allelic<br />

of CS a of SS effect b of CC of CS of SS effect<br />

qGCR7.1 7S RM214-RM500 64.8 62.3 2.5 69.3 69.3 68.2 1.1<br />

qGCR7.2 7L RM234-RM47 65.9 64.3 1.6 68.8 67.5 66.1 2.7<br />

qGCR8 8 RM547-RM72 67.6 64.3 2.1 66.1 67.1 64.2 1.9<br />

qGCR11 11 RM20B-RM332 66.1 63.5 4.1 68.4 67.4 67.4 1.0<br />

Chucheongbyeo (donor) 72.2 71.4<br />

Suweon365 (recurrent) 65.4 64.1<br />

a Homo of CC: one band for Chucheongbyeo; hetero of CS: two bands of Chucheongbyeo and Suweon365; homo of SS: one band<br />

for Suweon365. b Allelic effects in BC 3 F 1 and BC 4 F 2 are the value of CS-SS and CC-SS, respectively.<br />

Lee JS. 2003. QTL analysis for grain quality properties in a japonica<br />

rice combination. Ph.D. thesis. Yeungnam University, Korea.<br />

64 p.<br />

Tan YF, Li JX, Yu SB, Xing YZ, Xu CG, Zhang Q. 1999. The three<br />

important traits for cooking and eating quality of rice grains<br />

are controlled by a single locus in an elite rice hybrid, Shanyou<br />

63. Theor. Appl. Genet 99:642-648.<br />

Tian R, Jiang GH, Shen LH, Wang LQ, He YQ. 2004. Mapping quantitative<br />

trait loci underlying the cooking and eating quality of<br />

rice using a DH population. Mol. Breed., on-line, accessed<br />

on 30 Sept. 2004.<br />

Wan XY, Wan JM, Su CC, Wang CM, Shen WB, Li JM, Wang HL,<br />

Jiang L, Liu SJ, Chen LM, Yasui H, Yoshimura A. 2004. QTL<br />

detection for eating quality of cooked rice in a population of<br />

chromosome segment substitution lines. Theor. Appl. Genet.,<br />

on-line, 10.1007/s00122-004-1744-3.<br />

Zhou PH, Tan YF, He YQ, Xu CG, Zhang Q. 2003. Simultaneous<br />

improvement for four quality traits of Zhenshan 97, an elite<br />

parent of hybrid rice, by molecular marker-assisted selection.<br />

Theor. Appl. Genet. 106:326-331.<br />

Notes<br />

Authors’ addresses: H.G. Hwang, J.P. Suh, Y.C. Cho, I.S. Choi, H.C.<br />

Hong, Y.G. Kim, M.K. Kim, H.C. Choi, Y.T. Lee, National<br />

<strong>Institute</strong> of Crop Science, RDA, Suwon 441-857, Republic of<br />

Korea; S.J. Kwon, National <strong>Institute</strong> of Agricultural Biotechnology,<br />

RDA, Suwon 441-857, Korea, e-mail:<br />

yccho@rda.go.kr.<br />

Session 1: The genus Oryza, its diversity, and its evolution 63


SESSION 2<br />

Structure and function of the rice genome<br />

CONVENER: T. Sasaki (NIAS)<br />

CO-CONVENERS: H. Hirochika (NIAS) and H. Leung (<strong>IRRI</strong>)


The complete rice genome sequence<br />

and its application to breeding and genetics<br />

Takuji Sasaki<br />

<strong>Rice</strong> is one of the main staples in the world and is cultivated<br />

mainly in Asia, Africa, and Latin America using irrigated and<br />

upland ground for paddy fields. The major limiting factors for<br />

rice cultivation are climate, soil, and water. Except for the<br />

upland rice in Africa, rice plants grow mainly in tropical and<br />

semitropical areas characterized by a rainy season. The wild<br />

relatives of cultivated rice, Oryza sativa, are also widely distributed<br />

within nearly 20° north and south latitude (<strong>IRRI</strong> 2004).<br />

Archaeological evidence suggested that rice cultivation began<br />

about 10,000 years ago in southern China, with wild rice as<br />

the main resource. Although the exact origin of both O. sativa<br />

subsp. indica and subsp. japonica is still unknown, rice has<br />

been well domesticated even in such a “short” period and rice<br />

cultivation has become widespread, extending to 40° north and<br />

south latitude. The domestication of rice is undoubtedly one<br />

of the most important developments in human history and, at<br />

present, about half of the world population relies on rice for<br />

its daily main food source.<br />

Despite the long history of breeding and improvement<br />

of rice varieties adapted to a wide range of environmental conditions<br />

as well as varieties highly preferred by both farmers<br />

and consumers, novel rice varieties are still necessary to meet<br />

the demands of increasing population pressure coupled with<br />

decreasing resources for rice production. In addition, varieties<br />

with tolerance of biotic and abiotic stress, and high yield as<br />

well as good nutritional and cooking quality, will always be<br />

targeted by breeders and farmers. The breeding strategy used<br />

so far for developing new varieties is based on the selection of<br />

desirable phenotypes among progenies generated after crossing<br />

elite varieties. Since most agronomic traits are composed<br />

of more than two genes and, in extreme cases, ten to 15 genes,<br />

this strategy is similar to a “hit or miss” approach, making it<br />

extremely difficult to select the most preferable allele for each<br />

of the genes corresponding to a phenotype. We must be innovative<br />

in improving our rice breeding strategy for such complex<br />

traits mainly contributed to farming and agribusiness by<br />

introducing up-to-date scientific knowledge.<br />

Recent advances in molecular biology made it possible<br />

to acquire extensive knowledge of rice genetics such as the<br />

fundamental factors of <strong>here</strong>dity and the nucleotide sequence<br />

of the genome. In Japan, the Ministry of Agriculture, Forestry,<br />

and Fisheries (MAFF) started the rice genome project in 1991<br />

with the aim of analyzing the structure of the rice genome,<br />

understanding the rice plant based on its genetic composition,<br />

and using the information for innovative rice breeding strategies.<br />

From 1998, the project has served as a launching pad for<br />

sequencing the entire genome through international coordination<br />

and elucidating its function based on this information both<br />

genetically and reverse-genetically (NIAS 2004a, Sasaki 1998).<br />

This paper focuses on the rice genome sequencing efforts, with<br />

emphasis on the analysis and utility of the genome sequence in<br />

the future.<br />

How to sequence and decode the information of <strong>here</strong>dity<br />

The term “genome” refers to the total genetic information that<br />

defines a species. The size of the genome corresponds to the<br />

amount of nucleotide that comprises half of the chromosome<br />

pairs or haploid. This can be experimentally measured by flow<br />

cytometry and expressed as a nuclear C-value. The genome<br />

size of rice with 12 chromosomes has been estimated to be<br />

430 Mb (Royal Botanic Gardens 2004). <strong>Rice</strong> has the smallest<br />

genome size when compared with other major cereal crops<br />

such as maize, with 2,500 Mb, and wheat, with 16,000 Mb.<br />

However, even with the most advanced method of nucleotide<br />

sequencing, the size of rice is not an easy target for complete<br />

sequencing with high accuracy. In the case of rice, it is also<br />

important to assign the location of the sequence to its genomic<br />

position so that the information can be directly useful to breeders.<br />

This approach in sequencing analysis facilitates the identification<br />

of gene function by forward and reverse genetics and<br />

comparison of specific phenotypes among rice varieties based<br />

on the difference in nucleotide sequence. This is extremely<br />

important considering that t<strong>here</strong> are about 120,000 rice varieties<br />

worldwide and each variety is characteristically defined by<br />

the nucleotide sequences. Thus, an accurate and exact standard<br />

genome sequence is indispensable for subsequent goals<br />

in rice genomics.<br />

The rice genome sequencing effort has been an international<br />

collaboration since 1998. The <strong>International</strong> <strong>Rice</strong> Genome<br />

Sequencing Project (IRGSP) is currently composed of<br />

10 participating countries, led by Japan (Sasaki and Burr 2000,<br />

NIAS 2004b). A clone-by-clone sequencing strategy using a<br />

standard japonica rice variety, Nipponbare, has been adopted.<br />

Although each country’s contribution differs, each group has<br />

made significant progress in decoding the rice genome sequence.<br />

Japan has contributed in sequencing 55% of the entire<br />

genome, or an equivalent of 220 Mb genome sequence. In<br />

December 2002, the IRGSP finished the high-quality draft sequence<br />

of the entire genome, which is now available in public<br />

databases. It is expected that by December 2004 the entire<br />

Nipponbare genome, covered by nearly 3,400 BAC (bacterial<br />

artificial chromosome) and PAC (P1-derived artificial chromosome)<br />

clones, will be sequenced with 99.99% accuracy<br />

without any sequence gap. The genomic positional assignment<br />

of tiled BAC and PAC clones has been established based on<br />

66 <strong>Rice</strong> is life: scientific perspectives for the 21st century


genetically mapped DNA markers prior to the launching of<br />

the genome sequencing project so that every genome sequence<br />

can be associated with a specific position on the genetic map.<br />

Several genomic regions with highly repetitive sequence or<br />

unstable structure in host bacteria have not yet been completely<br />

sequenced. So far, only the centromeres of three chromosomes<br />

have been completely covered by BAC or PAC clones, with<br />

the centromeres of chromosomes 8 and 4, respectively, being<br />

completely sequenced (Wu et al 2004, Zhang et al 2004).<br />

Characteristics of the rice genome<br />

The most frequently asked and reasonable question refers to<br />

the total number of genes within the rice genome. To precisely<br />

predict the gene composition of rice, we need sufficient statistical<br />

data to fit the parameters used by prediction programs<br />

such as those constructed based on a hidden Markov model.<br />

The most useful evidence for gene prediction is the full-length<br />

cDNA sequence with information on the start and stop codons<br />

without interruption, and which, in correspondence to the genome<br />

sequence, can provide statistical information on nucleotide<br />

sequence at splice sites. Several prediction programs have<br />

been developed using various plant genome sequences. For<br />

rice, the FGENESH prediction program has been used for the<br />

analysis of the total number of genes and modeling of gene<br />

structure. Excluding transcripts of transposable elements, a total<br />

of 45,000 protein-coding sequences have been predicted at an<br />

average density of one gene per 8,200 bp. Chromosomes 1<br />

and 3 appear to be the most gene-rich chromosomes, w<strong>here</strong>as<br />

chromosome 12 is relatively gene-poor.<br />

The entire genome sequence has revealed many structural<br />

features of the rice genome. Tandem gene duplications<br />

have been widely observed among the 12 chromosomes. A dot<br />

matrix plot of all the predicted genes with significant homology<br />

to a given gene showed a clear diagonal line, indicating<br />

that a significant number of genes are duplicated and arrayed<br />

in tandem (Sasaki et al 2002). Although t<strong>here</strong> is not yet enough<br />

evidence of actual expression of each member of these genes,<br />

several duplicated genes have been captured as cDNAs or ESTs<br />

in many cases. Such a high degree of gene multiplication as<br />

observed in the rice genome has not been observed in any species<br />

so far sequenced, including the model dicot plant<br />

Arabidopsis thaliana. For the human genome, the number of<br />

genes is lower than the total number of transcripts because of<br />

frequent alternative splicing for one gene. This mechanism may<br />

be an adaptive mechanism to increase the repertoire of gene<br />

product corresponding to a different signal for transcription to<br />

the same gene. In contrast, a high degree of gene multiplication<br />

in the rice genome may be essential to prepare various<br />

gene sets for a similar transcript, as shown by the low frequency<br />

of alternative splicing in the rice genome using the<br />

information from rice full-length cDNAs. Further study on<br />

promoter analysis must elucidate how and when each of the<br />

multiplied similar genes is expressed to function and in which<br />

tissue of the rice plant.<br />

How to use sequence information in the future<br />

Currently, forward and reverse genetics methods have been<br />

widely used to identify specific genes corresponding to phenotypes.<br />

The reverse genetics method facilitates the mutation<br />

of genes to analyze the resulting phenotype. It is systematically<br />

applicable to a genome-wide survey of disrupted position<br />

by referring to the genome sequence. Some of the most<br />

commonly used biological factors for gene disruption include<br />

T-DNA from Agrobacterium tumefaciens and Ac/Ds from<br />

maize. In Arabidopsis, many mutants have been generated and<br />

the corresponding genes have been identified using this method.<br />

Both factors are being widely used for rice, mainly in countries<br />

such as Korea, China, France, and the United States.<br />

However, mutated rice plants using these factors are considered<br />

as recombinant plants. Because of strict regulations in<br />

Japan concerning transgenic plants, an alternative biological<br />

factor based on endogenous retrotransposon Tos17 is widely<br />

used. Tos17 is activated only by a stress such as tissue culture<br />

conditions for 3–5 months and the Tos17 transposed into 5–10<br />

new loci is stably harbored t<strong>here</strong> (Hirochika 2001). If this transposed<br />

Tos17 occasionally disrupts the open reading frame, regenerated<br />

rice plants will show mutation in the phenotype. <strong>Rice</strong><br />

plants with transposed Tos17 are not recombinant plants and<br />

can be cultivated as normal plants. This makes Tos17 a very<br />

efficient tool for gene-disruption studies in Japan. For screening<br />

of the disrupted sequence by Tos17, sequences flanking<br />

inserted Tos17 are collected in a database. Currently, nearly<br />

42,000 flanking sequences of 4,300 mutant lines have been<br />

analyzed (Miyao et al 2003). These sequences have been assigned<br />

to the genome sequence and it has been shown that<br />

Tos17 prefers disruption of the exon region instead of intron<br />

and intergenic regions. However, the distribution of disrupted<br />

regions is not even within the genome. This result suggests the<br />

necessity of using other complementary factors such as T-DNA<br />

and Ac/Ds for complete disruption of all rice genes.<br />

Forward genetics provides a procedure to identify and<br />

select individuals that possess a phenotype of interest. It normally<br />

depends on mutants of phenotype, which are generated<br />

intentionally by physical factors such as irradiation by gamma<br />

ray or fast neutrons; chemical agents such as N-methyl-Nnitrosourea;<br />

biological factors such as Tos17, T-DNA, and Ac/<br />

Ds; or unintentionally by unknown spontaneous factors. The<br />

major principle that led to gene identification using these mutants<br />

is based on precise genetic analysis by DNA markers,<br />

which have been developed from the genome sequence information.<br />

As a result, the map-based cloning strategy has advanced<br />

significantly because of the rapid progress of genome<br />

sequencing, t<strong>here</strong>by facilitating accurate detection of polymorphism<br />

even at a single nucleotide level. This strategy has led<br />

to the identification of a particular gene corresponding to mutation<br />

caused by a single gene. Many important genes such as<br />

genes with resistance to rice bacterial blight, Xa1 and Xa21,<br />

genes with resistance to rice blast disease, Pib and Pita, and<br />

genes corresponding to grass height, d1, gid2, slr1, and sd1,<br />

have been identified by map-based cloning. However, almost<br />

Session 2: Structure and function of the rice genome 67


all of the traits that are important for rice breeding are not<br />

controlled by a single gene. Instead, they are controlled by<br />

many genes known as quantitative trait loci or QTLs, and the<br />

phenotypes result from a complex mechanism of interaction<br />

of the gene products of these genes. QTL mapping is performed<br />

by the interval mapping method and the location of the QTL is<br />

shown as a score of probability, LOD. Recent progress in genetic<br />

analysis of QTLs using chromosomal substitution lines<br />

(CSL) evaluated by DNA markers has made it possible to isolate<br />

each QTL as a single Mendelian factor and to further identify<br />

the corresponding gene by map-based cloning. This strategy<br />

has been applied for the identification of genes of QTLs<br />

for rice heading date or flowering time. Among 14 QTLs of<br />

heading date in rice, four have been successfully identified<br />

(Yano et al 2001).<br />

Many biological processes that have not yet been characterized<br />

at the molecular level can now be reanalyzed using<br />

the genome sequence. It has been widely presumed that continuous<br />

variation in phenotypes can be attributed to the variation<br />

of corresponding alleles. However, no molecular tools are<br />

available to clarify the differences that could be useful for developing<br />

novel strategies in improving specific phenotypes.<br />

At present, the identification of genes involved in QTLs involves<br />

a thorough understanding of the difference of nucleotide<br />

sequence conferring the difference in degree of function<br />

as well as obtaining the fundamental information on the gene<br />

network expressed as a complex trait. The former can be attributed<br />

to the contribution of natural variation of nucleotide<br />

sequences in the corresponding member genes involved in<br />

QTLs. Natural variations derived from wild relatives of cultivated<br />

rice, which have remained in the genome after subsequent<br />

selection during the breeding process, are indispensable<br />

resources to identify more favorable traits for rice improvement.<br />

The gene network associated with the expression of the<br />

QTL must be elucidated to clarify the physiological and biochemical<br />

processes regarding the target QTL. If we could find<br />

out a meaningful nucleotide difference for phenotype, this information<br />

would be indispensable for marker-assisted selection<br />

and screening of germplasm, including elite breeding lines.<br />

The standard rice genome sequence will provide the major<br />

source of information to attain this goal.<br />

Future use of the genome sequence will also rely on an<br />

efficient informatics infrastructure. <strong>Rice</strong> genomics data are currently<br />

increasing exponentially day by day because of the increase<br />

in the number of rice genomics researchers encouraged<br />

by the availability of an accurate rice genome sequence. This<br />

means that rice genome databases should evolve from a storehouse<br />

for thousands of bases or amino acids to a “workhouse”<br />

attaching substantial information to the sequence. These databases<br />

should t<strong>here</strong>fore provide the framework to allow<br />

postsequencing analysis such as identifying genes and predicting<br />

the proteins they encode, determining when and w<strong>here</strong> the<br />

genes are expressed, and how they interact under each specified<br />

condition. To satisfy these demands, it is necessary to link<br />

the resources of various types of information. In addition, this<br />

information must be closely linked to available genetic resources<br />

for further research.<br />

Comparative genomics<br />

The complete genome sequence will be useful for comparing<br />

genomes at both the intraspecific and interspecific level. Colinearity<br />

of genes has been widely studied between the genomes<br />

of japonica rice and indica rice, among the different species of<br />

Oryza, and also among different cereals representing different<br />

genera. To understand the cultivated rice plant, O. sativa, comparison<br />

with its wild relatives such as O. rufipogon or O. barthii<br />

is indispensable. Comparative analysis of the genome sequence<br />

such as with single nucleotide polymorphism and insertion/<br />

deletion, the number and types of inserted transposable elements,<br />

and the degree of duplication of specified genes will<br />

provide important insights into why and how currently cultivated<br />

rice species arose from their wild relatives. Among the<br />

wild relatives, tetraploid Oryza species exist. The cultivated<br />

rice O. sativa is a nearly pure diploid, although several genomic<br />

regions have been revealed to be duplicated. Polyploidy<br />

is often observed in cultivated plant species because it is<br />

advantageous in getting more yield than the diploid. Bread<br />

wheat is the most famous case and sugarcane is also known<br />

for its high polyploidy. Until now, no molecular information<br />

on the factor inducing polyploidy is available. Comparative<br />

analysis based on bioinformatic analysis of genome sequence<br />

data on several Oryza species will provide fundamental information<br />

on how polyploidy of a genome could be introduced<br />

under cultivation pressure. If we can control the ploidy of the<br />

rice genome, an increase in yield might be attained much more<br />

easily than pinpoint modification of target sequences.<br />

Conclusions<br />

<strong>Rice</strong> genome analysis is a relatively young science similar to<br />

the genome analysis of other species such as humans. However,<br />

because of rapid progress and technological innovations,<br />

a lot of new molecular resources and tools such as molecular<br />

markers for precise genetic mapping and a high-quality genome<br />

sequence for comprehensive molecular analysis of genome<br />

structure and function have already become available<br />

for rice. What is needed next is a collection of genetic resources<br />

for applying the molecular tools for further identification of<br />

useful alleles. With the completion of a high-quality genome<br />

sequence of rice, it would be possible to explore the diversity<br />

among different rice varieties. Diversity within the genomic<br />

component is very important for finding new alleles for breeding<br />

novel varieties and for understanding the rice plant based<br />

on differences in nucleotide sequences among Oryza species<br />

and among the members of the Gramineae. After the divergence<br />

from the common ancestral species, about 60 million<br />

years ago, Oryza species as well as Zea and Hordeum species<br />

have evolved as unique cereal crops. A thorough understanding<br />

of the similarities and differences in genome structure, gene<br />

68 <strong>Rice</strong> is life: scientific perspectives for the 21st century


structure, and their functional organization could provide the<br />

key to maintaining a close balance between cereal production<br />

and world food security.<br />

References<br />

Hirochika H. 2001. Contribution of the Tos17 retrotransposon to<br />

rice functional genomics. Curr. Opin. Plant Biol. 4:118-122.<br />

<strong>IRRI</strong> (<strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>). 2004.<br />

www.knowledgebank.irri.org/wild<strong>Rice</strong>Taxonomy/default.htm.<br />

Miyao A, Tanaka K, Murata K, et al. 2003. Target site specificity of<br />

the Tos17 retrotransposon shows a preference for insertion<br />

within genes and against insertion in retrotransposon-rich regions<br />

of the genome. Plant Cell 15:1771-1780.<br />

NIAS (National <strong>Institute</strong> of Agrobiological Sciences). 2004a.<br />

www.nias.affrc.go.jp/project/inegenome_e/zenenki/<br />

zenenki_outlook_e.htm.<br />

NIAS (National <strong>Institute</strong> of Agrobiological Sciences). 2004b. http:/<br />

/rgp.dna.affrc.go.jp/IRGSP/.<br />

Royal Botanic Gardens. 2004. www.rbgkew.org.uk/cval/<br />

introduction.html.<br />

Sasaki T. 1998. The rice genome project in Japan. Proc. Natl. Acad.<br />

Sci. USA 95:2027-2028.<br />

Sasaki T, Burr B. 2000. <strong>International</strong> <strong>Rice</strong> Genome Sequencing<br />

Project: the effort to completely sequence the rice genome.<br />

Curr. Opin. Plant Biol. 3:138-141.<br />

Sasaki T, Matsumoto T, Yamamoto K, et al. 2002. The genome sequence<br />

and structure of rice chromosome 1. Nature 420:312-<br />

316.<br />

Wu J, Yamagata H, Hayashi-Tsugane M, et al. 2004. Composition<br />

and structure of the centromeric region of rice chromosome<br />

8. Plant Cell 16:967-976.<br />

Yano M, Kojima S, Takahashi Y, Lin H-X, Sasaki T. 2001. Genetic<br />

control of flowering time in rice, a short-day plant. Plant<br />

Physiol. 127:1425-1429.<br />

Zhang Y, Huang Y, Zhang L, et al. 2004. Structural features of the<br />

rice chromosome 4 centromere. Nucleic Acids Res. 32:2023-<br />

2030.<br />

Notes<br />

Author’s address: <strong>Rice</strong> Genome <strong>Research</strong> Program, NIAS/STAFF,<br />

1-2, Kannondai 2-chome, Tsukuba, Ibaraki 305-8602, Japan,<br />

e-mail: tsasaki@nias.affrc.go.jp.<br />

Acknowledgment: The program for rice genome research (<strong>Rice</strong> Genome<br />

Project GS-1101, 1102, 1103, 1201, 1301, and 1302) is<br />

supported by the Ministry of Agriculture, Forestry, and Fisheries<br />

(MAFF) of Japan. The <strong>Rice</strong> Genome <strong>Research</strong> Program<br />

(RGP) is a joint collaboration of the National <strong>Institute</strong> of<br />

Agrobiological Sciences (NIAS) and the <strong>Institute</strong> of the Society<br />

for Techno-innovation of Agriculture, Forestry, and Fisheries<br />

(STAFF).<br />

Exploitation and use of naturally occurring allelic variations<br />

in rice<br />

Masahiro Yano, Yasunori Nonoue, Tsuyu Ando, Ayahiko Shomura, Takehiko Shimizu, Izumi Kono, Saeko Konishi,<br />

Utako Yamanouchi, Tadamasa Ueda, Shin-ichi Yamamoto, and Takeshi Izawa<br />

Over the last decade, a tremendous amount of progress has<br />

been made in rice genome analysis, including in whole-genome<br />

sequencing (Sasaki 2003). This progress has provided powerful<br />

tools—DNA markers—for plant genetics and breeding.<br />

DNA markers have been used in the genetic analysis of agronomically<br />

important traits, such as disease and pest resistance,<br />

plant height, and grain quality. Many phenotypic traits of economic<br />

interest are controlled by naturally occurring allelic<br />

variations and environmental conditions. These traits often<br />

show complex and quantitative inheritance. Recent progress<br />

in rice genomics has had a large impact on our understanding<br />

of such complex traits. DNA markers are used in the genetic<br />

analysis of quantitative traits, such as heading date, environmental<br />

stress tolerance, and yield-related traits. This markerassisted<br />

approach has also made it possible to exploit hidden<br />

genetic factors contributing to the improvement of traits with<br />

agronomic importance and to clone genes involved in such<br />

complex traits at the molecular level (Yano 2001). Tightly<br />

linked DNA markers or causal genes can be used in markerassisted<br />

selection (MAS) in breeding programs. The advent of<br />

DNA markers has allowed us to practice MAS in rice breed-<br />

ing. This paper describes our recent progress in the markerassisted<br />

genetic and molecular dissection of several complex<br />

traits and our efforts to develop plant materials that are, or will<br />

be, valuable in the analysis of complex traits in rice.<br />

Genetic and molecular dissection of complex traits in rice<br />

Flowering time (heading date)<br />

Flowering time is a major determinant of the regional and seasonal<br />

adaptation of rice cultivars and is one of the important<br />

traits in breeding programs. Analysis of natural allelic variation<br />

has contributed significantly to the exploration of genes<br />

involved in flowering time in rice. In quantitative trait locus<br />

(QTL) analysis, 15 QTLs for heading date have been detected<br />

genetically by using different types of progeny derived from a<br />

cross between Nipponbare and Kasalath (Yano et al 2001).<br />

Near-isogenic lines (NILs) for each QTL have also been developed<br />

by successive backcrossing and MAS. Consequently,<br />

eight QTLs have been mapped as single Mendelian factors by<br />

using advanced backcross progeny (Yano et al 2001). Furthermore,<br />

four QTLs (Hd1, Hd3a, Hd5, and Hd6) have been cloned<br />

Session 2: Structure and function of the rice genome 69


y map-based strategies (Yano et al 2000, Takahashi et al 2001,<br />

Kojima et al 2002, Yamanouchi et al, unpublished data). Recently,<br />

two additional QTLs, Ehd1 (Doi et al 2004) and Lhd4<br />

(N. Kitazawa et al, unpublished data), have been identified by<br />

using different cross combinations. The series of studies on<br />

heading date clearly demonstrated that complex traits could<br />

be dissected not only genetically, but also at a molecular level<br />

(Izawa et al 2003).<br />

Seed dormancy and longevity<br />

Seed dormancy is an important trait because it affects resistance<br />

to preharvest sprouting. Seed dormancy has also been<br />

analyzed by marker-assisted genetic approaches. Five putative<br />

QTLs affecting seed dormancy have been detected on<br />

chromosomes 3, 5, 7 (2 regions), and 8 by using backcross<br />

inbred lines (BILs) derived from a backcross of Nipponbare/<br />

Kasalath//Nipponbare (Lin et al 1998). QTLs for seed dormancy<br />

(Sdr1) and heading date (Hd8) have been mapped to<br />

approximately the same region on chromosome 3 (Lin et al<br />

1998). To clarify whether Sdr1 and Hd8 could be dissected<br />

genetically, we carried out fine mapping by using advanced<br />

backcross progeny. As a result, Sdr1 and Hd8 were mapped to<br />

different loci. We thus successfully dissected two tightly linked<br />

QTLs by a marker-based approach (Takeuchi et al 2003). In<br />

addition, QTLs controlling seed longevity were identified by<br />

using 98 BILs derived from a cross between japonica cultivar<br />

Nipponbare and indica cultivar Kasalath. Three putative QTLs<br />

(qLG-2, qLG-4, and qLG-9) were detected on chromosomes<br />

2, 4, and 9, respectively (Miura et al 2002). Kasalath alleles<br />

increased seed longevity in these QTLs. Among the QTLs detected,<br />

qLG-9 has exhibited large effects on longevity.<br />

Cool-temperature tolerance<br />

Cool temperatures at the booting stage often cause an increase<br />

in the number of aborted microspores, eventually resulting in<br />

decreased rice yield. To identify the chromosomal regions controlling<br />

cool-temperature tolerance at the booting stage in rice,<br />

we performed QTL analysis with doubled-haploid lines derived<br />

from crosses between two temperate japonica cultivars,<br />

Akihikari (moderately cool-temperature sensitive) and<br />

Koshihikari (cool-temperature tolerant). Three QTLs were<br />

mapped on each of chromosomes 1, 7, and 11. For each QTL,<br />

alleles from Koshihikari increased the degree of cool-temperature<br />

tolerance (Takeuchi et al 2001). One major QTL, qCT-7,<br />

has been mapped as a single Mendelian factor, and positional<br />

cloning of qCT-7 has been progressing (Ueda et al, unpublished<br />

data).<br />

Exploitation of natural allelic variations<br />

Plant materials for the exploitation of genes<br />

with agricultural importance<br />

Sequencing of the entire rice genome has progressed greatly<br />

(Sasaki 2003). This achievement has contributed to the molecular<br />

analysis of complex traits, as mentioned above. Although<br />

sequence information and molecular tools have already<br />

been rapidly accumulated, plant materials for genetic analysis<br />

are still being developed because material development usually<br />

requires a long time and much labor. Thus, a lack of genetic<br />

materials would limit our comprehensive understanding<br />

of quantitative traits.<br />

In general, primary mapping populations, such as F 2 and<br />

recombinant inbred lines (RILs), are used for the detection of<br />

QTLs. QTLs with relatively large effects can be detected in<br />

the genetic analysis of primary mapping populations. However,<br />

some QTLs with minor effects and those with epistatic<br />

interactions with other loci might not be detected in QTL analysis<br />

(Yano and Sasaki 1997). These QTLs can be detected by<br />

using advanced backcross progeny. Even though QTLs of interest<br />

can be identified by using existing primary mapping<br />

populations, further development of NILs is required for fine<br />

mapping and cloning of QTLs. Development of these materials<br />

is laborious and time-consuming. This problem has prevented<br />

many researchers from performing map-based cloning<br />

of QTLs as a more general strategy in plant molecular genetics.<br />

To solve these problems, novel mapping populations—<br />

chromosome segment substitution lines (CSSLs) or introgression<br />

lines (ILs)—have been developed in rice (Fig. 1). In the<br />

CSSLs, a particular chromosome segment from a donor line is<br />

substituted in the genetic background of the recurrent line. The<br />

substituted segments cover all chromosomes in a whole set of<br />

lines (Fig. 1). These materials allow detailed and reliable QTL<br />

analyses. CSSLs have been developed on the basis of several<br />

cross-combinations and will be developed from crosses within<br />

the cultivated species, Oryza sativa (Table 1).<br />

The use of wild relatives as donor parents would be a<br />

more powerful way to exploit a wide range of allelic variations<br />

because they are adapted to specific environmental conditions,<br />

and variations in genes give advantages for adaptation.<br />

Many wild relatives exist in the O. sativa complex: seven<br />

species have been differentiated and have unique geographic<br />

distributions under special environmental conditions. Accessions<br />

of these species can be crossed with each other, and progeny<br />

can be produced by backcrossing. Thus, it is feasible to<br />

develop ILs covering whole rice chromosomes. These kinds<br />

of material are already being developed. Some accessions of<br />

wild relatives from O. glumaepatula, O. glaberrima, and O.<br />

meridionalis have been used as donor parental lines to develop<br />

ILs (Sobrizal et al 1999, Yoshimura A, personal communication).<br />

Potential advantages of CSSLs in QTL analysis<br />

The potential power of CSSLs and ILs in genetic analysis has<br />

been demonstrated (Kubo et al 2002, Ebitani et al 2005). For<br />

example, CSSLs or ILs can be used in genetic analysis to associate<br />

QTLs with particular chromosome regions and to<br />

quickly develop NILs of target regions containing QTLs of<br />

interest. In general, when an association is detected between a<br />

chromosomal region and a trait, it is often difficult to validate<br />

the QTLs, especially those representing very small genetic effects.<br />

In such a case, NILs are required to analyze genetic ef-<br />

70 <strong>Rice</strong> is life: scientific perspectives for the 21st century


A<br />

Koshihikari × Kasalath<br />

F<br />

BC 1 F 3<br />

SBC 2 F 1<br />

SBC F<br />

CSSL<br />

no. chr. 1<br />

CSSLs<br />

SBC 4 F 2<br />

× Koshihikari<br />

SL-201<br />

SL-202<br />

SL-203<br />

1<br />

SL-204<br />

SL-205<br />

SL-206<br />

BC 1 F 1<br />

SL-207<br />

SL-208<br />

SL-209<br />

SL-210<br />

SL-211<br />

× Koshihikari<br />

SL-212<br />

SL-213<br />

SL-214<br />

SL-215<br />

SL-216<br />

SL-217<br />

× Koshihikari<br />

SL-218<br />

SL-219<br />

SL-220<br />

× Koshihikari<br />

SL-221<br />

SL-222<br />

SL-223<br />

3 1<br />

SL-224<br />

SL-225<br />

SBC 3 F 2<br />

SL-226<br />

SBC 4 F SL-227<br />

1<br />

SL-228<br />

SL-229<br />

SL-230<br />

CSSLs<br />

B<br />

SL-232<br />

SL-233<br />

SL-234<br />

SL-235<br />

SL-236<br />

SL-237<br />

SL-238<br />

SL-239<br />

chr. 2<br />

chr. 3<br />

chr. 4 chr. 6<br />

chr. 5<br />

chr. 7<br />

chr. 8<br />

chr. 10 chr. 12<br />

chr. 9 chr. 11<br />

Fig. 1. Chromosome segment substitution lines (CSSLs) derived from a cross between Koshihikari and Kasalath. (A): Flowchart of<br />

the process of selection of CSSLs. (B): Graphical representation of genotypes of the CSSLs. The black segments indicate regions<br />

homozygous for Kasalath alleles; the white segments indicate regions homozygous for Koshihikari alleles; the hatched segments<br />

indicate heterozygous regions. Genotype classes of the 129 RFLP markers for the CSSLs can be obtained at the Web site of the<br />

<strong>Rice</strong> Genome Resource Center (www.rgrc.dna.affrc.go.jp/ine39.html).<br />

Table 1. Chromosome segment substitution lines (CSSLs) derived from crosses within the cultivated species<br />

Oryza sativa.<br />

Cross combination<br />

Population/ Number of Genotype data Reference<br />

Recurrent Donor generation lines<br />

Nipponbare (J) a Kasalath (I) a CSSL 54 125 RFLPs RGRC (2003)<br />

Asominori (J) IR24 (I) CSSL 91 85 RFLPs Kubo et al (2002)<br />

IR24 (I) Asominori (J) CSSL 70 87 RFLPs Kubo et al (2002)<br />

Sasanishiki (J) Habataki (I) CSSL 45 – –<br />

Koshihikari (J) Kasalath (I) CSSL 39 129 RFLPs Ebitani et al (2005)<br />

Koshihikari (J) Nona Bokra BC 3 F 3 /BC 4 F 2 – – –<br />

Koshihikari (J) Nipponbare (J) BC 3 F 1 – – –<br />

Nipponbare (J) Koshihikari (J) BC 3 F 1 – – –<br />

Koshihikari (J) IR64 (I) BC 1 F 1 – – –<br />

IR64 (I) Koshihikari (J) BC 1 F 1 – – –<br />

a J and I indicate japonica and indica cultivars, respectively.<br />

fects in detail. Because CSSLs normally have one chromosomal<br />

region substituted, they can be used as NILs themselves or as<br />

starting material to develop NILs.<br />

Development of NILs for QTLs is necessary for verification<br />

and characterization of the QTLs detected (Tanksley<br />

1993, Yano and Sasaki 1997). Once a QTL for a particular trait<br />

is detected, a CSSL can be used as a NIL itself or as a base<br />

material for NIL development. As only one chromosome fragment<br />

has been substituted, only one additional backcross will<br />

be required for NIL development. Such NILs allow us to combine<br />

two or three QTLs in one genetic background to clarify<br />

the epistatic interaction among the QTLs.<br />

Use of exploited natural allelic variations in rice<br />

breeding<br />

The advent of DNA marker technology has made it possible to<br />

establish new breeding strategies, such as marker-assisted<br />

breeding (Peleman and van der Voort 2003). That strategy requires<br />

comprehensive dissection and understanding of complex<br />

traits of interest. To that end, even if a large number of<br />

DNA markers are available, novel plant materials (mapping<br />

populations) such as ILs or CSSLs are necessary for markerassisted<br />

strategies to be used in practical breeding (Zamir 2001,<br />

Peleman and van der Voort 2003). As mentioned above, novel<br />

mapping populations and plant materials have already been<br />

developed. To enhance the exploitation and use of novel alleles<br />

for rice breeding, these CSSLs should be grown under<br />

Session 2: Structure and function of the rice genome 71


different environmental conditions, and comprehensive<br />

phenotyping should be performed on traits of economic importance,<br />

such as yield, cooking and eating quality, disease<br />

and pest resistance, and environmental-stress tolerance.<br />

Once we have found favorable alleles in donor varieties,<br />

those genes can be introduced systematically and rapidly<br />

into elite varieties in a given region, by the aid of MAS. Furthermore,<br />

by using a variety of NILs and DNA markers, we<br />

can introduce genes derived from different donor cultivars into<br />

elite rice cultivars (trait pyramiding). This strategy has not yet<br />

been used in phenotype-based selection in rice breeding.<br />

References<br />

Doi K, Izawa T, Fuse T, Yamanouchi U, Kubo T, Shimatani Z, Yano<br />

M, Yoshimura A. 2004. Ehd1, a B-type response regulator in<br />

rice, confers short-day promotion of flowering and controls<br />

FT-like gene expression independently of Hd1. Genes Dev.<br />

18:926-936.<br />

Ebitani T, Takeuchi Y, Nonoue Y, Yamamoto T, Takeuchi K, Yano<br />

M. 2005. Chromosome segment substitution lines carrying<br />

overlapping chromosome segments of indica rice cultivar<br />

‘Kasalath’ in a genetic background of japonica elite cultivar<br />

‘Koshihikari’. Breed. Sci. (In press.)<br />

Izawa T, Takahashi Y, Yano M. 2003. Comparative biology comes to<br />

bloom: genomic and genetic comparison of flowering pathways<br />

in rice and Arabidopsis. Curr. Opin. Plant Biol. 6:113-<br />

120.<br />

Kojima S, Takahashi Y, Kobayashi Y, Monna L, Sasaki T, Araki T,<br />

Yano M. 2002. Hd3a, a rice ortholog of the Arabidopsis FT<br />

gene, promotes transition to flowering downstream of Hd1<br />

under short-day condition. Plant Cell Physiol. 43:1096-1105.<br />

Kubo T., Aida Y, Nakamura K, Tsunematsu H, Doi K, Yoshimura A.<br />

2002. Reciprocal chromosome segment substitution series<br />

derived from Japonica and Indica cross of rice (Oryza sativa<br />

L.). Breed. Sci. 52:319-325.<br />

Lin SY, Sasaki T, Yano M. 1998. Mapping quantitative trait loci<br />

controlling seed dormancy and heading date in rice, Oryza<br />

sativa L., using backcross inbred lines. Theor. Appl. Genet.<br />

96:997-1003.<br />

Miura K, Lin SY, Yano M, Nagamine T. 2002. Mapping quantitative<br />

trait loci controlling seed longevity in rice (Oryza sativa L.).<br />

Theor. Appl. Genet. 104:981-986.<br />

Peleman JD, van der Voort JR. 2003 Breeding by design. Trends<br />

Plant Sci. 8:330-334.<br />

RGRC (<strong>Rice</strong> Genome Resource Center). 2003. Materials for genetic<br />

analysis: Nipponbare/Kasalath chromosome segment substitution<br />

lines (CSSL), 54 lines. www.rgrc.dna.affrc.go.jp/<br />

ine54.html.<br />

Sasaki T. 2003. <strong>Rice</strong> genome analysis: understanding the genetic<br />

secrets of the rice plant. Breed. Sci. 53:281-289.<br />

Sobrizal, Ikeda K, Sanchez PL, Doi K, Angeles ER, Khush GS,<br />

Yoshimura A. 1999. Development of Oryza glumaepatula<br />

introgression lines in rice, O. sativa L. <strong>Rice</strong> Genet. Newsl.<br />

16:107-108.<br />

Takahashi Y, Shomura A, Sasaki T, Yano M. 2001. Hd6, a rice quantitative<br />

trait locus involved in photoperiod sensitivity, encodes<br />

the alpha subunit of protein kinase CK2. Proc. Natl. Acad.<br />

Sci. USA 98:7922-7927.<br />

Takeuchi Y, Hayasaka H, Chiba B, Tanaka I, Shimano T, Yamagishi<br />

M, Nagano K, Sasaki T, Yano M. 2001. Mapping quantitative<br />

trait loci controlling cool-temperature tolerance at booting<br />

stage in temperate japonica rice. Breed. Sci. 51:191-197.<br />

Takeuchi Y, Lin SY, Sasaki T, Yano M. 2003. Fine-scale linkage<br />

mapping enables dissection of closely linked quantitative trait<br />

loci for seed dormancy and heading in rice. Theor. Appl. Genet.<br />

107:1174-1180.<br />

Tanksley SD. 1993. Mapping polygenes. Annu. Rev. Genet. 27:205-<br />

233.<br />

Yano M. 2001. Genetic and molecular dissection of naturally occurring<br />

variation. Curr. Opin. Plant Biol. 4:130-135.<br />

Yano M, Katayose Y, Ashikari M, Yamanouchi U, Monna L, Fuse T,<br />

Baba T, Yamamoto K, Umehara Y, Nagamura Y, Sasaki T.<br />

2000. Hd1, a major photoperiod sensitivity quantitative trait<br />

locus in rice, is closely related to the Arabidopsis flowering<br />

time gene CONSTANS. Plant Cell 12:2473-2483.<br />

Yano M, Kojima S, Takahashi Y, Lin HX, Sasaki T. 2001. Genetic<br />

control of flowering time in rice, a short-day plant. Plant<br />

Physiol. 127:1425-1429.<br />

Yano M, Sasaki T. 1997. Genetic and molecular dissection of quantitative<br />

traits in rice. Plant Mol. Biol. 35:145-153.<br />

Zamir D. 2001. Improving plant breeding with exotic genetic libraries.<br />

Nature Rev. Genet. 2:983-989.<br />

Notes<br />

Authors’ addresses: Masahiro Yano, Utako Yamanouchi, Tadamasa<br />

Ueda, Shin-ichi Yamamoto, and Takeshi Izawa, National <strong>Institute</strong><br />

of Agrobiological Sciences, Tsukuba, Ibaraki 305-8602,<br />

Japan; Yasunori Nonoue, Tsuyu Ando, Ayahiko Shomura,<br />

Takehiko Shimizu, Izumi Kono, and Saeko Konishi, <strong>Institute</strong><br />

of the Society for Techno-Innovation of Agriculture, Forestry,<br />

and Fisheries, Tsukuba, Ibaraki 305-0854, Japan, e-mail:<br />

myano@nias.affrc.go.jp.<br />

72 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Allelic and functional diversity of stress-tolerance genes<br />

in rice<br />

Hei Leung, Hehe Wang, Jianli Wu, Ma. Elizabeth Naredo, Marietta Baraoidan, Alicia Bordeos, Suzette Madamba, Gay Carrillo,<br />

Jatinder Sangha, Zenna Negussie, Jill Cairns, Bin Liu, Yolanda Chen, Darshan Brar, Il Ryong Choi, Cassiana Vera Cruz,<br />

Renee Lafitte, Luca Comai, and Kenneth L. McNally<br />

Most natural genetic variation in organisms is represented by<br />

simple base changes or small insertions/deletions (single nucleotide<br />

polymorphisms, SNPs, or single feature polymorphisms,<br />

SFPs). It is reasonable to assume that SNPs in both structural<br />

and regulatory genes are key drivers of phenotypic variation,<br />

and that they collectively account for many of the varietal differences<br />

in crop germplasm. SNP analysis has been used successfully<br />

in dissecting complex traits in other model organisms<br />

with practical implications (see recent examples in understanding<br />

the genetic basis of immunity in Drosophila,<br />

Lazzaro et al 2004, tracking asthma-related traits and cholesterol<br />

levels in humans, Laitinen et al 2004, Cohen et al 2004).<br />

Thus, a whole-genome SNP data set derived from diverse<br />

germplasm (i.e., SNP haplotypes encompassing the natural<br />

variation at any particular segment of the chromosome) has<br />

considerable potential for crop improvement.<br />

SNP discovery is important for breeding in two fundamental<br />

ways. First, it reveals DNA variation among varieties,<br />

thus providing the tools for selection in breeding programs.<br />

Second, SNPs provide the “anchor” to relate other forms of<br />

polymorphisms—biochemical, metabolic, physiological, and<br />

phenotypic performance (Fig. 1). We have taken both forward<br />

and reverse genetics approaches to identify induced and natural<br />

variants exhibiting a differential response to biotic and abiotic<br />

stresses. Three sources of genetic materials are used: mutants,<br />

germplasm from a gene bank collection, and advanced<br />

breeding lines. We select a set of candidate genes involved in<br />

stress tolerance based on convergent evidence of cross-species<br />

sequence inference, QTL position, and expression phenotypes.<br />

As a test case, a good level of blast resistance in elite<br />

breeding lines has been achieved using this strategy. We envision<br />

a systematic approach of associating phenotypes with<br />

genotypes through a broad sampling of induced and natural<br />

variation, which can reveal the functional relationships among<br />

regulatory and effector genes, and provide the needed information<br />

for maximizing the use of allelic variation in breeding.<br />

Phenotypic screen of induced variation<br />

A large collection of induced mutations has been generated by<br />

institutions and laboratories around the world (Hirochika et al<br />

2004). We have focused on the use of chemical and irradiation-induced<br />

mutations in an indica rice variety, IR64. From<br />

screening the IR64 mutant collection (primarily deletions and<br />

point mutations), we have genetically defined mutants with an<br />

altered response to multiple diseases (blast, bacterial blight,<br />

Genetic variation<br />

SNP and indels<br />

Connecting genomic variation<br />

with phenotypes and performance<br />

Profiles of<br />

l Transcripts<br />

l Proteins<br />

l Metabolites<br />

Interactions<br />

Phenotypes<br />

Performance<br />

Fig. 1. Gene function discovery involves relating genetic variation<br />

to phenotypes. Available whole-genome sequence provides the<br />

anchor to relate gene expression polymorphism to genomic variation.<br />

and tungro viruses), brown planthopper, and drought.<br />

From these screening experiments, we observe that gainof-function<br />

mutations can be found at considerable frequencies.<br />

We identified gain-of-resistance to brown planthopper,<br />

which is apparently controlled by a partially dominant mutation<br />

(J. Sangha, <strong>IRRI</strong>, unpublished data). Another mutant showing<br />

gain-of-resistance to rice tungro spherical virus (RTSV)<br />

was conditioned by a recessive mutation (N. Zenna and I. Choi,<br />

<strong>IRRI</strong>, unpublished data). A putative mutant with enhanced tolerance<br />

of water stress under field conditions has been isolated<br />

(Botwright and Lafitte 2002, J. Cairns and R. Laffitte, <strong>IRRI</strong>,<br />

unpublished). Zeng et al (2004) found that the lesion mimic<br />

gene SPL11 encodes a putative E3 ligase that functions as a<br />

negative regulator of cell death and broad-spectrum host resistance.<br />

These results suggest a significant role for negatively<br />

regulated networks in stress tolerance. Thus, a systematic<br />

screening for an agronomically important phenotype could<br />

yield better than expected results.<br />

Reverse genetics to detect induced and natural variation<br />

Based on results from expression and mapping studies as well<br />

as published reports (e.g., Cooper et al 2003), we developed a<br />

panel of candidate genes potentially involved in stress tolerance.<br />

Currently, a set of 32 candidate genes is used as targets<br />

for TILLING (Till et al 2003). These genes are selected based<br />

on several criteria: (1) high-quality sequence information from<br />

Session 2: Structure and function of the rice genome 73


indica and japonica rice, (2) implicated function based on sequence<br />

annotation, (3) functional role inferred from other species,<br />

(4) evidence that they are within QTL regions based on<br />

mapping studies, and/or (5) the region in which they occur<br />

undergoes allelic shifts under selection. For each gene, we apply<br />

TILLING to survey haplotypic and SNP variation in the 5′<br />

regulatory and coding regions in mutants, O. sativa germplasm,<br />

and wild relatives. Simultaneously, we evaluate the phenotypes<br />

associated with these alleles in natural germplasm and derived<br />

breeding lines.<br />

Choice of the genetic material is a key factor for the<br />

success of the approach. We have chosen a set of 200–400<br />

accessions representative of diverse genetic origins from different<br />

selection cycles in our rice breeding programs. These<br />

are taken from the accessions genotyped with neutral simple<br />

sequence repeat (SSR) markers, randomly distributed along<br />

the genome, such that the genetic structure can be assessed<br />

and considered in statistical models to test association. This<br />

collection will also be used to optimize the choice of subsets<br />

of inbreds for the SNP discovery analyses, and identification<br />

of haplotype patterns. To achieve cost-effective genotyping,<br />

multiples of 96 accessions are chosen to fit a high-throughput<br />

format. Moreover, to have sufficient power for statistical tests<br />

of association between polymorphism and phenotypes, at least<br />

200 inbred lines should be evaluated for phenotypes under<br />

homogeneous conditions.<br />

Initial results have been obtained from using primers<br />

designed from the coding sequence of protein phosphatase 2a-<br />

4 (PP2a4) on cultivated germplasm and from DREB1 and trehalose<br />

6-phosphatase (TPS) using cultivated and wild<br />

germplasm. We have detected mismatches (putative SNPs) for<br />

these genes across a range of germplasm. Three putative SNP<br />

haplotypes were detected for PP2a4 in 22 Korean japonica<br />

and Tongil (indica/japonica hybrid) varieties contrasted to<br />

Nipponbare. One SNP was detected in Milyang30, Taebaek,<br />

Samgang, Sindongjin, and Milyang23, a second was found in<br />

Milyang30 and Milyang23, and a third occurred in Suwon345.<br />

Furthermore, a putative SNP was also detected between SHZ2<br />

and LTH, the two parental lines of a breeding population developed<br />

for disease-resistance studies.<br />

For TPS on 48 germplasm accessions, the most distinct<br />

haplotype occurred in the contrast between Kun Min Tsieh<br />

Hunan and IR64. A mismatch at the same position was also<br />

detected in the contrast between Kun Min Tsieh Hunan and<br />

Nipponbare. The TPS primers were also tested on the wild<br />

germplasm panel, but amplicons were obtained only for the<br />

AA-genome species.<br />

In tests of DREB1 on cultivated rice, three putative SNP<br />

haplotypes have been detected in 96 accessions. The SNP detected<br />

between IR64 and Nipponbare is common to indica/<br />

japonica contrasts. A second haplotype occurred in the<br />

Mimidam and IR64 contrast, and a third was detected between<br />

Taichung Native 1 and Nipponbare. Interestingly, primers designed<br />

for the coding region of DREB1 produced amplicons<br />

from wild relatives as distant as the GG genome, but none for<br />

the distant HHJJ and HHKK genomes (E. Naredo and K.<br />

McNally, <strong>IRRI</strong>, unpublished data). Many putative SNPs can<br />

be detected in these distant contrasts, including an SNP that<br />

appears to be absent from most wild species and indica but<br />

present in japonica (Fig. 2).<br />

We have also tested the ability to detect mismatches in<br />

pools of germplasm. Pooling is an approach that is routinely<br />

used in TILLING and may be advantageous for EcoTILLING<br />

as a first-pass screen among lines that are considered closely<br />

related. Our results indicate that pools of up to 8-fold are possible,<br />

which will allow 768 accessions to be screened in a single<br />

run for preliminary analysis. By improving the throughput of<br />

the system, we will be in a position to identify variants in the<br />

large collection of germplasm (>100,000) accessions in the<br />

<strong>International</strong> <strong>Rice</strong> Genebank Collection held at <strong>IRRI</strong>.<br />

Disease resistance as a case study<br />

The recent work of Cohen et al (2004) showed that rare alleles<br />

in a few candidate genes can account for the complex phenotype<br />

of plasma cholesterol level in humans. In this case, strong<br />

association was established between SNP in the coding regions<br />

of three candidate genes and extreme phenotypes in two human<br />

populations. The study suggests that it is possible to associate<br />

SNP variants with phenotypes provided that opposing<br />

phenotypes are adequately described in one or more populations.<br />

We use disease resistance as a case study to test whether<br />

allelic variants can be selected that achieve the desired phenotypic<br />

performance in the field. In this case, we applied candidate<br />

defense-related genes as selection markers for blast resistance.<br />

Advanced lines with chromosomal segments carrying<br />

the positive alleles showed effective quantitative resistance in<br />

multiple locations over three years (Liu et al 2004). However,<br />

because each chromosomal segment carries many potential<br />

defense genes, confirmative evidence is needed. To gather more<br />

evidence to support that a candidate gene is responsible for<br />

phenotypic gain, we followed the introgression of specific alleles<br />

of members of the oxalate oxidase (germin-like-protein)<br />

gene family. Preliminary data suggest association of indels in<br />

the 5′ untranslated region of two members of the gene family<br />

with blast resistance observed in advanced breeding lines (G.<br />

Carrillo and C. Vera Cruz, <strong>IRRI</strong>, unpublished data). Work is in<br />

progress to isolate mutations in these candidate genes through<br />

a reverse genetics screen. We hope that an integration of genotypic<br />

and phenotypic data obtained from advanced germplasm<br />

and mutants could provide the means to put knowledge of gene<br />

function to use in practical breeding.<br />

References<br />

Botwright T, Lafitte R. 2002. Deletion mutants for screening of<br />

drought tolerance in rice. In: Progress toward developing resilient<br />

crops for drought-prone areas. Proceedings of an <strong>International</strong><br />

Workshop. Los Baños (Philippines): <strong>International</strong><br />

<strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>. p 114-115. www.irri.org/publications/<br />

limited/pdfs/ResilientCrops.pdf.<br />

74 <strong>Rice</strong> is life: scientific perspectives for the 21st century


A<br />

AA<br />

AA<br />

AA<br />

AA<br />

AA<br />

AA<br />

AA<br />

AA<br />

AA<br />

AA<br />

AA<br />

AA<br />

AA<br />

AA<br />

AA<br />

AA<br />

AA<br />

AA<br />

AA<br />

AA<br />

AA<br />

AA<br />

AA<br />

AA<br />

AA<br />

AA<br />

AA<br />

AA<br />

AA<br />

CCDC<br />

EE<br />

CC<br />

CC<br />

CCDC<br />

GG<br />

GG<br />

BBCC<br />

CC<br />

CC<br />

CC<br />

BB<br />

BBCC<br />

CC<br />

CC<br />

IIIJJ<br />

HHKK<br />

IR64<br />

NIP<br />

1 5 10 15 20 25 30 35 40 45<br />

B<br />

1 5 10 15 20 25 30 35 40 45 I/N 1 5 10 15 20 25 30 35 40 45 I/N<br />

C<br />

1 5 10 15 20 25 30 35 40 45 I/N 1 5 10 15 20 25 30 35 40 45 I/N<br />

Fig. 2. EcoTILLING of DREB1 on wild Oryza. DREB1 amplicons of a similar size were produced from<br />

47 wild Oryza species using primers designed from Nipponbare (A). Mixtures of these products<br />

were combined with either IR64 (left set of lanes) or Nipponbare (right set of lanes). The IRD700<br />

channel is shown in panel B and the IRD800 in C. Circles indicate clear differences present in<br />

both channels. Arrows indicate a mismatch present in japonica but absent from most wild and<br />

indica rice.<br />

Cohen JC, Kiss RS, Pertsemlidis A, Marcel YL, McPherson R, Hobbs<br />

HH. 2004. Multiple rare alleles contribute to low plasma levels<br />

of HDL cholesterol. Science 305:869-872.<br />

Cooper B, Clarke JD, Budworth P, Kreps J, Hutchison D, Park S,<br />

Guimil S, Dunn M, Luginbuhl P, Ellero C, Goff SA,<br />

Glazebrook J. 2003. A network of rice genes associated with<br />

stress response and seed development. Proc. Natl. Acad. Sci.<br />

USA 100:4945-4950.<br />

Hirochika H, Guiderdoni E, An G, Hsing Y, Eun MY, Han CD,<br />

Upadhyaya N, Ramachandran S, Zhang Q, Pereira A,<br />

Sundaresan V, Leung H. 2004. <strong>Rice</strong> mutant resources for gene<br />

discovery. Plant Mol. Biol. 54:325-334.<br />

Laitinen T, Polvi A, Rydman P, Vendelin J, Pulkkinen V, Salmikangas<br />

P, Mäkelä S, Rehn M, Pirskanen A, Rautanen A, Zucchelli M,<br />

Gullstén H, Leino M, Alenius H, Petäys T, Haahtela T, Laitinen<br />

A, Laprise C, Hudson TJ, Laitinen LA, Kere J. 2004. Characterization<br />

of a common susceptibility locus for asthma-related<br />

traits. Science 304:300-304.<br />

Lazzaro BP, Sceurman BK, Clark AG. 2004. Genetic basis of natural<br />

variation in D. melanogaster antibacterial immunity. Science<br />

303:1873-1876.<br />

Liu B, Zhang S, Zhu X, Yang Q, Wu S, Mei M, Mauleon R, Leach J,<br />

Mew T, Leung H. 2004. Candidate defense genes as predictors<br />

of quantitative blast resistance in rice. Mol. Plant-Microbe<br />

Interact. 17:1146-1152.<br />

Till BJ, Reynolds SH, Greene EA, Codomo CA, Enns LC, Johnson<br />

JE, Burtner AR, Young K, Taylor NE, Henikoff JG, Comai L,<br />

Henikoff S. 2003. Large-scale discovery of induced pointmutations<br />

with high-throughput TILLING. Genome Res.<br />

13:524-530.<br />

Zeng L, Qu S, Bordeos A, Yang C, Baraoidan M, Yan H, Xie Q,<br />

Nahm BH, Leung H, Wang GL. 2004. Spl11, a negative regulator<br />

of plant cell death and defense, encodes a U-Box/ARM<br />

repeat protein endowed with E3 ubiquitin ligase activity. Plant<br />

Cell 16:2795-2808.<br />

Notes<br />

Authors’ addresses: Division of Entomology and Plant Pathology,<br />

Genetic Resources Center, Division of Plant Breeding, Genetics,<br />

and Biochemistry, Division of Crop, Soil, and Water<br />

Sciences, <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>, DAPO Box<br />

7777, Metro Manila, Philippines; Department of Biology, University<br />

of Washington, Seattle, Washington, USA.<br />

Acknowledgments: This work is supported in part by the Swiss<br />

Agency for Development and Cooperation (SDC), Rockefeller<br />

Foundation, and Generation Challenge Program.<br />

Session 2: Structure and function of the rice genome 75


Functional genomics by reverse genetics<br />

Gynheung An<br />

Sequencing of the rice genome is nearly complete. T<strong>here</strong>fore,<br />

one of the most challenging goals now is to examine the functioning<br />

of its large number of genes. To facilitate such an evaluation,<br />

several reverse genetics approaches have been developed.<br />

Random insertional mutagenesis by transposons or T-<br />

DNA has been the most widely used for large-scale analyses.<br />

This technique is not only efficient for identifying knockout<br />

mutants, but can also be employed for promoter trapping and<br />

activation tagging. The recent establishment of a large number<br />

of insertional mutants will accelerate these reverse genetics<br />

approaches for studying gene function in this model monocot<br />

species.<br />

Insertional mutagenesis by T-DNA or transposon<br />

An efficient means for rice transformation is via the<br />

Agrobacterium-mediated cocultivation method. This technique<br />

allows researchers to obtain a suitable T-DNA tagging population.<br />

For example, An’s group has generated approximately<br />

100,000 fertile rice lines tagged by T-DNA (Jeon et al 2000,<br />

Jeong et al 2002), while work by Zhang and colleagues has<br />

resulted in more than 30,000 T-DNA insertional lines (Wu et<br />

al 2003). Several other groups have independently produced<br />

T-DNA insertional mutant lines. Because the average copy<br />

number of T-DNA inserts per line is 1.4 to 2.0, more than<br />

300,000 T-DNA tags have now been generated in rice. These<br />

populations are large enough to find a knockout in a given<br />

gene at more than 90% probability, assuming that T-DNA is<br />

randomly inserted into a chromosome.<br />

The maize Ac/Ds system has been used for large-scale<br />

generation of gene tagging via the Agrobacterium-mediated<br />

gene delivery method (Chin et al 1999, Kolesnik et al 2004).<br />

The germinal transposition frequency of Ds is high. Study of<br />

the transposition pattern in siblings has revealed that 79% contain<br />

at least two different insertions, suggesting late transposition<br />

during rice development (Kolesnik et al 2004). Moreover,<br />

repetitive ratoon culturing causes new transposition, at about<br />

30% frequency, demonstrating that this strategy can produce a<br />

large mutant population (Chin et al 1999).<br />

Retroelements are a major component of plant genomes.<br />

At least 17% of the rice genome consists of retrotransposons.<br />

One such element in rice is Tos17. Although its copy number<br />

is low, this can increase to up to 30 copies during tissue culture.<br />

More than 47,000 Tos17 insertion lines have been produced<br />

to generate insertional mutants in rice (Hirochika 2001,<br />

Miyao et al 2003).<br />

Activation tagging<br />

Insertional mutagenesis usually generates recessive loss-offunction<br />

mutations, making them unsuitable for functional<br />

analysis of redundant genes. Jeong et al (2002) have demonstrated<br />

that the CaMV 35S enhancer element efficiently increases<br />

the expression of nearby genes from either their 5′ or<br />

3′ ends. Based on this, they have devised a binary vector that<br />

carries the tetramerized 35S enhancers next to the left T-DNA<br />

border. This vector has now been used to generate activationtagging<br />

pools for more than 50,000 individual transformants<br />

(Jeong et al 2002). Moreover, examination of randomly selected<br />

tags in the intergenic regions has shown that approximately<br />

40% of the enhancer insertions increase nearby gene<br />

expression, proving that activation-tagging efficiency at the<br />

transcriptional level is quite high.<br />

Forward screening<br />

Insertional mutant lines are useful resources for studying gene<br />

function. However, most knockout mutations are recessive.<br />

T<strong>here</strong>fore, their phenotypes are not visible in the primary<br />

transgenic lines and can be detected only in the progeny generations.<br />

In their analyses of T-DNA tagging lines, Jeon et al<br />

(2000) have observed that the most common mutants are dwarfing<br />

(7.0%) and leaf-pigment alterations (9.5%). Developmental<br />

mutants have also been observed in their screening. One<br />

must determine whether these phenotypes are due to the insertion.<br />

Cosegregation of phenotypes with the insert DNA is a<br />

good indication that the phenotype is caused by the insert.<br />

Ultimately, the mutant phenotype must be confirmed by another<br />

allele or complemented by the wild-type gene. Tissue<br />

culturing is known to generate mutations not associated with<br />

insertions. Retrotransposons, such as Tos17 or Karma, are activated<br />

during tissue culture. Miniature inverted-repeat transposable<br />

elements (MITEs), such as mPing or Pong, can also<br />

act as mutagens. In addition, small insertions, deletions, and<br />

base substitutions may be induced in cultured cells. T<strong>here</strong>fore,<br />

a large portion of mutants are generated in these populations<br />

through a mechanism not associated with the introduced<br />

inserts. Nonetheless, insertional mutant populations are good<br />

resources for studying gene function with forward genetics.<br />

By analyzing insertional mutant pools, functions of a large<br />

number of genes have been determined.<br />

DNA pool screening<br />

Insertional mutant collections are more beneficial when used<br />

with reverse genetics approaches. With the near completion of<br />

rice genome sequencing, researchers are now identifying a large<br />

76 <strong>Rice</strong> is life: scientific perspectives for the 21st century


number of genes based on their sequence homology. Generally,<br />

groupings of related genes are formed, in which the functions<br />

of only one or a few have been elucidated. Reverse genetics<br />

approaches are excellent methods for studying a group<br />

of genes relatively quickly. In these approaches, mutants in a<br />

target gene are first collected, then their phenotypes are investigated.<br />

Double or multiple mutants may be generated as necessary<br />

for further assessment.<br />

Insertional mutants in a given gene can be isolated via<br />

PCR-based screening. Using a gene-specific primer and a<br />

primer located near the end of the insert, a DNA fragment flanking<br />

the insert element can be amplified and its sequence then<br />

determined. This strategy has already been successfully applied<br />

with Arabidopsis, petunia, and maize. Enoki et al (1999)<br />

and Hirochika (2001) have reported PCR-based reverse genetics<br />

screenings of the Ac and Tos17 insertion lines in rice.<br />

The DNA pools have been used for isolation of knockout mutations<br />

in several genes. DNA pools of the T-DNA insertional<br />

lines have also been generated and used for isolation of knockout<br />

and activation-tagging mutants (Lee et al 2003).<br />

Tag end sequence databases<br />

Tag end sequences (TES) that flank insert elements can be<br />

obtained by TAIL PCR, iPCR, or adaptor-ligation PCR. When<br />

numerous flanking sequences are generated, they are catalogued<br />

into databases. Although large-scale application of this<br />

alternative strategy requires considerable effort, once established,<br />

these databases can be easily shared with other scientists,<br />

thus facilitating the distribution of mutant materials and<br />

analysis of gene function. Because sequencing of the rice genome<br />

is nearly complete, flanking-sequence databases will<br />

become powerful tools for systematically analyzing the functions<br />

of a large number of genes in those species. The TES<br />

database has been derived from the Tos17 insertional mutant<br />

lines (Miyao et al 2003). Hirochika’s group has analyzed more<br />

than 20,000 TES from 4,316 mutant lines<br />

(www.postgresql.org). TES databases for T-DNA insertional<br />

lines have also been created by several laboratories. An et al<br />

(2003) have reported the establishment of a database of 3,793<br />

TES. Entries are now 24,299 (www.postech.ac.kr/life/pfg/risd).<br />

TES analyses reveal the distribution of insert elements in plant<br />

chromosomes. For example, most transposition events occur<br />

at a tightly linked site, as reported with Arabidopsis. T<strong>here</strong>fore,<br />

a short-range and highly preferential transposition system<br />

can be effectively used for targeted mutagenesis of closely<br />

linked genes.<br />

For any given gene, Ds transposes equally into exons<br />

and introns, indicating no preference toward the 5′ end for<br />

genes in Arabidopsis, maize, or rice. Analysis of 2,057 Ds flanking<br />

sequences in rice has demonstrated that Ds insertions are<br />

distributed randomly throughout that genome.<br />

Miyao et al (2003) have investigated more than 20,000<br />

unique insertion points at Tos17 tagged sites and report that<br />

insertion events are three times more frequent in genic regions<br />

than in intergenic regions. Consistent with this, Tos17 prefers<br />

gene-dense regions over centromeric heterochromatin regions.<br />

Although insertion target sites are distributed throughout the<br />

rice chromosomes, they tend to cluster. This phenomenon may<br />

reduce the efficiency of genome-wide gene disruption by Tos17.<br />

Analysis of TES has demonstrated that the frequency of T-<br />

DNA insertion into genic regions is greater than the expected<br />

probability given random insertion (An et al 2003). Frequencies<br />

are also higher at the beginning and end of the coding<br />

regions, as well as upstream near the start ATG codon. The<br />

overall GC content at the insertion sites is close to that measured<br />

for the entire rice genome. Functional classification of<br />

1,846 tagged genes has shown a distribution similar to that<br />

observed for all genes in the rice chromosomes. This indicates<br />

that T-DNA insertion is not biased toward a particular functional<br />

group (An et al 2003). At the chromosomal level, insertions<br />

are not evenly distributed; frequencies are higher at the<br />

ends and lower near the centromere. At certain sites, the frequency<br />

is greater than in the surrounding regions, proving that<br />

T-DNA insertion is not a random event.<br />

Prospects<br />

The number of insertional mutants accumulated thus far by<br />

the scientific community is large enough to saturate almost all<br />

the genes in japonica rice. It will be valuable to develop methods<br />

for tagging indica varieties. The rapid generation of TES<br />

databases is urgently needed for efficient use of this insertional<br />

mutant resource. DNA pools are useful for identifying the alleles<br />

of a given gene. Such reverse genetics materials are valuable<br />

to functional genomic analyses of a large number of genes<br />

in rice and for developing new varieties.<br />

References<br />

An S, Park S, Jeong DH, Lee DY, Kang HG, Yu JH, Hur J, Kim SR,<br />

Kim YH, Lee M, Han S, Kim SJ, Yang J, Kim E, Wi SJ, Chung<br />

HS, Hong JP, Choe V, Lee HK, Choi JH, Nam J, Kim SR,<br />

Park PB, Park KY, Kim WT, Choe S, Lee CB, An G. 2003.<br />

Generation and analysis of end sequence database for T-DNA<br />

tagging lines in rice. Plant Physiol. 133:2040-2047.<br />

Chin HG, Choe MS, Lee SH, Park SH, Koo JC, Kim NY, Lee JJ, Oh<br />

BG, Yi GH, Kim SC, Choi HC, Cho MJ, Han CD. 1999. Molecular<br />

analysis of rice plants harboring an Ac/Ds transposable<br />

element-mediated gene trapping system. Plant J. 19:615-<br />

623.<br />

Enoki H, Izawa T, Kawahara M, Komatsu M, Koh S, Kyozuka J,<br />

Shimamoto K. 1999. Ac as a tool for the functional genomics<br />

of rice. Plant J. 19:605-613.<br />

Hirochika H. 2001. Contribution of the Tos17 retrotransposon to<br />

rice functional genomics. Curr. Opin. Plant Biol. 4:118-122.<br />

Jeon JS, Lee S, Jung KH, Jun SH, Jeong DH, Lee J, Kim C, Jang S,<br />

Yang K, Nam J, An K, Han MJ, Sung RJ, Choi HS, Yu JH,<br />

Choi JH, Cho SY, Cha SS, Kim SI, An G. 2000. T-DNA insertional<br />

mutagenesis for functional genomics in rice. Plant J.<br />

22:561-570.<br />

Jeong DH, An S, Kang HG, Moon S, Han JJ, Park S, Lee HS, An K,<br />

An G. 2002. T-DNA insertional mutagenesis for activation<br />

tagging in rice. Plant Physiol. 130:1636-1644.<br />

Session 2: Structure and function of the rice genome 77


Kolesnik T, Szeverenyi I, Bachmann D, Kumar CS, Jiang S,<br />

Ramamoorthy R, Cai M, Ma ZG, Sundaresan V, Ramachandran<br />

S. 2004. Establishing an efficient Ac/Ds tagging system in<br />

rice: large-scale analysis of Ds flanking sequences. Plant J.<br />

37:301-314.<br />

Lee S, Kim J, Son JS, Nam J, Jeong DH, Lee K, Jang S, Yoo J, Lee<br />

J, Lee DY, Kang HG, An G. 2003. Systematic reverse genetic<br />

screening of T-DNA tagged genes in rice for functional genomic<br />

analyses: MADS-box genes as a test case. Plant Cell<br />

Physiol. 44:1403-1411.<br />

Miyao A, Tanaka K, Murata K, Sawaki H, Takeda S, Abe K,<br />

Shinozuka Y, Onosato K, Hirochika H. 2003. Target site specificity<br />

of the Tos17 retrotransposon shows a preference for insertion<br />

within genes and against insertion in retrotransposonrich<br />

regions of the genome. Plant Cell 15:1771-1780.<br />

Wu C, Li X, Yuan W, Chen G, Kilian A, Li J, Xu C, Li X, Zhou DX,<br />

Wang S, Zhang Q. 2003. Development of enhancer trap lines<br />

for functional analysis of the rice genome. Plant J. 35:418-<br />

427.<br />

Notes<br />

Author’s address: Pohang University of Science and Technology,<br />

Pohang 790-784, Republic of Korea, e-mail:<br />

genean@postech.ac.kr.<br />

Tissue culture-induced mutations and a new type<br />

of activation tagging as tools for functional analysis<br />

of rice genes<br />

Hirohiko Hirochika<br />

With the completion of genomic sequencing of rice, rice has<br />

been firmly established as a model organism for both basic<br />

and applied research. The next challenge is to uncover the functions<br />

of genes predicted by sequence analysis. Knockout of<br />

genes by insertional mutagenesis is a straightforward method<br />

for identifying gene functions. In Arabidopsis, whose entire<br />

genomic sequencing has been completed, mutant populations<br />

covering almost all the genes have been produced by using<br />

insertion elements, such as T-DNA, Ac/Ds, and En/Spm. While<br />

these mutant lines are important resources for forward genetics<br />

studies of gene function, their applications in reverse genetics<br />

are even more important with the available Arabidopsis<br />

genome sequence. Two primary approaches for reverse genetics<br />

analysis have been established. One is PCR screening of<br />

DNA pools from mutants using primers corresponding to a<br />

target sequence. The other is flanking sequence tag (FST) analysis,<br />

a strategy in which sequences flanking the insertion elements<br />

are determined in each mutant line to develop a database<br />

of knockout genes that can be searched electronically.<br />

Because of the labor- and time-demanding nature of PCR<br />

screening, FST database development is now the preferred<br />

strategy. Although investment in the FST database is high,<br />

screening of mutants is easy once the database is established.<br />

In several Arabidopsis laboratories (http://signal.salk.edu/<br />

tabout.html, http://atidb.cshl.org, and http://genoplanteinfo.infobiogen.fr),<br />

a large collection of FST data, totaling more<br />

than 100,000, has been established and opened to the public.<br />

A large-scale insertional mutagenesis has begun also in rice<br />

using T-DNA, Ac/Ds, and the endogenous retrotransposon<br />

Tos17. The current status of rice mutant resources has been<br />

recently summarized by Hirochika et al (2004). Here, I summarize<br />

recent progress in insertional mutagenesis in rice using<br />

Tos17 and its application to forward and reverse genetics studies.<br />

In addition, I also mention our new challenge, the development<br />

of activation tagged lines using full-length cDNA.<br />

Forward and reverse genetics using Tos17<br />

The unique features of Tos17 that make it a powerful genetic<br />

tool for forward and reverse genetics studies are summarized<br />

as follows. (1) Transposition can be regulated since Tos17 is<br />

activated by tissue culture and becomes silent in regenerated<br />

plants. (2) Highly mutagenic during tissue culture, Tos17 transposes<br />

preferentially into gene-rich, low-copy regions and about<br />

ten loci on average are disrupted in each plant regenerated<br />

from 5-month-old culture. (3) Integration target loci were<br />

widely distributed over the chromosomes, so that random insertion<br />

for saturation mutagenesis is feasible. (4) Induced<br />

mutations are stable and germinally transmitted in the next<br />

generation. (5) The original copy number is quite low, one to<br />

five depending on varieties, so that it is easy to identify the<br />

transposed copy responsible for the specific mutation. (6) Rearrangements<br />

are very rare at junctions between Tos17 ends<br />

and flanking host sequences, so that screening of mutants by<br />

PCR and analysis of disrupted genes can be carried out with<br />

high efficiency. (7) The transposon is endogenous, so that<br />

screening and characterization of mutants in the field are possible<br />

without any environmental concern. However, some features<br />

might also be disadvantageous. For example, transposition<br />

via a copy-and-paste mode means that no revertants can<br />

78 <strong>Rice</strong> is life: scientific perspectives for the 21st century


e obtained, although revertants are useful for confirming that<br />

a gene is tagged and can be obtained from the mutants induced<br />

by class II elements such as Ac/Ds.<br />

Forward genetics studies<br />

Traditional transposon tagging is still an important method for<br />

cloning important genes for functional analysis. The first direct<br />

evidence for the feasibility of tagging using Tos17 was<br />

shown by cloning genes involved in abscisic acid biosynthesis<br />

(Agrawal et al 2001) and causative genes for more than 20<br />

mutations have been cloned by using this strategy. R 1 (M 2 )<br />

generations of regenerated rice were screened for mutants based<br />

on the phenotypes in the field. About 50% of the regenerated<br />

lines examined showed many kinds of visible mutant phenotypes,<br />

such as dwarf, sterile, yellow, albino, virescent, viviparous,<br />

brittle, and spotted leaf. In addition to screening in the<br />

field, screening in vitro was also conducted to isolate genes<br />

involved in salt-stress tolerance, and root growth and development.<br />

Some of the mutants were picked out and further subjected<br />

to cosegregation analysis to determine whether the mutations<br />

were caused by Tos17 insertions. Genetic analysis<br />

showed that all these mutations are recessive, although some<br />

did not segregate in a 1:3 ratio. Because the copy number of<br />

Tos17 is low enough to visualize each transposed copy, the<br />

Tos17 copy causing the specific mutation can be identified by<br />

a simple DNA gel-blot analysis. Finally, the causative gene<br />

can be isolated by using IPCR (inverse PCR) or TAIL-PCR<br />

(thermal asymmetric interlaced-PCR). This situation is quite<br />

distinct from the tagging using endogenous transposable elements<br />

in other plants, such as maize and petunia, in which the<br />

copy number of transposable elements is high (approx. 100<br />

copies).<br />

Although gene-tagging with Tos17 is a powerful strategy<br />

for cloning genes, one fundamental problem should be<br />

noted. That is the relatively low tagging efficiency (5–10%)<br />

(Hirochika 2001, Agrawal et al 2001). This indicates that tissue<br />

culture-induced mechanisms other than Tos17 insertions<br />

cause untagged mutations with high frequency. Several lines<br />

of evidence indicated that untagged mutations involve deletions<br />

and point mutations induced by unknown mechanisms<br />

(G.K. Agrawal et al, unpublished results). Recent studies<br />

showed that these deletion mutations, providing complete lossof-function<br />

mutations, are also important resources for functional<br />

analysis of genes. These mutations can also be used as a<br />

resource for reverse genetics by using TILLING (Till et al<br />

2003) and PCR-based screening of deletions.<br />

Reverse genetics studies<br />

For reverse genetics, DNA pools for PCR screening or the FST<br />

database are needed to identify mutations in genes of interest.<br />

The first direct evidence for the feasibility of the use of Tos17<br />

for the PCR-screening strategy was shown by screening for a<br />

mutant of the homeobox gene (OSH15) (Sato et al 1999). DNA<br />

pools from 50,000 Tos17 insertion lines have been constructed<br />

and, so far, results from screening these DNA pools suggest a<br />

success rate of 50% for a given target sequence (H. Hirochika,<br />

unpublished results). Because of the finite nature of the DNA<br />

pool, it is not practical to distribute DNA pools publicly. In<br />

addition, PCR screening is labor- and time-intensive. Thus,<br />

generating an FST database as a public resource is a more<br />

desirable and practical strategy. As of June 2004, about 20,000<br />

independent flanking sequences from 6,000 lines have been<br />

determined (Miyao et al 2003; http://tos.nias.affrc.go.jp). Some<br />

other research groups constructing insertional mutant lines have<br />

also started to construct FST databases. T-DNA FST databases<br />

at Pohang University (www.postech.ac.kr/life/pfg/risd) and at<br />

Génoplante (http://genoplante-info.infobiogen.fr/oryzatagline)<br />

are open to the public. FST data are expected to be anchored<br />

to the public IRGSP genome sequence and positions of both<br />

predicted genes and FST data will be shown graphically on<br />

the physical map.<br />

In addition to FST databases, it is also important to make<br />

databases on phenotypes. To maximize the utility of phenotype<br />

databases, a common vocabulary for describing mutants<br />

should be adopted among the mutant producers in different<br />

projects. The Plant Ontology Consortium vocabulary provides<br />

such a common framework and integrates different fields of<br />

expertise specific to plants. If the phenotype database is linked<br />

to the FST database, functional assignment of genes will be<br />

greatly accelerated.<br />

Limitations and future prospects<br />

Several problems or limitations associated with features in<strong>here</strong>nt<br />

in insertional mutagenesis have been noted when functional<br />

analysis was carried out. One obvious problem is the<br />

lack of a mutant phenotype. In Arabidopsis, less than 2% of<br />

the insertional mutant lines showed a mutant phenotype. This<br />

problem may be largely due to gene redundancy. One possible<br />

solution is a combination of mutations by crossing, as has been<br />

successfully demonstrated in Arabidopsis (Liljegren et al<br />

2000). Considering the higher gene redundancy in rice, this<br />

problem may become more serious. Another problem is background<br />

mutations induced during the production of mutant<br />

lines, which make it unreliable to directly correlate phenotype<br />

with insertion mutations. Most of the background mutations<br />

are recessive and probably introduced by tissue culture. The<br />

molecular natures of the mutations are not known, but they<br />

may be deletions and point mutations as described in the previous<br />

section.<br />

To solve those problems, activation tagging inducing<br />

dominant mutations will be a complementary strategy. More<br />

than 50,000 activation-tagged lines have been produced already<br />

by using T-DNA with multimerized 35S enhancers (Jeong<br />

et al 2002). Considering the random insertion of T-DNA, a<br />

large number of tagged lines must be needed to overexpress<br />

all the genes. Recently, a more efficient activation tagging system<br />

has been developed in Arabidopsis (T. Ichikawa et al, unpublished<br />

results). This system, called Fox Hunting (full-length<br />

cDNA over-expressor gene hunting), uses transformation with<br />

T-DNA carrying an Arabidopsis full-length cDNA library under<br />

the control of the modified 35S promoter. By using this<br />

Session 2: Structure and function of the rice genome 79


system, random overexpression of the Arabidopsis full-length<br />

cDNA is possible. Considering gene redundancy in rice and<br />

the availability of a large number of full-length cDNAs (Kikuchi<br />

et al 2003), we have begun producing FOX lines of rice in<br />

which 15,000 independent rice full-length cDNA are<br />

overexpressed under the control of the ubiquitin promoter (H.<br />

Ichikawa et al, unpublished results).<br />

References<br />

Agrawal GK, Yamazaki M, Kobayashi M, Hirochika R, Miyao A,<br />

Hirochika H. 2001. Screening of the rice viviparous mutants<br />

generated by endogenous retrotransposon Tos17 insertion:<br />

tagging of a zeaxanthin epoxidase gene and a novel OsTATC<br />

gene. Plant Physiol. 125:1248-1257.<br />

Hirochika H. 2001. Contribution of the Tos17 retrotransposon to<br />

rice functional genomics. Curr. Opin. Plant Biol. 4:118-122.<br />

Hirochika H, Guiderdoni E, An G, Hsing Y, Eun MY, Han CD,<br />

Upadhyaya N, Ramachandran S, Zhang Q, Pereira A,<br />

Sundaresan V, Leung H. 2004. <strong>Rice</strong> mutant resources for gene<br />

discovery. Plant Mol. Biol. 54:325-334.<br />

Jeong DH, An S, Kang HG, Moon S, Han JJ, Park S, Lee HS, An K,<br />

An G. 2002. T-DNA insertional mutagenesis for activation<br />

tagging in rice. Plant Physiol. 130:1636-1644.<br />

Kikuchi S et al. 2003. Collection, mapping, and annotation of over<br />

28,000 cDNA clones from japonica rice. Science 301:376-<br />

379.<br />

Liljegren SJ, Ditta GS, Eshed Y, Savidge B, Bowman JL, Yanofsky<br />

MF. 2000. SHATTERPROOF MADS-box genes control seed<br />

dispersal in Arabidopsis. Nature 404:766-770.<br />

Miyao A, Tanaka K, Murata K, Sawaki H, Takeda S, Abe K,<br />

Shinozuka Y, Onosato K, Hirochika H. 2003. Target site specificity<br />

of the Tos17 retrotransposon shows a preference for insertion<br />

within genes and against insertion in retrotransposonrich<br />

regions of the genome. Plant Cell 15:1771-1780.<br />

Sato Y, Sentoku N, Miura Y, Hirochika H, Kitano H, Matsuoka M.<br />

1999. Loss-of-function mutations in the rice homeobox gene<br />

OSH15 affect the architecture of internodes resulting in dwarf<br />

plants. EMBO J. 18:992-1002.<br />

Till BJ, Reynolds SH, Greene EA, Codomo CA, Enns LC, Johnson<br />

JE, Burtner AR, Young K, Taylor NE, Henikoff JG, Comai L,<br />

Henikoff S. 2003. Large-scale discovery of induced pointmutations<br />

with high-throughput TILLING. Genome Res.<br />

13:524-530.<br />

Notes<br />

Author’s address: Molecular Genetics Department, National <strong>Institute</strong><br />

of Agrobiological Sciences, Kannondai 2-1-2, Tsukuba,<br />

Ibaraki 305-8602, Japan, e-mail: hirohiko@nias.affrc.go.jp.<br />

Toward genome-wide transcriptional analysis<br />

in rice using MAS oligonucleotide tiling-path microarrays<br />

Lei Li, Xiangfeng Wang, Xueyong Li, Ning Su, Viktor Stolc, Bin Han, Jiayang Li, Yongbiao Xue, Jun Wang, and Xing Wang Deng<br />

As the international efforts to completely sequence the rice<br />

genome are nearly completed, an immediate challenge and<br />

opportunity for the plant community is to comprehensively and<br />

accurately annotate the rice genome. This will lay a solid foundation<br />

for rice functional genomics and proteomics. We report<br />

<strong>here</strong> our current strategy to use integrative approaches centered<br />

on whole-genome nucleotide tiling-path microarray and<br />

array-guided full-length cDNA analysis for conducting genome-wide<br />

transcriptional analysis. Preliminary results suggest<br />

that these experimental approaches are useful in verifying<br />

predicted rice gene models and in identifying a significant<br />

number of new transcriptional units that were simply missed<br />

from current annotation. The pilot results further indicate that<br />

array data-guided RT-PCR cloning of full-length cDNA is<br />

emerging as an effective protocol to provide the much-needed<br />

experimental verification for those rice genes that lacked previous<br />

cDNA support. Thus, success of our effort described<br />

<strong>here</strong>in is likely to result in a more accurate annotation of all<br />

rice genes in the genome.<br />

Current status of rice genome annotation<br />

Estimation of the total gene number in rice based upon the<br />

initial draft sequences of Oryza. sativa L. subsp. japonica and<br />

indica ranged widely from 30,000 to 60,000 (Goff et al 2002,<br />

Yu et al 2002). Finished sequences of chromosomes 1, 4, and<br />

10 allowed a much fine-tuned estimation that placed the total<br />

gene number of rice between 57,000 and 62,500 (Feng et al<br />

2002, Sasaki et al 2002, The <strong>Rice</strong> Chromosome 10 Sequencing<br />

Consortium 2003). Although the fast-accumulating finished<br />

sequences will ultimately come to a conclusion for the total<br />

gene number estimation, it should be noted that about half of<br />

those annotated gene models lack experimental support. Further,<br />

between one-third and one-half of the predicted genes<br />

appear to have no recognizable homology in Arabidopsis and<br />

features that exhibit striking deviations from experimentally<br />

verified genes in other species. T<strong>here</strong>fore, experimental efforts<br />

complementary to computer-based genome annotation are<br />

needed to verify predicted genes and to discover new genes in<br />

rice.<br />

80 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Tiling array/cDNA analysis<br />

Gene prediction<br />

Whole-genome<br />

tiling array<br />

Array data<br />

analysis<br />

<strong>Rice</strong> genome<br />

annotation<br />

Gene-finding programs<br />

Comparative genomics<br />

cDNA cloning/sequencing<br />

New bioinformatic tools<br />

Fig. 1. A proposed workflow for using tiling microarray to improve rice genome annotation. Current rice<br />

genome annotation efforts focus on ab initio gene prediction, comparative genomics, and other<br />

nonexperimental methods (block arrow on the right). Experiment-oriented approaches such as wholegenome<br />

tiling microarray and full-length cDNA analysis are emerging as complements to the computation-based<br />

methods (block arrow on the left). Arrowheads indicate the direction of information flow. See<br />

text for more details.<br />

<strong>Rice</strong> whole-genome tiling-path microarray<br />

One powerful and proven annotation approach complementary<br />

to ab initio gene prediction, comparative genomics, and<br />

other nonexperimental methods is whole-genome tiling-path<br />

microarray analysis coupled with array-guided cDNA cloning<br />

(Shoemaker et al 2001, Kapranov et al 2002, Yamada et al<br />

2003). Figure 1 illustrates the strategy of our effort to enhance<br />

the rice genome annotation using an integrative approach centered<br />

on tiling microarrays. Essential to our approach is the<br />

design and development of custom tiling microarrays that represent<br />

the whole rice genome. Given the size of the rice genome<br />

(approx. 430 Mb) and the repetitive nature of our experiments,<br />

a suitable tiling microarray should offer high feature<br />

density, versatility of modification, and compatibility with<br />

our existing conventional microarray facility. These considerations<br />

led us to choose the Maskless Array Synthesizer (MAS)<br />

platform developed by NimbleGen (www.nimblegen.com,<br />

Stolc et al 2004).<br />

In the initial phase, a minimum tiling strategy was designed<br />

to efficiently represent the genome with a minimum<br />

number of interrogating oligos employed that were strategically<br />

allocated to each potential gene such that expression of<br />

these genes can be unambiguously assayed. Implementation<br />

of this design required approximately 6.5 million pairs of interrogating<br />

oligos to tile essentially all the nonrepetitive sequences<br />

of the genome (Table 1), resulting in a resolution of a<br />

pair of 36-mer interrogating oligos every 60-bp genome sequence<br />

on average. Table 1 also shows the number of tiling<br />

oligo pairs for each of the 12 chromosomes. When synthesized<br />

at a density of 389,287 oligos per slide (Stolc et al 2004),<br />

the interrogating oligos that tile the japonica and indica genomes<br />

can be accommodated onto a set of 32 and 34 MAS<br />

arrays, respectively. It is expected that once the workflow of<br />

processing the minimum tiling arrays is streamlined, higherresolution<br />

arrays will be designed and used to further our analysis.<br />

Table 1. Estimation of 36-mer oligo pairs<br />

for a minimum tiling of the rice genomes.<br />

Chr.<br />

japonica<br />

Oligo pairs<br />

indica<br />

1 758,477 843,677<br />

2 638,666 678,379<br />

3 618,937 747,025<br />

4 563,693 597,322<br />

5 456,837 536,721<br />

6 526,611 551,022<br />

7 487,411 478,130<br />

8 469,369 514,189<br />

9 367,182 378,664<br />

10 375,141 419,408<br />

11 424,379 404,151<br />

12 440,214 390,756<br />

Total 6,126,917 6,539,444<br />

A pilot tiling array hybridization experiment<br />

To test the rice tiling array hybridization conditions, data acquisition,<br />

and analysis procedures, a pilot experiment was<br />

conducted in which two tiling arrays representing a portion of<br />

chromosome 10 were hybridized with mixed cDNA targets<br />

derived from four tissues: seedling root, seedling shoot, panicle,<br />

and suspension-cultured cells. Analysis of the array data detected<br />

expression of 77% of the reference gene models. Specifically,<br />

expression of 80.2% of the full-length cDNA matched<br />

genes (198 out of 247) and 70.9% (175 out of 247) of the<br />

genes without previous experimental support were detected.<br />

Thus, the cDNA-confirmed genes served as positive controls<br />

and demonstrated the sensitivity and feasibility of this approach.<br />

The relatively lower detection rate for the unsupported<br />

genes suggests that they are expressed at lower levels or restricted<br />

to specific cell types/developmental stages. Alterna-<br />

Session 2: Structure and function of the rice genome 81


tively, some of these predicted genes might be false models<br />

that do not exist in vivo.<br />

Integration of tiling array data to improve rice genome<br />

annotation<br />

The hybridization data of the tiling microarrays can be used to<br />

further rice genome annotation (Fig. 1). For example, the hybridization<br />

data can provide support to or verification of predicted<br />

genes without prior experimental support, as detection<br />

of hybridization signals is strongly indicative of RNA synthesis<br />

directed by the genome segment represented by the interrogating<br />

oligos. Thus, the information generated from tiling<br />

arrays can be used to improve genome annotation by means of<br />

array-guided RT-PCR cloning and analysis of corresponding<br />

cDNAs. Likewise, the array data are also expected to reveal<br />

novel transcriptional units (i.e., those that were not included<br />

in any annotation but were detected by tiling arrays). In this<br />

regard, the array data could serve as a guidepost for cloning<br />

the corresponding cDNA by means of RT-PCR (Fig. 1). Compared<br />

with sequencing library-based full-length cDNA clones,<br />

which is considered the standard of gene annotation (Kikuchi<br />

et al 2003), array-assisted cDNA cloning and analysis will be<br />

targeted, and thus be more cost-effective and inclusive to cover<br />

the remaining portion of the rice genome that lacks corresponding<br />

expressed sequences.<br />

Compilation of reference genes for tiling array analysis<br />

For the sake of simplicity, a set of BGI (Beijing Genome <strong>Institute</strong>)<br />

japonica gene models was used as the reference genes in<br />

the pilot trial (Stolc et al 2004). To effectively decode the tiling<br />

microarray hybridization data, however, reference genes<br />

are critically important, for which a comprehensive set of rice<br />

gene models is precisely anchored in the genomic sequences.<br />

A unique advantage in rice is the availability of multiple annotations<br />

such as the TIGR (The <strong>Institute</strong> for Genomic <strong>Research</strong>)<br />

japonica annotation (www.tigr.org/tdb/e2k1/osa1/) and<br />

the BGI indica and japonica annotations (http://<br />

rise.genomics.org.cn). While each annotation has its own forte<br />

and weakness, comparison and analysis of these annotations<br />

should yield a more comprehensive inventory of gene models<br />

to be evaluated by tiling arrays than any single annotation can<br />

offer. Reference gene compilation also takes advantage of the<br />

EST and full-length cDNA collections in the TIGR and the<br />

Kikuchi full-length cDNA data sets (http://<br />

cdna01.dna.affrc.go.jp/cDNA/). For example, the full-length<br />

cDNA-confirmed genes could naturally serve as positive controls<br />

to test array data and be used as training data to improve<br />

rice gene-finding algorithms (Fig. 1). Moreover, rice sequences<br />

have been subjected to extensive comparative genomic analysis<br />

with other cereals and other plant species. Closer and further<br />

inspection of those data should help to identify common<br />

and unique cereal genes and to integrate multiple annotations<br />

to provide a more comprehensive representation of the rice<br />

genome content (Fig. 1).<br />

Development of new bioinformatic tools to facilitate rice<br />

genome annotation<br />

It has been realized from the pilot experiments that new computational<br />

tools need to be developed and validated to interpret<br />

tiling data and facilitate incorporation of tiling data to<br />

improve rice genome annotation. For example, algorithms to<br />

ascertain transcription need to be improved by incorporating<br />

more statistical parameters. Reliable tiling data in turn will<br />

provide better training data to improve gene prediction and<br />

other rice bioinformatic tools to enhance genome annotation<br />

(Fig. 1). The tiling data can be used in conjunction with several<br />

other public-funded rice genomics projects to maximize<br />

the detection of rice genes expressed at different developmental<br />

stages or under diverse environmental conditions. Consequently,<br />

improved genome annotation will also permit better<br />

array design to probe subtle transcriptional events such as alternative<br />

splicing, differential initiation and termination, etc.<br />

Finally, to present the tiling data in an accessible and informative<br />

form, an interactive database is required w<strong>here</strong> the tiling<br />

data will be correlated with the complete genome sequence<br />

with all the annotated rice genes and other genomic features<br />

linked to cDNA/EST sequences and proteomic and structural<br />

information. Applying these approaches in rice should aid in<br />

the current genomic efforts to provide a complete and accurate<br />

rice genome annotation that holds the key to unravel the<br />

biology of the agriculturally important cereal crops.<br />

The current research on japonica rice genome tiling array<br />

analysis in the laboratory of Xing Wang Deng at Yale University<br />

is supported by a grant from the National Science Foundation<br />

plant genome program (DBI-0421675). The collaborative<br />

effort in China was supported by the 863 rice functional<br />

genomics program from the Ministry of Science and Technology<br />

of China.<br />

References<br />

Feng Q, Zhang YJ, Hao P, Wang SY, Fu G, Huang YC, Li Y, Zhu JJ,<br />

Liu YL, Hu X, et al. 2002. Sequence and analysis of rice chromosome<br />

4. Nature 420:316-320.<br />

Goff SA, Ricke D, Lan TH, Presting G, Wang RL, Dunn M,<br />

Glazebrook J, Sessions A, Oeller P, Varma H, et al. 2002. A<br />

draft sequence of the rice genome (Oryza sativa L. ssp.<br />

japonica). Science 296:92-100.<br />

Kapranov P, Cawley SE, Drenkow J, Bekiranov S, Strausberg RL,<br />

Fodor SPA, Gingeras TR. 2002. Large-scale transcriptional<br />

activity in chromosomes 21 and 22. Science 296:916-919.<br />

Kikuchi S, Satoh K, Nagata T, Kawagashira N, Doi K, Kishimoto N,<br />

Yazaki J, Ishikawa M, Yamada H, Ooka H, et al. 2003. Collection,<br />

mapping, and annotation of over 28,000 cDNA clones<br />

from japonica rice. Science 300:1566-1569.<br />

Sasaki T, Matsumoto T, Yamamoto K, Sakata K, Baba T, Katayose<br />

Y, Wu JZ, Niimura Y, Cheng ZK, Nagamura Y, et al. 2002.<br />

The genome sequence and structure of rice chromosome 1.<br />

Nature 420:312-316.<br />

82 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Shoemaker DD, Schadt EE, Armour CD, He YD, Garrett-Engele P,<br />

McDonagh PD, Loerch PM, Leonardson A, Lum PY, Cavet<br />

G, et al. 2001. Experimental annotation of the human genome<br />

using microarray technology. Nature 409:922-927.<br />

Stolc V, Li L, Wang X, Li X, Su N, Tongprasit W, Han B, Xue Y, Li<br />

J, Snyder M, Gerstein M, Wang J, Deng X-W. 2004. Towards<br />

genome wide transcriptional unit analysis in rice using oligonucleotide<br />

tiling-path microarrays. Plant Mol. Biol. (In press.)<br />

The <strong>Rice</strong> Chromosome 10 Sequencing Consortium. 2003. In-depth<br />

view of structure, activity, and evolution of rice chromosome<br />

10. Science 300:1566-1569.<br />

Yamada K, Lim J, Dale JM, Chen H, Shinn P, Palm CJ, Southwick<br />

AM, Wu HC, Kim C, Nguyen M, et al. 2003. Empirical analysis<br />

of transcriptional activity in the Arabidopsis genome. Science<br />

302:842-846.<br />

Yu J, Hu S, Wang J, Shu WG, Li S, Liu B, Deng Y, Dai L, Zhou Y,<br />

Zhang X, et al. 2002. A draft sequence of the rice genome<br />

(Oryza sativa L. ssp. indica). Science 296:79-92.<br />

Notes<br />

Authors’ addresses: Lei Li, Xueyong Li, Ning Su, and Xing Wang<br />

Deng, Department of Molecular, Cellular, and Developmental<br />

Biology, Yale University, New Haven, CT 06520;<br />

Xiangfeng Wang, National <strong>Institute</strong> of Biological Sciences,<br />

Zhongguacun Life Science Park, Beijing 102206, China;<br />

Xiangfeng Wang and Jun Wang, Beijing <strong>Institute</strong> of Genomics,<br />

Chinese Academy of Sciences, Beijing 101300, China;<br />

Xueyong Li and Yongbiao Xue, National Center of Crop Design,<br />

China Bioway Biotech Group Co., Ltd., Beijing 100085,<br />

China; Xiangfeng Wang and Ning Su, Peking-Yale Joint Center<br />

for Plant Molecular Genetics and Agrobiotechnology, College<br />

of Life Sciences, Peking University, Beijing 100871,<br />

China; Viktor Stolc, Genome <strong>Research</strong> Facility, NASA Ames<br />

<strong>Research</strong> Center, MS 239-11, Moffett Field, CA 94035; Bin<br />

Han, National Center for Gene <strong>Research</strong>, Shanghai <strong>Institute</strong>s<br />

for Biological Sciences, Chinese Academy of Sciences, 500<br />

Caobao Road, Shanghai 200233, China; Jiayang Li, <strong>Institute</strong><br />

of Genetics and Developmental Biology, Chinese Academy<br />

of Sciences, Datun Road, Beijing 100101, China, e-mail:<br />

xingwang.deng@yale.edu.<br />

Candidate gene characterization at the Pup1 locus: a major<br />

QTL increasing tolerance of phosphorus deficiency<br />

Matthias Wissuwa, Kristy Gatdula, and Abdelbagi Ismail<br />

Phosphorus (P) deficiency is a major yield-limiting factor for<br />

rice, particularly under upland or rainfed lowland conditions<br />

(Kirk et al 1998). P deficiency is frequently not due to low<br />

soil-P content in absolute terms but due to tight binding of<br />

soil-P in forms that are not readily available to the plant. The<br />

development of rice cultivars capable of using a higher portion<br />

of this fixed P already present in soils could be an attractive<br />

and cost-effective approach to increasing rice yields on P-<br />

deficient soils.<br />

One promising step toward the development of more P-<br />

efficient cultivars was the identification of the Pup1 locus in a<br />

QTL mapping population that was derived from rice cultivars<br />

Nipponbare (low P uptake) and Kasalath (high P uptake)<br />

(Wissuwa et al 2002). The effect of Pup1 was confirmed using<br />

a near-isogenic line (NIL) carrying the positive Pup1 allele<br />

from Kasalath in the Nipponbare genetic background. NIL-<br />

Pup1 had three to four times the P uptake from a highly P-<br />

fixing volcanic ash soil than Nipponbare with equally high<br />

effects on biomass accumulation and grain yield (see Okada<br />

and Wissuwa, this volume). Further analysis suggested that<br />

roots of NIL-Pup1 were slightly more efficient in extracting<br />

soil-bound P and that this advantage helped to maintain higher<br />

root growth rates, with additional benefits for P uptake<br />

(Wissuwa 2004).<br />

Candidate gene identification<br />

Efforts at <strong>IRRI</strong> are now directed toward identifying the gene(s)<br />

at the Pup1 locus. Further fine mapping of Pup1 has advanced<br />

considerably and Pup1 has now been mapped to a 195-kb interval<br />

spanning three BAC clones on chromosome 12 (Fig. 1).<br />

Gene annotation in the Pup1 region identified 31 putative<br />

genes. Only one of those is a known gene, w<strong>here</strong>as some sequence<br />

similarities to known genes exist for an additional four<br />

genes. The remaining annotations were for hypothetical proteins<br />

(13) and transposable elements (13). None of the sequence<br />

similarities suggested an association with processes involved<br />

in P uptake or metabolism. This would suggest that Pup1 is<br />

most likely a novel gene. It is also possible, however, that the<br />

gene is simply absent or highly distorted in Nipponbare, which<br />

would make annotations based on Nipponbare sequence data<br />

impossible.<br />

Gene-specific primers have been developed for the putative<br />

genes located in the Pup1 interval with the aim to investigate<br />

P-deficiency-induced expression patterns. Nipponbare<br />

and NIL-Pup1 were grown in nutrient solution with three levels<br />

of P supply: excess P (50 µM), low P (1 µM), and zero P.<br />

RNA was isolated from roots and shoots of 5-week-old plants.<br />

RT-PCR performed on transcribed RNA samples identified<br />

two candidate genes that showed differential expression depending<br />

on genotype and P supply (Fig. 2). Candidate gene #1<br />

Session 2: Structure and function of the rice genome 83


kb Line A B C<br />

M18<br />

50<br />

B<br />

AC<br />

1<br />

HG28<br />

134<br />

HG29<br />

141<br />

M50<br />

227<br />

B<br />

AC<br />

2<br />

Pup interval<br />

M59<br />

273<br />

T20<br />

329<br />

B<br />

AC<br />

3<br />

M69<br />

354<br />

Pup 1 region<br />

pseudomolecule<br />

Phenotype: N K K<br />

Genotype:<br />

Nipponbare<br />

Kasalath<br />

Fig. 1. Fine mapping of Pup1 to a 195-kb interval on chromosome 12, using selected<br />

recombinant lines. The phenotype of lines A and B places Pup1 upward of<br />

marker T20, while line C places Pup1 downward of HG28. The Pup1 interval spans<br />

three BAC clones and gene annotation identified 31 hypothetical genes in that<br />

region.<br />

Candidate gene #1<br />

Candidate gene #2<br />

N<br />

Pup1<br />

N<br />

Pup1<br />

N<br />

Pup1<br />

N<br />

Pup1<br />

N<br />

Pup1<br />

N<br />

Pup1<br />

High P Low P Zero P High P Low P Zero P<br />

Fig. 2. Expression patterns (RT-PCR) for two Pup1 candidate genes that are<br />

up-regulated by P deficiency in NIL-Pup1. In Nipponbare (N), gene #1 (at<br />

110 bp) was not expressed at all, w<strong>here</strong>as gene #2 (at 540 bp) was constitutively<br />

expressed. Expression analysis was conducted using root RNA<br />

sampled from 5-week-old plants that were grown in nutrient solution under<br />

three levels of P supply (50 µM P, 1 µM P, zero P).<br />

84 <strong>Rice</strong> is life: scientific perspectives for the 21st century


was not expressed in Nipponbare but expression was induced<br />

by P deficiency in NIL-Pup1. Further analysis suggests that<br />

this sequence codes for a small soluble protein (52 aa) most<br />

likely targeted for the nucleus. The second candidate gene follows<br />

a similar P-deficiency-induced expression pattern in NIL-<br />

Pup1, but, in this case, it is strongly and constitutively expressed<br />

in Nipponbare, regardless of P supply. The protein<br />

encoded by this gene contains one transmembrane helix. Further<br />

expression profiling using additional time points and a<br />

shoot-tissue control is currently being done and should provide<br />

a more detailed picture of these two candidate genes.<br />

That none of the annotated genes in the Pup1 region can<br />

be associated with genes known to be involved in P metabolism<br />

or uptake is unfortunate in terms of facilitating gene identification.<br />

However, this may not be very surprising considering<br />

that most genes related to P uptake that have been identified<br />

up to now, such as P transporters, phytases, or phosphatases,<br />

have been identified using low-P nutrient solutions<br />

as the screening medium. These genes do possess important<br />

functions in P metabolism and uptake but so far it has not been<br />

shown that they can be used to improve tolerance of P deficiency<br />

in the field. In contrast, Pup1 was mapped and its effect<br />

was confirmed in a P-deficient soil. This may be an indication<br />

that alleles most useful for improvements of abiotic stress<br />

tolerance of plants will have to be identified in natural environments.<br />

The positive effect of Pup1 on tolerance of P deficiency<br />

has repeatedly been confirmed in the field using NIL-Pup1.<br />

Recently, it has also been validated that this effect was not<br />

limited to a Nipponbare genetic background or to the specific<br />

soil conditions at the field site used to map and confirm the<br />

QTL. Following a cross to the donor parent Kasalath, Pup1<br />

was transferred into the background of two tropical rice cultivars,<br />

IR36 and IAC47. The introgression of Pup1 was monitored<br />

using flanking markers. Several introgression lines were<br />

evaluated together with a well-adapted local check variety at a<br />

P-deficient field site in the Philippines that had soil properties<br />

very different from those of the original field. The variability<br />

among introgression lines was high but a majority outperformed<br />

both recurrent parents. The best line exceeded the tolerant local<br />

check in grain yield by 26%. This represented a quite remarkable<br />

achievement considering that none of the lines had<br />

been selected at the test site. Given that variability among a<br />

small set of test lines was high, it appeared feasible to make<br />

additional gains through selection. This success has convinced<br />

breeders at <strong>IRRI</strong> to use the most promising introgression line<br />

as a donor to transfer the Pup1 locus to elite breeding material<br />

lacking tolerance of P deficiency.<br />

References<br />

Kirk GJD, George T, Courtois B, Senadhira D. 1998. Opportunities<br />

to improve phosphorus efficiency and soil fertility in rainfed<br />

lowland and upland rice ecosystems. Field Crops Res. 56:73-<br />

92.<br />

Wissuwa M. 2004. Combining a modelling with a genetic approach<br />

in establishing associations between genetic and physiological<br />

effects in relation to phosphorus uptake. Plant Soil. (In<br />

press.)<br />

Wissuwa M, Wegner J, Ae N, Yano M. 2002. Substitution mapping<br />

of Pup1: a major QTL increasing phosphorus uptake of rice<br />

from a phosphorus-deficient soil. Theor. Appl. Genet. 105:890-<br />

897.<br />

Notes<br />

Authors’ address: <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>, Los Baños,<br />

Philippines, e-mail: m.wissuwa@cgiar.org.<br />

Wrap-up of Session 2<br />

Extensive analysis of the rice genome in the last decade has led<br />

to the development of valuable tools that have contributed a great<br />

deal toward significant progress in rice molecular genetics. With<br />

the completion of a high-quality map-based sequence of the rice<br />

genome, it is expected that rice research will take on a new dimension.<br />

As reviewed by T. Sasaki of NIAS, the sequencing effort<br />

was organized in 1998 as a collaboration of 10 countries or regions,<br />

which made up the <strong>International</strong> <strong>Rice</strong> Genome Sequencing<br />

Project (IRGSP). By adopting a common strategy and sharing<br />

resources, the IRGSP successfully completed the sequencing of<br />

japonica rice variety Nipponbare at the end of 2004. This session<br />

highlighted research based on information derived from the<br />

genome sequence.<br />

M. Yano of NIAS described studies on map-based cloning<br />

of QTLs for rice heading date or flowering time. Heading date is a<br />

crucial characteristic for adaptation to different cultivation areas<br />

since rice is widely cultivated from the equatorial region to about<br />

40º N and S. This suggests the existence of several QTLs for rice<br />

heading date. M. Yano identified at least 14 QTLs for heading<br />

date and found out that about half of them were photoperiodsensitive<br />

genes. Using a series of chromosomal substitution lines<br />

as a resource for the cloning of each targeted gene of the photoperiod-sensitive<br />

genes, several, such as Hd1, Hd3a, Hd5, Ehd1,<br />

and Lhd4, have been isolated. The difference in sequences among<br />

these genes and their combination in rice varieties could explain<br />

the phenotype of heading date at each cultivation area. This strategy<br />

relies on genetic analysis and requires accurate genome sequence<br />

information to facilitate designing DNA markers that can<br />

be used to narrow down the candidate region of a targeted gene.<br />

The identification of genes or allelic diversity by reverse genetics<br />

methods also requires access to genome sequence information.<br />

Session 2: Structure and function of the rice genome 85


H. Leung of <strong>IRRI</strong> reviewed the importance of allelic diversity<br />

in evaluating a germplasm collection, which is a key factor in<br />

sustaining agricultural productivity. The ability to assess genetic<br />

variation in rice is enhanced by information on single nucleotide<br />

polymorphism (SNP). Since several germplasm collections exist<br />

for rice, information on SNPs of important phenotypes and the<br />

construction of a database are desirable for crop improvement.<br />

G. An of Pohang University of Science and Technology<br />

(POSTECH) in Korea and H. Hirochika of NIAS focused on artificial<br />

knockout of rice genes by insertional mutagenesis. G. An<br />

used a T-DNA mediated by Agrobacterium and the Ac/Ds system<br />

of maize for generating insertion mutants in rice. H. Hirochika<br />

used a rice endogenous retrotransposon, Tos17, as a tool. These<br />

insertion elements are preferentially inserted in the genome with<br />

T-DNA normally inserted into any genomic region and Tos17 mainly<br />

into genic regions. The utility of gene disruption lines depends on<br />

the degree of saturation of insertion. So far, 50,000 Tos17 mutant<br />

lines have been generated, but it is still necessary to increase<br />

the insertion points so that all the genes could be covered.<br />

However, this may not be feasible considering a relatively<br />

high redundancy of family genes in the rice genome. If one of the<br />

family genes is disrupted, the remaining genes might complement<br />

this disruption and the phenotype will not be altered. In<br />

addition, since activation of Tos17 is induced during tissue culture,<br />

the occurrence of somaclonal variation may obstruct the<br />

identification of affected phenotypes. When a novel phenotype is<br />

accompanied by this genomic rearrangement, the phenotype must<br />

be analyzed genetically and not by a reverse genetics method. In<br />

such cases, it is necessary to develop a novel method of in planta<br />

gene disruption or silencing to induce stable mutations.<br />

In the last five years, the correspondence between various<br />

phenotypes and genes has been widely explored using genetic<br />

and reverse genetics methods. The phenotypes associated with<br />

increased yield such as plant height and architecture, which are<br />

controlled by many genes, are well-known targets of breeding.<br />

The Green Revolution, which brought dramatic increases in cereal<br />

grain yields in the late 1960s, was due largely to reduced<br />

plant height, increased photosynthetic activity, and increased<br />

efficiency of fertilizer use for high yields. For rice, a mutant of<br />

semidwarfism (sd1) was used as a donor of reduced height of<br />

many rice varieties such as IR8 of <strong>IRRI</strong> and Reimei in Japan. M.<br />

Matsuoka of Nagoya University has identified many genes affecting<br />

rice plant height, including sd1, and revealed the outline of a<br />

signal transduction pathway of gibberellic acid, which is the key<br />

plant hormone controlling plant height. For wheat, another gene,<br />

Rht1, has been used for breeding a semidwarf plant. It has been<br />

reported that this gene is also involved in the signal transduction<br />

pathway of gibberellin. The corresponding locus of Rht1 in rice is<br />

known as slr1, which gives a mutation of slender phenotype.<br />

Both genes carry a mutation in molecular domains, which affect<br />

the perception of gibberellin and control the signal of this event<br />

to the next step. As documented by M. Matsuoka, our knowledge<br />

on the physiological interaction of gibberellin and rice genes<br />

is still limited and further studies on the molecular events in line<br />

with signal transduction of gibberellin are necessary. This must<br />

be implemented using the detailed genomic information on rice.<br />

Xing-Wang Deng of Yale University reported on a comparative<br />

tiling-path microarray analysis of the transcription units of<br />

both japonica and indica subspecies using 60-mer DNA chips.<br />

The genome-wide transcription analysis facilitated the identification<br />

of additional expression-supported gene models. Ideally, such<br />

an array is expected to detect a change in gene expression under<br />

various environmental or biotic stresses. In addition, a large-scale<br />

microarray covering the entire genome can be used to validate<br />

the expression of predicted genes in the genome sequence.<br />

The topics covered at this conference represent only some<br />

of the current focus in rice genetics and genomics. The completion<br />

of the rice genome sequence will pave the way for novel<br />

approaches in clarifying many biological phenomena. The molecular<br />

mechanisms for biotic and abiotic stresses can be elucidated<br />

by identifying the genes involved in these phenotypes. Also,<br />

linkage disequilibrium can be evaluated practically using the genome<br />

sequence to provide a novel tool for mapping important<br />

agronomic traits. It is expected that further advances in rice molecular<br />

genetics will promote ground-breaking research that will<br />

facilitate a complete understanding of the biology of rice, the<br />

inheritance of agronomically important traits, and the control of<br />

various biological pathways that are necessary to continually improve<br />

the rice plant.<br />

86 <strong>Rice</strong> is life: scientific perspectives for the 21st century


SESSION 3<br />

Opportunities and challenges<br />

of transgenic rice<br />

CONVENER: F. Takaiwa (NIAS)<br />

CO-CONVENERS: N. Oka (NIAS) and S. Datta (<strong>IRRI</strong>)


Overproduction of C 4<br />

enzymes in transgenic rice:<br />

an approach for improved photosynthesis and crop yield<br />

Mitsue Miyao-Tokutomi and Hiroshi Fukayama<br />

Most terrestrial plants, including many important crops, such<br />

as rice, wheat, soybean, and potato, assimilate CO 2 through<br />

the C 3 photosynthetic pathway and are classified as C 3 plants.<br />

However, some plants, such as maize and sugarcane, possess<br />

the C 4 photosynthetic pathway in addition to the C 3 pathway,<br />

and these are classified as C 4 plants. The C 4 pathway acts to<br />

concentrate CO 2 at the site of the reactions of the C 3 pathway,<br />

and thus inhibits photorespiration. This CO 2 -concentrating<br />

mechanism, together with modifications of leaf anatomy, enables<br />

C 4 plants to achieve high photosynthetic capacity and<br />

high water- and nitrogen-use efficiencies. As a consequence,<br />

the transfer of C 4 traits to C 3 plants is one strategy being adopted<br />

for improving the photosynthetic performance of C 3 plants.<br />

The C 4 pathway consists of three key steps: (1) the initial<br />

fixation of CO 2 in the mesophyll cell cytosol by phosphoenolpyruvate<br />

carboxylase (PEPC) to form a C 4 acid, (2)<br />

decarboxylation of a C 4 acid in the bundle-sheath cells to release<br />

CO 2 , and (3) regeneration of the primary CO 2 acceptor<br />

phosphoenolpyruvate in the mesophyll cell chloroplasts by<br />

pyruvate, orthophosphate dikinase (PPDK). The decarboxylation<br />

reaction is catalyzed by one or more of the three enzymes,<br />

namely, NADP-malic enzyme (NADP-ME), NADmalic<br />

enzyme, and phosphoenolpyruvate carboxykinase (PEP-<br />

CK). The enzymes involved in the C 4 pathway are also present<br />

in C 3 plants, probably mostly in the photosynthetic mesophyll<br />

cells, although their activities in C 3 plants are very low.<br />

In the leaves of C 3 plants, photosynthesis and subsequent<br />

carbon and nitrogen metabolism proceed mainly in the mesophyll<br />

cells. To have a significant effect on metabolism, any<br />

genes for C 4 enzymes (C 4 photosynthetic genes) introduced<br />

into C 3 plants will need to be expressed at high levels in these<br />

cells. A strategy based on the evolutionary scenario of C 4 genes<br />

has enabled C 4 enzymes to be expressed at high levels and in<br />

desired locations in the leaves of C 3 plants (Matsuoka et al<br />

2001, Miyao 2003).<br />

How to overproduce C 4<br />

enzymes<br />

in the mesophyll cells of C 3<br />

plants<br />

Recent comparative studies have revealed that C 3 plants have<br />

at least two different types of genes homologous to C 4 genes,<br />

one encoding enzymes of “housekeeping” function (C 3 -specific<br />

genes) and the other similar to the C 4 genes of C 4 plants<br />

(C 4 -like genes), though expression of the latter is very low or<br />

even undetectable in C 3 plants (Miyao 2003). It is now postulated<br />

that C 4 genes evolved from a set of preexisting counterpart<br />

genes in ancestral C 3 plants, with modifications at the site<br />

and in the level of expression in the leaves and kinetic proper-<br />

C 4 plant<br />

Ancestral<br />

C 4 plant<br />

C 4 -specific gene<br />

Enhancer elements<br />

Cell-specific elements<br />

Modification of kinetics<br />

C 4 -like gene<br />

Light-responsive elements<br />

Ancestral gene<br />

C 3 -specific gene<br />

C 3 -specific gene<br />

Fig. 1. A schematic representation of the evolution of C 4 -specific<br />

genes.<br />

ties of enzymes (Fig. 1; Miyao 2003). This hypothesis is based<br />

on previous observations that the promoters of the maize C 4 -<br />

specific PEPC and PPDK genes can drive high-level expression<br />

of a reporter gene in transgenic rice plants in an organspecific<br />

and mesophyll-cell-specific manner as in maize<br />

(Matsuoka et al 1993, 1994). It was found recently that this<br />

could also be the case for genes of C 4 enzymes located in the<br />

bundle-sheath cells of C 4 plants (see Miyao 2003). These findings<br />

have important implications that C 3 plants possess the<br />

regulatory factors necessary for high-level expression of C 4<br />

genes, and, more importantly, that the introduction of the intact<br />

C 4 -specific genes would lead to high-level expression of<br />

the C 4 enzymes in the leaves of C 3 plants.<br />

Enzymes located in the mesophyll cells of C 4<br />

plants<br />

The introduction of the intact maize C 4 -specific gene, which<br />

contained all exons and introns and its own promoter and terminator<br />

sequences, was effective in overproducing PEPC and<br />

PPDK in rice leaves (Ku et al 1999, Fukayama et al 2001).<br />

The activities of PEPC and PPDK in transgenic rice leaves<br />

increased up to 110-fold and 40-fold, respectively, that of<br />

nontransformants (Table 1). The level of the maize PEPC and<br />

PPDK proteins accounted for 12% and 35%, respectively, of<br />

total leaf soluble protein at most. In these transgenic rice plants,<br />

the levels of transcripts and protein and the activity of the introduced<br />

C 4 enzyme in the leaves all correlated well with the<br />

copy number of the introduced gene. In addition, the levels of<br />

transcripts per copy of the maize C 4 -specific gene were comparable<br />

in both maize and transgenic rice plants and the maize<br />

gene was expressed in a similar organ-specific manner. These<br />

observations suggest that the maize C 4 -specific genes behave<br />

in a qualitatively and quantitatively similar way in both maize<br />

and transgenic rice plants.<br />

88 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. Increase in activities of C 4 enzymes in transgenic rice leaves.<br />

C 4 enzyme<br />

Highest enzyme activity (increase in fold) a<br />

(location in C 4 plants) Introduced construct References<br />

Over rice activity Over maize activity<br />

PEPC (MC) Intact maize gene 110 3–4 Ku et al (1999)<br />

PPDK (MC) <strong>Rice</strong> Cab prom::maize FL C 4 cDNA 5


An approach for introducing the C 4<br />

pathway into rice leaves<br />

Overproduction of the maize C 4 -specific PEPC or PPDK did<br />

not affect the growth of rice plants, while that of the maize C 4 -<br />

specific NADP-ME led to stunting and bleaching of leaf color<br />

(Tsuchida et al 2001). This stunting was not suppressed by cooverproduction<br />

of any of the maize PEPC, the maize PPDK,<br />

and the sorghum NADP-malate dehydrogenase (NADP-<br />

MDH), or a combination of the three. Thus, the rice C 3 -specific<br />

NADP-ME instead of the maize C 4 -specific isoform has<br />

been adopted for the introduction of the C 4 pathway into rice.<br />

Transgenic rice plants overproducing three (PEPC, PPDK, and<br />

NADP-ME) or four enzymes (PEPC, PPDK, NADP-ME, and<br />

NADP-MDH) are now being produced.<br />

References<br />

Fukayama H, Hatch MD, Tamai T, Tsuchida H, Sudoh S, Furbank<br />

RT, Miyao M. 2003. Activity regulation and physiological<br />

impacts of the maize C 4 -specific phosphoenolpyruvate carboxylase<br />

overproduced in transgenic rice plants. Photosynth.<br />

Res. 77:227-239.<br />

Fukayama H, Tsuchida H, Agarie S, Nomura M, Onodera H, Ono K,<br />

Lee B-H, Hirose S, Toki S, Ku MSB, Makino A, Matsuoka<br />

M, Miyao M. 2001. Significant accumulation of C 4 -specific<br />

pyruvate, orthophosphate dikinase in a C 3 plant, rice. Plant<br />

Physiol. 127:1136-1146.<br />

Ku MSB, Agarie S, Nomura M, Fukayama H, Tsuchida H, Ono K,<br />

Hirose S, Toki S, Miyao M, Matsuoka M. 1999. High-level<br />

expression of maize phosphoenolpyruvate carboxylase in<br />

transgenic rice plants. Nat. Biotech. 17:76-80.<br />

Matsuoka M, Furbank RT, Fukayama H, Miyao M. 2001. Molecular<br />

engineering of C 4 photosynthesis. Annu. Rev. Plant Physiol.<br />

Plant Mol. Biol. 52:297-314.<br />

Matsuoka M, Kyozuka J, Shimamoto K, Kano-Murakami Y. 1994.<br />

The promoters of two carboxylases in a C 4 plant (maize) direct<br />

cell-specific, light-regulated expression in a C 3 plant (rice).<br />

Plant J. 6:311-319.<br />

Matsuoka M, Tada Y, Fujimura T, Kano-Murakami Y. 1993. Tissuespecific<br />

light-regulated expression directed by the promoter<br />

of a C 4 gene, maize pyruvate, orthophosphate dikinase, in a<br />

C 3 plant, rice. Proc. Natl. Acad. Sci. USA 90:9586-9590.<br />

Miyao M. 2003. Molecular evolution and genetic engineering of C 4<br />

photosynthetic enzymes. J. Exp. Bot. 54:179-189.<br />

Miyao-Tokutomi M, Fukayama H, Tamai T, Matsuoka M. 2001. Highlevel<br />

expression of C 4 photosynthesis enzymes in transgenic<br />

rice. In: PS2001 Proceedings, 12th <strong>International</strong> Congress on<br />

Photosynthesis, S39-001. Canberra (Australia): CSIRO Publishing.<br />

Tsuchida H, Tamai T, Fukayama H, Agarie S, Nomura M, Onodera<br />

H, Ono K, Nishizawa Y, Lee B-H, Hirose S, Toki S, Ku MSB,<br />

Matsuoka M, Miyao M. 2001. High-level expression of C 4 -<br />

specific NADP-malic enzyme in leaves and impairment of<br />

photoautotrophic growth of a C 3 plant, rice. Plant Cell Physiol.<br />

42:138-145.<br />

Notes<br />

Authors’ address: Photosynthesis Laboratory, National <strong>Institute</strong> of<br />

Agrobiological Sciences, Kannondai, Tsukuba 305-8602, Japan.<br />

The uptake and translocation of minerals in rice plants<br />

Naoko K. Nishizawa<br />

The uptake and translocation of metal nutrients in plants are<br />

essential for plant growth and, since plants are the primary<br />

source of food for humans, the nutritional value of plants is of<br />

central importance to human health. The most widespread human<br />

nutritional problem in the world is iron (Fe) deficiency<br />

(WHO 2003). Increasing the ability of plants to provide higher<br />

levels of minerals, such as Fe, will have a dramatic impact on<br />

human health. Increasing the Fe uptake from soils is a prerequisite<br />

to increase the amount of Fe in the edible parts of plants.<br />

This can be aided by identifying the transporters involved in<br />

the translocation of Fe within plants.<br />

Despite its abundance in soils, much Fe is present in the<br />

insoluble Fe(III) form and not readily available to plants. T<strong>here</strong>fore,<br />

plants have evolved two distinct uptake strategies<br />

(Marschner et al 1986). Graminaceous plants use a chelation<br />

strategy and release low-molecular-weight compounds,<br />

phytosiderophores, from their roots to chelate Fe(III) in the<br />

soil (Takagi 1976). Three molecules of S-adenosyl-methionine<br />

are combined with nicotianamine synthase (NAS) to form<br />

nicotianamine (NA) in both graminaceous and<br />

nongraminaceous plants (Mori and Nishizawa 1987, Shojima<br />

et al 1990). In graminaceous plants, the amino group of NA is<br />

transferred by nicotianamine aminotransferase (NAAT), and<br />

the resultant keto form is reduced to deoxymugineic acid<br />

(DMA) and other mugineic acid family phytosiderophores<br />

(MAs). <strong>Rice</strong> secretes DMA, the first member of MAs. A recent<br />

study showed that transgenic rice containing NAAT genes<br />

from barley is more tolerant than nontransgenic individuals of<br />

low-Fe availability in calcareous soil since transgenic rice<br />

plants secrete higher amounts of MAs than do wild-type plants<br />

(Takahashi et al 2001).<br />

All other plant groups use a reduction strategy composed<br />

of Fe(III) reductase and Fe(II) transporter. They do not produce<br />

or release phytosiderophores. However, nongraminaceous<br />

plants synthesize NA, which is the biosynthetic precursor of<br />

MAs and structurally similar. NA chelates metal cations, including<br />

Fe(II) and Fe(III). Unlike MAs, NA is not secreted,<br />

and is thought to have a role in metal homeostasis in<br />

nongraminaceous plants. Since Higuchi et al (1999) isolated<br />

the first NAS gene from Hordeum vulgare, NAS genes have<br />

90 <strong>Rice</strong> is life: scientific perspectives for the 21st century


A<br />

ZmYS1<br />

OsYSL16<br />

OsYSL2<br />

OsYSL9<br />

OsYSL15<br />

B<br />

Root<br />

+Fe<br />

–Fe<br />

+Fe<br />

Leaf<br />

–Fe<br />

OsYSL2<br />

OsYSL10<br />

OsYSL5<br />

OsYSL11<br />

OsYSL6<br />

OsYSL6<br />

OsYSL13<br />

OsYSL14<br />

OsYSL13<br />

OsYSL12<br />

OsYSL14<br />

OsYSL7<br />

OsYSL15<br />

OsYSL17<br />

OsYSL18<br />

OsYSL8<br />

OsYSL1<br />

OsYSL16<br />

rRNA<br />

0.1<br />

OsYSL3<br />

OsYSL4<br />

Fig. 1. (A) The unrooted phylogenic tree for the 18 OsYSL amino acid sequences. ZmYS1 is the Fe(III)-phytosiderophore<br />

transporter from maize. (B) RNA gel-blot analysis of OsYSL transcripts in Fe-sufficient and Fe-deficient rice plants. Only the<br />

expression of OsYSL2, OsYSL6, OsYSL13, OsYSL14, OsYSL15, and OsYSL16 was detected in these plants. The bottom panel<br />

shows ethidium bromide-stained rRNA as a loading control. +Fe: Fe-sufficient plants, –Fe: Fe-deficient plants.<br />

been isolated from barley again, and from tomato, Arabidopsis<br />

thaliana, rice, and maize. In graminaceous plants, the Fe(III)-<br />

phytosiderophore complex is taken up by a specific transporter<br />

at the root surface. Maize yellow stripe 1 (YS1) is the gene<br />

encoding the Fe(III)-phytosiderophore transporter (Curie et al<br />

2001).<br />

Our search for YS1 homologues in the Oryza sativa L.<br />

subsp. japonica (cv. Nipponbare) rice genomic database identified<br />

18 putative YS1-like genes (OsYSL) that exhibited 36%<br />

to 76% sequence similarity to YS1 (Koike et al 2004) (Fig.<br />

1A). Further, we examined whether Fe regulates the expression<br />

of these genes in rice (Fig. 1B). Using Northern blot analysis,<br />

the transcripts of six genes were detected in roots or leaves<br />

of Fe-sufficient or Fe-deficient rice plants. OsYSL6 was constitutively<br />

expressed in both the roots and leaves of either Fesufficient<br />

or Fe-deficient plants, with Fe deficiency slightly<br />

reducing its expression. OsYSL13 was preferentially expressed<br />

in the shoots, and Fe deficiency reduced its expression.<br />

OsYSL14 was expressed in both roots and shoots, and Fe status<br />

had no effect on its expression. OsYSL15 was expressed<br />

only in roots and the expression was highly induced by Fe<br />

deficiency. OsYSL16 was expressed in both roots and shoots,<br />

and the expression in roots was slightly increased by Fe deficiency.<br />

We could not detect the transcripts of other members<br />

of OsYSLs in these plants by Northern blot analysis.<br />

The high expression of OsYSL2 in the leaves but not in<br />

the roots of Fe-deficient plants led us to hypothesize that<br />

OsYSL2 is a transporter involved in the long-distance transport<br />

of Fe in rice, but is not a rice Fe(III)-phytosiderophore<br />

for iron uptake from the soil. Based on the nucleotide sequence,<br />

OsYSL2 was predicted to encode a polypeptide of 674<br />

amino acids containing 14 putative transmembrane domains.<br />

Subcellular localization of OsYSL2 and green fluorescent protein<br />

(GFP), together with the presence of the putative transmembrane<br />

domains, showed that OsYSL2 is a transporter that<br />

is localized in the plasma membrane.<br />

The cell-type specificity of OsYSL2 expression was investigated<br />

using promoter (1.5 kb):β-glucuronidase (GUS)<br />

analysis. Although Northern blot analysis did not detect OsYSL2<br />

transcripts in the roots, GUS staining resulting from OsYSL2<br />

promoter activity showed a dotted pattern in phloem companion<br />

cells in the central cylinder of Fe-sufficient roots. The activity<br />

in companion cells increased in Fe-deficient roots, but<br />

no GUS staining was observed in epidermal or cortical cells,<br />

even in Fe-deficient roots. This absence of OsYSL2 promoter<br />

activity in the root epidermis or cortex supports the contention<br />

that OsYSL2 is not an Fe(III)-phytosiderophore transporter<br />

involved in the uptake of Fe from the soil. GUS staining was<br />

observed in phloem cells of the vascular bundles of leaves and<br />

leaf sheaths of Fe-sufficient rice. The phloem-specific expression<br />

of the OsYSL2 promoter suggested that OsYSL2 is involved<br />

in the phloem transport of Fe. In Fe-deficient leaves, the<br />

OsYSL2 promoter was active in all tissues, with particularly<br />

strong GUS activity evident in companion cells. Since the re-<br />

Session 3: Opportunities and challenges of transgenic rice 91


productive organs are major sinks for Fe and are important in<br />

supplying Fe for human needs, we examined OsYSL2 expression<br />

in flowers and developing seeds. The OsYSL2 promoter<br />

was active during reproductive development in rice.<br />

We examined the transport activity and substrate specificity<br />

of OsYSL2 using Xenopus laevis oocytes. OsYSL2 was<br />

heterologously expressed in the oocytes and the substrate-induced<br />

inward currents at –60 mV were measured in response<br />

to several related compounds. Surprisingly, OsYSL2 transported<br />

Fe(II)-NA and Mn(II)-NA, but did not transport Fe(III)-DMA<br />

or Mn(II)-DMA. This suggested, t<strong>here</strong>fore, that OsYSL2 is a<br />

metal-NA transporter in rice but not an Fe(III)-DMA transporter.<br />

These studies with rice have established that OsYSL2 is<br />

an Fe-regulated metal-NA transporter that is involved in<br />

phloem transport and the translocation of mineral nutrients in<br />

grains. The presence of a metal-NA transporter in rice and its<br />

expression in the phloem companion cells clearly demonstrated<br />

that metals, at least Fe and Mn, are transported in the phloem<br />

as NA complexes. Together with the expression of OsNAS3 in<br />

the leaves of Fe-sufficient plants, these results suggest that NA<br />

functions in intracellular delivery of Fe as well as in its<br />

phloem transport. The expression of OsYSL2 in reproductive<br />

organs also suggests that translocation of Fe into grains is mediated<br />

by NA and that manipulating OsYSL2 and OsNAS3<br />

changes the Fe content in rice grains.<br />

This is the first identification of a metal-NA transporter,<br />

OsYSL2, involved in long-distance transport of Fe and accumulation<br />

of Fe in grains. Our results with rice, along with those<br />

of previous studies with tobacco (Takahashi et al 2003), provide<br />

molecular evidence that NA is a chelator that mediates<br />

metal transport in the phloem and regulates intracellular metal<br />

distribution in graminaceous and dicotyledonous plants. Furthermore,<br />

these results indicate that higher plants have a single<br />

strategy for the phloem transport of Fe, although graminaceous<br />

plants and other plant groups have different strategies for Fe<br />

uptake from the soil.<br />

An approach to produce rice plants that can tolerate Fe<br />

deficiency would be the alteration of the expression patterns<br />

of genes that regulate Fe homeostasis. T<strong>here</strong>fore, we aimed to<br />

make superpromoters highly responsive to Fe deficiency by<br />

combining the recently identified IDE1 and IDE2 elements<br />

with other enhancer-like sequences to enhance gene expression<br />

in Fe-deficient roots of rice plants (Kobayashi et al 2004).<br />

Fe deficiency-responsive element 1 (IDE1) and IDE2 are cisacting<br />

elements that are responsible for Fe-deficiency-inducible<br />

and root-specific expression of the barley (H. vulgare L.)<br />

gene IDS2 (Fe-deficiency-specific clone no. 2) (Kobayashi et<br />

al 2003). Modules containing IDE1 and IDE2 of the IDS2 promoter<br />

were used as repeats or were linked to the Fe-deficiencyresponsive<br />

promoter of barley IDS3 (Fe-deficiency-specific<br />

clone no. 3), and were connected to known enhancer-like sequences.<br />

Five artificial promoters, as well as the native promoters<br />

of barley IDS2 or IDS3, were connected individually<br />

upstream of GUS and were introduced into rice (Fig. 2).<br />

Transgenic rice plants were grown under control or Fe-deficient<br />

conditions, and GUS expression was analyzed. The artificial<br />

promoter that contained one module of IDE1 and IDE2<br />

conferred strong Fe-deficiency-inducible GUS expression to<br />

the roots of rice plants. The artificial promoters induced prominent<br />

gene expression in Fe-deficient rice plant roots, although<br />

the repetition of the elements had no obvious effect. Histochemical<br />

observations revealed that GUS expression driven<br />

by artificial and native promoters was spatially similar, and<br />

expression was dominant within vascular bundles and root exodermis.<br />

These findings suggest that t<strong>here</strong> is coordinated expression<br />

of the genes that are involved in Fe-deficiency-induced<br />

Fe uptake in rice. This supports the possibility that a<br />

common mechanism regulates the expression of graminaceous<br />

genes that are involved in Fe acquisition. We propose that it<br />

would be advantageous to use the artificial and native promoters<br />

of IDS2 and IDS3 to produce crops that are tolerant of Fe<br />

deficiency.<br />

References<br />

Curie C, Panaviene Z, Loulergue C, Dellaporta SL, Briat JF, Walker<br />

EL. 2001. Maize yellow stripe 1 encodes a membrane protein<br />

directly involved in Fe(III) uptake. Nature 409:346-349.<br />

Higuchi K, Suzuki K, Nakanishi H, Yamaguchi H, Nishizawa NK,<br />

Mori S. 1999. Cloning of nicotianamine synthase genes, novel<br />

genes involved in the biosynthesis of phytosiderophores. Plant<br />

Physiol. 119:471-479.<br />

Kobayashi T, Nakayama Y, Itai RN, Nakanishi H, Yoshihara T, Mori<br />

S, Nishizawa NK. 2003. Identification of novel cis-acting elements,<br />

IDE1 and IDE2, of the barley IDS2 gene promoter<br />

conferring iron-deficiency-inducible, root-specific expression<br />

in heterogeneous tobacco plants. Plant J. 36:780-793.<br />

Kobayashi T, Nakayama Y, Takahashi M, Inoue H, Nakanishi H,<br />

Yoshihara T, Mori S, Nishizawa NK. 2004. Construction of<br />

artificial promoters highly responsive to iron deficiency. Soil<br />

Sci. Plant Nutr. (In press.)<br />

Koike S, Inoue H, Mizuno D, Takahashi M, Nakanishi H, Mori S,<br />

Nishizawa NK. 2004. OsYSL2 is a rice metal-nicotianamine<br />

transporter that is regulated by iron and expressed in the<br />

phloem. Plant J. 39:415-424.<br />

Marschner H, Römheld V, Kissel M. 1986. Different strategies in<br />

higher plants in mobilization and uptake of iron. J. Plant Nutr.<br />

9:695-713.<br />

Mori S, Nishizawa N. 1987. Methionine as a dominant precursor of<br />

phytosiderophores in Graminaceae plants. Plant Cell Physiol.<br />

28:1081-1092.<br />

Shojima S, Nishizawa NK, Fushiya S, Nozoe S, Irifune T, Mori S.<br />

1990. Biosynthesis of phytosiderophores: in-vitro biosynthesis<br />

of 2′-deoxymugineic acid from L-methionine and<br />

nicotianamine. Plant Physiol. 93:1497-1503.<br />

Takagi S. 1976. Naturally occurring iron-chelating compounds in<br />

oat- and rice-root washing. I. Activity measurement and preliminary<br />

characterization. Soil Sci. Plant Nutr. 22:423-433.<br />

Takahashi M, Nakanishi H, Kawasaki S, Nishizawa NK, Mori S.<br />

2001. Enhanced tolerance of rice to low iron availability in<br />

alkaline soils using barley nicotianamine aminotransferase<br />

genes. Nature Biotech. 19:466-469.<br />

92 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Fig. 2. Sequence comparison of IDE1 with other Fe-deficiency-inducible promoters<br />

and IDE2. IDS2 IDE1+ represents IDE1 and its 3′-flanking 4 bp, which is strikingly<br />

conserved in the HvNAAT promoters. The palindromic sequence in IDE1 is indicated<br />

with a red box and arrowhead. Brackets in IDE1 and IDE2 indicate the sites of mutations<br />

in linker-scanning analysis. Orange letters indicate sequences identical to<br />

IDE1+. The distances (in bp) from the translation start sites are shown in parentheses.<br />

Sequences highly homologous to IDE1 were found in many other Fe-deficiencyinducible<br />

promoters. A sequence highly homologous to IDE1 was also found at –772/<br />

–789 of the IDS2 promoter itself. IDE2 was also homologous to IDE1 and its 3′-<br />

flanking 4 bp. Neither IDE1 nor IDE2 showed substantial homology to other known<br />

cis-acting elements involved in Fe metabolism or root-specific expression. HvNAAT-<br />

A and HvNAAT-B, barley nicotianamine aminotransferase genes; HvNAS1, barley<br />

nicotianamine synthase gene; HvIDS3, barley Fe-deficiency-specific clone no. 3<br />

(mugineic acid synthase gene); OsNAS1 and OsNAS2, rice nicotianamine synthase<br />

genes; OsIRT1, rice ferrous Fe transporter gene; AtFRO2, Arabidopsis thaliana ferric-chelate<br />

reductase gene; AtIRT1, A. thaliana ferrous Fe transporter gene; AtNAS1,<br />

AtNAS2, and AtNAS4, A. thaliana nicotianamine synthase genes. IDE1 and IDE2 are<br />

novel cis-acting elements. Conserved cis-acting elements homologous to IDE1 and<br />

IDE2, along with cognate trans-acting factors, may function in various genes and<br />

plant species.<br />

Takahashi M, Terada Y, Nakai I, Nakanishi H, Yoshimura E, Mori S,<br />

Nishizawa NK. 2003. Role of nicotianamine in the intracellular<br />

delivery of metals and plant reproductive development.<br />

Plant Cell. 15:1263-1280.<br />

WHO (World Health Organization). 2003. www.who.int/nut/ida.htm.<br />

Notes<br />

Author’s addresses: Graduate School of Agricultural and Life Sciences,<br />

The University of Tokyo, 1-1 Yayoi, Bunkyo-ku, Tokyo<br />

113-8657, Japan, and Core <strong>Research</strong> for Evolutional Science<br />

and Technology (CREST), e-mail: annaoko@mail.ecc.utokyo.ac.jp.<br />

Session 3: Opportunities and challenges of transgenic rice 93


Improving drought and cold-stress tolerance<br />

in transgenic rice<br />

Kazuko Yamaguchi-Shinozaki and Kazuo Shinozaki<br />

Drought, high salinity, and freezing are environmental conditions<br />

that have adverse effects on plant growth and crop productivity.<br />

Plants respond and adapt to these stresses to survive<br />

under stress conditions at the molecular and cellular levels as<br />

well as at the physiological and biochemical levels. Expression<br />

of a variety of genes is induced by these stresses in diverse<br />

plants. The products of these genes are thought to function<br />

not only in stress tolerance but also in the regulation of<br />

gene expression and signal transduction in stress responses<br />

(Shinozaki et al 2003).<br />

Genetic engineering is useful for improving the stress<br />

tolerance of plants. Several different approaches have been<br />

attempted to improve the stress tolerance of plants by gene<br />

transfer (Shinozaki et al 2003). The genes selected for transformation<br />

were those involved in encoding enzymes required<br />

for the biosynthesis of various osmoprotectants. Other genes<br />

that have been selected for transformation include those that<br />

encoded enzymes for modifying membrane lipids, LEA protein,<br />

and detoxification enzymes. In all these experiments, a<br />

single gene for a protective protein or an enzyme was<br />

overexpressed under the control of the constitutive 35S cauliflower<br />

mosaic virus (CaMV) promoter in transgenic plants,<br />

although several genes have been shown to function in environmental<br />

stress tolerance and response. The genes encoding<br />

protein factors that regulate gene expression and signal transduction<br />

and that function in stress responses may be useful for<br />

improving the tolerance of plants of stresses by gene transfer<br />

as they can regulate many stress-inducible genes involved in<br />

stress tolerance.<br />

DREB/DRE regulon in Arabidopsis<br />

To understand the molecular process of signal transduction<br />

from the perception of the stresses to gene expression, we isolated<br />

many environmental stress-inducible genes in Arabidopsis<br />

thaliana. The products of these genes are thought to function<br />

not only in stress tolerance but also in the regulation of gene<br />

expression and in signal transduction in the stress response.<br />

These gene products can be classified into two groups. The<br />

first group includes proteins that probably function in protecting<br />

cells from dehydration. The second group of gene products<br />

contains protein factors that are involved in further regulation<br />

of gene expression and signal transduction and that function<br />

in stress response (Shinozaki et al 2003).<br />

We analyzed the expression of the drought-inducible<br />

genes and identified at least four independent regulatory systems<br />

in drought-responsive gene expression: two are ABAdependent<br />

and two are ABA-independent. In one of the ABA-<br />

independent pathways, a cis-acting element with nine base pairs<br />

(TACCGACAT), named the dehydration-responsive element<br />

(DRE), is involved in dehydration, and high-salt and low-temperature–induced<br />

gene expression (Yamaguchi-Shinozaki and<br />

Shinozaki 1994).<br />

Two cDNA clones that encode DRE-binding proteins,<br />

DREB1A/CBF3 and DREB2A, were isolated by using yeast<br />

one-hybrid screening (Liu et al 1998). cDNA clones encoding<br />

two DREB1A homologs (named DREB1B/CBF1 and<br />

DREB1C/CBF2) and one DREB2A homolog (DREB2B) were<br />

also isolated (Liu et al 1998). Expression of the DREB1A gene<br />

and its two homologs was induced by low-temperature stress,<br />

w<strong>here</strong>as expression of the DREB2A gene and its homolog was<br />

induced by dehydration. These results indicate that two independent<br />

families of DREB proteins, DREB1 and DREB2, function<br />

as trans-acting factors in two separate signal transduction<br />

pathways under low-temperature and dehydration conditions,<br />

respectively.<br />

Overexpression of the cDNA encoding DREB1A in<br />

transgenic Arabidopsis plants activated the expression of many<br />

of these stress-tolerance genes under normal growing conditions<br />

and resulted in improved tolerance of drought, salt loading,<br />

and freezing (Liu et al 1998, Kasuga et al 1999). To identify<br />

target stress-inducible genes of DREB1A, we performed<br />

microarray analysis. We searched for downstream genes in<br />

transgenic plants overexpressing DREB1A using the full-length<br />

cDNA microarray and GeneChip array. We identified more<br />

than 40 genes as the DREB1A downstream genes (Seki et al<br />

2001, Maruyama et al 2004). The products of these genes were<br />

not only proteins known to function against stress but also<br />

protein factors involved in further regulation of signal transduction<br />

and gene expression in response to stress.<br />

However, use of the strong constitutive CaMV 35S promoter<br />

to drive expression of DREB1A also resulted in severe<br />

growth retardation under normal growing conditions. In contrast,<br />

expression of DREB1A from the stress-inducible rd29A<br />

promoter gave rise to minimal effects on plant growth while<br />

providing an even greater tolerance of stress conditions than<br />

did expression of the gene from the CaMV 35S promoter<br />

(Kasuga et al 1999). We also analyzed the effect of<br />

overexpression of DREB1A on stress tolerance and growth<br />

retardation in transgenic tobacco plants using the constitutive<br />

CaMV 35S promoter and the stress-inducible rd29A promoter<br />

(Kasuga et al 2004). Overexpression of DREB1A improved<br />

drought- and low-temperature stress tolerance in tobacco. The<br />

stress-inducible rd29A promoter minimized the negative effects<br />

on plant growth in tobacco. These results indicate that<br />

the stress-inducible rd29A promoter and the DREB1A gene<br />

94 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. List of characterized and predicted OsDREB genes from Oryza sativa var. japonica.<br />

Gene name Amino acid Genomic sequence Chromosome mRNA<br />

residues acc. no. no.<br />

OsDREB1A 238 – – AF300970, AY345233,<br />

AF494422, AK071519,<br />

AK105599<br />

OsDREB1B 218 – – AF300972, AY319971<br />

OsDREB1C 214 AP002838, AP001168 6 AY327040<br />

OsDREB1D 253 AP002536, AB023482 6 AF243384, AY345235<br />

OsDREB1E 236 AP004163, a AP004632 8<br />

OsDREB1F 219 AP003448 1 AY345234<br />

OsDREB1G 219 AL606640 4 AY114110<br />

OsDREB1H 224 AP005775, AP006060 2 AK106041, AK060550<br />

OsDREB1I 251 AP004163, b AP004632 8<br />

OsDREB2A 274 AP003301 1 AF300971, AK067313<br />

OsDREB2B 298 AC134927, AC134928 5 AK099221, AK071850<br />

OsDREB2C 230 AP004623 8 AY339375, AK108143<br />

OsDREB2D 261 AC135924 5 AK103822, AK102559<br />

a<br />

AP004162 15673 base–14966 base. b AP004162 19564 base–18812 base.<br />

are quite useful for improving drought, salt, and freezing stress<br />

tolerance not only in Arabidopsis but also in other kinds of<br />

dicot plants.<br />

DREB/DRE regulon in rice<br />

<strong>Rice</strong>, an important crop plant, has now emerged as an ideal<br />

model species for the study of crop genes because of its commercial<br />

value, relatively small genome size (approx. 430 Mb),<br />

diploid origin (2x=24), and close relationship with other important<br />

cereal crops. It is important to analyze the DRE/DREB<br />

(CRT/CBF) regulon in rice to understand the molecular mechanisms<br />

of stress tolerance and produce monocots with higher<br />

stress tolerance by gene transfer. We isolated five cDNAs for<br />

DREB homologs, OsDREB1A, 1B, 1C, 1D, and 2A, and analyzed<br />

their functions in rice (Dubouzet et al 2003). The<br />

OsDREB proteins were specifically bound to the DRE sequence<br />

and activated the transcription of a GUS reporter gene<br />

driven by the DRE sequence in rice protoplasts. Expression of<br />

the OsDREB1A and 1B genes was induced by low-temperature<br />

stress, w<strong>here</strong>as the expression of the OsDREB2A gene<br />

was induced by dehydration. Recently, we searched the rice<br />

genome database for amino acid sequences of the ERF/AP2<br />

domains of DREB and ERF, and found an additional five<br />

DREB1A homologs, OsDREB1E, OsDREB1F, OsDREB1G,<br />

OsDREB1H, and OsDREB1I, and three DREB2A homologs,<br />

OsDREB2B, OsDREB2C, and OsDREB2D, in rice (Table 1).<br />

We generated transgenic Arabidopsis overexpressing the<br />

OsDREB1A cDNA. The rice OsDREB1A protein exhibits a<br />

function similar to that of the Arabidopsis DREB1A protein in<br />

transgenic Arabidopsis plants (Dubouzet et al 2003). We also<br />

generated transgenic rice plants overexpressing the rice<br />

OsDREB or Arabidopsis DREB cDNAs and analyzed their<br />

tolerance of drought, high-salt, and cold stress. These transgenic<br />

plants showed high tolerance of these stresses.<br />

On the other hand, we carried out microarray analysis<br />

using rice cDNAs to identify stress-inducible genes in response<br />

to dehydration, high salt, and low temperature in rice (Rabbani<br />

et al 2003). We confirmed stress-inducible expression of the<br />

candidate genes selected by microarray analysis using RNA<br />

gel-blot analysis, and finally identified a total of 73 genes as<br />

stress-inducible genes in rice (Fig. 1). Among them, 36, 62,<br />

57, and 43 genes were induced by cold, drought, high salinity,<br />

and ABA, respectively. The products of the identified rice genes<br />

are classified into functional proteins and regulatory proteins<br />

like those of Arabidopsis (Rabbani et al 2003). Comparative<br />

analysis of stress-inducible genes in Arabidopsis and rice revealed<br />

a considerable level of similarity in stress responses<br />

between the two genomes at a molecular level. Among 73 identified<br />

stress-inducible genes in rice, 51 have already been reported<br />

in Arabidopsis with a similar function or gene name.<br />

These results indicate that rice has many stress-inducible genes<br />

in common with Arabidopsis, even though these two plants<br />

evolved separately a million years ago. Common stress-inducible<br />

genes include LEA proteins, antifreeze proteins, detoxification<br />

enzymes, and so on. All these genes are up-regulated in<br />

response to at least one of the abiotic stresses in rice and reported<br />

as stress-inducible genes in Arabidopsis. Transcriptome<br />

analysis of rice also revealed novel stress-inducible genes,<br />

suggesting some differences between Arabidopsis and rice in<br />

their response to stress.<br />

We analyzed expression of the stress-inducible genes<br />

identified by the cDNA microarray and Northern blot analyses<br />

in the transgenic rice plants overexpressing the OsDREB1A<br />

or DREB1C cDNAs and detected overexpression of some<br />

stress-inducible genes. The promoter regions of these genes<br />

contain the DRE sequences. These results indicate that t<strong>here</strong><br />

is a DRE/DREB regulon in the stress-responsible signal transduction<br />

in rice similar to that in Arabidopsis. The DREB/DRE<br />

regulon should be useful for producing transgenic dicots and<br />

Session 3: Opportunities and challenges of transgenic rice 95


A. Genes induced by cold, drought, and high-salinity<br />

stresses and by ABA application:<br />

D. Genes induced by drought and high-salinity stresses and<br />

by ABA application:<br />

G. Genes induced by drought and high-salinity stresses:<br />

H. Genes induced by drought stress and by ABA application:<br />

B. Genes induced by cold, drought, and high-salinity stresses:<br />

I. Genes induced by cold stresses:<br />

C. Genes induced by cold and drought stresses and by ABA<br />

application:<br />

E. Genes induced by cold and drought stresses:<br />

J. Gene expressed constitutively:<br />

F. Gene induced by cold and high-salinity stresses:<br />

Fig. 1. RNA gel-blot analysis of stress-inducible genes. Each lane was loaded with 10 µg of total RNA isolated from 2-wk-old rice seedlings that were exposed to H 2 O, dehydration,<br />

250 mM NaCl, 100 µM ABA, and 4 °C cold treatment for 1, 2, 5, 10, and 24 h. RNA was analyzed by gel-blot hybridization with gene-specific probes of selected stress-inducible<br />

clones by rice cDNA microarray. Stress-inducible clones were classified into various groups on the basis of their expression patterns in RNA gel-blot analysis under each stress<br />

treatment.<br />

96 <strong>Rice</strong> is life: scientific perspectives for the 21st century


monocots with higher tolerance of drought, high salinity, and/<br />

or cold stress.<br />

References<br />

Dubouzet JG, Sakuma Y, Ito Y, Kasuga M, Dubouzet EG, Miura S,<br />

Seki M, Shinozaki K, Yamaguchi-Shinozaki K. 2003.<br />

OsDREB genes in rice, Oryza sativa L., encode transcription<br />

activators that function in drought-, high-salt- and cold-responsive<br />

gene expression. Plant J. 33:751-763.<br />

Kasuga M, Liu Q, Miura S, Yamaguchi-Shinozaki K, Shinozaki K.<br />

1999. Improving plant drought, salt, and freezing tolerance<br />

by gene transfer of a single stress-inducible transcription factor.<br />

Nature Biotechnol. 17:287-291.<br />

Kasuga M, Miura S, Shinozaki K, Yamaguchi-Shinozaki K. 2004. A<br />

combination of the Arabidopsis DREB1A gene and stress-inducible<br />

rd29A promoter improved drought- and low-temperature<br />

stress tolerance in tobacco by gene transfer. Plant Cell<br />

Physiol. 45:346-350.<br />

Liu Q, Kasuga M, Sakuma Y, Abe H, Miura S, Yamaguchi-Shinozaki<br />

K, Shinozaki K. 1998. Two transcription factors, DREB1 and<br />

DREB2, with an EREBP/AP2 DNA binding domain separate<br />

two cellular signal transduction pathways in drought- and lowtemperature-responsive<br />

gene expression, respectively, in<br />

Arabidopsis. Plant Cell 10:1391-1406.<br />

Maruyama K, Sakuma Y, Kasuga M, Ito Y, Seki M, Goda H, Shimada<br />

Y, Yoshida S, Shinozaki K, Yamaguchi-Shinozaki K. 2004.<br />

Identification of cold-inducible downstream genes of the<br />

Arabidopsis DREB/CBF3 transcriptional factor using two<br />

microarray systems. Plant. J 38:982-993.<br />

Rabbani MA, Maruyama K, Abe H, Khan MA, Katsura K, Ito Y,<br />

Yoshiwara K, Seki M, Shinozaki K, Yamaguchi-Shinozaki K.<br />

2003. Monitoring expression profiles of rice (Oryza sativa<br />

L.) genes under cold, drought and high-salinity stresses, and<br />

ABA application using both cDNA microarray and RNA gel<br />

blot analyses. Plant Physiol. 133:1755-1767.<br />

Seki M, Narusaka M, Abe H, Kasuga M, Yamaguchi-Shinozaki K,<br />

Carninci P, Hayashizaki Y, Shinozaki K. 2001. Monitoring<br />

the expression pattern of 1300 Arabidopsis genes under<br />

drought and cold stresses using a full-length cDNA microarray.<br />

Plant Cell 13:61-72.<br />

Shinozaki K, Yamaguchi-Shinozaki K, Seki M. 2003. Regulatory<br />

network of gene expression in the drought and cold stress<br />

responses. Curr. Opin. Plant Biol. 6:410-417.<br />

Yamaguchi-Shinozaki K, Shinozaki K. 1994. A novel cis-acting element<br />

in an Arabidopsis gene is involved in responsiveness<br />

to drought, low-temperature, or high-salt stress. Plant Cell<br />

6:251-264.<br />

Notes<br />

Authors’ addresses: Kazuko Yamaguchi-Shinozaki, Biological Resources<br />

Division, Japan <strong>International</strong> <strong>Research</strong> Center for<br />

Agricultural Sciences (JIRCAS), Tsukuba, Ibaraki; Laboratory<br />

of Plant Molecular Physiology, Graduate School of Agricultural<br />

and Life Sciences, The University of Tokyo, Tokyo,<br />

CREST, JST, Japan; Kazuo Shinozaki, Laboratory of Plant<br />

Molecular Biology, RIKEN Tsukuba <strong>Institute</strong>, Tsukuba,<br />

Ibaraki, CREST, JST, Japan, e-mail:<br />

kazukoys@jircas.affrc.go.jp.<br />

Broad-spectrum disease resistance in transgenic rice<br />

Motoshige Kawata<br />

Environmental stresses exert a critical influence on rice yields<br />

and pathogen attacks are sometimes the most devastating biotic<br />

stress. In a humid temperate climate, fungal rice blast<br />

caused by Magnaporthe grisea is the most serious problem.<br />

Bacterial leaf blight caused by Xanthomonas oryzae is a serious<br />

disease of rice in subtropical and tropical areas. The enhancement<br />

of disease resistance in rice has made a great contribution<br />

toward increasing the productivity of rice and decreasing<br />

the application of pesticides, which can negatively<br />

affect human health and the environment. Genetic engineering<br />

has given us opportunities and challenges for transgenic rice<br />

for improving disease resistance, based on recent advances in<br />

molecular biology. Cloning of several disease-resistance genes<br />

is providing insights into their function and how they protect<br />

plants against pathogen attacks.<br />

Developing domestic gene technologies<br />

Plant gene engineering meant to bring transgenic rice into practical<br />

use must address environmental safety and consumer concerns,<br />

and thus the development of new technologies is impor-<br />

tant. To develop new domestic gene technologies, we hit upon<br />

the idea of incorporating disease-resistance genes from vegetables,<br />

employing a selection technique that uses rice genes,<br />

and keeping the transgenes from functioning in the edible portions<br />

of transgenic rice. Based on this idea, we successfully<br />

developed new transgenic rice strains with multiple disease<br />

resistance by integrating new domestic gene technologies, including<br />

new selection marker genes from rice, defensin genes<br />

from vegetables, which are highly effective in conferring disease<br />

resistance, and new callus-specific and green-tissue-specific<br />

promoters from rice. We confirmed that the transgenes<br />

are specifically expressed in the callus or green tissue, w<strong>here</strong>as<br />

expression is suppressed in rice grains.<br />

Defensin genes<br />

Defensins are antimicrobial proteins found in a wide variety<br />

of organisms and that exhibit powerful antimicrobial activity<br />

against fungi and bacteria. In recent years, progress has been<br />

achieved in analyzing the characteristics of their antimicrobial<br />

activity against plant pathogens. Studies of the general<br />

mechanism on antimicrobial activity have been reported and<br />

Session 3: Opportunities and challenges of transgenic rice 97


ALS Trp Ser<br />

Cells that expressed ALS gene suffer growth inhibition in the<br />

existence of bispyribac sodium (BS)<br />

BS<br />

mutated ALS<br />

(mALS)<br />

Leu<br />

Ile<br />

Cells that expressed mALS gene do not suffer growth<br />

inhibition even in the existence of BS<br />

BS<br />

Fig. 1. Effect of the mutated acetolactate synthase gene (mALS).<br />

the detailed mechanisms of antimicrobial activity on defensin<br />

peptide have been studied (Thevissen et al 2004). Plant<br />

defensins have four disulfide bonds, distinguishing them structurally<br />

from the defensins of insects and mammals, which have<br />

three disulfide bonds (Fant et al 1998).<br />

Mature plant defensin proteins comprise 45 to 54 amino<br />

acid residues, and are small, basic proteins rich in cysteine.<br />

Their expression is observed in Cruciferae plants, as well as<br />

in sorghum, dahlias, and many other plants. Although their<br />

amino acid structures are diverse, cysteine residues are well<br />

preserved, and the alpha helix motif stabilized by cysteine is<br />

common to these defensins. Cruciferae defensin proteins,<br />

which belong to the group exhibiting the strongest antimicrobial<br />

activity, are expressed in places such as seed surfaces.<br />

They exist as gene clusters, and their expression characteristics<br />

and structures differ. One characteristic is that slight amino<br />

acid sequential differences change the strength of antibacterial<br />

activity and effectiveness against pathogens (De Samblanx<br />

et al 1997). Defensin genes exist in commonly consumed<br />

Cruciferae vegetables. They exhibit antibiotic activity against<br />

a wide variety of pathogens such as fungi and bacteria, but<br />

rice plants do not have them. We isolated and determined the<br />

structures of defensin gene clusters from eight kinds of vegetables,<br />

and found that adding defensin proteins suppressed<br />

the growth of rice blast hyphae in vitro (Kawata et al 2004).<br />

New promoters<br />

Developing transgenic plants endowed with practical traits such<br />

as disease resistance requires taking steps so that transgenes<br />

are expressed only in the necessary places, and not in the rice<br />

grains. We isolated the green-leaf-specific promoter, which was<br />

expressed in stems and leaves, and the callus-specific promoter.<br />

These promoters were not expressed in the rice grains, including<br />

the germ. Moreover, we modified the isolated promoters,<br />

such as adding restriction enzyme recognition sites, t<strong>here</strong>by<br />

making it possible to easily construct the vectors used for transformation.<br />

These new technologies make it possible to induce<br />

the functioning of “disease-resistance genes” and “marker genes<br />

that can select transformed cells” at the necessary time for each,<br />

and these techniques suppress the accumulation of transgene<br />

proteins in rice grains.<br />

New selection markers<br />

Acetolactate synthase (ALS) is one of the enzymes that is related<br />

to metabolism, and it is widely found in plants. It is one<br />

of the target enzymes for herbicides. Cells that expressed the<br />

ALS gene suffer growth inhibition in the existence of bispyribac<br />

sodium (BS), but a natural mutation with resistance to this<br />

herbicidal effect has been found among cultured rice plant cells.<br />

An investigation into the reason for this resistance revealed<br />

that inhibition of enzyme activity changed because of the replacement<br />

of amino acid sequences at two locations in the ALS<br />

protein (mALS) (Fig.1). Formerly, the marker genes used in<br />

the development of transgenic plants involved mainly antibiotic<br />

resistance genes obtained from microorganisms or other<br />

organisms. This new selection marker gene (mALS) can be used<br />

in place of antibiotic resistance selection marker genes.<br />

Transgenic rice that integrates domestic gene technologies<br />

Transgenic rice strains developed with multiple disease-resistance<br />

genes are characterized by the integration of original<br />

new technologies, incorporating genes with high disease resistance<br />

from vegetables. In addition to mALS ligated downstream<br />

from the rice callus-specific promoter, and a defensin<br />

gene ligated downstream from the rice green-leaf-specific promoter,<br />

we constructed a binary vector incorporating an expression<br />

cassette consisting of the rice P10 terminator ligated downstream<br />

from each gene (Fig. 2). Transformation was accomplished<br />

by using seeds of rice variety Dontokoi. Estimation of<br />

the rice blast resistance and bacterial leaf blight allowed us to<br />

obtain transgenic plants that had been endowed with resistance<br />

to these pathogens. We confirmed that this resistance is stably<br />

inherited (Kawata et al 2003). This positively confirmed that<br />

the defensin gene makes it possible to develop transgenic rice<br />

strains with high resistance to fungi (the rice blast fungus) and<br />

bacteria (bacterial leaf blight). We also found that the resistance<br />

conferred by this gene is not specific to a particular race<br />

98 <strong>Rice</strong> is life: scientific perspectives for the 21st century


pCsp mALS P10 pLsp Def P10<br />

Fig. 2. Vector construction for the development of transgenic rice by making use of<br />

domestic gene technologies. pCsp = callus-specific promoter from rice, mALS = mutated<br />

acetolactate synthase gene as selection marker, P10 = rice 10K prolamine<br />

terminator, pLsp = green-tissue-specific promoter from rice, Def = defensin gene as<br />

disease-resistance gene.<br />

of rice blast fungus. The transgenic plants did not have any<br />

significant difference with a nontransgenic variety in traits such<br />

as leaf shape or fertility, and we were able to obtain progeny<br />

seeds. We analyzed the expression specificity of the callusspecific<br />

promoter and the green-leaf-specific promoter, and<br />

confirmed that expression was suppressed in the rice grains.<br />

We investigated whether defensin has any significant homology<br />

between known allergens and toxic proteins. With reference<br />

to the Report of a Joint FAO/WHO Expert Consultation<br />

(2001), homology was assessed as significant when either or<br />

both of the following were true: (1) overall homology is 35%<br />

or more and (2) eight or more neighboring amino acid sequences<br />

match. We confirmed that defensin peptides have no<br />

significant amino acid sequence homology either with known<br />

allergen proteins or with toxic proteins.<br />

Creating new demand<br />

T<strong>here</strong> is potential consumer demand for natural antimicrobial<br />

agents that offer eco-friendliness and excellent safety (Zasloff<br />

2002). By focusing on the defensins, which exhibit broad antimicrobial<br />

activity, as new natural antimicrobial agents, we<br />

expect that new antimicrobial agents will be developed, leading<br />

to the creation of new demand among consumers. It has<br />

been shown that animal and insect defensins inhibit the growth<br />

of human disease-related bacteria (Saido-Sakanaka et al 1999).<br />

This indicates the possibility that these defensins can be used<br />

for the prevention and treatment of human diseases and food<br />

poisoning. Analytical research on plant defensins has also<br />

broadened in scope from only targeting plant pathogens, and<br />

t<strong>here</strong> are hopes for the elucidation of pharmacological characteristics<br />

through antimicrobial activity spectrum analyses of<br />

diverse pathogenic organisms.<br />

References<br />

De Samblanx GW, Goderis IJ, Thevissen K, Raemaekers R, Fant F,<br />

Borremans F, Acland DP, Osborn RW, Patel S, Broekaert WF.<br />

1997. Mutational analysis of a plant defensin from radish<br />

(Raphanus sativus L.) reveals two adjacent sites important<br />

for antifungal activity. J. Biol. Chem. 272(2):1171-1179.<br />

Fant F, Vranken W, Broekaert W, Borremans F. 1998. Determination<br />

of the three dimensional solution structure of Raphanus sativus<br />

antifungal protein 1 by 1H NMR. J. Mol. Biol. 279:257-270.<br />

Kawata M, Nakajima T, Yamamoto T, Mori K, Oikawa T, Fukumoto<br />

F, Kuroda S. 2003. Genetic engineering for disease resistance<br />

in rice (Oryza sativa L.) using antimicrobial peptides. JARQ<br />

37(2):71-76.<br />

Kawata M, Nakajima T, Mori K, Oikawa T, Kuroda S. 2004. Genetic<br />

engineering for blast disease resistance in rice, using a<br />

plant defensin gene from Brassica species. Proceedings of<br />

the 3rd IRBC Congress. (In press.)<br />

Saido-Sakanaka H, Ishibashi J, Sagisaka A, Momotani E, Yamakawa<br />

M. 1999. Synthesis and characterization of bactericidal<br />

oligopeptides designed on the basis of an insect anti-bacterial<br />

peptide. Biochem. J. 338:29-33.<br />

Thevissen K, Warnecke DC, Francois IE, Leipelt M, Heinz E, Ott C,<br />

Zahringer U, Thomma BP, Ferket KK, Cammue BP. 2004.<br />

Defensins from insects and plants interact with fungal<br />

glucosylceramides. J. Biol. Chem. 279(6):3900-3905.<br />

Zasloff M. 2002. Antimicrobial peptides of multicellular organisms.<br />

Nature 415:389-395.<br />

Notes<br />

Author’s address: Hokuriku Department of <strong>Rice</strong> <strong>Research</strong>, National<br />

Agriculture <strong>Research</strong> Center, Inada, Joetsu, Niigata 943-0193,<br />

Japan, and Graduate School of Natural Science and Technology,<br />

Niigata University, Ikarashi, Niigata 950-2181, Japan.<br />

Golden <strong>Rice</strong> and improvement of human nutrition<br />

Swapan Datta, Vilas Parkhi, Mayank Rai, Jing Tan, Niranjan Baisakh, Lina Torrizo, Editha Abrigo, Norman Oliva,<br />

Md. Alamgir Hossain, Russel Julian, Anindya Bandyopadhyay, and Karabi Datta<br />

Deficiencies of vitamin A, iron, and zinc are widespread in<br />

Asia and in developing countries, w<strong>here</strong> the main diet is plantbased<br />

and the staple food is rice. <strong>Rice</strong> provides 40–70% of the<br />

total calories consumed in developing Asian countries. In<br />

Southeast Asia, an estimated 250,000 people go blind each<br />

year because of vitamin-A deficiency (VAD). Diet is the only<br />

source of vitamin A in mammals since they cannot manufacture<br />

it on their own. Most of the dietary vitamin A is of plantfood<br />

origin in the form of provitamin A that is converted to<br />

vitamin A in the body (Sivakumar 1998). So far, none of the<br />

Session 3: Opportunities and challenges of transgenic rice 99


screened exotic rice germplasm has shown the presence of β-<br />

carotene in polished seeds. Nevertheless, t<strong>here</strong> is tremendous<br />

potential for using the genetic variability of carotenoid levels<br />

in unpolished rice germplasm (Tan et al 2004).<br />

More than half of all women and children in South and<br />

Southeast Asian countries are anemic. Anemia limits growth<br />

and cognitive development in children and increases the incidence<br />

of death among severely anemic women during childbirth.<br />

Biofortified rice with enhanced minerals and provitamin<br />

A could complement existing nutrition interventions and<br />

provide a sustainable and low-cost way of reaching people who<br />

do not have access to the normal food market because of their<br />

poor economic conditions. Food consumption studies suggest<br />

that doubling the iron in rice can increase the iron intake of the<br />

poor by 50%. <strong>Rice</strong> germplasm screening shows that a doubling<br />

of iron and zinc in unmilled rice is feasible (Gregorio et<br />

al 2000).<br />

Materials and methods<br />

Several indica cultivars (IR64, BR29, Mot Bui, NHCD, BR28,<br />

IR68144) were used for transformation in conferring β-carotene<br />

biosynthesis in rice seeds. BR29, IR68144, and IR64 were<br />

used for iron improvement in rice endosperm. Transformation,<br />

regeneration, molecular analysis (PCR, Southern, RT-PCR),<br />

event selection, and biochemical analysis (carotenoid profiling<br />

by HPLC analysis) were conducted as described earlier<br />

(Datta et al 2003, Vasconcelos et al 2003, Tan et al 2004). The<br />

iron content of both polished and brown rice was estimated by<br />

using either atomic absorbance mass spectrometry (AA-MS)<br />

or inductively coupled plasma-optical emission spectrophotometry<br />

(ICP-OES). Transformation (biolistic and<br />

Agrobacterium) protocols were as described before (Datta et<br />

al 2003, Vasconcelos et al 2003). The pGPTV-bar/Fer vector<br />

for iron (Vasconcelos et al 2003) and pBaal3 and pCaCar<br />

(based on mannose selection) were used for β-carotene engineering<br />

in rice seeds (Datta et al 2003; unpublished data).<br />

Lysine improvement is in progress using the dapA gene from<br />

Corynobacterium, introduced in two rice cultivars by biolistic<br />

transformation.<br />

Results and discussion<br />

Iron deficiency is the leading human nutritional disorder in<br />

the world and very limited work has been done to reduce iron<br />

deficiency compared to progress in enhancing vitamin A and<br />

iodine in plant-based diets. Goto et al (1999) reported enhancement<br />

of iron in japonica rice seeds. We showed that the expression<br />

of the soybean ferritin gene, driven by the endospermspecific<br />

glutelin promoter, led to higher iron and zinc levels in<br />

transgenic rice grains. This is the first report showing enhanced<br />

zinc and iron in rice grains after polishing. Brown rice is rarely<br />

consumed and polishing of the rice grain brings about a considerable<br />

loss of micronutrients by removing the outer layers.<br />

Expression of the soybean ferritin gene under the control of<br />

the glutelin promoter in rice has proven to be effective in enhancing<br />

grain nutritional levels, not only in brown grain but<br />

also in polished grain (Vasconcelos et al 2003).<br />

Zinc deficiency has been associated with complications<br />

in pregnancy and delivery, as well as growth retardation, congenital<br />

abnormalities, and retarded neuro-behavioral and immunological<br />

development in the fetus (Vasconcelos et al 2003).<br />

Interestingly, we found that, along with enhanced iron, zinc<br />

levels were likewise increased in our transgenic ferritin rice.<br />

We obtained 27.9 µ g –1 iron and 55.5 µ g –1 zinc in unpolished<br />

transgenic rice seeds. This accounts for a 2–3-fold increase in<br />

iron compared with that of the control. The high levels of concentration<br />

of iron and zinc remained in rice grains after polishing<br />

(12–15 µ g –1 iron in transgenic seed in the T 3 generation<br />

versus 5–7 µ g –1 in control seed). Iron and zinc levels in<br />

rice grain may vary because of soil properties, weather, and<br />

some unknown factors (Gregorio et al 2000).<br />

Vitamin A plays an important role in a wide variety of<br />

physiological functions in human beings. Biosynthesis of carotenoids<br />

in plants takes place within the plastids, chloroplasts<br />

of photosynthetic tissues, and chromoplasts of fruits and flowers.<br />

Chlorophyll, tocopherols, plastoquinone, phylloquinone,<br />

gibberellins, and carotenoids all share a common biosynthetic<br />

precursor, geranylgeranyl/diphosphate (GGPP), which is derived<br />

from a plastidic isoprenoid metabolism. The genes necessary<br />

for the four enzymes (phytoene synthase, phytoene<br />

desaturase, ζ-carotene desaturase, and lycopene cyclase) catalyze<br />

to complete the pathway toward β-carotene (provitamin<br />

A) biosynthesis from GGPP (Misawa et al 1990). Conventional<br />

interventions (distribution, fortification, diet diversification)<br />

have been helpful in defeating VAD but are not effective<br />

enough. Conventional plant breeding to alter, modify, or introduce<br />

this biosynthetic machinery into the target endosperm<br />

tissues in rice has been impossible as of now, as no endospermactive<br />

carotenoid biosynthetic genes have been found thus far<br />

in the available rice gene pool (Tan et al 2004, Fig. 1). Thus,<br />

the transgenic approach offers the most realistic way to improve<br />

rice by incorporating genes coming from sources other<br />

than rice into rice and showing β-carotene expression in rice<br />

seeds (Figs. 1 and 2). Based on the proof of concept of β-<br />

carotene rice in japonica rice published by Ye et al (2000), we<br />

carried out this work in indica rice and several tropical indica<br />

cultivars (BR29, IR64, Mot Bui, NHCD, BR28, IR68144) were<br />

transformed and showed expression of β-carotene genes (Datta<br />

et al 2003, Parkhi et al, unpublished data, Fig. 2).<br />

Agrobacterium-mediated transformation along with the<br />

POSITECH TM (mannose selection) system works well with<br />

several cultivars. Expression of β-carotene varies among cultivars,<br />

as it was found that IR64 did not show much expression<br />

compared with BR29. Introgressed IR64 from original Golden<br />

<strong>Rice</strong> (T309) also showed lower carotenoid levels (Baisakh et<br />

al, unpublished data). Efforts have been made to select a<br />

transgenic event with a simple and low-copy transgene for a<br />

Mendelian 3:1 segregation pattern and eventually to develop<br />

homozygous lines with acceptable agronomic performance.<br />

The bioavailability of micronutrients (iron and zinc) and<br />

β-carotene needs to be studied. Since ferritin is used as a natu-<br />

100 <strong>Rice</strong> is life: scientific perspectives for the 21st century


AU KDML 105<br />

AU<br />

Ase Pindjau<br />

0.040<br />

0.035<br />

0.030<br />

0.025<br />

0.020<br />

0.015<br />

0.010<br />

0.005<br />

0.000<br />

–0.005<br />

–0.010<br />

10 20 30 40 50 60 70<br />

0.040<br />

0.035<br />

0.030<br />

0.025<br />

0.020<br />

0.015<br />

0.010<br />

0.005<br />

0.000<br />

lut<br />

b-crt<br />

5 10 15 20 25 30<br />

AU<br />

0.040<br />

0.035<br />

0.030<br />

0.025<br />

0.020<br />

0.015<br />

0.010<br />

0.005<br />

0.000<br />

IR64 (transgenic)<br />

lut<br />

5 10 15 20 25 30 5 10 15 20 25 30<br />

Minutes<br />

b-crt<br />

Fig. 1. Carotenoid profile for selected rice cultivars under both polished and unpolished conditions.<br />

Curves in red = polished seeds. Curves in blue = unpolished seeds. Curves in green = control seeds.<br />

KDML 105 and Ase Pindjau (from Thailand and Indonesia) are nontransgenic seeds, w<strong>here</strong>as IR64 and<br />

BR29 are genetically engineered Golden indica rice (lut = lutein, β-crt = β-carotene).<br />

AU<br />

0.040<br />

0.035<br />

0.030<br />

0.025<br />

0.020<br />

0.015<br />

0.010<br />

0.005<br />

0.000<br />

BR29 (transgenic)<br />

lut<br />

Minutes<br />

b-crt<br />

Fig. 2. Golden indica BR29 (control at left and transgenic segregating<br />

line at right) showing expression of beta-carotene in<br />

rice seeds after polishing (carotenoid levels ranged from 0.5<br />

to 3.14 µg g –1 . Transformation was carried out with mannose<br />

selection (PMI) and the Agrobacterium system.<br />

ral source of iron in the early development of animals and<br />

plants, ferritin-iron bioavailability should not be a problem. In<br />

fact, iron in transgenic rice with ferritin has already been tested<br />

in iron-deficient rats, and rice diets were as effective as the<br />

FeSO 4 diet in replenishing hematocrit (Murray-Kolb et al<br />

2002). Further studies suggest that a relatively small supplement<br />

of vitamin A or β-carotene can double the absorption of<br />

endogenous nonhaem iron from cereal, resulting in a significant<br />

increase in carotenoid in cereal diets (Graham and Rosser<br />

2000). Thus, β-carotene-enriched rice helps reduce vitamin-A<br />

deficiency and protect against iron-deficiency anemia.<br />

Biofortified rice with enhanced nutrition (β-carotene, iron, zinc,<br />

and lysine) along with other superior agronomic traits and yield<br />

could support the food-health and livelihood of the millions of<br />

people who need them most.<br />

References<br />

Datta K, Baisakh N, Oliva N, Torrizo L, Abrigo E, Tan J, Rai M,<br />

Rehana S, Al-Babili S, Beyer P, Potrykus I, Datta SK. 2003.<br />

Bioengineered ‘golden’ indica rice cultivars with beta-carotene<br />

metabolism in the endosperm with hygromycin and mannose<br />

selection systems. Plant Biotechnol. J. 1:81-90.<br />

Goto F, Yoshihara T, Shigemoto N, Toki S, Takaiwa F. 1999. Iron<br />

fortification of rice seed by the soybean ferritin gene. Nature<br />

Biotechnol. 17:282-286.<br />

Session 3: Opportunities and challenges of transgenic rice 101


Graham RD, Rosser JM. 2000. Carotenoids in staple foods: their<br />

potential to improve human nutrition. Food Nutr. Bull.<br />

21(4):404-409.<br />

Gregorio G, Senadhira D, Htut H, Graham R. 2000. Breeding for<br />

trace mineral density in rice. Food Nutr. Bull. 21(4):382-387.<br />

Misawa N, Nakagawa M, Kobayashi K, Yamano S, Izawa Y,<br />

Nakamura K, Harashima K. 1990. Elucidation of the Erwinia<br />

uredovora carotenoid biosynthetic pathway by functional<br />

analysis of gene products expressed in Escherichia coli. J.<br />

Bacteriol. 172:6704-6712.<br />

Murray-Kolb L, Takaiawa F, Goto F, Yoshihara T, Theil E, Beard J.<br />

2002. Transgenic rice is a source of iron for iron-depleted<br />

rats. J. Nutr. 132(5):957-960.<br />

Sivakumar B. 1998. Current controversies in carotene nutrition. Ind.<br />

J. Med. Res. 108:157-166.<br />

Tan J, Baisakh N, Oliva N, Torrizo L, Abrigo E, Datta K, Datta SK.<br />

2004. HPLC carotenoid profiles of rice germplasm. Int. J. Food<br />

Sci. Technol. (Submitted.)<br />

Vasconcelos M, Datta K, Oliva N, Khalekuzzaman M, Torrizo L,<br />

Krishnan S, Oliveira M, Goto F, Datta SK. 2003. Enhanced<br />

iron and zinc accumulation in transgenic rice with the ferritin<br />

gene. Plant Sci. 64(3):371-378.<br />

Ye X, Al-Babili S, Klöti A, Zhang J, Lucca P, Beyer P, Potrykus I.<br />

2000. Engineering the provitamin A (β-carotene) biosynthetic<br />

pathway into (carotenoid-free) rice endosperm. Science<br />

287:303-305.<br />

Notes<br />

Authors’ address: Plant Breeding, Genetics, and Biochemistry Division,<br />

<strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>, DAPO Box 7777,<br />

Metro Manila, Philippines.<br />

Acknowledgments: We thank the USAID and HarvestPlus Challenge<br />

Program (“Breeding Crops for Better Nutrition”) for financial<br />

and research support and Dr. Peter Beyer for providing<br />

us with the pCaCar and pBaal3, Dr. S.C. Falco (DuPont) for<br />

dapA, Syngenta for pmi, and Dr. F. Goto for the ferritin gene.<br />

Health-promoting transgenic rice suppressing<br />

life-related disease and type-I allergy<br />

Fumio Takaiwa<br />

Higher plants are an attractive host for the production of recombinant<br />

proteins for pharmaceutical and nutraceutical applications.<br />

Plant production offers many advantages, the most<br />

prominent of which are cost savings relative to animal<br />

transgenic systems, easy control of the production scale, and<br />

freedom from animal-derived pathogens. When recombinant<br />

proteins are expressed in seed under the control of a seedspecific<br />

promoter, they are highly and stably accumulated in a<br />

specific organelle designated as a protein body. Taking advantage<br />

of these properties, the seed has been used as an ideal<br />

bio-reactor for the production of recombinant proteins.<br />

<strong>Rice</strong> is one of the most important crops and food resources<br />

in the world. <strong>Rice</strong> seed has several advantages over<br />

the other cereal crops, such as easier storage and processing,<br />

greater biomass, and lower production costs. In addition, a<br />

transformation system of rice has been established and the<br />

whole genome sequence, including mitochondria and chloroplasts,<br />

is now available. T<strong>here</strong>fore, rice seed can be used as a<br />

good platform for producing recombinant proteins.<br />

The rice seed production system<br />

For use as a bio-reactor for the production of recombinant proteins<br />

or a direct delivery system of bioactive peptides or vaccines,<br />

establishment of a high expression system is required.<br />

Final accumulation levels are regulated at several steps of tran-<br />

scription and posttranscription, including translation, mRNA<br />

stability, transport, protein stability, and folding, among others.<br />

It has been found that the transcription level primarily<br />

determines the expression level. T<strong>here</strong>fore, screening for strong<br />

promoters from genes expressed in maturing seed has been<br />

carried out first. Promoter activities of more than 20 genes<br />

were assayed in stable transgenic rice seed by fusing their promoters<br />

to the GUS reporter gene, and then introducing their<br />

chimeric genes into the rice genome by Agrobacterium-mediated<br />

transformation. From the results of this promoter analysis,<br />

rice seed promoters are classified into several types based<br />

on their expression patterns in seed. It was shown that glutelin,<br />

26-kDa globulin, and 10-kDa prolamin promoters exhibited<br />

strong promoter activities in this order and different expression<br />

patterns in the endosperm (Qu and Takaiwa 2004).<br />

Prolamin, glutelin, and globulin promoters directed expression<br />

in the outer layer, subaleurone layer, and inner starchy<br />

endosperm, respectively. T<strong>here</strong>fore, we have selected and used<br />

the glutelin, 26-kDa globulin, and 10-kDa prolamin promoters<br />

for the expression of foreign proteins in transgenic rice<br />

seed dependent upon that purpose.<br />

Irrespective of high transcripts, it has been occasionally<br />

observed that final products were at a very low level. In this<br />

case, the space for accumulation of recombinant proteins or<br />

subcellular localization as well as codon usage or mRNA stability<br />

is critical. Low-storage-protein mutants such as LGC-1<br />

102 <strong>Rice</strong> is life: scientific perspectives for the 21st century


pmol (4 MU min –1 mg –1 protein)<br />

60<br />

50<br />

40<br />

30<br />

20<br />

10<br />

1.3 kB GluB-1<br />

2.3 kB GluB-1<br />

GluB-2<br />

GluB-4<br />

10 kDa Pro<br />

13 kDa Pro<br />

16 kDa Pro<br />

Glb-1<br />

REG-2<br />

Ole18<br />

b-conglycinin<br />

AlaAT<br />

GOGAT<br />

AGPase<br />

PPDK<br />

SBE1<br />

Ubiquitin<br />

Fig. 1. GUS activities expressed by various promoters in maturing seeds at 17 days after flowering.<br />

GUS activity is expressed as pmol (4 MU min –1 µg –1 protein).<br />

will become good hosts, giving rise to a high accumulation of<br />

foreign proteins, because they can provide ample space for<br />

accumulation. It has been confirmed by crossing between<br />

transgenic rice and a mutant that the transgene product was<br />

enhanced more than twofold in a low storage background (Tada<br />

et al 2003).<br />

Transgenic rice accumulating soybean glycinin<br />

Soybean protein has a function to lower the cholesterol level<br />

in human serum and is one of the best plant food proteins in<br />

terms of nutritional quality. The major storage proteins of soybean<br />

are glycinin and β-conglycinin. Glycinin is superior to<br />

β-conglycinin in nutritional value as well as in functional properties.<br />

Soybean proteins are deficient in sulfur-containing amino<br />

acids and rich in lysine, and rice proteins are the opposite.<br />

T<strong>here</strong>fore, if soybean glycinin were highly accumulated in rice<br />

seeds, an improvement of nutritional value and endowment of<br />

functional properties such as gel-formation and emulsifying<br />

abilities would be expected. We previously generated<br />

transgenic rice accumulating soybean glycinin A1aB1b<br />

(Katsube et al 1999). In this study, two representative types of<br />

glycinin (A1aB1b and A3B4) belonging to different subclasses<br />

were expressed in the endosperm tissue under the control of<br />

glutelin GluB-1 and 26-kDa globulin promoters, respectively.<br />

Furthermore, to enhance their accumulation levels, they were<br />

transferred into the low-storage-protein background of LGC-<br />

1 by crossing. It was shown that A1aB1b was much more highly<br />

accumulated than A3B4 in transgenic rice. When both glycinins<br />

were expressed together, the A3B4 level increased about threefold<br />

more than the level obtained by the expression of A3B4<br />

alone, thus indicating a requirement of assembly between different<br />

subunits for the stable accumulation of A3B4. In the<br />

LGC background, soybean glycinin was accumulated as a major<br />

storage protein, accounting for 30% to 40% of total rice seed<br />

protein. The glycinin level also increased more than twice compared<br />

with that of the normal background. Glycinin was extracted<br />

as salt-soluble globulin and acid-soluble glutelin fractions,<br />

thus suggesting that hybrid glycinin-glutelin oligomers<br />

were also formed in transgenic rice seed. When the lysine and<br />

protein levels in the seed were examined and compared between<br />

a transgenic line expressing both glycinins and the lowglutelin<br />

mutant background line, they were remarkably enhanced<br />

from 0.23 to 0.41 g per 100 g of seed and from 6.9 to<br />

10.9 g per 100 g of seed, respectively.<br />

Transgenic rice accumulating bioactive peptides<br />

It has been observed that some bioactive peptides derived from<br />

digests of food proteins are active after oral administration<br />

even though specific activities are not high compared with the<br />

endogenous bioactive peptides. Such peptides are expected to<br />

be effective in preventing lifestyle-related diseases such as<br />

hypertension, high cholesterol, and diabetes, among others.<br />

Biological activities of peptides could be strengthened by replacement<br />

of amino acid residues. Taking advantage of these<br />

Session 3: Opportunities and challenges of transgenic rice 103


modified peptides with high specific activity, transgenic crops<br />

to prevent lifestyle-related diseases can be generated.<br />

An antihypertensive peptide ovokinin-like sequence derived<br />

from egg white alubumin (Matoba et al 2001) was inserted<br />

into highly variable regions of seed storage proteins to<br />

confer upon them a potent anti-hypertensive function. Bioactive<br />

peptides were usually introduced into hypervariable regions<br />

of rice’s major storage protein glutelins, which are located in<br />

the C terminal regions of acidic and basic subunits. In this<br />

study, tandem modified ovokinin was inserted into at least two<br />

sites of the C terminal region of the acidic subunit of glutelin.<br />

To release bioactive peptide from the seed storage protein, the<br />

bioactive peptide was flanked by Asn or Lyn amino acids, the<br />

target site of the typsin small-intestine digestive enzyme. It is<br />

anticipated that bioactive peptide could be released from storage<br />

protein in the small intestine after digestion with digestive<br />

enzymes after oral feeding. This functional glutelin gene containing<br />

antihypertensive peptides was transcriptionally fused<br />

to the rice glutelin promoter and then introduced into the rice<br />

genome. The modified glutelin was highly accumulated in rice<br />

seed. On the other hand, when a small size of bioactive peptide<br />

of less than 30 amino acids was directly synthesized in<br />

transgenic plants, transgenic plants accumulating it have not<br />

yet been obtained. This is due to rapid clearance in the plant<br />

cell after synthesis. T<strong>here</strong>fore, it has been demonstrated that<br />

the best way for production in transgenic plants is for bioactive<br />

peptide to be synthesized as a part of the seed storage protein.<br />

Transgenic rice alleviating Japanese cedar pollinosis<br />

Peptide immunotherapy using dominant T-cell epitopes is safer<br />

and more effective than the conventional treatment of type-I<br />

allergic diseases due to no binding to the specific IgE antibody<br />

and high dose administration. It is possible to use rice<br />

seed as a direct delivery system for peptide vaccine. Japanese<br />

cedar pollinosis is an important allergic rhinoconjunctivitis in<br />

Japan in spring. We have generated transgenic rice accumulating<br />

epitope peptide of Japanese cedar pollen allergens (Cryj1<br />

and Cryj2) in the endosperm. The codon-optimized gene coding<br />

for hybrid epitope peptide consisting of seven major human<br />

T-cell epitopes (96 amino acids) derived from the cedar<br />

pollen allergens was synthesized (Hirahara et al 2001). To enhance<br />

the accumulation level of the 7 crp peptide, glutelin<br />

GluB-1 signal peptide and the KDEL ER retention signal were<br />

attached to the N and C termini of the 7 crp peptide, respectively.<br />

When this gene was introduced and expressed in the<br />

endosperm tissue of rice under the control of the glutelin GluB-<br />

1 promoter, the 7 crp peptide was detected as a visible band in<br />

CBB-stained gel. About 60 µg of 7 crp peptide was accumulated<br />

in one grain of the highest accumulating line, accounting<br />

for about 3% to 4% of the total seed protein (Fig. 2). The 7 crp<br />

peptide in seed was not glycosylated and was resistant to boiling<br />

for 20 min. Oral administration of these transgenic rice<br />

seeds to specific mice before priming with pollen proteins suppressed<br />

the IgE level to about one-third of that obtained by<br />

feeding nontrasgenic rice seeds, thus indicating that immunological<br />

tolerance was induced by this transgenic rice. Taken<br />

together, these results provide insight into the efficacy of using<br />

transgenic rice for oral immunotherapy against Japanese<br />

cedar pollinosis.<br />

References<br />

Hirahara K, Tatsuta T, Takatori T, et al. 2001. Preclinical evaluation<br />

of an immunotherapeutic peptide comprising 7 T-cell determinants<br />

of Cry j1 and Cry j2 , the major Japanese cedar pollen<br />

allergens. J. Allergy Clin. Immunol. 108:94-100.<br />

Katsube T, Kurisaka N, Ogawa M, Maruyama M, Ohtsuka R, Utsumi<br />

S, Takaiwa F. 1999. Accumulation of soybean glycinin and its<br />

assembly with the glutelins in rice. Plant Physiol. 120:1063-<br />

1073.<br />

Matoba N, Doyama N, Yamada Y, Maruyama N, Utsumi S, Yoshikawa<br />

M. 2001. Design and production of genetically modified soybean<br />

protein with anti-hypertensive activity by incorporating<br />

potent analogue of ovokinin(2-7). FEBS Lett. 497:50-54.<br />

Qu LQ, Takaiwa F. 2004. Evaluation of tissue specificity and expression<br />

strength of rice seed component gene promoters in<br />

transgenic rice. Plant Biotechnol. J. 2:113-125.<br />

Tada Y, Utsumi S, Takaiwa F. 2003. Foreign gene products can be<br />

enhanced by introduction into low storage protein mutants.<br />

Plant Biotechnol. J. 1:411-422.<br />

Notes<br />

Author’s address: Laboratory of Gene Engineering, Department of<br />

Plant Biotechnology, National <strong>Institute</strong> of Agrobiological<br />

Sciences, Kannondai 2-1-2, Tsukuba, Ibaraki 305-8602, Japan.<br />

104 <strong>Rice</strong> is life: scientific perspectives for the 21st century


A<br />

2.3 k GluB-1 pro GluB-1 sig 7 crp KDEL 0.6 k GluB-1 3′<br />

B<br />

Western<br />

analysis<br />

CBB staining<br />

NT TF<br />

NT<br />

TF<br />

kDa<br />

kDa<br />

75<br />

75<br />

50<br />

50<br />

37<br />

Glutelin<br />

(acidic)<br />

37<br />

25<br />

Glutelin<br />

(basic)<br />

25<br />

15<br />

Prolamin<br />

7 crp<br />

15<br />

10<br />

10<br />

7 Crp<br />

Fig. 2. (A) Vector construct used to generate transgenic rice expressing the 7 crp gene in<br />

endosperm tissue. (B) Accumulation of the 7 Crp peptide in seeds of transgenic rice plants.<br />

Total protein was extracted from a seed of nontransformant (NT) or transgenic rice (TF:<br />

pGPTV-HPT-GluB-1pro sig/7Crp+KDEL #10), separated by 15% SDS-PAGE, and then stained<br />

with CBB or immunoblotted with anti-7 Crp antibody.<br />

Producing rice plants with a site-specific base change<br />

in the acetolactate synthase gene by chimeraplast-directed<br />

gene targeting<br />

A. Okuzaki and K. Toriyama<br />

Chimeraplasts, which are also called chimeric RNA/DNA oligonucleotides,<br />

have been reported to cause site-specific base<br />

changes in chromosomal targets in mammalian cells (see Hohn<br />

and Puchta 1999, Oh and May 2001, Graham and Dickson<br />

2002 for reviews). Chimeraplasts consist of 68 synthesized<br />

oligonucleotides that have a DNA “mutator” region of five<br />

nucleotides complementary to the target site flanked by 2′-Omethyl<br />

RNA bridges of 8–12 nucleotides each. This DNA mutator<br />

region can cause a site-specific base change in the endogenous<br />

gene. The first uses of chimeraplasts causing sitespecific<br />

base changes in plant cells were reported in maize<br />

(Zhu et al 1999) and tobacco (Beetham et al 1999). In both<br />

cases, gene targeting has been directed toward generating base<br />

changes that result in a chemically selectable phenotype. The<br />

targeted gene has been an acetohydroxyacid synthase (AHAS)<br />

gene in maize (Zhu et al 1999, 2000) and an acetolactate synthase<br />

(ALS) gene in tobacco (Beetham et al 1999). Both ALS<br />

and AHAS are the first common enzymes in the biosynthetic<br />

pathway of the branched-chain amino acids leucine, isoleusine,<br />

and valine. Mutations of certain amino acids in these proteins<br />

have been known to confer resistance to ALS-inhibiting herbicides<br />

(Shimizu et al 2002). The efficiency of gene conversion<br />

mediated by chimeraplasts in maize was estimated to be 10 –4 .<br />

In the same manner, we demonstrated that chimeraplastdirected<br />

gene targeting is feasible in rice (Okuzaki and<br />

Toriyama 2004). In our current study, we further confirmed<br />

the feasibility in rice using anther culture–derived haploid cells<br />

as well as scutellum-derived diploid cells. We also investigated<br />

whether the haploid state promoted the efficiency of<br />

chimeraplast-directed gene targeting.<br />

Session 3: Opportunities and challenges of transgenic rice 105


′ ′<br />

Fig. 1. Chimeraplast Ch-W548L, which is designed to substitute TTG (a leucine codon) at codon 548 for<br />

TGG (a tryptophan codon). Uppercase letters, DNA residues; lowercase letters, 2′-0-methyl-RNA residues;<br />

bold letters, target codon.<br />

Materials and methods<br />

A japonica rice variety, Taichung 65 (Oryza sativa L.), was<br />

used in our study. A 6–8-day-old callus derived from scutellum<br />

of mature seeds and a 5-week-old callus derived from<br />

anther culture were used as target cells. The calli were placed<br />

on a plate in a circle 2.5 cm in diameter for delivery of<br />

chimeraplasts.<br />

Chimeraplast design and delivery<br />

Three chimeraplasts were designed based on the sequence of<br />

the rice ALS gene (accession numbers AB049822 and<br />

AB049823 in the DDBJ databases). A Ch-W548L (Fig. 1) was<br />

designed to substitute TTG (a leucine codon) at codon 548 for<br />

TGG (a tryptophan codon). In chimeraplast S627I, AGT for<br />

serine was replaced by ATT for isoleucine. Ch-P171A was<br />

designed with the Pro-171 codon CCC altered to contain a<br />

mismatch codon, GCC, which encodes alanine. Chimeraplasts<br />

were delivered to callus cells by particle bombardment<br />

(Okuzaki and Toriyama 2004). Calli were selected on N6 medium<br />

supplemented with 0.25–0.5 µM Bispyribac-sodium (BS,<br />

Kumiai Chemical Industry Co., Ltd., Shizuoka, Japan). A plasmid<br />

containing cauliflower mosaic virus 35S promoter and<br />

green fluorescent protein (35S-GFP) was also delivered for<br />

the estimation of the number of cells receiving gold particles.<br />

Molecular characterization of herbicide-resistant<br />

plants<br />

Genomic DNA was extracted from the leaves of regenerated<br />

plants. Target sequences were amplified from the DNA using<br />

Ex Taq polymerase and the ALS primers (Okuzaki and<br />

Toriyama 2004). Amplified fragments were gel-purified and<br />

were either directly sequenced or sequenced after cloning into<br />

a pCR 2.1 TOPO vector.<br />

Results and discussion<br />

Feasibility of chimeraplast-directed gene targeting<br />

At first, we delivered a mixture of Ch-W548L and Ch-S627I<br />

to scutellum-derived calli by particle bombardment. Three independent<br />

calli resistant to BS were obtained out of 20 plates<br />

of calli (Table 1). Direct sequencing of the PCR products of<br />

the regenerated plants showed two overlapping peaks of T and<br />

G, and consequently the N nucleotide designation in the chromatograms<br />

at the target nucleotide in codon 548, in the same<br />

manner as we reported previously (Okuzaki and Toriyama<br />

2004). However, no base changes were observed in the whole<br />

coding region of the ALS gene, including another target codon,<br />

627. Sequencing of the cloned PCR products demonstrated<br />

that both unconverted wild-type (TGG) and converted mutant<br />

alleles (TTG) were present in codon 548 in all three plants.<br />

The base change in ALS was transmitted to T 1 seedlings. The<br />

frequency of calli having predicted conversion at the target<br />

site of W548L after delivery of Ch-W548L was 0.12 per plate.<br />

Out of 44 control plates, which included the delivery of Ch-<br />

S627I, delivery of gold particles only, and no bombardment<br />

treatment, 4 plants showed resistance to BS (Table 1). These<br />

plants also contained the same base change in codon 548, which<br />

seemed to be caused by spontaneous mutation. The frequency<br />

of spontaneous mutation of W548L was calculated to be 0.09<br />

per plate.<br />

Next, we delivered chimeraplasts to anther culture–derived<br />

calli. Bombardment of a mixture of three chimeraplasts<br />

(Ch-W548L + Ch-S627I + Ch-P171A) and a mixture of two,<br />

including Ch-W548L, yielded 22 BS-resistant calli, all of which<br />

contained the predicted conversion sequence, TTG, at Trp-548<br />

codon (Table 1). Out of 23 control plates, in which Ch-W548L<br />

was not delivered, 11 calli showed resistance to BS, having<br />

the same base change, TTG, in codon 548, which was likely<br />

caused by spontaneous mutation. The frequency of calli having<br />

a predicted conversion at the target site of Ch-W548L after<br />

delivery of Ch-W548L was 0.96 per plate, and was twice<br />

as high as the frequency of spontaneous mutation, which was<br />

0.47 per plate. These results confirmed that the chimeraplastdirected<br />

gene targeting was feasible in rice.<br />

Estimation of gene conversion frequency per cell<br />

We estimated gene conversion efficiency using the following<br />

calculation: Gene conversion frequency = (Number of calli<br />

having predicted gene conversion per plate – Number of calli<br />

having spontaneous mutation per plate) / Total cells receiving<br />

chimeraplasts per plate. The total cells receiving chimeraplasts<br />

were estimated by transient expression of 35S-GFP. Gene conversion<br />

frequency mediated by chimeraplasts was estimated<br />

to be 3.3 × 10 –5 and 3.2 × 10 –4 for scutellum-derived calli and<br />

anther culture–derived calli, respectively. The frequency of<br />

chimeraplast-directed ALS W548L change in anther-culture<br />

calli was ten times higher than that of scutellum calli.<br />

106 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. Number of calli having the predicted base change when chimeraplast was<br />

delivered to scutellum calli or anther-culture calli. In parentheses is the frequency of<br />

gene conversion (TTG) at codon 548 per plate.<br />

Number of Number of calli having predicted<br />

Delivered chimeraplast plates bombarded base change<br />

W548L S627I P171A<br />

Scutellum calli<br />

Ch-W548L + Ch-S627I 20 3 0 0<br />

Ch-W548L 5 0 0 0<br />

Total with Ch-W548L 25 3 (0.12)<br />

Ch-S627I 6 2 0 0<br />

Gold particles only 13 1 0 0<br />

No bombardment 25 1 0 0<br />

Total without Ch-W548L 44 4 (0.09)<br />

Anther-culture calli<br />

Ch-W548L + Ch-S627I + ChP171A 8 13 2 0<br />

Ch-W548L + Ch-S627I 7 5 0 0<br />

Ch-W548L + Ch-P171A 8 4 1 0<br />

Total with Ch-W548L 23 22 (0.96)<br />

Ch-S627I + Ch-P171A 8 5 0 0<br />

Gold particles only 7 1 0 0<br />

No bombardment 8 5 0 0<br />

Total without Ch-W548L 23 11 (0.48)<br />

Does the haploid state promote targeting efficiency<br />

In this study, we used anther culture–derived calli to investigate<br />

whether the haploid state promotes the efficiency of<br />

chimeraplast-directed gene targeting. Ploidy analysis of anther-derived<br />

calli after 5 wk of culture, which was carried out<br />

using flow cytometry after staining nuclei with DAPI, showed<br />

that these calli contained 60% haploid-state cells. The ploidy<br />

of calli having a predicted gene conversion was estimated from<br />

the sequence pattern of direct sequencing analysis. If t<strong>here</strong> is a<br />

single peak of the converted nucleotide at a target site, gene<br />

conversion is considered to occur in a haploid-state cell. In<br />

contrast, double peaks of the converted and unconverted nucleotide<br />

indicate that gene conversion occurred in a doubled-haploid<br />

cell. Direct sequencing at codon 548 in 22 calli having<br />

W548L change after delivery of Ch-W548L demonstrated that<br />

8 calli had a single peak of T, w<strong>here</strong>as 13 calli had double<br />

peaks of G and T. For calli obtained by spontaneous mutation,<br />

six calli had a single peak of T and five had double peaks of T<br />

and G. T<strong>here</strong> was no significant difference in the gene conversion<br />

frequency between haploid cells and doubled-haploid<br />

cells. This result indicated that the haploid state did not promote<br />

targeting efficiency in rice. A similar result has also been<br />

reported in tobacco (Kochevenko and Willmitzer 2003).<br />

Co-conversion at separate sites is the next subject<br />

In our study, calli containing co-conversion at two sites were<br />

not obtained in the co-delivery of two or three distinct<br />

chimeraplasts. Co-conversions at separate sites is the next subject<br />

to be examined in order to direct base changes for<br />

nonselectable genes.<br />

References<br />

Beetham PR, Kipp PB, Sawycky XL, Arntzen CJ, May GD. 1999. A<br />

tool for functional plant genomics: chimeric RNA/DNA oligonucleotides<br />

cause in vivo gene-specific mutations. Proc.<br />

Natl. Acad. Sci. USA 96:8774-8778.<br />

Graham IR, Dickson G. 2002. Gene repair and mutagenesis mediated<br />

by chimeric RNA-DNA oligonucleotides: chimeraplasty<br />

for gene therapy and conversion of single nucleotide polymorphisms<br />

(SNPs). Biochim. Biophys. Acta 1587:1-6.<br />

Hohn B, Puchta H. 1999. Gene therapy in plants. Proc. Natl. Acad.<br />

Sci. USA 96:8321-8323.<br />

Kochevenko A, Willmitzer L. 2003. Chimera RNA/DNA oligonucleotide-based<br />

site-specific modification of the tobacco<br />

acetolactate synthase gene. Plant Physiol. 132:174-184.<br />

Oh TJ, May GD. 2001. Oligonucleotide-directed plant gene targeting.<br />

Curr. Opin. Biotech. 12:169-172.<br />

Okuzaki A, Toriyama K. 2004. Chimeric RNA/DNA oligonucleotidedirected<br />

gene targeting in rice. Plant Cell Rep. 22:509-513.<br />

Shimizu T, Nakayama I, Nagayama K, Miyazawa T, Nezu Y. 2002.<br />

Acetolactate synthase inhibitors. In: Boger P, Wakabayashi<br />

K, Hirai K, editors. Herbicide classes in development. Berlin:<br />

Springer-Verlag. p 1-41.<br />

Zhu T, Peterson DJ, Tagliani L, St. Clair G, Baszczynski C, Bowen<br />

B. 1999. Targeted manipulation of maize genes in vivo using<br />

chimeric RNA/DNA oligonucleotides. Proc. Natl. Acad. Sci.<br />

USA 96:8768-8773.<br />

Zhu T, Mettenburg K, Peterson DJ, Tagliani L, Baszczynski CL.<br />

2000. Engineering herbicide-resistant maize using chimeric<br />

RNA/DNA oligonucleotides. Nat. Biotechnol. 18:555-558.<br />

Session 3: Opportunities and challenges of transgenic rice 107


Notes<br />

Authors’ address: Laboratory of Plant Breeding and Genetics, Graduate<br />

School of Agricultural Science, Tohoku University, Aobaku,<br />

Sendai 981-8555, Japan, e-mail:<br />

torikin@bios.tohoku.ac.jp, okku@bios.tohoku.ac.jp.<br />

Transgenic rice plants expressing wheat catalase<br />

show improved tolerance for chilling-induced damage<br />

in membranes<br />

Haruo Saruyama, Hidenori Onodera, and Matsuo Uemura<br />

Active oxygen species (AOS) such as superoxide radical<br />

(O 2 – ), hydrogen peroxide (H 2 O 2 ), and hydroxyl radical (OH • )<br />

are generally produced during the biological process. The mitochondrial<br />

respiratory chain and the photosynthetic process<br />

are the major sites w<strong>here</strong> AOS are produced. Indeed, approximately<br />

2–3% of the oxygen used by the mitochondria can be<br />

converted into superoxide and H 2 O 2 (Puntarulo et al 1988).<br />

Since plant growth depends on the balance between the production<br />

and detoxification of AOS, functional stability of AOSscavenging<br />

enzymes, such as superoxide dismutase, catalase,<br />

and ascorbate peroxidase, is critical for plant survival under<br />

stress environments. In fact, many transgenic plants expressing<br />

such antioxidant enzymes were reported. We previously<br />

confirmed that the expression of wheat catalase in transgenic<br />

rice plants shows tolerance for chilling injury (Matsumura et<br />

al 2002). Although improved tolerance for stress circumstances<br />

was reported, the functional mechanism of the tolerance has<br />

not been revealed. To make clear the reasons for improved<br />

tolerance in transgenic rice plants for low-temperature injury,<br />

we examined the effect of chilling (5 o C up to 8 days) on electrolyte<br />

leakage, mitochondrial membrane integrity, fatty acid<br />

peroxidation, and photosynthetic and respiratory activities.<br />

Materials and methods<br />

Transgenic rice plants (CT 2-6-4) in which wheat catalase<br />

cDNA was expressed and nontransgenic control rice plants<br />

(cultivar Yuukara) (Matsumura et al 2002) were used in this<br />

study. All plants were grown in a growth chamber for 20 days<br />

under conditions of 12 h light (262 µmol m –2 s –1 ) at 25 o C and<br />

12 h dark at 20 o C.<br />

The effects of chilling (12 h light, 60 µmol m –2 s –1 at 5<br />

o C and 12 h dark at 5 o C) on these plants were examined with<br />

the method previously reported (Matsumura et al 2002).<br />

Catalase (CAT; EC 1.11.1.6) activity in leaves was measured<br />

according to Matsumura et al (2002). H 2 O 2 concentration<br />

in leaves was measured according to Patterson et al (1984).<br />

Electrolyte leakage was measured as follows. Leaf cuttings<br />

(3 cm) from plants after various treatments were added<br />

to 3.0 mL of water in a test tube and shaken for 2.5 h. The<br />

conductivity of the solution (value 1) was measured with a<br />

conductivity meter (Twin Cond B-173, Horiba, Japan). Next,<br />

the samples were boiled for 30 min and shaken again for 2.5 h,<br />

and the conductivity (value 2) was measured. The electrolyte<br />

leakage value (%) was expressed as (value 1)/(value 2) times<br />

100.<br />

Mitochondrial activity was measured by TTC reduction<br />

according to Steponkus and Lanphear (1967). Fatty acid<br />

peroxidation was measured by the TBA reaction according to<br />

Heath and Packer (1968). Photosynthetic activity was examined<br />

by measuring the value of Fv/Fm using a Plant Efficiency<br />

Analyzer (Hansatech) according to Clarke and Campbell<br />

(1996). Respiratory activity was analyzed by measuring the<br />

decrease in oxygen using Oxytherm (Hansatech).<br />

Results and discussion<br />

Visible damage by chilling<br />

After plants were exposed at 5 o C for 8 d, visible damage by<br />

chilling was compared. As Figure 1 shows, leaves of<br />

nontransgenic rice after 8 d of chilling were as severely damaged<br />

as wit<strong>here</strong>d. However, such severe damage did not occur<br />

to the leaves of transgenic rice. These data clearly demonstrate<br />

that transgenic rice plants are more cold-tolerant than<br />

nontransgenic rice.<br />

Chilling effect on catalase activity and H 2<br />

O 2<br />

content<br />

While the catalase activity in leaves of nontransgenic rice at<br />

25 o C was around 100 (µmol mg –1 protein min –1 ), the transgenic<br />

rice showed values of approximately 700. After 4 d of chilling,<br />

the activities in both nontransgenic and transgenic rice<br />

were reduced to approximately 60 and 390, respectively (Fig.<br />

2). After 8 d, the transgenic rice showed 4 times higher residual<br />

activity than the control (Matsumura et al 2002).<br />

In the transgenic plants, the content of H 2 O 2 (about 0.36<br />

µmol g –1 FW) was kept low during chilling. In contrast, the<br />

nontransgenic plants showed an increased content of H 2 O 2 by<br />

chilling, and, at the end of the 8-d chilling period, the content<br />

reached a level two times that of the control (about 0.68 µmol<br />

g –1 FW). Thus, high catalase activities remaining in the<br />

108 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Catalase activity (mmol min –1 mg –1 protein)<br />

800<br />

Nontransgenic<br />

Transgenic<br />

700<br />

600<br />

500<br />

400<br />

300<br />

Fig. 1. Visible damage from chilling. Transgenic and nontransgenic<br />

plants were grown in a growth chamber for 1 mo and then chilled<br />

at 5 °C for 8 d. (A) Nontransgenic rice plant (control), (B) transgenic<br />

rice plant.<br />

200<br />

100<br />

transgenic plants seem to prevent an increase in H 2 O 2 content<br />

after chilling.<br />

0<br />

0 1 2 3 4<br />

Chilling period (day)<br />

Electrolyte leakage induced by chilling<br />

Both the transgenic and nontransgenic plants showed the same<br />

leakage value (10%) after 2 d of chilling. However, the leakage<br />

of the control plants increased dramatically to approximately<br />

60% at 4 d and reached 69% at 8 d. In contrast, the<br />

transgenic plants indicated a gradual increase in the leakage,<br />

and the value was only 36% after 8 d. This lower electrolyte<br />

leakage, which is essential for membrane integrity (Uemura et<br />

al 1995), suggests that effective detoxification of H 2 O 2 by the<br />

elevated catalase activity contributes to the maintenance of<br />

membrane integrity in the transgenic plants at low temperatures.<br />

Effect of chilling on photosynthetic activity<br />

Photosynthetic activities in both transgenic and nontransgenic<br />

plants were decreased gradually by chilling. However, we could<br />

not find a difference in Fv/Fm values between them during the<br />

chilling up to 8 d. Because the Fv/Fm value indicated only the<br />

activity of photosystem II, other systems or components in the<br />

photosynthesis machinery may be considered as the injury sites.<br />

Fig. 2. Effect of chilling on catalase activity. <strong>Rice</strong> plants grown for<br />

1 mo were chilled at 5 °C for the indicated period and catalase<br />

activity in leaves was then measured at 25 °C.<br />

Effect of chilling on respiratory<br />

and mitochondrial activity<br />

Although respiratory activity was decreased by the chilling,<br />

approximately 80% of the activity remained after 8 d of chilling<br />

in both the transgenic and nontransgenic plants, suggesting<br />

that t<strong>here</strong> were no differences in the chilling sensitivity of<br />

the respiratory chain between them. Next, we examined the<br />

effect of chilling on mitochondrial activity, with TTC reduction<br />

as an index of membrane integrity as reported by Steponkus<br />

(1971). TTC reduction did not change until 2 d of chilling in<br />

both the transgenic and nontransgenic plants. A prolonged chilling<br />

treatment resulted in a decrease in value in nontransgenic<br />

rice to 68% and 46% at 6 and 8 d, respectively. In contrast, the<br />

transgenic plants showed no decrease in value during chilling<br />

of up to 6 d and only decreased to 57% at 8 d. T<strong>here</strong>fore, we<br />

conclude that the oxidative damage from chilling on the membrane-associated<br />

mitochondrial function in transgenic plants<br />

was minimized but not in nontransgenic rice plants. The reason<br />

for the discrepancy between the results of the respiratory<br />

and TTC reduction activities, however, is not clear at this<br />

moment.<br />

Membrane fatty acid peroxidation<br />

Because membrane fatty acids are the major target of<br />

peroxidation by H 2 O 2 (Iturbe-Ormaetxe et al 1998), we examined<br />

the formation of peroxidation products of fatty acids, TBA,<br />

Session 3: Opportunities and challenges of transgenic rice 109


y chilling. When the value at the beginning of chilling was<br />

taken as 100%, the value of nontransgenic rice increased dramatically<br />

to 301%, 339%, and 343% at 4, 6, and 8 d of chilling,<br />

respectively. In the transgenic rice plants, in contrast, the<br />

value was lower than that of the nontransgenic plants (183%<br />

and 289% at 4 and 6 d, respectively). However, at 8 d, the<br />

value in the transgenic rice showed almost the same value as<br />

in the nontransgenic rice (344%). Thus, membrane fatty acids<br />

in the nontransgenic plants, but not in the transgenic plants,<br />

are considered to be readily peroxidized by H 2 O 2 by chilling.<br />

From these results, we concluded that the enhanced tolerance<br />

of chilling in transgenic rice plants is partly due to the<br />

effective removal of H 2 O 2 by the overexpressed catalase and<br />

increased stability of the membrane during chilling.<br />

References<br />

Clarke AK, Campbell D. 1996. Inactivation of the petE gene for<br />

plastocyanin lowers photosynthetic capacity and exacerbates<br />

chilling-induced photoinhibition in the Cyanobacterium<br />

Synechococcus. Plant Physiol. 112:1551-1561.<br />

Heath RL, Packer L. 1968. Photoperoxidation in isolated chloroplasts.<br />

I. Kinetics and stoichimetry of fatty acid peroxidation.<br />

Arch. Biochem. Biophys. 125:189-198.<br />

Iturbe-Ormaetxe I, Escuredo PR, Arrese-Igor C, Becana M. 1998.<br />

Oxidative damage in pea plants exposed to water deficit or<br />

paraquat. Plant Physiol. 116:173-181.<br />

Wrap-up of Session 3<br />

Matsumura T, Tabayashi N, Kamagata Y, Souma C, Saruyama H.<br />

2002. Wheat catalase expressed in transgenic rice can improve<br />

tolerance against low temperature stress. Physiol. Plant.<br />

116:317-327.<br />

Patterson BD, MacRae EA, Ferguson IB. 1984. Estimation of hydrogen<br />

peroxide in plant extract using titanium (IV). Anal.<br />

Biochem. 139:487-494.<br />

Puntarulo S, Galleano M, Sanchez RA, Boveris A. 1988. Hydrogen<br />

peroxide metabolism in soybean embryonic axes at the onset<br />

of germination. Plant Physiol. 86:626-630.<br />

Steponkus PL, Lanphear FO. 1967. Refinement of the triphenyl tetrazolium<br />

chloride method of determining cold injury. Plant<br />

Physiol. 42:1423-1426.<br />

Steponkus PL. 1971. Effect of freezing on dehydrogenase activity<br />

and reduction of triphenyl tetrazolium chloride. Cryobiology<br />

8:570-573.<br />

Uemura M, Joseph RA, Steponkus PL. 1995. Cold acclimation of<br />

Arabidopsis thaliana: effect on plasma membrane lipid composition<br />

and freeze-induced lesions. Plant Physiol. 109:15-<br />

30.<br />

Notes<br />

Authors’ addresses: H. Saruyama, Hokkaido Green-Bio <strong>Institute</strong>,<br />

Naganuma, Hokkaido 069-1317, Japan, e-mail:<br />

66379635@people.or.jp; H. Onodera and M. Uemura,<br />

Cryobiosystem <strong>Research</strong> Center, Faculty of Agriculture, Iwate<br />

University, Morioka, Iwate 020-8550, Japan.<br />

Acknowledgments: This work was supported in part by a Grant-in-<br />

Aid for the 21st Century COE Program to Iwate University<br />

from the MEXT, Japan, to MU.<br />

<strong>Rice</strong> is the most important food crop for half the world’s population.<br />

Because of the growing population in Asian countries, more<br />

rice will have to be produced from less land for cultivation. Genetic<br />

engineering of rice could solve this problem by permitting<br />

higher productivity, including more resistance to biotic and abiotic<br />

stresses as an alternative technology of conventional breeding.<br />

Biotechnology using genetic engineering makes it possible<br />

to introduce valuable genes from all organisms into the rice genome.<br />

The application of genetic engineering is not limited to<br />

agriculture but is relevant to industry as molecular farming. <strong>Rice</strong><br />

can be used as a bio-reactor for producing high added value<br />

such as biopharmaceuticals (antibodies, vaccines).<br />

In Session 3, six leading researchers reviewed the present<br />

status of studies on transgenic rice. Transgenic rice for improved<br />

input traits showing resistance to biotic and abiotic stress and<br />

output traits with improved quality of rice grain has been developed.<br />

To increase rice productivity, M. Tokutomi’s research group<br />

has introduced genes coding for maize C 4 -specific photosynthetic<br />

enzymes such as PEPC, PPDK, and NADP malic enzyme. Although<br />

transgenic rice overexpressing C 4 enzymes exhibited a higher<br />

photosynthetic rate, these plants showed little increase in yield.<br />

Tolerance of unfavorable circumstances such as not using Fedeficient<br />

soil is important for expanding cultivation land to enhance<br />

rice production worldwide. N. Nishizawa showed that<br />

transgenic rice plants were tolerant of low Fe availability in calcareous<br />

soil when barley genes encoding the enzymes involved<br />

in the biosynthesis of mugineic acid family phyotosiderophores<br />

(MAs) were introduced into the rice genome. This is because<br />

transgenic rice plants secrete higher amounts of deoxymugineic<br />

acid. Her group has characterized the transporter genes involved<br />

in the uptake and translocation of iron and zinc from the soil.<br />

Plant productivity is affected severely by environmental<br />

stresses such as cold, drought, and high salinity. K. Shinozaki’s<br />

group has identified a cis-regulatory element designated as the<br />

dehydration response element box (DREB), which is conserved<br />

in promoters of many genes implicated in gene regulation in response<br />

to the above stress. They demonstrated that the DREB<br />

transcription factor gene is quite useful for improving tolerance<br />

of environmental stresses in transgenic rice, when the DREB recognizing<br />

the conserved sequence was overexpressed under the<br />

control of a stress-inducible promoter.<br />

Yield is severely decreased by pathogen attacks such as<br />

fungal rice blast. Disease resistance can be enhanced by intro-<br />

110 <strong>Rice</strong> is life: scientific perspectives for the 21st century


ducing disease-resistance genes. M. Kawata suggested that an<br />

antimicrobial peptide such as defensin expressed in transgenic<br />

rice exhibited effective resistance against rice blast and bacterial<br />

leaf blight in field tests.<br />

To engineer transgenic rice acceptable to many consumers,<br />

the introduction of output traits with consumer benefits into<br />

rice grain is necessary. Output traits are those for improving not<br />

only macronutrients such as proteins, carbohydrates, and oils<br />

but also micronutrients such as vitamin A, iron, and zinc for food<br />

and feed. Furthermore, both these nutrients and biofunctional<br />

materials contributing to human health are targets of transgenic<br />

rice. Target characters are quite different between developing<br />

and developed countries.<br />

Many people in South Asia suffer from deficiency in iron<br />

and vitamin A, which causes blindness, anemia, and poor growth.<br />

<strong>Rice</strong> grain offers an excellent delivery system for these missing<br />

micronutrients because of the ease of storage and high daily<br />

consumption. S. Datta reported that iron-fortified rice and “golden<br />

rice,” rich in provitamin A, have been developed by expression of<br />

the iron storage protein ferritin and several enzyme genes involved<br />

in beta-carotene biosynthesis, respectively, in the endosperm<br />

tissue of several tropical indica rice varieties. This<br />

transgenic rice will help solve health problems in Asia.<br />

In developed countries, life-style-related diseases such as<br />

hypertension, diabetes, and high cholesterol are social problems<br />

and these have been gradually increasing. In addition, patients<br />

suffering from allergenic diseases such as pollen and food allergy<br />

are rapidly increasing. If rice were transformed to alleviate or<br />

prevent these diseases with an appropriate daily diet, transgenic<br />

rice grain would be of direct benefit to many consumers in developed<br />

countries, thus indicating a high potential for acceptance<br />

by consumers. F. Takaiwa discussed transgenic rice grain with a<br />

function to decrease serum cholesterol level by accumulating<br />

the soybean storage protein glycinin in the endosperm tissue.<br />

The soy-rice was rich in the essential amino acid lysine deficient<br />

in rice grain.<br />

It was demonstrated that oral feeding of transgenic rice<br />

grain to mice before sensitization with allergen suppressed the<br />

IgE level in spleen cells, indicating that oral feeding induces immunological<br />

tolerance.<br />

Session 3: Opportunities and challenges of transgenic rice 111


SESSION 4<br />

Improving rice yield potential<br />

CONVENER: M. Kondo (NARO)<br />

CO-CONVENERS: H. Ikehashi (Nihon Univ.) and S. Peng (<strong>IRRI</strong>)


Photosynthesis improvement in rice:<br />

Rubisco as a target for enhancing N-use efficiency<br />

Amane Makino<br />

Ribulose-1,5-bisphosphate (RuBP) carboxylase/oxygenase<br />

(Rubisco) catalyzes two competing reactions, photosynthetic<br />

CO 2 fixation and photorespiratory carbon oxidation. Quantitative<br />

analyses of the photosynthetic gas exchange and Rubisco<br />

activity in C 3 plants have revealed that Rubisco is a rate-limiting<br />

factor for potential photosynthesis under the present atmospheric<br />

air conditions. In addition, Rubisco is the most abundant<br />

leaf protein and large amounts of nitrogen are invested in<br />

this protein, accounting for 15% to 30% of leaf-N content.<br />

T<strong>here</strong>fore, genetic modification to enhance Rubisco efficiency<br />

in crops would have great agronomic importance as a prospect<br />

to enhance N-use efficiency for potential photosynthesis.<br />

This paper discusses the possible approaches for photosynthetic<br />

improvement by enhancing Rubisco efficiency in rice.<br />

Is enhancement of Rubisco efficiency feasible<br />

Large variations in the kinetic properties of Rubisco exist<br />

among enzymes from different groups of photosynthetic species<br />

(for a review, see Bainbridge et al 1995). Such natural<br />

variations suggested that it is possible to alter the enzyme to<br />

favor the specificity for CO 2 relative to O 2 and to enhance the<br />

specific activity (catalytic turnover rate per unit of enzyme).<br />

However, a negative correlation has also been found between<br />

the CO 2 /O 2 specificity and the catalytic turnover rate. In addition,<br />

Rubiscos from higher plants have the highest specificity<br />

for CO 2 to O 2 among all photosynthetic organisms, and their<br />

variation is very small. Although a higher CO 2 /O 2 specificity<br />

than higher-plant Rubiscos was previously discovered for a<br />

few red algae, the catalytic rate of algal Rubiscos was too low.<br />

Thus, it may be difficult to find a super Rubisco in nature.<br />

In spite of no variation in CO 2 /O 2 specificity among<br />

higher-plant Rubiscos, comparative studies of Rubisco activity<br />

among higher plants revealed significant differences in specific<br />

activity (Table 1). Rubisco from rice had the lowest specific<br />

activity, which was significantly lower than that from<br />

wheat. In addition, the difference in the specific activity between<br />

rice and wheat reflected the observed difference in the<br />

light-saturated rate of photosynthesis at atmospheric CO 2 levels<br />

(Fig. 1). These results indicate that Rubisco limits the potential<br />

photosynthesis in C 3 plants and that the lower specific<br />

activity from rice would make it possible to improve photosynthesis<br />

by introducing a more efficient Rubisco into rice<br />

cultivars. Unfortunately, no variability in the kinetic properties<br />

of Rubisco has been found among rice varieties, including<br />

old and modern cultivars (Makino et al 1987). Significant variations<br />

existed only on the basis of different genotypes in the<br />

Oryza genus (Makino et al 1987), suggesting that Rubisco<br />

Table 1. Rubisco-specific activity from several C 3<br />

higher plants. a<br />

Species<br />

Specific activity<br />

(mol CO 2 m –2 s –1 at 25 °C)<br />

Oryza sativa 15.5 ± 0.8<br />

Triticum aestivum 23.0 ± 0.4<br />

Triticum monococcum 16.2 ± 0.9<br />

Aegilops squarrosa 16.4 ± 0.3<br />

Spinacia oleracea 24.1 ± 0.8<br />

Phaseolus vulgaris 16.6 ± 0.2<br />

Pisum sativum 20.4 ± 0.4<br />

Nicotiana tobaccum 18.3 ± 1.1<br />

a Data are taken from Makino (2003) and Evans and Austin<br />

(1986).<br />

Photosynthesis at 36 Pa CO 2 (mmol m –2 s –1 )<br />

50<br />

40<br />

30<br />

20<br />

10<br />

Triticum aestivum<br />

Oryza sativa<br />

0 0 1.0 2.0 3.0 4.0 5.0<br />

Rubisco (g m –2 )<br />

Fig. 1. Light-saturated photosynthesis in air versus Rubisco content<br />

in leaves of rice (open circles) and wheat (closed circles)<br />

(Makino 2003). Measurements were made on leaves at different<br />

ages at a temperature of 25 °C, an irradiance of 1,800 µmol<br />

quanta m –2 s –1 , and an external CO 2 partial pressure of 36 Pa.<br />

cannot be a target for classical crossbreeding among cultivars.<br />

Similarly, in the Triticum genus, variation in the specific activity<br />

for a main cultivar of wheat, T. aestivum, was not significant,<br />

w<strong>here</strong>as t<strong>here</strong> were some differences correlated with<br />

the genome constitution in Triticum and Aegilops genotypes<br />

114 <strong>Rice</strong> is life: scientific perspectives for the 21st century


(Evans and Austin 1986, see Table 1). In addition, Evans and<br />

Austin (1986) found that Rubisco from T. aestivum has the<br />

highest specific activity and that the occurrence of the highest<br />

specific activity is associated with possession of the B-type<br />

chloroplast genome, which encodes a large subunit of Rubisco.<br />

Although the divergence in the small subunit had been considered<br />

to be a more important causal factor for the variations in<br />

Rubisco activity because the large subunit is more conserved,<br />

the results of Evans and Austin suggested that the rbcL gene<br />

of a highly efficient Rubisco can be targeted for improving<br />

photosynthesis.<br />

Recently, technology for plastid transformation, at least<br />

with tobacco, has enabled a more precise manipulation and<br />

replacement of the chloroplast-coded large subunit of Rubisco<br />

(for a review, see Andrews and Whitney 2003). Such plastid<br />

transformation provides a transgenic tobacco with a hybrid of<br />

Rubisco with large and small subunits derived from different<br />

higher plants. For example, replacing tobacco rbcL with sunflower<br />

rbcL showed that, although the hybrid Rubisco is enzymatically<br />

active, its activity is extremely low. These results<br />

indicate that hybrid Rubisco with a large foreign subunit, once<br />

introduced to a host plant, does not function to its full potential.<br />

Thus, the replacement of Rubisco with an existing more<br />

efficient Rubisco requires the complete replacement of both<br />

large and small subunits. Of course, another problem with the<br />

manipulation of Rubisco is to develop plastid transformation<br />

techniques for the major crop species, including rice.<br />

Rubisco activase is essential for the full function of<br />

Rubisco activity, but Rubisco activase from tobacco is not effective<br />

for the activation of Rubisco from spinach, barley, and<br />

wheat. T<strong>here</strong>fore, it is possible that the replacement of Rubisco<br />

activase is also required for the full function of foreign Rubisco.<br />

Genetic manipulation of the amount of Rubisco<br />

An increase in Rubisco content theoretically leads to an improvement<br />

of photosynthesis under CO 2 -limited conditions.<br />

An attempt to increase Rubisco content by supplementation<br />

with an additional sense rbcS gene showed increases in Rubisco<br />

content for a given leaf-N content (Makino et al, unpublished).<br />

However, gas exchange analyses on transgenic rice with<br />

overexpressed Rubisco indicated that photosynthesis is CO 2 -<br />

saturated under normal CO 2 levels (37 Pa CO 2 ). These greater<br />

increases in Rubisco are assumed to lead to an imbalance<br />

among the in vivo capacities of Rubisco and other photosynthetic-limiting<br />

factors. This may have been caused by the nonspecific<br />

reallocation of N to Rubisco from other components<br />

limiting photosynthesis, which resulted in a decrease in the<br />

capacity for RuBP regeneration.<br />

When a leaf is senescent, the Rubisco content decreases<br />

faster than that of other photosynthetic components. T<strong>here</strong>fore,<br />

the maintenance of Rubisco content in a leaf during senescence<br />

also has agronomic importance. However, although<br />

the degradation of Rubisco is the major determinant of Rubisco<br />

content in a senescent leaf (Makino et al 1984), its degradation<br />

mechanism is largely unknown. Although the degradation<br />

of Rubisco by reactive oxygen was observed for isolated chloroplasts<br />

in the presence of inhibitors for antioxidant enzymes,<br />

the degradation process in a leaf may be more strictly regulated<br />

than expected. For example, a selective suppression of<br />

the degradation of Rubisco was suggested to occur in the senescent<br />

leaf of rbcS antisense rice with a decreased Rubisco<br />

content (Ishizuka et al 2004).<br />

What is a target for improving RuBP regeneration<br />

To maintain higher Rubisco efficiency, higher RuBP regeneration<br />

capacity is required. Comparative analyses of the photosynthetic<br />

characteristics between rice and wheat indicated<br />

that the capacity for RuBP regeneration is also greater in wheat<br />

than in rice (Sudo et al 2003). This higher capacity for RuBP<br />

regeneration in wheat was most closely related to a greater<br />

cytochrome f content. As RuBP regeneration capacity is limited<br />

by the electron transport capacity and/or Pi regeneration<br />

capacity during sucrose and starch syntheses, the cytochrome<br />

b6/f complex may conceivably be a factor in the RuBP regeneration<br />

capacity. Thus, the enhancement of the cytochrome b6/<br />

f complex content may be another important target for improving<br />

photosynthesis to maintain the balance between the capacities<br />

of Rubisco and RuBP regeneration.<br />

Introduction of C 4<br />

characteristics into rice<br />

Generally, C 4 plants show a higher rate for photosynthetic CO 2<br />

assimilation than C 3 plants because C 4 plants have a mechanism<br />

for eliminating photorespiration by increasing the concentration<br />

of CO 2 around Rubisco. T<strong>here</strong>fore, another approach<br />

to improving photosynthesis is to introduce C 4 characteristics<br />

into rice (for a review, see Miyao 2003). However, even when<br />

photosynthesis was measured under saturating CO 2 levels (100<br />

Pa CO 2 ), the rate of photosynthesis for a given leaf-N content<br />

was higher in maize than in rice (Makino et al 2003). Since the<br />

amount of Rubisco in C 3 plants is excessive for CO 2 -saturated<br />

photosynthesis, it is possible that an excess investment of N in<br />

Rubisco in C 3 plants led to lower photosynthesis in rice than<br />

in maize under conditions of saturating CO 2 . However, the<br />

photosynthetic rate in maize leaves was still higher than that<br />

in leaves of the rbcS antisense rice with optimal Rubisco for<br />

CO 2 -saturated photosynthesis. These results indicate that, even<br />

if photorespiration is eliminated and Rubisco content is optimized<br />

for saturating CO 2 conditions, photosynthetic efficiency<br />

is still higher in maize than in rice. This higher efficiency of<br />

photosynthesis in maize resulted from the saving of N due to<br />

the lower amount of Rubisco of a higher V max /Km(CO 2 ) type<br />

and allowed a greater N investment in thylakoid components<br />

(Makino et al 2003). The N cost for the C 4 cycle enzymes was<br />

not large in maize, and the greater content of the thylakoid<br />

components may have led to an enhancement of RuBP regeneration.<br />

Recent genetic manipulation to express high levels of<br />

C 4 cycle enzymes from maize at target locations in rice is becoming<br />

well established (for a review, see Miyao 2003). Such<br />

Session 4: Improving rice yield potential 115


technology may lead to the eventual successful driving of the<br />

complete C 4 cycle in rice in the near future. To improve photosynthetic<br />

efficiency in rice, however, optimal protein allocation<br />

with a lower amount of Rubisco of a type different from<br />

that in C 3 plants, as well as the Kranz leaf anatomy to obtain<br />

an efficient CO 2 -concentrating mechanism, is essential.<br />

References<br />

Andrews TJ, Whitney SM. 2003. Manipulating ribulose bisphosphate<br />

carboxylase/oxygenase in the chloroplasts of higher plants.<br />

Arch. Biochem. Biophys. 414:159-169.<br />

Bainbridge G, Madgwick P, Parmar S, Mitchell R, Paul M, Pitts J,<br />

Key AJ, Parry MAJ. 1995. Engineering Rubisco to change its<br />

catalytic properties. J. Exp. Bot. 46:1269-1276.<br />

Evans JR, Austin RB. 1986. Ribulose-1,5-bisphosphate carboxylase<br />

specific activity in relation to wheat genotype. Planta 167:344-<br />

350.<br />

Ishizuka M, Makino A, Suzuki Y, Mae T. 2004. The amount of ribulose-1,5-bisphosphate<br />

carboxylase/oxygenase (Rubisco) protein<br />

and levels of mRNAs of rbcS and rbcL in the leaves at<br />

different positions in transgenic rice plants with decreased<br />

content of Rubisco. Soil Sci. Plant Nutr. 50:233-239.<br />

Makino A. 2003. Rubisco and nitrogen relationships in rice: leaf<br />

photosynthesis and plant growth. Soil Sci. Plant Nutr. 49:319-<br />

327.<br />

Makino A, Mae T, Ohira K. 1984. Relation between nitrogen and<br />

ribulose-1,5-bisphosphate carboxylase in rice leaves from<br />

emergence through senescence. Plant Cell Physiol. 25:429-<br />

437.<br />

Makino A, Mae T, Ohira K. 1987. Variations in the contents and<br />

kinetic properties of ribulose-1,5-bisphosphate carboxylases<br />

among rice species. Plant Cell Physiol. 28:799-804.<br />

Makino A, Sakuma H, Sudo E, Mae T. 2003. Differences between<br />

maize and rice in N-use efficiency for photosynthesis and protein<br />

allocation. Plant Cell Physiol. 44:952-956.<br />

Miyao M. 2003. Molecular evolution and genetic engineering of C 4<br />

photosynthetic enzymes. J. Exp. Bot. 54:179-189.<br />

Sudo E, Makino A, Mae T. 2003. Differences between rice and wheat<br />

in ribulose-1,5-bisphosphate regeneration capacity per unit<br />

of leaf-N content. Plant Cell Environ. 26:255-263.<br />

Notes<br />

Author’s address: Department of Applied Plant Science, Graduate<br />

School of Agricultural Science, Tohoku University, 1-1<br />

Tsutsumidori-Amamiyamachi, Aoba-ku, Sendai 981-8555,<br />

Japan.<br />

Carbon metabolism to improve sink and source function<br />

R. Ohsugi<br />

Sink and source function and their relationship are important<br />

aspects to understand the regulatory mechanism of crop production<br />

such as rice. In terms of carbon metabolism, the source<br />

function in rice leaves includes photosynthetic carbon fixation,<br />

sucrose formation, and its loading into sieve elements.<br />

The sink function in rice panicles includes sucrose unloading,<br />

its breakdown, and starch biosynthesis. In addition, leaf sheaths<br />

and culms show sink and source functions before and after<br />

heading, respectively. In the latter stage, starch breakdown is<br />

a function of major carbon metabolism.<br />

<strong>Rice</strong> genome research has been developing widely, providing<br />

a huge amount of gene information, DNA markers, and<br />

high-throughput technologies such as DNA microarray, allowing<br />

us to analyze these complex networks of carbon metabolism.<br />

At the same time, this makes it possible to elucidate the<br />

genetic basis of physiological traits such as sink and source<br />

function using a genetic map and DNA markers.<br />

I introduce some examples of these new approaches on<br />

sink and source functions.<br />

Source function<br />

Recent progress in the generation of a molecular genetic map<br />

and markers has made it possible to map individual genes as-<br />

sociated with complex traits, quantitative trait loci (QTLs).<br />

Ishimaru et al (2001a) applied QTL analysis to physiological<br />

traits, including sink and source functions. Using backcross<br />

inbred lines of Nipponbare (japonica) × Kasalath (indica), a<br />

rice function map was constructed by collating the results on<br />

QTLs for 23 important agronomic, physiological, and morphological<br />

traits. The source function-related traits such as<br />

chlorophyll content in leaves, photosynthetic ability, and δ 13 C<br />

value were mapped. These traits were first mapped in the QTL<br />

analysis of rice in their study. One of three QTLs controlling<br />

chlorophyll content partly overlapped with that controlling<br />

yield, although most of these source function-related traits did<br />

not overlap with that controlling yield.<br />

Among these source function-related QTLs, Ishimaru et<br />

al (2001b) further analyzed Rubisco content, soluble protein<br />

content, and nitrogen content in flag leaves of rice. The kinetics<br />

of Rubisco and the ratio of Rubisco to total leaf nitrogen<br />

(N) are the two main factors determining N-use efficiency for<br />

photosynthetic carbon fixation. Since the kinetics of Rubisco<br />

is very difficult to change, the ratio of Rubisco to total leaf N<br />

content is the main target for the improvement of N-use efficiency.<br />

In their function map, QTLs controlling Rubisco content<br />

were not detected near QTLs for total leaf N content, indicating<br />

that contents of Rubisco and total leaf N are controlled<br />

116 <strong>Rice</strong> is life: scientific perspectives for the 21st century


y different genetics. QTLs that controlled the ratio of Rubisco<br />

to total leaf N were detected, suggesting that some genetic<br />

factor(s) may be involved in determining this ratio.<br />

Temporary sink function (sink to source transition)<br />

Grain filling and yield are affected by the amount of carbohydrates<br />

supplied from two organs: mature leaves and leaf sheaths<br />

plus culms. Nonstructural carbohydrates (NSCs) in leaf sheaths<br />

and culms are mainly translocated to panicles, and play an<br />

important role in compensating for the lack of a source supply<br />

by photosynthesis after heading. NSC accumulation may be<br />

particularly important for grain filling in high-yielding cultivars<br />

that bear a large number of spikelets, which require a large<br />

supply of carbohydrates.<br />

Nagata et al (2002) applied QTL analysis to elucidate<br />

the genetic basis of NSC accumulation in leaf sheaths and culms<br />

of rice, for the first time in the main cereal crops, using backcross<br />

inbred lines from the cross Sasanishiki(japonica)/<br />

Habataki (indica)//Sasanishiki///Sasanishiki. They found QTLs<br />

affecting NSC accumulation on chromosomes 1, 4, 5, 7, 11,<br />

and 12. Of these, the indica allele of the QTLs found on chromosomes<br />

5 and 11 increased NSC accumulation and exerted<br />

some effects on the reduction in the percentage of incompletely<br />

filled spikelets, suggesting that the expression of these QTLs<br />

could improve grain filling of rice.<br />

Recently, Ebitani et al (2004) developed introgression<br />

lines (ILs) with a chromosome segment of Kasalath (indica) in<br />

the genetic background of Koshihikari (japonica). Once a QTL<br />

of interest is detected on a particular chromosome using ILs,<br />

near-isogenic lines for QTLs (QTL-NILs) can be developed<br />

in one or two additional generations from advanced backcross<br />

populations. Using these 39 ILs grown in the field in 2003<br />

when it was a cold summer, we examined starch accumulation<br />

in the second leaf sheath below the flag leaf. Measurements<br />

were done twice: at the heading stage and 14 days after heading<br />

(DAH). Two ILs whose starch contents were similar to<br />

that of Koshihikari at the heading stage but significantly decreased<br />

(P


efficiently with the large-scale measurement of gene expression<br />

for NILs and/or ILs that include target loci. The combination<br />

of QTL analysis and high-throughput technologies such<br />

as microarray could be very useful for this purpose.<br />

References<br />

Ebitani T, Yano M, Takarada T, Omoteno M, Takeuchi Y, Nonoue S,<br />

Yamamoto Y. 2004. Novel breeding approach through development<br />

of introgression lines in rice. Proceedings of the 4th<br />

<strong>International</strong> Crop Science Congress, 26 September-1 October<br />

2004, Brisbane, Australia. CD-ROM.<br />

Ishimaru K, Yano M, Aoki N, Ono K, Hirose T, Lin S Y, Monna L,<br />

Sasaki T, Ohsugi R. 2001a. Toward mapping of physiological<br />

and agronomic characters on a rice function map: QTL analysis<br />

and comparison between QTLs and expressed sequence<br />

tags. Theor. Appl. Genet. 102:793-800.<br />

Ishimaru K, Kobayashi N, Ono K, Yano M, Ohsugi R. 2001b. Are<br />

contents of Rubisco, soluble protein and nitrogen in flag leaves<br />

of rice controlled by the same genetics J. Exp. Bot. 52:1827-<br />

1833.<br />

Ishimaru T, Matsuda T, Ohsugi R, Yamagishi T. 2003. Morphological<br />

development of rice caryopses located at the different positions<br />

in a panicle from early to middle stage of grain filling.<br />

Funct. Plant Biol. 30:1139-1149.<br />

Ishimaru T, Hirose T, Takahashi K, Sasaki H, Ohsugi R, Yamagishi<br />

T. 2004. Relationship between endosperm development and<br />

the gene expression of cell wall invertase isoforms: comparison<br />

between superior and inferior caryopses. Jpn. J. Crop Sci.<br />

73(Extra issue):170-171.<br />

Nagata K, Shimizu H, Terao T. 2002. Quantitative trait loci for<br />

nonstructural carbohydrate accumulation in leaf sheaths and<br />

culms of rice (Oryza sativa L.) and their effects on grain filling.<br />

Breed. Sci. 52:275-283.<br />

Yamagishi J, Miyamoto N, Hirotsu R, Laza RC, Nemoto K. 2004.<br />

QTLs for branching, floret formation, and pre-flowering floret<br />

abortion of rice panicle in a temperate japonica × tropical<br />

japonica cross. Theor. Appl. Genet. 10.1007/s00122-004-<br />

1795-5.<br />

Zhu T, Budworth P, Chen W, Provart N, Chang H-S, Guimil S, Su<br />

W, Estes B, Zou G, Wang X. 2003. Transcriptional control of<br />

nutrient partitioning during rice grain filling. Plant Biotech.<br />

J. 1:59-70.<br />

Notes<br />

Author’s address: Graduate School of Agricultural and Life Sciences,<br />

The University of Tokyo, e-mail: aohsugi@mail.ecc.utokyo.ac.jp.<br />

Improving radiation-use efficiency: the acclimation<br />

of photosynthesis to high irradiance in rice leaves<br />

E.H. Murchie, S. Hubbart, S. Peng, and P. Horton<br />

Sunlight is the principal energy source for crops. It is also highly<br />

variable; differences in light levels caused by season, climate,<br />

and position can affect the photosynthetic rate and productivity<br />

of crops. High yields are generally attained under highirradiance<br />

conditions, in which photosynthesis is often saturated<br />

and in full sunlight the number of photons may exceed<br />

photosynthetic requirements. The converse may be true in lowirradiance<br />

conditions such as the tropical wet season, in which<br />

light interception is lower (Weerakoon et al 2000). Here, photosynthesis<br />

may often be light-limited and growing periods are<br />

longer and low-yielding (<strong>IRRI</strong> 1998). These long-term patterns<br />

are punctuated by short-term variation in light. Ideally, a<br />

crop would rapidly maximize photosynthesis according to prevailing<br />

local conditions.<br />

Understanding the processes that affect the efficiency of<br />

transduction of light energy by crops is central to the improvement<br />

of yield potential: this was highlighted by one recent study<br />

that showed that the radiation-use efficiency (biomass produced<br />

per unit of radiation energy intercepted) of rice is low, even<br />

among C 3 crops, and this is a major limitation to yield potential<br />

(Mitchell et al 1998). An increase in leaf-level photosynthetic<br />

capacity at ambient CO 2 levels is likely to lead to an<br />

increased radiation conversion factor (RCF) (Sheehy et al<br />

2000). It is essential to understand how such variation is accommodated<br />

efficiently within the plant such that biomass production<br />

rates are not affected, or can even be improved. This<br />

is largely carried out by processes termed acclimation. Acclimation<br />

is defined as a change in composition or morphology<br />

of the plant that is a specific response to an environmental<br />

change. T<strong>here</strong> is ample evidence in plant science for significant<br />

variation in the capacity for acclimation to a number of<br />

environmental factors.<br />

Additionally, it is vital to consider that the requirements<br />

for light and N are strongly linked: the efficient use of highirradiance<br />

levels (high photosynthetic rates) requires the assimilation<br />

of large quantities of N. Leaf N content stored in<br />

the lower leaves of the canopy is essential for high grain yield<br />

(Sheehy et al 2000) and any attempt to improve photosynthesis<br />

must take this into account.<br />

This paper summarizes the responses of rice plants to<br />

excess irradiance. Genotype variation in light responses is<br />

described. Emphasis is placed on photosynthesis and the identification<br />

of limitations to biomass productivity.<br />

118 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Photosynthesis in saturating light<br />

This section identifies the limitations to photosynthesis in highlight<br />

environments at the leaf level. However, it is recognized<br />

that a crop canopy consists of a population of leaves with different<br />

photosynthetic capacities and operating at varying degrees<br />

of saturation. In response to an incrementing light level,<br />

starting from darkness, photosynthesis in a given leaf will in<br />

the first instance show light-limiting rates that give way to light<br />

saturation at higher light intensities. The light intensity at which<br />

saturation is reached is dependent on the capacity for assimilation<br />

by the leaf, which is in turn dependent on growth and<br />

measurement parameters. However, the intensity at which saturation<br />

is reached is particularly important since it defines the<br />

efficiency of photosynthesis at high-light levels. For rice growing<br />

in the field in the tropical dry season, irradiance can exceed<br />

2,000 µmol m –2 s –1 (Murchie et al 1999). However, it has<br />

been shown that photosynthesis in rice leaves generally saturates<br />

at just over 1,000 µmol m –2 s –1 . T<strong>here</strong>fore, a large proportion<br />

of incoming irradiance is in excess of assimilatory requirements.<br />

This causes photo-protective responses to be induced<br />

even under otherwise ideal conditions (Murchie et al<br />

1999). If photosynthesis is limited by additional factors such<br />

as water availability, this can exacerbate stress responses.<br />

The saturation of photosynthesis at the leaf level is a<br />

recognized contributor to RCF values (Mitchell et al 1998).<br />

Additional events can be observed at high irradiance, which,<br />

under certain conditions, may limit photosynthesis. Mid-day<br />

depression of photosynthesis is a temporary reduction in photosynthetic<br />

rate often associated with the high leaf temperatures<br />

and vapor pressure deficits that occur in bright conditions.<br />

It has been observed in rice (Black et al 1995, Murchie<br />

et al 1999) though mechanistically it remains somewhat undefined.<br />

Photoinhibition is a reduction in quantum yield caused<br />

by prolonged exposure (hours or days) to high irradiance. It is<br />

caused by damage to, or down-regulation of, primary photosynthetic<br />

reactions. It may also contribute to a reduction in<br />

photosynthetic rate. It has been observed in rice plants in the<br />

dry season in the Philippines even under well-watered, optimal<br />

conditions (Murchie et al 1999). Under saturating irradiance,<br />

photoinhibition will not necessarily affect the rate of assimilation.<br />

However, since it affects primary photosynthetic<br />

events, efficiency at low light may be affected: should a transition<br />

to low light follow a prolonged period of high light, the<br />

assimilation rate will be reduced (Horton 2000, Zhu et al 2004).<br />

Acclimation to high irradiance: genotype variation<br />

Plants respond to irradiance levels in the long term by adjusting<br />

the components of photosynthesis. This can occur on a<br />

morphological level, in terms of leaf thickness, as well as a<br />

chloroplast level, in which the stoichiometry of individual components<br />

can vary. Generally, these responses maintain the efficiency<br />

of photosynthesis in low light while enhancing the capacity<br />

of photosynthesis in high light.<br />

Difference in photosynthetic capacity<br />

between high and low growth irradiance (%)<br />

25<br />

20<br />

15<br />

10<br />

5<br />

0<br />

IR8 IR22 IR40 IR42 IR45 IR54 IR68 IR72 NPT<br />

Cultivar<br />

Fig. 1. Photosynthetic responses to growth under low light (LL:<br />

250 µmol m –2 s –1 ) and high light (HL: 1,500 µmol m –2 s –1 ) in historical<br />

<strong>IRRI</strong> cultivars. Values shown are differences between HL<br />

and LL for light-saturated photosynthesis measured at ambient<br />

CO 2 (2,000 µmol m –2 s –1 , 360 µL L –1 CO 2 .<br />

Through a series of field and laboratory experiments,<br />

we have demonstrated large changes in the response of rice<br />

leaf photosynthesis to irradiance during and after leaf expansion<br />

(Murchie et al 2002, Murchie, Hubbart, Horton, unpublished<br />

data). One important observation to arise from these<br />

studies was that acclimation of photosynthesis seemed to be<br />

restricted to relatively low light intensities: above around 1,000<br />

µmol m –2 s –1 , acclimation of photosynthetic capacity was limited.<br />

Additionally, variation among genotypes was noted: the<br />

new plant type, for example, had very high photosynthetic capacities<br />

at very low growth irradiance.<br />

Such data may present a novel angle in future research<br />

for understanding limitations to photosynthesis in dynamic systems.<br />

Measurements of photosynthetic capacity and leaf composition<br />

at growth irradiances that are (1) limiting and (2) saturating<br />

for photosynthesis should give information on the range<br />

of conditions over which a particular plant or genotype is able<br />

to respond. T<strong>here</strong>fore, we grew a range of historical and modern<br />

<strong>IRRI</strong> cultivars to the ninth-leaf stage in controlled conditions<br />

at two light levels (LL: 250 µmol m –2 s –1 and HL: 1,500<br />

µmol m –2 s –1 ). Photosynthesis, Rubisco, protein, and chlorophyll<br />

content were measured along with morphological parameters<br />

such as leaf area and dry weight.<br />

The difference in light-saturated photosynthesis between<br />

HL and LL plants is shown in Figure 1. The variation is striking:<br />

in particular, the older rice varieties possessed a much<br />

greater range of variation, which was largely caused by a higher<br />

photosynthetic capacity at higher irradiance. The mechanism<br />

of this is unknown since correlation with Rubisco amount or<br />

chlorophyll content was not high. Stomatal conductance but<br />

not stomatal frequency correlated with P max . Additionally,<br />

changes in leaf area were not correlated with changes in either<br />

Session 4: Improving rice yield potential 119


P max or Rubisco. Currently, it is difficult to ascribe this variation<br />

to any consistent feature of biochemistry or morphology.<br />

It is notable that the highest rate of photosynthesis and the<br />

highest capacity for acclimation were as recorded by the oldest<br />

cultivar, IR8. Such variation in leaf photosynthesis in old<br />

and new rice cultivars has not been extensively recorded. It<br />

has been suggested that essential factors such as leaf area index<br />

and N responses may have acted as a surrogate for lightsaturated<br />

rates of leaf photosynthesis during breeding programs<br />

over the last 30 years (Richards 2000). If so, research into the<br />

causes of this loss, and of the genotypic variation in leaf photosynthesis<br />

in general, may generate extremely useful data for<br />

the improvement of yield potential.<br />

References<br />

Black CC, Tu Z-P, Counce PA, Yao P-F, Angelov MN. 1995. An<br />

integration of photosynthetic traits and mechanisms that can<br />

increase crop photosynthesis and grain production. Photosynthesis<br />

Res. 46:169-175.<br />

Horton P. 2000. Prospects for crop improvement through the genetic<br />

manipulation of photosynthesis: morphological and biochemical<br />

aspects of light capture. J. Exp. Bot. 51:475-485.<br />

<strong>IRRI</strong> (<strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>). 1998. <strong>IRRI</strong> research<br />

report for 1998: irrigated rice ecosystems. Manila (Philippines):<br />

<strong>IRRI</strong>.<br />

Mitchell PL, Sheehy JE, Woodward FI. 1998. Potential yields and<br />

the efficiency of radiation use in rice. <strong>IRRI</strong> Discussion Paper<br />

Series No. 32. Manila (Philippines): <strong>International</strong> <strong>Rice</strong> <strong>Research</strong><br />

<strong>Institute</strong>. 62 p.<br />

Murchie EH, Hubbart S, Chen YZ, Peng SB, Horton P. 2002. Acclimation<br />

of rice photosynthesis to irradiance under field conditions.<br />

Plant Physiol. 130:1999-2010.<br />

Murchie EH, Chen Y-Z, Hubbart S, Peng S, Horton P. 1999. Interactions<br />

between senescence and leaf orientation determine in<br />

situ patterns of photosynthesis and photoinhibition in fieldgrown<br />

rice. Plant Physiol. 119:553-563.<br />

Richards RA. 2000. Selectable traits to increase crop photosynthesis<br />

and yield of grain crops. J. Exp. Bot. 51:447-458.<br />

Sheehy JE, Mitchell PL, Dionara J, Ferrer A. 2000. What governs<br />

ceiling yield and its rate of attainment In: Peng S, Hardy B,<br />

editors. 2001. <strong>Rice</strong> research for food security and poverty alleviation.<br />

Proceedings of the <strong>International</strong> <strong>Rice</strong> <strong>Research</strong><br />

Conference, March-April 2000. Los Baños (Philippines): <strong>International</strong><br />

<strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>. p 69-77.<br />

Weerakoon WMW, Ingram KT, Moss DN. 2000. Atmospheric carbon<br />

dioxide and fertiliser effects on radiation interception by<br />

rice. Plant Soil 220:99-106.<br />

Zhu X-G, Ort DR, Whitmarsh J, Long SP. 2004. The slow reversibility<br />

of photosystem II thermal energy dissipation on transfer from<br />

high to low light may cause large losses in carbon gain by<br />

crop canopies: a theoretical analysis. J. Exp. Bot. 55:1167-<br />

1175.<br />

Notes<br />

Authors’ addresses: E.H. Murchie, S. Hubbart, and P. Horton, University<br />

of Sheffield, Department of Molecular Biology and<br />

Biotechnology, Firth Court, Western Bank, S10 2TN, UK; S.<br />

Peng, Crop, Soil, and Water Sciences Division, <strong>International</strong><br />

<strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>, DAPO Box 7777, Metro Manila, Philippines,<br />

e-mail: e.h.murchie@sheffield.ac.uk.<br />

Sink-source relationship and yield potential of rice: effect of<br />

ethylene on grain filling of late-flowering spikelets<br />

P.K. Mohapatra and Rashmi Mohapatra<br />

Poor filling of spikelets on the basal primary branches of the<br />

rice panicle limits genetic potential for yield and produces<br />

grains unsuitable for human consumption (Mohapatra et al<br />

1993). The problem is more acute in the newly developed super<br />

rice with heavy panicles. Spikelet development is very slow<br />

in the proximal part of the panicle; it results in poor partitioning<br />

of dry matter for grain filling (Mohapatra et al 1993). Assimilates<br />

for grain filling are received from the flag leaf and<br />

photo-assimilatory tissues located within the panicle structure<br />

(Yoshida 1981). Senescence of these organs is programmed<br />

genetically, and has a fixed time schedule. T<strong>here</strong>fore, it will<br />

be of interest to know if the late-developed basal spikelets of<br />

the rice panicle become source-limited for assimilates during<br />

their peak period of growth because of the coincidence of senescence<br />

of the photosynthetic tissues. Similarly, the formation<br />

of ABA or ethylene during senescence of these organs<br />

may make the spikelets sink-limited for growth. Ethylene has<br />

been identified as a regulator of senescence in detached rice<br />

leaves (Lin et al 2002), but nothing is known about its role in<br />

the regulation of senescence in intact plants and grain filling.<br />

The application of triazolic compounds reduces ethylene production<br />

in plants, and t<strong>here</strong>by delays senescence (Fletcher et<br />

al 2000). In contrast, 2-chloroethylphosphonic acid (CEPA)<br />

application enhances ethylene production and may expedite<br />

senescence. We need to ascertain the role of ethylene in regulating<br />

the filling of rice spikelets. It is also desirable to distinguish<br />

its action from that of senescence-controlled reduction<br />

in assimilate supply through depletion of source activity.<br />

Materials and methods<br />

A high-yielding rice plant, Oryza sativa cv. Mahanadi<br />

(IR19661-131-1-3 × Savitri), was cultivated in irrigated field<br />

conditions of the Regional <strong>Research</strong> Station, Chiplima, during<br />

120 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. Variations in yield parameters of rice (cv. Mahanadi) panicle at maturity following different types of chemical treatments<br />

during the wet season of 2000. The ± values indicate standard deviation.<br />

Wt. of Wt. of No. of No. of Av wt. of Percentage of<br />

Type of panicle total No. of filled barren spikelets<br />

treatment (g) spikelets spikelets spikelets spikelets (mg) Filled Barren<br />

(g) spikelets spikelets<br />

H 2 O 6.12 ± 0.95 3.76 ± 0.48 190.7 ± 31.7 151.7 ± 34.1 40.0 ± 8.2 19.70 ± 0.80 79.5 ± 5.3 21.0 ± 2.4<br />

Uniconazole 6.85 ± 0.03 3.94 ± 0.15 201.0 ± 1.4 167.5 ± 6.4 33.5 ± 7.7 19.62 ± 0.85 83.3 ± 3.3 16.7 ± 2.8<br />

Paclobutrazol 7.14 ± 0.79 4.10 ± 0.67 202.7 ± 4.6 176.7 ± 14.5 26.0 ± 1.1 20.24 ± 2.88 87.3 ± 5.0 12.8 ± 5.0<br />

CEPA 5.54 ±0 .56 2.78 ± 0.40 204.3 ± 36.5 126.7 ± 13.8 77.7 ± 5.0 13.58 ± 0.46 62.0 ± 4.8 38.0 ± 4.8<br />

the wet season of 2000. The experimental area was divided<br />

into three parts. In each part, uniformly developed plants were<br />

divided into four groups for growth regulator treatments. On<br />

each day, 0.5 mL of the chemicals paclobutrazol (100 µL L –1 )<br />

and uniconazole (0.5 mg L –1 ), 2-CEPA (10 –5 M), and H 2 O in<br />

aqueous solution were injected into the boot (the leaf sheath<br />

enclosure confining the young panicle before emergence) of<br />

the flag leaf. The treatments began 5 d before the day of anthesis<br />

and continued for 5 d.<br />

Plants were harvested from the day of treatment to maturity<br />

at 5–7-d intervals. Six spikelets from the uppermost primary<br />

branch (apical) and eight spikelets from the lowermost<br />

primary branch (basal) were collected from the panicle on the<br />

main shoot of four different plants in each treatment. The apical<br />

spikelets emerged 5–6 d earlier than the basal spikelets. In<br />

each set, the lemma and palea (glumes) were dissected out,<br />

weighed fresh, and used for biochemical analyses. The four<br />

sets of spikelets were used for estimation of pigments, soluble<br />

carbohydrates, lipid peroxidation, and activity of peroxidase<br />

enzyme, respectively. At maturity, grain yield of the panicle<br />

was estimated. Separate samples were taken for measuring ethylene<br />

concentration of the panicle, basal and apical primary<br />

branches, flag leaf, and boot of the flag-leaf sheath. The cut<br />

end of the plant material was dipped in 1 mL of water inside a<br />

test tube. The test tube was sealed and incubated for 2 h in<br />

darkness before 1 mL of head space gas was used for ethylene<br />

estimation in a gas chromatograph (model 6890, Hewlett-<br />

Packard Company, USA, equipped with a flame ionization<br />

detector) (Naik and Mohapatra 2000).<br />

Results<br />

Grain yield and yield components<br />

Uniconazole and paclobutrazol treatments improved panicle<br />

weight, spikelet weight, and number of filled spikelets, and<br />

reduced the number of barren spikelets significantly (Table<br />

1). In contrast, CEPA application had the opposite effect. The<br />

triazolic compounds did not improve the average weight of<br />

spikelets, but CEPA application depressed it significantly.<br />

Ethylene concentration of panicle,<br />

primary branches, flag leaf, boot, and spikelets<br />

Ethylene concentration of the plant organs was low at 5 d before<br />

anthesis; it reached a peak at anthesis and declined t<strong>here</strong>after<br />

(Fig. 1). It was minimum at maturity. The concentration<br />

of ethylene inside the boot of the flag leaf also increased temporally<br />

during the pre-anthesis period. The ethylene concentration<br />

of the apical primary branch was lower than that of the<br />

basal branch of the panicle. The treatment with triazolic compounds<br />

decreased the concentration of ethylene of the boot<br />

and the plant organs significantly, but CEPA increased the concentration.<br />

The treatment with the chemicals was more effective<br />

on the basal branch than on the apical branch.<br />

Pigment concentration of glumes<br />

The concentrations of chlorophylls, carotenoids, soluble sugars,<br />

proteins, and free amino acids of the glumes increased<br />

temporally from 5 d before to 1 wk after anthesis. It declined<br />

t<strong>here</strong>after till maturity in the apical branch (data not included).<br />

In the basal branch, the concentration of these materials increased<br />

for a longer time before declining. During the declining<br />

phase, the glumes of basal spikelets possessed a higher<br />

concentration of the materials than those of the apical spikelets.<br />

The treatment with the triazolic compounds improved the<br />

concentration significantly in the glumes of basal spikelets,<br />

but CEPA application had the opposite effect. The chemical<br />

treatments did not change the concentration of the materials in<br />

the apical spikelets.<br />

Peroxidase activity and peroxidation<br />

of lipids in glumes<br />

The activity of the enzyme peroxidase and the amount of lipid<br />

peroxidation in the glumes of apical spikelets increased from<br />

5 d before to 16 d past anthesis and declined t<strong>here</strong>after till<br />

maturity (data not presented). The activity was higher in the<br />

glumes of the basal spikelets than in the apical spikelets. Peroxidase<br />

activity increased up to 23 d past anthesis in the basal<br />

spikelets and declined t<strong>here</strong>after. The treatment with triazolic<br />

compounds increased activity of the enzyme, w<strong>here</strong>as CEPA<br />

decreased it significantly. The treatment with chemicals was<br />

not effective on the apical spikelets.<br />

Session 4: Improving rice yield potential 121


Ethylene concentration (nmol g –1 fresh wt. h –1 )<br />

6<br />

(Apical primary branch, 2000)<br />

5<br />

4<br />

H 2 O<br />

UCZ<br />

PBZ<br />

CEPA<br />

6<br />

5<br />

4<br />

(Basal primary branch, 2000)<br />

3<br />

3<br />

2<br />

2<br />

1<br />

1<br />

0<br />

10<br />

8<br />

6<br />

0<br />

12<br />

(Flag leaf, 2000) (Panicle, 2000)<br />

10<br />

8<br />

6<br />

4<br />

4<br />

2<br />

2<br />

0<br />

–5 0 5<br />

0<br />

–5 0 5<br />

Ethylene concentration (nmol mL –1 of air)<br />

5.0<br />

4.5<br />

4.0<br />

H 2 O<br />

UCZ<br />

PBZ<br />

CEPA<br />

(Boot, 2000)<br />

3.5<br />

3.0<br />

2.5<br />

2.0<br />

1.5<br />

1.0<br />

0.5<br />

0<br />

–5 –4 –3 –2 –1<br />

Days from anthesis<br />

Fig. 1. The effect of uniconazole, paclobutrazol, and 2-chloroethylphosphonic acid on the ethylene<br />

concentration of apical and basal primary branches, panicle, flag leaf, and boot of the flag<br />

leaf of rice at anthesis during the wet season of 2000. Anthesis date is recorded when the apical<br />

spikelets reach that stage. This time scale is used for all organs except the basal primary branch.<br />

122 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Discussion<br />

A comparison of the concentration of proteins, photosynthetic<br />

pigments, peroxidase activity, and lipid peroxidation of glumes<br />

of apical and basal spikelets quantified the magnitude of difference<br />

existing between the senescence patterns of the two<br />

contrasting spikelets. The juvenile phase of development was<br />

slower and the senescence phase was faster in the basal spikelets<br />

than in the apical spikelets. The concentration of soluble<br />

carbohydrates and amino acids of the glumes exhibited a similar<br />

temporal fluctuation. This indicated the close correlation<br />

between assimilate concentration and developmental stages of<br />

the organs. <strong>Rice</strong> seed is a caryopsis. The real function of the<br />

seed coat is carried out by the lemma and palea, and their development<br />

is related to that of the seed. The lemma and palea<br />

unite to enclose hull space and this space determines grain<br />

size (Yoshida 1981). Hence, a close association between endosperm<br />

filling and the senescence pattern of the glumes is<br />

expected. In our study, the glumes of the inferior spikelets remained<br />

green for a longer time than those of the superior spikelets,<br />

but endosperm filling did not improve. T<strong>here</strong>fore, the senescence<br />

pattern of the glumes may not be necessarily coincidental<br />

to or causative of grain filling.<br />

The estimation of ethylene from different parts of the<br />

panicle and flag leaf indicated its involvement in the regulation<br />

of senescence and grain maturation. Ethylene concentration<br />

increased and decreased in the pre- and postanthesis stages,<br />

respectively. This is similar to the observation from another<br />

high-yielding rice cv., Lalat (Naik and Mohapatra 2000). Ethylene<br />

produced by the dominant spikelets of the panicle and<br />

flag leaf at anthesis accumulated inside the boot of the flag<br />

leaf sheath and increased the concentration temporarily. The<br />

apical spikelets emerged from the boot at anthesis, but the basal<br />

spikelets remained inside it for about 5–6 d more. Exposure to<br />

ethylene inside the boot could have retarded the development<br />

of basal spikelets. In contrast, the apical spikelets developed<br />

faster and enjoyed freedom from the constraints of the flagleaf<br />

enclosure. When the basal spikelets reached anthesis, the<br />

inferior spikelets produced more ethylene (Fig. 1) and this ethylene<br />

might be responsible for the faster degradation of lipids<br />

of the glumes during the senescence phase. Ethylene is easily<br />

mobile within flower organs and works as a signal for interorgan<br />

communication during senescence; in maize, ethylene<br />

released by the dominant spikelets at pollination retards the<br />

growth of inferior spikelets (Cheng and Lur 1996). Our study<br />

and our previous work (Mohapatra et al 2000, Naik and<br />

Mohapatra 2000) lead to the conclusion that ethylene produced<br />

by the apical spikelets and flag leaf at anthesis accumulated in<br />

the boot. It enhanced the senescence of the basal spikelets of<br />

the panicle and resulted in poor filling (the r value between<br />

boot ethylene concentration and % of filled spikelets was<br />

–0.77).<br />

In our study, grain filling of the basal spikelets occurred<br />

during the senescence phase of the flag leaf and panicle. This<br />

apparent coincidence suggests the possibility of a source limitation<br />

for assimilates. However, deficiency of assimilates restricting<br />

grain filling of irrigated rice was ruled out (Mohapatra<br />

et al 1993, Yang et al 2002). Instead, it was opined that poor<br />

filling is affected by the low cytokinin level of the inferior<br />

endosperm (Yang et al 2002). A compromise between our study<br />

and that of Yang et al (2002) suggests an assumption that ethylene<br />

may be triggering a deficiency of cytokinin in the inferior<br />

endosperm and causing poor cell division and grain filling.<br />

Simultaneously, ethylene is also responsible for the promotion<br />

of senescence of the source organs. But poor filling<br />

cannot be consequential to a shortage of assimilates through<br />

depletion of source activity. Murchie et al (2002) found no<br />

consistent relationship between the rate of grain filling and<br />

photosynthesis of rice leaves. The gradient of metabolic potential<br />

between superior and inferior spikelets is established at<br />

the early stage of seed development (Qu-Lee and Setter 1985).<br />

High metabolic potential precludes adverse ethylene action on<br />

apical spikelets, but not on basal spikelets. At this stage, competition<br />

for limiting assimilates is less likely to occur because<br />

of the low demand for sink activity (Mohapatra et al 1993,<br />

Yang et al 2002).<br />

References<br />

Cheng CY, Lur HS. 1996. Ethylene may be involved in abortion of<br />

maize caryopses. Physiol. Plant. 98:245-252.<br />

Fletcher RA, Gilley A, Sankhla N, Davis TD. 2000. Triazoles as<br />

plant growth regulators and stress protectants. Hort. Rev.<br />

24:55-138.<br />

Lin CC, Hsu YT, Kao CH. 2002. Ammonium ion, ethylene and NaClinduced<br />

senescence of detached rice leaves. Plant Growth<br />

Regul. 37:85-92.<br />

Mohapatra PK, Naik PK, Patel R. 2000. Ethylene inhibitors improve<br />

dry partitioning and development of late flowering spikelets<br />

on rice panicles. Austr. J. Plant Physiol. 22:311-323.<br />

Mohapatra PK, Patel R, Sahu SK. 1993. Time of flowering affects<br />

grain quality and spikelet partitioning within the rice panicle.<br />

Austr. J. Plant Physiol. 20:231-241.<br />

Murchie EH, Yang J, Hubbart S, Horton P, Peng S. 2002. Are t<strong>here</strong><br />

associations between grain-filling rate and photosynthesis in<br />

the flag leaves of field-grown rice J. Exp. Bot. 53:2217-2224.<br />

Naik PK, Mohapatra PK. 2000. Ethylene inhibitors enhanced sucrose<br />

synthase activity and promoted grain filling of basal<br />

rice kernels. Austr. J. Plant Physiol. 27:997-1008.<br />

Qu-Lee T-M, Setter TL. 1985. Enzyme activities of starch and sucrose<br />

pathways and growth of apical and basal maize kernels.<br />

Plant Physiol. 79:848-851.<br />

Yang J, Zhang J, Huang Z, Wang Z, Zhu Q, Liu L. 2002. Correlation<br />

of cytokinin levels in the endosperm and roots with cell number<br />

and cell division activity during endosperm development<br />

in rice. Ann. Bot. 90:369-377.<br />

Yoshida S. 1981. Fundamentals of rice crop science. Manila (Philippines):<br />

<strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>.<br />

Session 4: Improving rice yield potential 123


Notes<br />

Authors’ address: School of Life Science, Sambalpur University, Jyoti<br />

Vihar, Sambalpur 768019, India, e-mail:<br />

pravat48@hotmail.com.<br />

Acknowledgments: This work was supported by a research grant to<br />

P.K. Mohapatra by the Indian Council of Agricultural <strong>Research</strong>,<br />

New Delhi.<br />

Impact of increased source capacity on rice yield:<br />

a case study with CO 2<br />

enrichment<br />

Toshihiro Hasegawa, Kazuhiko Kobayashi, Mark Lieffering, Han Yong Kim, Hidemitsu Sakai, Hiroyuki Shimono,<br />

Yasuhiro Yamakawa, Mayumi Yoshimoto, and Masumi Okada<br />

Grain yields of rice (Oryza sativa L.) as well as other major<br />

cereals have increased markedly in the last century. Genetic<br />

improvements have contributed largely to these increases. Yield<br />

potential can be increased by increasing biomass production<br />

and/or increasing allocation to harvested organs. Genetic improvements<br />

in the yield potential of major cereals have largely<br />

been through the latter. Photosynthesis plays a central role in<br />

biomass production and recent varieties tend to have longer<br />

photosynthetic duration than older varieties, but only limited<br />

evidence exists that the maximum photosynthetic capacity has<br />

been improved. Even w<strong>here</strong> improved photosynthetic capacity<br />

was observed, no direct evidence of biomass increase was<br />

shown (review: Evans 1993). Efforts are under way to improve<br />

the genetic potential of photosynthesis, but the question “Does<br />

improving photosynthesis benefit crop production” needs to<br />

be answered experimentally.<br />

Photosynthetic capacity under current atmospheric CO 2<br />

concentrations ([CO 2 ]) is generally limited by the carboxylation<br />

process in the Calvin cycle. Increases in [CO 2 ] accelerate<br />

carboxylation velocity by increasing [CO 2 ] supply from stomata<br />

and reducing photorespiration (review: Long et al 2004).<br />

In general, CO 2 enrichment studies aim to identify the magnitude<br />

of changes in crops with increased [CO 2 ], but these results<br />

can also be used to infer the impact of increased photosynthesis<br />

on crop yield.<br />

Among various experimental facilities that have been<br />

used in elevated CO 2 studies, free-air CO 2 enrichment (FACE)<br />

systems, which do not have enclosures and t<strong>here</strong>fore a minimum<br />

of artifacts, are usually regarded as providing the best<br />

estimates of yield responses to elevated [CO 2 ] in the open field.<br />

Across all species, fewer FACE than chamber experiments have<br />

been conducted, though the rice FACE system has been running<br />

at two sites (Japan and China) for more than three years.<br />

Many data have been accumulated, leading to reviews of the<br />

yield responses of a range of plant species to FACE (Kimball<br />

et al 2002, Long et al 2004). To expand on these reviews, this<br />

paper summarizes the FACE effects on photosynthesis, biomass,<br />

and yield of rice in order to examine the effect of increased<br />

source capacity on grain yield. The rice results are<br />

compared with those of other C 3 species responses reviewed<br />

by Kimball et al (2002) and Long et al (2004).<br />

Data<br />

Most of the rice responses to elevated [CO 2 ] presented in this<br />

paper are from the FACE experiment conducted in Shizukuishi,<br />

Iwate, Japan (39 o 38′N, 140 o 57′E) from 1998 to 2000. The<br />

design of the FACE system was reported by Okada et al (2001)<br />

and growth conditions were given by Kim et al (2003a). Briefly,<br />

rice was grown in farmers’ paddies equipped with 12-m-diameter<br />

FACE systems. Pure CO 2 gas was released from peripheral<br />

emission tubes 0.5 m above the canopy, the sides of the<br />

emission depending on the wind direction. The target [CO 2 ] at<br />

the center of the FACE plots was 200 µmol mol –1 above the<br />

ambient [CO 2 ]. Each plot had some subplot treatments such as<br />

N rates and varieties, but <strong>here</strong> we present only the results from<br />

cultivar Akitakomachi under standard N conditions (8–9 g<br />

m –2 of N).<br />

For this paper, growth and yield data in Shizukuishi were<br />

from Kim et al (2003a,b). Leaf photosynthesis data were from<br />

Seneweera et al (2002) and Anten et al (2003). In the former<br />

study, [CO 2 ] and [H 2 O] exchange rates were measured on the<br />

top fully expanded leaves on two occasions during the season,<br />

w<strong>here</strong>as in the latter study light-saturated CO 2 assimilation<br />

(Asat) and maximum apparent quantum yield of CO 2 uptake<br />

(QY) were measured at different positions of the canopy at<br />

around flowering. By also measuring canopy light attenuation<br />

and leaf area distribution, Anten et al (2003) estimated canopy<br />

photosynthesis by integrating the photosynthesis of sunlit and<br />

shaded leaves.<br />

Other rice data presented in this paper come from the<br />

rice-wheat FACE experiment conducted in Wuxi (31 o 37′N,<br />

120 o 28′E), Jiangsu, China, in 2001, 2002, and 2003. A FACE<br />

system similar to the one in Shizukuishi was used. Final biomass<br />

and grain yield data of cultivar Wuxiangjing 14 (Huang<br />

et al 2004) are presented in this study.<br />

To compare rice growth and yield responses to FACE<br />

with those of other C 3 species, we present data from a review<br />

by Kimball et al (2002) and a meta-analysis conducted by Long<br />

et al (2004) as a reference; the latter reviewed results from<br />

large-scale (>8 m) FACE experiments only.<br />

124 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Results and discussion<br />

Biomass production is a result of canopy light interception<br />

and conversion of the intercepted light to biomass; leaf area<br />

influences the former and photosynthesis the latter. The effect<br />

of FACE on peak leaf area was not significant for all years;<br />

this agreed with the average C 3 responses in the meta-analysis<br />

of Long et al (2004). Although this implies that carbon supply<br />

is not limiting to leaf area growth, it also indicates that the<br />

FACE effects on biomass should appear largely through increased<br />

source capacity rather than increased light capture, so<br />

the FACE studies can provide us with evidence as to how much<br />

increased grain yield depends on increased photosynthetic rates.<br />

Light-saturated photosynthesis (Asat) is generally limited<br />

by carboxylation or by ribulose 1,5-bisphosphate regeneration.<br />

These processes are well represented by two parameters<br />

obtained from leaf gas exchange measurements: maximum<br />

carboxylation rate (Vc,max) and maximum rate of electron<br />

transport (Jmax). For rice, the FACE treatment decreased<br />

both Vc,max and Jmax, with the larger reduction observed in<br />

the former; this was commonly observed in other C 3 species<br />

(Fig. 1). In rice, the FACE effects were larger in the flag leaf<br />

than in the 8th leaf at the active tillering stage. Nitrogen content<br />

per unit leaf area (Narea) was also reduced with the FACE<br />

treatment by 6% in rice, and a similar reduction was reported<br />

in the meta-analysis (4%).<br />

The data reported by Seneweera et al (2002) in the rice<br />

FACE experiment indicated that both Vc,max and Jmax are<br />

highly sensitive to the decrease in Narea; these relationships<br />

largely explain the variation in both parameters with elevated<br />

[CO 2 ] and leaf age. According to the relationships among<br />

Vc,max, Jmax, and Narea, enhancement of Asat by elevated<br />

[CO 2 ] is greater w<strong>here</strong> Narea is large, and becomes progressively<br />

smaller as Narea declines. In fact, Asat measured on the<br />

8th leaf at the active tillering stage showed a large enhancement<br />

of about 40% (Seneweera et al 2002), and measurements<br />

t<strong>here</strong>after by Anten et al (2003) and those on the flag leaf by<br />

Seneweera et al (2002) resulted in lower rates of enhancement,<br />

about 20% and 4%, respectively. These changes related well<br />

to the changes in Narea.<br />

Elevated CO 2 also has a positive influence on the maximum<br />

apparent quantum yield of CO 2 uptake (QY, Fig. 1). In<br />

rice, Anten et al (2003) reported about a 20% increase in QY<br />

at around the heading stage with FACE; this was slightly larger<br />

than the enhancement in the meta-analysis of C 3 species (Long<br />

et al 2004). Consequently, both Asat and QY contribute to the<br />

carbon gain enhancement of the canopy.<br />

The enhancement of canopy photosynthesis (Acanopy)<br />

estimated from the leaf photosynthetic parameters was 24%<br />

for rice (Anten et al 2003), which was slightly lower but comparable<br />

to the daily integral of leaf CO 2 uptake (A’) in the<br />

meta-analysis. The crop growth rate (CGR) around flowering,<br />

however, was enhanced by elevated [CO 2 ] to a lesser extent of<br />

4–15%. Canopy gas exchange was not measured in the FACE<br />

experiments, but, according to Sakai et al (2001), who measured<br />

canopy gas exchange in controlled chambers, CO 2 enrichment<br />

by 300 µmol mol –1 increased net canopy CO 2 uptake<br />

and the CGR around flowering by similar ratios (11% and 9%,<br />

respectively). The relationship between leaf- and canopy-level<br />

gas exchange and crop growth needs to be better understood<br />

to account for why leaf photosynthetic enhancement did not<br />

translate well into increased biomass production.<br />

The enhancement of final biomass by FACE ranged from<br />

9% to 15% in Shizukuishi. This was similar to that obtained in<br />

Wuxi, China (7–14%), despite the large difference in climatic<br />

conditions. However, the enhancement ratios of rice biomass<br />

are lower than the average response of C 3 species.<br />

Seed yield enhancement was similar to but slightly larger<br />

than biomass enhancement: 13–16% in Shizukuishi and 8–18%<br />

in Wuxi. These values lie at the lower edge of the confidence<br />

intervals of the average yield responses of C 3 species (mean:<br />

24%). A large variation in the grain yield response to elevated<br />

[CO 2 ] exists among C 3 crops. Wheat yield responses to FACE<br />

under ample N and water were similar to those of rice, but<br />

substantially larger harvestable yield enhancements were observed<br />

in potato and cotton (Kimball et al 2002). It is worth<br />

noting that no enhancement of the aboveground biomass was<br />

recorded for potato. This may suggest that many important<br />

traits can regulate the effect of increased source capacity on<br />

yield.<br />

Conclusions<br />

In rice, a 20–40% increase in Asat occurred with FACE before<br />

anthesis. T<strong>here</strong>after, photosynthetic enhancement was rather<br />

limited because both Jmax and Vc,max decreased with decreasing<br />

leaf N content: this was low with elevated [CO 2 ] and decreased<br />

as the crop aged. The rice FACE experiments in Japan<br />

and China revealed that grain yield enhancement by elevated<br />

CO 2 under standard N supplies ranged from 8% to 18% (mean:<br />

13.5%), with no marked differences between locations. The<br />

magnitude of the yield enhancement was smaller than that of<br />

other C 3 species (the meta-analysis mean: 24%). Plant traits<br />

that moderate the effects of elevated [CO 2 ] on grain yield need<br />

to be identified under season-long examinations to fully take<br />

advantage of increased source capacity for yield improvement.<br />

References<br />

Anten NPR, Hirose T, Onoda Y, Kinugasa T, Kim HY, Okada M,<br />

Kobayashi K. 2003. Elevated CO 2 and nitrogen availability<br />

have interactive effects on canopy carbon gain in rice. New<br />

Phytol. 161:459-471.<br />

Evans LT. 1993. Crop evolution, adaptation and yield. Cambridge<br />

(UK): Cambridge University Press. 500 p.<br />

Huang JY, Yang HJ, Yang LX, Liu HJ, Dong GC, Zhu JG, Wang YL.<br />

2004. Effects of free-air CO 2 enrichment (FACE) on yield<br />

formation of rice (Oryza sativa L.) and its causes. Sci. Agric.<br />

Sin. (In press.)<br />

Kim HY, Lieffering M, Kobayashi K, Okada M, Mitchell MW,<br />

Gumpertz M. 2003a. Effects of free-air CO 2 enrichment and<br />

nitrogen supply on the yield of temperate paddy rice crops.<br />

Field Crops Res. 83:261-270.<br />

Session 4: Improving rice yield potential 125


SF<br />

S8<br />

VC,max<br />

Meta (C 3 species)<br />

<strong>Rice</strong><br />

Other C 3 crops<br />

SF<br />

S8<br />

Jmax<br />

SF<br />

S8<br />

V,max/Jmax<br />

A<br />

Narea<br />

Asat<br />

SF A S8<br />

QY<br />

A’<br />

Acanopy<br />

CGR<br />

Final biomass<br />

<strong>Rice</strong> (Shizukuishi)<br />

<strong>Rice</strong> (Wuxi)<br />

Agricultural yield<br />

<strong>Rice</strong> (Shizukuishi)<br />

<strong>Rice</strong> (Wuxi)<br />

Wheat (Maricopa)<br />

Potato (Rapolano)<br />

Cotton (Maricopa)<br />

–40 –20 0 20 40 60<br />

% increase with elevated [CO 2 ]<br />

Fig. 1. The percent change under elevated [CO 2 ] of (1) maximum carboxylation<br />

rate (Vc,max), (2) maximum rate of electron transport (Jmax),<br />

(3) the ratio of Vc,max:Jmax, (4) N content per unit leaf area (Narea), (5)<br />

light-saturated CO 2 assimilation (Asat), (6) maximum apparent quantum<br />

yield of CO 2 uptake (QY), (7) daily integral of leaf CO 2 uptake (A’), (8)<br />

estimated daily net canopy CO 2 assimilation at the heading stage<br />

(Acanopy), (9) crop growth rate (CGR) around the heading stage, (10)<br />

final biomass, and (11) seed yield. Meta-analysis results of large-scale<br />

free-air CO 2 enrichment experiments for C 3 species along with 95% confidence<br />

intervals (Long et al 2004) are presented as a reference. <strong>Rice</strong><br />

leaf photosynthetic properties are from Seneweera et al (2002) and Anten<br />

et al (2003); S8 and SF beside symbols stand for the 8th-leaf and flagleaf<br />

measurements, respectively, of Seneweera et al (2002), and A for<br />

Anten et al’s measurements. <strong>Rice</strong> growth and yield data in Shizukuishi,<br />

Japan, are from Kim et al (2003a,b) and in Wuxi, China, from Huang et al<br />

(2004). Agricultural yield data of other C 3 crops (seed for wheat, tuber<br />

for potato, and boll for cotton) were from Kimball et al’s (2002) review;<br />

only results from crops grown under ample water and nitrogen conditions<br />

are presented.<br />

126 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Kim HY, Lieffering M, Kobayashi K, Okada M, Miura S. 2003b.<br />

Seasonal changes in the effects of elevated CO 2 on rice at<br />

three levels of nitrogen supply: a free-air CO 2 enrichment<br />

(FACE) experiment. Global Change Biol. 9:826-837.<br />

Kimball BA, Kobayashi K, Bindi M. 2002. Responses of agricultural<br />

crops to free-air CO 2 enrichment. Adv. Agron. 77:293-<br />

368.<br />

Long SP, Ainsworth EA, Rogers A, Ort DR. 2004. Rising atmospheric<br />

carbon dioxide: plants FACE the future. Annu. Rev. Plant Biol.<br />

55:557-594.<br />

Okada M, Lieffering M, Nakamura H, Yoshimoto M, Kim HY,<br />

Kobayashi K. 2001. Free-air CO 2 enrichment (FACE) using<br />

pure CO 2 injection: system description. New Phytol. 150:251-<br />

260.<br />

Sakai H, Yagi K, Kobayashi K, Kawashima S. 2001. <strong>Rice</strong> carbon<br />

balance under elevated CO 2 . New Phytol. 150:241-249.<br />

Seneweera SP, Conroy JP, Ishimaru K, Ghannoum O, Okada M,<br />

Lieffering M, Kim HY, Kobayashi K. 2002. Changes in sourcesink<br />

relations during development influence photosynthetic<br />

acclimation of rice to free-air CO 2 enrichment (FACE). Funct.<br />

Plant Biol. 29:945-953.<br />

Notes<br />

Possibilities for and constraints to<br />

improving canopy photosynthesis<br />

J.E. Sheehy, A.V. Elmido, P. Pablico, M.J.A. Dionora, and A.B. Ferrer<br />

Authors’ addresses: Toshihiro Hasegawa, Hidemitsu Sakai, and<br />

Mayumi Yoshimoto, National <strong>Institute</strong> for Agro-Environmental<br />

Sciences, Tsukuba, Ibaraki 305-8604, Japan, e-mail:<br />

thase@niaes.affrc.go.jp; Kazuhiko Kobayashi, University of<br />

Tokyo, Japan; Mark Lieffering, Ag<strong>Research</strong> Grassland, New<br />

Zealand; Han Yong Kim, Chonnam University, South Korea;<br />

Hiroyuki Shimono, Yasuhiro Yamakawa, and Masumi Okada,<br />

National Agricultural <strong>Research</strong> Center for Tohoku Region,<br />

Japan.<br />

We have a unique opportunity to solve all of the rice production<br />

problems of Asia by redesigning one plant mechanism:<br />

photosynthesis. A lack of scientific understanding of the yieldshaping<br />

mechanisms, combined with a triumph of correlation<br />

over common sense, have led to the commonly held belief<br />

that leaf photosynthesis and yield are unrelated. To counter<br />

that misconception, we argue the link between photosynthesis<br />

and yield and explore what it would take to be a C 4 rice plant.<br />

Recent discoveries of single-cell C 4 photosynthesis could provide<br />

new impetus to convert rice from a C 3 to a C 4 photosynthetic<br />

system without having to incorporate the Kranz anatomy<br />

(Sage 2002).<br />

Solar energy captured in photosynthesis gives plants the<br />

capacity to grow. Two aspects of energy capture set the limits<br />

for crop growth in a given thermal environment. The first is<br />

the quantity of energy captured, and that depends on the available<br />

irradiance and the fraction absorbed by the crop canopy.<br />

The second is the efficiency with which the absorbed energy<br />

is used for the chain of synthetic processes that culminate in<br />

harvestable yield. Modern cultivars with erect leaves absorb<br />

all the available photosynthetically active radiation, leaving<br />

little room for further improvements in energy capture. In highyielding<br />

rice, sink size is unlikely to limit yield; the potential<br />

sink size is almost double that actually realized.<br />

In plants using the C 3 photosynthetic pathway (rice,<br />

wheat, etc.), oxygen competes for the active sites on the key<br />

photosynthetic enzyme, Rubisco, leading to as much as a 30%<br />

loss of captured CO 2 in a process known as photorespiration.<br />

The C 4 syndrome evolved from the C 3 syndrome and C 4 plants<br />

have a photosynthetic system that concentrates CO 2 around<br />

Rubisco, and so nearly saturates the carboxylation reaction<br />

and eliminates photorespiration. Consequently, C 4 plants use<br />

water more effectively. In addition, C 4 crops require less nitrogen<br />

fertilizer because they make better use of nitrogen in<br />

photosynthesis. The maximum rate of leaf photosynthesis for<br />

both C 3 and C 4 plants appears to vary linearly with nitrogen<br />

content per unit leaf area over a wide range of nitrogen concentrations<br />

(Evans and von Caemmerer 2000). Assuming the<br />

data shown by Evans and von Caemmerer (2000) could be<br />

described by linear relationships, then maize had a gradient of<br />

approximately 0.74 µmol CO 2 s –1 mmol –1 N compared with<br />

that for C 3 plants (rice and wheat) of 0.26 µmol CO 2 s –1<br />

mmol –1 N: a threefold difference in leaf photosynthetic nitrogen-use<br />

efficiency (Table 1).<br />

Photosynthesis in C 3 plants should benefit more from<br />

rising concentrations of atmospheric carbon dioxide than the<br />

photosynthesis in C 4 plants. However, work of Baker et al<br />

(1990) showed that canopy photosynthesis in rice did not respond<br />

to increases in atmospheric CO 2 beyond 50 Pa. Average<br />

atmospheric concentration of carbon dioxide increased by approximately<br />

4.5 Pa from 1968 to 1998. However, over that<br />

period, yield for the same cultivar (IR8) grown on the <strong>IRRI</strong><br />

farm at nitrogen inputs of approximately 150 kg N ha –1 fell by<br />

2.6 t ha –1 (Peng et al 1999).<br />

Session 4: Improving rice yield potential 127


Table 1. A comparison of three attributes of maize (C 4 ) and rice (C 3 )<br />

and the advantage of the C 4 over the C 3 system under current CO 2<br />

conditions. WUE (transpiration) is water-use efficiency, RUE (PAR)<br />

is radiation-use efficiency, PNUE is photosynthetic nitrogen-use<br />

effectiveness. Source: (a) from various sources, (b) Kiniry et al<br />

(1989), and (c) Evans and von Caemerrer (2000).<br />

WUE RUE (PAR) PNUE<br />

(g DW kg –1 H 2 O) (g DW MJ –1 ) (µm CO 2 s –1 mmol –1 N)<br />

Zea mays (C 4 ) 2.9 a 3.3 b 0.74 c<br />

Oryza sativa (C 3 ) 1.6 a 2.2 b 0.26 c<br />

C 4 /C 3 advantage 1.8 1.5 2.8<br />

Dry weight (t ha –1 )<br />

12<br />

10<br />

8<br />

6<br />

4<br />

2<br />

The link between yield and photosynthesis<br />

T<strong>here</strong> are two nearly equal phases of growth in rice (Fig. 1),<br />

with about half of the first phase of vegetative growth preceding<br />

the second phase of reproductive growth (largely the<br />

panicle). The growth of the panicle is largely heterotrophic<br />

and in high-yielding rice has a maximum growth rate about<br />

the same as that achieved by the autotrophic vegetative component.<br />

How could the growth rates of both components be<br />

increased by 50% T<strong>here</strong> is a linear relationship between accumulated<br />

intercepted photosynthetically active solar radiation<br />

and accumulated biomass; the slope of that linear relationship<br />

is known as the radiation-use efficiency (ε). The relationship<br />

between the growth rate of shoots (dW s /dt) and ε is<br />

dW s /dt = ε I int (1)<br />

w<strong>here</strong> I int is the total amount of photosynthetically active radiation<br />

(PAR) intercepted by the crop for the same day. To<br />

increase growth rates by 50%, the value of ε would have to<br />

increase by 50%, from the average value of ε for rice of 2.2 g<br />

dry weight (DW) MJ –1 PAR to 3.3 g DW MJ –1 PAR, the average<br />

value for maize (Table 1, Kiniry et al 1989). The link between<br />

ε and photosynthesis on any given day can be written<br />

as<br />

ε = (1 - β) [(P g (t) – R(t) – D(t))] /I int (t) (2)<br />

w<strong>here</strong> β is the root weight ratio, P g is the rate of canopy gross<br />

photosynthesis, R is the rate of shoot and root respiration, D is<br />

the loss of dry matter through detachment, and t is time in<br />

days. On a given day, to increase ε by 50%, photosynthesis<br />

would have to increase by a little more than 50%, that is, to<br />

values comparable with those of C 4 plants.<br />

Upper limits to canopy photosynthesis<br />

The simple model of Monteith (1965) shows that the maximum<br />

photosynthetic leaf area index of an erect canopy is approximately<br />

6.6. The sunlit leaf area index (L o ) reached a maximum<br />

of 3.3 and photosynthetically active shaded leaf area index<br />

(L s ) reached its maximum at approximately 3.0. Sinclair<br />

and Sheehy (1999) proposed that the third class of leaves in<br />

0<br />

0 20 40 60 80 100 120<br />

DAT<br />

Fig. 1. The two phases of rice growth for IR72 growing in the dry<br />

season of 2001 at <strong>IRRI</strong> with nonlimiting fertilizer applications. Open<br />

squares denote vegetative parts and filled squares denote panicles.<br />

DAT = days after transplanting.<br />

the canopy (L n ) were those that were close to the light compensation<br />

point and largely useful for the N they contributed<br />

to the grain (L n = L – L o – L s ; w<strong>here</strong> L is the total LAI). Sheehy<br />

(2000) went on to show that the loss through senescence of L s<br />

and L n would reduce canopy photosynthesis by about 22–27%.<br />

The maximum rate of canopy photosynthesis (P gmax ) has an<br />

asymptotic value given by<br />

P gmax = L o A mo + L s A ms as I → ∞ (3)<br />

w<strong>here</strong> I is the incident PAR, A mo is the maximum rate of sunlit<br />

leaf photosynthesis, and A ms is the maximum rate of shaded<br />

leaf photosynthesis. The maximum quantum yield of the canopy<br />

at full light interception is<br />

dP g /dI = α(1 + τ) as I → 0 (4)<br />

w<strong>here</strong> α is the leaf quantum yield in low irradiance and τ is<br />

leaf transmittance. It can be seen that the limits for canopy<br />

photosynthesis are set by the properties of the individual leaves.<br />

At LAIs greater than approximately 6.0, improvements in<br />

canopy photosynthesis can only result from improvements in<br />

leaf quantum yield and/or leaf photosynthesis.<br />

At daytime temperatures typical of the tropics (>26 °C),<br />

the quantum yield of C 4 plants is greater than that of C 3 plants<br />

(Ehleringer and Björkman 1977) and the optimum temperature<br />

for rice plants is close to 30 °C, w<strong>here</strong>as that for C 4 plants<br />

is closer to 36 °C. Climate change models predict that by 2100<br />

mean planet-wide surface temperatures will rise by 1.4 to 5.8<br />

°C, making C 4 -ness even more desirable for tropical and semitropical<br />

environments.<br />

128 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Redesigning photosynthesis<br />

T<strong>here</strong> are four strategies for producing a C 4 rice plant: (1)<br />

achieve single-cell C 4 photosynthesis by combining the C 4<br />

pathway and the Calvin cycle in one cell, (2) produce a C 3 -C 4<br />

intermediate with reduced photorespiration, (3) produce a C 4<br />

rice with Kranz anatomy and specialization of chloroplast function<br />

in mesophyll and bundle-sheath cells, and (4) produce<br />

more Rubisco, or better Rubisco, or find ways to make Rubisco<br />

work harder.<br />

All of the genes for the C 4 syndrome are already present<br />

in C 3 plants and some plants switch between C 3 and C 4 modes<br />

of photosynthesis. In the sedge Eleocharis vivipara, the submerged<br />

culms are C 3 but the emergent culms are C 4 with the<br />

Kranz anatomy (Ueno et al 1988). Orcuttia has been shown to<br />

have two types of anatomy: the terrestrial leaves are C 4 with<br />

Kranz anatomy but submerged leaves have C 4 biochemistry<br />

without Kranz anatomy (Keeley 1998). Hibberd and Quick<br />

(2002) showed that cells in stems and petioles of a typical C 3<br />

plant, tobacco, displayed C 4 characteristics, opening up the<br />

possibility that a form of C 4 -ness may already exist in some<br />

rice plants.<br />

Recently, another plant has been reported to operate the<br />

C 4 mechanism within single cells (Voznesenskaya et al 2002).<br />

In the chenopod Borszczowia aralocaspica, the elongated<br />

chlorenchymatous cells are closely packed, without intercellular<br />

air spaces, at the inner end w<strong>here</strong> they have abundant,<br />

large chloroplasts. The outer two-thirds of the cells have the<br />

appearance of mesophyll cells, with normal air spaces.<br />

Work in progress<br />

At <strong>IRRI</strong>, we have been screening the wild rice collection for<br />

evidence of C 4 traits. The δ 13 C values range from –31% to<br />

–25% and the interveinal spacing (at the middle of the blade)<br />

ranges from 167 to 313 µm (the value for IR72 is 227 µm).<br />

The number of vascular bundles per unit width was not related<br />

to the overall width of the leaf. Currently, we are counting the<br />

number of chloroplasts in the bundle-sheath cells and measuring<br />

the mesophyll cell size. Work is under way to transfer maize<br />

genes for PEP carboxylase (PEPC) and pyruvate, orthophosphate<br />

dikinase (PPDK), individually and in combination, into<br />

elite <strong>IRRI</strong> indica cultivars. Table 1 shows the advantage of<br />

maize over rice in water-use efficiency, radiation-use efficiency,<br />

and photosynthetic nitrogen-use efficiency. It is hard to imagine<br />

any trait other than C 4 photosynthesis that could increase<br />

the value of rice by US$44 billion annually through increased<br />

yield and reduced water and nitrogen costs.<br />

References<br />

Baker JT, Allen LH Jr, Boote KJ, Jones P, Jones JW. 1990. <strong>Rice</strong><br />

photosynthesis and evapotranspiration in subambient, ambient<br />

and superambient carbon dioxide concentrations. Agron.<br />

J. 82:834-840.<br />

Ehleringer J, Björkman O. 1977. Quantum yields for CO 2 uptake in<br />

C 3 and C 4 plants: dependence on temperature, [CO 2 ], and [O 2 ]<br />

concentration. Plant Physiol. 59:86-90.<br />

Evans JR, von Caemmerer S. 2000. Would C 4 rice produce more<br />

biomass than C 3 rice In: Sheehy JE, Mitchell PL, Hardy B,<br />

editors. Redesigning rice photosynthesis to increase yield.<br />

Proceedings of the Workshop on The Quest to Reduce Hunger:<br />

Redesigning <strong>Rice</strong> Photosynthesis, 30 Nov.-3 Dec. 1999,<br />

Los Baños, Philippines. Makati City (Philippines): <strong>International</strong><br />

<strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong> and Amsterdam (The Netherlands):<br />

Elsevier Science B.V. p 53-71.<br />

Hibberd JM, Quick WP. 2002. Characteristics of C 4 photosynthesis<br />

in stems and petioles of C 3 flowering plants. Nature 415:451-<br />

454.<br />

Keeley JE. 1998. C 4 photosynthetic modifications in the evolutionary<br />

transition from land to water in aquatic grasses. Oecologia<br />

116:85-97.<br />

Kiniry JR, Jones CA, O’Toole JC, Blanchet R, Cabelguenne M,<br />

Spanel DA. 1989. Radiation use efficiency in biomass accumulation<br />

prior to grain-filling for five crop species. Field Crops<br />

Res. 20:51-64.<br />

Monteith JL. 1965. Light distribution and photosynthesis in field<br />

crops. Ann. Bot. 29:17-37.<br />

Peng S, Cassman KG, Virmani SS, Sheehy JE, Khush GS. 1999.<br />

Yield potential trends of tropical rice since the release of IR8<br />

and the challenge of increasing rice yield potential. Crop Sci.<br />

39:1552-1559.<br />

Sage RF. 2002. C 4 photosynthesis in terrestrial plants does not require<br />

Kranz anatomy. Trends Plant Sci. 7:283-285.<br />

Sheehy JE. 2000. Limits to yield for C 3 and C 4 rice: an agronomist’s<br />

view. In: Sheehy JE, Mitchell PL, Hardy B, editors. Redesigning<br />

rice photosynthesis to increase yield. Proceedings of<br />

the Workshop on The Quest to Reduce Hunger: Redesigning<br />

<strong>Rice</strong> Photosynthesis, 30 Nov.-3 Dec. 1999, Los Baños, Philippines.<br />

Makati City (Philippines): <strong>International</strong> <strong>Rice</strong> <strong>Research</strong><br />

<strong>Institute</strong> and Amsterdam (The Netherlands): Elsevier Science<br />

B.V. p 39-52.<br />

Sinclair TR, Sheehy JE. 1999. Erect leaves and photosynthesis in<br />

rice. Science 283:1456-1457.<br />

Ueno O, Samejima M, Muto S, Miyachi S. 1988. Photosynthetic<br />

characteristics of an amphibious plant, Eleocharis vivipara:<br />

expression of C 4 and C 3 modes in contrasting environments.<br />

Proc. Natl. Acad. Sci. USA 85:6733-6737.<br />

Voznesenskaya EV, Franceschi VR, Kiirats O, Artyusheva EG, Freitag<br />

H, Edwards GE. 2002. Proof of C 4 photosynthesis without<br />

Kranz anatomy in Binertia cycloptera (Chenopodiaceae). Plant<br />

J. 31:649-662.<br />

Notes<br />

Authors’ address: Crop, Soil, and Water Sciences Division, <strong>International</strong><br />

<strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong> (<strong>IRRI</strong>), DAPO Box 7777, Metro<br />

Manila, Philippines, e-mail: j.sheehy@cgiar.org.<br />

Session 4: Improving rice yield potential 129


Progress in breeding the new plant type<br />

for yield improvement: a physiological view<br />

Shaobing Peng, Rebecca C. Laza, Romeo M. Visperas, Gurdev S. Khush, and Parminder Virk<br />

Increasing yield is still the most important objective of rice<br />

breeding programs in developing countries because of the<br />

growing demand for food resulting from population growth<br />

and a reduction in area devoted to rice production. The <strong>International</strong><br />

<strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong> (<strong>IRRI</strong>) began developing the<br />

new plant type (NPT) rice through ideotype breeding approaches<br />

in 1989 (Khush 1995). The goal was to develop an<br />

NPT with a yield potential 20–25% higher than that of existing<br />

semidwarf rice varieties under a tropical environment during<br />

the dry season. The NPT was designed based on the results<br />

of simulation modeling and the new traits were mostly morphological<br />

since these are easier to select than physiological<br />

traits in breeding programs. The proposed NPT has a low<br />

tillering capacity (3 to 4 tillers when direct-seeded), few unproductive<br />

tillers, 200 to 250 grains per panicle, a plant height<br />

of 90 to 100 cm, thick and sturdy stems, leaves that are thick,<br />

dark green, and erect, a vigorous root system, 100 to 130 days’<br />

growth duration, and increased harvest index (Peng et al 1994).<br />

In 1989, about 2,000 entries from the <strong>IRRI</strong> germplasm<br />

bank were grown to identify donors for the desired traits (Khush<br />

1995). Donors for the low-tillering trait, large panicles, thick<br />

stems, a vigorous root system, and short stature were identified<br />

in the “bulu” or javanica germplasm mainly from Indonesia.<br />

This germplasm is now referred to as the tropical japonica<br />

(Khush 1995). Hybridization began in the dry season of 1990.<br />

The first-generation NPT lines based on tropical japonicas were<br />

developed in less than 5 years. They were grown in a replicated<br />

observational trial for the first time in late 1993. As intended,<br />

the NPT lines had large panicles, few unproductive<br />

tillers, and lodging resistance. However, they did not yield well<br />

because of limited biomass production and poor grain filling<br />

(Peng and Khush 2003). Low biomass production was caused<br />

by an excessive reduction in tillering capacity and low photosynthetic<br />

rate. Poor grain filling was associated with panicle<br />

morphology and source limitation. The poor grain filling of<br />

NPT lines was probably caused by the lack of apical dominance<br />

within a panicle (Yamagishi et al 1996), the compact<br />

arrangement of spikelets on the panicle (Khush and Peng 1996),<br />

a limited number of large vascular bundles for assimilate transport<br />

(S. Akita, personal communication), and source limitation<br />

because of early leaf senescence (Ladha et al 1998). The<br />

first-generation NPT lines were also susceptible to diseases<br />

and insects and had poor grain quality. T<strong>here</strong>fore, they could<br />

not be released for planting in farmers’ fields. However, they<br />

are valuable genetic materials used in rice breeding programs<br />

worldwide.<br />

Breeding of the second-generation new plant type<br />

In 1995, development of second-generation NPT lines began<br />

by crossing first-generation tropical japonica NPT lines with<br />

elite indica parents. Multiple site-year comparisons of firstgeneration<br />

NPT lines with the highest-yielding indica varieties<br />

have shown that the original NPT design did not have sufficient<br />

tillering capacity. An increase in tillering capacity is<br />

needed to increase biomass production and to improve compensation<br />

when tillers are lost because of insect damage or<br />

other causes during the vegetative stage. A slightly smaller<br />

panicle size without a change in panicle length also appeared<br />

to be advantageous to reduce the compact arrangement of spikelets.<br />

Genes from indica parents have effectively reduced panicle<br />

size and increased tillering capacity in the second-generation<br />

NPT lines. Indica germplasm also helped improve other NPT<br />

attributes such as grain quality and disease and insect resistance.<br />

Some second-generation NPT lines (F 5 generation) with<br />

the above refinements were then selected and were planted in<br />

a replicated observational trial for the first time in the 1998<br />

wet season. These second-generation NPT lines have been<br />

tested in breeders’ replicated yield trials since the 2001 dry<br />

season and in replicated agronomic trials since the 2002 dry<br />

season. However, only data from the replicated agronomic trials<br />

in the dry seasons of 2003 and 2004 will be presented in<br />

this paper.<br />

Performance of the second-generation new plant type<br />

Field experiments were conducted under flooded irrigation at<br />

the <strong>IRRI</strong> farm in the dry season of 2003 and 2004. Five second-generation<br />

NPT lines and five indica inbred check varieties<br />

were grown. Seedlings were transplanted at a hill spacing<br />

of 20 × 20 cm. The plants received a basal fertilizer supply of<br />

30 kg P ha –1 , 40 kg K ha –1 , and 5 kg Zn ha –1 incorporated 1 d<br />

before transplanting. Total N fertilizer applied was 200 kg<br />

ha –1 in four splits: basal (60 kg ha –1 ), midtillering (40 kg ha –1 ),<br />

panicle initiation (60 kg ha –1 ), and heading (40 kg ha –1 ). Standard<br />

cultural management practices were followed. To avoid<br />

yield loss, pests were intensively controlled using recommended<br />

pesticides.<br />

In the 2003 dry season, PSBRc52 produced the highest<br />

yield among indica inbred check varieties and IR72967-12-2-<br />

3 was the top yielder among the second-generation NPT lines<br />

(Table 1). IR72967-12-2-3 produced 10.16 t ha –1 , which was<br />

significantly higher than the yield of PSBRc52. The higher<br />

yield was associated with the higher aboveground total biomass<br />

production and greater grain weight in IR72967-12-2-3.<br />

130 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. Crop growth duration, grain yield, and yield attributes of second-generation new plant type lines and<br />

check varieties grown at the <strong>IRRI</strong> farm in the dry season of 2003.<br />

Crop Grain Biomass Harvest Panicles Spikelets Grain 1,000-grain<br />

Genotype duration yield production index m –2 panicle –1 filling weight<br />

(d) (t ha –1 ) (g m –2 ) (%) (no.) (no.) (%) (g)<br />

Indica checks<br />

PSBRc52 117 9.51 1,762 49.8 483 94.4 86.9 22.2<br />

IR72 117 9.31 1,731 49.2 468 84.5 89.4 24.1<br />

PSBRc54 119 9.06 1,766 47.2 412 106.0 84.1 22.7<br />

IR8 133 8.72 1,858 41.8 379 94.8 76.0 28.4<br />

PSBRc82 111 8.54 1,515 50.8 452 82.2 87.6 23.7<br />

Mean 119 9.03 1,726 47.8 439 92.4 84.8 24.2<br />

Second-generation new plant type lines<br />

IR72967-12-2-3 125 10.16 1,877 47.1 385 112.3 73.6 27.8<br />

IR73930-41-5-3-1 117 9.00 1,729 47.0 395 100.4 82.8 24.8<br />

IR71700-247-1-1-2 111 8.97 1,480 54.1 493 106.6 77.0 19.8<br />

IR73935-51-1-3-1 117 8.59 1,566 46.3 366 97.7 84.8 24.0<br />

IR72158-16-3-3-1 121 6.27 1,712 32.5 343 113.4 56.9 25.1<br />

Mean 118 8.60 1,673 45.4 396 106.1 75.0 24.3<br />

LSD (0.05) 0.49 126 2.3 28 6.4 3.6 1.2<br />

Table 2. Crop growth duration, grain yield, and yield attributes of second-generation new plant type lines and<br />

check varieties grown at the <strong>IRRI</strong> farm in the dry season of 2004.<br />

Crop Grain Biomass Harvest Panicles Spikelets Grain 1,000-grain<br />

Genotype duration yield production index m –2 panicle –1 filling weight<br />

(d) (t ha –1 ) (g m –2 ) (%) (no.) (no.) (%) (g)<br />

Indica checks<br />

IR72903-121-2-1-2 124 9.32 1,907 44.7 376 118.6 79.1 24.2<br />

PSBRc18 116 8.37 1,775 42.6 418 103.0 78.6 22.4<br />

PSBRc52 111 8.04 1,612 43.3 466 95.3 78.8 20.0<br />

IR68440-36-2-2-3 116 7.96 1,758 42.1 447 107.9 79.1 19.4<br />

IR72 116 7.25 1,720 41.4 481 81.8 82.1 22.0<br />

Mean 117 8.19 1,754 42.8 438 101.3 79.5 21.6<br />

Second-generation new plant type lines<br />

IR72158-16-3-3-1 118 8.76 1,795 42.0 350 135.6 61.8 25.7<br />

IR71700-247-1-1-2 110 8.65 1,493 47.5 512 99.5 74.7 18.6<br />

IR72967-12-2-3 118 8.28 1,786 42.4 352 120.0 66.0 27.2<br />

IR73459-120-2-2-3 124 7.78 1,850 39.7 339 108.3 81.9 24.4<br />

IR73930-41-5-3-1 116 7.39 1,617 41.6 364 98.3 80.1 23.5<br />

Mean 117 8.17 1,708 42.6 383 112.3 72.9 23.9<br />

LSD (0.05) 0.65 112 2.9 26 9.3 4.0 0.4<br />

Overall, the second-generation NPT lines did not outyield the<br />

indica inbred check varieties. T<strong>here</strong> was a small difference in<br />

biomass production and harvest index between the two groups.<br />

Grain filling of the second-generation NPT lines was poorer<br />

than that of the indica inbred check varieties. The spikelet number<br />

per panicle of the second-generation NPT lines was less<br />

than 115, and was on average 15% greater than that of the<br />

indica inbred check varieties.<br />

In the 2004 dry season, an indica inbred line (IR72903-<br />

121-2-1-2) produced the highest yield (Table 2). IR71700-247-<br />

1-1-2 recorded the highest harvest index in both seasons. The<br />

grain yield in the 2004 dry season was lower than that in the<br />

2003 dry season because of lower solar radiation and higher<br />

minimum temperature in the 2004 dry season. Overall, t<strong>here</strong><br />

was no significant difference in grain yield, biomass production,<br />

and harvest index between the second-generation NPT<br />

lines and indica inbred check varieties. As observed in the 2003<br />

dry season, grain filling of the second-generation NPT lines<br />

was poorer than that of the indica inbred check varieties. On<br />

average, spikelet number per panicle of the second-generation<br />

NPT lines was 11% greater than that of the indica inbred check<br />

varieties, which was just enough to compensate for the reduction<br />

in panicle number per m 2 .<br />

Session 4: Improving rice yield potential 131


Directions for further improvement<br />

Progress has been made in the second-generation NPT lines<br />

developed by crossing elite indica with improved tropical<br />

japonica and by modifying the original plant type design. Indica<br />

germplasm also helped improve other NPT attributes such<br />

as grain quality and disease and insect resistance. Many second-generation<br />

NPT lines outyielded the first-generation NPT<br />

lines in both the dry and wet seasons because of their improved<br />

crop biomass production and grain-filling percentage. Occasionally,<br />

the second-generation NPT lines outyielded the indica<br />

inbred check varieties. Overall, the second-generation NPT<br />

lines have not shown yield superiority over the indica inbred<br />

check varieties because of the following reasons:<br />

1. The second-generation NPT lines did not show higher<br />

biomass production or harvest index than the indica<br />

inbred check varieties.<br />

2. The panicle size of the second-generation NPT lines<br />

was not substantially greater than that of the indica<br />

inbred check varieties.<br />

3. The grain-filling percentage of the second-generation<br />

NPT lines has not reached the same level as that of<br />

the indica inbred check varieties.<br />

To further improve the grain yield of the second-generation<br />

NPT lines, the source-sink relation should be balanced by<br />

improving photosynthesis and delaying leaf senescence of the<br />

top three leaves during the ripening phase. The morphology of<br />

the top three leaves and the panicle position within the canopy<br />

are also critical for maintaining the balance between source<br />

and sink. Panicles with an average size of 150 spikelets per<br />

panicle are necessary to assure the increase in sink capacity.<br />

These morpho-physiological traits can be expressed as the yield<br />

attributes that are relatively easy to measure in breeding programs.<br />

These yield attributes are 330 panicles per m 2 , 150<br />

spikelets per panicle, 80% grain filling, 25 mg of grain weight<br />

(based on oven-dry weight), 20 t ha –1 of aboveground total<br />

biomass (based on oven-dry weight), and 50% harvest index.<br />

These attributes are required to produce a yield of 11 t ha –1 at<br />

14% moisture content. As the effort of breeding for secondgeneration<br />

NPT continues, we expect that more elite secondgeneration<br />

NPT lines with improved yield potential, disease<br />

and insect resistance, and grain quality will be developed at<br />

<strong>IRRI</strong>. These elite second-generation NPT lines should increase<br />

the yield potential of irrigated lowland rice by about 10% in<br />

the tropics. Concurrent modification of crop management practices<br />

such as transplanting with different seedling age, planting<br />

geometry, fertilization, irrigation scheme, and weed control<br />

is required for the NPT lines to fully express their yield<br />

potential.<br />

References<br />

Khush GS. 1995. Breaking the yield frontier of rice. GeoJournal<br />

35:329-332.<br />

Khush GS, Peng S. 1996. Breaking the yield frontier of rice. In:<br />

Reynolds MP, Rajaram S, McNab A, editors. Increasing yield<br />

potential in wheat: breaking the barriers. El Batán (Mexico):<br />

<strong>International</strong> Maize and Wheat Improvement Center. p 36-<br />

51.<br />

Ladha JK, Kirk GJD, Bennett J, Peng S, Reddy CK, Reddy PM,<br />

Singh U. 1998. Opportunities for increased nitrogen-use efficiency<br />

from improved lowland rice germplasm. Field Crops<br />

Res. 56:41-71.<br />

Peng S, Khush GS. 2003. Four decades of breeding for varietal improvement<br />

of irrigated lowland rice in the <strong>International</strong> <strong>Rice</strong><br />

<strong>Research</strong> <strong>Institute</strong>. Plant Prod. Sci. 6:157-164.<br />

Peng S, Khush GS, Cassman KG. 1994. Evaluation of a new plant<br />

ideotype for increased yield potential. In: Cassman KG, editor.<br />

Breaking the yield barrier. Proceedings of a Workshop on<br />

<strong>Rice</strong> Yield Potential in Favorable Environments. Los Baños<br />

(Philippines): <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>. p 5-20.<br />

Yamagishi T, Peng S, Cassman KG, Ishii R. 1996. Studies on grain<br />

filling characteristics in “New Plant Type” rice lines developed<br />

in <strong>IRRI</strong>. Jpn. J. Crop Sci. 65(Extra issue No. 2):169-<br />

170.<br />

Notes<br />

Authors’ addresses: Shaobing Peng, Rebecca C. Laza, and Romeo<br />

M. Visperas, Crop, Soil, and Water Sciences Division, <strong>International</strong><br />

<strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong> (<strong>IRRI</strong>), DAPO Box 7777,<br />

Metro Manila, Philippines; Gurdev S. Khush, 416 Cabrillo<br />

Avenue, Davis, CA 95616, USA; Parminder Virk, Plant Breeding,<br />

Genetics, and Biochemistry Division, <strong>IRRI</strong>.<br />

Current status and prospects of rice breeding<br />

for increased yield in China<br />

Wan Jianmin<br />

<strong>Rice</strong> is the main staple food in China, being planted on 23% of<br />

the world’s rice area and contributing 37% of global rice production.<br />

<strong>Rice</strong> production in China plays an important role for<br />

the Chinese people and also affects the world rice market. Although<br />

China, w<strong>here</strong> one-fifth of the world’s population de-<br />

pends on 7% of the world’s arable land, will not encounter any<br />

food security problems in the next few years, it has hidden<br />

risks of food shortage as its rapid economic growth eats away<br />

at arable land.<br />

132 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Area (million ha)<br />

40<br />

35<br />

30<br />

25<br />

Area of rough rice<br />

Area of hybrid rice<br />

20<br />

15<br />

10<br />

5<br />

0<br />

1976 1978 1980 1982 1984 1986 1988 1990 1992 1994 1996 1998 2000<br />

Year<br />

Fig. 1. Area of hybrid rice (million ha).<br />

Current situation of breeding to increase rice yield in China<br />

A look back at crop breeding for super high yield<br />

A series of high-yielding semidwarf varieties has made dramatic<br />

progress in rice cultivation since the 1950s. Hybrid rice<br />

at the end of the 1970s marked another breakthrough in China’s<br />

rice production (Yang et al 1996, Zhou et al 1997, Huang et al<br />

2003). For the first time in 1977, hybrid rice was produced in<br />

farmers’ fields. Subsequently, the area of hybrid rice expanded<br />

rapidly to 54% of the total rice area in 1997, and has remained<br />

at more than 60% since then (Fig. 1).<br />

Despite this progress, China’s grain output dipped from<br />

a record high of 512 million tons in 1998 to 435 million tons<br />

in 2003. In view of the rising population and falling number of<br />

hectares of land across the world, the most effective and economical<br />

way to increase production is considered to be growing<br />

hybrid rice. Hybrid rice, which has been grown in China<br />

for a long period, will continue to play a significant role in<br />

guaranteeing China’s food security.<br />

Advancement of the program<br />

for super high-yielding rice<br />

The current technology of hybrid rice can increase the yield<br />

ceiling by 15–20% over that of the best commercial varieties.<br />

Several breeding programs for super high-yielding rice have<br />

been proposed since the 1980s. In 1996, the Chinese Ministry<br />

of Agriculture set up a super high-yielding rice program with<br />

the targets listed in Table 1.<br />

In recent years, a cooperative research program in hybrid<br />

rice breeding has been conducted by the Jiangsu Academy<br />

of Agricultural Sciences and China National Hybrid <strong>Rice</strong><br />

<strong>Research</strong> Center. In this program, TGMS (thermosensitive<br />

genetic male sterility) line Pei’ai64S was used as the female<br />

parent and test-crossed with a number of breeding lines. Then,<br />

several combinations with a super high yield potential were<br />

screened, including Pei’ai64S/E32, which attained an average<br />

yield as high as 13.26 t ha –1 , with growth duration of 130 days<br />

on a total area of 0.24 ha at three locations in 1997. This hy-<br />

Table 1. Yield standards (t ha –1 ) set for super rice in China. a<br />

Phase<br />

Hybrid rice<br />

Yield<br />

Early-season Late-season Single-season increase<br />

indica indica rice<br />

Before 1996 7.50 7.50 8.25 0<br />

1996-2000 9.75 9.75 10.50 >20%<br />

2001-2005 11.25 11.25 12.00 >40%<br />

a It is required that grain yield be up to standards at two locations of an ecological<br />

area with a planting scale of 6.7 ha at each location for two consecutive years.<br />

brid has met the standard of super high-yielding rice, though<br />

only in a yield trial in a small area. Pei’ai64S/E32 is characterized<br />

by a set of yield components that lead to a theoretical<br />

yield of 13.95 t ha –1 and actual yield of 12.87 t ha –1 . Several<br />

hybrids, such as Chuanxiangyou2, P088S/0293, and<br />

IIyouming86, increased their yield by more than 20%.<br />

Theory of breeding for super high-yielding rice<br />

Two-line and three-line systems<br />

Currently, the three-line system of hybrid rice production is<br />

being followed. But it is known that the two-line system, based<br />

on the photosensitive or thermosensitive genetic male sterility<br />

(P or T-GMS) system, is more efficient and cost-effective.<br />

Combination of ideotype and heterosis<br />

Since Johan and Jeroen (2003) proposed the ideotype concept,<br />

several models have been proposed for super high-yielding<br />

rice: the low-tillering and large panicle model by Khush<br />

(1996), the bushy type and rapid-growing model by Huang<br />

(2003), the ideal plant type and huge rice model by Yang et al<br />

(1996), and the heavy panicle model by Zhou et al (1997).<br />

The new plant type (NPT) being developed by <strong>IRRI</strong> might<br />

raise current yield by 20–25%. These models, yet to be proven<br />

in practice, provide the leading concepts for super high-yield-<br />

Session 4: Improving rice yield potential 133


ing programs since they are based on certain theories and practical<br />

experiences.<br />

Based on the characteristics of Pei’ai64S/E32 in hybrid<br />

rice breeding, Yuan (1997) proposed a morphological model<br />

of super high-yielding rice in terms of (1) plant height, (2) the<br />

uppermost three leaves, (3) plant type, (4) panicle weight and<br />

number, (5) leaf area index (LAI) and ratio of leaf area to grains,<br />

and (6) harvest index of above 0.55.<br />

Use of intersubspecific heterosis<br />

As the heterosis of intersubspecific hybrids is much stronger<br />

than that of intervarietal hybrids, its use is one of the most<br />

feasible approaches for realizing super high yield. To exploit<br />

intersubspecific super high-yielding hybrid rice, the development<br />

of various lines with wide compatibility (WC), especially<br />

lines with a broad spectrum of compatibility, is important (Wan<br />

and Ikehashi 1996). By incorporating WC genes into restorer<br />

lines and male sterile lines of indica, japonica, or intermediate<br />

type, each with a different growth duration, various super highyielding<br />

hybrids will be developed for different ecological<br />

environments.<br />

Genotype × environment interactions<br />

in breeding super high-yielding rice<br />

The present superior-yielding varieties exhibit variable performance<br />

because of a high proportion of G × E interaction.<br />

T<strong>here</strong> is a need to identify and release stably yielding varieties<br />

even on a specific-area basis, instead of relatively less stable<br />

varieties on a wide-area basis. T<strong>here</strong> are strong genotypic differences<br />

among varieties for this interaction as well as methods<br />

for selecting varieties that are more stable across environments.<br />

Prior to releasing varieties, it is possible to select varieties<br />

with a stable performance even in unfavorable environments<br />

or management regimes.<br />

Future prospects of breeding rice for higher yield in China<br />

The extension of already released varieties is an immediate<br />

possibility for breaking the yield barrier. Further, the new plant<br />

type or super rice, hybrid rice, and genetically engineered<br />

transgenic rice are on the horizon.<br />

Germplasm enhancement<br />

The historic discovery of the semidwarfing gene (sd1) in<br />

Taichung (Taiwan, China) revolutionized rice production in<br />

the world, extending varieties carrying this gene to almost all<br />

the rice-growing countries. Following this model, favorable<br />

QTLs have been identified from a set of wild rice based on<br />

molecular analyses and field experiments. Near-isogenic lines<br />

carrying the QTLs are created by marker-facilitated backcrossing<br />

and selection.<br />

× indica hybrids, the next breakthrough in yield could be set in<br />

motion by the use of indica × tropical japonica and indica ×<br />

NPT rice.<br />

Breeding by design<br />

Breeding by design is a concept that aims to control all allelic<br />

variation at all loci of agronomic importance (Steven 1998,<br />

Ashikari and Matsuoka 2002, Johan and Jeroen 2003), which<br />

involves the integrative, complementary application of the technological<br />

tools and materials currently available to develop<br />

superior varieties. This concept can be achieved by a combination<br />

of precise genetic mapping, high-resolution genotyping,<br />

and extensive phenotyping. This approach to all traits of agronomic<br />

importance will require great organizational skills and<br />

will be a major effort. The systematic application of markerassisted<br />

selection could lead to the production of superior varieties<br />

within five to ten years.<br />

References<br />

Ashikari M, Matsuoka M. 2002. Application of rice genomics to<br />

plant biology and breeding. Bot. Bull. Acad. Sin. 43:1-11.<br />

Huang Y. 2003. Construction and advancement of rice ecological<br />

breeding system. World Sci. Tech. Res. 4:1-8. (In Chinese.)<br />

Johan DP, Jeroen RV. 2003. Breeding by design. Trends Plant Sci.<br />

8:330-334.<br />

Khush GS. 1996. Prospects of and approaches to increasing the genetic<br />

yield potential of rice. In: Evenson RE et al, editors.<br />

<strong>Rice</strong> research in Asia: progress and priorities. Wallingford<br />

(UK): CAB <strong>International</strong> and <strong>IRRI</strong>. p 59-71.<br />

Steven JK. 1998. Marker-assisted selection as a strategy for increasing<br />

the probability of selecting superior genotypes. Crop Sci.<br />

38:1164-1174.<br />

Wan J, Ikehashi H. 1996. Two new loci for hybrid sterility in cultivated<br />

rice. Theor. Appl. Genet. 92:183-190.<br />

Yang S, Zhang B, Chen W, Xu Z, Wang J. 1996. Theories and methods<br />

of rice breeding for maximum yield. Acta Agron. Sin.<br />

22(3):295-304.<br />

Yuan L. 1997. Hybrid rice breeding for super high yield. Hybrid<br />

<strong>Rice</strong> 12(6):1-6.<br />

Zhou K, Wang X, Li S, Li P, Li H, Huang G, Liu T, Shen M, 1997.<br />

The study on heavy panicle type of inter-subspecific hybrid<br />

rice (Oryza sativa L.). Sci. Agric. Sin. 30(5):91-93.<br />

Notes<br />

Author’s address: <strong>Institute</strong> of Crop Sciences, Chinese Academy of<br />

Agricultural Sciences, Beijing 100081, China, e-mail:<br />

wanjm@caas.net.cn.<br />

Hybrid rice<br />

All the rice hybrids grown so far are indica hybrids, except for<br />

japonica hybrids in the northern part of China. Since the indica<br />

× tropical japonica hybrids are shown to outyield indica<br />

134 <strong>Rice</strong> is life: scientific perspectives for the 21st century


A large-grain rice cultivar, Akita 63, exhibits high yield<br />

and N-use efficiency for grain production<br />

Tadahiko Mae, Ayako Inaba, Yoshihiro Kaneta, Satoshi Masaki, Mizuo Sasaki, and Amane Makino<br />

It is estimated that the world’s population will increase 1.4- to<br />

1.5-fold by 2025, and this projected increase will be mostly in<br />

Asia (<strong>IRRI</strong> 1995). More than 90% of the world’s production<br />

of rice is in Asia. It is t<strong>here</strong>fore crucial to increase rice production<br />

within a relatively short period. With little scope for expanding<br />

the area of land available for rice cultivation, this increase<br />

in rice production must be achieved by an increase in<br />

yield from the land currently used for such cultivation. On the<br />

other hand, interest is increasing in the environmental impact<br />

of nitrogen (N) management practices (Cassman et al 1998).<br />

T<strong>here</strong>fore, it is desirable to have high-yielding rice cultivars<br />

with high N-use efficiency for grain production. However, selection<br />

or breeding of such rice cultivars has not been seriously<br />

attempted (Ladha et al 1998, Ying et al 1998a,b).<br />

A new large-grain japonica-type cultivar of rice, Akita<br />

63, has recently been released by the Akita Agricultural Experimental<br />

Station in northern Japan and its grain size is 30–<br />

31 mg, which is 25–50% larger than that of current japonica<br />

cultivars. In test cultivation with standard levels of fertilization<br />

at different locations in Akita Prefecture and in different<br />

years, the average yield of Akita 63 was 18% higher than that<br />

of Akitakomachi, which is the current leading cultivar of Akita<br />

Prefecture (Masaki et al, unpublished data), indicating that<br />

Akita 63 might be a new type of high-yielding cultivar with<br />

high N-use efficiency. Although high productivity with large<br />

grain cultivars of rice has been previously reported (Kobayashi<br />

et al 1990, Wang et al 1995), their physiological (internal) N-<br />

use efficiency (NUE) defined as grain yield per unit of N ac-<br />

cumulated in the aboveground part at harvest was not examined.<br />

Herein, we report on the achievement of a high yield of<br />

over 12 t ha –1 of rough rice with Akita 63 and analyze the<br />

factors responsible for its high yield compared with the yield<br />

of common reference cultivars. Finally, the yield-limiting factors<br />

of recent japonica cultivars are discussed in terms of physiological<br />

NUE.<br />

Materials and methods<br />

Akita 63 was grown with different levels of N supply (0–160<br />

kg N ha –1 ) in an experimental field of the Agricultural Experimental<br />

Station of Akita Prefecture, Japan (39°34′N, 140°11′E,<br />

16 m altitude), for three years (2000-02). As reference cultivars<br />

of japonica rice, a high-yielding local cultivar<br />

(Yukigesyou), a common cultivar (Toyonishiki), and a modern<br />

cultivar (Akitakomachi) were also grown with the same N<br />

treatments. The soil type was a Gley soil (Eutric Gleysols; FAO)<br />

with pH 5.3, 31.6 g total C kg –1 , 2.4 g total N kg –1 , and 25.2<br />

cmol kg –1 cation exchange capacity. Phosphorus (43 kg P<br />

ha –1 as fused phosphate) was applied to all plots 30 days before<br />

transplanting. Potassium was not supplied because of its<br />

sufficient level in the soil. Two to four levels of N fertilization<br />

were applied by using ammonium sulfate and controlled-release<br />

fertilizers (urea LP100 type and LPS100 type polyolefincoated,<br />

Chisso Co., Japan) (Table 1). A basal application was<br />

conducted a week before transplanting. Weeds, insects, and<br />

Table 1. Rates of nitrogen application for rice cultivation.<br />

Year<br />

N treatment<br />

Nitrogen application (g N m -2 )<br />

Basal dressing Topdressing Total<br />

2000 High level 2 a + 6 b 2 a × 4 times 16<br />

Standard level 4 a 2 a × 1 time 6<br />

No application 0 0 0<br />

Single application 10 b 0 10<br />

2001 High level 4 a + 7 b 2 a × 2 times 15<br />

Standard level 4 a 2 a × 1 time 6<br />

No application 0 0 0<br />

Single application 10 b + 4 c 0 14<br />

2002 High level 4 a + 7 b 2 a × 2 times 15<br />

Standard level 4 a 2 a × 2 times 8<br />

a Ammonium sulfate. b Controlled-release fertilizer (urea LP100 type polyolefin-coated, Chisso<br />

Co., Japan). c Controlled-release fertilizer (urea LSP100 type polyolefin-coated, Chisso Co.,<br />

Japan).<br />

Session 4: Improving rice yield potential 135


Panicle dry weight (g m –2 )<br />

1,500<br />

1,200<br />

900<br />

600<br />

300<br />

Akita 63 in 2000<br />

Akita 63 in 2001<br />

Akita 63 in 2002<br />

Yukigeshou in 2000<br />

Toyonishiki in 2001<br />

Akitakomachi in 2000<br />

Akitakomachi in 2002<br />

Akita 63: y = 48.32x + 276.7<br />

R 2 = 0.853<br />

Reference y = 52.89x + 91.1<br />

cultivars: R 2 = 0.961<br />

0<br />

0 5 10 15 20 25<br />

Plant nitrogen content (g m –2 )<br />

Fig. 1. Relationship between panicle dry weight and plant nitrogen content<br />

per unit land area at harvest in Akita 63 and the reference cultivars.<br />

diseases were controlled as required to avoid yield loss. All<br />

the experimental plots were arranged in a randomized design<br />

with three replicates, except in the case of Toyonishiki, for<br />

which t<strong>here</strong> were only two replicates at the standard level and<br />

no application treatments in 2001. The area of each plot was<br />

26.25 m 2 (3.5 m wide and 7.5 m long). About 30 five-day-old<br />

seedlings were transplanted with a rice transplanter on a day<br />

in the middle of May at a hill spacing of 0.3 × 0.14 m (24 hills<br />

m –2 ) with 4–5 seedlings per hill.<br />

The sample plants were separated into leaf blades, culms<br />

plus leaf sheaths, panicles, and other parts (dead parts and nonreproductive<br />

tillers). Leaf area was measured with a leaf area<br />

meter (Type-AMM, Hayashi-Denko, Tokyo, Japan). All<br />

samples were oven-dried at 105 °C for several days, weighed,<br />

and powdered. At the time of harvest, plants from three additional<br />

hills with the mean panicle number from each plot were<br />

collected and hand-threshed for measurement of the number<br />

of filled and unfilled spikelets, and grain weight. A survey of<br />

yield was carried out as follows: plants from 80 hills were collected<br />

from the center part of each plot. Winnowed unhulled<br />

rice weight was measured after reaping, threshing, and wind<br />

selection. Unhulled rice of 80 hills was husked to obtain whole<br />

brown rice, and then put through a 1.8-mm sieve to remove<br />

any immature kernels (brown rice). The weight of winnowed<br />

unhulled rice and that of brown rice was adjusted to a moisture<br />

content of 0.15 g H 2 O g –1 fresh weight. The harvest index<br />

was defined as the ratio of panicle dry weight to the total dry<br />

weight of the aboveground part.<br />

N content was determined with Nesler’s reagent after<br />

Kjeldahl digestion of powdered samples with H 2 SO 4 and H 2 O 2 .<br />

Results and discussion<br />

The grain yield of Akita 63 was 22–58% higher than that of<br />

the reference cultivars for all N treatments throughout the threeyear<br />

period. The yields were high in 2000 and 2001 and low in<br />

2002, mainly because of the differences in climatic conditions<br />

during the culture period among the three years. The highest<br />

yield was 12.8 t ha –1 of rough rice (9.83 t ha –1 of brown rice),<br />

close to the highest yield of japonica rice (10.52 t ha –1 of brown<br />

rice) previously recorded in Japan (Honya 1989). The dry<br />

weight of the aboveground part, the number of total spikelets,<br />

and the amount of N accumulated in the aboveground part<br />

(plant N) per unit land area at harvest were almost the same<br />

between Akita 63 and the reference cultivars in 2000 and larger<br />

in Akita 63 than in the reference cultivars in 2001 and 2002<br />

for all the N treatments. However, the dry weight of the<br />

aboveground part and the number of total spikelets for a given<br />

amount of plant N per unit land area at harvest did not differ<br />

between Akita 63 and the reference cultivars. Clear differences<br />

in sink capacity (total spikelet number per unit land area × the<br />

weight of 1,000 kernels) and panicle dry weight for a given<br />

amount of plant N per unit land area were found between Akita<br />

63 and the reference cultivars. The sink capacity was 30–40%<br />

greater in Akita 63 than in the reference cultivars because the<br />

weight of 1,000 kernels was 29–36% greater in Akita 63. Figure<br />

1 shows the relationship between panicle dry weight and<br />

plant N content per unit land area at harvest. The panicle dry<br />

weight for a given amount of plant N per unit land area was<br />

12–43% greater in Akita 63 than in the reference cultivars.<br />

This was because the ratio of dry matter partitioning to the<br />

136 <strong>Rice</strong> is life: scientific perspectives for the 21st century


panicle (harvest index) was higher in Akita 63 than in the reference<br />

cultivars. The difference was more pronounced with<br />

less plant N content. No difference in the relationship between<br />

leaf area index and plant N content per unit land area was found<br />

between Akita 63 and the reference cultivars, but panicle dry<br />

weight for a given unit of leaf area index was 13–48% greater<br />

in Akita 63 than in the reference cultivars.<br />

Reaccumulation of dry matter or starch in the culms and<br />

leaf sheaths was remarkable in the later stage of grain filling in<br />

the reference cultivars, but not in Akita 63. The reaccumulation<br />

in the reference cultivars could be attributed to their insufficient<br />

sink capacity because the proportion of the number of<br />

ripened grains to the total number of grains was more than<br />

90% even for the high N treatment in the reference cultivars,<br />

w<strong>here</strong>as the proportion was lower than 79% for the same N<br />

treatment in Akita 63. Those results indicate that Akita 63,<br />

which has a greater sink capacity for a given amount of plant<br />

N per unit land area, still had the capacity for further accumulation<br />

of dry matter in its panicles even in the later stage of<br />

grain filling, while the reference cultivars, which have relatively<br />

smaller sink capacities, had already nearly reached the<br />

upper limit of accumulation and had almost no space for further<br />

accumulation in their panicles in the later stage of grain<br />

filling. Thus, dry matter was mostly translocated into the culms<br />

and leaf sheaths in the late stage of grain filling in the reference<br />

cultivars under given growth conditions. As a consequence,<br />

the physiological (internal) N-use efficiency was higher<br />

in Akita 63 than in the reference cultivars. When the partitioning<br />

of 13 C into panicles, culms, leaf sheaths, leaf blades, and<br />

roots was examined at harvest after the photosynthetic assimilation<br />

of 13 CO 2 at different stages of grain filling, the proportion<br />

of 13 C partitioned into panicles was higher at all stages of<br />

grain filling in Akita 63 than in reference cultivar Toyonishiki<br />

(Mae et al, unpublished data). Reaccumulation of nonstructural<br />

carbohydrates in the culms and leaf sheaths at the later stages<br />

of grain filling seems to be a characteristic of the common<br />

cultivars of japonica rice. Similar trends have been previously<br />

reported between a high-yielding indica cultivar, Milyang 23,<br />

and a common japonica cultivar, Nipponbare (Saito et al 1991,<br />

Tsukaguchi et al 1996). Our study indicates that the enlargement<br />

of sink capacity per unit of plant N might increase the<br />

yield potential of common japonica cultivars of rice and improve<br />

their physiological N-use efficiency.<br />

Honya K. 1989. Analysis of high-yield cultivation of rice. Tokyo<br />

(Japan): Hakuyosha. 36 p. (In Japanese.)<br />

<strong>IRRI</strong> (<strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>). 1995. <strong>Rice</strong> facts. Manila<br />

(Philippines): <strong>IRRI</strong>. p 2.<br />

Kobayashi A, Koga Y, Uchiyamada H, Samoto S, Horiuchi H, Miura<br />

K, Okuno K, Fujita Y, Uehara Y, Ishizaka S, Nakagahara M,<br />

Yamada T, Maruyama K. 1990. Breeding a new rice variety,<br />

Oochikara. Bull. Hokuriku National Agric. Exp. Stn. 32:85-<br />

104. (In Japanese.)<br />

Ladha JK, Kirk GJD, Bennett J, Peng S, Reddy CK, Reddy PM,<br />

Singh U. 1998. Opportunities for increasing nitrogen-use efficiency<br />

from improved lowland rice germplasm. Field Crops<br />

Res. 56:41-71.<br />

Saito K, Kashiwagi N, Kinoshita T, Ishihara H. 1991. Characteristics<br />

of dry matter production process in high yielding rice<br />

varieties. IV. Dry matter accumulation in the panicle. Jpn. J.<br />

Crop Sci. 60:255-263.<br />

Tsukaguchi T, Horie T, Ohnishi M. 1996. Filling percentage of rice<br />

spikelets as affected by availability of non-structural carbohydrates<br />

at the initial phase of grain filling. Jpn. J. Crop Sci.<br />

65:445-452.<br />

Wang W, Yamamoto Y, Nitta Y. 1995. Analysis of the factors of high<br />

yielding ability for a japonica type rice line, 9004, bred in<br />

China. 1. Comparison of yield ability with a Japanese rice<br />

variety under the same level of spikelet number per area. Jpn.<br />

J. Crop Sci. 64:545-555.<br />

Ying J, Peng S, He Q, Yang H, Yang C, Visperas RM, Cassman KG.<br />

1998a. Comparison of high-yield rice in tropical and subtropical<br />

environments. I. Determinants of grain and dry matter<br />

yields. Field Crops Res. 57:71-84.<br />

Ying J, Peng S, Yang C, Neng Zhou, Visperas RM, Cassman KG.<br />

1998b. Comparison of high-yield rice in tropical and subtropical<br />

environments. II. Nitrogen accumulation and utilization<br />

efficiency. Field Crops Res. 57:85-93.<br />

Notes<br />

Authors’ addresses: Tadahiko Mae, Ayako Inaba, Mizuo Sasaki, and<br />

Amane Makino,<br />

Department of Applied Plant Science, School of Agricultural Science,<br />

Tohoku University, 1-1 Tsutsumidori-Amamiyamachi,<br />

Aoba-ku, Sendai 981-8555, Japan; Yoshihiro Kaneta and<br />

Satoshi Masaki, the Agricultural Experimental Station of Akita<br />

Prefecture, Aikawa Yuuwamachi Kawabe-gun, Akita Prefecture<br />

010-1231, Japan, e-mail:<br />

hikomae@biochem.tohoku.ac.jp.<br />

References<br />

Cassman KG, Peng S, Olk DC, Ladha JK, Reichardt W, Dobermann<br />

A, Singh U. 1998. Opportunities for increased nitrogen-use<br />

efficiency from improved resource management in irrigated<br />

rice systems. Field Crops Res. 56:7-39.<br />

Session 4: Improving rice yield potential 137


Using heterosis and hybrid rice<br />

to increase yield potential in China<br />

Xuhua Zhong, Shaobing Peng, Feng Wang, and Nongrong Huang<br />

The use of heterosis and hybrid rice has been one of the most<br />

important achievements in China. Hybrid rice occupies about<br />

15 million ha of fields, or half of China’s rice-planting area.<br />

The yield potential of hybrid rice is about 20% greater than<br />

that of inbreds. Since its adoption in 1976, hybrid rice had<br />

been planted on 271 million ha of rice land until 2001 in China.<br />

The increased grain from hybrid rice can feed 60 million people<br />

annually.<br />

China’s rice yield has experienced two quantum leaps<br />

since the 1950s (Peng et al 2004). The first one resulted from<br />

the extension of semidwarf rice varieties in the 1960s. <strong>Rice</strong><br />

yield increased from 2.08 t ha –1 in 1961 to 3.14 t ha –1 in 1966,<br />

with an annual increase of 0.21 t ha –1 . The second leap was<br />

brought about by the development of hybrid rice in 1976. Grain<br />

yield increased from 3.50 t ha –1 in 1976 to 5.36 t ha –1 in 1984,<br />

with an annual increase of 0.23 t ha –1 . To feed the increasing<br />

population, China’s rice production must increase from 177<br />

million tons in 2003 to 240 million t in 2030. Yield must increase<br />

from 6.27 to 7.66 t ha –1 during the same period. Hybrid<br />

rice is expected to play an important role in the new increase<br />

in rice yield potential.<br />

Three generations of hybrid rice<br />

Three-line hybrid rice<br />

The first-generation hybrids used intervarietal heterosis through<br />

the three-line approach. Cytoplasmic genetic male sterility<br />

(CMS) was used to facilitate hybrid seed production. Yuan<br />

started his pioneering work on hybrid rice breeding in 1964.<br />

However, no significant progress was achieved until 1970,<br />

when the male sterile wild rice plant, “wild abortive,” was<br />

found. In 1973, all three lines—male sterile lines (A lines),<br />

maintainer lines (B lines), and restorer lines (R lines)—were<br />

made available. The heterosis of hybrid rice was shown by<br />

faster tillering, greater leaf area index, higher dry matter production,<br />

and a stronger root system. The three-line hybrids<br />

yielded 20% more than the best inbred check varieties. Planting<br />

area of hybrids was 0.135 million ha in 1976, which expanded<br />

rapidly to 8.84 million ha in 1984 and 16.6 million ha<br />

in 1990.<br />

Two-line hybrid rice<br />

The yield of hybrid rice remained stagnant until the mid-1980s.<br />

To break the yield barrier, the two-line approach using<br />

intersubspecific heterosis was proposed (Yuan 1997). Environment-sensitive<br />

genic male sterility, including photoperiodand<br />

thermosensitive sterility (P/TGMS), was employed in this<br />

approach. In contrast with the three-line system, normal vari-<br />

eties can be used as restorers to produce hybrid F 1 . The possibility<br />

to find good combinations is much greater than with the<br />

three-line approach. Second-generation hybrids yielded 5–10%<br />

more than three-line hybrids although their grain filling was<br />

poor.<br />

Super hybrid rice<br />

The Ministry of Agriculture of China established a mega project<br />

on the development of super rice in 1996 (Min et al 2002).<br />

The objectives were<br />

1. To develop “super” rice varieties with a maximum<br />

yield of 9–10.5 t ha –1 by 2000, 12 t ha –1 by 2005, and<br />

13.5 t ha –1 by 2015 measured from a planting area of<br />

at least 6.7 ha.<br />

2. To develop “super” rice varieties with a yield potential<br />

of 12 t ha –1 by 2000, 13.5 t ha –1 by 2005, and 15<br />

t ha –1 by 2015. These yields will be achieved in experimental<br />

and demonstration plots.<br />

3. To raise the national average rice yield to 6.9 t ha –1<br />

by 2010 and 7.5 t ha –1 by 2030.<br />

In addition, the super rice varieties should outyield the<br />

locally wide-grown check varieties by 10%, or daily yield<br />

achieve 100 kg ha –1 , with acceptable grain quality and pest<br />

resistance. Significant progress has been achieved in China’s<br />

super hybrid rice breeding in recent years.<br />

Strategy for super hybrid rice breeding<br />

The strategy for super hybrid rice breeding was to combine<br />

the ideotype approach with the use of intersubspecific heterosis<br />

(Yuan 1997). This was different from the counterpart<br />

projects of other countries and/or organizations. According to<br />

the principles of hybrid rice breeding, t<strong>here</strong> are two ways to<br />

achieve super high yield. One is to make full use of the dominant<br />

complementary effects of the two parents to improve the<br />

morphological characteristics of the hybrid. Another is to extend<br />

the genetic diversity of the parents to increase the heterosis<br />

level. The heterosis of intersubspecific hybrids is much<br />

stronger than that of intervarietal ones. The use of<br />

intersubspecific hybrids is thus the most feasible approach for<br />

super high yield. The discovery of P/TGMS and wide compatibility<br />

(WC) genes made it possible to directly use<br />

intersubspecific heterosis. Several WC lines were developed<br />

as “bridges” to overcome the too great genetic difference in<br />

typical intersubspecific hybrids, which resulted in physiological<br />

barriers. The WC lines could freely cross with both indica<br />

and japonica varieties without problems in grain filling (Yang<br />

et al 1996).<br />

138 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. Selected super hybrid rice released by the provincial or national seed board.<br />

Variety Breeder Planting area Year of Province of<br />

(000 ha) release release<br />

Lianyoupeijiu Jiangsu Academy of Agricultural Sciences; 3,700 1999 Jiangsu<br />

China National Hybrid <strong>Rice</strong> R&D Center<br />

Xieyou 9308 China National <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong> 673 1999 Zhejiang<br />

D you 527 Sichuan Agricultural University 667 2001 Sichuan<br />

Ganyou 527 Sichuan Agricultural University 533 2002 Sichuan<br />

Ganyou 827 Sichuan Agricultural University 133 2003 Sichuan<br />

Eryouhang 1 Fujian Academy of Agricultural Sciences 167 2004 Fujian<br />

Teyouhang 1 Fujian Academy of Agricultural Sciences 67 2002 Fujian<br />

Yueza 122 Guangdong Academy of Agricultural Sciences 80 2001 Guangdong<br />

Yueza 889 Guangdong Academy of Agricultural Sciences 20 2004 Guangdong<br />

Lianyou 932 Hubei Academy of Agricultural Sciences 13 2002 Hubei<br />

Liaoyou 1518 North China Japonica Hybrid <strong>Rice</strong> R&D Center n.a. a 2002 Liaoning<br />

P88S/0293 China National Hybrid <strong>Rice</strong> R&D Center n.a. n.a. n.a.<br />

a n.a. = not available.<br />

Morphological design of super hybrid rice<br />

The poor grain filling of second-generation hybrids and<br />

progress in <strong>IRRI</strong>’s new plant type breeding led Chinese scientists<br />

to pay more attention to morphology. Different versions<br />

of morphological design were developed according to regional<br />

ecological conditions. Well adopted are the “panicle-underleaves”<br />

type for the Yangtze River region (Yuan 2001), the<br />

“heavy-panicle” type for western China (Zhou et al 1997), and<br />

the “rapid-early-growth-and-deep-root” type for South China<br />

(Huang 2001).<br />

Yuan (2001) suggested the panicle-under-leaves type<br />

with the following morphological traits:<br />

Plant height about 100 cm, with culm length of 70<br />

cm.<br />

Top three leaves:<br />

1. Long: flag leaf is 50 cm and -2nd and -3rd leaves<br />

55 cm in length. The top two leaves are higher<br />

than the top of the panicle.<br />

2. Erect: leaf angles of the flag, -2nd, and -3rd leaves<br />

are around 5°, 10°, and 20°, respectively.<br />

3. Narrow and V-shaped: the leaves look narrow but<br />

they are 2 cm wide when flattened.<br />

4. Thick: 55 g m –2 of specific leaf weight for the<br />

top three leaves.<br />

Plant type: moderately compact type with moderate<br />

tillering capacity; droopy panicles, the panicle top<br />

about 60 cm from the ground after filled; erect leaf<br />

canopy without appearance of panicles.<br />

Panicle weight and number: grain weight is 5 g per<br />

panicle; 270–300 panicles m –2 .<br />

Leaf area index (LAI): the LAI of the top three leaves<br />

is about 6.<br />

Harvest index: about 0.55.<br />

Performance of selected super hybrid rice<br />

More than 10 hybrid varieties that meet the super rice criteria<br />

have been released by the provincial or national seed board<br />

(Table 1). The cumulated planting area of super hybrid rice is<br />

estimated at 6 million ha.<br />

Lianyoupeijiu is a two-line intersubspecific hybrid (Lu<br />

and Zou 2003). The female parent Pei’ai64S is an intermediate<br />

type between indica and japonica, w<strong>here</strong>as the restorer 9311<br />

is a typical indica line. In the 1997-98 yield trial, Lianyoupeijiu<br />

achieved 9.56 t ha –1 and outyielded check variety Shanyou 63<br />

by 7.75%. An average yield of 12.15 t ha –1 was achieved in a<br />

67.8-ha area in Jiangsu Province in 2001.<br />

Xieyou 9308 is a three-line intersubspecific hybrid<br />

(Cheng and Zhai 2000). The female parent Xieqingzao-A is a<br />

typical indica sterile line. The restorer line Zhonghui 9308 is<br />

an intermediate type. Grain yield ranged from 10.53 to 11.95 t<br />

ha –1 in farmers’ fields of 6.7 ha in Zhejiang Province during<br />

1999-2001 and a yield of 12.23 t ha –1 was recorded in a 697-<br />

m –2 field.<br />

Liaoyou 1518 is a japonica hybrid (Hua et al 2003). The<br />

female parent 151A is a japonica line. The male parent C418<br />

is an indica line with good compatibility with the japonica variety.<br />

In field trials in 2001, Liaoyou 1518 yielded from 8.37<br />

to 12.08 t ha –1 and outyielded check variety Liaojing 454 by<br />

6.37–30.2%.<br />

Common characteristics of released super hybrid rice<br />

The super hybrids have several characteristics in common:<br />

Many super hybrids, such as Lianyoupeijiu, Xieyou<br />

9308, Yueza 122, Liaoyou 1518, and P88S/0293, use<br />

indica-japonica intersubspecific heterosis.<br />

Large sink. The panicle size is significantly enlarged,<br />

with a small reduction in panicle number m –2 . Spikelets<br />

reach 35,000–45,000 m –2 .<br />

Session 4: Improving rice yield potential 139


Conclusions<br />

Large source. The top three leaves of Lianyoupeijiu<br />

are longer and wider than those of the check varieties<br />

and age more slowly (Cheng and Zhai 2000).<br />

Good plant type. Plant height is 110–120 cm and taller<br />

than that of check varieties. The top three leaves are<br />

more erect during grain filling. For example, the leaf<br />

angle was 5.1 o , 8.1 o , and 15.1 o for the flag, 2nd, and<br />

3rd leaves of Lianyoupeijiu, and 7.3 o , 16.3 o , and 24.0 o<br />

for those of Shanyou 63, respectively.<br />

Super hybrids have more root biomass and a greater<br />

ratio of roots is located in deep soil than the check<br />

variety Shanyou 63. This is related to the slower senescence<br />

of leaves during grain filling.<br />

The increase in grain yield is mainly due to the increase<br />

in biomass while the harvest index remains unchanged.<br />

Hybrid rice has contributed significantly to increasing China’s<br />

rice production. The use of rice heterosis has experienced three<br />

stages, three-line, two-line, and super hybrid rice, and yield<br />

potential has increased continuously. China’s super hybrid rice<br />

breeding program is successful. The combination of the<br />

ideotype approach and the use of intersubspecific heterosis is<br />

a feasible strategy to raise rice yield potential. This is verified<br />

by the release of more than 10 super hybrids in recent years.<br />

The common characteristics of super hybrid rice are a large<br />

sink, large source, taller plant, good plant type, and strong root<br />

system with prolonged activity. Greater biomass production is<br />

the main reason for the higher grain yield of super hybrid rice.<br />

References<br />

Cheng SH, Zhai HQ. 2000. Comparison of some plant type components<br />

in super high-yielding hybrids of intersubspecies rice.<br />

Acta Agron. Sin. 26(6):713-718.<br />

Hua ZT, Wang YR, Wang Y, Dai GJ, Cai W, Zhang ZX, Hao XB, Su<br />

YA, Li QY. 2003. Breeding and application of japonica super<br />

hybrid rice Liaoyou 1518. Liaoning Agric. Sci. 2003(5):51-<br />

52.<br />

Huang YX. 2001. <strong>Rice</strong> ideotype breeding of Guangdong Academy<br />

of Agricultural Sciences in retrospect. Guangdong Agric. Sci.<br />

3:2-6.<br />

Lu CG, Zou JS. 2003. Comparative analysis on plant type of two<br />

super hybrid rice and Shanyou 63. Sci. Agric. Sin. 36(6):633-<br />

639.<br />

Min SK, Cheng SH, Zhu DF. 2002. China’s super rice breeding and<br />

demonstration in rice production fields: an overview. China<br />

<strong>Rice</strong> 2:5-7.<br />

Peng S, Laza RC, Visperas RM, Khush GS, Virk P. 2004. <strong>Rice</strong>:<br />

progress in breaking the yield ceiling. Proceedings of the 4th<br />

<strong>International</strong> Crop Science Congress, 26 Sept-1 Oct 2004,<br />

Brisbane, Australia. Published on CD-ROM. Web site<br />

www.regional.org.au/au/cs.<br />

Yang SR, Zhang LB, Chen WF, Xu ZJ, Wang JM. 1996. Theories<br />

and methods of rice breeding for maximum yield. Acta Agron.<br />

Sin. 22(3):295-304.<br />

Yuan LP. 1997. Hybrid rice breeding for super high yield. Hybrid<br />

<strong>Rice</strong> 12(6):1-6.<br />

Yuan LP. 2001. Breeding of super hybrid rice. In: Peng S, Hardy B,<br />

editors. <strong>Rice</strong> research for food security and poverty alleviation.<br />

Los Baños (Philippines): <strong>International</strong> <strong>Rice</strong> <strong>Research</strong><br />

<strong>Institute</strong>. p 143-149.<br />

Zou KD, Wang XD, Li SG, Li P, Li HY, Huang GT, Liu TQ, Shen<br />

MS. 1997. The study on heavy panicle type of intersubspecific<br />

hybrid rice (Oryza sativa L.). Sci. Agric. Sin. 30(5):91-93.<br />

Notes<br />

Authors’ addresses: Xuhua Zhong, Feng Wang, and Nongrong<br />

Huang, The <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>, Guangdong Academy of<br />

Agricultural Sciences, Guangzhou 510640, China, e-mail:<br />

xzhong1@pub.guangzhou.gd.cn; Shaobing Peng, Crop, Soil,<br />

and Water Sciences Division, <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong><br />

(<strong>IRRI</strong>), DAPO Box 7777, Metro Manila, Philippines,<br />

e-mail: s.peng@cgiar.org.<br />

Breeding and prevalence of japonica hybrid rice<br />

variety Mitsuhikari<br />

Atsushi Nakamura<br />

In most rice-growing countries in Asia, achieving self-sufficiency<br />

in rice production and maintaining price stability are<br />

important. Since the 1980s, many Asian countries, and especially<br />

China, have developed breeding of hybrid rice to increase<br />

yield.<br />

Since 1986, Mitsui Chemicals, Inc. (MCI) has developed<br />

a breeding program for a japonica hybrid rice variety<br />

acceptable to Japanese markets. To breed a new variety possessing<br />

both high yield and good eating quality, we aimed at<br />

traits such as plant type (erect leaf), ear type (panicle weight),<br />

strength against lodging (stiffness), and grain quality (amy-<br />

lose content, etc.). In 2000, MCI registered the first commercial<br />

japonica hybrid rice varieties, Mitsuhikari 2003 and<br />

Mitsuhikari 2005, which were bred by combining a conventional<br />

breeding method and modern biotechnology in Japan.<br />

MCI started selling these seeds in Japan in 2002.<br />

Mitsuhikari 2003 and 2005 possess high yield and good<br />

eating quality. To gain wide acceptance in Japan, it is necessary<br />

to detect suitable districts to make full use of these varieties.<br />

On the other hand, Mitsuhikari varieties have some undesirable<br />

traits such as long culms and a long growing period. To<br />

improve these traits, we have continuously developed a hy-<br />

140 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. Yield performance and grain quality of Mitsuhikari varieties and MH 3001. a<br />

Culm Panicle Brown rice Amylose Protein<br />

Variety Yield Heading length length Panicles content content Eating<br />

(t ha –1 ) (d) (cm) (cm) m –2 100-grain Length Width (%) (%) quality b<br />

wt (g) (mm) (mm)<br />

Mitsuhikari<br />

2003 7.1 140 91 26.3 283 2.11 5.5 3.0 19.5 8.2 70<br />

2005 6.7 138 90 26.2 262 2.06 5.6 3.0 18.8 7.4 77<br />

MH 3001 7.1 126 82 26.0 305 2.25 5.7 3.0 19.2 7.5 74<br />

Check 5.5 120 91 17.7 400 2.14 5.2 3.0 19.0 7.9 75<br />

(Koshihikari)<br />

a Values mean average of 2001-02. Input dose of fertilizer was 100 kg N ha -1 . b Eating quality means the analyzed value of the grain quality inspector<br />

(Satake RCTA11A).<br />

brid rice breeding program. The fruit of our efforts, a new<br />

japonica hybrid rice line, MH 3001, appeared in 2002.<br />

This study presents the productivity and prevalence of<br />

both Mitsuhikari varieties and MH 3001.<br />

Materials and methods<br />

Mitsuhikari varieties<br />

Mitsuhikari 2003 and 2005 were selected after the evaluation<br />

of 800 different F 1 s crossed between Japanese varieties as females<br />

and japonica-like restorer lines from China as males.<br />

They have erect leaves, panicle weight type, long growing<br />

periods, long culms, and strength to resist lodging. For the<br />

easy production of F 1 seeds, the female lines were cytoplasmic<br />

male sterile (CMS) lines produced through asymmetric<br />

fusion (Akagi et al 1989). We have also developed DNA markers<br />

such as PCR, RAPD, and microsatellites that can identify<br />

CMS lines, restorer lines, and F 1 s (Akagi et al 1995, Ichikawa<br />

et al 1997). These markers are powerful tools for breeding<br />

parental lines and certifying F 1 seed purity.<br />

MH 3001<br />

Since 1993, we have developed some dwarf restorer lines. From<br />

1998 to 2002, performance tests of F 1 s produced between<br />

japonica CMS lines and these restorer lines were practiced.<br />

One combination, whose productivity and eating quality were<br />

the same as those of Mitsuhikari 2005, but whose growing<br />

period and plant height were shorter than those of Mitsuhikari<br />

2005, was selected. The F 1 of this combination was named<br />

MH 3001.<br />

Yield performance and grain quality<br />

We assessed the productivity and grain quality of Mitsuhikari<br />

varieties and MH 3001, as compared with those of Koshihikari<br />

(check variety) at MCI’s research paddy field in Ibaraki Prefecture<br />

from 2001 to 2002. Their productivity was expressed<br />

by brown rice yields after screening with a net of 1.75-mm<br />

mesh. Also, agronomic traits such as culm length, panicle<br />

length, panicles m –2 , and both the weight and size of brown<br />

rice were measured. We analyzed grain quality such as amylose<br />

content, protein content, and eating quality with a rice<br />

quality inspector (Satake RCTA11A).<br />

Performance test of Mitsuhikari<br />

Since 1995, performance tests of Mitsuhikari varieties have<br />

been carried out at the prefectural agricultural research center<br />

in seven districts, Kanto, Tokai, Kinki, Chugoku, Shikoku,<br />

Kyusyu, and Okinawa. Cropping practices followed those of<br />

each district. The input doses of fertilizer were 70–120 kg N<br />

ha –1 . Productivity was expressed by the yield of brown rice<br />

after screening.<br />

Results and discussion<br />

Table 1 shows the yield performance and grain quality of<br />

Mitsuhikari 2003 and 2005 and MH 3001. They yielded nearly<br />

30% more than Koshihikari. Their growing period to heading<br />

date was 30–40 days longer than that of Koshihikari. The<br />

panicle length of these hybrids was also about 10 cm longer<br />

than that of Koshihikari, and their period from heading to<br />

maturation took more than twice as long as that of Koshihikari.<br />

The culm length of Mitsuhikari varieties and Koshihikari was<br />

about 90 cm, and that of MH 3001 was about 80 cm. This trait<br />

of MH 3001 will be an advantage for tolerance of lodging.<br />

The grain weight of MH 3001 was the heaviest among<br />

the four varieties. The length of brown rice of all the hybrids<br />

was longer than that of Koshihikari. For grain quality, both the<br />

amylose and protein contents of these hybrids were much the<br />

same as those of Koshihikari. Also, eating quality of the hybrids<br />

was similar to that of Koshihikari.<br />

Table 2 shows the results of the performance test. In all<br />

of the districts, the productivity of Mitsuhikari 2003 was higher<br />

than that of Mitsuhikari 2005. Mitsuhikari varieties cropped<br />

in the southern districts of Japan have outyielded the checks<br />

by more than 20%. This result means that these southern districts<br />

are suitable for growing Mitsuhikari varieties to exploit<br />

their real productivity. We estimated that Mitsuhikari 2003 and<br />

2005 were cropped on about 1,000 ha last year, mostly in southern<br />

districts. On the other hand, the new hybrid line, MH 3001,<br />

is earlier in heading than Mitsuhikari varieties. We expect that<br />

Session 4: Improving rice yield potential 141


Table 2. Productivity (yield in t ha -1 ) of Mitsuhikari varieties in different districts. a<br />

Variety<br />

District<br />

Kanto Tokai Kinki Chugoku Shikoku Kyusyu Okinawa<br />

Mitsuhikari<br />

2003 6.9 (117) 7.3 (124) 7.4 (123) 7.5 (132) 7.2 (126) 6.9 (128) 4.3 (130)<br />

2005 6.7 (114) 6.6 (112) 7.3 (122) 6.5 (114) 6.1 (107) 6.9 (128) 4.1 (124)<br />

Check 5.9 (100) 5.9 (100) 6.0 (100) 5.7 (100) 5.7 (100) 5.4 (100) 3.3 (100)<br />

a Values mean average of each district (1995-2003). Input doses of fertilizer were 70-120 kg N ha -1 . Numbers in parentheses<br />

mean increase rate vis-à-vis the check.<br />

this line will be accepted w<strong>here</strong> Mitsuhikari 2003 and 2005<br />

have not prevailed. MH 3001 is now under registration.<br />

References<br />

Akagi H, Sakamoto M, Negishi T, Fujimura T. 1989. Construction<br />

of rice cybrid plants. Mol. Gen. Genet. 215:501-506.<br />

Akagi H, Nakamura A, Sawada R, Oka M, Fujimura T. 1995. Genetic<br />

diagnosis of cytoplasmic male sterile cybrid plants of<br />

rice. Theor. Appl. Genet. 90:948-951.<br />

Ichikawa N, Kishimoto N, Inagaki A, Nakamura A, Koshino Y,<br />

Yokozeki Y, Oka M, Samoto S, Akagi H, Higo H, Shinjyo C,<br />

Fujimura T, Shimada H. 1997. A rapid PCR-aided selection<br />

of a rice line containing the Rf-1 gene which is involved in<br />

restoration of the cytoplasmic male sterility. Mol. Breed.<br />

3:195-202.<br />

Notes<br />

Author’s address: Mitsui Chemicals Incorporation, Agrochemicals<br />

Division, Bio-product Department, 2893, Kaminoshima,<br />

Azumamachi, Inashiki-gun, Ibaraki-ken 300-0732, Japan, e-<br />

mail: atsushi.nakamura@mitsui-chem.co.jp.<br />

Dry-matter production and nitrogen distribution<br />

in a female-sterile line of rice<br />

Morio Kato, Sachio Maruyama, and Masao Yokoo<br />

The functional relations between the source capacity of leaves<br />

and the sink capacity of panicles affect dry-matter production<br />

and determine rice yield. The source-sink relation has so far<br />

been studied on rice plants from which their panicles were<br />

artificially removed. In rice, however, the role of panicle photosynthesis<br />

is not neglected and the role of hulls as a nutrient<br />

pool is important. We planned to analyze the source-sink relation<br />

and the accumulation of dry matter in intact plants. Under<br />

the assumption that the sink capacity of panicles is negligible,<br />

we examined the source-sink relation in a female-sterile line<br />

of rice (FS1), and characterized the effects of losing the sink<br />

function of panicles on dry-matter production and nitrogen<br />

distribution among plant organs.<br />

Materials and methods<br />

A female-sterile line (FS1) and a normal fertile line (Fujisaka<br />

5) of rice (Oryza sativa L.) were used. FS1 is a progeny from<br />

the cross between Japanese variety Fujisaka 5 and Indonesian<br />

variety Tjina four times backcrossed by Fujisaka 5 as a recur-<br />

rent parent. FS1 resembles Fujisaka 5 for most plant types, but<br />

has panicles with few ripened grains because of incomplete<br />

embryo sac formation (Yokoo 1984).<br />

Germinated seeds were sown on 21 April in a plastic<br />

box containing rice nursery soil. Two seedlings at the 6-leaf<br />

stage were transplanted to a 1/5,000 area of a Wagner pot.<br />

Plants were placed under natural conditions in a vinyl house<br />

from April to September 2000 at the Agricultural and Forestry<br />

<strong>Research</strong> Center, University of Tsukuba.<br />

At 10 days before heading and during the period from<br />

heading to maturity (42 d after heading), 6 plants were harvested<br />

every 7 d and divided into 6 parts: roots, culms plus<br />

leaf sheaths (stems), leaf blades, dead leaves, panicles, and<br />

late tillers that appeared after heading. All the samples were<br />

oven-dried at 80 °C for 72 h and their dry weights were determined.<br />

The dried plant materials were ground in a mill, and<br />

their carbon and nitrogen contents were determined by a C-N<br />

Corder (MT600, Yanaco, Japan). The amounts of carbon and<br />

nitrogen of each organ were determined by multiplying dry<br />

weights by each content.<br />

142 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Dry weight (g plant –1 )<br />

80<br />

70<br />

Root<br />

Culm + leaf sheath<br />

Leaf blade<br />

Dead leaf<br />

Panicle<br />

Late tiller<br />

FS1<br />

Fujisaka 5<br />

60<br />

50<br />

40<br />

30<br />

20<br />

10<br />

0<br />

–10 0 7 14 21 28 35 42<br />

Days after heading<br />

–10 0 7 14 21 28 35 42<br />

Days after heading<br />

Fig. 1. Changes in dry weights of each organ in FS1 and Fujisaka 5 during the ripening stage.<br />

Results<br />

Growth characteristics<br />

FS1 and Fujisaka 5 headed 88 and 89 d after sowing, respectively.<br />

Culm and panicle lengths of FS1 were much longer than<br />

those of Fujisaka 5. The number of panicles was almost equal<br />

in both lines. In FS1, late tillers developed rapidly from basal<br />

and upper lateral buds in the last half of the ripening stage.<br />

Changes in dry-matter production<br />

and distribution among organs<br />

Total dry weights were 48.5 and 40.4 g plant –1 at heading time<br />

and 75.3 and 58.8 g plant -1 at maturity in FS1 and Fujisaka 5,<br />

respectively. The distribution of dry weight to each organ differed<br />

during the period from heading to maturity (Fig. 1). The<br />

dry weight of panicles increased rapidly 10 to 20 d after heading<br />

in Fujisaka 5, but remained unchanged in FS1 during maturity.<br />

The dry-matter partitioning ratios of panicles at maturity<br />

were 9% and 40% in FS1 and Fujisaka 5, respectively.<br />

Though the dry weight of leaf blades decreased after heading<br />

in both lines, the decrease in FS1 was slower than that in<br />

Fujisaka 5. The dry weight of stems in Fujisaka 5 decreased at<br />

14 d after heading with the rapid increase in panicle weight,<br />

and remained steady during the late ripening stage. On the other<br />

hand, the stem dry weight in FS1 continued to increase until<br />

28 d after heading and then decreased rapidly with the<br />

appearence of late tillers. Stems occupied more than half of<br />

the total dry matter in both lines at heading. During the ripening<br />

stage, the dry-matter partitioning ratio of stems decreased<br />

to 34% at maturity with the increase in panicle weight in<br />

Fujisaka 5, but that in FS1 increased to 62% until 4 wk after<br />

heading and still remained at 43% at maturity. The dry weight<br />

of late tillers increased after 28 d of heading and occupied<br />

24% of the total dry weight at maturity in FS1. Root dry weight<br />

of Fujisaka 5 decreased during the ripening stage, but that of<br />

FS1 remained steady or increased slightly.<br />

Changes in carbon and nitrogen contents<br />

of each organ<br />

Average carbon contents in a whole plant of both lines were<br />

42–43% during the ripening stage. While t<strong>here</strong> were no significant<br />

differences in carbon contents of each organ between<br />

FS1 and Fujisaka 5 at heading, the differences in leaf blades,<br />

stems, and panicles were significant at maturity. However, the<br />

changes in carbon accumulation of each organ showed a trend<br />

similar to that of the dry weights in both lines because the<br />

difference in the content between lines and the changes during<br />

ripening were small.<br />

Average nitrogen contents in a whole plant were 1.0%<br />

and 1.2% at heading and those decreased to 0.6% and 0.9% at<br />

maturity in FS1 and Fujisaka 5, respectively. The nitrogen contents<br />

in leaf blades of both lines were 2.5–2.7% at heading,<br />

and decreased relatively slower in FS1 than in Fujisaka 5, so<br />

those at maturity were 1.8% and 1.4% in FS1 and Fujisaka 5,<br />

respectively. Though t<strong>here</strong> were no significant differences in<br />

the nitrogen content of each organ between FS1 and Fujisaka<br />

5 at heading, the differences were significant in every organ at<br />

maturity. Particularly, nitrogen contents of panicles and stems<br />

were significantly lower in FS1 than in Fujisaka 5.<br />

Changes in nitrogen accumulation<br />

and distribution of each organ<br />

Total nitrogen accumulation in a whole plant did not increase<br />

during the ripening stage and the total amounts per plant were<br />

439 mg in FS1 and 504 mg in Fujisaka 5 at maturity (Fig. 2).<br />

After heading, the amount of nitrogen in leaf blades decreased<br />

rapidly and that in panicles increased, which occupied above<br />

a half of the whole-plant nitrogen 21 d after heading in Fujisaka<br />

Session 4: Improving rice yield potential 143


Nitrogen (g plant –1 )<br />

0.6<br />

0.5<br />

Root<br />

Culm + leaf sheath<br />

Leaf blade<br />

Dead leaf<br />

Panicle<br />

Late tiller<br />

FS1<br />

Fujisaka 5<br />

0.4<br />

0.3<br />

0.2<br />

0.1<br />

0.0<br />

–10 0 7 14 21 28 35 42 –10 0 7 14 21 28 35 42<br />

Days after heading<br />

Days after heading<br />

Fig. 2. Changes in nitrogen accumulation of each organ in FS1 and Fujisaka 5 during the ripening stage.<br />

5. The partitioning ratio to stems also declined rapidly during<br />

the period from 7 to 21 d after heading. On the contrary, in<br />

FS1, the decline in nitrogen partitioning ratio to leaf blades<br />

was slower, and the partitioning ratio to panicles was almost<br />

steady. The nitrogen partitioning ratio to stems increased gradually<br />

until 21 d after heading, and then decreased rapidly to<br />

21% at maturity with the apperance of late tillers. The partitioning<br />

ratio to roots decreased with ripening in Fujisaka 5,<br />

but that of FS1 remained comparatively higher. While panicles<br />

accumulated 55% of the total nitrogen in Fujisaka 5 at maturity,<br />

late tillers were the largest sink organ for nitrogen in FS1,<br />

occupying 32% of the total nitrogen of a whole plant.<br />

Conclusions<br />

FS1 did not decrease dry-matter production irrespective of the<br />

loss of sink function of panicles. The slower decrease in nitrogen<br />

concentration in leaf blades caused retarded leaf senescence<br />

and the maintenance of relatively higher photosynthetic<br />

activity in FS1 (Kato et al 2004). Its vegetative organs such as<br />

culms, leaf sheaths, late tillers, and roots substituted for panicles<br />

as photosynthate and nitrogen sinks. The results of the changes<br />

in dry-matter and nitrogen distribution indicated that, in the<br />

final ripening stage, the carbohydrate and nitrogen accumulated<br />

in stems rapidly translocated to late tillers. This unique<br />

pattern of dry-matter and nitrogen distribution retarded the<br />

senescence of leaves and the decline in leaf photosynthesis,<br />

and then contributed to the increase in dry-matter production<br />

during the ripening stage. FS1 is considered to have larger<br />

amounts of carbon and nitrogen in stems than Fujisaka 5. This<br />

suggests the possibility of using FS1 for biological production<br />

as a forage crop. However, the sink capacity for nitrogen in<br />

panicles was so strong that vegetative organs such as stems<br />

and late tillers could not fulfill it. The difference between the<br />

dry-weight and nitrogen distribution patterns in organs caused<br />

the change in carbon-nitrogen balance during the ripening stage.<br />

The present results on dry-matter production and nitrogen accumulation<br />

were obtained from the limited conditions for root<br />

growth and nitrogen nutrition in pots. Further field experiments<br />

under higher nitrogen nutrition levels are needed to evaluate<br />

the potential biomass productivity and nitrogen accumulation<br />

of this female-sterile line of rice.<br />

References<br />

Kato M, Kobayashi K, Ogiso E, Yokoo M. 2004. Photosynthesis<br />

and dry-matter production during ripening stage in a femalesterile<br />

line of rice. Plant Prod. Sci. 7:184-188.<br />

Yokoo M. 1984. Female sterility in an Indica-Japonica cross of rice.<br />

Jpn. J. Breed. 34:219-227.<br />

Notes<br />

Authors’ address: Graduate School of Life and Environmental Sciences,<br />

University of Tsukuba, e-mail:<br />

katomo@sakura.cc.tsukuba.ac.jp.<br />

144 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Cytokinin as a causal factor of varietal differences<br />

in the reduction in leaf level of ribulose-1,5-bisphosphate<br />

carboxylase/oxygenase during senescence in rice plants<br />

Taiichiro Ookawa, Yukiko Naruoka, Ayumi Sayama, and Tadashi Hirasawa<br />

Dry matter production and yield are higher in rice cultivar<br />

Akenohoshi than in cultivar Nipponbare, primarily because of<br />

a smaller decrease in the rate of photosynthesis during the ripening<br />

stage of Akenohoshi (Jiang et al 1988). The rate of<br />

photosynthesis and nitrogen content during senescence are both<br />

closely correlated with leaf levels of ribulose-1,5-bisphosphate<br />

carboxylase/oxygenase (Rubisco). During leaf senescence,<br />

Akenohoshi shows a smaller decrease in levels of Rubisco than<br />

Nipponbare, and we have previously demonstrated that<br />

Akenohoshi maintains larger amounts of nitrogen in leaves<br />

during ripening. This may account for the differences in the<br />

ability of these two cultivars to maintain high leaf levels of<br />

Rubisco (Ookawa et al 2003). The high leaf nitrogen content<br />

in Akenohoshi results from both greater total accumulation of<br />

nitrogen and greater partitioning of nitrogen to leaves.<br />

It was also observed that larger amounts of cytokinin<br />

were transported from the roots to the aboveground parts of<br />

the plant during the ripening stage by Akenohoshi and<br />

Nipponbare (Soejima et al 1995). Cytokinin can delay senescence<br />

and recent studies have illustrated the importance of<br />

cytokinin in the control of senescence (Gan and Amasino 1995).<br />

Cytokinins might also contribute to the maintenance of high<br />

Rubisco content. However, it remains to be determined whether<br />

cytokinin suppresses a decline in Rubisco content.<br />

Several studies have reported that cytokinin can induce<br />

the expression of photosynthetic genes and promote protein<br />

synthesis. It can be assumed that suppressing the decrease in<br />

accumulation of Rubisco gene transcripts by cytokinin results<br />

in the maintenance of high Rubisco levels during leaf senescence.<br />

Cytokinin also affects nitrogen partitioning in the whole<br />

plant (Jordi et al 2000). High nitrogen partitioning to leaves<br />

by cytokinin probably results in the maintenance of high<br />

Rubisco levels during senescence.<br />

In the following experiments, our main aims were t<strong>here</strong>fore<br />

(1) to compare the levels of Rubisco, nitrogen, and rbcL<br />

and rbcS transcripts between Nipponbare and Akenohoshi, (2)<br />

to analyze the effects of exogenous cytokinin on levels of<br />

Rubisco, nitrogen, and rbcL and rbcS transcripts in leaves of<br />

rice during the ripening stage, and (3) to analyze the effects of<br />

exogenous cytokinin on the nitrogen content of leaves by determining<br />

nitrogen absorption and partitioning to various organs<br />

in the whole plant.<br />

Methods<br />

<strong>Rice</strong> seedlings (Oryza sativa L., cvs. Nipponbare and<br />

Akenohoshi) were transplanted to Wagner pots (1/2,000 a)<br />

filled with soil on 27 May. In this study, Nipponbare plants<br />

were treated with additional nitrogen fertilizer and cytokinin.<br />

Ammonium sulfate was applied to some pots on 1 September<br />

at a dose of 10 g per pot as additional nitrogen fertilizer (NF).<br />

For the treatment with cytokinin, 30 mL of a 10 -4 M solution<br />

of 6-benzylaminopurine (BA), containing 0.05% Tween 20 as<br />

a surfactant, was sprayed on the aboveground parts of each<br />

hill at 2-day intervals from 5 September. Levels of Rubisco<br />

and nitrogen were determined in the same flag leaf of the main<br />

stem. Levels of Rubisco were determined by the single radial<br />

immunodiffusion method. Nitrogen was quantitated using a<br />

CN analyzer (MT-600, Yanaco Inc., Kyoto, Japan). For quantification<br />

of mRNA, the flag leaves on the main culms were<br />

collected between 1000 and 1100 on a clear day and were immediately<br />

frozen in liquid nitrogen. Levels of rbcL and rbcS<br />

mRNA were determined by Northern blotting analysis.<br />

Comparison of Rubisco, nitrogen, and rbcL<br />

and rbcS mRNA levels in leaves<br />

Changes in Rubisco and rbcL and rbcS mRNA levels in leaves<br />

during ripening were compared between the two cultivars. At<br />

the heading stage, t<strong>here</strong> were no differences between the two<br />

cultivars, but, after heading, levels of Rubisco and rbcL and<br />

rbcS mRNA remained higher in Akenohoshi than in Nipponbare<br />

(Fig. 1A, C, and D).<br />

The nitrogen content in flag leaves was higher in<br />

Nipponbare and Akenohoshi at the heading stage. After heading,<br />

the nitrogen content decreased more slowly in Akenohoshi<br />

than in Nipponbare (Fig. 1B).<br />

Effects of treatment with 6-benzylaminopurine<br />

and nitrogen fertilizer on Rubisco, nitrogen, and rbcL<br />

and rbcS mRNA levels in leaves<br />

In Nipponbare controls, Rubisco content in flag leaves decreased<br />

with time after heading. Rubisco content remained<br />

substantially higher in plants treated with NF or BA in<br />

Nipponbare than in the controls (Fig. 1A). Levels of rbcL and<br />

rbcS mRNA decreased with time in the controls. However,<br />

levels remained high in plants treated with NF or BA during<br />

ripening (Fig. 1C, D).<br />

In the controls, nitrogen content declined with time in<br />

flag leaves. In contrast, nitrogen content decreased but remained<br />

relatively high during ripening when compared with<br />

the controls (Fig. 1B).<br />

Session 4: Improving rice yield potential 145


Rubisco content (g m –2 )<br />

Nitrogen content (g m –2 )<br />

3<br />

A 1.5<br />

c<br />

B<br />

2<br />

c<br />

c<br />

b<br />

a<br />

b<br />

b<br />

a<br />

a<br />

1.0<br />

a<br />

c<br />

b<br />

c<br />

b<br />

ab<br />

a<br />

1<br />

0<br />

Control (NI)<br />

BA (NI)<br />

NF (NI)<br />

Akenohoshi<br />

0.5<br />

0<br />

Relative level of rbcL mRNA (%)<br />

Relative level of rbcS mRNA (%)<br />

120<br />

100<br />

80<br />

60<br />

40<br />

20<br />

a<br />

b<br />

b<br />

b<br />

a<br />

a<br />

a<br />

C<br />

120<br />

100<br />

80<br />

60<br />

40<br />

20<br />

c<br />

c<br />

b<br />

a<br />

c<br />

bc<br />

b<br />

a<br />

D<br />

0<br />

31 Aug 10 Sep 20 Sep 30 Sep<br />

Date<br />

0<br />

31 Aug 10 Sep 20 Sep 30 Sep<br />

Fig. 1. Effects of 6-benzylaminopurine (BA) and additional nitrogen fertilizer (NF) application on the Rubisco<br />

content (A), nitrogen content (B), and relative levels of rbcL mRNA (C) and rbcS mRNA (D) in flag leaves of<br />

Nipponbare (NI). The plants of Akenohoshi were grown in the same conditions as the control for Nipponbare.<br />

Vertical bars represent standard deviations (n = 3). Symbols with different letters are significantly different<br />

at the 5% level (LSD).<br />

Date<br />

Relationships between Rubisco content, levels of rbcL<br />

and rbcS mRNA, and nitrogen content<br />

The relationships between Rubisco content, levels of rbcL and<br />

rbcS mRNA, and nitrogen content were compared among the<br />

controls, BA- and NF-treated Nipponbare plants, and<br />

Akenohoshi plants. T<strong>here</strong> were close relationships between<br />

Rubisco content and levels of rbcL and rbcS mRNA, irrespective<br />

of treatment and cultivar (rbcL: r = 0.90, rbcS: r = 0.98).<br />

In previous studies, cytokinin promoted the expression of genes<br />

for photosynthetic proteins by increasing transcription (Suzuki<br />

et al 1994). T<strong>here</strong>fore, cytokinin likely also contributed to the<br />

maintenance of high leaf levels of Rubisco in NF- and BAtreated<br />

plants.<br />

Over a wide range of nitrogen contents, t<strong>here</strong> was also a<br />

close positive correlation between Rubisco content and nitrogen<br />

content (r = 0.80). T<strong>here</strong> was also a close correlation between<br />

nitrogen content and levels of both rbcL and rbcS mRNA<br />

(rbcL: r = 0.74, rbcS: r = 0.85).<br />

Effects of BA and NF on accumulation<br />

and partitioning of nitrogen<br />

The high leaf nitrogen content was maintained not only in NFtreated<br />

Nipponbare plants but also in BA-treated Nipponbare<br />

plants. The total amount of accumulated nitrogen during the<br />

late-ripening stage was much larger after NF treatment when<br />

compared with the controls (Table 1), and the partitioning of<br />

nitrogen to leaves increased significantly as a result of NF treatment.<br />

T<strong>here</strong>fore, the maintenance of high leaf nitrogen content<br />

in NF-treated plants resulted not only from an increase in<br />

total nitrogen accumulation by the entire plant but also from<br />

an increase in nitrogen partitioning to leaves. T<strong>here</strong> was no<br />

difference in terms of the increase in nitrogen whole-plant content<br />

between BA-treated plants and controls from the heading<br />

stage to the late-ripening stage. The partitioning of nitrogen to<br />

leaves at the late-ripening stage was considerably higher in<br />

BA-treated plants than in the controls, but less nitrogen was<br />

partitioned to panicles in the former than in the latter (Table<br />

1). These results showed that maintenance of high leaf nitrogen<br />

content in BA-treated plants was caused by an increase in<br />

nitrogen partitioning to leaves and a decrease in partitioning<br />

146 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. Comparisons of nitrogen content, changes in nitrogen content, and nitrogen partitioning to various<br />

organs in entire plants. a<br />

Nitrogen content (mg hill –1 ) Nitrogen partitioning (%)<br />

Changes in nitrogen<br />

Organ Heading Late ripening content (mg hill –1 ) Heading Late ripening<br />

(31 Aug) (25 Sep) (31 Aug) (25 Sep)<br />

Whole plant<br />

Control 592.4 ± 35.1 635.7 ± 19.3 a 43.3 100 100<br />

BA – 653.9 ± 15.8 a 61.5 – 100<br />

NF – 1,024.6 ± 6.2 b 432.2 – 100<br />

Leaves<br />

Control 292.4 ± 12.1 142.9 ± 4.9 a –149.5 49.4 ± 1.0 22.6 ± 0.3 a<br />

BA – 238.7 ± 3.2 b –53.7 – 36.5 ± 1.3 b<br />

NF – 307.2 ± 3.5 c 14.8 – 30.0 ± 0.6 c<br />

Culms + leaf sheaths<br />

Control 202.0 ± 18.2 114.1 ± 3.1 a –87.9 34.0 ± 1.0 17.9 ± 0.5 a<br />

BA – 115.2 ± 0.3 a –86.8 – 17.6 ± 0.4 a<br />

NF – 202.3 ± 12.2 b 0.3 – 19.7 ± 1.0 b<br />

Panicles<br />

Control 58.2 ± 1.6 328.7 ± 8.9 a 270.5 9.8 ± 0.4 51.5 ± 0.7 a<br />

BA – 259.7 ± 18.8 b 201.5 – 39.8 ± 2.0 b<br />

NF – 459.4 ± 3.1 c 401.2 – 44.8 ± 0.5 c<br />

Roots<br />

Control 39.8 ± 4.2 50.1 ± 7.4 a 10.3 6.8 ± 0.4 8.0 ± 1.0 a<br />

BA – 40.3 ± 1.6 b 0.5 – 6.2 ± 0.4 b<br />

NF – 55.7 ± 0.6 a 15.9 – 5.5 ± 0.0 b<br />

a Data represent means ± standard deviations of results from three replicates. Nitrogen partitioning is expressed as the nitrogen content<br />

of the indicated organs as a percentage of the total nitrogen content of the whole plant. Means followed by different letters are<br />

significantly different at the 5% level of probability (LSD).<br />

to panicles, rather than an increase in whole-plant accumulation<br />

of nitrogen.<br />

Jordi et al (2000) used a 15 N tracer to investigate patterns<br />

of nitrogen partitioning in transgenic tobacco plants, in<br />

which the gene for cytokinin-synthetic enzyme,<br />

isopentenyltransferase, was specifically expressed in senescent<br />

leaves. They found that high levels of Rubisco were maintained,<br />

reflecting the partitioning of a large amount of 15 N to leaves. A<br />

large amount of nitrogen was partitioned to leaves in<br />

Akenohoshi, with a high cytokinin activity in xylem sap compared<br />

with that in Nipponbare (Ookawa et al 2003). These<br />

results indicate that cytokinin has an effect on nitrogen partitioning.<br />

Conclusions<br />

Cytokinin affects both the synthesis of Rubisco in leaves and<br />

the partitioning of nitrogen to leaves in rice plants during ripening.<br />

This suggests that cytokinin causes the differences in<br />

Rubisco reduction during senescence, thus resulting in differences<br />

in the reduction of photosynthesis between Akenohoshi<br />

and Nipponbare. T<strong>here</strong>fore, capacity of the roots for cytokinin<br />

synthesis is an important determinant of the ability of rice<br />

plants to maintain photosynthetic rate in leaves during ripening<br />

in high-yielding rice cultivars.<br />

References<br />

Gan S, Amasino RM. 1995. Inhibition of leaf senescence by<br />

autoregulated production of cytokinin. Science 270:1986-<br />

1987.<br />

Jiang CZ, Hirasawa T, Ishihara K. 1988. Physiological and ecological<br />

characteristics of high yielding varieties in rice plants: leaf<br />

photosynthetic rates. Jpn. J. Crop Sci. 57:139-145.<br />

Jordi W, Schapendonk A, Davelaar E, Stoopen GM, Pot CS, De Visser<br />

R, Rhijn JA, Gan S, Amasino RM. 2000. Increased cytokinin<br />

levels in transgenic P SAG12 -IPT tobacco plants have large direct<br />

and indirect effects on leaf senescence, photosynthesis<br />

and N partitioning. Plant Cell Environ. 23:279-289.<br />

Ookawa T, Naruoka U, Yamazaki T, Suga J, Hirasawa T. 2003. A<br />

comparison of the accumulation and partitioning of nitrogen<br />

in plants between two rice cultivars, Akenohoshi and<br />

Nipponbare, at the ripening stage. Plant Prod. Sci. 6:172-178.<br />

Soejima H, Sugiyama T, Ishihara K. 1995. Changes in the chlorophyll<br />

contents of leaves and in levels of cytokinins in root<br />

exudates during ripening of rice cultivars Nipponbare and<br />

Akenohoshi. Plant Cell Physiol. 36:1105-1114.<br />

Suzuki I, Cretin C, Omata T, Sugiyama T. 1994. Transcriptional and<br />

posttranscriptional regulation of nitrogen-responding expression<br />

of phosphoenolpyruvate carboxylase gene in maize. Plant<br />

Physiol. 105:1223-1229.<br />

Notes<br />

Authors’ address: Tokyo University of Agriculture and Technology,<br />

e-mail: ookawa@cc.tuat.ac.jp.<br />

Session 4: Improving rice yield potential 147


Measurement and evaluation of rice plant type<br />

by means of an image analysis method and a 3-D digitizer<br />

Masaaki Oka and Takashi Ogawa<br />

In the breeding of high-yielding rice varieties, plant type is<br />

very important. Plant type is closely related to sunlight-receiving<br />

efficiency. The plant type of rice has changed over time<br />

and many varieties with varied plant type have been developed<br />

recently to achieve higher yield. To advance the research<br />

on high-yielding rice breeding further, new methods for measuring<br />

plant type are indispensable. A method for evaluating<br />

what kind of plant type is ideal is also required.<br />

We developed a method for measuring rice plant type<br />

by means of image analysis and a 3-D digitizer. The system<br />

using a 3-D digitizer can also calculate the light-receiving leaf<br />

area of a rice plant. By using this method, we compared the<br />

characteristics of plant type and the light-receiving efficiency<br />

of some rice varieties. (All computer software in this experiment<br />

was written in Microsoft VisualBasic.net.)<br />

Calculation<br />

Koshihikari-ah01 Threshold value 126<br />

Image analysis of plant type<br />

Materials and methods<br />

Fifteen rice varieties (three popular varieties, five high-yielding<br />

varieties, two hybrid rice varieties bred in Japan, four new<br />

plant type—NPT—lines bred by <strong>IRRI</strong>, and a Korean variety)<br />

were cultivated in a paddy field. The side-view photographs<br />

of a single rice plant were taken before heading, at heading<br />

time, and at the ripening stage. After changing these image<br />

data to a binary image (Fig. 1, upper right), the two-dimensional<br />

distribution of aerial part density was calculated (lower<br />

left). To compare the characteristics of plant type, the following<br />

numerical factors were obtained (lower right):<br />

Results<br />

Factor 1: Plant height<br />

Factor 2: Two-dimensional area of the plant on a binary<br />

image<br />

Factor 3: (Height at which the plant area is divided into<br />

two equally)/(Plant height)<br />

Factor 4: (Horizontal distance between the center axis<br />

and the portion in which 90% of the plant area is contained)/(Plant<br />

height)<br />

At the ripening stage, most NPT lines (IR65600-127-6-2-3,<br />

IR71218-5-2-1, etc.) showed lower plant height and higher<br />

values of Factors 3 and 4. New high-yielding varieties bred in<br />

Japan (Fukuhibiki, Habataki, etc.) showed a similar tendency.<br />

In contrast, high-yielding hybrid rice bred in Japan (Mitsuhikari<br />

2003 and 2005) with a longer culm showed a higher value of<br />

Factor 3 and lower value of Factor 4. Both Factor 3 and 4<br />

Factor 1 124<br />

Factor 2 2108.617<br />

Factor 3 0.5<br />

Factor 4 0.1290323<br />

Fig. 1. Image analysis of the plant type of Koshihikari at the ripening<br />

stage. Binary image (upper right), the distribution of plant density<br />

(lower left), and calculated factors 1–4 (lower right).<br />

values of popular varieties in Japan (Hitomebore, etc.) were<br />

lower. Milyang 23, a Korean variety, bred from a cross between<br />

japonica and indica rice, showed a value near the middle<br />

of the new high-yielding varieties and popular varieties (Oka<br />

and Ogawa 2004).<br />

Measuring plant type by using a 3-D digitizer<br />

Materials and methods<br />

We used an electromagnetic 3-D digitizer to measure a detailed<br />

solid structure of rice plant type. Using a 3-D digitizer,<br />

three-dimensional coordinates of points on the edge of all<br />

leaves of the rice plant (nine points per leaf) were obtained.<br />

One plant had about 100–150 leaves and it took 1.0 to 1.5<br />

hours to measure all the leaves of one plant. After a single leaf<br />

was divided into 13 triangles by using the coordinate data, the<br />

area, the angle to the level surface, and the coordinate of the<br />

center of gravity of each triangle were calculated. Total leaf<br />

area and averaged leaf angle were calculated in each space<br />

divided at intervals of 10 cm horizontally and vertically, and<br />

the spatial distribution of leaf area and leaf angle was drawn<br />

148 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Calculation<br />

Total leaf area (a): 2,570 cm 2<br />

Leaf area receiving direct sunlight (b) 475 cm 2<br />

Percentage of (b) to (a): 18%<br />

South<br />

Fig. 2. The calculation of leaf area receiving direct sunlight of Hitomebore about 20 days before<br />

heading. The canopy consists of six plants and the target plant is in the center of the back row. The<br />

light-receiving triangles and the shaded triangles are drawn by thick solid lines and thin dotted lines,<br />

respectively.<br />

by computer graphics. The characteristics of leaf distribution<br />

of three rice varieties (Hitomebore, Milyang 23, and<br />

Mitsuhikari 2005) were compared by this method.<br />

Results<br />

The differences of leaf distribution among three varieties were<br />

not clear before heading, but, as the developmental stage advanced,<br />

the characteristics of leaf distribution became more<br />

prominent. At the ripening stage, Hitomebore had many slanting<br />

leaves that protruded outward in the middle height. In<br />

Milyang 23, leaves were more erect at the upper height than in<br />

Hitomebore. Mitsuhikari 2005 was taller than the others, and<br />

its leaves stood straight at about every height and were densely<br />

distributed near the vertical center line of the plant (Oka et al<br />

2003).<br />

Calculation of light-receiving efficiency<br />

It is thought that the rice plant with ideal plant type has a larger<br />

area of leaves that receive direct sunlight and shows a higher<br />

percentage of sunny leaf area to total leaf area. To evaluate the<br />

light-receiving efficiency of the rice plant, we made computer<br />

software to calculate the area of light-receiving leaves when<br />

the sun rose at any angle.<br />

Light-receiving leaf area of an isolated single plant<br />

The three-dimensional structure of a rice plant was rotated in<br />

the direction that was the viewpoint of the sun, and we inves-<br />

tigated whether each triangle into which a leaf was divided<br />

received direct sunlight or not. When the center of gravity of<br />

one triangle was in the inside of the other triangle, we judged<br />

that they overlapped each other. In addition, the triangle near<br />

the sun was recorded as sunny and the other was recorded as<br />

shade. After this calculation was performed for the combination<br />

of all triangles, the percentage of leaf area receiving direct<br />

sunlight was determined.<br />

Light-receiving leaf area of the rice canopy<br />

In our experimental paddy field, rice plants were planted at 24<br />

by 24 cm. The three-dimensional coordinates of the leaves of<br />

five plants that were placed at 24-cm intervals (east, southeast,<br />

south, southwest, and west of the target plant) were calculated.<br />

By examining the mutual shading among all triangles<br />

of leaves of these five plants, the light-receiving efficiency of<br />

the target plant was evaluated by the same method as for an<br />

isolated single plant.<br />

The light-receiving efficiencies of three rice varieties<br />

were compared. The result for Hitomebore before heading is<br />

shown in Figure 2. When the angle of elevation of the sun was<br />

70 degrees and the azimuth angle was 15 degrees from the<br />

south to the east, the leaf area receiving direct sunlight was<br />

475 cm 2 and the percentage to the total leaf area was 18%. At<br />

the same angle of the sun, the percentages of Milyang 23 and<br />

Mitsuhikari 2005 were 19% and 9%, respectively.<br />

Session 4: Improving rice yield potential 149


Conclusions<br />

By using the image analysis method, the rough characteristics<br />

of plant type of many rice varieties can be recognized in a<br />

short time. As the calculation speed of the computer became<br />

faster, it became possible to do image analysis easily using a<br />

personal computer. We are making the database of a rice profile<br />

image now. By combining this database and the image<br />

analysis method in this experiment, we will be able to develop<br />

an epochal analysis system for the rice plant type.<br />

The detailed solid structure of the rice plant can be measured<br />

by a 3-D digitizer. In addition, the area of light-receiving<br />

leaves can be calculated. The light-receiving efficiency of<br />

a rice plant can be evaluated by performing calculations of<br />

sunny leaf area of a plant irradiated from various directions.<br />

This system can also calculate the light-receiving efficiency<br />

of a virtual rice plant type, for example, a plant whose leaf<br />

angle, leaf shape, or internode length of an actual plant was<br />

changed. The ideal rice plant type will be found by repeating<br />

Wrap-up of Session 4<br />

this simulation experiment. The target of our research is an<br />

automatic evaluation system on rice plant type by using new<br />

measurement techniques, information technology, and simulation<br />

experiments.<br />

References<br />

Oka M, Yamauchi M, Imaizumi Y. 2003. Measurement of spatial<br />

leaf distribution of three rice varieties by means of 3-D digitizer.<br />

Breed. Sci. 5(supple. 1):204. (In Japanese.)<br />

Oka M, Ogawa T. 2004. Characteristics of plant type of some new<br />

high-yielding rice varieties measured by computer image<br />

analysis. Breed. Sci. 6(supple. 1):83. (In Japanese.)<br />

Notes<br />

Authors’ address: Miyagi University of Education, e-<br />

mail:maoka@staff.miyakyo-u.ac.jp.<br />

Improving rice yield potential is a persistent research target for<br />

food security. Its significance is magnifying with the increasing<br />

need for improving the efficiency in the use of land, water, and<br />

other natural resources, and labor for rice culture. With the<br />

completion of the rice genome sequence, more tools are becoming<br />

available for understanding the genetic control of plant<br />

functions. Considering this background, this session had two major<br />

aims:<br />

1. To elucidate the key physiological and morphological<br />

traits to be targeted to improve yield potential by summarizing<br />

research carried out after the Green Revolution.<br />

2. To characterize recently developed high-yielding genetic<br />

resources, including hybrid rice, and to evaluate the<br />

possible contribution of molecular breeding to the improvement<br />

of rice yield potential.<br />

Six papers were presented on physiological processes that<br />

govern rice yield potential and five papers on breeding for increased<br />

rice yield potential. The following key points and future<br />

prospects can be extracted from the papers presented:<br />

1. A balanced increase in source and sink capacity is the<br />

key to enhancing rice yield potential since it is obvious<br />

that source and sink capacity interact in determining<br />

yield (P.K. Mahapatra, S. Peng). Understanding and<br />

quantifying sink strength are a major challenge in explaining<br />

the differences among genotypes in<br />

remobilization efficiency, grain filling, and harvest index.<br />

High remobilization ability was shown to improve yield,<br />

harvest index, and N-use efficiency in new japonica variety<br />

Akita-63, with large grain size (T. Mae). It is expected<br />

that recent progress in understanding carbon<br />

metabolism related to grain filling at the molecular level<br />

will help to manipulate sink strength (R. Ohsugi).<br />

2. It is clear that enhancing biomass production without<br />

reducing harvest index would be an effective way to improve<br />

rice yield potential. The increase in biomass production<br />

will largely depend on improving radiation-use<br />

efficiency and canopy photosynthetic rate. Improving<br />

Rubisco efficiency would have great importance as a<br />

prospect for enhancing N-use efficiency (A. Makino).<br />

The introduction of C 4 photosynthesis is a challenging<br />

option (J. Sheehy). The results of experiments under<br />

elevated CO 2 conditions suggested that increased<br />

canopy photosynthesis capacity increased biomass and<br />

yield, but to a lesser extent than single-leaf photosynthesis<br />

(T. Hasegawa). The relationship among leaf- and<br />

canopy-level gas exchange and crop growth needs to<br />

be studied. During the entire crop-growing season, enhancement<br />

of biomass production during the ripening<br />

phase would be most effective in improving rice yield<br />

potential, followed by high biomass production during<br />

the reproductive growth stage. Significant genotypic<br />

variation has been found in biomass production at these<br />

stages. Further understanding is needed on the mechanisms<br />

through which sink strength affects source-related<br />

ability, for example, photosynthesis and stomatal<br />

conductivity, and biomass production after the reproductive<br />

stage.<br />

3. The interaction of yield determination with environment<br />

needs further attention. The effectiveness of traits should<br />

be evaluated in adaptability to different environments.<br />

For example, breeding for large panicle size with more<br />

150 <strong>Rice</strong> is life: scientific perspectives for the 21st century


spikelets per panicle has proven to be effective in increasing<br />

rice yield potential in temperate and subtropical<br />

regions. However, the following questions remain<br />

unanswered: (1) Does a panicle-weight-type rice variety<br />

perform well in the tropics (2) Can a panicle-weighttype<br />

rice variety achieve good grain filling without using<br />

heterosis (S. Peng). High radiation in the dry season<br />

under tropical conditions causes photoinhibition and<br />

lower radiation-use efficiency (E. Murchie). Adaptation<br />

to tropical/temperate conditions or dry-/wet-season conditions<br />

must be considered. Exhaustive results from QTL<br />

analyses for yield traits indicated a general tendency<br />

that each of the QTLs for yield traits made a rather small<br />

contribution, with a large interaction of environmental<br />

and genetic factors (Z. Li). A statistical tool for QTL ×<br />

environment analysis should be useful for figuring out<br />

the adaptability of traits and solving complexity in markerassisted<br />

selection for yield under various conditions.<br />

4. The secondary improvement of new plant type (NPT)<br />

tropical japonica by hybridizing indica and tropical<br />

japonica types steadily showed a higher yield level than<br />

indica check cultivars but a slightly lower yield than hybrids.<br />

Further potential was suggested by the concurrent<br />

improvement of several traits of the NPT.<br />

5. T<strong>here</strong> is no question that hybrid rice technology has<br />

contributed to the increase in rice yield potential. Recent<br />

progress in China for hybrid rice breeding was reviewed<br />

(Zhong et al). Several new hybrids, called “super”<br />

hybrids, released starting in the late 1990s attained<br />

a yield increase of 10–15% over that of previous<br />

hybrids, indicating further potential for genetic improvement.<br />

A commercial hybrid in Japan, Mituhikari, achieved<br />

an acceptable level of eating quality in cooked rice as<br />

well as a yield increase of 20–30%. This attempt indicated<br />

a way toward high-productivity rice farming with<br />

an assured marketability in the gray area of the rice<br />

industry in industrialized countries (A. Nakamura).<br />

6. Further improvement in rice yield potential will continue<br />

to rely on conventional cross-breeding approaches.<br />

Ideotype breeding, hybrid rice breeding, and the modern<br />

biotechnology approach are powerful supplements<br />

to the empirical breeding approach in crop improvement<br />

for yield potential. An efficient collaboration mechanism<br />

between physiology and breeding is essential in these<br />

efforts.<br />

Session 4: Improving rice yield potential 151


SESSION 5<br />

Broadening the gene pool<br />

and exploiting heterosis in cultivated rice<br />

CONVENER: Y. Fukuta (JIRCAS/<strong>IRRI</strong>)<br />

CO-CONVENERS: D. Mackill (<strong>IRRI</strong>) and R. Ikeda (JIRCAS)


Developing aerobic rice in Brazil<br />

B. da S. Pinheiro, E. da M. de Castro, O.P. de Moraes, and F. Breseghello<br />

In the mid-1980s, upland rice varieties of tropical japonica<br />

extraction attained an area bigger than 4.5 million ha under<br />

Brazilian savannas. Afterward, crop area decreased gradually<br />

and markedly, attaining only 1.8 million ha in 2003. However,<br />

production has not declined at the same level because average<br />

yield doubled in the period 1986-2003, rising from 1.1 to 1.9<br />

t ha –1 . This was due to both crop migration toward more favored<br />

areas in rain distribution, and the adoption of modernplant-type<br />

varieties, tropical japonica × indica derivatives. The<br />

impact of improved-plant-type varieties and associated technologies<br />

in the favored localities of the savanna region put<br />

forward a new concept of upland rice, leading to a new denomination—aerobic<br />

rice. The shift in breeding strategies over<br />

time and the genetic gain attained in the latter part of the 1990s<br />

are presented and discussed in this paper.<br />

The National Upland <strong>Rice</strong> Breeding Program<br />

Since its inception in 1974, the former National <strong>Research</strong> Center<br />

for <strong>Rice</strong> and Beans (CNPAF) of Embrapa, located in Goiás,<br />

has been developing and coordinating the National Upland <strong>Rice</strong><br />

Breeding Program. The objectives and priorities of the program<br />

have changed from time to time to cope with the alterations<br />

in geographic distribution of the crop, cropping system,<br />

and consumers’ taste for the product. According to Pinheiro<br />

(2003), it can be divided into three distinct periods: (1) phase<br />

1, 1975-85, higher emphasis on drought tolerance, blast resistance,<br />

and yield stability, targeting exclusively the unfavored<br />

savanna conditions; (2) phase 2, 1985-90, breeding strategy<br />

expanded to include selection for high yield potential, targeting<br />

favorable savanna conditions as well; (3) phase 3, 1990 to<br />

the present, higher emphasis on blast resistance, grain appearance,<br />

and yield potential, targeting mainly favored conditions.<br />

Drought was a strong priority during phase 1 of the breeding<br />

program, which relied on progenitors of the tropical<br />

japonica group, from both national and African origin, but will<br />

not be covered in this paper. After the studies of Steinmetz et<br />

al (1988a,b), the breeding strategy was expanded to obtain<br />

genotypes to be grown under supplementary irrigation and in<br />

favored microregions for rainfall distribution during phase 2.<br />

Progenitors of the indica group were involved in crosses, segregating<br />

generations were evaluated under supplementary irrigation,<br />

and advanced lines tested exclusively in favorable<br />

locations. A noticeable move from the frontier land to more<br />

favored areas for water distribution led to a decrease in the<br />

priority for drought tolerance in phase 3. Currently, drought<br />

evaluation results do not restrict the release of aerobic rice<br />

varieties.<br />

Even with alterations in the program objectives and plant<br />

ideotype, some basic strategies have been maintained for a<br />

long time. To create plant populations to be used in the subsequent<br />

steps of the program, recurrent selection schemes are<br />

widely used. Progenitor combination capacity is evaluated to<br />

obtain more successful crosses. Pure lines are developed<br />

through population advances by mass selection within families.<br />

Some characteristics, such as plant type, grain appearance,<br />

growth cycle, and resistance to major diseases, are selected<br />

for starting from early generations. Yield trials are carried<br />

out at three levels, encompassing observational trials, preliminary<br />

trials, and advanced yield trials under a multi-institutional<br />

network composed of breeders and connected specialists,<br />

located in various localities of the savanna region.<br />

Table 1 presents relevant data on aerobic rice lines,<br />

pooled from the best advanced yield trials, 86 out of 198, of<br />

the National Upland Breeding Network, conducted for three<br />

years at representative sites of the savanna region.<br />

Main program strategies<br />

Breeding for blast resistance<br />

In spite of the difficulties in breeding for blast resistance, breeders<br />

and pathologists were able to cooperate strongly since the<br />

initial steps of the program (Prabhu et al 1999). Donors possessing<br />

ample spectra of resistance were selected for the National<br />

Blast Nurseries conducted in nine locations throughout<br />

the country, and widely used in crosses. Results of subsidiary<br />

tests for leaf blast performed by pathologists in field nurseries<br />

were provided to breeders before field selection, in which segregating<br />

lines are evaluated under high pressure for leaf and<br />

panicle blast. Lines showing high scores in these environments<br />

are eliminated. Recurrent selection schemes have been used<br />

to generate resistant lines (Filippi et al 1994). The strong priority<br />

for blast resistance still holds true in the aerobic rice breeding<br />

program. But, although great care has been taken to produce<br />

and release blast-resistant varieties, their average life is<br />

very short because of the high variability of the pathogen under<br />

the upland ecosystem. The severity of the disease decreases<br />

the sustainability of the exploitation.<br />

Two strategies are currently being used to cope with this<br />

problem: increasing the number of releases possessing contrasting<br />

blast-tolerance genes and submitting the most promising<br />

advanced lines to a side backcross scheme, to transfer different<br />

genes of blast resistance to a given line. When the resistance<br />

of the original line breaks down, various isolines would<br />

be available to replace it. This procedure is accompanied by<br />

monitoring of the prevailing blast races in the region.<br />

Breeding for grain quality<br />

Grain quality was not a strong priority during phase 1 of the<br />

breeding program because the long and bold grains of tradi-<br />

154 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. Mean values for yield and agronomic characteristics of aerobic rice varieties and<br />

lines, compared with those of traditional upland checks, 1 measured in the best advanced<br />

yield trials of the National Upland Breeding Network.<br />

Yield Days to Plant Lodging Leaf Panicle Grain<br />

Cultivar or line (kg ha –1 ) 50% height score blast blast discoloration<br />

flowering (cm) score score score<br />

CNAs 8812 4,419 87 100 1.3 1.8 1.9 2.7<br />

CNAs 8817 4,089 79 104 2.2 2.0 2.6 3.0<br />

CNAs 8989 4,739 80 99 1.9 2.3 2.5 3.2<br />

CNAs 8983 4,747 80 99 1.9 2.2 2.4 3.0<br />

CNAs 9019 4,757 77 104 3.3 2.0 2.1 2.1<br />

CNAs 9023 4,299 77 104 2.8 1.6 2.0 2.2<br />

CNAs 9025 3,964 77 107 2.5 1.7 2.4 2.5<br />

CNAs 9026 4,148 74 98 3.0 2.0 3.2 2.8<br />

CNAs 9045 4,162 85 109 1.9 2.0 2.1 2.7<br />

CNAs 10217 4,029 81 99 0.7 2.1 2.3 2.3<br />

CNAs 10222 4,272 79 101 1.0 2.0 2.1 2.3<br />

CNAs 10260 4,288 78 96 0.9 2.0 2.2 2.7<br />

BRSMG Conai 4,216 71 96 2.0 2.6 4.0 3.3<br />

BRS Bonança 4,315 82 98 1.2 1.9 1.8 2.3<br />

BRS Primavera 4,124 76 110 3.6 2.4 3.2 2.6<br />

BRS Talento 4,440 86 98 1.9 2.0 2.3 2.3<br />

Caiapó 1 4,054 90 122 3.7 2.2 2.1 3.0<br />

Canastra 3,433 87 107 2.3 2.4 2.5 2.8<br />

Carajás 1 4,422 77 103 2.3 2.1 2.3 2.5<br />

Maravilha 4,110 94 105 1.8 2.1 2.3 3.0<br />

Progresso 3,904 97 102 2.3 2.2 1.9 3.0<br />

BRS Soberana 3,920 76 114 3.2 2.2 2.9 2.7<br />

tional upland varieties were considered the standard for quality.<br />

During the 1980s, a successful marketing strategy was proposed<br />

by the irrigated rice producers’ associations and industry<br />

in southern Brazil to change consumer preferences and increase<br />

the national demand for long and slender grains. Visual<br />

selection for grain dimensions (length, width, thickness) and<br />

endosperm appearance is routinely made starting with the first<br />

segregating generations. To assist in the process, a chart was<br />

developed, based on standard varieties, which allows for quick<br />

field and laboratory scoring of grain dimensions. Starting with<br />

the F 5 generation, individual plants are selected for intermediate<br />

values of both amylose content and gelatinization temperature.<br />

This routine methodology has been adapted to use<br />

dehulled grains, thus reducing the sample size and decreasing<br />

the factor of variation induced by the milling process. In the<br />

F 6 generation, when grain availability is increased, grain translucency<br />

and milling recovery are also evaluated. The result of<br />

this concentrated effort is a high proportion of lines possessing<br />

long, slender, and translucent grains, with high to intermediate<br />

amylose content, low to intermediate gelatinization temperature,<br />

and milling recovery higher than 55%. The complete<br />

set of grain quality criteria is also applied during the yield<br />

testing program.<br />

Although t<strong>here</strong> have been releases of improved-planttype<br />

varieties for the favored savanna conditions since the early<br />

1990s, the biggest impact was attained with varieties Maravilha<br />

and BRS Primavera, released in 1996. They were the first upland<br />

varieties that combine high grain quality and desirable<br />

aerobic rice ideotype, that is, 90–110 cm of plant stature, 200–<br />

250 tillers m –2 , erect leaves, resistance to lodging, and yield<br />

potential around 6 t ha –1 (Pinheiro 1999).<br />

A preference survey among rice millers indicated that<br />

BRS Primavera received preference ratings very close to those<br />

of BR IRGA 409, currently considered the most commercially<br />

competitive irrigated rice variety (Guimarães et al 2001). Most<br />

recent releases, such as BRS Talento and BRS Soberana, have<br />

grains that warrant ample acceptance by industry and consumers<br />

(Table 2). These varieties have cooking characteristics and<br />

commercial qualities similar to those of American long-grain<br />

varieties.<br />

Measuring advances of the breeding program<br />

The estimation of genetic gain, considering the period 1995-<br />

2000, indicates a consistent decrease in growth cycle duration<br />

of 0.52 day year –1 , which is desirable for the new profile of<br />

aerobic rice as a component of cropping systems. Besides the<br />

reduced time of exposition to biotic and abiotic stresses, the<br />

short growth cycle opens up an opportunity to insert it as a<br />

succession crop after soybean, to benefit from the remaining<br />

part of the rainy season in the savanna.<br />

Plant height decreased by 0.85 cm year –1 . Till 1998, t<strong>here</strong><br />

was a consistent decrease of 2.6 cm year –1 , when the program<br />

was reoriented to include lines with an intermediate height,<br />

which are more competitive with weeds. Lodging score has<br />

decreased at 4.16% per year because of both direct selection<br />

and plant size reduction. Positive gains were also attained for<br />

Session 5: Broadening the gene pool and exploiting heterosis in cultivated rice 155


Table 2. Grain quality data of representative aerobic rice varieties, compared<br />

with those of irrigated 1 and upland 2 quality checks (int. = intermediate).<br />

Varieties Milling Amylose Gelatinization Grain Grain<br />

yield content temperature length width<br />

(cm) (cm)<br />

BR IRGA 409 1 High 27.0 (int.) 7.0 (low) 6.81 2.06<br />

Caiapó 2 High 26.2 (int.) 3.9 (int.) 6.29 2.43<br />

Maravilha High 22.1 (low) 3.1 (high) 6.91 2.02<br />

BRS Primavera Low 26.3 (int.) 4.9 (int.) 7.29 1.96<br />

Canastra High 21.3 (low) 3.0 (high) 6.99 2.14<br />

BRS Bonança High 27.3 (int.) 3.4 (high) 6.22 2.29<br />

Carisma Medium 26.9 (int.) 3.9 (int.) 6.65 1.84<br />

BRS Talento Medium 26.8 (int.) 3.8 (int.) 6.93 1.92<br />

BRS Soberana Medium 25.8 (int.) 4.7 (int.) 7.08 1.95<br />

panicle blast and grain discoloration, whose scores have decreased<br />

at 1.59% and 1.81% per year, respectively. Although<br />

the overall yield gain was only 0.37% per year, it was very<br />

significant when only the favored region of the Brazilian savanna<br />

was considered, attaining a value as high as 1.85% per<br />

year in the state of Mato Grosso.<br />

The introduction of indica germplasm to the genetic base<br />

of the traditional upland tropical japonica population, associated<br />

with strong selection pressure for grain characteristics,<br />

probably imposed a restriction on possible gains for drought<br />

tolerance. The first aerobic rice releases do not possess the<br />

same level of drought tolerance as the traditional upland varieties,<br />

derived from crosses within only the japonica group<br />

(Pinheiro 2003). However, the program now holds a representative<br />

number of elite lines, japonica versus indica derivatives,<br />

providing a sound basis for further improving yield, blast resistance,<br />

and drought tolerance.<br />

Concluding remarks<br />

The alteration in plant type and grain quality of upland rice,<br />

toward its evolution to aerobic rice, led to an increase in yield<br />

potential and national market acceptance. Its increased participation<br />

in grain cropping systems, under no-tillage or minimum<br />

tillage, is foreseen. Moreover, aerobic rice could greatly<br />

contribute to environmental sustainability, avoiding new savanna<br />

deforestation, when used in the rice-pasture association,<br />

to renew the extensive areas of degraded pasture in the Brazilian<br />

savannas.<br />

References<br />

Filippi MC, Prabhu, AS, Neves PCF, Notteghen JL. 1994. Eficiência<br />

da seleção recorrente sobre a resistência parcial à brusone em<br />

arroz de sequeiro. Fitopatol. Bras. (Brasília): 19:279.<br />

Guimarães EP, Vieira NRA, Pinheiro BS. 2001. Breeding for specialty<br />

rice in Latin America: status and perspectives. In:<br />

Chaudhary RC, Tran VD, editors. Specialty rices of the world:<br />

breeding, production and marketing. Rome: FAO. p 317-322.<br />

Pinheiro BS. 1999. Características morfológicas da planta<br />

relacionadas à produtividade. In: Vieira NRA, Santos AB,<br />

Sant’ana EP, editors. A cultura do arroz no Brasil. Santo<br />

Antônio de Goiás (Brazil): Embrapa Arroz e Feijão. p 116-<br />

147.<br />

Pinheiro BS. 2003. Integrating selection for drought tolerance into a<br />

breeding program: the Brazilian experience. In: Fischer KS,<br />

Lafitte R, Fukai S, Atlin G, Hardy B, editors. Breeding rice<br />

for drought-prone environments. Los Baños (Philippines):<br />

<strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>. p 75-83.<br />

Prabhu AS, Filippi MC, Ribeiro AS. 1999. Doenças e seu controle.<br />

In: Vieira NRA, Santos AB, Sant’ana EP, editors. A cultura<br />

do arroz no Brasil. Santo Antônio de Goiás (Brazil): Embrapa<br />

Arroz e Feijão. p 262-307.<br />

Steinmetz S, Reyniers FN, Forest F. 1988a. Caracterização do regime<br />

pluviométrico e do balanço hídrico do arroz de sequeiro<br />

em distintas regiões produtoras do Brasil: síntese e<br />

interpretação dos resultados. EMBRAPA-CNPAF Documentos<br />

23. Goiânia (Brazil): EMBRAPA-CNPAF. v. 1. 66 p.<br />

Steinmetz S, Reyniers FN, Forest F. 1988b. Caracterização do regime<br />

pluviométrico e do balanço hídrico do arroz de sequeiro<br />

em distintas regiões produtoras do Brasil: catálogo básico de<br />

dados. EMBRAPA-CNPAF Documentos 23. Goiânia (Brazil):<br />

EMBRAPA-CNPAF. v. 2. 278 p.<br />

Notes<br />

Author’s address: Embrapa Arroz e Feijão, Caixa Postal 179, 75375-<br />

000 Santo Antônio de Goiás, GO, Brazil, e-mail:<br />

beatriz@cnpaf.embrapa.br.<br />

156 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Broadening the gene pool of rice<br />

through introgression from wild species<br />

D.S. Brar<br />

World rice production has more than doubled, from 257 million<br />

tons in 1966 to 600 million t in 2000. To meet the growing<br />

needs of the human population, rice production must increase<br />

by 25% during the next 20 years. Further, several biotic<br />

and abiotic stresses adversely affect rice productivity. Some<br />

of the major diseases and pests affecting rice production are<br />

bacterial blight (BB), blast, sheath blight, tungro virus disease,<br />

and rice yellow mottle virus (RYMV), and insects such as<br />

brown planthopper (BPH), stem borer, and Asian and African<br />

gall midge. Similarly, abiotic stresses such as drought, cold,<br />

salinity, acidity, iron toxicity, and submergence reduce rice<br />

production. Changes in insect biotypes and disease races are<br />

becoming a continuing threat to rice production. T<strong>here</strong> is thus<br />

an urgent need to broaden the rice gene pool through introgression<br />

of genes from new and diverse sources. Wild species<br />

are an important reservoir of useful genes for tolerance of biotic<br />

and abiotic stresses.<br />

Useful traits of Oryza species<br />

The genus Oryza has two cultivated and 22 wild species. Of<br />

the two cultivated species, O. sativa (2n=24 AA), commonly<br />

referred to as Asian rice, is grown worldwide, w<strong>here</strong>as O.<br />

glaberrima (2n=24 AA), “African rice,” is cultivated in a limited<br />

area in West Africa. The wild species have 2n=24 or 48<br />

chromosomes representing 10 genomic types (AA, BB, BBCC,<br />

CC, CCDD, EE, FF, GG, HHJJ, and HHKK). The wild species<br />

germplasm maintained in the <strong>IRRI</strong> genebank contains 2,500<br />

accessions of AA-genome types, 500 accessions of O.<br />

officinalis complex, 35 accessions of O. meyeriana complex,<br />

21 accessions of O. ridleyi complex, 19 accessions of O.<br />

brachyantha, and 1 accession of O. schlechteri.<br />

Several incompatibility barriers, such as low crossability,<br />

increased sterility, and limited recombination between chromosomes<br />

of wild and cultivated species, limit the transfer of<br />

useful genes (Brar and Khush 1986, 2002). Recent advances<br />

in tissue culture and genomics have enabled the production of<br />

wide hybrids among distantly related species and allowed researchers<br />

to precisely monitor the introgression of chromosome<br />

segments from wild into cultivated species. More recently,<br />

BAC libraries of wild species representing 10 different genomes<br />

have been developed by the Arizona Genomics <strong>Institute</strong><br />

in Tucson (Rod Wing, personal communication, 2004),<br />

which offer new opportunities for map-based cloning of useful<br />

genes/QTLs.<br />

Alien gene introgression<br />

The main objectives of our wide hybridization program are<br />

(1) to broaden the gene pool of rice by transferring useful genes<br />

for resistance to major diseases and insects and tolerance of<br />

abiotic stresses and to enhance the grain yield of rice through<br />

the introgression of QTLs/yield-enhancing loci from wild species,<br />

(2) to tag alien genes/QTLs introgressed from wild species<br />

with molecular markers for use in marker-assisted selection<br />

(MAS), (3) to characterize alien introgression using molecular<br />

cytogenetic techniques, and (4) to isolate agronomically<br />

important genes/QTLs using BAC libraries of Oryza.<br />

Some accomplishments made in collaboration with national<br />

agricultural research and extension systems (NARES)<br />

partners and advanced research institutes (ARI) are discussed<br />

below.<br />

Production of interspecific hybrids,<br />

alien introgression lines, and mapping populations<br />

Direct crosses and embryo rescue techniques have been used<br />

to successfully produce hybrids between rice (AA) and all other<br />

wild species (except O. schlechteri). Backcrossing with the<br />

recurrent rice parent is used to produce fertile progenies. Introgression<br />

lines (2n=24) have been produced from crosses of<br />

AA with various wild species representing AA, BBCC, CC,<br />

CCDD, EE, FF, GG and HHJJ genomes except for O. sativa<br />

(AA) × O. coarctata (HHKK) (Brar and Khush 2002).<br />

Doubled haploids (DH) have been produced from O.<br />

sativa × O. glaberrima. Similarly, recombinant inbred lines<br />

(RILs) from crosses of rice with A-genome wild species and<br />

near-isogenic lines (NILs) derived through backcrossing carrying<br />

small segments from distant genomes serve as mapping<br />

populations. Segregating populations derived from crosses of<br />

alien introgression lines × recurrent rice parents are also used<br />

in mapping genes/QTLs.<br />

Production of monosomic alien addition lines<br />

(MAALs) and chromosome segmental substitution<br />

lines (CSSL)<br />

MAALs (2n=25) have been produced representing 6 to 10<br />

chromosomes from 7 wild species (CC, BBCC, CCDD, EE,<br />

FF, GG, and HHJJ genomes). CSSL are being developed from<br />

O. rufipogon, O. longistaminata, and O. glaberrima in the<br />

background of O. sativa using molecular markers. These CSSL<br />

are important resources in fine mapping of genes and functional<br />

genomics.<br />

Session 5: Broadening the gene pool and exploiting heterosis in cultivated rice 157


Table 1. Progress in the transfer of agronomically important genes<br />

from wild Oryza species into cultivated rice at <strong>IRRI</strong>. a<br />

Donor Oryza species<br />

Trait Wild species Genome Accession<br />

number<br />

Transferred to O. sativa<br />

Grassy stunt resistance O. nivara AA 101508<br />

Bacterial blight resistance O. longistaminata AA –<br />

O. officinalis CC 100896<br />

O. minuta BBCC 101141<br />

O. latifolia CCDD 100914<br />

O. australiensis EE 100882<br />

O. brachyantha FF 101232<br />

Blast resistance O. minuta BBCC 101141<br />

Brown planthopper O. officinalis CC 100896<br />

resistance O. minuta BBCC 101141<br />

O. latifolia CCDD 100914<br />

O. australiensis EE 100882<br />

Whitebacked planthopper O. officinalis CC 100896<br />

resistance<br />

Cytoplasmic male sterility O. perennis AA 104823<br />

O. glumaepatula AA 100969<br />

Tungro resistance O. rufipogon AA 105908<br />

O. rufipogon AA 105909<br />

O. rufipogon AA 106423<br />

Introgression lines under evaluation<br />

Yellow stem borer O. longistaminata AA 110404<br />

O. rufipogon AA –<br />

Sheath blight resistance O. minuta BBCC 101141<br />

O. rufipogon AA –<br />

Increased elongation ability O. rufipogon AA CB751<br />

Tolerance of acidity and iron O. glaberrima AA Many<br />

and aluminum toxicity O. rufipogon AA 106412<br />

O. rufipogon 106423<br />

Resistance to nematodes O. glaberrima AA Many<br />

a<br />

Modified from Brar and Khush (2002).<br />

Alien gene transfer and varietal development<br />

Genes for resistance to BPH, BB, blast, and grassy stunt and<br />

tungro virus, tolerance of acidity, and cytoplasmic male sterility<br />

have been introgressed from different A-genome wild species,<br />

including distantly related genomes (CC, BBCC, CCDD,<br />

EE, FF), into elite breeding lines of rice (see Brar and Khush<br />

2002, Multani et al 2003, Table 1). Some of these lines carrying<br />

genes from wild species for resistance to BPH and tungro<br />

and tolerance of acid sulfate soil conditions have been released<br />

as commercial varieties.<br />

During 2002, three varieties were released from wide<br />

crosses. One of the breeding lines, IR73678-6-9-B from IR64<br />

× O. rufipogon, was released as variety AS996 for commercial<br />

cultivation in the Mekong Delta of Vietnam. This variety is<br />

grown on more than 100,000 ha. Another variety, Matatag 9<br />

(IR73385-1-4-3-2-1-6), has been released for cultivation in<br />

tungro-prone areas of the Philippines. Similarly, another highyielding<br />

elite line (IR72102-4-159-1-3) from O. sativa × O.<br />

longistaminata has been released as variety NSICRC112 in<br />

the Philippines. Earlier, five <strong>IRRI</strong> breeding lines from O. sativa<br />

× O. officinalis were released as BPH-resistant varieties<br />

(MTL98, MTL103, MTL105, MTL110, MTL114) in Vietnam.<br />

Recently, variety Dhanrasi (IE15358) from the cross of B32-<br />

sel-4 × O. rufipogon was released by the Directorate of <strong>Rice</strong><br />

<strong>Research</strong> in Hyderabad, India (T. Ram, personal communication,<br />

2004).<br />

Some of the indica alien introgression lines developed<br />

at <strong>IRRI</strong> have shown a wide spectrum of resistance to BPH and<br />

blast in Korea. These lines are being used by the Rural Development<br />

Administration (RDA) to broaden the gene pool of<br />

japonica rice.<br />

We are evaluating advanced progenies derived from different<br />

wide crosses for resistance to stem borer and tolerance<br />

of aluminum toxicity, P deficiency, and iron toxicity. Some O.<br />

rufipogon accessions resistant to sheath blight have been identified<br />

and are being used to produce advanced introgression<br />

lines. Progenies derived from O. sativa × O. glaberrima have<br />

shown increased tolerance of iron toxicity under field conditions.<br />

Advanced introgression lines are under evaluation for<br />

the transfer of weed competitive ability from O. glaberrima<br />

into O. sativa.<br />

Enhancing the yield potential of rice<br />

Wild species are phenotypically inferior but are valuable genetic<br />

resources for enhancing the yield potential of rice (Xiao<br />

et al 1998). Preliminary results at <strong>IRRI</strong> from the crosses of<br />

new plant type (NPT) × O. longistaminata and IR64 × O.<br />

rufipogon indicate possibilities to improve rice grain yield by<br />

introgressing yield-enhancing loci/QTLs.<br />

Molecular mapping of introgressed genes/QTLs<br />

and characterization of introgression<br />

The introgressed genes Bph10, Pi9(t), and Xa21 have been<br />

mapped. One of the genes, Xa21 for BB resistance, has been<br />

used via MAS in gene pyramiding at <strong>IRRI</strong> and by NARES in<br />

the Philippines, India, China, and Thailand. Genes introgressed<br />

for BPH and tungro tolerance are being mapped for use in<br />

MAS. One of the major QTLs for tolerance of aluminum toxicity<br />

introgressed from O. rufipogon has been mapped on chromosome<br />

3, which is conserved across other cereal species<br />

(Nguyen et al 2003).<br />

Molecular marker analysis has revealed limited introgression<br />

of small chromosome segments from distant genomes<br />

(FF, GG) of Oryza into rice. However, introgression among<br />

cultivated rice and A-genome wild species is frequent for all<br />

12 chromosomes. We are developing genome-specific clones<br />

using representational difference analysis (RDA) to characterize<br />

alien introgression.<br />

Molecular characterization using GISH<br />

GISH techniques have been used successfully to characterize<br />

parental genomes, extra alien chromosomes, and<br />

homoeologous pairing between rice and genomes of several<br />

wild species, which were difficult to identify through conventional<br />

cytogenetic techniques.<br />

158 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Two new genomes (GG and HHJJ) have been assigned<br />

for O. granulata and O. ridleyi based on molecular divergence<br />

involving total genomic DNA hybridization (Aggarwal et al<br />

1997). RDA was used to identify transposable elements in rice<br />

(Panaud et al 2002).<br />

Development of novel genetic resources<br />

for functional genomics<br />

Near-isogenic alien introgression lines, particularly those having<br />

short introgressed segments derived from crosses of O.<br />

sativa with species having distant genomes of Oryza, have<br />

become novel genetic resources for functional genomics.<br />

<strong>Research</strong> priorities and future outlook<br />

With the advances in tissue culture and molecular markers,<br />

genomics, and molecular cytogenetics, the outlook for broadening<br />

the gene pool of rice for tolerance of major biotic and<br />

abiotic stresses through the introgression of genes from wild<br />

species seems more promising than before. Some of the priorities<br />

for future research in wide hybridization are listed below.<br />

Broadening the gene pool for tolerance<br />

of major biotic and abiotic stresses<br />

Emphasis should be given to transferring genes from wild species<br />

for traits for which genetic variability is limited in the<br />

cultivated germplasm. Priority traits include resistance to sheath<br />

blight and stem borer and tolerance of salt and drought. T<strong>here</strong><br />

is a need to search for micronutrients such as high iron and<br />

zinc in the polished grains of wild species. Genes with a broad<br />

spectrum of tolerance of biotic and abiotic stresses introgressed<br />

from wild species should be transferred into elite indica and<br />

japonica cultivars.<br />

Pyramiding of genes/QTLs with a broad spectrum<br />

of resistance<br />

A number of genes for tolerance of biotic stresses have been<br />

introgressed from wild species into rice and also tagged with<br />

molecular markers. MAS should be practiced to pyramid genes<br />

to develop durable resistance to pests. Emphasis should be<br />

given to enhancing tolerance of abiotic stresses by combining<br />

genes/QTLs governing tolerance at different stages of development<br />

and for different component traits/mechanisms of tolerance.<br />

Identifying and introgressing QTLs/yield-enhancing<br />

loci from wild species<br />

Molecular analysis has revealed novel QTLs/yield-enhancing<br />

loci in wild species. T<strong>here</strong> is a need to identify and introgress<br />

such alleles/QTLs, particularly from A-genome wild species,<br />

into modern rice varieties for enhancing yield potential.<br />

Enhancing homoeologous pairing/recombination<br />

One of the major bottlenecks in alien gene transfer is the limited<br />

homoeologous pairing between rice and distantly related<br />

species of Oryza. One approach would be to isolate the gene(s)<br />

controlling homoeologous pairing such as the Ph<br />

(homoeologous pairing) gene in wheat and use such genes to<br />

promote homoeologous recombination in rice. This would be<br />

particularly important in species such as O. brachyantha (FF),<br />

O. granulata (GG), and O. ridleyi (HHJJ), which otherwise<br />

show restricted recombination with the cultivated rice genome.<br />

Isolation of agronomically important genes/QTLs<br />

through positional cloning<br />

Wild species carry genes with a wide spectrum of tolerance of<br />

biotic and abiotic stresses. BAC libraries of different wild species<br />

representing each genomic type of Oryza should be used<br />

for fine mapping and isolation of agronomically important<br />

genes/QTLs.<br />

GISH-assisted selection for alien introgression<br />

Emphasis should be given to developing efficient GISH protocols<br />

to detect and monitor alien introgression in the backcross<br />

progenies. Molecular cytogenetic techniques involving<br />

molecular markers, GISH, FISH, and fiber-FISH should be<br />

used to precisely determine the mechanism of alien gene transfer<br />

in the face of limited homoeologous pairing.<br />

Producing haploids from species crosses<br />

Chromosome elimination through species crosses has proven<br />

to be a valuable mechanism to produce haploids in wheat, barley,<br />

and oat. Such a haploid-inducing system needs to be identified<br />

in rice, which could be complementary, to produce haploids<br />

in indica rice, in which anther culture response is low<br />

and limited to only specific genotypes.<br />

References<br />

Aggarwal RK, Brar DS, Khush GS. 1997. Two new genomes in the<br />

Oryza complex identified on the basis of molecular divergence<br />

analysis using total genomic DNA hybridization. Mol. Gen.<br />

Genet. 254:1-12.<br />

Brar DS, Khush GS. 1986. Wide hybridization and chromosome<br />

manipulation in cereals. In: Evans DH, Sharp WR, Ammirato<br />

PV, editors. Handbook of plant cell culture. Vol. 4. Techniques<br />

and applications. New York (USA): MacMillan Publishers.<br />

p 221-263.<br />

Brar DS, Khush GS. 2002. Transferring genes from wild species<br />

into rice. In: Kang MS, editor. Quantitative genetics, genomics<br />

and plant breeding. Wallingford (UK): CAB <strong>International</strong>.<br />

p 197-217.<br />

Multani DS, Khush GS, delos Reyes BG, Brar DS. 2003. Alien gene<br />

introgression and development of monosomic alien addition<br />

lines from Oryza latifolia Desv. to rice, Oryza sativa L. Theor.<br />

Appl. Genet. 107:395-405.<br />

Nguyen BD, Brar DS, Bui BC, Nguyen TV, Pham LN, Nguyen HT.<br />

2003. Identification and mapping of the QTLs for aluminum<br />

tolerance introgressed from the new source, Oryza rufipogon<br />

Griff., into indica rice (Oryza sativa L.). Theor. Appl. Genet.<br />

106:583-593.<br />

Session 5: Broadening the gene pool and exploiting heterosis in cultivated rice 159


Panaud O, Vitte C, Hivert J, Muzlak S, Talag J, Brar DS, Sarr A.<br />

2002. Characterization of transposable elements in the genome<br />

of rice (Oryza sativa L.) using representational difference<br />

analysis (RDA). Mol. Genet. Genom. 268:113-121.<br />

Xiao J, Li J, Grandillo S, Ahn SN, Yuan L, Tanksley SD, McCouch<br />

SR. 1998. Identification of trait-improving quantitative trait<br />

loci alleles from a wild rice relative, Oryza rufipogon. Genetics<br />

150:899-909.<br />

Notes<br />

Author’s address: <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>, DAPO Box<br />

7777, Metro Manila Philippines.<br />

Acknowledgment: The help provided by NARES partners, <strong>IRRI</strong> colleagues,<br />

and the wide hybridization team is duly acknowledged.<br />

Mutation in seed reserves and its use<br />

for improving grain quality in rice<br />

Hikaru Satoh, Ken-ichi Ohtsubo, and Yasunori Nakamura<br />

The improvement of grain quality is one of the most important<br />

subjects in rice breeding. For this, genetic resources of endosperm<br />

properties must be collected, characterized, and evaluated.<br />

In maize, various kinds of mutants for polysaccharides,<br />

lipids, or proteins are known. These mutants greatly contributed<br />

to the improvement of the grain quality of maize, and<br />

thus expanded the use of maize not only as a food but also as<br />

an important industrial material in food chemistry. In addition,<br />

they offered valuable information on the study of gene<br />

action in the biological processes of metabolic regulation in<br />

higher plants and led us to develop the novel genetic resources<br />

improving these properties.<br />

Starch plays an important role in the eating quality of<br />

cooked rice and the processing quality of industrial uses. In<br />

rice, the mutants of starch properties had been little known<br />

except for the waxy endosperm. We treated the fertilized egg<br />

cells of rice with MNU (Satoh and Omura 1979) and obtained<br />

several thousand rice mutants for embryo or endosperm properties<br />

(Satoh 1985), in which various kinds of mutants modifying<br />

starch properties were found, as many as in maize (Satoh<br />

and Omura 1981, Satoh et al 2003).<br />

Structure of starch and its biosynthesis<br />

<strong>Rice</strong> starch consists of two types of glucose polymers, 20%<br />

amylose and 80% amylopectin. Amylose is an essentially linear<br />

molecule composed of α-(1,4)-linked glucosidic chains,<br />

although recently another type of amylose possessing some<br />

very short-branched chains was reported. Amylopectin is a<br />

highly branched glucan with α-(1,6) glucosidic bonds that connect<br />

linear chains. Hizukuri (1986) proposed a cluster model<br />

for amylopectin. In this model, A and B 1 chains form a single<br />

cluster, w<strong>here</strong>as B 2 and B 3 chains extend to two and three clusters,<br />

respectively. Amylopectin is much larger in molecular size<br />

than amylose, tenfold or more. The amylose to amylopectin<br />

ratio and their structures greatly influence the rheological properties<br />

of starch.<br />

Amylose is synthesized by ADP glucose<br />

pyrophosphorylase (AGPase) and granule-bound starch synthase<br />

I (GBSSI), which is encoded by the Waxy gene. Amy-<br />

lopectin is synthesized by concerted reactions catalyzed by<br />

soluble starch synthase (SS), starch-branching enzyme (BE),<br />

and starch-debranching enzyme (DBE), using ADP-glucose as<br />

a substrate. In addition, multiple isoforms were found in each<br />

enzyme, that is, three isoforms of SS and BE, and two isoforms<br />

of DBE in developing endosperm of rice, respectively. T<strong>here</strong>fore,<br />

at least these eight genes are responsible for amylopectin<br />

biosynthesis in rice endosperm.<br />

Mutants modifying amylose content<br />

To improve starch quality, novel genetic resources must be<br />

developed and evaluated. For this purpose, we need to elucidate<br />

the genetic regulation mechanism of starch biosynthesis<br />

and the interrelationships among the gene, enzyme, starch structure,<br />

and rheological properties. A mutant is one of the most<br />

helpful materials for this purpose.<br />

After the MNU treatment, many mutants with modified<br />

amylose content were obtained in rice (Yano et al 1988). They<br />

were classified into waxy type and dull type with lower amylose<br />

content. Amylose content in endosperm starch varied from<br />

0.3% to 12.8%, depending on the mutant line. Phenotypes of<br />

dull mutants were intermediate between those of nonwaxy rice<br />

and waxy rice, and t<strong>here</strong> was good agreement between the phenotype<br />

and amylose content. Thermal gelatinization of rice<br />

starch is influenced by amylose content. T<strong>here</strong> is little difference<br />

in the initiation of gelatinization of endosperm starch<br />

among the waxy, dull, and wild type. However, the termination<br />

temperature of gelatinization is remarkably different among<br />

them. When the amylose content increases, the termination temperature<br />

of gelatinization of endosperm starch shifts to a high<br />

temperature. When starch is gelatinized in 4 M urea solution,<br />

granules with lower amylose content swell more. However,<br />

these mutations did not alter amylopectin fine structure. These<br />

facts indicate that amylose content affects the termination temperature<br />

of gelatinization of starch and the swelling power of<br />

gel, but it has little influence on the initiation of gelatinization.<br />

160 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Mutants involved in amylopectin biosynthesis<br />

The branching enzyme is the only enzyme that can introduce<br />

α-1,6 glucosidic linkages into α-polyglucans and t<strong>here</strong>fore it<br />

plays an essential role in the biosynthesis of amylopectin. Three<br />

isoforms of branching enzyme (BE I, BE IIa, and BE IIb) are<br />

observed in rice endosperm. Recently, we isolated mutants for<br />

the respective isoforms of BE, that is, mutants lacking in BE I<br />

(Satoh et al 2003) or BE IIb activity (Nishi et al 2001) and a<br />

mutant decreasing remarkably in BE IIa activity (Satoh et al<br />

2003). All of the BE mutants were controlled by respective<br />

single genes independent from each other. The grains of the<br />

BE IIb mutant are markedly smaller than those of the wild<br />

type and are usually floury in appearance, indicating that this<br />

enzyme affects starch accumulation.<br />

In contrast, the endosperm of BE I and BE IIa mutants<br />

exhibited the normal phenotype and contained the same amount<br />

of starch as the wild type. BE IIb mutation specifically decreased<br />

the short chains with less than DP 17, suggesting that<br />

BE IIb contributes to the synthesis of A chains of amylopectin.<br />

In contrast, the amylopectin of the BE I mutant was characterized<br />

by a significant decrease in long chains with more than<br />

DP 38 and short chains with DP 12 to 23, and a marked increase<br />

in short chains with less than DP 12, suggesting that BE<br />

I specifically synthesizes both B 1 chains and B 3 chains. However,<br />

a notable alteration in the chain length distribution profile<br />

was not observed in the BE IIa mutation.<br />

It is t<strong>here</strong>fore reasonable to assume that the three forms<br />

of BE play distinct roles in the formation of amylopectin<br />

branches in rice. The endosperm starch from the BE I mutant<br />

had the lowest onset temperature for thermo-gelatinization. In<br />

contrast, the BE IIb mutant showed the highest onset temperature<br />

for thermo-gelatinization. The BE IIa mutation had little<br />

influence on the gelatinization of starch but exhibited the highest<br />

enthalpy. These findings indicate that the genetic modification<br />

of amylopectin fine structure is responsible for changes<br />

in physicochemical and rheological properties of the starch.<br />

The results support the view that alterations in amylopectin<br />

structure, in particular in short chains within clusters, might<br />

play a critical role in the rheological properties of starch. It is<br />

t<strong>here</strong>fore likely that genetic modification of the gene for BEs<br />

will lead to the synthesis of novel types of starch as new materials<br />

for the food and starch industries.<br />

Native-PAGE/activity staining analysis for the<br />

debranching enzyme showed that sugary1 mutation is lacking<br />

in isoamylase activity (ISA) and is followed by a marked reduction<br />

in expression levels of pullulanase (Nakamura et al<br />

1997). Two kinds of nonallelic sugary mutants have been identified<br />

in rice. Sugary mutations increased short chains and decreased<br />

long chains dramatically. Rheological properties of<br />

the sugary1 mutant are characterized by extremely lower viscosity<br />

in contrast to that of the wild type (Wong et al 2003).<br />

These results also imply that amylopectin fine structure is important<br />

in determining rheological properties of starch and the<br />

genetic modification of DBE also led to the development of<br />

novel starch in rice.<br />

Recently, we isolated some of the mutants involved in<br />

soluble starch synthase (SS). A preliminary examination showed<br />

that these SS mutations altered the fine structure of amylopectin<br />

and its rheological properties as well as BE and DBE mutations.<br />

The details are under investigation. In addition to these<br />

mutations, we isolated various kinds of mutants by MNU treatment.<br />

These mutations also modified the amylopectin fine structure<br />

and rheological properties.<br />

Spontaneous mutation for starch biosynthesis<br />

A wide variation in apparent amylose content was detected in<br />

local rice germplasm collected from Bangladesh. Genetical<br />

and biochemical analyses showed that this wide variation is<br />

caused by spontaneous mutations in the GBSS gene, especially<br />

the indica-type GBSS gene, Wx-a. At least three spontaneous<br />

mutations lowering the gene expression of Wx-a have been<br />

found in Bangladeshi local rice germplasm (Jahan et al 2002a).<br />

Cooking quality is markedly different between japonica<br />

and indica rice. Alkali digestibility is one of the most important<br />

indicators for the difference in cooking quality between<br />

them as well as the amylose content because t<strong>here</strong> is a tight<br />

correlation between alkali digestibility and gelatinization temperature<br />

in rice starch. Indica rice is resistant to alkali digestibility,<br />

w<strong>here</strong>as japonica rice is easily digested by alkali solution.<br />

Umemoto et al (2002) made clear that the difference in<br />

alkali digestibility and urea gelatinization is caused by the difference<br />

in the chain length distribution of amylopectin, and<br />

these characters are controlled by the same gene. RFLP analysis<br />

showed clearly that a gene encoding SSIIa is responsible<br />

for this character.<br />

However, wide variation was found in amylopectin chain<br />

length distribution as well as in alkali digestibility in BGD<br />

culivars (Jahan et al 2002b). Similar variations were observed<br />

in local rice germplasm collected from other countries such as<br />

Myanmar, Pakistan, African countries, and so on. These variations<br />

might be caused partly by the other amylopectin biosynthetic<br />

enzymes in addition to SSIIa because wide variation was<br />

found in the activity level not only of SSIIa but also of other<br />

SSs, BEs, and DBEs. RFLPs for the genes involved in starch<br />

biosynthesis supported this assumption.<br />

Many kinds of mutant genes involved in starch biosynthesis<br />

have been identified in both rice and maize. The analysis<br />

of these mutants affecting the production of starch-synthesizing<br />

enzymes will provide the in vivo function of the corresponding<br />

enzymes and lead to breeding rice varieties having<br />

novel properties of starch.<br />

References<br />

Hizukuri S. 1986. Polymodal distribution of the chain lengths of<br />

amylopectins, and its significance. Carbohydr. Res. 147:342-<br />

347.<br />

Jahan MS, Kumamaru T, Hamid A, Satoh H. 2002a. Diversity of<br />

granule-bound starch synthase (GBSS) level in Bangladesh<br />

rice cultivars. <strong>Rice</strong> Genet. Newsl. 19:69-71.<br />

Session 5: Broadening the gene pool and exploiting heterosis in cultivated rice 161


Jahan MS, Nishi A, Hamid A, Satoh H. 2002b. Variation in amylopectin<br />

fine structure of Bangladesh rice cultivars. <strong>Rice</strong> Genet.<br />

Newsl. 19:72-74.<br />

Nakamura Y, Kubo A, Shimamune T, Mastuda T, Harada K, Satoh<br />

H. 1997. Correlation between activities of starch debranching<br />

enzyme and α-polyglucan structure in endosperms of sugary-<br />

1 mutants of rice. Plant J. 12:143-153.<br />

Nishi A, Nakamura Y, Tanaka N, Satoh H. 2001. Biochemical and<br />

genetic analyses of the effects of amylose-extender mutation<br />

in rice endosperm. Plant Physiol. 127:1-14.<br />

Satoh H. 1985. Genic mutations affecting endosperm properties in<br />

rice. Gamma Field Symp. 24:17-37.<br />

Satoh H, Omura T. 1979. Induction of mutation by the treatment of<br />

fertilized egg cell with N-methyl-N-nitrosourea in rice. J. Fac.<br />

Agric. Kyushu Univ. 24:165-174.<br />

Satoh H, Omura T. 1981. New endosperm mutations induced by<br />

chemical mutagens in rice, Oryza sativa L. Jpn. J. Breed.<br />

31:316-325.<br />

Satoh H, Nishi A, Fujita N, Kubo A, Nakamura Y, Kawasaki T, Okita<br />

WT. 2003. Isolation and characterization of starch mutants in<br />

rice. J. Appl. Glycosci. 50:225-230.<br />

Satoh H, Nishi A, Yamashita K, Takemoto Y, Tanaka Y, Hosaka Y,<br />

Sakurai A, Fujita N, Nakamura Y. 2003. Starch branching<br />

enzyme I-deficient mutation specifically affects the structure<br />

and properties of starch in rice endosperm. Plant Physiol.<br />

133:1111-1121.<br />

Umemoto T, Yano M, Satoh H, Shomura A, Nakamura Y. 2002.<br />

Mapping of a gene responsible for the difference in amylopectin<br />

structure between japonica-type and indica-type rice varieties.<br />

Theor. Appl. Genet. 104:1-8.<br />

Wong KS, Kubo A, Jane JL, Harada K, Satoh H, Nakamura Y. 2003.<br />

Structures and properties of amylopectin and phytoglycogen<br />

in the endosperm of sugary-1 mutants of rice. J. Cereal Sci.<br />

37:139-149.<br />

Yano M, Okuno K, Satoh H, Omura T. 1988. Chromosomal location<br />

of genes conditioning low amylose content of endosperm<br />

starches in rice, Oryza sativa L. Theor. Appl. Genet. 76:183-<br />

189.<br />

Notes<br />

Authors’ addresses: Hikaru Satoh, Faculty of Agriculture, Kyushu<br />

University (Hakozaki, Fukuoka 812-8581, Japan); Ken-ichi<br />

Ohtsubo, National Food <strong>Research</strong> <strong>Institute</strong> (Kan-nondai,<br />

Tsukuba, Ibaraki 305-8642; Yasunori Nakamura, Faculty of<br />

Bioresource Science, Akita Prefectural University<br />

(Shimoshinjo-Nakano, Akita-City 010-0195, Japan), e-mail:<br />

hdatoh@agr.kyushu-u.ac.jp.<br />

Heterosis in rice for increasing yield, production efficiency,<br />

and rural employment opportunities<br />

Sant S. Virmani<br />

Heterosis is known to be a major factor for increased production<br />

in several crops, including rice. It has become the basis of<br />

multibillion-dollar agribusiness worldwide. Hybrid varieties<br />

in maize, sorghum, sunflower, and rice added 90 million tons<br />

annually to global food production, which spared about 34<br />

million ha of land from cultivation of these crops to meet global<br />

demand (Duvick 1999). Hybrid rice technology, commercialized<br />

in China, has spread to about 50% of the 30 million<br />

ha of rice area of that country, contributing 60% of its national<br />

paddy production. Inbred rice covers the other 50% of the area,<br />

contributing only 40% of the national paddy production. In<br />

China, rice hybrids (6.9 t ha –1 ) on average have outyielded<br />

inbred rice (5.4 t ha –1 ) by 1.5 t ha –1 (Ma and Yuan 2003). Since<br />

1979, <strong>IRRI</strong> has been exploring the prospects of exploiting<br />

heterosis in the tropics to increase rice yield potential in the<br />

light of increasing rice demand, decreasing land area and water<br />

resources for rice production, and the need for sparing rice<br />

land for crop diversification to increase farmers’ income. This<br />

paper summarizes the progress made so far and discusses the<br />

future prospects of hybrid rice in the tropics.<br />

Extent of yield heterosis<br />

Data gat<strong>here</strong>d at <strong>IRRI</strong> and in India, the Philippines, Bangladesh,<br />

Indonesia, Vietnam, Myanmar, and Sri Lanka clearly provide<br />

evidence for a 15–20% yield advantage of rice hybrids over<br />

inbred high-yielding varieties (HYVs) (Virmani et al 2003).<br />

Even in Korea and Egypt, w<strong>here</strong> yield levels are considerably<br />

higher, a yield advantage (10–15%, 1–1.5 t ha –1 ) of rice hybrids<br />

over inbred HYVs has been reported (Virmani et al 2003).<br />

Heterosis for yield in rice hybrids has been attributed to their<br />

increased dry matter production caused by higher leaf area<br />

index, higher crop growth rate, and increased harvest index<br />

resulting from increased spikelet number and increased grain<br />

weight. Parental lines developed at <strong>IRRI</strong> and shared freely with<br />

national programs during the past 15–20 years have contributed<br />

significantly toward achieving these results. More than<br />

40 heterotic rice hybrids, developed by the public and private<br />

sector, have been commercialized during the past ten years in<br />

some countries outside China. Those known to be derived from<br />

<strong>IRRI</strong>-bred parental lines are listed in Table 1. The yield advantage<br />

of rice hybrids over inbred HYVs was even higher<br />

(20–30%) in farmers’ fields in the Philippines and India, perhaps<br />

because of their homeostatic effects. During 2004, al-<br />

162 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. List of some hybrids (derived from <strong>IRRI</strong>-bred germplasm) released for commercial cultivation in some tropical<br />

countries during 1994-2004.<br />

Nature of Country Year<br />

Name of hybrid Parentage breeding released released<br />

institution<br />

APHR-1 IR58025A/Vajram Public India 1994<br />

APHR-2 IR62829A/MTU 9992 Public India 1994<br />

MGR-1 (IR64610H) IR62829A/IR9761-19-1R Public India 1994<br />

KRH-1 (IR64611H) IR58025A/IR9761-19-1R Public India 1994<br />

Magat (PSB Rc26H or IR64616H) IR62829A/IR29723-143-3-2-1R Public Philippines 1994<br />

CNRH-3 IR62829A/Ajaya Public India 1995<br />

DRRH-1 (IR65489H) IR58025A/IR40750-82-2-2-3R Public India 1996<br />

KRH-2 IR58025A/KMR-3 Public India 1996<br />

Pant Sankar Dhan-1 IR58025A/UPRI 93-133 Public India 1997<br />

PHB-71 <strong>IRRI</strong>-bred A line Private India 1997<br />

ADTRH-1 IR58025A/IR66 Public India 1998<br />

CORH-2 IR58025A/C20R Public India 1998<br />

Narendra Sankar Dhan-2 IR58025A/NDR 3026 Public India 1998<br />

Sahyadri (IR69690H) IR58025A/BR827-35-2-1-1-1R Public India 1998<br />

Mestizo (PSB Rc72H or IR68284H) IR58025A/IR34686-179-1-2-1R Public Philippines 1997<br />

HYT-57 (IR69690H) IR58025A/BR827-35-2-1-1-1R Public Vietnam 1999<br />

Proagro 6201 <strong>IRRI</strong>-bred A line Private India 2000<br />

BRRI Dhan Hybrid 1 (IR69690H) IR58025A/BR827-35-2-1-1-1R Public Bangladesh 2001<br />

HRI 120 (6444) <strong>IRRI</strong>-bred A line Private India 2001<br />

Intani 1 <strong>IRRI</strong>-bred A and R line Private Indonesia 2001<br />

Intani 2 <strong>IRRI</strong>-bred A and R line Private Indonesia 2001<br />

Rokan (IR69690H) IR58025A/BR827-35-2-1-1-1R Public Indonesia 2002<br />

Maro IR58025A and <strong>IRRI</strong>-developed R line Public Indonesia 2002<br />

Mestizo 2 (NSIC Rc114H or IR75207H) IR68888A/IR62161-184-3-1-3-2R Public Philippines 2002<br />

Mestizo 3 (NSIC Rc116H or IR75217H) IR68897A/IR60819-34-2R Public Philippines 2002<br />

Bigante (NSIC Rc124H or Mestizo 4) Developed using <strong>IRRI</strong> germplasm Private Philippines 2004<br />

IR78386H a IR68897A/IR71604-4-1-4-4-4-2-2-2R Public Philippines 2004<br />

a Recommended for release by the <strong>Rice</strong> Technical Working Group, Philippines, 25 November 2004.<br />

most 1.4 million ha were covered with rice hybrids in India<br />

(560,000 ha), the Philippines (200,000 ha), Vietnam (600,000<br />

ha), Bangladesh (40,000 ha), Indonesia (5,000 ha), and<br />

Myanmar (5,000 ha). <strong>Rice</strong> hybrids have also been commercialized<br />

in the United States (Walton 2003) and Japan (Takita<br />

2003). Several other countries (Sri Lanka, Thailand, Egypt,<br />

Brazil, Iran, Malaysia, and Pakistan) should be commercializing<br />

this technology in the next 3–5 years.<br />

<strong>Rice</strong> hybrids have also shown significant heterosis for<br />

earliness. The higher yield coupled with slightly shorter duration<br />

resulted in higher per-day productivity (68–78 kg d –1<br />

ha –1 ) than inbred HYVs (62–72 kg d –1 ha –1 ) (Virmani and<br />

Kumar 2004). The shorter duration of rice hybrids can result<br />

in a savings of water and creation of niches w<strong>here</strong> an additional<br />

crop can be grown to allow crop diversification. Peng et<br />

al (2003) observed higher N-use efficiency in an <strong>IRRI</strong>-rice<br />

hybrid—IR68284H (named as Mestizo 1 in the Philippines)—<br />

than in a widely grown inbred HYV, IR72. Earlier studies at<br />

<strong>IRRI</strong> had shown a significantly higher response of an <strong>IRRI</strong><br />

hybrid (IR64616H, named as Magat in the Philippines) to the<br />

application of N at booting than IR72. These results clearly<br />

show the increased production efficiency of rice hybrids compared<br />

with inbred rice and illustrate how hybrid rice becomes<br />

relevant in the current competitive global economic scenario.<br />

Breeding of parental lines to exploit heterosis in rice<br />

Cytoplasmic male sterility and the fertility restoration system<br />

have been primarily used to develop heterotic rice hybrids in<br />

and outside China (Virmani 1996). During the past decade,<br />

thermo- (TGMS) and photoperiod-sensitive genic male sterility<br />

(PGMS) systems have also been developed in China (Ma<br />

and Yuan 2003) and outside China (Virmani and Ilyas-Ahmed<br />

2001). Commercially usable parental lines to develop tropical<br />

rice hybrids must have adaptability to tropical conditions. In<br />

addition, the male sterile lines used for this purpose must have<br />

complete and stable male sterility, and good outcrossing potential<br />

essential for economically viable hybrid seed production.<br />

Likewise, commercially usable restorer lines should restore<br />

normal fertility in the derived hybrids and provide adequate<br />

pollen for a prolonged period for economically viable<br />

seed production. The TGMS system is the most effective for<br />

developing tropical rice hybrids; the PGMS system cannot be<br />

used for lack of sufficient variation in daylength during the<br />

year (Virmani and Ilyas-Ahmed 2001). Tropical TGMS lines<br />

possessing a low critical sterility point (CSP), complete and<br />

stable male sterility in the wet and dry seasons, and good fertility<br />

reversion in available high-altitude locations are now<br />

available at <strong>IRRI</strong> and in national programs.<br />

Session 5: Broadening the gene pool and exploiting heterosis in cultivated rice 163


Among the first set of <strong>IRRI</strong>-bred CMS lines, IR58025A,<br />

IR62829A, IR68888A, and IR68897A have been used to develop<br />

several tropical commercial rice hybrids in India, the<br />

Philippines, Vietnam, Indonesia, and Bangladesh (Table 1).<br />

The most widely used CMS line, IR58025A, resulted in hybrids<br />

possessing aroma and somewhat sticky grains on cooking.<br />

More recently, CMS lines possessing better grain quality<br />

and higher outcrossing than IR58025A have been developed<br />

(Virmani and Kumar 2004). Some of these also possess a different<br />

CMS system. These are being used extensively at <strong>IRRI</strong><br />

and are shared with public and private research institutions in<br />

national agricultural research and extension systems (NARES)<br />

to enable them to breed improved hybrids.<br />

Elite indica and indica/tropical japonica derivative lines<br />

possess 30–40% restorer lines, which are usable as such to<br />

develop heterotic rice hybrids in tropical countries. Restorer<br />

frequency in temperate and tropical japonica rice is negligible<br />

and is very low in basmati rice. To develop rice hybrids in<br />

these genetic backgrounds, restorer lines have to be bred by<br />

transferring Rf genes from indica rice. To increase the frequency<br />

of restorer and maintainer lines in the tropics, R × R and B × B<br />

crosses are made routinely in <strong>IRRI</strong>’s hybrid rice breeding program.<br />

The nuclear male sterility–facilitated recurrent selection<br />

approach is also being used to develop maintainer and<br />

restorer composite populations from which B and R lines are<br />

extracted. These populations are also shared with national programs<br />

to enable them to extract locally adapted B and R lines.<br />

Marker-aided selection, using STS markers found linked with<br />

Rf3 and Rf4 genes, is being used at <strong>IRRI</strong> to increase the efficiency<br />

of selecting fertility restorer lines for wild abortive<br />

(WA), Dissi, and Gambiaca cytoplasm inducing male sterility<br />

in rice.<br />

Six <strong>IRRI</strong>-bred TGMS lines—IR68301S, IR73727-23S,<br />

IR73834S, IR75589-31S, IR75589-41-13-17-15-3S, and<br />

IR75589-41-13-17-15-22S—have been found to have a low<br />

CSP and are being used to develop tropical two-line rice hybrids.<br />

Other tropical rice-growing countries (India, Vietnam,<br />

and the Philippines) are also developing TGMS lines. Markeraided<br />

selection has been used at <strong>IRRI</strong> to pyramid tms genes to<br />

develop more stable TGMS lines.<br />

Grain quality and biotic resistance of rice hybrids<br />

Acceptable grain quality of the commercial rice hybrids is essential<br />

to ensure profitability to hybrid rice farmers. Hybridity<br />

does not impair grain quality if the parents chosen to develop<br />

heterotic hybrids possess acceptable grain quality (Khush et<br />

al 1988). T<strong>here</strong>fore, a critical evaluation of parents for grain<br />

quality is necessary before using them in hybrid breeding. Similarly,<br />

hybrids showing strong heterosis for yield should be<br />

evaluated critically for grain quality before their release and<br />

commercialization.<br />

Biotic stress resistance of hybrids was determined by<br />

the resistance of their parental lines and evaluating whether<br />

this resistance was dominant or recessive. Hybrid vigor does<br />

not make rice hybrids more or less resistant than the parental<br />

lines (Cohen et al 2003). The most widely used WA-CMS<br />

system was not found associated with susceptibility to blast,<br />

bacterial blight, brown planthopper, and whitebacked<br />

planthopper. Nevertheless, the use of genetically diverse CMS<br />

systems is advocated to avoid potential genetic vulnerability<br />

of rice hybrids in the tropics w<strong>here</strong> disease/insect pressure is<br />

high.<br />

Hybrid rice seed production technology<br />

and rural employment opportunities<br />

Extensive research and seed production experiences in China,<br />

at <strong>IRRI</strong>, and in other countries have helped in identifying guidelines<br />

and practices for hybrid rice seed production, which are<br />

packaged in manuals (Virmani and Sharma 1993) and research<br />

papers (Mao 1988, Virmani 1996, Virmani et al 2002, Virmani<br />

and Kumar 2004). A seed production manual is also available<br />

in CD form and can be accessed from the <strong>IRRI</strong> Knowledge<br />

Bank at www.knowledgebank.irri.org/hybrid<strong>Rice</strong>Seed/<br />

hybrid<strong>Rice</strong>Seed.htm. Using these practices, hybrid seed yields<br />

ranging from 0.7 to 4 t ha –1 (average 1–1.5 t ha –1 ) have been<br />

obtained in the tropics. Seed yields are getting higher as seed<br />

growers and their supervisors gain experience.<br />

The production of hybrid rice seed is labor-intensive but<br />

economically viable enough to attract seed companies. More<br />

than 60 seed companies in the public, private, and NGO sectors<br />

are working in Asia to produce and market hybrid rice<br />

seeds. Seed production operations (such as differential planting<br />

of male and female rows, roguing, flag-leaf clipping, GA 3<br />

application, separate harvesting and processing of pollen and<br />

seed parents, etc.) require at least 50 person-days of additional<br />

labor compared with normal nonmechanized inbred rice cultivation.<br />

Increasing area under hybrid rice creates increasing<br />

demand for hybrid rice seeds, resulting in large areas of hybrid<br />

seed production, which in turn creates additional rural<br />

employment opportunities in labor-surplus countries through<br />

the seed industry. In labor-scarce countries, such as Japan and<br />

the U.S., hybrid rice seed production technology is mechanized<br />

(Walton 2003, Takita 2003).<br />

Future opportunities<br />

Opportunities exist to enhance heterosis through indica/tropical<br />

japonica crosses since the level of heterosis of intervarietal<br />

groups is higher than in intravarietal groups (Virk et al 2003).<br />

Recent results at <strong>IRRI</strong> have shown stronger heterosis for yield<br />

in indica/new plant type (NPT) crosses in which the NPT parent<br />

was derived from indica/tropical japonica crosses (Table<br />

2). The identification and use of heterotic groups and gene<br />

blocks may also help to further enhance heterosis. Hybrid<br />

breeding efficiency is increased by using the TGMS system<br />

and nuclear male sterility–facilitated recurrent selection to<br />

breed parental lines. Also, molecular marker-aided selection<br />

helps in identifying fertility restorers, TGMS lines, and heterotic<br />

gene blocks. Transgenic parental lines possessing resistance<br />

to bacterial blight and stem borers can be developed by<br />

164 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 2. Percent heterosis for yield in indica/NPT hybrids versus indica/indica hybrids<br />

evaluated in retestcross nursery at <strong>IRRI</strong>, 2004 wet season.<br />

Total no. % Percent yield advantage over<br />

Hybrid of hybrids heterotic best inbred check<br />

tested hybrids<br />

Range<br />

Mean<br />

Indica/indica 85 40.0 1.33– 81.40 30.57 ± 23.68<br />

Indica/NPT 40 47.5 5.81–131.40 42.7 ± 37.66<br />

using Xa21 and Bt genes to develop transgenic rice hybrids<br />

possessing resistance to these stresses.<br />

Early vegetative vigor and the better developed root system<br />

of hybrid rice make it adaptable to low-temperature-prone<br />

(during the boro season) and salinity-prone irrigated rice areas.<br />

Recent results at <strong>IRRI</strong> showed better adaptation of certain<br />

hybrids under alternate wetting-and-drying conditions and indicated<br />

prospects for increasing water-use efficiency through<br />

hybrids. Hybrids have also shown better adaptation to aerobic<br />

conditions (George et al 2002) and certain rainfed lowland<br />

conditions. Hence, the prospects for hybrid rice in these ecosystems<br />

should be explored. Brown rice of some rice hybrids<br />

was found to show a higher iron content in their grain than<br />

popular inbred HYVs and t<strong>here</strong> was evidence of heterosis for<br />

this trait (Gregorio, pers. comm.); hence, commercial rice hybrids<br />

in and outside China should be critically evaluated for<br />

iron and zinc content in their brown and polished rice to find<br />

out whether any of these happen to combine high yield with<br />

high iron and zinc content. Continuous diversification of CMS<br />

systems of commercial rice hybrids would be a good strategy<br />

to avoid the risk of potential genetic vulnerability associated<br />

with some disease/insect problems. Apomixis is the ultimate<br />

genetic tool to fix heterosis in rice, which would make it widely<br />

used even by resource-poor farmers. Attempts should t<strong>here</strong>fore<br />

be intensified to develop this tool using modern genetic<br />

tools.<br />

Heterosis in rice is useful for increasing farmers’ income,<br />

contributing to national food security, and increasing production<br />

efficiency. The associated labor-intensive hybrid seed production<br />

helps to create additional rural employment opportunities<br />

through the seed industry.<br />

References<br />

Cohen MB, Bernal CC, Virmani SS. 2003. Do rice hybrids have<br />

heterosis for insect resistance A study with Nilaparvata lugens<br />

(Hemiptera: Delphacidae) and Marasmia patnalis (Lepidoptera:<br />

Pyralidae). J. Econ. Entomol. 96(6):1935-1941.<br />

Duvick DN. 1999. Heterosis: feeding people and protecting natural<br />

resources. In: Coors JG, Pandey S, editors. The genetics and<br />

exploitation of heterosis in crops. Madison, Wis. (USA):<br />

American Society of Agronomy, Crop Science Society of<br />

America, Soil Science Society of America. p 19-29.<br />

George, T, Magbanua R, Laza M, Atlin G, Virmani S. 2002. Magat,<br />

a wetland semidwarf hybrid rice for high-yielding production<br />

on irrigated dryland. Int. <strong>Rice</strong> Res. Notes 27(1):26-28.<br />

Khush GS, Kumar I, Virmani SS. 1988. Grain quality of hybrid rice.<br />

In: Hybrid rice. Proceedings of the <strong>International</strong> Symposium<br />

on Hybrid <strong>Rice</strong>, Changsha, Hunan, China, 6-10 Oct. 1986.<br />

p 201-215.<br />

Ma GH, Yuan LP. 2003. Hybrid rice achievements and development<br />

in China. In: Virmani SS, Mao CX, Hardy B, editors. Hybrid<br />

rice for food security, poverty alleviation, and environmental<br />

protection. Proceedings of the 4th <strong>International</strong> Symposium<br />

on Hybrid <strong>Rice</strong>, Hanoi, Vietnam, 14-17 May 2002. Los Baños<br />

(Philippines): <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>. p 247-<br />

256.<br />

Mao CX. 1988. Hybrid rice seed production in China. In: <strong>Rice</strong> seed<br />

health. Manila (Philippines): <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>.<br />

p 277-282.<br />

Peng S, Yang J, Laza RC, Sanico AL, Visperas RM, Son TT. 2003.<br />

Physiological bases of heterosis and crop management strategies<br />

for hybrid rice in the tropics. In: Virmani SS, Mao CX,<br />

Hardy B, editors. Hybrid rice for food security, poverty alleviation,<br />

and environmental protection. Proceedings of the 4th<br />

<strong>International</strong> Symposium on Hybrid <strong>Rice</strong>, Hanoi, Vietnam,<br />

14-17 May 2002. Los Baños (Philippines): <strong>International</strong> <strong>Rice</strong><br />

<strong>Research</strong> <strong>Institute</strong>. p 153-172.<br />

Takita T. 2003. Hybrid rice research and development in Japan. In:<br />

Virmani SS, Mao CX, Hardy B, editors. Hybrid rice for food<br />

security, poverty alleviation, and environmental protection.<br />

Proceedings of the 4th <strong>International</strong> Symposium on Hybrid<br />

<strong>Rice</strong>, Hanoi, Vietnam, 14-17 May 2002. Los Baños (Philippines):<br />

<strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>. p 337-340.<br />

Virk PS, Khush GS, Virmani SS. 2003. Breeding strategies for enhancing<br />

heterosis in rice. In: Virmani, SS, Mao CX, Hardy B,<br />

editors. Hybrid rice for food security, poverty alleviation, and<br />

environmental protection. Proceedings of the 4th <strong>International</strong><br />

Symposium on Hybrid <strong>Rice</strong>, Hanoi, Vietnam, 14-17 May 2002.<br />

Los Baños (Philippines): <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>.<br />

p 21-30.<br />

Virmani SS. 1996. Hybrid rice. Adv. Agron. 57:377-462.<br />

Virmani SS, Ilyas-Ahmed M. 2001. Environment-sensitive genic<br />

male sterility (EGMS) in crops. Adv. Agron. 72:139-195.<br />

Virmani SS, Kumar I. 2004. Development and use of hybrid rice<br />

technology to increase rice productivity in the tropics. Int.<br />

<strong>Rice</strong> Res. Notes 29(1):10-20.<br />

Virmani SS, Mao CX, Hardy B, editors. 2003. Hybrid rice for food<br />

security, poverty alleviation, and environmental protection.<br />

Proceedings of the 4th <strong>International</strong> Symposium on Hybrid<br />

<strong>Rice</strong>, Hanoi, Vietnam, 14-17 May 2002. Los Baños (Philippines):<br />

<strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>. 407 p.<br />

Session 5: Broadening the gene pool and exploiting heterosis in cultivated rice 165


Virmani SS, Mao CX, Toledo RS, Hossain M, Janaiah A. 2002.<br />

Hybrid rice seed production technology and its impact on seed<br />

industries and rural employment opportunities in Asia. Technical<br />

Bulletin 156. Taiwan (China): Food & Fertilizer Technology<br />

Center.<br />

Virmani SS, Sharma HL. 1993. Manual for hybrid rice seed production.<br />

Manila (Philippines): <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>.<br />

Walton M. 2003. Hybrid rice for mechanized agriculture. In: Virmani<br />

SS, Mao CX, Hardy B, editors. Hybrid rice for food security,<br />

poverty alleviation, and environmental protection. Proceedings<br />

of the 4th <strong>International</strong> Symposium on Hybrid <strong>Rice</strong>,<br />

Hanoi, Vietnam, 14-17 May 2002. Los Baños (Philippines):<br />

<strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>. p 97-104.<br />

Notes<br />

Author’s address: Principal scientist (plant breeding), <strong>International</strong><br />

<strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>, DAPO Box 7777, Metro Manila,<br />

Philippines, e-mail: s.virmani@cgiar.org.<br />

Harnessing molecular markers in hybrid rice<br />

commercialization in the Philippines<br />

E.D. Redoña, L.M. Perez, L.R. Hipolito, V.E. Elec, I.A. Pacada, L.M. Borines, R.O. Solis, S.A. Ordoñez, and J. Agarcio<br />

In 2002, commercialization of hybrid rice technology became<br />

Philippine agriculture’s banner program for attaining self-sufficiency<br />

and increasing productivity and profitability in rice,<br />

and generating rural employment. Four public hybrids (Magat,<br />

Mestizo, Mestiso 2, and Mestiso 3) and four proprietary hybrids—Magilas<br />

(Monsanto), SL8 (SL Agritech), Bigante<br />

(Bayer CropScience), and Rizalina 28 (Hy<strong>Rice</strong>)—were made<br />

available to farmers. With intensified training efforts, 40 seed<br />

growers’ cooperatives were formed that produce 60–70% of<br />

the program’s seed requirements. From 2001 to 2003, hybrids<br />

yielded 6.03 t ha –1 versus the 4.44 t ha –1 average for certified<br />

inbred seeds. Average seed production yields increased from<br />


A<br />

PR1A<br />

PR2A<br />

IR62829A<br />

JinanteA<br />

913A<br />

PMS8A<br />

PragathiA<br />

IR58025A<br />

IR68901A<br />

IR68886A<br />

IR68901A<br />

IR68896A<br />

IR68902A<br />

IR78371A<br />

IR70960A<br />

IR69626A<br />

IR68280A<br />

IR69627A<br />

IR69622A<br />

28A<br />

IR70963A<br />

LianA<br />

Phil<strong>Rice</strong><br />

Phil<strong>Rice</strong><br />

<strong>IRRI</strong><br />

YAU<br />

YAU<br />

<strong>IRRI</strong><br />

<strong>IRRI</strong><br />

<strong>IRRI</strong><br />

<strong>IRRI</strong><br />

<strong>IRRI</strong><br />

<strong>IRRI</strong><br />

<strong>IRRI</strong><br />

<strong>IRRI</strong><br />

<strong>IRRI</strong><br />

<strong>IRRI</strong><br />

<strong>IRRI</strong><br />

<strong>IRRI</strong><br />

<strong>IRRI</strong><br />

<strong>IRRI</strong><br />

YAU<br />

<strong>IRRI</strong><br />

YAU<br />

1<br />

2<br />

3<br />

4<br />

5<br />

6<br />

7<br />

8<br />

9<br />

Cluster 1<br />

Cluster 2<br />

B<br />

0.00 0.25 0.50 0.75 1.00<br />

PR24067A a<br />

PR35731 a<br />

GinA c<br />

28 A c<br />

913 A c<br />

PMS8 A a<br />

IR58025A b<br />

IR62829A b<br />

IR66901A b<br />

IR68902A b<br />

IR69627A b<br />

IR70371A b<br />

IR16365-5 A b<br />

Lian A c<br />

IR16549A b<br />

IR17076A b<br />

BO A d<br />

IR68886A b<br />

IR69625A b<br />

IR69625A b<br />

IR70369A b<br />

IR72079A b<br />

PR35732A a<br />

IR72083A b<br />

IR70368A b<br />

IR72795A b<br />

PR35733A a<br />

PR35734A a<br />

PR35735A a<br />

PR35736A a<br />

PR35737A a<br />

PMS10 A c<br />

PR35738A a<br />

Pragathi A c<br />

MH841-21 A c<br />

IR68896A b<br />

IR69626A b<br />

IR68280A b<br />

IR16727-7A b<br />

IR69617A b<br />

IR16331A b<br />

IR16375A b<br />

IR69622A b<br />

PR35739A a<br />

IR68888A b<br />

IR70370A b<br />

1<br />

2<br />

3<br />

4<br />

5<br />

6<br />

7<br />

8<br />

C<br />

IR58025B<br />

85.1<br />

100<br />

IR78378B<br />

IR78375B<br />

IR78376B<br />

IR79123B<br />

IR78369B<br />

(59.2%)<br />

94.9<br />

IR68888B<br />

IR68897B<br />

IR70369B<br />

(69%)<br />

IR73328B<br />

PR3B<br />

97.2<br />

IR78367B<br />

(~58%)<br />

PR2B<br />

PR4B<br />

PR9B<br />

0.57 0.68 0.78 0.89 1.00<br />

Coefficient<br />

<strong>IRRI</strong><br />

Phil<strong>Rice</strong><br />

98.1<br />

(76.5%)<br />

100.0<br />

0.52 0.63 0.74 0.85 0.96<br />

IR68301s<br />

IR73827-23s<br />

IR73834s<br />

Fig. 1. Diversity analysis of hybrid rice germplasm. (A) CMS line dendrogram using 20 microsatellite markers, 25 RAPDs, and 10 +3/+3<br />

AFLP primer combinations (Redoña et al 1998). (B) Clustering of 46 diverse CMS lines based on 65 microsatellite loci. (C) Dendrogram of<br />

15 maintainer (B) lines based on 64 microsatellite loci and 255 allele types (Perez 2004). (D) Six TGMS lines clustered using 64 microsatellite<br />

loci and 129 allele types (Perez 2004).<br />

D<br />

(52.1%)<br />

(63.5%)<br />

Coefficient<br />

100.0<br />

(90.1%)<br />

(96.4%)<br />

TGMS1<br />

TGMS4<br />

TGMS6<br />

<strong>IRRI</strong><br />

Phil<strong>Rice</strong><br />

performance of the hybrids was highest for grain yield and<br />

percent spikelet fertility at 62% and 25.6%, respectively. However,<br />

the relationship between heterosis and genetic diversity<br />

was generally weak for most of the traits.<br />

Marker-aided pyramiding of bacterial blight (BB)<br />

resistance genes<br />

Some commercial hybrids in the Philippines, including the<br />

high-yielding and popular Mestizo, are susceptible to the<br />

Xanthomonas oryzae pv. oryzae (Xoo)-caused BB disease that<br />

is prevalent in the wet season. The disease can cause tremendous<br />

yield losses if severe infection occurs before flowering.<br />

To address this potential problem, single and/or pyramids of<br />

Xa4, Xa7, and Xa21 BB resistance genes were introgressed<br />

into five B lines of commercialized and promising hybrids—<br />

IR58025B, IR62829B, 913B, LianB, and BoB (Borines et al<br />

2003). B lines with 2–3 gene pyramids showed much shorter<br />

lesions in response to diagnostic Xoo races, indicating an increased<br />

and wider resistance spectrum against BB than B lines<br />

containing single genes. Xa4 and Xa7 genes together in different<br />

maintainer backgrounds imparted a complementary gene<br />

Session 5: Broadening the gene pool and exploiting heterosis in cultivated rice 167


action in conferring a higher level of resistance to race 3-<br />

PXO340, and in LianB background to race 10-PXO341.<br />

In two-line hybrid breeding, three potential TGMS materials<br />

(F 2 plants no. 450, 473, and 700) homozygous for Xa4,<br />

Xa7, and Xa21 genes were identified in a segregating population<br />

developed from the cross TGMS1(–Xa)/AR32-19-3-<br />

3(+Xa21)/DiR32(+Xa4/+Xa7) (Perez 2004). STS PCR markers<br />

M5F/R and Xa21F/R were used to detect the presence of<br />

Xa7 and Xa21, respectively (Fig. 2A). These lines exhibited<br />

high degrees of resistance to Xoo race 1 (PXO61), race 2<br />

(PXO86), and race 6 (PXO99) in the greenhouse using an induced<br />

screening method and they are potential genetic stocks<br />

for the development of BB-resistant hybrids.<br />

Molecular tagging of TGMS genes in rice<br />

In hybrid rice breeding, screening for the TGMS trait is an<br />

intensive process influenced by environment. Tagging TGMS<br />

genes from new donors with DNA markers would increase the<br />

speed and efficiency of developing two-line hybrids. Based<br />

on a 301 microsatellite marker survey, four possible chromosomal<br />

locations (i.e., chromosomes 1, 2, 6, and 12) of the tgms<br />

gene from a new donor were identified by single-marker analysis<br />

and interval mapping procedures using One-Way ANOVA<br />

and Qgene software, respectively. The highest LOD score was<br />

6.48 between RM24 and RM113 on chromosome 1 (Fig. 2B).<br />

Most of the 11 microsatellite markers highly associated with<br />

sterility were located on chromosome 6. Three peaks were identified<br />

in this region with LOD scores >3.0, indicating the presence<br />

of a possible gene/QTL for the tgms gene in chromosome<br />

6 (Fig. 2B). Saturating this region with more markers and identifying<br />

tightly linked markers for use in TGMS line selection<br />

would expedite two-line hybrid development, thus further widening<br />

the genetic base of hybrids for the Philippine commercialization<br />

program.<br />

Hybrid seed purity analysis based on mitochondrial<br />

genome analysis<br />

Genetic purity in hybrid seeds is essential for full heterosis<br />

expression and is t<strong>here</strong>fore a prerequisite for a successful commercialization<br />

program. Based on analysis of mitochondrial<br />

DNA sequences of CMS and fertile rice, the orf61-atp6-orf79<br />

region of the rice mitochondrial genome revealed two regions<br />

polymorphic among IR58025A (CMS), its B line (IR58025B),<br />

and hybrid (Mestizo). The a6P5 and MdF1 primers designed<br />

to amplify these regions produced 300-bp and 500-bp bands,<br />

respectively, that discriminated the B line from the CMS line<br />

and the hybrid. Successful detection of B line off-types in mixtures<br />

was demonstrated using the bulked DNA assay. This technique<br />

is starting to be used by the Philippine National Seed<br />

Quality Control Services for seed purity testing in the hybrid<br />

commercialization program.<br />

Conclusions<br />

DNA marker applications are finding relevant uses in addressing<br />

problems and challenges arising from commercializing<br />

hybrid rice in the Philippines. Genetic diversity analyses using<br />

markers have been useful for ensuring a diverse germplasm<br />

pool for hybrid breeding and avoiding the redundant use of<br />

similar genetic materials. While the utility of randomly selected<br />

markers for predicting heterosis cannot as yet be ascertained,<br />

the usefulness of markers in the tagging and pyramiding of<br />

useful genes in parental materials, and in seed purity analysis,<br />

has been demonstrated. As intellectual property protection<br />

becomes emphasized, with the recent passage of the Philippine<br />

Plant Variety Protection Law, DNA profiling and identification<br />

of diagnostic alleles for specific hybrid germplasm<br />

will find useful applications. An exciting but yet unsuccessful<br />

application of molecular markers is in the development of heterotic<br />

pools to enhance and sustain higher heterosis levels. As<br />

the Philippines needs to produce 65% more rice relative to<br />

current production by 2025, promising biotechnological tools<br />

such as molecular marker technology will continue to be used<br />

for increasing the speed, efficiency, and accuracy of hybrid<br />

rice breeding procedures while finding other relevant applications<br />

in other aspects of hybrid rice technology commercialization.<br />

References<br />

Borines LM, Redoña ED, Porter B, White F, Natural MP, Vera Cruz<br />

CM, Leung H. 2003. Marker-assisted pyramiding of bacterial<br />

blight resistance in parental lines of hybrid rice. In: Proceedings<br />

of the Arnel R. Hallauer <strong>International</strong> Symposium on Plant<br />

Breeding, Mexico City, Mexico. p 168-169.<br />

Ordoñez SA. 2003. Genetic variation of restorer lines in rice (Oryza<br />

sativa L.). Unpublished MS thesis. University of the Philippines<br />

Los Baños, Laguna, Philippines. 83 p.<br />

Perez LM. 2004. Development of bacterial blight-resistant<br />

thermosensitive genetic male sterile (TGMS) lines for hybrid<br />

rice (Oryza sativa L.) production. Unpublished MS thesis.<br />

University of the Philippines Los Baños, Laguna, Philippines.<br />

92 p.<br />

Redoña ED, Hipolito LR, Ocampo TD, Sebastian LS. 1998. Molecular<br />

polymorphism of rice cytoplasmic-genetic male sterile<br />

(CMS) lines based on AFLP, RAPD and microsatellite<br />

markers. Philipp. J. Crop Sci. 23(1):12-20.<br />

Notes<br />

Authors’ addresses: E.D. Redoña, L.M. Perez, L.R. Hipolito, V.E.<br />

Elec, I.A. Pacada, R.O. Solis, S.A. Ordoñez, and J. Agarcio,<br />

Philippine <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong> (Phil<strong>Rice</strong>), Muñoz, Nueva<br />

Ecija, Philippines; L.M. Borines, Leyte State University<br />

(LSU), Baybay, Leyte, Philippines, e-mail:<br />

edredona@philrice.gov.ph.<br />

168 <strong>Rice</strong> is life: scientific perspectives for the 21st century


A<br />

M<br />

TGMS1<br />

IRBB4/7<br />

AR32-19-3-3<br />

IRBB7<br />

IRBB4<br />

IR24<br />

450<br />

473<br />

700<br />

M<br />

1,170 bp<br />

294 bp<br />

1,000 bp<br />

Chr 1<br />

Chr 6<br />

B<br />

RM128<br />

RM170<br />

RM259<br />

RM220<br />

RM275<br />

RM237<br />

RM1<br />

RM276<br />

RM5<br />

RM111<br />

RM140<br />

RM113<br />

RM3<br />

RM248<br />

RM24<br />

RM162<br />

RM102<br />

6.48 3.0 0.0<br />

LOD<br />

RM243<br />

3.0 0.0<br />

LOD<br />

RM50<br />

Fig. 2. Use of DNA markers in two-line hybrid breeding. (A) Genotyping of potential TGMS<br />

materials (F 2 plants no. 450, 473, and 700) showing the 294-bp allele for Xa7 (M5F/R primer)<br />

and 1,000-bp allele for Xa21 (Xa21F/R primer) for bacterial blight resistance in rice. TGMS1 is<br />

a susceptible parent, w<strong>here</strong>as IRBB4/7 (DiR32) and AR32-19-3-3 are donor parents for Xa4/<br />

Xa7 and Xa21, respectively. IRBB7, IRBB4, and IR24 are check varieties (Perez 2004). (B)<br />

Possible location of tgms gene (LOD = 6.48) on chromosome 1. Three peaks with LOD>3.0<br />

found on chromosome 6 suggest the presence of a QTL.<br />

Session 5: Broadening the gene pool and exploiting heterosis in cultivated rice 169


Genetic evolution of Rf1 locus for the fertility restorer gene<br />

of BT-type CMS rice<br />

Tomohiko Kazama and Kinya Toriyama<br />

Cytoplasmic male sterility (CMS) is a maternally inherited trait<br />

that results in the inability to produce fertile pollen. It is usually<br />

attributed to mitochondrial defects. In some cases, pollen<br />

fertility is recovered by a nuclear-encoded gene, the fertility<br />

restorer gene (Rf). Recently, Rf genes have been cloned in<br />

Petunia (Bentolila et al 2002) and kosena radish (Koizuka et<br />

al 2003). Both of the Rf genes have been shown to encode the<br />

PPR motif. PPR proteins contain a characteristic tandem array<br />

of 35 amino acid motifs, and t<strong>here</strong>fore are termed a<br />

pentatricopeptide repeat (Small and Peeters 2000). The identification<br />

of Rf genes in Petunia and radish as PPR-containing<br />

genes suggests that searching for PPR motif genes near known<br />

restorer loci should be a useful strategy to identify Rf genes in<br />

other species.<br />

In rice, one particular CMS system has been obtained<br />

by combining the cytoplasm of Chinsurah Boro II with the<br />

nuclear genome of Taichung 65 (Shinjyo 1975). It is called<br />

BT-type. In this CMS line, pollen fertility can be restored<br />

gametophytically by the presence of a single dominant nuclear<br />

gene, Rf1. It has been reported that t<strong>here</strong> are two copies of<br />

atp6 in BT-type mitochondria (Akagi et al 1994, Iwabuchi et<br />

al 1993, Kadowaki et al 1990). One is a normal atp6 (N-atp6),<br />

which is usually present in rice mitochondria. The other is an<br />

additional atp6 (B-atp6), which contains a unique sequence<br />

(orf79) located downstream of the normal atp6 sequence.<br />

We followed a positional cloning strategy to identify the<br />

Rf1 gene. After mapping of the Rf1 locus, we searched for<br />

ORFs containing a mitochondrial targeting signal and PPR<br />

motif in the genome of Nipponbare. Three such genes, named<br />

PPR8-1, PPR8-2, and PPR8-3, respectively, existed in a tandem<br />

array. The genomic fragments of each gene were obtained<br />

from cultivar Milyang23, whose genotype is Rf1/Rf1, and were<br />

introduced into a CMS line, BTA (rf1/rf1) (Kazama and<br />

Toriyama 2003).<br />

Here we report on the pollen and seed fertility in the<br />

complementation test. Restoration of fertility by the PPR8-1<br />

gene demonstrated that PPR8-1 was the Rf1 gene. Processing<br />

of the B-atp6 and N-atp6 RNA was examined in transgenic<br />

plants. In view of the sequence similarity of Rf1 to PPR8-2<br />

and PPR8-3, the genomic evolution of the Rf1 gene was discussed.<br />

Complementation tests and analysis of transgenic plants<br />

Each DNA fragment containing Rf1, PPR8-2, and PPR8-3 was<br />

introduced into a CMS line, BTA (rf1/rf1), by Agrobacteriummediated<br />

gene transfer. Pollen fertility was examined in 35<br />

A B C<br />

Fig. 1. Restoration of pollen and seed fertility in the complementation<br />

test. (A) Sterile pollen of a CMS line (BTA [ms-bo]rf1/rf1).<br />

(B) Pollen of the transgenic BTA line with the PPR8-1 gene. Half of<br />

the pollen grains were stained with I 2 -KI solution, indicating that<br />

the fertility of pollen grains with the PPR8-1 gene was restored.<br />

(C) Normal seed set of the transgenic BTA line with the PPR8-1<br />

gene.<br />

transgenic plants with the PPR8-1 gene. Twenty plants showed<br />

near 50% fertility, indicating that the transgene was segregated<br />

in the pollen, and pollen with PPR8-1 restored the fertility<br />

(Fig. 1). These transgenic plants with the PPR8-1 showed normal<br />

seed set (Fig. 1), demonstrating that the PPR8-1 gene restored<br />

the fertility. Fertility was not restored by PPR8-2 or<br />

PPR8-3 genes. These results demonstrated that PPR8-1 was<br />

the Rf1 gene.<br />

To reveal the possible interaction between Rf1 protein<br />

and the CMS-associated gene in mitochondria, we focused on<br />

the transcripts of orf79 that had been reported to be specific<br />

for Rf1 genotype and derived from the processing of the B-<br />

atp6 RNA. A portion of the 3′ end of B-atp6 containing orf79<br />

was used as a probe for Northern blot analysis of mature anthers.<br />

The transcripts of orf79 were detected in BTR (Rf1/Rf1)<br />

and F 1 (Rf1/rf1), but not in BTA (rf1/rf1), as previously reported.<br />

In the transgenic BTA with Rf1, the signal was detected.<br />

In contrast, the signal was not detected in the transgenic plants<br />

with PPR8-2 and PPR8-3. This result indicates that protein<br />

encoded by Rf1 is involved in processing of B-atp6 RNA.<br />

The N-atp6 RNA contains the 3′ noncoding region that<br />

may be cleaved by Rf1 protein. To investigate whether the N-<br />

atp6 RNA is processed by Rf1 protein or not, we performed<br />

RT-PCR analysis to detect specifically unprocessed N-atp6<br />

RNA. The unprocessed RNA was detected in BTA, transgenic<br />

BTA with PPR8-2, and transgenic BTA with PPR8-3. On the<br />

other hand, it was not detected in BTR (Rf1/Rf1) and transgenic<br />

BTA with Rf1, indicating that the primer site of the 3′ noncoding<br />

region in the N-atp6 was cleaved off by the action of Rf1 protein.<br />

This result indicates that Rf1 protein is also involved in<br />

N-atp6 RNA processing.<br />

170 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Sequencing of each gene<br />

To compare each gene with Rf1, we sequenced each fragment<br />

of Milyang23. The ORFs of PPR8-2 and PPR8-3 are 93.2%<br />

and 93.7% identical to Rf1 at the nucleotide level, respectively<br />

(Table 1). The ORFs of Rf1, PPR8-2, and PPR8-3 encode 791<br />

aa, 683 aa, and 794 aa, respectively. The predicted proteins of<br />

PPR8-2 and PPR8-3 are 92.3% and 89.0% similar to that of<br />

Rf1, respectively. The number of PPR motifs is 18 for Rf1, 16<br />

for PPR8-2, and 18 for PPR8-3 (Table 1). These three genes<br />

are present in a tandem array in Milyang23 and appear to be<br />

originated from triplication in the coding region, although t<strong>here</strong><br />

is a deletion in the PPR8-2 coding region. PPR8-2 and PPR8-<br />

3 were shown to be expressed in anthers.<br />

Discussion<br />

Table 1. Similarity of Rf1 to PPR8-2 and PPR8-3.<br />

Gene No. of No. of Identity<br />

amino acids PPR motifs to Rf1(%)<br />

Rf1 791 18 –<br />

PPR8-2 683 16 93.2<br />

PPR8-3 794 18 93.7<br />

Rf1 protein is likely to directly regulate the processing event<br />

of B-atp6 RNA. The structure of the 3′ flanking region of N-<br />

atp6 is quite different from that of B-atp6, yet Rf1 protein<br />

promotes the processing of N-atp6 RNA. This indicates that<br />

Rf1 protein recognizes atp6 RNA structure rather than orf79<br />

RNA or the junction between atp6 and orf79.<br />

It is interesting that t<strong>here</strong> are two highly homologous<br />

PPR genes adjacent to the Rf1 gene, and these genes do not<br />

contribute male fertility restoration and B-atp6 RNA processing.<br />

The high homology to Rf1 suggests that PPR8-2 and PPR8-<br />

3 protein may recognize a certain mitochondrial housekeeping<br />

gene RNA, in the same manner as Rf1 protein recognizes<br />

housekeeping atp6 RNA. It will be worthwhile to determine<br />

whether PPR8-2 and PPR8-3 protein affect the profile of mitochondrial<br />

housekeeping gene transcripts in transgenic plants.<br />

We propose the hypothesis that the Rf1 gene is evolved from<br />

highly homologous genes that regulate expression of certain<br />

housekeeping genes in mitochondria in order to reduce the<br />

expression of the CMS-associated gene.<br />

Materials and methods<br />

Plant materials<br />

We used near-isogenic lines that differ at the Rf1 gene locus.<br />

These lines have been derived from a backcross of Chinsurah<br />

Boro II × Taichung 65. They are [normal] rf1/rf1 Taichung 65<br />

as a maintainer line (BTB), B 21 F 1 [ms-bo] rf1/rf1 as a CMS<br />

line (BTA), and B 12 F 8 [ms-bo] Rf1/Rf1 as a restorer line (BTR).<br />

The genotype of Nipponbare is rf1/rf1 and that of Milyang23<br />

is Rf1/Rf1.<br />

Northern blot analysis<br />

Total RNA was isolated from 100 mg of mature anthers and<br />

calli of BTA, BTR, F 1 (BTA × BTR), and transformants using<br />

the RNeasy Plant mini kit (Qiagen, Hilden, Germany), and 10<br />

µg of each RNA underwent Northern blot analysis. A part of<br />

the B-atp6 gene of BTR was amplified and labeled with<br />

digoxigenin using the PCR DIG probe synthesis kit.<br />

Reverse transcription (RT)-PCR analysis<br />

First-strand cDNA was synthesized with pd(N)6 Random<br />

Hexamer primer using the First-strand cDNA synthesis kit<br />

(Amersham Biosciences Corp., Piscataway, NJ, USA). The<br />

forward primer, primer-a, lies in the 5′ noncoding region of<br />

the N-atp6 gene. The reverse primer, primer-b, lies in the 3′<br />

untranslated region of the N-atp6 gene.<br />

References<br />

Akagi H, Sakamoto M, Shinjo C, Shimada H, Fujimura T. 1994. A<br />

unique sequence located downstream from the rice mitochondrial<br />

atp6 may cause male sterility. Curr. Genet. 25:52-58.<br />

Bentolila S, Alfonso AA, Hanson MR. 2002. A pentatricopeptide<br />

repeat-containing gene restores fertility to cytoplasmic malesterile<br />

plants. Proc. Natl. Acad. Sci. USA 99:10887-10892.<br />

Iwabuchi M, Kyozuka J, Shimamoto K. 1993. Processing followed<br />

by complete editing of an altered mitochondrial atp6 RNA<br />

restores fertility of cytoplasmic male sterile rice. EMBO J.<br />

12:1437-1446.<br />

Kadowaki K, Suzuki K, Kazama S. 1990. A chimeric gene containing<br />

the 5′ portion of atp6 is associated with cytoplasmic malesterility<br />

of rice. Mol. Gen. Genet. 224:10-16.<br />

Kazama T, Toriyama K. 2003. A pentatricopeptide repeat-containing<br />

gene that promotes the processing of aberrant atp6 RNA<br />

of cytoplasmic male sterile rice. FEBS Lett. 544:99-102.<br />

Koizuka N, Imai R, Fujimoto H, Hayakawa T, Kimura Y, Kohno-<br />

Murase J, Sakai T, Kawasaki S, Imamura J. 2003. Genetic<br />

characterization of a pentatricopeptide repeat protein gene,<br />

orf687, that restores fertility in the cytoplasmic male-sterile<br />

Kosena radish. Plant J. 34:407- 415.<br />

Shinjyo C. 1975. Genetical studies of cytoplasmic male sterility and<br />

fertility restoration in rice, Oryza sativa L. Sci. Bull. Coll.<br />

Agric. Univ. Ryukyu 22:1-57.<br />

Small ID, Peeters N. 2000. The PPR motif—a TPR-related motif<br />

prevalent in plant organellar proteins. Trends Biochem. Sci.<br />

25:46-47.<br />

Notes<br />

Authors’ address: Graduate School of Agricultural Science, Tohoku<br />

University, e-mail: tomo-k@bios.tohoku.ac.jp.<br />

Acknowledgments: We thank Kazue Imataka for her helpful technical<br />

assistance for the transformation of rice plants. This study<br />

was partially supported by a grant-in-aid from the Ministry of<br />

Education, Science, and Culture, Japan, and by a grant for the<br />

<strong>Rice</strong> Genome Project from the Ministry of Agriculture, Forestry,<br />

and Fisheries, Japan.<br />

Session 5: Broadening the gene pool and exploiting heterosis in cultivated rice 171


A polygenic balance model in yield components as revealed<br />

by QTL analysis in rice<br />

Wilhelm E. Hagiwara, Kazumitsu Onishi, Itsuro Takamure, and Yoshio Sano<br />

Under stabilizing selection, typical or intermediate phenotypes<br />

are favored, encouraging the development of hidden variation<br />

within and between populations (Mather and Jinks 1982).<br />

Based on the polygenic balance theory, repulsion phase linkage<br />

could be accumulated along a chromosome as demonstrated<br />

in Drosophila (Thoday 1960). Such a linked group of polygenes<br />

might be reshuffled through recombination, resulting in<br />

the formation of newly derived extreme phenotypes or transgression.<br />

Our study was conducted to gain insight into the genetic<br />

architecture of quantitative traits in grain characteristics<br />

between the two rice subspecies, the so-called indica and<br />

japonica types. The grain dimension is well differentiated between<br />

these two rice subspecies in a quantitative manner, affecting<br />

grain quality (Redoña and Mackill 1998). To enhance<br />

the power to detect linked QTLs with small effects, a large<br />

chromosome segment from an indica type was first introgressed<br />

by backcrosses into a japonica type of rice. Then, the<br />

introgressed segment was dissected by repeated self-pollinations<br />

after hybridization with the recurrent parent. The resulting<br />

recombinant inbred lines (RILs) are expected to enhance<br />

the efficiency to detect minor QTLs because of the reduction<br />

in the residual variation. We report <strong>here</strong> that a cluster of QTLs<br />

affecting grain characteristics is present on a chromosome 6<br />

segment showing repulsion and coupling linkages, and that<br />

transgressive segregation appears through recombination within<br />

the chromosome segment.<br />

Materials and methods<br />

Plant materials<br />

T65wx was a near-isogenic line (NIL) of T65 (a japonica type<br />

of Oryza sativa from Taiwan) carrying wx (waxy) from<br />

Kinoshitamochi (japonica). T65Wx-pat was a NIL of T65 carrying<br />

a chromosome 6 segment of Patpaku, an indica type from<br />

Taiwan (Dung et al 1998). An F 1 plant between T65Wx-pat<br />

and T65wx was self-pollinated to give the F 2 generation, which<br />

was advanced to the F 7 generation using the single-seed descent<br />

(SSD) method. The plants were expected to carry different<br />

lengths of introgressed segments from Patpaku in the T65wx<br />

background and they were regarded as near-isogenic RILs. In<br />

total, 163 RILs were established and used in our experiment.<br />

Grain characteristics were measured in seeds (unhulled grains)<br />

and kernels (hulled grains) of the RILs (F 7 generation) and the<br />

parents. For each of the 163 RILs, two plants were examined.<br />

The average length and breadth (expressed in mm) from 6 seeds<br />

per plant and the weight (in grams) of 10 grains per plant were<br />

calculated.<br />

Genotyping with molecular markers<br />

A total of 17 PCR-based markers were used to determine the<br />

extent of the introgressed chromosome segments in the RILs.<br />

Nine of these markers (RM508, RM589, RM510, RM204,<br />

RM314, RM253, RM136, RM527, and RM3) were<br />

microsatellite markers (McCouch et al 2002), and one marker<br />

(C214) was a cleaved amplified polymorphic sequence (CAPS)<br />

marker (<strong>Rice</strong> Genome <strong>Research</strong> Program, http://<br />

rgp.dna.affrc.go.jp). In addition, three PCR-based markers were<br />

designed from two RFLP (restriction fragment length polymorphism)<br />

markers, R2291 and S1520, and one STS (sequenced<br />

tagged site) marker, R2349. In addition, gene-specific<br />

markers were designed from the Wx, Se1, RFT1, and alk<br />

genes.<br />

Data analysis<br />

A linkage map was constructed using Map Manager QTX software<br />

(Manly et al 2001). To detect QTLs, we employed interval<br />

mapping and MQM mapping methods using MapQTL version<br />

4 (Van Ooijen et al 2002). The empirical LOD thresholds<br />

corresponding to the genome-wide significance at the 1% level<br />

were estimated by permutation tests, for each trait. The additive<br />

genetic effect, the percentage of variance explained by<br />

each QTL (PVE), and the total variance explained by all the<br />

QTLs affecting a trait were obtained with MapQTL in the final<br />

multiple-QTL model in which one cofactor marker was<br />

fixed per QTL. Two-way ANOVA was used to detect digenic<br />

interactions between QTLs. The markers with the highest LOD<br />

score found by MQM mapping for each QTL were assumed to<br />

be at the possible position of the QTL.<br />

Results and discussion<br />

Segregation for seed dimension in the RILs<br />

The seed and kernel were shorter and wider in T65wx than in<br />

T65Wx-pat, suggesting that genes for the traits might be located<br />

on the introgressed segment of chromosome 6. T65wx<br />

showed higher values in the weights of seeds and kernels (SW<br />

and KW) than did T65Wx-pat. Each of the six traits showed a<br />

continuous variation among the RILs.<br />

Detection of putative QTLs for grain characteristics<br />

The linkage map was constructed based on the segregation of<br />

17 markers in all the RILs, and had a length of 72.5 cM. In<br />

total, 10 QTLs responsible for the six traits were detected<br />

(Table 1). The percentage of the phenotypic variance explained<br />

(PVE) ranged from 6.8% for a QTL controlling seed breadth<br />

(SB) to 43.7% for a QTL controlling kernel length (KL).<br />

172 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. QTLs for the six grain characteristics detected in the RILs based on the<br />

MQM mapping method. a Map position Effects on phenotype<br />

Trait NML (cM)<br />

LOD PVE a<br />

Seed length (SL) RFT1 12.6 8.82 18.4 –0.22<br />

S1520 19.3 4.77 9.4 0.17<br />

Hd1 51.8 7.04 14.3 0.14<br />

Seed breadth (SB) RFT1 12.6 6.77 14.4 –0.07<br />

S1520 19.3 3.38 6.8 0.06<br />

Hd1 51.8 5.43 11.3 –0.05<br />

Kernel length (KL) Hd1 51.8 21.30 43.7 0.16<br />

Kernel breadth (KB) RM3 62.2 10.41 24.4 –0.06<br />

Seed weight (SW) RM3 62.2 9.51 22.6 –0.01<br />

Kernel weight (KW) RM3 62.2 9.63 22.8 –0.01<br />

a<br />

NML indicates the marker locus nearest to the QTL or the marker with the highest LOD score peak.<br />

PVE is the percentage of the phenotypic variance explained. a is the additive effect of the Patpaku<br />

allele and the positive value indicates that the effect of the genotype of the indica parent (Patpaku) is<br />

in the direction of increasing the measured value of the trait.<br />

Three QTLs were detected for seed length (SL) and SB,<br />

at approximately the same locations, near the RFT1, S1520,<br />

and Hd1 markers (Table 1). Regarding the Patpaku-derived<br />

QTLs near RFT1, S1520, and Hd1, it should be noted that the<br />

QTL near RFT1 decreased both SL and SB, while that near<br />

S1520 increased both of them and the QTL near Hd1 increased<br />

SL but decreased SB (Table 1). The detection of the effect of<br />

each QTL on SL depended on the genotypes of the other two<br />

QTLs (Table 2); however, it could be due to a small number of<br />

some genotypes because two-way ANOVA failed to detect any<br />

significant interactions between QTLs for SL. For SB, twoway<br />

ANOVA detected distinct epistatic effects (interactions)<br />

between the RFT1 and Hd1 markers (F = 14.64, P = 0.0002)<br />

as well as between the Hd1 and S1520 markers (F = 7.92, P =<br />

0.0055), suggesting that the effect of each QTL also depended<br />

highly on the genotypes of the other linked QTLs for SB (Table<br />

2). For seed weight, only one QTL was detected near the RM3<br />

marker.<br />

In contrast to the characteristics of seeds, the length and<br />

breadth of kernels were each controlled by a single QTL with<br />

high LOD scores and PVE (Table 1). For KL, one QTL was<br />

detected near the Hd1 marker, and that for KB was detected<br />

near RM3, showing their slightly different position (Table 1).<br />

The Patpaku allele increased KL, w<strong>here</strong>as the T65wx allele<br />

increased KB. For KW, a single QTL was also detected near<br />

RM3.<br />

The detection of multiple QTLs of small effects in our<br />

experiments is possibly related to the elimination of effects of<br />

segregating genes on other chromosomes. The variance caused<br />

by segregation on other chromosome regions increases the residual<br />

variance for the interval under consideration, reducing<br />

the power for QTL detection (Lynch and Walsh 1998). Consequently,<br />

multiple segregating QTLs tend to reduce the efficiency<br />

to detect significant associations between phenotype<br />

and genotype in the whole-genome QTL mapping.<br />

Hidden genetic variation<br />

Actually, the RILs with the highest or lowest values in SL and<br />

SB resulted from an accumulation of QTLs with positive or<br />

negative effects (Table 2). Thus, the transgressive segregation<br />

revealed that a hidden genetic variation was concealed in the<br />

introgressed segment even though the phenotypic difference<br />

in grain characteristics was slight between the parental lines.<br />

Linked QTLs with different signs in effects are suggested to<br />

occur alternately along a chromosome under the polygenic<br />

balance model (Mather 1943). Such linked QTLs on a chromosome<br />

behave as an effective factor in segregating populations,<br />

although the polygenic balance model is an extreme<br />

metaphor (Lynch and Walsh 1998). This leads us to consider<br />

that adaptive traits might be created in part through the reconstruction<br />

of gene combinations in the flanking region using<br />

preexisting variation rather than newly derived mutations. Some<br />

agriculturally valuable traits might also have been reconstructed<br />

in this way, as predicted from frequent transgressions.<br />

References<br />

Dung LV, Inukai T, Sano Y. 1998. Dissection of a major QTL for<br />

photoperiod sensitivity in rice: its association with a gene<br />

expressed in an age-dependent manner. Theor. Appl. Genet.<br />

97:714-720.<br />

Lynch M, Walsh B. 1998. Genetics and analysis of quantitative traits.<br />

Sinauer Associates, Inc., Sunderland.<br />

Manly KF, Cudmore Jr RH, Meer JM. 2001. Map Manager QTX,<br />

cross-platform software for genetic mapping. Mammalian<br />

Genome 12:930-932.<br />

Mather K, Jinks JL. 1982. Biometrical genetics. 3rd ed. New York,<br />

NY (USA): Chapman and Hall.<br />

Mather K. 1943. Polygenic inheritance and natural selection. Biol.<br />

Rev. 18:32-65.<br />

Session 5: Broadening the gene pool and exploiting heterosis in cultivated rice 173


Table 2. Phenotypic effects of each marker allele depending on the genotypes of the<br />

other two markers (background) for seed length (SL) and breadth (SB). a<br />

Genotype<br />

Trait (in mm)<br />

Number<br />

Background Marker SL t-test SB t-test of plants<br />

allele<br />

Hd1(T); RFT1(T) S1520(T) 6.57<br />

ns<br />

3.48 * 76<br />

S1520(P) 6.80 3.63 3<br />

Hd1(T); RFT1(P) S1520(T) 5.95 ** 3.30<br />

ns<br />

7<br />

S1520(P) 6.43 3.37 20<br />

Hd1(P); RFT1(T) S1520(T) 6.80<br />

ns<br />

3.34<br />

ns<br />

17<br />

S1520(P) 6.93 3.38 4<br />

Hd1(P); RFT1(P) S1520(T) 6.38 * 3.11 ** 2<br />

S1520(P) 6.74 3.37 34<br />

S1520(T); RFT1(T) Hd1(T) 6.57 ** 3.48 ** 76<br />

Hd1(P) 6.80 3.34 17<br />

S1520(T); RFT1(P) Hd1(T) 5.95<br />

ns<br />

3.30<br />

ns<br />

7<br />

Hd1(P) 6.38 3.11 2<br />

S1520(P); RFT1(T) Hd1(T) 6.80<br />

ns<br />

3.63 * 3<br />

Hd1(P) 6.93 3.38 4<br />

S1520(P); RFT1(P) Hd1(T) 6.43 ** 3.37<br />

ns<br />

20<br />

Hd1(P) 6.74 3.37 34<br />

Hd1(T); S1520(T) RFT1(T) 6.57 ** 3.48 ** 76<br />

RFT1(P) 5.95 3.30 7<br />

Hd1(T); S1520(P) RFT1(T) 6.80<br />

ns<br />

3.63 ** 3<br />

RFT1(P) 6.43 3.37 20<br />

Hd1(P); S1520(T) RFT1(T) 6.80 ** 3.34 ** 17<br />

RFT1(P) 6.38 3.11 2<br />

Hd1(P); S1520(P) RFT1(T) 6.93<br />

ns<br />

3.38<br />

ns<br />

4<br />

RFT1(P) 6.74 3.37 34<br />

a (T) and (P) refer to the T65wx- and Patpaku-derived alleles, respectively. SL (seed length) and SB (seed<br />

breadth) were measured in mm. The statistical difference was based on the t-test. ns = not significant. *<br />

and ** show significance at 5% and 1% probability, respectively.<br />

McCouch SR, Teytelman L, Xu Y, Lobos KB, Clare K, Walton M,<br />

Fu BY, Maghirang R, Li ZK, Xing YZ, Zhang QF, Kono I,<br />

Yano M, Fjellstrom R, DeClerck G, Schneider D, Cartinhour<br />

S, Ware D, Stein L. 2002. Development and mapping of 2240<br />

new SSR markers for rice (Oryza sativa L.). DNA Res. 9:199-<br />

207.<br />

Redoña ED, Mackill DJ. 1998. Quantitative trait locus analysis for<br />

rice panicle and grain characteristics. Theor. Appl. Genet.<br />

96:957-963.<br />

Thoday JM. 1960. Effects of disruptive selection. III. Coupling and<br />

repulsion. Heredity 14:35-49.<br />

Van Ooijen JW, Boer MP, Jansen RC, Maliepaard C. 2002.<br />

MapQTL® 4.0, software for the calculation of QTL position<br />

on genetic maps. Wageningen (Netherlands): Plant <strong>Research</strong><br />

<strong>International</strong>.<br />

Notes<br />

Authors’ address: Plant Breeding Laboratory, Graduate School of<br />

Agriculture, Hokkaido University, Sapporo 060-8589, Japan,<br />

e-mail: rysano@abs.agr.hokudai.ac.jp.<br />

Wrap-up of Session 5<br />

Three conveners, Y. Fukuta (Japan <strong>International</strong> <strong>Institute</strong> for Agricultural<br />

Sciences, JIRCAS), D. Mackill (<strong>International</strong> <strong>Rice</strong> <strong>Research</strong><br />

<strong>Institute</strong>, <strong>IRRI</strong>), and R. Ikeda (JIRCAS), organized Session 5,<br />

chaired by B. Mishra, Directorate of <strong>Rice</strong> <strong>Research</strong>, Indian Council<br />

of Agricultural <strong>Research</strong>. Three scientists presented papers on<br />

broadening the gene pool and two on exploiting heterosis in cultivated<br />

rice.<br />

B.S. Pinheiro, of Embrapa Arroz e Feijão, discussed “Aerobic<br />

rice development in Brazil.” She summarized upland breeding<br />

research under Brazilian savannas from the mid-1970s to 2003.<br />

In the mid-1980s, upland rice varieties of a tropical japonica<br />

background were grown in the Brazilian savannas. Afterward, crop<br />

area gradually and then markedly decreased. However, production<br />

did not decline at the same level because average yield<br />

doubled from 1986 to 2003. This was due to both crop migration<br />

toward areas with more favorable rainfall distribution and<br />

the adoption of modern plant-type varieties, tropical japonica ×<br />

indica derivatives. The impact of improved plant-type varieties<br />

and associated technologies in favored localities of the savanna<br />

region gave rise to a new concept of upland rice, leading to a<br />

174 <strong>Rice</strong> is life: scientific perspectives for the 21st century


new designation—aerobic rice. Drought was a strong priority in<br />

the first breeding program, which relied on tropical japonica progenitors.<br />

In the next step, the genotypes to be grown under supplementary<br />

irrigation and in favored microregions for rainfall distribution<br />

were developed using indica varieties in crosses. A noticeable<br />

move from the frontier land to more favored areas for<br />

water distribution led to a decrease in priority for drought tolerance.<br />

Breeders and pathologists were instead able to cooperate<br />

strongly for breeding for blast resistance and grain quality. The<br />

introduction of indica germplasm to the genetic base of the traditional<br />

upland tropical japonica population was combined with<br />

strong selection pressure for grain characteristics. The first aerobic<br />

rice releases did not possess the same level of drought tolerance<br />

as the traditional upland varieties derived from crosses only<br />

within the japonica group. However, the program now possesses<br />

a representative number of elite lines, japonica versus indica<br />

derivatives, providing a sound basis to further improve yield, blast<br />

resistance, and drought tolerance. The alteration of plant type<br />

and grain quality of upland rice, toward its evolution to aerobic<br />

rice, led to an increase in yield potential and national market<br />

acceptance. Increased involvement in grain cropping systems,<br />

under no tillage or minimum tillage, is foreseen. Moreover, aerobic<br />

rice could greatly contribute to environmental sustainability,<br />

thus avoiding new savanna deforestation, when used in the ricepasture<br />

association, to renew the extensive areas of degraded<br />

pasture in the Brazilian savannas.<br />

H. Satoh of Kyushu University talked about “Mutation in<br />

seed reserves and its use for improving grain quality in rice,”<br />

improvement of grain quality being one of the most important<br />

subjects in rice breeding. For this purpose, genetic sources with<br />

different endosperm properties must be collected, characterized,<br />

and evaluated. Although a wide variation in seed storage starch<br />

and seed storage protein properties is found among cultivated<br />

rice and has been used widely in rice varieties, for example, variation<br />

in cooking quality between japonica and indica rice, only a<br />

few genes involved in this variation have been identified so far.<br />

By using a treatment of egg cells of rice fertilized with MNU,<br />

several thousand rice mutants were found for embryo or endosperm<br />

properties. In addition, a wide variation originated spontaneously<br />

in seed reserves was detected in local rice germplasm.<br />

The genetics and effects of specific genes on qualitative and<br />

quantitative changes in carbohydrates, proteins, or lipids in the<br />

rice endosperm have also been observed. The possibility of using<br />

mutants and germplasm was discussed for endosperm breeding.<br />

D.S. Brar of <strong>IRRI</strong> analyzed “Broadening the gene pool of<br />

rice through introgression from wild species.” Wild species are<br />

an important reservoir of genes for tolerance of biotic and abiotic<br />

stresses. However, several genetic barriers, including low crossability,<br />

sterility, and reduced homoeologous pairing/recombination,<br />

limit the transfer of genes from wild species into cultivated<br />

rice (Oryza sativa L.). Applications of embryo rescue, anther culture,<br />

molecular markers, and genomic in situ hybridization (GISH)<br />

facilitate alien introgression. Genes for resistance to brown<br />

planthopper, bacterial blight, blast, tungro, and grassy stunt; tolerance<br />

of acid sulfate conditions; and cytoplasmic male sterility<br />

have been introgressed from different wild species (AA, BBCC,<br />

CC, CCDD, EE, FF genomes). Breeding lines carrying alien genes<br />

for resistance to and tolerance of these traits have been released<br />

as varieties. Examples are AS996 from IR64 × O. rufipogon in<br />

Vietnam, NSICRC112 with high yielding ability from O. sativa ×<br />

O. longistaminata in the Philippines, and Matatag 9 from IR64 ×<br />

O. rufipogon for tungro-prone areas of the Philippines. Advanced<br />

progenies are under evaluation for tolerance of stem borer, nematodes,<br />

and aluminum and iron toxicity. O. rufipogon accessions<br />

resistant to sheath blight have been identified. O. sativa × O.<br />

glaberrima progenies are being evaluated for weed competitive<br />

ability. Some of the introgressed alien genes have been mapped.<br />

A major QTL for tolerance of aluminum toxicity introgressed from<br />

O. rufipogon has been mapped on chromosome 3, and is conserved<br />

across other cereals.<br />

S.S. Virmani of <strong>IRRI</strong> covered “Heterosis in rice for increasing<br />

yield, production efficiency, and rural employment opportunities.”<br />

<strong>IRRI</strong> started hybrid rice research in 1979 for the tropics<br />

collaboratively with interested national agricultural research and<br />

extension systems. With an appropriate choice of parents, a 15–<br />

20% yield advantage (1–1.5 t ha –1 ) from hybrids was also obtained<br />

in the tropics. Heterosis for early maturity and yield resulted<br />

in increased per-day productivity of hybrids, which also<br />

showed increased nitrogen-use efficiency and better adaptability<br />

than inbreds to saline soils, the aerobic rice environment, the<br />

alternate wetting-and-drying irrigation system, and more favorable<br />

rainfed lowland ecosystems. Increased leaf area index and<br />

increased grain number per panicle and grain weight contributed<br />

to the higher yield of hybrids. <strong>IRRI</strong> has facilitated their commercialization<br />

in the tropics by developing and freely sharing genetically<br />

diverse CMS, maintainer, and restorer lines (for 3-line hybrids)<br />

and temperature-sensitive genetic male sterile (TGMS) lines<br />

(for 2-line hybrids). <strong>IRRI</strong>-bred hybrids and/or parental lines resulted<br />

in coverage of about 1 million ha under hybrid rice in Vietnam,<br />

India, the Philippines, Bangladesh, Indonesia, and Myanmar.<br />

Labor-intensive seed production and processing helped generate<br />

additional rural employment opportunities through the seed industry.<br />

Through hybrid rice research at <strong>IRRI</strong>, progress in and contributions<br />

of heterosis breeding were shown. Future work should<br />

focus on increasing yield and stability, grain quality, disease/insect<br />

resistance, and seed production efficiency. Genetic analysis<br />

for each character under heterosis was also indicated.<br />

E.D. Redoña, Philippine <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong> (Phil<strong>Rice</strong>),<br />

analyzed “The commercialization of hybrid rice in the Philippines.”<br />

Commercialization of this technology has become the Philippine<br />

government’s banner program for agriculture. Hybrid rice is being<br />

pursued to attain rice self-sufficiency, increase rice productivity<br />

and profitability, and generate additional employment. Progress<br />

has been made in areas such as breeding, seed production, seed<br />

industry development, and capacity building since 1998. Four<br />

public hybrids and four proprietary hybrids were provided to farmers.<br />

With increased efforts in enhancing seed production capacity,<br />

with the assistance of various training courses, 21 hybrid<br />

seed growers’ cooperatives have been established that now produce<br />

about 70% of the program’s seed requirements. From 2001<br />

to 2003, hybrids attained an average yield of 6.03 t ha –1 across<br />

provinces and seasons versus the 4.44 t ha –1 average of certi-<br />

Session 5: Broadening the gene pool and exploiting heterosis in cultivated rice 175


fied inbred seeds, for a 34% advantage. Among the key factors<br />

related to the progress made are strong support at the policy<br />

level, engagement of the private sector, increased capacity enhancement<br />

activities, front-line demonstrations, development of<br />

production support, rewards and marketing assistance systems,<br />

involvement of local government units, and a massive information<br />

campaign. A successful communication and extension system<br />

for hybrid rice breeding was also demonstrated.<br />

In summary, the potential of wide hybridization (between<br />

indica and japonica, or between cultivated and wild rice), and<br />

mutants and germplasm for different endosperm traits, was discussed<br />

for broadening of the gene pool and application to rice<br />

breeding. In particular, the exploitation of heterosis through hybrid<br />

rice production was considered a good example of broadening<br />

the gene pool to achieve higher yield.<br />

176 <strong>Rice</strong> is life: scientific perspectives for the 21st century


SESSION 6<br />

Trends in crop establishment<br />

and management in Asia<br />

CONVENER: M. Yamauchi (NARO)<br />

CO-CONVENER: D. Johnson (<strong>IRRI</strong>)


Trends in crop establishment methods<br />

in Asia and research issues<br />

Sushil Pandey and Lourdes Velasco<br />

Economic factors and recent changes in rice production technology<br />

are the major drivers that have led to shifts from transplanting<br />

to the direct-seeding method of rice establishment in<br />

Asia. The rising cost of labor, the need to intensify rice production<br />

through double and triple cropping, the development<br />

of high-yielding short-duration modern varieties, and the availability<br />

of chemical weed control methods have jointly led to<br />

this switchover. As the rice production systems of Asia undergo<br />

further adjustments in response to the rising scarcity of<br />

land, water, and labor, pressure will increase for a shift toward<br />

direct-seeding methods. This paper provides a brief overview<br />

of the trends in crop establishment methods in Asia, their impact,<br />

and implications for research and technology development.<br />

The direct-seeded area in Asia is estimated to be about<br />

29 million ha, which is approximately 21% of the total rice<br />

area in Asia (Table 1). This includes upland and submergenceprone<br />

ecosystems w<strong>here</strong> direct seeding is the traditional<br />

method. If these ecosystems are excluded, the direct-seeded<br />

area is approximately 15 million ha. The shift toward direct<br />

seeding occurred during the late 1980s to mid-1990s, mainly<br />

in rapidly growing economies such as Malaysia and Thailand<br />

as well as in countries w<strong>here</strong> rapid intensification of the rice<br />

production system took place (for example, Vietnam). However,<br />

the growth rate in direct-seeded rice area appears to have<br />

slowed down considerably in recent years.<br />

Determinants of adoption of alternative<br />

crop establishment methods<br />

At a general level, the availability of water and the opportunity<br />

cost of labor can be considered the major determinants of<br />

Table 1. Direct-seeded rice area by ecosystem in various Asian countries.<br />

Irrigated + Irrigated + Area direct-<br />

Flood-prone rainfed lowland rainfed lowland seeded as a % Total rice Total area % of total<br />

Country + upland area a area direct- of irrigated + area a direct-seeded area directrice<br />

area a seeded rainfed seeded<br />

(million ha) lowland area (million ha)<br />

South Asia 8.4 47.8 6.3 13 56.2 14.9 26<br />

Bangladesh 1.9 8.8 0.1 1 10.7 2.0 19<br />

India 6.5 36.0 5.5 15 42.5 12.0 28<br />

Pakistan 2.1 2.1<br />

Sri Lanka 0.9 0.7 78 0.9 0.7 77<br />

Southeast Asia 4.0 68.2 8.3–10.3 11–14 72.2 12.3–14.3 17–20<br />

Cambodia 0.2 1.7 1.9 0.2 10<br />

China 0.5 31.6 1–2.5 3–8 32.1 1.5–3 5–9<br />

Indonesia 1.2 9.8 0.8 8 11.0 2.0 18<br />

Laos 0.2 0.4 0.6 0.2 33<br />

Malaysia 0.1 0.6 0.4 67 0.7 0.5 71<br />

Myanmar 0.6 5.7 6.3 0.6 9<br />

Philippines 0.2 3.4 1.3 38 3.6 1.5 42<br />

Thailand 0.5 9.1 2.8 31 9.6 3.3 34<br />

Vietnam 0.5 5.9 2–2.5 34–42 6.4 2.5–3 39–47<br />

East Asia 3.2 0.1 3 3.2 0.1 3<br />

Japan 2.1 2.1<br />

Korea 1.1 0.1 9 1.1 0.1 9<br />

Total 12.4 119.2 14.7–16.7 12–14 131.6 27.3–29.3 21–22<br />

a<br />

Huke and Huke (1997). Sources of direct-seeded area: Bangladesh—Huke and Huke (1997) and personal communication with S. Bhuiyan. India—<br />

Palaniappan and Purushothaman (1991). Sri Lanka—Pathinayake et al (1991). Cambodia—Helmers (1997). China—personal communication with Lu<br />

Ping. Indonesia—Huke and Huke (1997) and personal communication with Dr. Hamdane Pane. Malaysia—Huke and Huke (1997) and own estimate.<br />

Myanmar—Huke and Huke (1997) and own estimate. Philippines—Phil<strong>Rice</strong>-BAS (1995) and own estimate. Thailand—personal communication with<br />

Dr. Booribon Somrith and data from Agricultural Extension Office, Khon Kaen. Japan—personal communication with Yujiro Hayami. Vietnam—personal<br />

communication with T.P. Tuong and Government Statistical Office (1997). Korea—Kim (1995).<br />

178 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Water<br />

availability<br />

High<br />

Low<br />

TPR<br />

DSR/TPR<br />

Low<br />

Fig. 1. Wage rate and water availability as determinants of crop<br />

establishment methods. DRS = direct-seeded rice, TPR = transplanted<br />

rice.<br />

crop establishment methods (Fig. 1). A low wage rate and assured<br />

supply of adequate water are conditions favorable for<br />

transplanting. Incentives for direct seeding increase when water<br />

availability is low (or uncertain) and wage rates are high.<br />

Much of the recent spread of direct seeding in Southeast Asian<br />

countries has been in response to rising wage rates. When water<br />

availability is low (or uncertain) and the wage rate is low,<br />

either the direct-seeding or transplanting method can be used,<br />

depending on field hydrological conditions.<br />

Two major types of adjustments in crop establishment<br />

methods have been made in response to the rising cost of labor.<br />

In temperate Asian countries such as Japan, Korea, and<br />

Taiwan (China), the shortage of farm labor led to a change<br />

from manual to mechanical transplanting. On the other hand,<br />

in tropical countries such as Malaysia and Thailand, the labor<br />

shortage induced a shift to direct seeding. Small farm size,<br />

intensive cultivation of rice, a long history of transplanting<br />

culture, and the relatively high price of rice in East Asian countries<br />

partly explain their ad<strong>here</strong>nce to transplanting.<br />

Impact of the shift to direct seeding<br />

Wage rate<br />

High<br />

DSR/TPR<br />

DSR<br />

Farm-level studies have shown that direct-seeding methods<br />

produce higher income than transplanting (Table 2). Despite a<br />

slightly lower average yield than that of transplanted rice under<br />

farmers’ field conditions, direct-seeded rice has been found<br />

to result in higher net profit as the savings in labor cost outweighs<br />

the value of lost output. This has occurred especially<br />

in areas w<strong>here</strong> the cost of labor has risen rapidly in relation to<br />

the price of rice. In addition, total farm income has increased<br />

w<strong>here</strong> direct seeding facilitated double cropping of rice in areas<br />

that had only one crop of transplanted rice previously (such<br />

as the Mekong Delta, Vietnam, and Iloilo, Philippines).<br />

The likely future trend<br />

Despite the rapid spread of direct seeding in several Southeast<br />

Asian countries, transplanting is still the dominant method of<br />

crop establishment. Because of differences in rice production<br />

systems and economic conditions, it is more convenient to<br />

examine the likely scenario for East, Southeast, and South Asia<br />

separately.<br />

In East Asia, w<strong>here</strong> rice production systems are inputintensive,<br />

a major shift to direct seeding in response to a further<br />

escalation in the wage rate is unlikely to occur. In comparison<br />

with other Asian countries, these countries are more<br />

industrialized and have higher per capita incomes. Farm income<br />

is maintained at a higher level through policies that keep<br />

the price of rice high in comparison with the international<br />

market price. Under this situation, a potential threat to farmer<br />

income because of a wage increase is likely to be addressed by<br />

policy changes that compensate farmers for a loss in profits<br />

rather than by changes in the method of crop establishment.<br />

Direct seeding is likely to expand further in Southeast<br />

Asian countries with low population densities, especially in<br />

areas w<strong>here</strong> the cost of labor is escalating. However, this type<br />

of wage-induced shift is a function of the rate of growth of the<br />

economy. A slowdown in economic growth rate because of<br />

macroeconomic constraints may result in some shift back to<br />

transplanting, such as what happened during the Asian economic<br />

crisis of 1997. In very densely populated areas such as<br />

Java, western China, and the Red River Delta of Vietnam, transplanting<br />

is likely to continue to remain the dominant culture in<br />

the near to medium term.<br />

In South Asia, w<strong>here</strong> population density is high and overall<br />

economic growth is slow, economic incentives for a shift to<br />

direct seeding are likely to remain weak. The pattern of adoption<br />

of direct seeding in Southeast Asia shows that direct seeding<br />

is first adopted in the dry season, because of better water<br />

control, rather than in the wet season. In South Asia, dry-season<br />

rice accounts for only about 12% of the total rice area<br />

versus 22% in Southeast Asia. In addition, the overall proportion<br />

of rainfed rice area in South Asia is higher. These features<br />

of rice systems may result in a slower adoption of direct seeding<br />

in South Asia.<br />

<strong>Research</strong> implications<br />

The primary economic motives for a shift to direct seeding are<br />

the savings in labor cost and the possibility of crop intensification.<br />

The priority research issue depends on which of the<br />

two motives is likely to play the dominant role in a particular<br />

ecoregion. If the main driving force for the transition to direct<br />

seeding is the rapidly rising wage rate, research to generate<br />

labor-saving technological innovations would have a high priority,<br />

such as mechanical tillage and labor-saving weed control<br />

methods. W<strong>here</strong> drought and early submergence impede<br />

the adoption of direct seeding, research to develop varieties<br />

Session 6: Trends in crop establishment and management in Asia 179


Table 2. Economic returns to different crop establishment methods in the wet<br />

season.<br />

Place Dry-seeded Wet-seeded Transplanted % Difference<br />

($ ha –1 )<br />

Suphanburi, Thailand a<br />

Cash cost b 152 148 3<br />

Gross returns c 505 476 6<br />

Gross margin d 353 328 8<br />

Net returns e 168 132 27<br />

Pangasinan, Philippines f<br />

Cash cost 230 273 –16<br />

Gross returns 608 666 –9<br />

Gross margin 378 393 –4<br />

Net returns 288 247 17<br />

Iloilo (double cropped), Philippines g<br />

Cash cost 736 441 67<br />

Gross returns 1,627 904 80<br />

Gross margin 891 464 92<br />

Net returns 695 382 82<br />

a Source: Isvilanonda (1990). All values converted to $ using the exchange rate US$1 = B20. b Cost of<br />

all purchased inputs. c Gross value of output. d Gross value of output minus the cost of purchased inputs.<br />

e Gross value of output minus the cost of purchased and family-owned inputs. f Pandey et al (1995).<br />

g Pandey and Velasco (1998). The comparison is between two crops of wet-seeded rice versus only one<br />

crop of transplanted rice.<br />

and crop management practices to relax these constraints is<br />

needed.<br />

However, if crop intensification is the major reason for<br />

direct seeding, research to facilitate early establishment and<br />

early harvest of the direct-seeded crop would have a higher<br />

priority, as this will permit timely planting of the subsequent<br />

crop. The development of short-duration varieties would be<br />

important in this case. Even though the cost of labor may be<br />

initially low in these areas, intensification of land use may lead<br />

to labor shortages because of peak labor demand during the<br />

harvesting of the previous crop and establishment of the succeeding<br />

crop within a short period. Suitable mechanical devices<br />

for land preparation that can reduce the turnaround time<br />

between crops could help achieve a higher and more stable<br />

yield of the second crop.<br />

The high costs of weed control could be a major factor<br />

constraining the widespread adoption of direct seeding. The<br />

key to the success of direct-seeded rice is the availability of<br />

efficient weed control techniques. Varieties with early seedling<br />

vigor and crop management technologies that help reduce<br />

the competitive effects of weeds on crops are needed. It is<br />

essential, however, to evaluate the environmental and health<br />

consequences of potential technologies that are based on chemical<br />

means of weed control.<br />

Empirical analyses have indicated that the technical efficiency<br />

of rice production is lower and more variable for direct-seeded<br />

rice than for transplanted rice (Pandey and Velasco<br />

1999). This suggests the existence of a higher “yield gap” between<br />

the “best-practice” farmer and the average farmer when<br />

rice is direct-seeded. A greater variability of technical efficiency<br />

of direct-seeded rice could be partly due to the use of varieties<br />

that were originally developed for transplanted culture. Varieties<br />

that are specifically targeted for direct-seeded methods<br />

could help reduce such yield gaps. Better crop management<br />

practices, especially those that facilitate early and more uniform<br />

establishment, can be similarly helpful.<br />

Precise water management is critical for high productivity<br />

of wet-seeded rice (De Datta and Nantasomsaran 1991). A<br />

high level of control of water flow on irrigated fields is hence<br />

desirable. However, most irrigation systems in Asia have been<br />

designed to supply water to transplanted rice for which precision<br />

in water management is not as critical. Suitable modifications<br />

of irrigation infrastructure could ensure a high yield of<br />

direct-seeded rice and also improve water-use efficiency. In<br />

addition, appropriate mechanical systems of field leveling that<br />

ensure uniformity in field water level are needed.<br />

References<br />

De Datta SK, Nantasomsaran P. 1991. Status and prospects of direct<br />

seeded flooded rice in tropical Asia. In: Direct seeded flooded<br />

rice in the tropics. Selected papers from the <strong>International</strong> <strong>Rice</strong><br />

<strong>Research</strong> Conference. Manila (Philippines): <strong>International</strong> <strong>Rice</strong><br />

<strong>Research</strong> <strong>Institute</strong>. p 1-16.<br />

Helmers K. 1997. <strong>Rice</strong> in the Cambodian economy: past and present.<br />

In: Nesbitt HJ, editor. <strong>Rice</strong> production in Cambodia. Manila<br />

(Philippines): <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>. p 1-14.<br />

180 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Huke RE, Huke EH. 1997. <strong>Rice</strong> area by type of culture: South, Southeast,<br />

and East Asia. Manila (Philippines): <strong>International</strong> <strong>Rice</strong><br />

<strong>Research</strong> <strong>Institute</strong>. 59 p.<br />

Isvilanonda S. 1990. Effects of pregerminated direct seeding technique<br />

on factor use and the economic performance of rice<br />

farming: a case study in an irrigated area of Suphan Buri. In:<br />

Fujimoto A, editor. Thai rice farming in transition. Tokyo (Japan):<br />

World Planning Commission.<br />

Kim SC. 1995. Weed control technology of direct seeded rice in<br />

Korea. Paper presented at the <strong>International</strong> Symposium on<br />

Weed Control under Direct Seeded <strong>Rice</strong>, 31 July 1995,<br />

Omagari, Akita, Japan.<br />

Palaniappan SP, Purushothaman S. 1991. Rainfed lowland rice farming<br />

system in Tamil Nadu (India): status and future thrust. In:<br />

Proceedings of the Rainfed Lowland <strong>Rice</strong> Farming Systems<br />

<strong>Research</strong> Planning Meeting, Myanmar, August 1991. Manila<br />

(Philippines): <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>.<br />

Pandey S, Velasco LE. 1998. Economics of direct-seeded rice in<br />

Iloilo: lessons from nearly two decades of adoption. Social<br />

Sciences Division Discussion Paper. Manila (Philippines):<br />

<strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>.<br />

Pandey S, Velasco LE. 1999. Economics of alternative rice establishment<br />

methods in Asia: a strategic analysis. Social Sciences<br />

Division Discussion Paper. Manila (Philippines): <strong>International</strong><br />

<strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>.<br />

Pandey S, Velasco L, Masicat P, Gagalac F. 1995. An economic analysis<br />

of rice establishment methods in Pangasinan, Central<br />

Luzon. Social Sciences Division Discussion Paper. Manila<br />

(Philippines): <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>.<br />

Pathinayake BD, Nugaliyadde L, Sandanayake CA. 1991. Direct<br />

seeding practices for rice. In: Sri Lanka in direct-seeded<br />

flooded rice in the tropics. Manila (Philippines): <strong>International</strong><br />

<strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>.<br />

Phil<strong>Rice</strong>-BAS (Bureau of Agricultural Statistics). 1995. Provincial<br />

rice statistics. Muñoz, Nueva Ecija (Philippines): Philippine<br />

<strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>.<br />

Notes<br />

Authors’ address: <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>, e-mail:<br />

sushil.pandey@cgiar.org.<br />

Direct seeding and weed management in Korea<br />

Soon-Chul Kim and Woon-Goo Ha<br />

In 1991, the Rural Development Administration (RDA) introduced<br />

dry drill seeding and water seeding of rice with water<br />

seeding being either wet-drill-sown or water broadcast-seeded.<br />

Despite problems, the direct-seeding area has increased rapidly;<br />

however, only about 8–9% of the total rice area was under<br />

direct seeding in 2003 (RDA 2003). The main constraints<br />

to direct seeding are weed problems and rainfall fluctuation<br />

during seeding time.<br />

Weed ecology in direct-seeded paddy<br />

Weed growth is greatly influenced by cultivation method (Kim<br />

et al 1992) and thus the adoption of direct-seeding technology<br />

results in shifts in weed growth in terms of dry matter production<br />

and composition of dominant species. The greatest weed<br />

growth is recorded in dry-seeded rice, followed by waterseeded<br />

rice, mechanically transplanted rice, and manually transplanted<br />

rice (Table 1).<br />

Early rice growth and water management are considered<br />

as the main factors accounting for the above differences. Yield<br />

losses from weed competition are related closely to weed<br />

growth, with complete crop loss occurring w<strong>here</strong> weeds are<br />

not managed. Changes in crop establishment method from<br />

transplanting to direct seeding changed not only weed dry<br />

matter production but also the composition of the weed species.<br />

In transplanted rice fields, the most troublesome weeds<br />

were Eleocharis kuroguwai (20%), Sagittaria trifolia (16%),<br />

S. pygmaea (13%), Echinochloa crus-galli (12%), and<br />

Monochoria vaginalis (11%) (Kim et al 1992). Approximately<br />

50% of weed biomass was accounted for by perennial weeds.<br />

In dry-seeded rice, on the other hand, annual grasses were the<br />

most predominant weeds, such as E. crus-galli (54%), Digitaria<br />

adscendens (9%), Leptochloa chinensis (8%), Setaria viridis<br />

(6%), and weedy rice (Oryza sativa subsp. spontanea, 5%). In<br />

water seeding, E. crus-galli (37%) was also the most important<br />

weed species even though the degree of dominance was<br />

lower than in dry-seeded rice. The second most important weed<br />

was Aneilema keisak (15%), followed by Ludwigia prostrata<br />

(11%) and Leersia japonica (7%). Weed growth in directseeded<br />

rice was dominated by E. crus-galli, which became the<br />

most important weed and had a slightly lower value in waterseeded<br />

rice than in dry-seeded rice. Most of the annual grass<br />

weeds occurring in direct-seeded rice fields belonged to the<br />

C 4 photosynthetic pathway (Table 2).<br />

Recently, weedy rice (including red rice) has become<br />

widely distributed in farmers’ fields. The possible origins of<br />

weedy rice were summarized by Kim (1995b) as follows:<br />

Shattered grains of the previous year<br />

Outcross between cultivated rice species<br />

Outcross between cultivated rice and red rice (dormant<br />

seeds)<br />

Outcross between wild-type rice and weedy rice (red<br />

rice)<br />

Outcross between red rice species<br />

Dormant red rice or wild-type rice itself<br />

The degree of contamination by weedy rice observed in<br />

fields was highly variable, ranging from 0.5% to 35.2% for<br />

the southern area. However, it was difficult to estimate the<br />

correct degree of contamination and distribution pattern for<br />

all farmers’ fields because field observations were made and<br />

Session 6: Trends in crop establishment and management in Asia 181


Table 1. Weed growth and yield losses caused by weed and rice<br />

competition in various cultivation methods.<br />

Cultivation method Weed weight Yield loss<br />

(g m –2 ) a (%)<br />

Transplanting<br />

Manual (40–45 days old) 741 10–20<br />

Mechanical<br />

Old seedlings (30–35 days old) 843 25–30<br />

Young seedlings (8–10 days old) 1,020 30–35<br />

Direct seeding<br />

Water seeding 1,643 40–60<br />

Dry seeding 2,300 70–100<br />

a<br />

Weeds were harvested in the nonweeded plot.<br />

Table 2. Dominant weed species associated with establishment<br />

method. a<br />

Transplanting Dry seeding Water seeding<br />

El. kuroguwai (20) b Ec. crus-galli (54) Ec. crus-galli (37)<br />

Sa. trifolia (16) D. adscendens (9) An. keisak (15)<br />

Sa. pygmaea (13) Lp. chinensis (8) Lu. prostrata (11)<br />

Ec. crus-galli (12) Se. viridis (6) Lr. japonica (7)<br />

M. vaginalis (11) O. sativa subsp. spontanea (5) El. kuroguwa i(6)<br />

Sc. juncoides (6) Ae. indica (4) Sc. juncoides (6)<br />

Lu. prostrata (4) An. keisak (3) M. vaginalis (5)<br />

An. keisak (4) Pl. hydropiper (3) Pt. distinctus (4)<br />

Cy. serotinus (3) Al. aequalis var. amurensis (3) Sa. pygmaea (3)<br />

Pt. distinctus (3) Ca. bursa-pastoris (3) Cy. serotinus (3)<br />

Diversity 0.118 0.317 0.190<br />

Index<br />

a<br />

El = Eleocharis, Sa = Sagittaria, Ec = Echinochloa, M = Monochoria, Sc = Scirpus,<br />

Lu = Ludwigia, An = Aneilema, Cy = Cyperus, Pt = Potamogeton, D = Digitaria, Lp<br />

= Leptochloa, Se = Setaria, Ae = Aeschynomene, Pl = Polygonum, Al = Alopecurus,<br />

Ca = Capsella, Lr = Leersia, O = Oryza. b Values in parentheses are % relative biomass.<br />

Source: Kim et al (1992).<br />

sampling done only in fields that had conspicuous rice plants<br />

that were markedly different from cultivated rice in heading<br />

date and plant height. Sometimes, hybrid swarms of many intergrades<br />

existed in the same place and thus it was impossible<br />

to collect all the variations.<br />

The taxonomic traits of weedy rice were highly variable<br />

in grain shape, awn length, awn color, apiculus color, pericarp<br />

color, and endosperm type. Similarly, the important agronomic<br />

traits of weedy rice were also highly variable, including maturity,<br />

plant height, spikelet fertility, grain shattering, and dormancy<br />

(Kim 1995a). Because of introgression, most of these<br />

traits exhibited discrete characters. In dry-seeded rice, early<br />

seeding enhanced the growth of weedy rice. Double-cropped<br />

dry-seeded rice with barley, rye, or Italian ryegrass significantly<br />

reduced the growth of weedy rice by 33–66%.<br />

Sulfonylurea herbicide was first introduced in 1989 in<br />

rice paddy fields, starting with bensulfuron-methyl, followed<br />

by pyrazosulfuron-ethyl (Kim 1994a). In 2004, nine sulfonylurea<br />

herbicides, including these two, were widely used and<br />

about 75% of rice herbicides (117 sulfonylurea mixtures /155<br />

in total herbicides) were mixtures of sulfonylurea herbicides<br />

(KCPA 2004). This was equivalent to about 63.3% of the total<br />

market value. Since 1999, six weed species were reported as<br />

sulfonylurea-resistant, exhibiting cross resistance among sulfonylurea<br />

herbicides. Monochoria korsakowii was the first,<br />

reported in 1999, followed by M. vaginalis, Lindernia dubia,<br />

Rotala indica, Scirpus juncoides, and Cyperus difformis (Im<br />

et al 2004).<br />

Several herbicides effective for controlling sulfonylurearesistant<br />

weeds were screened. Before seeding or rice transplanting,<br />

oxadiazon, thiobencarb, fentrazamide, oxadiargyl, and<br />

butachlor were highly effective, w<strong>here</strong>as those for application<br />

at the 2–3-leaf stage of weeds were simetryn, carfentrazonethyl,<br />

pyriminobac-methyl, and benzobicyclon.<br />

Effective weed control<br />

Dry-seeded rice<br />

Good seedling establishment, proper weed management, and<br />

freedom from lodging are important for good yield. However,<br />

weed control is the key factor in dry-seeded rice and thus the<br />

success of direct seeding is almost totally reliant on effective<br />

weed control. Dry seeding has a dry period (up to about 30<br />

days from seeding) and subsequent permanent flood period.<br />

Most weeds occur during the dry period and Echinochloa species<br />

are of prime importance in this period. Echinochloa species<br />

grow faster than rice because of the different temperature<br />

regime for seed germination and different physiological and<br />

morphological traits (Kim and Moody 1989). Differences between<br />

rice and Echinochloa species in the period of seedling<br />

emergence were greater at early seeding than at late seeding<br />

and this difference can be important in deciding optimum herbicide<br />

application time. For example, seedling emergence at<br />

early seeding (1 April) required 36 days for rice emergence<br />

and 20 days for Echinochloa, w<strong>here</strong>as for late seeding of June<br />

20 these were 9 days and 5 days, respectively.<br />

Weed control should be practiced before 20 days after<br />

seeding and, among five herbicide applications, herbicidal efficacy<br />

was the greatest at the 12–15 DAS application (rice<br />

emergence stage).<br />

Seedling emergence of rice and Echinochloa species<br />

varies by seeding time and moisture regime and, thus, deciding<br />

on herbicide application time should be based on seedling<br />

growth status, not on days from seeding.<br />

In the permanent flood period, the application of oneshot<br />

herbicide is recommended either as early or intermediate<br />

application after flooding. Early applications (0–10 days after<br />

flooding) consist mostly of soil-applied herbicides for grass<br />

weeds such as butachlor, thiobencarb, benfuresate, dithiopyr,<br />

anilofos, molinate, esprocarb, pyrazolate, pentoxazone, and<br />

several mixtures of these with sulfonylurea, bensulfuron-methyl,<br />

pyrazosulfuron-ethyl, and imazosulfuron. At intermediate<br />

application (15–25 days after flooding), the majority are<br />

182 <strong>Rice</strong> is life: scientific perspectives for the 21st century


one-shot sulfonylurea mixtures for controlling annual grasses<br />

and perennial weeds. For late application (30–40 days after<br />

flooding), mostly, foliar-applied herbicide mixtures are recommended<br />

using bispyribac-sodium, cyhalofop-butyl,<br />

penoxaprop-P-ethyl, pyribenzoxim with propanil, bentazon,<br />

azimsulfuron, ethoxysulfuron, etc.<br />

For dry-seeded rice, in general, two herbicide applications<br />

are recommended: one at the dry period either just before<br />

rice emergence or just after rice emergence and the other<br />

at the flood period.<br />

Wet-seeded rice<br />

The newly developed “press-type” wet seed drill is an improved<br />

technology that avoids the problem of lodging for the soilsurface<br />

seeding method or poor seedling establishment for the<br />

subsoil seeding method (Kim 1994b). However, this technology<br />

has some problems for seedling establishment because of<br />

the difficulty in uniform harrowing operation, water management<br />

after seeding, herbicide application, bird damage, and<br />

algae infestation.<br />

The field should not be flooded for at least 6–8 days<br />

after seeding to provide enough oxygen for seed germination<br />

and enable good root anchorage. Furthermore, soil drying is<br />

necessary to have good root anchorage and good seedling establishment<br />

and to minimize the infestation of fresh-water algae.<br />

The improved technology of seed pressing and no irrigation<br />

during 6–8 days after seeding allowed all types of seed<br />

regimes, whether pregerminated or not. Good root anchorage<br />

significantly reduces the incidence of herbicidal phytotoxicity,<br />

particularly to sulfonylurea mixtures such as dimepiperate/<br />

bensulfuron-methyl or molinate/pyrazosulfuronethyl that are<br />

currently being recommended in the wet/water-seeding method.<br />

One-shot herbicides of sulfonylurea mixtures are currently<br />

recommended after good root anchorage. Effective weed<br />

control has mostly relied on good tillage operations (particularly<br />

on harrowing operations) and the degree of root anchorage<br />

when the first herbicide is applied. In general, herbicide<br />

selection for wet seeding w<strong>here</strong> t<strong>here</strong> is flooding is relatively<br />

narrow compared with dry seeding because of the better rice<br />

root anchor regime at herbicide application time. T<strong>here</strong>fore,<br />

herbicide selection should be undertaken with care in wet seeding.<br />

For early applications (10–20 days after seeding), single<br />

or sulfonylurea mixtures of molinate, dimepiperate, dymron,<br />

fenclorim, pyrazolate, mefenacet, cyhalofop-butyl,<br />

pyriminobac-methyl are recommended. For late applications<br />

(30–40 days after seeding), herbicide recommendations are<br />

the same as for dry seeding.<br />

In general, pregerminated seeds are much safer than<br />

ungerminated seeds to most herbicides. This suggests that<br />

pregerminated seeds should be used and roots should be well<br />

anchored with shoot emergence through the soil when the first<br />

herbicide is applied. Based on these results, two herbicide recommendations,<br />

either a one-shot single application or two systematic<br />

applications, are suggested. The choice of herbicide<br />

application is mainly determined by the weed flora in the target<br />

field.<br />

Water-seeded rice<br />

Water seeding requires good management at the farmers’ level<br />

in terms of irrigation management to ensure a good stand and<br />

have no lodging problems. Farmers usually make a small irrigation/drainage<br />

canal in the field at regular intervals using tractor<br />

passing or a small machine or manually pulled stone. The<br />

surface water after seeding is drained out through this canal to<br />

allow good anchorage by the root system, thus ensuring a good<br />

seedling stand, good lodging tolerance, and less herbicidal<br />

phytotoxicity. The general recommendations for herbicide<br />

application are similar to those of wet seeding, except that<br />

thiobencarb can be used before rice seeding. Besides this, early<br />

and intermediate applications (10–20 days after seeding) and<br />

late applications (30–40 days after seeding) are the same as in<br />

wet seeding.<br />

The relative importance of weed control in the total rice<br />

labor requirement is greatest in direct-seeded rice, and is 8–<br />

10% for transplanted rice versus 13–15% for direct-seeded<br />

rice. This requirement is likely to surpass 25% when technologies<br />

such as minimum or no-tillage technology and large-scale<br />

mechanization are adopted. Currently, weed control practices<br />

are too reliant on herbicide. T<strong>here</strong>fore, an integrated weed<br />

management system is needed in the future.<br />

The basic concepts for integrated weed control combine<br />

the possible control methods of agrochemical, physical, ecological,<br />

and biological methods. These can be applied repeatedly<br />

without risking harm to the environment, and they may<br />

be more economical and require less input.<br />

In direct seeding, the weedy rice problem could have<br />

prime importance. T<strong>here</strong>fore, thorough and systematic research<br />

is needed. Weeds resistant to sulfonylurea are also an important<br />

consideration, in both direct seeding and rice cultivation<br />

as a whole.<br />

Reference<br />

Im IB, Kim JK, Kim SK, Kuk YI, 2004. Control of sulfonylurea<br />

resistant Lindernia dubia (L.) Pennell in the rice paddy field.<br />

Korean J. Weed Sci. 24(1):7-13.<br />

KCPA (Korea Crop Protection Association). 2004. Manual of agrochemicals.<br />

Seoul (Korea): KCPA. 989 p<br />

Kim SC.1995a. Latest advancement in cultivation methods and weed<br />

management of rice production in Korea. Weeds of Kyushu<br />

25:29-36<br />

Kim SC.1995b. Weed control in the rice crop. In: Labor saving culture<br />

of rice crop. Text for ‘95 training of extension workers.<br />

Seoul (Korea): Rural Development Administration. p 63-86.<br />

Kim SC. 1994a. The success of dry seeding of rice relies on weed<br />

management. Agric. Tech. RDA 335:1-4.<br />

Kim SC.1994b. Improvement of seedling establishment in wet drillseeded<br />

rice. Res. Ext. RDA 35(3):44-47.<br />

Kim SC, Oh YJ, Kwon YW. 1992. Weed flora of agricultural area in<br />

Korea. Korean J. Weed Sci. 12(4):317-334.<br />

Session 6: Trends in crop establishment and management in Asia 183


Kim SC, Moody K. 1989. Germination and seedling development<br />

of rice and Echinochloa species. Korean J. Weed Sci. 9(2):108-<br />

115.<br />

RDA (Rural Development Administration). 2003. Reference for rice<br />

crop. Korea: RDA. 216 p.<br />

Notes<br />

Authors’ address: National Yeongnam Agricultural <strong>Research</strong> <strong>Institute</strong>,<br />

RDA, Milyang 627-130, Korea, e-mail:<br />

kim0sc@rda.go.kr.<br />

Direct-seeding cultivation of rice in Japan: stabilization<br />

of seedling establishment and improvement<br />

of lodging resistance<br />

Satoshi Yoshinaga<br />

The aging of farmers and falling rice prices are creating severe<br />

problems for farmers in Japan, and this has led to demand<br />

for a reduction in the costs and labor required for rice (Oryza<br />

sativa L.) production in recent years. Direct seeding, which<br />

does not require seedlings to be raised or transplanted, is regarded<br />

as the most effective method of reducing costs and labor.<br />

However, direct-seeded fields currently represent less than<br />

1% of the total rice area, although dry-seeded fields increased<br />

during the 1970s before the use of transplanting machines became<br />

widespread. One disadvantage of direct seeding, hindering<br />

its widespread use, is the instability of rice yields of direct-seeded<br />

fields compared with those of transplanted fields.<br />

The main factors responsible for the lower yields in wet-seeded<br />

fields are poor seedling establishment and frequent plant lodging.<br />

Recently, improved methods that stabilize seedling establishment<br />

and promote lodging resistance have been developed<br />

and the area of wet-seeded rice cultivation has doubled within<br />

the past 5 years. This paper discusses recent improvements<br />

that stabilize seedling establishment and lodging resistance in<br />

wet-seeded rice.<br />

Stabilization of seedling establishment<br />

In Japan, most popular rice cultivars with high taste quality do<br />

not show sufficient lodging resistance under wet-seeded conditions,<br />

as they are bred for transplanting. Seeding such cultivars<br />

on the soil surface often causes severe lodging during the<br />

ripening period. This disadvantage can be minimized by seeding<br />

in the soil, but lower and slower rates of seedling emergence<br />

result from the anaerobic conditions around the seed.<br />

Furthermore, direct seeding in Japan is usually conducted in<br />

periods of low temperature of less than 20 °C daily mean temperature,<br />

which may result in lower and slower rates of seedling<br />

emergence. Solutions to these problems are important to<br />

further develop wet-seeding cultivation and recent research<br />

has focused on stabilizing seedling establishment in the soil.<br />

Development of oxygen-generating products<br />

Ota and Nakayama (1970) reported that coating rice seeds with<br />

calcium peroxide (CaO 2 ), acting as a source of oxygen, pro-<br />

motes the seedling emergence of direct-seeded rice in flooded<br />

soil. Experiments on the practical use of CaO 2 in the 1970s<br />

contributed to the development of an oxygen-generating product<br />

containing CaO 2 and its commercial release (Calper Fine<br />

Granule). T<strong>here</strong>after, pregerminated seeds coated with the<br />

oxygen-generating product (simply called “coated seeds” <strong>here</strong>after)<br />

could be sown in soil at depths of 5–20 mm in submerged<br />

conditions.<br />

Water management after seeding<br />

Until the mid-1990s, fields were flooded after direct seeding<br />

because it was believed that flooding was necessary to maintain<br />

a more constant and higher soil temperature during seedling<br />

establishment. At that time, to control weeds, herbicide<br />

was usually applied under flooded conditions. However, seedling<br />

establishment was unstable with this type of water management,<br />

even when coated seeds were used. Oba (1997) suggested<br />

that drainage after seeding enhanced seedling establishment<br />

compared with flooding for rice coated and directseeded<br />

in the soil. Several reports (Yoshinaga et al 2000, Sato<br />

and Maruyama 2002, Tsuchiya et al 2004) on the effects of<br />

drainage after seeding show that oxidized soil conditions surrounding<br />

the seeds improved seedling establishment and stimulated<br />

initial growth (Table 1). It has also been shown that the<br />

time taken for seedling emergence in drained conditions is similar<br />

to that in flooded conditions, although the minimum soil<br />

temperature during emergence may be lower in drained conditions.<br />

Furthermore, improved herbicides that can control weeds<br />

at a later growth stage were developed and their use has supported<br />

the widespread drainage after seeding because improved<br />

herbicides can control weeds even if they are applied after<br />

rice seedling emergence subsequent to drainage. For these reasons,<br />

drainage subsequent to the seeding of coated seeds had<br />

become widespread by the end of the 1990s and it has contributed<br />

to the recent increases in the area cultivated by wet seeding.<br />

Further experiments are required to decrease the dose of<br />

CaO 2 or replace the use of CaO 2 and reduce costs by developing<br />

cultivars with high emergence ability at low temperature.<br />

184 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. Relationship between water management and seedling emergence<br />

in field conditions. a<br />

Water Soil Seedling Floating Dry weight<br />

management temperature emergence seedlings (mg plant –1 )<br />

after seeding (°C) (%) (%)<br />

Flooding 25.8 a 67.1 b 6.0 a 43.2 b<br />

Drainage 25.2 a 76.5 a 0.2 b 63.3 a<br />

a Seeds were coated with calcium peroxide and seeded in the soil at 10-mm depth. Data are<br />

means of 2–3 years. Soil temperature is the average of 2 weeks after seeding at 10-mm depth.<br />

Dry weight was measured at 2–3 weeks after seeding. Values followed by the same letter are<br />

not significantly different at the 5% level according to LSD. (Yoshinaga et al 2000.)<br />

Improvement of lodging resistance<br />

Lodging is problematic for rice production as it makes harvesting<br />

by machine difficult. Furthermore, the lodging of rice<br />

plants during the ripening period results in a yield reduction<br />

owing to decreased canopy photosynthesis from self-shading<br />

and also decreases grain quality because of the increased coloring<br />

of brown rice and/or decreased taste (Matsue et al 1991,<br />

Setter et al 1997). Wet-seeded rice is more susceptible to lodging<br />

during the ripening period than is transplanted rice. Popular<br />

cultivars are used in direct seeding to achieve better producer<br />

prices, although they do not generally show sufficient<br />

lodging resistance. T<strong>here</strong>fore, alternative means of improving<br />

the lodging resistance of direct-seeded rice are required such<br />

as amending nitrogen application, seeding depth, and seeding<br />

method. A decrease in nitrogen fertilization limits culm elongation<br />

and improves lodging resistance. The smaller amount<br />

of nitrogen application, however, might reduce yield in directseeded<br />

rice. Deeper seeding depths have been tested in conjunction<br />

with the use of coated seeds, and this has reduced the<br />

root lodging of direct-seeded rice. The base of the rice hills,<br />

however, is still shallow in these conditions and lodging resistance<br />

is insufficient. When comparing different seeding methods,<br />

lodging resistance is considered to be the highest in hillseeded<br />

rice and higher in row-seeded rice than in broadcastseeded<br />

rice (Ogata and Matsue 1998). However, practical hillseeders<br />

did not exist until the late 1990s, and previously direct<br />

seeding had been conducted by broadcast or row seeding.<br />

A practical hill-seeder was developed in the late 1990s.<br />

The hill-seeder, combined with a harrow, enabled seeding and<br />

puddling to be performed simultaneously (Shimotsubo and<br />

Togashi 1996). The seeder effectively drives seeds into the<br />

puddled soil intermittently by using a rotating disk, and the<br />

established seedlings form hills. The greater seeding depth<br />

effectively prevents the floating and lodging of seedlings, while<br />

hill seeding effectively increases lodging resistance. Hillseeded<br />

rice has a greater resistance to lodging than broadcastseeded<br />

rice across a range of plant densities (Fig. 1) or seeding<br />

depths (Yoshinaga et al 2001). The higher lodging resistance<br />

of hill-seeded rice is due to its larger number of panicles<br />

per hill, which is composed of several plants (Yoshinaga et al<br />

2001).<br />

Hill seeding has enabled popular cultivars with low lodging<br />

resistance to be grown in wet-seeding areas. The area cultivated<br />

by the hill-seeder has been increasing since 1998 and<br />

overtook the area cultivated by broadcasting in 2002. Hill seeding<br />

occupied 24% of the total area of wet-seeded rice in 2003<br />

and it can be said that the hill-seeder has contributed to the<br />

recent widespread application of wet seeding.<br />

To further improve lodging resistance, the introduction<br />

of cultivars with improved lodging resistance is important together<br />

with studies on the interaction of nitrogen application<br />

with seeding methods.<br />

Conclusions<br />

The recent improvements in the stability of establishment under<br />

direct seeding have contributed to the recent increase in<br />

direct-seeded area. For the further stabilization and widespread<br />

adoption of direct seeding, developments in plant breeding are<br />

required to allow the introduction of cultivars with desirable<br />

traits for direct-seeding cultivation. Improved crop management<br />

that corresponds to seeding methods and cultivars is also<br />

required.<br />

References<br />

Matsue Y, Mizuta K, Furuno K, Yoshida T. 1991. Studies on palatability<br />

of rice grown in northern Kyushu. Jpn. J. Crop Sci.<br />

60:490-496.<br />

Oba S. 1997. Seedling emergence improving method by draining<br />

(just after seeding) in wet seeding cultivation of rice. Nogyo<br />

Gijutsu 52:33-34.<br />

Ogata T, Matsue Y. 1998. Studies on direct sowing culture of rice in<br />

northern Kyushu. Jpn. J. Crop Sci. 67:485-491.<br />

Ota Y, Nakayama M. 1970. Effects of seed coating with calcium<br />

peroxide on germination under submerged conditions in rice<br />

plant. Proc. Crop Soc. Jpn. 39:535-536.<br />

Sato T, Maruyama S. 2002. Seedling emergence and establishment<br />

under drained conditions in rice direct-sown into puddled and<br />

leveled soil. Plant Prod. Sci. 5:71-76.<br />

Session 6: Trends in crop establishment and management in Asia 185


Pushing resistance (g culm –1 )<br />

100<br />

80<br />

60<br />

40<br />

20<br />

1998 BS<br />

1999 BS<br />

1998 HS<br />

1999 HS<br />

0<br />

0 50 100 150 200<br />

Plant density (no. m –2 )<br />

Fig. 1. Relationship between plant density and pushing resistance in<br />

broadcast-seeded rice (BS) and hill-seeded rice (HS). Pushing resistance<br />

was measured at 20 days after heading by bending a hill 45 o<br />

from the vertical at 15-cm height. Vertical bars indicate standard<br />

error (n = 3). (Yoshinaga et al 2001.)<br />

Setter TL, Laureles EV, Marazedo AM. 1997. Lodging reduces yield<br />

of rice by self-shading and reductions in canopy photosynthesis.<br />

Field Crops Res. 49:95-106.<br />

Shimotsubo K, Togashi T. 1996. Study on submerged direct seeding<br />

combined puddling with seeding operation. Jpn. J. Crop Sci.<br />

65(Extra issue 1):12-13.<br />

Tsuchiya M, Sato T, Maruyama S. 2004. Growth enhancement by<br />

drainage during seedling establishment in rice direct-sown into<br />

puddled and leveled soil. Plant Prod. Sci. 7:324-328.<br />

Yoshinaga S, Nishida M, Wakimoto K, Tasaka K, Matsushima K,<br />

Togashi T, Shimotsubo K. 2000. Effects of drainage after submerged<br />

direct-seeding on the effectiveness of fertilized nitrogen<br />

and the growth and yield of rice plants. Jpn. J. Crop Sci.<br />

69:481-486.<br />

Yoshinaga S, Wakimoto K, Tasaka K, Matsushima K, Togashi T,<br />

Shimotsubo K. 2001. Improvement of lodging resistance in<br />

submerged direct seeding rice cultivation using a newly developed<br />

’Shooting hill-seeder’. Jpn. J. Crop Sci. 70:186-193.<br />

Notes<br />

Author’s address: National Agricultural <strong>Research</strong> Center for Tohoku<br />

Region, NARO, Japan, e-mail: yosinaga@affrc.go.jp.<br />

Direct seeding of aerobic rice in China<br />

Guang Hui Xie, Jun Yu, Jing Yan, Huaqi Wang, and Xiurong Zhu<br />

The food supply in China must increase by 50–60% over the<br />

next 30 years for a population that is estimated to reach 1.6<br />

billion by 2030. <strong>Rice</strong> is vital to more than half of the population<br />

and it is the most important field crop in China. However,<br />

lowland rice cultivation area dropped from 33.76 million ha<br />

in 1981 to 29.96 million ha in 2000 mainly because of water<br />

shortages. Current projections suggest that by 2030 t<strong>here</strong> will<br />

be a shortfall of 12.9 billion m 3 of water to meet the demand<br />

of the country (Li and Duan 2002). Since rice is the most water-consuming<br />

crop, alternative rice cultivation strategies that<br />

require less water and increase water productivity are urgent.<br />

Variety improvement and water saving of aerobic rice<br />

Many traditional upland rice types have been grown in hilly<br />

rainfed regions in China for hundreds of years with very low<br />

186 <strong>Rice</strong> is life: scientific perspectives for the 21st century


inputs. However, these varieties produce a low yield even under<br />

relatively high-input conditions. During the past two decades,<br />

rice breeders have worked at variety improvement and<br />

more and more high-yielding and good-quality rice varieties<br />

adapted to aerobic soil conditions have been emerging and<br />

released officially. Most of these varieties were claimed to have<br />

a high yield potential, from 6.0 to 8.0 t ha –1 . Since the mid-<br />

1980s, a new way of rice cultivation took place in northern<br />

China: high-yielding rice seeded directly in aerobic nonpuddled<br />

and nonflooded soils (Bouman 2001). This high-input system<br />

is replacing lowland rice in areas w<strong>here</strong> water scarcity makes<br />

lowland rice impossible.<br />

Like wheat or maize, aerobic rice is grown on land prepared<br />

without water: a fine and firm seedbed is established<br />

with a wide range of soil water content. It is seeded either in<br />

holes or in strips. A shallow irrigation is applied immediately<br />

after sowing if the soil is too dry for seed to germinate and<br />

emerge. During the whole growth duration, no standing water<br />

is required. Consequently, irrigation water for aerobic rice is<br />

less than 50–70% of that for lowland rice in northern China<br />

(Wang et al 2002).<br />

Distribution of aerobic rice in China<br />

According to incomplete statistics, during a few years, the cultivation<br />

area of aerobic rice reached around 190,000 ha in 2000,<br />

constituting only 0.6% of China’s total rice cultivation area<br />

(Wang et al 2002). Because water shortages are more severe<br />

in the northern part of the country than in the southern, aerobic<br />

rice is mainly distributed in regions of northern and northeastern<br />

China, with 80,000 and 60,000 ha, respectively. Lowland<br />

rice area in northern China, which includes Beijing and<br />

Tianjin municipalities, and Hebei, Shandong, and Henan provinces,<br />

decreased dramatically by 17.5% from 1980 to 2001.<br />

Northeastern China, comprising Liaoning, Jilin, and<br />

Heilongjiang provinces, is the leading region for producing<br />

good-quality japonica rice, for which cultivation area dropped<br />

by 5.1% from 1990 to 2001. However, Liaoning is the only<br />

province suited to growing aerobic rice climatically. In Jilin<br />

and Heilongjiang, located to the north of Liaoning, the frostfree<br />

period is too short to grow aerobic rice, which needs direct<br />

seeding instead of raising seedlings in a greenhouse. In<br />

regions of central and southwestern China, w<strong>here</strong> rainfall is<br />

more than in the north regions, about 50,000 ha of aerobic rice<br />

are grown.<br />

Direct seeding of aerobic rice in northern China<br />

Aerobic rice is grown soon after winter wheat or the vegetable<br />

harvest in the region, with cumulative temperature ranging from<br />

4,000 to 5,000 °C and precipitation from 580 to 1,000 mm.<br />

Varieties Han Dao 277, Han Dao 297, Han Dao 65, Wushi<br />

Han Dao, Xiahan 51, and Han 946 are popularly or potentially<br />

cultivated. Optimal seeding dates have been documented from<br />

1 to 10 June. It is not recommended to sow aerobic rice after<br />

15 June, after which yield decreases by 324 kg ha –1 for every<br />

day late. For most cases, seeding rates in the region vary from<br />

120 to 150 kg ha –1 , and rice is sown in strips 25–30 cm apart<br />

and 2–3 cm deep, as breeders recommended (Wang et al 2001).<br />

An amount of 60–80 kg N ha –1 is applied as basal, with a total<br />

of 115–150 kg N ha –1 for most farmers. Generally, two other<br />

nitrogen splits (40–60 and 20–40 kg N ha –1 ) are placed at<br />

tillering and elongation stages, respectively. All phosphorus<br />

and potassium fertilizers are applied as basal at rates of 75–<br />

120 kg P 2 O 5 ha –1 and 20–30 kg K 2 O ha –1 ; however, in many<br />

cases, farmers do not use any potassium fertilizer. Irrigation is<br />

essential for relatively high yield. In the region, a shallow irrigation<br />

is conducted soon after sowing because of no irrigation<br />

during a very short period between harvest and seeding. Irrigation<br />

at the tillering stage is not required in most cases since<br />

it coincides with the rainy season owing to summer monsoon<br />

activities, until it lasts 15–20 days without available rain for<br />

sandy soils and 20–30 days for clay soils (Fan et al 2004).<br />

However, it was found that aerobic rice showed more tolerance<br />

of water stress at an early stage than at a late stage. Enough<br />

soil moisture during panicle forming and heading stages must<br />

be maintained, and irrigation is recommended for every 10<br />

days without rain (Fan et al 2004). Weed control is more important<br />

for direct seeding aerobic rice than for transplanting<br />

rice. Oxadiazon, butachlor, thiobencarb, and quinclorac are<br />

used as preemergence herbicides, and a mixture of butachlor<br />

and oxadiazon has been recommended and accepted widely.<br />

Propanil, butachlor, bentazone, and oxadiazon or their combinations<br />

are frequently applied for postemergence herbicides.<br />

Direct seeding of aerobic rice in northeastern China<br />

In northeastern China, aerobic rice is mainly grown as a single<br />

crop in Liaoning Province, w<strong>here</strong> cumulative temperature fluctuates<br />

from 2,731 to 3,674.3 °C, and precipitation is 350–1,100<br />

mm. Han Dao 297, Han 946, Dangeng 8, and Danhandao 1<br />

are the predominant varieties and they are seeded in strips at<br />

112.5 kg ha –1 directly at the end of April. Amounts of 50–75<br />

kg N ha –1 , 45 kg P 2 O 5 ha –1 , and 5 kg K 2 O ha –1 are recommended<br />

to be applied as basal, and 50–75 kg N ha –1 is applied<br />

as topdressing. A mixture of 4.5 kg ha –1 oxadiazon and 4.5 kg<br />

ha –1 butachlor is spread as a preemergence herbicide; a mixture<br />

of 3 kg ha –1 butachlor and 375 g ha –1 quinclorac is applied<br />

after emergence if needed.<br />

Direct seeding of aerobic rice in central China<br />

Multiyear average rainfall is 700–1,600 mm and cumulative<br />

temperature is 4,500–6,500 °C in the region. Aerobic rice is<br />

mainly grown on hilly rainfed land or intercropped with perennial<br />

crops such as trees of tea, fruit, and mulberry in their<br />

young period. It is also cultivated following winter wheat or<br />

rapeseed. Predominant varieties are Han Dao 277, Han Dao<br />

502, Wushi Handao, Zhonghan 3, and Han Dao 86-76. Aerobic<br />

rice, being rich in frost-free days and diverse in cropping<br />

systems, is directly seeded from the end of March to the beginning<br />

of June in central China. In most cases, it is seeded in<br />

Session 6: Trends in crop establishment and management in Asia 187


Table 1. Recommended target yield components of aerobic rice and<br />

the effect of high seed rates.<br />

Panicle Grain Filled Grain Yield<br />

Variety number number grain % weight (kg ha –1 )<br />

m –2 panicle –1 (g 10 –3 grains)<br />

Suggestions of breeders for high yield<br />

Han Dao 65 270 100 90 26 6,318<br />

Han Dao 277 255 98 95 28 6,647<br />

Han Dao 297 320 85 90 25 6,120<br />

Han Dao 502 280 110 90 29 8,039<br />

Farmers’ practice with 120–150 kg ha –1 seeding rate<br />

Han Dao 65 292 88 68 28.1 5,079<br />

Han Dao 277 344 57 85 26.5 3,870<br />

Han Dao 297 340 64 86 24.9 4,883<br />

Han Dao 502 334 83 70 28.4 5,438<br />

holes with 25–28 cm between rows and 15–18 cm in rows<br />

since the seeding rate is as low as 40–60 kg ha –1 . Farmers also<br />

used direct seeding in strips at 75–90 kg ha –1 . Fertilizer application<br />

rates are 120–150 kg N ha –1 , 40–90 kg P 2 O 5 ha –1 , and<br />

80–100 kg K 2 O ha –1 .<br />

Challenges and future emphasis<br />

Although a potential yield of 6.0–8.0 t ha –1 is claimed for aerobic<br />

rice, actual yield is estimated at 4.0–5.0 t ha –1 across all<br />

regions in China (Table 1). Aerobic rice yields in Anhui and<br />

Hubei provinces averaged 3.4–4.5 t ha –1 in 2003 according to<br />

field estimates. This yield has not satisfied farmers and for<br />

this reason the area of aerobic rice has not increased as in previous<br />

years. Moreover, compared with traditional lowland rice,<br />

improved aerobic rice exhibits a yield potential that is usually<br />

70% of that of paddy conditions.<br />

Agronomists have paid little attention to aerobic rice cultivation<br />

for the last two decades, during which improved varieties<br />

increasingly emerged, and no data are available for managers<br />

and technicians to make proper suggestions to farmers.<br />

Recommendations tend to follow those used for upland rice<br />

cultivation. For example, a seeding rate of 120 kg ha –1 or more<br />

is used widely in northern and northeastern China for aerobic<br />

rice. This rate is used for upland rice cultivation because the<br />

percentage of seedling survival and tillering ability is very low<br />

in poor hilly soils with little input. For high-yielding aerobic<br />

rice, assuming 80% emergence, a 120 kg ha –1 seeding rate<br />

would give 330–370 plants m –2 , which would lead to much<br />

more than the 250–300 panicles m –2 , which is the recommended<br />

optimal panicle number for yield of around 6–8 t ha –1 . This<br />

could lead to weak plant growth, very small panicles, and a<br />

low yield of 3.8–5.4 t ha –1 (Table 1). Field experiments with<br />

seeding-rate treatments showed that a seeding rate of 60–80<br />

kg ha –1 produced a significantly higher yield (more than 6.0 t<br />

ha –1 ) because of the higher proportion of productive tillers<br />

(Feng et al 2003). It also suggested that nitrogen fertilizer of<br />

no more than 120 kg N ha –1 could meet the need for aerobic<br />

rice growth with a yield of 5.0–6.0 t ha –1 .<br />

T<strong>here</strong>fore, it is crucial to promote and stabilize the yield<br />

of aerobic rice with a target level of 6.0 t ha –1 , and we believe<br />

that this is possible. Greater attention should be paid to investigating<br />

crop establishment according to the following questions:<br />

1. Is the high yield of aerobic rice dependent on main<br />

stems or tillers for different varieties, or what percentage<br />

of tillers contributes to yield Is this directly<br />

related to seeding rate Experience in lowland rice in<br />

China across the north to south suggests that it is essential<br />

to promote as many tillers as possible and to<br />

promote a productive tiller percentage as high as 90%<br />

or more for high yield (Lin 2000).<br />

2. How do we manage fertilization according to nutrient<br />

uptake by aerobic rice to obtain high yields Improved<br />

varieties differ from lowland or traditional<br />

upland rice with low productivity. However, no data<br />

on mechanisms for nutrient uptake by the new type<br />

rice in China are available on which to base fertilizer<br />

recommendations (Xie et al 2003).<br />

Additionally, as rice establishment changes from transplanting<br />

to direct seeding, we face challenges for weed control,<br />

irrigation regimes, and sowing mechanisms.<br />

References<br />

Bouman BAM. 2001 Water-efficient management strategies in rice<br />

production. Int. <strong>Rice</strong> Res. Notes 16(2):17-22.<br />

Fan JH, Cai CH, Zhan Y, Li XC, Sun PZ. 2004. Water-saving cultivation<br />

technology of aerobic rice. Shandong Agric. Sci. 1:45-<br />

46.<br />

Feng SZ, Yang HG, Liu WX, Peng MX, Liu FM, Ma DL. 2003.<br />

Effects of sowing rates on the yield formation of aerobic rice<br />

after wheat. Crop Res. 17(2):73-77.<br />

Li YN, Duan AW. 2002. Introduction to water resources and watersaving<br />

agriculture. In: Qian YB, Li YN, Yang G, editors. Studies<br />

on new technology of water-saving agriculture. Zhengzhou<br />

(China): Yellow River Water Conservancy Press. p 8-12.<br />

Lin QH. 2000. <strong>Rice</strong> population quality and regulation. In: Lin QH,<br />

editor. Crop population quality. Shanghai (China): Shanghai<br />

Scientific & Technical Publishers. p 42-217.<br />

Wang H, Bouman BAM, Zhao D, Wang C, Moya PF. 2002. Aerobic<br />

rice in northern China: opportunities and challenges. In:<br />

Bouman BAM, Hengsdijk H, Hardy B, Bindraban PS, Tuong<br />

TP, Ladha JK, editors. Water-wise rice production. Manila<br />

(Philippines): <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>. p 143-<br />

154.<br />

Wang SX, Yin HQ, Tang BJ, Wang YT, Leng GX. 2001. High-yielding<br />

cultivation technology of aerobic rice in Huanghuai Plain.<br />

Henan Agric. Sci. 11:11-12.<br />

Xie GH, Wang SY, Wang HQ, Zhao M. 2003. Mineral nutrition uptake<br />

and fertilization effects of aerobic rice. Sci. Agric. Sin.<br />

36:1171-1176.<br />

Notes<br />

Authors’ address: College of Agronomy and Biotechnology, China<br />

Agricultural University, Beijing 100094, China, e-mail:<br />

xiegh@cau.edu.cn.<br />

188 <strong>Rice</strong> is life: scientific perspectives for the 21st century


An overview on direct seeding<br />

for rice crop establishment in the Philippines<br />

Jovino L. de Dios, Evelyn F. Javier, Myrna D. Malabayabas, Madonna C. Casimero, Alex J. Espiritu<br />

The Philippines is situated in Southeast Asia, with tropical climate<br />

and wet and dry seasons. <strong>Rice</strong> is the staple food and has<br />

been cultivated since time immemorial. Before the introduction<br />

of wetland rice, direct seeding in the “caiñgin” or slash<br />

and burn on mountain slopes (Fig. 1A) and secano or “dry<br />

planting” on undulating lands to flatlands (Fig. 1B) were practiced.<br />

Shifting cultivation<br />

Migrants from mainland Asia carried the traditions of lowland<br />

rice cultivation to the Philippines during the second millen-<br />

nium B.C. (www.riceweb.org/History.htm#Origin), later called<br />

“tubigan” or transplanting (Camus 1921). When irrigation systems<br />

were introduced in 1840, only 30% of the total area<br />

planted to rice was irrigated until 1913 and only a few farms<br />

had sufficient irrigation water for two rice crops a year (Alfonso<br />

and Catambay 1948).<br />

Transplanting became common when irrigation pumps<br />

and canals were constructed in the 1950s (Sta Iglesia and Lawas<br />

1959) and the National Irrigation Administration was created<br />

in 1963. Almost all flatlands (approx. 3.126 million ha) were<br />

planted to rice during the wet season but the majority are still<br />

rainfed. When irrigated area increased to 1,387,855 ha (NIA<br />

Fig. 1. Different methods of rice planting in the Philippines (A-D) and adoption of<br />

direct seeding in average percentage of the regional area (E). A: caiñgin on mountain<br />

slopes, B: secano or dry seeding on flatland, C: lipat-tanim or transplanted<br />

rice, D: dalatan or sabog-tanim in wet paddies.<br />

Session 6: Trends in crop establishment and management in Asia 189


Table 1. Relative distribution (%) of farms reported practicing direct seeding or<br />

transplanting as crop establishment in the Philippines.<br />

Year<br />

Direct seeding<br />

Transplanting<br />

Jan to Jun cropping Jul to Dec cropping Jan to Jun cropping Jul to Dec cropping<br />

(dry season) (wet season) (dry season) (wet season)<br />

1998 62.77 37.23 66.05 33.95<br />

1999 67.85 32.15 64.27 35.73<br />

2000 65.88 34.12 68.82 31.18<br />

2001 69.23 30.77 68.33 31.67<br />

2002 67.02 32.98 71.27 28.73<br />

Source: Phil<strong>Rice</strong>-BAS (2004).<br />

2004), t<strong>here</strong> were more dry-season rice crops in areas with<br />

enough water. The introduction of short-duration<br />

nonphotosensitive rice varieties and effective fertilizer management<br />

by <strong>IRRI</strong> led to improved yields.<br />

The shift from transplanting (Fig. 1C) to wet direct seeding<br />

(WDS) or “sabog-tanim” (Fig. 1D) with improved management<br />

practices for weeds, pests, water, and fertilizer could<br />

be due to high production costs (De Datta 1986, De Datta and<br />

Flinn 1986), labor scarcity for transplanting during the peak<br />

season, the opportunity for early establishment for more cropping<br />

and maximizing available soil moisture, avoidance of bad<br />

weather conditions during harvesting, and conserving more<br />

water. In Central Luzon, Philippines, for example, the adoption<br />

rate of WDS was from


t ha –1 season –1<br />

t ha –1 season –1<br />

5<br />

4<br />

Regional average yield of rice in the wet season<br />

Transplanted<br />

Direct seeded<br />

A<br />

5<br />

4<br />

Regional average yield of rice in the dry season<br />

Transplanted<br />

Direct seeded<br />

B<br />

3<br />

3<br />

2<br />

2<br />

1<br />

1<br />

0<br />

1 2 3 4 5 6 7 8 9 10 11 12 13<br />

Region<br />

ARMM<br />

0<br />

1 2 3 4 5 6 7 8 9 10 11 12 13<br />

Region<br />

ARMM<br />

%<br />

%<br />

Dry season<br />

Wet season<br />

80<br />

C<br />

60<br />

D<br />

60<br />

40<br />

40<br />

20<br />

20<br />

0<br />

Broadleaves Sedges Grasses<br />

0<br />

Broadleaves Sedges Grasses<br />

Weed type<br />

Weed type<br />

mm %<br />

60<br />

800<br />

Water used (mm)<br />

E<br />

Water saved (%)<br />

50<br />

600<br />

40<br />

400<br />

200<br />

30<br />

20<br />

10<br />

0<br />

Continuously<br />

flooded<br />

Irrigation when<br />

no floodwater<br />

Shallow irrigation<br />

(0–2 cm)<br />

Irrigation every<br />

14 d<br />

0<br />

Water management<br />

Fig. 2. Regional average yields of direct-seeded and transplanted rice in the Philippines (A and B), weed-type distribution for wet- and<br />

dry-season wet direct-seeded rice (C and D), and water used and saved by using controlled irrigation (E).<br />

w<strong>here</strong>as pregerminating means soaking the seeds for 12–24 h,<br />

followed by incubating for 24–35 h. Dry and primed seeds are<br />

usually sown in dry to moist soil, w<strong>here</strong>as pregerminated seeds<br />

are usually sown in saturated soil.<br />

Sowing methods. Broadcast seeding is the most common<br />

method because of simplicity. Drilling or distributing seeds<br />

evenly in rows is done manually or by a seeder. Dibbling or<br />

localized planting of seeds is done in small holes created by a<br />

pointed object thrust into the soil. This is common in caiñgin<br />

(minimal or zero-tillage).<br />

Seeding rate. Most farmers used seeding rates of up to<br />

200 kg of seed ha -1 although the recommended rate is 60–80<br />

kg ha –1 (Table 2). The wide variation among regions could be<br />

attributed to their culture, skills, technical knowledge, and the<br />

presence of adverse conditions for DS such as uncontrolled<br />

water and the presence of pests that affect crop establishment.<br />

Higher seeding rates would be beneficial if no weed control is<br />

planned (Guyer and Quadranti 1985), but it is not necessary to<br />

use high seeding rates to suppress weeds if an effective herbicide<br />

is used (Castin and Moody 1989).<br />

Session 6: Trends in crop establishment and management in Asia 191


Table 2. Average seeding rates (in kg ha -1 ) in<br />

the Philippines.<br />

Year Direct seeding Transplanted<br />

1998 155 101<br />

1999 151 92<br />

2000 150 91<br />

2001 143 89<br />

2002 146 94<br />

Mean 151 94<br />

Recommended 60–80 20–40<br />

Source: Phil<strong>Rice</strong> Statistics 1970-2002.<br />

Crop care<br />

Weed problems. Early control of weeds efficiently alleviates<br />

weed problems because it lessens competition between rice<br />

and weeds that emerge simultaneously in direct seeding.<br />

Farmers normally practice hand weeding. Nevertheless,<br />

in wet broadcast seeding, hand weeding is more difficult and,<br />

before weeds are removed, damage has been done to rice. Hand<br />

weeding might be too slow and it might not coincide with the<br />

best time to minimize competition. If weeding is delayed beyond<br />

20 d after emergence, irreparable damage is done. During<br />

early establishment, weeds have 20–30% of their growth,<br />

while the crop has 2–3% of its growth (Moody 1990).<br />

Major weeds include grasses such as Echinochloa spp.<br />

and Leptochloa chinensis, sedges such as Cyperus spp. and<br />

Fimbristylis miliacea, and broadleaves such as Monochoria<br />

vaginalis, Sphenoclea zeylanica, and Ludwigia octovalvis.<br />

During the wet season, sedges and broadleaves dominate, while<br />

only broadleaves dominate during the dry season (Fig. 2C,D).<br />

However, some cultural management practices help mitigate<br />

this problem. Properly prepared land, managed water, and selected<br />

herbicides based on types of weeds present, water status,<br />

and growth stage of the crop are very important. Some<br />

herbicides such as safened butachlor at 0.75 kg ai ha –1 and<br />

safened pretilachlor at 0.3 kg ai ha –1 applied at 3 DAS work<br />

well in WDS with controlled irrigation.<br />

Weed control strategies must be well integrated for better<br />

long-term control and environmental protection. Timing of<br />

herbicide application is very important.<br />

Fertilizer management. Basal N is not recommended.<br />

Instead, NPK fertilizers are applied 10–20 d after seeding<br />

(DAS). More nitrogen fertilizer during panicle initiation is<br />

recommended. The most efficient time for fertilizer N application<br />

is during panicle initiation, while basal is less efficient<br />

because (1) the surge of available-N from inorganic fertilizer<br />

is a mismatch for the low N requirement of young plants, (2)<br />

t<strong>here</strong> is still high N from the soil during the early part of the<br />

season, (3) the practice of suspending irrigation 10–20 DAS<br />

to hasten seedling survival and to stabilize soil may trigger<br />

high N loss, and (4) an early high-N supply may give more<br />

chance for weeds to compete with rice. Around panicle initiation,<br />

the N uptake rate and requirement are high, w<strong>here</strong>as N<br />

application during tillering is condition-specific. The use of<br />

real-time N management such as the leaf color chart strategy<br />

was also introduced in direct seeding.<br />

Water management. Pond water during land preparation<br />

aids in land leveling. Shallow pond water 10–14 days after the<br />

crop had established until the time when weed germination is<br />

still critical helps prevent weeds from germinating or slows<br />

the growth of others. Mabbayad (1967) reported that weed<br />

weight decreased markedly even at a shallow water depth of<br />

2.5 cm.<br />

Water is also very important in establishing good WDS.<br />

The field is drained within 2 wk after seeding by constructing<br />

shallow drainage ditches or “canaletes” inside the paddy to<br />

prevent floods when rains come just after seeding.<br />

Dry seeding and semidryland preparation save a significant<br />

amount of water during land preparation. Controlled irrigation<br />

can save as much as 50% of water and the corresponding<br />

labor cost for irrigation (Fig. 2E). Good land preparation<br />

also helps in water savings. Because of water scarcity, the localized<br />

testing of aerobic rice technology to save more irrigation<br />

water is under way. Aerobic rice technology means growing<br />

rice in aerated soil with characteristic high yields and fertilizer<br />

response comparable with those of irrigated lowland<br />

rice culture.<br />

References<br />

Alfonso DJ, Catambay AB. 1948. A study of the net duty of irrigation<br />

water for lowland rice in Calamba, Laguna. Philipp. Agric.<br />

32(2):87-113.<br />

Camus JS. 1921. <strong>Rice</strong> in the Philippines. Philipp. Agric. Rev. 14(1):7-<br />

86.<br />

Castin EM, Moody K 1989. Effect of different seeding rates, moisture<br />

regimes, and weed control treatments on weed growth<br />

and yield of wet-seeded rice. In: Proceedings of the 12th Asian-<br />

Pacific Weed Science Society Conference, Seoul, Korea.<br />

p 337-343.<br />

De Datta SK. 1986. Technology development and the spread of direct-seeded<br />

flooded rice in Southeast Asia. Exp. Agric. 22:417-<br />

426.<br />

De Datta SK, Flinn JC. 1986. Technology and economics of weed<br />

control in broadcast-seeded flooded tropical rice. In: Noda K,<br />

Mercado BL, editors. Weeds and the environment in the tropics.<br />

Bangkok (Thailand): Asian Pacific Weed Agency.<br />

Guyer R, Quadranti M. 1985. Effect of seed rate and nitrogen level<br />

on the yield of direct wet-seeded rice. In: Proceedings of the<br />

10th Asian-Pacific Weed Science Society Conference,<br />

Chiangmai, Thailand. p 304-311.<br />

Khan MAK, Bhuiyan SI, Undan RC. 1992. Assessment of directseeded<br />

rice in an irrigated system in the Philippines.<br />

Bangladesh <strong>Rice</strong> J. 3(1&2):14-20.<br />

Mabbayad BB. 1967. Tillage techniques and planting methods for<br />

lowland rice. M.Sc. thesis. University of the Philippines College<br />

of Agriculture, College, Laguna, Philippines.<br />

Moody K. 1990. Post-planting weed control in direct-seeded rice.<br />

Paper presented at a <strong>Rice</strong> Symposium, 25-27 September 1990,<br />

Malaysian Agricultural <strong>Research</strong> and Development <strong>Institute</strong>,<br />

Penang, Malaysia.<br />

192 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Moody K, Cordova VG. 1985. Wet-seeded rice. In: Women in rice<br />

farming. Manila (Philippines): <strong>International</strong> <strong>Rice</strong> <strong>Research</strong><br />

<strong>Institute</strong>. p 467-478.<br />

NIA (National Irrigation Administration). 2004. Irrigation development.<br />

www.nia.da.gov.ph/Systems/Irrigation_Development.htm,<br />

19 August 2004.<br />

Phil<strong>Rice</strong>, BAS. 2004. Philippine rice statistics 1970-2002. Volume<br />

2. Muñoz, Nueva Ecija (Philippines): Phil<strong>Rice</strong>, BAS.<br />

Sta Iglesia JC, Lawas JM. 1959. Effects of pump irrigation on farmers’<br />

organization, operation and income of rice farms in Sto.<br />

Domingo and La Purisima, Nabua, Camarines Sur. In: A halfcentury<br />

of Philippine agriculture. BA Golden Jubilee Committee.<br />

Manila (Philippines): Graphics House. 463 p.<br />

Notes<br />

Authors’ address: Philippine <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>, Science City<br />

of Muñoz, Nueva Ecija 3119, Philippines, e-mail:<br />

jldeDios@philrice.gov.ph.<br />

<strong>Rice</strong> establishment in drought-prone areas of Bangladesh<br />

M.A. Mazid, M.A. Mortimer, C.R. Riches, A. Orr, B. Karmaker, A. Ali, M.A. Jabbar, and L.J. Wade<br />

The High Barind Tract of northwest Bangladesh is droughtprone,<br />

with the majority of the 1,200–1,400-mm mean annual<br />

rainfall occurring in June to October. Limited irrigation potential<br />

restricts cropping intensity to 175%, considerably less<br />

than in districts w<strong>here</strong> irrigation allows two or three rice crops<br />

each year (Nur-E-Elahi et al 1999). The majority of farmers<br />

produce a single crop of transplanted rainfed rice, grown in<br />

this monsoon season. Some 80% of the area then lies fallow in<br />

the postrice rabi season. The challenge in the Barind is to simultaneously<br />

improve the reliability and yield of rice while<br />

increasing total system productivity by increasing the area<br />

planted to postrice rabi crops, including chickpea, linseed, and<br />

mustard (Mazid et al 2003). Mazid et al (2002, 2003) have<br />

proposed that the productivity of Barind soils can be increased<br />

by switching from transplanted rice (TPR) to direct-seeded<br />

rice (DSR) to allow more reliable establishment of rabi crops<br />

on residual moisture immediately after the rice harvest.<br />

Chickpea, a drought-tolerant and high-value crop, can be grown<br />

successfully when seeded after rice in late October to mid-<br />

November. This can make significant contributions to higher<br />

productivity and improved farm income. A late onset of the<br />

monsoon delays transplanting as a minimum of 600 mm of<br />

cumulative rainfall is needed to complete ploughing, puddling,<br />

and transplanting. Direct seeding can be completed after<br />

ploughing, however, following only 150 mm of cumulative<br />

rainfall (Saleh and Bhuiyan 1995). Earlier planted DSR matures<br />

1–2 weeks before transplanted rice, thus reducing the<br />

risk of terminal drought and allowing earlier planting of a following<br />

nonrice crop (Saleh et al 2000). An earlier rice harvest<br />

can also be achieved by planting early-maturing rice varieties.<br />

Swarna, the most widely grown cultivar, matures after 140 to<br />

145 days and, when transplanted, may not be harvested until<br />

early to mid-November. In many years, soil dries rapidly at<br />

this time, reducing the likelihood of successful chickpea establishment.<br />

DSR reduces labor and draft power requirements for rice<br />

establishment by 16% and 30%, respectively, compared with<br />

TPR. However, weeds are a major constraint to the adoption<br />

of DSR as the in<strong>here</strong>nt advantage of weed control afforded by<br />

transplanted rice in standing water is lost (Mazid et al 2002).<br />

Labor shortages for many households prevent timely first weeding<br />

of transplanted rice so that with current practices 34% of<br />

farmers lose over 0.5 t ha –1 of the attainable rice yield because<br />

of weed competition (Mazid et al 2001). The additional weed<br />

problems in DSR may be overcome, however, by applying a<br />

preemergence herbicide (Mazid et al 2001). We report on the<br />

productivity of direct seeding of an early-maturing rice cultivar<br />

with herbicide application, followed by chickpea in the<br />

postrice season.<br />

Methods<br />

Systems trial<br />

The productivity of two rice cultivars when direct-seeded or<br />

transplanted was evaluated in the Barind from 2001 to 2003<br />

under differing nutrient regimes. Modern cultivar BRRI dhan<br />

39 (BR39) (maturity 120–125 days) was compared with the<br />

widely grown Swarna (maturity 145–150 days). The experiment<br />

was conducted with a split-split plot design with main<br />

plots (3) as crop establishment and associated weed management,<br />

subplots (4) as nutrient management, and sub-subplots<br />

(2) as cultivars. Establishment treatments were (1) transplanted<br />

rice (TPR)—soil puddled prior to transplanting and plots handweeded<br />

twice at 30 and 45 days after transplanting (DAT); (2)<br />

direct-seeded rice (DSR)—soil ploughed prior to dry seeding<br />

(2001) or ploughed and puddled before direct seeding of<br />

pregerminated seed (2002 and 2003) in rows by hand, with<br />

hand weeding at 21, 33, and 45 days after sowing (DAS); (3)<br />

direct-seeded rice with chemical weed control (DSRH)—as<br />

with DSR but with oxadiazon (375 g a.i. ha –1 ) applied 2–4<br />

days after seeding, with one hand weeding at 33 DAS. Nutrient<br />

regimes were (kg ha –1 ) (1) single superphosphate, 40 P +<br />

40 K; (2) compound 60 N + 40 P + 40 K; (3) farmyard manure<br />

(FYM) + inorganic fertilizer totaling 60 N + 50 P + 50 K; and<br />

Session 6: Trends in crop establishment and management in Asia 193


Table 1. Effect of rice establishment method and rice cultivar on grain yield of rice<br />

and a postrice chickpea crop (t ha –1 ± S.E.), 2002-04, Rajabari, northwest<br />

Bangladesh.<br />

Crop Transplanted rice Direct-seeded rice<br />

BR39 Swarna BR39 Swarna<br />

<strong>Rice</strong><br />

2001 1.92 ± 0.10 2.79 ± 0.19 2.91 ± 0.12 2.85 ± 0.11<br />

2002 2.80 ± 0.13 2.59 ± 0.11 2.96 ± 0.08 3.75 ± 0.15<br />

2003 0.61 ± 0.08 0.51 ± 0.05 1.62 ± 0.21 2.67 ± 0.16<br />

Chickpea<br />

2001-02 – a – 1.01 ± 0.06 0.91 ± 0.05<br />

2002-03 – – 0.76 ± 0.05 0.49 ± 0.04<br />

2003-04 – – 0.38 ± 0.04 0.16 ± 0.02<br />

a<br />

= chickpea not sown.<br />

(4) diammonium phosphate (DAP) (18% N) + Guti slow-release<br />

urea (45%N) totaling 43 N + 40 P + 40 K. <strong>Rice</strong> was<br />

harvested in a 5-m 2 area. Biomass of individual weed species<br />

was recorded in two unweeded quadrats per plot at 28 DAS/<br />

DAT and total weed biomass at 45 DAS/DAT.<br />

Trials began at 16 sites during the 2003 monsoon season<br />

to verify the profitability of a DSR rice-chickpea system.<br />

Chickpea (cv. Barisola 2) was sown after the harvest of Swarna<br />

or three shorter-duration BRRI dhan cultivars established by<br />

either transplanting or direct seeding. Prior to dry direct seeding<br />

in June, the land was ploughed (at least 3 times) with an<br />

animal-drawn country plough and leveled with a ladder. Seed<br />

was sown in lines by hand into furrows opened by a handpulled<br />

lithao (plough). Seedbeds were established at the same<br />

time and seedlings were transplanted at approximately 30 DAS<br />

following conventional ploughing and puddling operations. In<br />

direct-seeded rice, a single application of oxadiazon (375 g<br />

a.i. ha –1 ) was made to control weeds, w<strong>here</strong>as, in transplanted<br />

rice, pretilachlor (450 g a.i. ha –1 ) was applied.<br />

Seasonal variation in rainfall was considerable. The annual<br />

rainfall in 2001, 2002, and 2003 was 1,475, 1,464, and<br />

932 mm, respectively. In July 2003, rainfall was 2.5 times less<br />

than in the same month in previous years and in 2001 it was<br />

highest in October.<br />

Results<br />

Systems trial<br />

T<strong>here</strong> were significant effects of cropping system on the phenology<br />

of rice. Flowering was always later with cv. Swarna<br />

and under transplanting (P broadleaf<br />

weeds.<br />

The yields of chickpea after direct-seeded rice were significantly<br />

higher following BR39 than after Swarna in 2002<br />

and 2003 (P


Grain yield (t ha –1 )<br />

8<br />

6<br />

4<br />

0.65 ± 0.07<br />

0.67 ± 0.06<br />

0.70 ± 0.07<br />

0.61 ± 0.06<br />

the relatively low chickpea yields obtained on-farm in 2003,<br />

after either transplanted or direct-seeded rice, provided worthwhile<br />

additional income given the crop’s low input costs and<br />

high market value. Further studies are continuing to evaluate<br />

the profitability and sustainability of direct-seeding and ricechickpea<br />

systems under farmer management.<br />

2<br />

0<br />

Conclusions<br />

BR31 BR32 BR39 Swarna<br />

Cultivar<br />

Fig. 1. Productivity (t ha –1 ) of rice and chickpea<br />

grown in transplanted rice (open columns) and<br />

direct-seeded rice (solid columns) systems.<br />

Data are means of 16 on-farm sites in 2003<br />

(monsoon and rabi seasons). Weed control in<br />

rice is by preemergence herbicide. Data above<br />

each pair of bars are chickpea yields (t ha –1 ±<br />

S.E.).<br />

The systems trial confirmed that replacing transplanted rice<br />

with direct-seeded rice could improve farm productivity in the<br />

Barind by allowing a greater opportunity to raise a high-value<br />

rabi crop. The early-season weed flush associated with direct<br />

seeding can be successfully controlled by oxadiazon applied<br />

preemergence. However, one subsequent manual weeding will<br />

be essential for yield protection from weed competition and to<br />

prevent a buildup of Alternanthera sessilis, Cyperus iria, and<br />

Paspalum distichum in particular. While extensive cultivar<br />

evaluation is under way, cvs. BR31 and BR32 represent promising<br />

lines for direct seeding. BR39, on the other hand, is not<br />

suitable for direct seeding as sterility is a major problem when<br />

it is planted early because it tends to flower in rains. Successful<br />

chickpea cropping after rice is contingent upon the presence<br />

of residual soil moisture and the time-window for successful<br />

chickpea establishment may be difficult to exploit.<br />

Chickpea yields in the systems trial reported above were always<br />

higher because crops were established immediately after<br />

the rice harvest. In on-farm trials in 2003, the potential advantage<br />

from direct seeding was not evident because widespread<br />

rain showers during the first two weeks of October favored<br />

establishment regardless of the time of the rice harvest. High<br />

yields were not achieved, however, because of late-season<br />

drought. Our associated socioeconomic studies indicate that,<br />

although farmers are keen to gain additional income from growing<br />

chickpea, many, particularly resource-poor share-croppers<br />

who pass 50% of their production to the landlord, need practices<br />

that maximize rice yield. To be widely adopted for direct<br />

seeding in place of Swarna, an early-maturing rice cultivar will<br />

need to be high-yielding and sheath-blight-resistant. The reduction<br />

in input costs (no nursery and substitution of labor<br />

with a herbicide) that can be achieved with direct seeding and<br />

early planting of chickpea was evaluated favorably by an onfarm<br />

trial with farmers in 2003. Farmers considered that even<br />

References<br />

Mazid MA, Bhuiyan SI, Mannan MA, Wade LJ. 2002. Dry-seeded<br />

rice for enhanced productivity of rainfed drought-prone lands:<br />

lessons from Bangladesh and the Philippines. In: Pandey S,<br />

Mortimer M, Wade LJ, Tuong TP, Hardy B, editors. Direct<br />

seeding in Asian rice systems: strategic research issues and<br />

opportunities. Manila (Philippines): <strong>International</strong> <strong>Rice</strong> <strong>Research</strong><br />

<strong>Institute</strong>. p 185-201.<br />

Mazid MA, Jabber MA, Riches CR, Robinson EJZ, Mortimer M,<br />

Wade LJ. 2001. Weed management implications of introducing<br />

dry-seeded rice in the Barind Tract of Bangladesh. Proceedings<br />

of the BCPC Conference–Weeds 2001. 1:211-216.<br />

Mazid MA, Jabber MA, Mortimer M, Wade LJ, Riches CR, Orr AW.<br />

2003. Improving rice-based cropping systems in north-west<br />

Bangladesh: diversification and weed management. The BCPC<br />

<strong>International</strong> Congress, Crop Production and Protection.<br />

p 1029-1034.<br />

Nur-E-Elahi AH, Khan MR, Siddique A, Saha M, Nasim M,<br />

Shahidullah SM. 1999. Existing cropping patterns of<br />

Bangladesh: potential techniques and strategies for improving<br />

system productivity. In: Mandal MR, editor. Proceedings<br />

of the Workshop on Modern <strong>Rice</strong> Cultivation in Bangladesh.<br />

Gazipur (Bangladesh): Bangladesh <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>.<br />

p 107-169.<br />

Saleh AFM, Bhuiyan SI. 1995. Crop and rainwater management strategies<br />

for increasing productivity of rainfed lowland rice systems.<br />

Agric. Syst. 49:259-276.<br />

Saleh AFM, Mazid MA, Bhuiyan SI. 2000. Agrohydrologic and<br />

drought-risk analyses of rainfed cultivation in northwest<br />

Bangladesh. In: Tuong TP, Kam SP, Wade LJ, Pandey S,<br />

Bouman BAM, Hardy B, editors. Characterizing and understanding<br />

rainfed environments. Manila (Philippines): <strong>International</strong><br />

<strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>. p 233-244.<br />

Notes<br />

Authors’ addresses: M.A. Mazid, Bangladesh <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong><br />

(BRRI), Post Rangpur Cadet College, Rangpur 5404,<br />

Bangladesh, e-mail: brrirang@bdonline.com; M.A. Mortimer,<br />

University of Liverpool, L69 3BX, UK; C.R. Riches and A.<br />

Orr, Natural Resources <strong>Institute</strong>, University of Greenwich,<br />

ME4 4TB, UK; B. Karmaker and A. Ali, BRRI, Post<br />

Shyampur, Rajshahi, Bangladesh; M.A. Jabbar, BRRI, Post<br />

BRRI, Gazipur, Bangladesh; L.J. Wade, The University of<br />

Western Australia, Crawley, WA 6009, Australia.<br />

Acknowledgments: This work was partially funded by the UK Department<br />

for <strong>International</strong> Development (Crop Protection<br />

Programme Project R8234). However, the views expressed<br />

are not necessarily those of DFID. Support has also been received<br />

from the Consortium for Unfavorable <strong>Rice</strong> Environments<br />

(ADB/<strong>IRRI</strong>).<br />

Session 6: Trends in crop establishment and management in Asia 195


Emerging issues in weed management of direct-seeded rice<br />

in Malaysia, Vietnam, and Thailand<br />

M. Azmi, D.V. Chin, P. Vongsaroj, and D.E. Johnson<br />

Malaysia’s rice area was 692,600 ha for the combined dryand<br />

wet-season crops in 2000. In Peninsular Malaysia, rice<br />

double cropping in the eight granary areas accounted for a<br />

third of this total. Direct seeding (DS) as an alternative to the<br />

traditional transplanting method in the main granaries in Malaysia<br />

began in the late 1970s and t<strong>here</strong>after expanded rapidly<br />

(Azmi and Abdullah 1998). By 2000, this method accounted<br />

for more than 90% of the total rice area planted. Wet seeding<br />

rather than dry is favored but is only feasible w<strong>here</strong> good water<br />

management is possible. DS is undertaken by hand broadcasting<br />

or using a motorized blower.<br />

<strong>Rice</strong> is the most important crop in Vietnam and Thailand.<br />

The crop is grown in Vietnam on 4.2 million ha or<br />

74.1% of the arable land and produces 29 million tons every<br />

year. The Mekong River Delta in the south and Red River Delta<br />

in the north are the two main regions for rice production, occupying<br />

52% and 18% of the national rice area. In the Red<br />

River Delta, rice is largely transplanted and double-cropped,<br />

w<strong>here</strong>as, in the Mekong Delta, about half the rice area is irrigated,<br />

t<strong>here</strong> are three growing seasons, and the crop is mainly<br />

direct-seeded. Wet seeding is the most common practice (about<br />

60% of the area), with water seeding, zero tillage, and dry<br />

seeding making up the balance. <strong>Rice</strong> cultivation in Thailand<br />

covers about 10 million ha. At the end of the 1990s, the majority<br />

of the rainfed rice area was dry direct-seeded and the remainder<br />

transplanted, w<strong>here</strong>as irrigated areas in the Central<br />

Plain were largely wet-seeded. Ten years earlier, however, most<br />

of the rainfed areas had been transplanted, as were 30% of the<br />

irrigated areas of the Central Plain, with the remaining areas<br />

being dry-seeded. This rapid change in establishment methods<br />

was the result of labor shortages in rural areas, particularly<br />

during the peak season.<br />

Weed succession in rice ecosystems<br />

The widespread introduction of DS, the repeated use of herbicides,<br />

and limited irrigation supplies in the 1990s are the factors<br />

responsible for the shift in weed species populations in<br />

rice ecosystems. Grasses, such as Echinochloa crus-galli, along<br />

with other Echinochloa spp. (E. oryzicola, E. colona, E.<br />

stagnina, and E. picta), Leptochloa chinensis, and Ischaemum<br />

rugosum, which were not prevalent and dominant in Malaysian<br />

rice fields in the 1970s (Azmi et al 1993), became widespread<br />

in the 1990s. Weed surveys were carried out in areas<br />

w<strong>here</strong> direct seeding was being introduced to replace transplanting<br />

from 1989 to 1993. In 1989, while transplanting was<br />

the principal system, Monochoria vaginalis, Sphenoclea<br />

guyanensis, Fimbristylis miliacea, and Leptochloa flava were<br />

dominant weeds. In 1993, these were replaced by L. chinensis,<br />

E. crus-galli, M. vaginalis, and E. colona in areas that were<br />

by then mostly direct-seeded. From 1981 to 1994, the areas<br />

infested by L. chinensis grew by an estimated 4% per annum<br />

and all areas in Muda were infested by 1992. A similar trend<br />

was observed in Vietnam, w<strong>here</strong> E. crus-galli, L. chinensis,<br />

and weedy rice were dominant weeds in the DS systems (Chin<br />

2001). In Thailand, Sphenoclea zeylanica, Monochoria<br />

vaginalis, and Marsilea minuta are dominant in the transplanted<br />

systems, w<strong>here</strong>as E. crus-galli, L. chinensis, Cyperus iria, and<br />

C. difformis are dominant in the wet-seeded areas (Vongsaroj<br />

1997). Some of the shifts in the importance of weed species as<br />

a result of changes in crop establishment method from traditional<br />

transplanting (1970s) to DS culture are shown in Table<br />

1. Weedy rice is difficult to control because of its similarity to<br />

the rice plant. It was detected in Malaysia in 1988 (Azmi and<br />

Abdullah 1998) and Vietnam in 1994 (Chin 2001), and t<strong>here</strong><br />

has also been a rapid ingression of weedy rice in the DS area<br />

of the Central Region of Thailand in recent years. Recent weed<br />

surveys conducted in Malaysia found that weedy rice (Oryza<br />

sativa) had become a problem, and the weed is thought to be a<br />

serious threat to rice production (Azmi et al 2003).<br />

Yield loss from weeds<br />

Yield losses largely depend on season, weed species, weed<br />

density, rice cultivar, and growth rate and density of weeds<br />

and rice. Weedy rice at 35% infestation can cause about a 60%<br />

yield loss (Watanabe et al 1997) and, under a serious infestation,<br />

a yield loss of 74% was recorded in DS rice (Azmi and<br />

Abdullah 1998).<br />

Impact of prolonged herbicide usage in direct-seeded rice<br />

Labor shortages have led to an increase in direct seeding and a<br />

rapid increase in the use of and reliance on herbicides. This<br />

reliance has resulted in an undesirable shift in weed species<br />

and concerns about environmental contamination. Phenoxy and<br />

sulfonylurea compounds are widely used herbicides in Malaysia,<br />

Vietnam, and Thailand to control broadleaf weeds and<br />

sedges in DS rice. Weeds resistant to these herbicides have<br />

evolved and t<strong>here</strong> is evidence that weed species such as S.<br />

zeylanica, Marsilea minuta, and F. miliacea have developed<br />

resistance to phenoxy herbicides (Watanabe et al 1997). Lately,<br />

acetolactate-synthase (ALS) inhibitor-resistant biotypes have<br />

been reported in several weed species in many countries, including<br />

Malaysia (Azmi and Baki 2003). ALS-inhibitor herbicides,<br />

including sulfonylurea, are widely used in the world<br />

196 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. Weed shift from transplanting to the direct-seeding method.<br />

Irrigated transplanting Extensive direct Intensive direct<br />

seeding seeding<br />

Grasses<br />

Isachne globosa Echinochloa crus-galli complex E. crus-galli<br />

Leersia hexandra Leptochloa chinensis L. chinensis<br />

Ischaemum rugosum<br />

I. rugosum<br />

Oryza sativa (weedy rice)<br />

O. sativa (weedy rice)<br />

Broadleaf weeds<br />

Limnocharis flava L. flava L. flava a<br />

Monochoria vaginalis M. vaginalis S. guyanensis b<br />

M. minuta L. hyssopifolia Sphenoclea zeylanica b<br />

Sphenoclea zeylanica M. minuta M. crenata b<br />

Limnophila erecta a<br />

Sedges<br />

Scirpus grossus Cyperus iria C. iria<br />

Fimbristylis miliacea<br />

F. miliacea b<br />

C. difformis<br />

a<br />

Biotypes with herbicide resistance against 2,4-D and ALS-inhibitor herbicides. b Species/biotypes with herbicide<br />

resistance against 2,4-D.<br />

because of their low dosage, mammalian toxicity, and herbicide<br />

injury in many crops.<br />

Weedy rice<br />

The term “weedy rice” refers to populations of annual Oryza<br />

species that diminish farmer income both quantitatively through<br />

yield reduction and qualitatively through lowered commodity<br />

value at harvest (Mortimer et al 2000). Weedy rice populations<br />

are easy-shattering weedy types of rice, and are unwanted<br />

plants among cultivated rice. These weedy rice populations<br />

are found in Malaysia, Vietnam, and Thailand. In Malaysia, a<br />

close relationship between weedy rice and cultivated varieties<br />

has been shown, giving a strong indication that evolutionary<br />

forces are still present in the rice ecosystems (Abdullah et al<br />

1997). According to Mortimer et al (2000), three factors that<br />

determine the population of weedy rice are (1) seed remaining<br />

dormant in the soil over crop seasons, (2) dissemination through<br />

crop seed contamination, and (3) seeds returning from plants<br />

in the previous crop. No single control measure will effectively<br />

control weedy rice. An integrated approach involving<br />

cultural, physical, and chemical interventions is expected to<br />

be effective in managing the weedy rice problem in a sustainable<br />

manner. Unless the problem is addressed, weedy rice in<br />

many areas poses a major threat to sustainable DS rice production.<br />

Water seeding<br />

Besides tillage practices, good water management is an important<br />

prerequisite for controlling weedy rice and other weed<br />

species. Further, water seeding (WS) can be practiced in leveled<br />

fields with levees w<strong>here</strong> the water depth at seeding time<br />

is 5–10 cm, sufficient to suppress weedy rice (Chin et al 2000).<br />

Water seeding as opposed to wet seeding is effective in weedy<br />

rice suppression and can reduce populations by 70–76%. In<br />

Vietnam, WS can be practiced 10–20 days earlier than wet<br />

seeding, allowing farmers to save water. Further, energy inputs<br />

can be reduced by nearly half because of the lack of drainage<br />

at the beginning of the cropping period and reduced irrigation<br />

requirements from tillering to ripening. Weed control<br />

input for WS is also reduced by one-half to a third that of wet<br />

and dry seeding, and a 69% reduction in the weedy rice population<br />

was recorded after WS practices in Selangor, Malaysia<br />

(Azmi 2004, unpublished data). WS practices for two consecutive<br />

seasons reduced weedy rice infestation to below 10%.<br />

Conclusions<br />

Effective weed management practices are an important prerequisite<br />

in DS rice culture with herbicide application seemingly<br />

indispensable. With the advent of herbicide-resistant weed<br />

biotypes and unwarranted environmental contamination following<br />

the continuous and indiscriminate use of herbicides in<br />

Malaysia, Vietnam, and Thailand, a more sustainable integrated<br />

weed management (IWM) technology needs to be developed.<br />

This might be through the thorough understanding of the biology,<br />

ecology, and socioeconomics of the major weeds in the<br />

rice ecosystems. IWM, the promotion of biological and cultural<br />

control options, and minimizing the use of herbicides are<br />

seen as keys to sustainable rice-farming systems in the region.<br />

Session 6: Trends in crop establishment and management in Asia 197


References<br />

Abdullah MZ, Vaughan DA, Watanabe H, Okuno K. 1997. The origin<br />

of weedy rice in Muda and Tg. Karang areas in Peninsular<br />

Malaysia. MARDI Res. J. 24(2):169-174.<br />

Azmi M, Abdullah MZ. 1998. A manual for the identification and<br />

control of padi angin (weedy rice) in Malaysia. Serdang (Malaysia):<br />

MARDI Publication. 18 p.<br />

Azmi M, Baki BB, Mashhor M. 1993. Weed communities in principal<br />

rice-growing areas in Peninsular Malaysia. MARDI Report<br />

No. 165. 15 p.<br />

Azmi M, Baki BB. 2003. Weed species diversity and management<br />

practices in the Sekinchan Farm Block, Selangor’s South West<br />

Project – a highly productive rice area in Malaysia. Proceedings<br />

1, 19th Asian-Pacific Weed Science Society Conference,<br />

17-21 March 2003, Philippines. p 174-184.<br />

Azmi M, Sivapragasam A, Abdullah MZ, Muhamad H. 2003. Weedy<br />

rice management through integration of cultural, physical and<br />

chemical interventions in direct-seeded rice. Paper presented<br />

at the <strong>International</strong> <strong>Rice</strong> Conference 2003, 13-16 Oct. 2003,<br />

Alor Setar, Kedah, Malaysia.<br />

Chin DV, Hien TV, Hien TV. 2000. Weedy rice in Vietnam. In: Baki<br />

BB, Chin DV, Mortimer M, editors. Wild and weedy rice in<br />

rice ecosystems in Asia: a review. Limited Proceedings No. 2.<br />

Los Baños (Philippines): <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>.<br />

p 45-50.<br />

Mortimer M, Pandey S, Piggin C. 2000. Weedy rice: approaches to<br />

ecological appraisal and implications for research priorities.<br />

In: Baki BB, Chin DV, Mortimer M, editors. Wild and weedy<br />

rice in rice ecosystems in Asia: a review. Limited Proceedings<br />

No. 2. Los Baños (Philippines): <strong>International</strong> <strong>Rice</strong> <strong>Research</strong><br />

<strong>Institute</strong>. p 97-105.<br />

Vongsaroj P. 1997. Weed management in paddyfields. Botany and<br />

Weed Science Division, Department of Agriculture, Bangkok.<br />

Bangkok (Thailand): Amarin Printing Company. 175 p.<br />

Watanabe H, Azmi M, Md Zuki I.1997. Emergence of major weeds<br />

and their population change in wet-seeded rice fields in the<br />

Muda area, Peninsular Malaysia. Proceedings of 16th Asian<br />

Pacific Weed Science Society. p 246-250.<br />

Notes<br />

Authors’ addresses: M. Azmi, MARDI <strong>Rice</strong> <strong>Research</strong> Centre, Locked<br />

Bag 203, 13200 Kepala Batas, Penang, Malaysia,<br />

azmiman@mardi.my; D.V. Chin, Cuu Long Delta <strong>Rice</strong> <strong>Research</strong><br />

<strong>Institute</strong>, Omon, Can Tho, Vietnam; P. Vongsaroj, Department<br />

of Agriculture, Bangkok, Thailand; D.E. Johnson,<br />

<strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>, DAPO Box 7777, Metro<br />

Manila, Philippines.<br />

Changing from transplanted rice to direct seeding<br />

in the rice-wheat cropping system in India<br />

Y. Singh, Govindra Singh, David Johnson, and Martin Mortimer<br />

<strong>Rice</strong> and wheat are the staple food crops of India, contributing<br />

nearly 80% of the total food-grain production, and the ricewheat<br />

rotation is the principal cropping pattern of the Indo-<br />

Gangetic Plains, w<strong>here</strong> the system occupies some 13.5 million<br />

ha. Demand for food grains in India is expected to grow and<br />

the requirement for 2025 is estimated to be a 40% production<br />

increase compared with 2003-04. T<strong>here</strong> has, however, been<br />

stagnation in rice productivity in recent years, and long-term<br />

experiments show a declining rice yield trend (Padre and Ladha<br />

2004). Further, increasing costs are leading to demand for<br />

change in rice production methods to improve returns to farmers.<br />

Direct seeding in place of transplanting is one alternative<br />

being considered.<br />

In the Indo-Gangetic Plains, rice is traditionally transplanted<br />

at the end of the dry season (May/June) and, after the<br />

rice harvest, wheat is sown (November/December). Direct<br />

seeding has already replaced transplanting in many parts of<br />

Southeast Asia. The combined effects of changing water availability<br />

and the opportunity cost of labor are driving reevaluation<br />

of crop establishment methods. Pandey and Velasco (2002)<br />

argued that low wage rates and adequate water supply favor<br />

transplanting but direct seeding is likely to increase in circumstances<br />

of labor scarcity and increasing wage rates. These latter<br />

conditions are now common in parts of India and farmers<br />

are considering the alternatives offered by direct seeding.<br />

Balasubramanian and Hill (2002) commented that direct<br />

seeding offers the advantages of reduced labor requirements<br />

and drudgery, earlier crop maturity, more efficient water<br />

use and higher tolerance of water deficit, fewer methane<br />

emissions as the system is more aerobic, and often higher profit<br />

in areas with an assured water supply. Weeds, however, are the<br />

main constraint for farmers practicing direct seeding since the<br />

in<strong>here</strong>nt weed control from standing water at crop establishment<br />

is lost. Differing levels of farmers’ resources, land development<br />

and infrastructure, or weather patterns may dictate different<br />

direct-seeding practices in the Indo-Gangetic Plains.<br />

Options available to farmers include wet seeding with sprouted<br />

seeds (broadcast or drum seeding) on puddled fields, dry drilling<br />

of seed with or without prior cultivation, or broadcasting<br />

dry seed after dry-cultivating the field. This paper summarizes<br />

results from an ongoing study of the options for direct-seeded<br />

rice in the Indo-Gangetic Plains.<br />

198 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. Effects of rice establishment method and weed control on grain yield (t ha –1 ) and<br />

standard errors (SE) of rice in 2001 and 2002 in on-station and on-farm experiments. See<br />

text for details.<br />

2001 weed management 2002 weed management<br />

Establishment<br />

method On-station On-farm On-station On-farm<br />

CW HW TO CW TO CW HW TO CW TO<br />

TP 7.8 7.2 5.9 4.9 3.4 6.1 5.5 4.6 5.8 3.6<br />

WS 8.1 5.6 1.0 – – 6.8 5.4 0.9 5.9 2.2<br />

DS 6.1 1.0 0.0 4.9 2.6 6.7 5.1 1.0 6.3 3.6<br />

ZT 6.6 1.5 0.0 – – 5.7 5.4 0.2 – –<br />

SE 0.04 0.24 0.23 0.21<br />

Materials and methods<br />

Treatments compared rice establishment methods as main-plot<br />

treatments with subplots of weed management treatments in<br />

rice, as follows:<br />

Main plots (60 m 2 )—rice establishment:<br />

TP = conventional transplanting of approximately 21-<br />

day-old plants after soil puddling, 20 × 20-cm spacing<br />

(seedling nursery established at the same time<br />

as direct seeding).<br />

WS = wet seeding (pregerminated, drum-seeded, 35 kg<br />

ha –1 ) after soil puddling, 20-cm row spacing.<br />

DS = dry seeding (50 kg ha –1 ) after conventional tillage,<br />

20-cm row spacing.<br />

ZT = dry seeding (50 kg ha –1 ), zero-tillage after flush<br />

irrigation (7 d before glyphosate application).<br />

Subplots (20 m 2 )—intensity of weeding, postemergence weed<br />

control in rice:<br />

TO = unweeded checks.<br />

CW = weed-free “best-bet herbicide treatment” followed<br />

by two manual weedings. In TP plots, butachlor<br />

(1.5 kg a.i. ha –1 ) was applied 2 DAT; on the WS<br />

plots, anilofos (0.4 kg a.i. ha –1 ) was used 5 days<br />

after seeding (DAS); and, for the DS and ZT,<br />

pendimethalin (1.0 kg a.i. ha –1 ) was applied 1 DAS.<br />

HW = one manual weeding 30 DAS.<br />

From each subplot, weed counts and biomass (fresh<br />

weight) by species were taken from two 0.25 m × 1 m quadrats<br />

covering 5 crop rows. After the rice harvest, the experimental<br />

area was sown to wheat after either conventional tillage or<br />

zero-tillage (as strips). The overall experimental design was a<br />

strip, split-plot design, with four complete randomized replications<br />

as follows: wheat (cv. PBW-343 or PBW-154, 100 kg<br />

ha –1 , 20-cm row spacing) was sown in December into either<br />

conventionally prepared plots (harrowed, rotavated, and leveled)<br />

or zero-tilled plots (paraquat, 0.5 kg a.i. ha –1 ), 1 week<br />

before seeding. Yield estimates were taken from 5 m 2 . Full<br />

experimental details are given in Singh et al (2003). In farmers’<br />

fields, CW and TO treatments were imposed as described<br />

above for TP, WS, and DS establishment methods.<br />

Results<br />

In 2001, grain yield from transplanted rice was similar to that<br />

of wet-seeded rice when weeds were controlled (CW), w<strong>here</strong>as<br />

yield from dry-seeded rice (DS, ZT) was about 20% less (Table<br />

1). A single hand weeding (HW) was insufficient to prevent<br />

major yield loss from weeds in either the DS or ZT rice and<br />

yield loss was complete without weed control (TO). In 2002,<br />

when weeds were controlled (CW), yields under WS and DS<br />

were similar or higher than under TP and ZT. Yield losses because<br />

of weed competition, however, were less severe than in<br />

2001 and, with a single weeding (HW), yield in dry-seeded<br />

areas decreased by an average of 16% versus 80% in 2001. In<br />

farmers’ trials in 2001, equivalent rice yields were achieved<br />

from DS and TP rice, with potential yield losses from weeds<br />

(TO) being 30% in TP and almost 50% in DS. In 2002, DS<br />

rice gave the highest grain yield, while potential losses from<br />

weeds were the lowest in TP (37%), followed by DS (44%)<br />

and WS (62%).<br />

Weed species shifts in response to crop establishment<br />

are well known. At the start of the experiment in 2000, in the<br />

absence of weeding, Echinochloa colona, Caesulia axillaries,<br />

and other broadleaf weeds (other dicots) and Fimbristylis<br />

miliacea were the most abundant weeds at 56 DAS in both the<br />

transplanted and dry-seeded plots (Fig. 1). After three seasons<br />

under transplanting, however, E. colona, Commelina diffusa,<br />

and Ischaemum rugosum were dominant, w<strong>here</strong>as, in dryseeded<br />

rice, C. diffusa dominated. Furthermore, by 2002,<br />

Leptochloa chinensis, an annual grass previously unrecorded<br />

at the site, was noted, and Cyperus rotundus, a perennial sedge,<br />

had also become proportionally more abundant in dry-seeded<br />

areas over the three years up to 2002. The population dynamics<br />

of individual weeds responded noticeably to establishment<br />

method. E. colona, C. rotundus, C. diffusa, and I. rugosum all<br />

declined in abundance (density at 28 DAT/56 DAS) under trans-<br />

Session 6: Trends in crop establishment and management in Asia 199


Biomass (g m –2 ) at 28 DAT<br />

10<br />

2000<br />

Transplanted rice<br />

Density (m –2 ) at 28 DAT<br />

Echinochloa colona<br />

Cyperus rotundus<br />

1.0<br />

0.1<br />

10<br />

Other<br />

(dicot)<br />

2002<br />

C. axillaris<br />

E. colona<br />

F. miliacea<br />

I. rugosum<br />

C. diffusa<br />

C. rotundus<br />

100<br />

10<br />

E. colona<br />

0.01<br />

1.0<br />

C. diffusa<br />

I. rugosum<br />

C. axillaris<br />

100<br />

Ischaemum rugosum<br />

Commelina diffusa<br />

0.1<br />

C. rotundus<br />

0.01<br />

F. miliacea<br />

10<br />

Biomass (g m –2 ) at 56 DAS<br />

10<br />

2000<br />

Dry drill-seeded rice<br />

Density (m –2 ) at 56 DAS<br />

Echinochloa colona<br />

Cyperus rotundus<br />

1.0<br />

C. axillaris<br />

E. colona<br />

Other<br />

(dicot) F. miliacea<br />

I. rugosum<br />

C. diffusa<br />

100<br />

0.1<br />

10<br />

2002<br />

C. rotundus<br />

10<br />

C. diffusa<br />

E. colona<br />

0.01<br />

1.0<br />

C. rotundus<br />

L. chinensis<br />

C. difformis F. miliacea<br />

I. rugosum<br />

100<br />

Ischaemum rugosum<br />

Commelina diffusa<br />

0.1<br />

C. axillaris<br />

10<br />

0.01<br />

2000 2002 2004<br />

2001 2003<br />

Year<br />

2000 2002 2004<br />

2001 2003<br />

Year<br />

Fig. 1. Changes in abundance of weed species in relation to crop establishment method. Diagrams on the left are rank abundance curves<br />

based on biomass at 28 DAT or 56 DAS comparing plots in 2000 and 2002. Diagrams on the right illustrate change in density (mean ±<br />

standard error of mean) of selected species (at 28 DAT or 56 DAS) over five seasons. Log 10 scales.<br />

Caesulia axillaris- = C. axilliaris Echinochloa colona = E. colona Fimbristylis miliacea = F. miliacea<br />

Commelina diffusa = C. diffusa Cyperus rotundus = C. rotundus Ischaemum rugosum = I. rugosum<br />

Cyperus difformis = C. difformis Leptochloa chinensis = L. chinensis<br />

200 <strong>Rice</strong> is life: scientific perspectives for the 21st century


planting. Conversely, E. colona and C. diffusa increased in<br />

density over 2000-04 under direct seeding, while seasonal<br />

variation was evident in C. rotundus and I. rugosum.<br />

Analyses of the costs and returns of rice production by<br />

the different establishment systems, based on farm yields, indicate<br />

that gross returns were broadly similar for each of the<br />

crop management systems. The costs of nursery beds, land<br />

preparation, and labor for transplanting, however, resulted in<br />

a benefit-cost ratio for TP approximately half that of DS rice.<br />

Relative to TP, DS required approximately 40% of the total<br />

water by volume and substantially less labor.<br />

Discussion<br />

Direct seeding offers farmers in the Indo-Gangetic Plains more<br />

independence from the hired migrant labor required for transplanting<br />

and enables the rice crop to be established earlier in<br />

the monsoon season. In turn, early rice establishment, combined<br />

with the shorter duration of direct-seeded rice, facilitates<br />

earlier sowing of the following wheat crop and improves<br />

wheat yield. Coupled with water savings in rice, the introduction<br />

of direct seeding offers considerable system-wide benefits.<br />

However, successful direct seeding of rice is contingent<br />

upon effective weed management early in the life of the crop.<br />

This study has shown that the use of a herbicide (pendimethalin<br />

for drill-seeded rice and anilofos for wet-seeded rice) followed<br />

by one hand weeding will protect yield from weed competition.<br />

Although in some seasons supplementary hand weeding<br />

may be unnecessary, removal of “escapes” through failed application<br />

or tolerance is essential for competitive grasses<br />

such as I. rugosum. It may also be necessary to alter crop management<br />

practices to prevent an undesirable shift in weed species,<br />

particularly to Cyperus rotundus. This may be achieved<br />

by rotation of crop establishment methods or the incorporation<br />

of other cultural measures or stale seedbed treatments.<br />

Current trends of increasing labor costs in many regions<br />

of the Indo-Gangetic Plains, and the increasing concerns over<br />

water availability in the long term, suggest that direct seeding<br />

will become an increasingly attractive option for farmers. Further<br />

research is required, however, to determine the<br />

sustainability of weed management practices and the extent to<br />

which the crop establishment methods are suited to farmers’<br />

circumstances that vary in terms of resources, soil, and infrastructure.<br />

Delivery of knowledge on the integration of crop<br />

establishment and weed management practices to farmers remains<br />

a pressing need.<br />

References<br />

Balasubramanian V, Hill JE. 2002. Direct seeding of rice in Asia:<br />

emerging issues and strategic research needs for the 21st century.<br />

In: Pandey S et al. Direct seeding: research strategies<br />

and opportunities. Proceedings of the <strong>International</strong> Workshop<br />

on Direct Seeding in Asian <strong>Rice</strong> Systems, 25-28 January 2000,<br />

Bangkok, Thailand. Los Baños (Philippines): <strong>International</strong><br />

<strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>. p 15-39.<br />

Padre AT, Ladha JK. 2004. Integrating yield trends of rice-wheat<br />

systems using the linear mixed effects model and meta-analysis.<br />

In: <strong>Rice</strong>-wheat information sheet. <strong>Rice</strong>-Wheat Consortium,<br />

New Delhi, India. p 1-3.<br />

Pandey S, Velasco L. 2002. Economics of direct seeding in Asia:<br />

patterns of adoption and research priorities. In: Pandey S et<br />

al, editors. Direct seeding: research strategies and opportunities.<br />

Proceedings of the <strong>International</strong> Workshop on Direct<br />

Seeding in Asian <strong>Rice</strong> Systems, 25-28 January 2000, Bangkok,<br />

Thailand. Los Baños (Philippines): <strong>International</strong> <strong>Rice</strong> <strong>Research</strong><br />

<strong>Institute</strong>. p 3-14.<br />

Singh G, Singh Y, Singh VP, Singh RK, Singh P, Johnson DE,<br />

Mortimer M, Orr A. 2003. Direct seeding as an alternative to<br />

transplanted rice for the rice-wheat system of the Indo-<br />

Gangetic plains: sustainability issues related to weed management.<br />

In: Proceedings of an <strong>International</strong> Congress held<br />

at the SECC, Glasgow, Scotland, UK, 12-14 Nov. 2003. p 7<br />

F-9-1035.<br />

Notes<br />

Authors’ addresses: Y. Singh and Govindra Singh, G.B. Pant University<br />

of Agriculture & Technology, Pantnagar 263145, India;<br />

David E. Johnson, <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>,<br />

DAPO Box 7777, Metro Manila, Philippines; Martin<br />

Mortimer, School of Biological Sciences, University of<br />

Liverpool, Liverpool, UK, e-mail:<br />

pratibhasingh_84@rediffmail.com.<br />

Acknowledgments: This work was partially funded by the UK Department<br />

for <strong>International</strong> Development (Crop Protection<br />

Programme Project R8233). However, the views expressed<br />

are not necessarily those of DFID.<br />

Session 6: Trends in crop establishment and management in Asia 201


Seedling recruitment in direct-seeded rice:<br />

weed biology and water management<br />

A.M. Mortimer, O. Namuco, and D.E. Johnson<br />

In rice cropping, water constitutes a powerful selective agent<br />

for weed management (Mortimer and Hill 1999). Permanently<br />

flooded fields of transplanted rice that are unweeded by 45<br />

days after transplanting (DAT) exhibit a weed flora different<br />

from fields w<strong>here</strong> the soil remains saturated. Noticeable differences<br />

are also evident across toposequences w<strong>here</strong> land<br />

formation imposes different drainage and flooding regimes in<br />

rainfed rice (Pane et al 2000). However, it is the timing, duration,<br />

and depth of flooding events in association with the<br />

method of crop establishment that govern the precise nature<br />

of weed suppression by water. Wet seeding onto a saturated<br />

puddled soil with subsequent flooding 10–15 days afterward<br />

in comparison with transplanting into standing water alters the<br />

dominance hierarchy of weeds with the replacement of obligate<br />

aquatic dicotyledonous species by semiaquatic species,<br />

including competitive grasses. Weed species shifts may be relatively<br />

rapid. From observations of farmers’ fields, Azmi and<br />

Mashor (1995) recorded that seven seasons of wet seeding<br />

resulted in the appearance of 21 new weed species, particularly<br />

Echinochloa species and forms of “weedy” rice, and the<br />

exclusion of 12 others.<br />

Understanding the processes underlying the selective<br />

nature of water in governing the recruitment and survival of<br />

weed species involves comparative autecological studies of<br />

seed germination and seedling and plant growth in relation to<br />

flooding regimes. These regimes may vary from permanently<br />

aerobic but moist soils, through continuously saturated anaerobic<br />

soils, to saturated soils subject to varying water depths<br />

arising from periodic flooding and drainage, either as a result<br />

of rainfall variation or as a policy of water management. Potentially,<br />

plants may experience all of these flooding regimes<br />

at different stages in their life cycle and the diversity in rice<br />

weed floras is in part because, in many semiaquatic species,<br />

the rooting systems of adult plants are tolerant of, or adapted<br />

to, submergence in flooded soils. However, controlled studies<br />

of weed community dynamics in transplanted and wet-seeded<br />

rice emphasize the fact that weeds are recruited early in the<br />

life of both crops. In transplanted rice continuously flooded at<br />

shallow (< 50 mm) or deeper (approx. 100 mm) depth, recruitment<br />

of plants to the weed community occurred only in<br />

the first 10–20 DAT and subsequently losses continued until<br />

the rice harvest. In wet-seeded rice initially sown on saturated<br />

soil and subsequently flooded to these depths by 10–15 days<br />

after seeding (DAS), recruitment of sedges and dicotyledonous<br />

species was restricted to the same early period in contrast<br />

to graminaceous species that increased in overall density up to<br />

60 DAS (Hill et al 2001). Cohort recruitment of weeds in dry-<br />

seeded rice may, however, extend over a longer period than in<br />

wet-seeded rice, depending on the time of initiation and depth<br />

of flooding.<br />

Intrinsically, seed size confers an advantage in seedling<br />

establishment (autotrophic net gain in biomass after germination).<br />

From a phyto-centric seedling point of view, the emergence<br />

of photosynthetic tissue above a water surface is a critical<br />

life-history event in that t<strong>here</strong> is a relatively abrupt increase<br />

in available photosynthetically active radiation (PAR) and absence<br />

of hypoxic conditions. Successful water seeding of rice<br />

relies upon rapid mobilization of these reserves that is partly<br />

dependent upon dissolved oxygen in floodwater and, similarly,<br />

successful direct seeding of rice requires the absence of flooding<br />

immediately after sowing. Understanding seed and seedling<br />

biology at this stage in the life cycle is critical in understanding<br />

the role of water management in governing weed seedling<br />

recruitment. We briefly review the available knowledge.<br />

Weed biology: toward a definition of functional weed types<br />

Germination<br />

Seed size in rice weeds varies on a logarithmic range from<br />

approximately 10 µg (Sphenoclea zeylanica, Cyperus<br />

difformis) to greater than 10 4 µg (Rottboellia cocchinensis) and<br />

seed size in weed species is well known to be associated with<br />

suites of dormancy/germination traits. In small-seeded species,<br />

the absence of oxygen (Monochoria vaginalis) or lowered<br />

oxygen concentration (Zinzania aquatica), fluctuating diurnal<br />

temperatures (Najas graminea), and differential responses to<br />

spectral light ratios (Sphenoclea zeylanica) have all been shown<br />

to be cues involved in response mechanisms that govern seed<br />

germination rates underwater. Phytochrome-mediated switches<br />

in response to red/far-red light ratios provide another probable<br />

mechanism governing germination although t<strong>here</strong> has been<br />

little detailed work on the features of photocontrol of germination<br />

of many small-seeded rice weeds (Sanders 1994). Gap<br />

detection mechanisms are moreover likely to confer fitness<br />

advantages in a rice-weed community that will experience<br />

largely uniform canopy closure, often within 30–40 days.<br />

Equally evident is the fact that small-seeded species (e.g.,<br />

Cyperus difformis) exhibit polymorphisms in germination response<br />

to flooding, providing “bet-hedging” tactics against<br />

unpredictable flooding events. Conversely, some species exhibit<br />

little or no innate or induced dormancy and germinate<br />

rapidly on the surface of saturated soils (Fimbristylis miliacea,<br />

Echinochloa colona, Kim and Moody 1989) but not underwater.<br />

It is useful, t<strong>here</strong>fore, to attempt to qualitatively group weed<br />

202 <strong>Rice</strong> is life: scientific perspectives for the 21st century


species by cues for germination response although such a classification<br />

may be blurred by ecotypic differentiation. The classification<br />

of species on character states such as obligate requirements<br />

for germination, physiological (Cyperus difformis)<br />

or somatic dormancy polymorphisms (Ischaemum rugosum),<br />

and gap detection mechanisms is a first step in identifying<br />

groups of species that respond differentially to flooding and<br />

that may not reflect taxonomic fidelity.<br />

Transition to autotrophy<br />

Very early plant growth patterns are characterized by the rate<br />

of transition from heterotrophy to autotrophy. Once committed<br />

by germination to growth, seedling ability to photosynthesize<br />

underwater at lowered light intensities and to mobilize<br />

resources to develop photosynthetic structures out of water<br />

are key traits influencing survivorship. Understanding the role<br />

of water depth in prohibiting weed recruitment is then concerned<br />

with the growth dynamics of seedlings underwater and<br />

response to depth-dependent light regimes. Recent research at<br />

<strong>IRRI</strong> has measured the growth responses of a range of weed<br />

species underwater in fully illuminated conditions and total<br />

darkness. Echinochloa crus-galli and Cyperus difformis illustrate<br />

dramatic differences in resource mobilization and partitioning<br />

(Fig. 1). In the larger-seeded grass, carbohydrate mobilization<br />

and partitioning to root and shoot resulted in the<br />

onset of autotrophy before leaf emergence from an illuminated<br />

water column. Under total darkness, in contrast, the maximum<br />

shoot height achieved before exhaustion of reserves was 80<br />

mm, with evidence of enhanced height extension rate. In C.<br />

difformis, net assimilation of biomass occurred below a 45-<br />

mm water column in full illumination, but biomass was not<br />

partitioned into photosynthetic tissue that emerged above the<br />

water surface, by 300 thermal units (TU). Root length (a partial<br />

surrogate of root biomass) extension was noticeable immediately<br />

after germination under both light regimes, suggesting<br />

that carbohydrate assimilate was partitioned to roots in the<br />

first instance. Maximum shoot height was achieved in the dark<br />

regime over 300 TU. Emergence of leaf tissue from illuminated<br />

water columns was not achieved until 700 TU (data not<br />

shown) but plants returned to lighted conditions from after 300<br />

TU in darkness did not grow. These two species differ sharply<br />

in their response to flooding regimes, with C. difformis maintaining<br />

a longer aquatic stage before emergence from the water<br />

column because of underwater photosynthesis. In contrast,<br />

in E. crus-galli, seedling growth depended on emergence from<br />

the water column before reserve use was complete.<br />

Water management for direct-seeded rice<br />

The preceding discussion allows for the ready identification<br />

of two functional types in response to water at the time of direct<br />

seeding: those species in which early establishment success<br />

is critically dependent upon height extension in relation<br />

to water depth and those in which it is not. It is a likely supposition<br />

that some species in the latter category may also possess<br />

ecological correlates in terms of gap detection mechanisms at<br />

germination. While the extent to which these types simply represent<br />

ends of a continuum and the possible role of<br />

heterophyllic tissue are unclear, quantification of growth responses<br />

as illustrated above enables two questions to be answered:<br />

(1) What is the minimum depth required to prohibit<br />

establishment in clear and dark turbid water, thus capturing<br />

the range of field conditions (2) How long must seedlings be<br />

submerged for seed reserves to be exhausted While answers<br />

are species-specific and require thermal time measurement,<br />

they are pertinent in defining the suppressive effect of water<br />

and providing a causal explanation of variation in weed recruitment<br />

patterns.<br />

Comparative studies on Leptochloa chinensis illustrated<br />

a growth strategy similar to that of E. crus-galli with respect<br />

to seed reserve partitioning to shoot and leaf structures, although<br />

both the specific growth rate and height extension rate<br />

of aboveground biomass were twofold lower. Germination in<br />

this species is strongly suppressed by standing water (>15 mm)<br />

and establishment was found to be prohibited by water depths<br />

of >50 mm. Experimental dose-response studies with<br />

pretilachlor for early postemergence control of both E. crusgalli<br />

and L. chinensis have shown that significantly reduced<br />

doses of the herbicide can be employed if coupled with precise<br />

flooding regimes that take into account plant size and<br />

height extension rate after application.<br />

Jackson and Ram (2003) have recently emphasized the<br />

opportunities for selecting for tolerance of complete submergence<br />

in established plants based on the SUB1 locus. Moreover,<br />

Caton (2002) has illustrated the importance of quantifying<br />

seed reserve mobilization in direct seeding. The extent to<br />

which genes that ensure rapid establishment and submergence<br />

tolerance can be exploited for germplasm adapted for direct<br />

seeding remains a pressing research issue (Yamauchi and<br />

Biswas 1997). However, it is worth remarking that the extent<br />

to which submergence tolerance can be of use in weed management<br />

may be constrained by the evolutionary responses<br />

within the Echinochloa genus, which reflects a wide spectrum<br />

of flood tolerance (Kennedy et al 1989).<br />

References<br />

Azmi M, Mashor M. 1995. Weed succession from transplanting to<br />

direct seeding methods in Kembubu rice area. Malaysian J.<br />

Biosci. 6:143-153.<br />

Caton BP. 2002. Simulating seed reserve mobilization and seedling<br />

growth of rice in DSRICE1. Field Crops Res. 76:55-69.<br />

Hill JE, Mortimer AM, Namuco OS, Janiya JD. 2001. Water and<br />

weed management in direct-seeded rice: are we headed in the<br />

right direction In: Peng S, Hardy B, editors. <strong>Rice</strong> research<br />

for food security and poverty alleviation. Los Baños (Philippines):<br />

<strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>. p 491-510.<br />

Jackson MB, Ram PC. 2003. Physiological and molecular basis of<br />

susceptibility and tolerance of rice plants to complete submergence.<br />

Ann. Bot. 91:227-241.<br />

Session 6: Trends in crop establishment and management in Asia 203


Biomass (mg)<br />

9<br />

Echinochloa crus-galli<br />

0.04<br />

Primary root length (mm)<br />

Cyperus difformis<br />

15<br />

Root and shoot<br />

biomass (illuminated)<br />

0.03<br />

Root length<br />

(illuminated)<br />

12<br />

6<br />

Total biomass<br />

(illuminated)<br />

9<br />

3<br />

Structural seed<br />

biomass<br />

Root and shoot<br />

biomass (dark)<br />

0.02<br />

0.01<br />

Total biomass<br />

(dark)<br />

Root length (dark)<br />

6<br />

3<br />

0<br />

0.00<br />

0<br />

Shoot height (mm)<br />

200<br />

15<br />

150<br />

12<br />

Under full illumination<br />

9<br />

100<br />

In dark<br />

In dark<br />

6<br />

Under full illumination<br />

50<br />

3<br />

0<br />

0 100 200 300<br />

Thermal units (°C days)<br />

0<br />

0 100 200 300<br />

Thermal units (°C days)<br />

Fig. 1. Seedling growth responses in Echinochloa crus-galli and Cyperus difformis in response to flooding. Germinated<br />

seeds were placed in water columns containing nutrients to a depth of 50 mm and either illuminated (light/dark) on a 12-<br />

h cycle or maintained in total darkness at a temperature of 30/20 °C day/night. PAR = 450 µE m –2 s –1 . Repeated destructive<br />

harvests were taken over the time course, enabling fit of the functions shown.<br />

Kennedy RA, Fox TC, Dybiec LD, Rumpho ME. 1989. Biochemical<br />

adaptations to anoxia in rice and Echinochloa seeds. In:<br />

Taylorson RB, editor. Recent advances in the development<br />

and germination of seeds. New York (USA): Plenum Press.<br />

p 151-163.<br />

Kim SC, Moody K. 1989. Germination of two rice cultivars and<br />

several weed species. Korean J. Weed Sci. 9:116-122.<br />

Mortimer AM, Hill JE. 1999. Weed species shifts in response to<br />

broad-spectrum herbicides in sub-tropical and tropical crops.<br />

Brighton Crop Protection Conference (1999) 2:425-437.<br />

Pane H, Noor ES, Dizon M, Mortimer AM. 2000. Weed communities<br />

of gogorancah rice and reflections on management. In:<br />

Tuong TP, Kam SP, Bouman B, Pandey S, Wade L, Hardy B,<br />

editors. Characterizing and understanding rainfed rice environments.<br />

Manila (Philippines): <strong>International</strong> <strong>Rice</strong> <strong>Research</strong><br />

<strong>Institute</strong>. p 269-287.<br />

Sanders BA. 1994. The need for understanding the life cycle of the<br />

rice weed Cyperus difformis. Aust. J. Exp. Agric. 34:1031-<br />

1038.<br />

204 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Yamauchi M, Biswas JK. 1997. <strong>Rice</strong> cultivar difference in seedling<br />

establishment in flooded soil. Plant Soil 189:145-153.<br />

Notes<br />

Authors’ addresses: A.M. Mortimer, School of Biological Sciences,<br />

University of Liverpool, Liverpool L69 7ZB, UK; O. Namuco<br />

and D.E. Johnson, <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>,<br />

DAPO Box 7777, Metro Manila, Philippines, e-mail: A.M.<br />

Mortimer@liverpool.ac.uk.<br />

Acknowledgments: This work was partially funded by the UK Department<br />

for <strong>International</strong> Development (Crop Protection<br />

Programme Project R8233). However, the views expressed<br />

are not necessarily those of DFID.<br />

The crop protection industry’s view on trends<br />

in rice crop establishment in Asia and their impact<br />

on weed management techniques<br />

Jean-Louis Allard, Kee Fui Kon, Yasuo Morishima, and Ruediger Kotzian<br />

Farmers in South and Southeast Asia will have to increase rice<br />

production significantly to meet the needs of a growing population.<br />

Competition between industry and agriculture for water,<br />

labor, and land will oblige rice farmers to intensify production<br />

while using less labor and water. The risk of herbicide<br />

overuse coming from those changes was highlighted in the<br />

1990s (Naylor 1994). Weed management practices must t<strong>here</strong>fore<br />

be integrated and adapted to new cropping systems and<br />

associated weed problems (Labrada 2004).<br />

In northeast Asia, the change in diet, opening of commodity<br />

markets, aging farmers, and reduction in the cultivated<br />

area also compel rice farmers to increase productivity while<br />

maintaining higher product quality. These changes will have a<br />

significant impact on crop establishment and water management<br />

practices. They will also affect weed populations and<br />

herbicide use.<br />

Until recently, the crop protection industry was focusing<br />

on the discovery of new active ingredients. High development<br />

costs and a stagnating and fragmented rice crop protection<br />

market are leading to a reduced investment in discovery<br />

and development of new rice herbicides. With less chemical<br />

innovation, the crop protection industry in the future will have<br />

to adapt use recommendations for current active ingredients<br />

in order to solve new weed problems and ensure reliable performance<br />

under changing cropping practices and conditions.<br />

In the future, recommendations for herbicide use will increasingly<br />

take into account integrated weed management techniques<br />

(Kudsk and Streibig 2003).<br />

This paper describes changes in weed problems and their<br />

management in three major Asian rice-cropping systems. Sustainable<br />

weed management solutions based on development<br />

activities from Syngenta in Asia are used to illustrate how the<br />

crop protection industry responds to changes.<br />

Trends and impact on weed management techniques<br />

Direct seeded wet-sown rice<br />

Direct seeded wet-sown rice is widely practiced in Southeast<br />

Asia, the southern provinces of China, and South Korea. The<br />

technique has been widely known since the 1980s and, after a<br />

rapid initial development, further expansion has slowed down<br />

because of the high constraints of this cropping system. Chemical<br />

weed control is essential to avoid yield losses but high crop<br />

sensitivity at the early stages restricts the number of active<br />

ingredients that can be used. Accurate leveling and good water<br />

management are also required to ensure adequate weed<br />

control. High infestations of grasses such as Echinochloa crusgalli<br />

(L.) Beauv. and Leptochloa chinensis (L.) become dominant<br />

after a few cropping seasons. Weedy rice (Oryza sativa<br />

L. fp. spontanea) is expanding in areas w<strong>here</strong> wet-sown rice is<br />

grown continuously, such as Vietnam, Malaysia, Sri Lanka,<br />

Thailand, and Korea (Baki et al 2000). Resistance of grass<br />

weeds such as Echinochloa or Leptochloa spp. to propanil,<br />

quinclorac, and ACC-ase inhibitors is starting to appear in several<br />

countries. Resistance of annual broadleafs and sedges to<br />

ALS-inhibitors has been frequently detected in Korea (Park<br />

2004) and is starting to appear in China.<br />

During recent years, the crop protection industry has introduced<br />

more flexible and powerful postemergence herbicides<br />

from the ACC-ase and ALS-inhibitor groups for grass or broadspectrum<br />

weed control. Increasing reliance on such chemical<br />

classes will intensify the risk of developing weed resistance<br />

(Valverde et al 2000). Syngenta is adopting an alternative approach.<br />

The 25-year-old herbicide/safener combination<br />

pretilachlor/fenclorim is being rejuvenated by using an earlier<br />

application timing 3–7 days before seeding. The earlier application<br />

eliminated the major constraint for farmers, which is<br />

that it must be sprayed on mud within a few days after seeding<br />

(Fig. 1). Direct application by dripping the concentrate or<br />

Session 6: Trends in crop establishment and management in Asia 205


Fig. 1. Conventional herbicide application in direct-seeded wet-sown rice in Thailand.<br />

Fig. 2. Application of pretilachlor/fenclorim during leveling.<br />

slightly diluted product into water at the last leveling is easy<br />

(Fig. 2). Crop tolerance is excellent. Performance is stable and<br />

less affected by weather conditions or water management than<br />

conventionally applied products. The method provides reliable<br />

broad-spectrum weed control, including Leptochloa sp.<br />

and weedy rice. It also offers farmers a herbicide with a different<br />

mode of action as a resistance management tool. This example<br />

shows how exploring novel use recommendations for<br />

an old product can provide a solution to new weed problems.<br />

Transplanted rice in South and Southeast Asia<br />

In areas with increasing labor costs, farmers will implement<br />

techniques that reduce production costs and increase yield and<br />

cropping intensity. Techniques such as the use of younger seedlings<br />

and reduction in hand weeding and herbicides such as<br />

2,4-D or sulfonylureas will lead to an increase in Echinochloa<br />

spp. infestations. In areas with reduced water availability such<br />

as “tail areas” of irrigated perimeters or during El Niño years,<br />

or in areas with high cropping intensity, farmers will need techniques<br />

to reduce water use and time for soil preparation.<br />

The role of industry will be to register herbicides for<br />

controlling grasses and train farmers in the safe and effective<br />

use of such products. New formulations for easier application<br />

with a shaker bottle may be favored over products applied<br />

through only foliar application. Syngenta is also promoting<br />

preplanting applications with nonselective herbicides such as<br />

paraquat, allowing quick planting without tillage in several<br />

Chinese provinces (Fig. 3) or reduced tillage in Indonesia and<br />

eastern India. The technique helps farmers to speed up soil<br />

preparation and planting by up to 1 month and reduce water<br />

206 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Fig. 3. Farmers planting rice without tillage in southern China.<br />

consumption by up to 15% (Kartaatmadja et al 2004). Application<br />

of paraquat followed by no-tillage is currently the only<br />

technique allowing sustainable rice cultivation in Indonesian<br />

tidal rice. The development of reduced- or no-tillage together<br />

with an adapted rice cropping system remains a possibility in<br />

the fast-growing no-till wheat area in northwest India.<br />

Transplanted rice in northeast Asia<br />

In northeast Asia, stringent pesticide laws will be enforced to<br />

ensure the safety of users, consumers, and the environment.<br />

Aging “weekend or part-time” farmers and also professional<br />

farmers managing a large number of fields will require broadspectrum<br />

herbicides to control annual and perennial weeds<br />

(“one-shot herbicides”), which can be easily applied through<br />

dripping at planting or later from dikes or into water inlets.<br />

Sulfonylurea herbicide-resistant (SU-R) annual broadleafs or<br />

sedges such as Monochoria vaginalis (Burm. f.) Presl var.<br />

plantaginea (Roxb.) Solms-Laub. and Scirpus juncoides Roxb.<br />

subsp. juncoides Roxb. are already widely distributed and will<br />

continue to expand (Itoh and Uchino 2002). The control of<br />

these weeds will require resistance prevention measures or the<br />

addition of an antiresistance component into herbicide combinations.<br />

Maintenance and reinforcement of registration dossiers<br />

for new and old herbicidal active ingredients will continue to<br />

be a key priority for the crop protection industry. However,<br />

because of limited financial investment in a stagnating market,<br />

cost and benefit will need to be balanced, which could<br />

lead to the divestment or phasing-out of older or economically<br />

nonviable active ingredients.<br />

Responding to farmers’ demands, the industry will increasingly<br />

focus new developments on so-called “easy-to-apply”<br />

herbicides such as “Jumbos” or SC formulations. Herbicides<br />

that can be applied during other operations such as leveling<br />

or transplanting will also gain in importance.<br />

The crop protection industry is also working intensively<br />

on new solutions to SU-R problems. Specialized active ingredients<br />

such as carfentrazone, bromobutide, benzobicyclon, or<br />

others are being added into the already complex “one-shot”<br />

mixtures, adding to production costs and restricting formulation<br />

options. It is pertinent to compare the cost of a resistance<br />

prevention strategy with the cost of the cure. Calculations based<br />

on Italian rice production systems have, for example, shown<br />

that rotation of different herbicide mode of actions can prevent<br />

or delay the appearance of resistance at a much lower<br />

cost than using curative treatments when the resistant weed<br />

population has developed (Orson 1999). In northeast Asia, it<br />

has been recognized that repeated use of “one-shot” products<br />

in rice, relying only on sulfonylureas to control annual<br />

broadleafs and sedges, is one of the main causes of the development<br />

of ALS-resistance (Itoh 2001). In line with the Herbicide<br />

Resistance Action Committee (HRAC 2004) guidelines<br />

for the prevention of resistance, Syngenta recommends an application<br />

of pretilachlor applied preplanting or preemergence<br />

in sequence with a pyriftalid-based “one-shot” to delay the<br />

development of SU-R weeds in farmers’ fields in both Korea<br />

and Japan (Table 1).<br />

Recommendations and conclusions<br />

In the coming years, scarcer land, labor, and water in conjunction<br />

with the need for intensification will drive significant<br />

changes in cultivation techniques and weed management in<br />

Asian rice production.<br />

The number of farmers switching from transplanting to<br />

direct seeding is expected to be minor and limited to large<br />

Session 6: Trends in crop establishment and management in Asia 207


Table 1. Effect on SU-R SCPJO (Scirpus juncoides Roxb. subsp. juncoides Roxb.) with sequential use of pretilachlor<br />

followed by a pyriftalid/pretilachlor-based mixture. Results of a field trial in Miyagi Prefecture, Japan, in 2003.<br />

Chemicals (formulation) Dosage Timing a % Control on SCPJO<br />

(g a.i. ha –1 ) (evaluated at 40 DAT)<br />

Bensulfuron-methyl (WP) 51 3 DAT 46<br />

Pretilachlor (EW) 400 3 DAT 90<br />

Pyriftalid/pretilachlor/azimsulfuron/bensulfuron-methyl (GR) 180/180/6/30 3 DAT 85<br />

Pretilachlor (EW) → 400 → 3 DAT→<br />

pyriftalid/pretilachlor/azimsulfuron/bensulfuron-methyl (GR) 180/180/6/30 24 DAT b 100<br />

a<br />

Chemicals were applied at 3 DAT (3 days after transplanting of rice) at preemergence of SCPJO. b The sequential application followed at 24<br />

DAT.<br />

farms w<strong>here</strong> this technique increases productivity significantly.<br />

In most cases, farmers will improve productivity by adapting<br />

their current cultivation system. Reduced- or no-tillage is one<br />

of those opportunities to reduce water consumption and increase<br />

cropping intensity. Herbicides will replace hand-weeding<br />

to reduce costs. Younger seedlings will also be used more<br />

frequently to reduce the workload and cost of nursery maintenance.<br />

Those changes will lead to a higher use of herbicides,<br />

particularly in tropical Asia.<br />

The “thrown seedling” method, currently widely practiced<br />

in China, may be a further alternative to transplanting for<br />

smaller farms. Larger farms will aim at improving productivity<br />

through mechanization. Dry soil cultivation with large tractors<br />

will be the first option, but reduced- or no-tillage may<br />

also become popular. Intensive dry-seeded rice as it is widely<br />

practiced in the United States, Brazil, and now Italy could appear<br />

in limited areas in Asia. However, this system relies on<br />

good availability of irrigation water and a high input of preand<br />

postemergence herbicides (2–4 applications at a cost of<br />

US$100–250 ha –1 ). The high chemical input can be managed<br />

in an environmentally acceptable way. Favorable areas could<br />

be large farms in northwest India, Malaysia, and Thailand.<br />

In areas with an already high use of herbicides such as<br />

direct-seeded wet-sown or mechanically transplanted rice,<br />

farmers will require herbicides, which are easier to apply and<br />

solve new weed problems such as weedy rice or SU-R weeds.<br />

The role of the crop protection industry will be to introduce<br />

new solutions responding to new farmers’ needs through novel<br />

use recommendations, formulations, and antiresistance strategies<br />

based mostly on current active ingredients. To ensure safety<br />

to farmers and the environment, strong regulatory standards<br />

will be required and will have to be implemented. Training<br />

and stewardship programs will also be needed to ensure the<br />

safe and sustainable use of herbicides. As a global leader in<br />

weed control, Syngenta remains committed to delivering innovative<br />

solutions to Asia’s rice farmers.<br />

References<br />

Baki BB, Chin DV, Mortimer M, editors. 2000. Wild and weedy<br />

rice in rice ecosystems in Asia: a review. Limited Proceedings<br />

No. 2. Los Baños (Philippines): <strong>International</strong> <strong>Rice</strong> <strong>Research</strong><br />

<strong>Institute</strong>.<br />

HRAC (Herbicide Resistance Action Committee). 2004. Guidelines<br />

to the management of herbicide resistance.<br />

www.plantprotection.org/HRAC/Guideline.html.<br />

Itoh K. 2001. An overview of resistance in Japan and Asia. Japan-<br />

Australia Seminar, Utsunomiya University. p 3-4.<br />

Itoh K, Uchino A. 2002. Sulfonylurea-resistant weeds in paddy rice<br />

fields of Japan. In: Agrochemical resistance, extent, mechanism,<br />

and detection. Washington, D.C. (USA): The American<br />

Chemical Society. p 168-180.<br />

Kudsk P, Streibig JC. 2003. Herbicides: a two-edged sword. Weed<br />

Res. 43(2):90-102.<br />

Kartaatmadja S, Pane H, Wirajaswadi L, Sembiring H, Simatupang<br />

S, Bachrein S, Ismadi D, Fagi AM. 2004. Optimizing the use<br />

of natural resources and increasing rice productivity. Proceedings<br />

of the 4th ISCO Conference, Brisbane, Australia. Paper<br />

758.<br />

Park TJ. 2004. Herbicide resistance in rice in Korea.<br />

www.weedscience.org/in.asp.<br />

Labrada R. 2004. The need for improved weed management in rice.<br />

www.fao.org/DOCREP/006/Y4751E/y4751e01.html.<br />

Orson JH. 1999. The cost of herbicide resistance.<br />

www.plantprotection.org/HRAC/cost.html.<br />

Naylor K. 1994. Economic growth threatens to bring herbicide overuse<br />

to Asia. www.stanford.edu/dept/news/pr/94/<br />

940405Arc4350.html.<br />

Valverde BE, Riches CR, Caseley JC. 2000. Prevention and management<br />

of herbicide resistant weeds in rice. Electronic Book,<br />

p 123. www.weedscience.org/in.asp.<br />

Notes<br />

Authors’ addresses: Jean-Louis Allard and Kee Fui Kon, Syngenta<br />

Asia Pacific Pet. Ltd., 250 Northbridge Road #39-00, Raffles<br />

City Tower, Singapore 179101; Yasuo Morishima, Syngenta<br />

Japan K.K. 21F, Office Tower X, 1-8-10, Harumi, Chuo-Ku,<br />

Tokyo 104-6021, Japan; Ruediger Kotzian, Syngenta Crop<br />

Protection AG, Scwarzwaldallee 256, CH 4002, Basel, Switzerland,<br />

e-mail: jean-louis.allard@syngenta.com.<br />

208 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Improved anchorage and bird protection with iron-coated<br />

seeds in wet direct seeding of rice crops<br />

Minoru Yamauchi<br />

The shift in rice establishment method from transplanting to<br />

direct seeding has recently become prominent in Asia. Direct<br />

seeding constitutes either dry or wet seeding. Puddling the field<br />

is characteristic of rice crop production and is generally considered<br />

to increase soil nutrient supply, suppress weed infestation,<br />

and increase water holding, thus contributing to<br />

sustainability. Puddling is conducted for transplanting and wet<br />

seeding, but not for dry seeding. T<strong>here</strong>fore, poor water holding<br />

and heavy weed infestation are major problems in dryseeded<br />

rice fields.<br />

A variable rice plant stand is the major constraint to wet<br />

seeding. Puddling creates an anaerobic soil environment, thus<br />

making seed germination and growth unstable, particularly<br />

when seeds are sown beneath the soil surface. In the tropics,<br />

farmers broadcast pregerminated seeds onto the puddled soil<br />

after drainage. It was recently shown that rice cultivars tolerant<br />

of anaerobic soil could be sown underground (Yamauchi<br />

et al 2000). In Japan, farmers are recommended to seed “oxygen-supplier”<br />

chemical (major ingredient CaO 2 )-coated<br />

pregerminated seeds at a soil depth of 10–20 mm after drainage.<br />

When the seeding depth is too deep, however, emergence<br />

and plant stand are poor. In contrast, seeding on the surface or<br />

in shallow soil may lead to floating seedlings when water is<br />

subsequently introduced. Drainage at seeding tends to stimulate<br />

weed growth.<br />

Water seeding is a form of wet seeding in which<br />

pregerminated seeds are sown in standing water. In the tropics,<br />

it is practiced when drainage is difficult. In Japan, it was<br />

practiced in a limited area before the materialization of “oxygen-supplier”<br />

coating technology. Although water seeding is<br />

advantageous in water-saving and weed control, the occurrence<br />

of floating or lodging of seedlings limits adoption.<br />

This paper describes the new technology developed to<br />

overcome the floating and lodging problems of rice seedlings<br />

in standing water.<br />

Hypothesis<br />

Seedlings in water are buoyant and tend to be poorly anchored,<br />

leading to floating or lodged seedlings. We can improve anchorage<br />

by increasing the specific gravity of seeds by adhering<br />

heavy material on the husk. Among the materials commonly<br />

used in agriculture, iron has a high specific gravity of 7.9. We<br />

confirmed by use of pregerminated seeds that the occurrence<br />

of floating seedlings was reduced by iron coating (Yamauchi<br />

2002a).<br />

Seed vigor is important to achieve a rapid and uniform<br />

plant stand in fields (Yamauchi and Tun Winn 1996). The ger-<br />

mination process could be subdivided into imbibition, activation,<br />

and postgermination stages. We found that drying seeds<br />

at the activation stage could increase seed vigor by increasing<br />

the germination rate (Yamauchi 2002b). Dry seeds with high<br />

vigor produced in this manner were found to have the potential<br />

to attain the same level of plant stand as pregerminated<br />

seeds.<br />

We hypothesized that coating “high-vigor dry seeds” with<br />

iron could make wet seeding more adaptable and labor-saving<br />

(Yamauchi 2003). Because dry seeds are storable, iron-coated<br />

dry seeds can be prepared in advance of the busy farm season.<br />

Preparation of iron-coated seeds<br />

The procedure described <strong>here</strong> is designed for and being tested<br />

by rice farmers in Japan. Seeds with more than a 95% germination<br />

percentage are surface-sterilized by soaking in sterilant<br />

solution for 24 h, followed by ordinary soaking in tap water<br />

for 24–48 h at 15–20 °C. The soaking time depends on the<br />

temperature and cultivar. Soaking is stopped just before coleoptile<br />

emergence on the husk, then the seeds are dried. The<br />

seeds thus prepared are vigorous.<br />

Seeds are coated with a mixture of iron powder and calcined<br />

gypsum (CaSO 4 0.5 H 2 O, 5–25% of iron powder weight)<br />

(Yamauchi 2004). The iron is in a reduced form. The amount<br />

of iron used for coating is determined by the ratio of iron to<br />

seed weight. When the coating ratio is as high as 1, it is recommended<br />

that an electric motor-driven granulator be used because<br />

the weight of the mixture is too heavy to handle manually.<br />

When the ratio is 0.1, granulation could be achieved in a<br />

container by mixing seeds and the mixture by hand. Portions<br />

of the mixture are poured successively onto the seeds while<br />

water is sprayed occasionally to help the granulation. When<br />

the granulation is over, calcined gypsum alone is dressed so<br />

that the surface of coated seeds becomes smooth and not chalky.<br />

Because wetting the mixture of iron powder and gypsum<br />

initiates rapid oxidation of iron, the temperature of coated<br />

wet seeds increases. T<strong>here</strong>fore, the seeds must be spread in a<br />

shallow layer and dried. Otherwise, t<strong>here</strong> is a risk that seeds<br />

will be injured and die because of the heat.<br />

The well-dried coated seeds can be stored at room temperature<br />

for several months without a significant decrease in<br />

germination percentage. The specific gravity and single-seed<br />

weight of seeds thus produced are increased with the increase<br />

in iron-coating ratio (Figs. 1 and 2).<br />

Session 6: Trends in crop establishment and management in Asia 209


Single-seed weight (mg)<br />

150<br />

100<br />

50<br />

0<br />

Specific gravity<br />

4<br />

3<br />

Fig. 2. Intact (top) and iron-coated (bottom) rice seeds.<br />

2<br />

1<br />

0<br />

0 1 2 3 4<br />

Iron-coating ratio<br />

Fig. 1. The relationship between iron-coating<br />

ratio and specific gravity and singleseed<br />

weight. Iron-coating ratio = iron powder<br />

weight/seed weight.<br />

Characteristics of direct seeding with iron-coated dry seeds<br />

Performance in wet and water seeding<br />

We tested the seedling establishment and grain yield of rice<br />

from iron-coated seeds with coating ratios of 0.5, 1, and 2 in<br />

comparison with “oxygen-supplier” chemical-coated seeds in<br />

wet and water seeding. “Oxygen-supplier” chemical-coated<br />

seeds floated in water seeding, achieving a plant stand of 62%,<br />

w<strong>here</strong>as iron-coated seeds did not float, achieving a plant stand<br />

of 82–94%. In wet seeding, the “oxygen-supplier” chemicalcoated<br />

seeds were damaged by sparrows, w<strong>here</strong>as the ironcoated<br />

seeds were affected only slightly, exhibiting 64% and<br />

81–94% plant stand, respectively. Thus, the plant stand of ironcoated<br />

seeds is more consistent than that of “oxygen-supplier”<br />

chemical-coated seeds under the experimental conditions used<br />

<strong>here</strong>. T<strong>here</strong> were little differences in grain yield (5,280–5,660<br />

kg ha –1 ) among the treatments. Our recent study showed that<br />

the coating ratio could be reduced as low as 0.1, although this<br />

depends on soil properties, crop management, and seeding<br />

practices.<br />

Seeding at the right interval after puddling is important<br />

to the success of direct seeding and poor timing may end in a<br />

poor plant stand. We tested the relationship between the time<br />

of seeding after puddling and plant stand in water seeding.<br />

The iron-coated seeds anchored well and established seedlings<br />

successfully even when the time of seeding was 5–6 d after<br />

puddling. However, noncoated dry seeds failed to achieve anchorage<br />

and floated, even when seeded on the same day of<br />

puddling.<br />

In wet seeding, the soil surface tends to become hard<br />

after drainage. When the seeds are broadcast-seeded onto such<br />

hard soil, the contact between seed and soil is poor and seeds<br />

may become desiccated and die. Iron-coated seeds are advantageous<br />

because the seeds are heavy and become buried more<br />

easily in soil. Thus, iron-coated dry seeds seem to allow greater<br />

flexibility in terms of seeding time in water and wet seeding.<br />

Bird damage<br />

Seeds and seedlings are vulnerable to bird attack in the field.<br />

When the field is drained as in wet seeding, they were often<br />

destroyed by sparrows (Passer montanus). When the field is<br />

flooded for water seeding, the seeds are eaten by ducks (Anas<br />

poecilorhyncha). T<strong>here</strong>fore, it is difficult to avoid bird damage,<br />

particularly when sparrows and ducks are in the vicinity.<br />

It was noted, however, that iron-coated seeds are more resistant<br />

to sparrow attack at seeding. Sparrows cannot break the<br />

husk of iron-coated seeds and thus cannot eat the caryopsis.<br />

Ducks are still able to eat the iron-coated seeds in flooded<br />

fields, however, and, t<strong>here</strong>fore, when ducks are expected to<br />

attack, it is recommended to drain the field.<br />

Environmental effects<br />

The use of iron-coated seeds for direct seeding should be discussed<br />

and evaluated in terms of sustainability. While most<br />

water used for puddling has to be drained in ordinary wet seeding,<br />

it is not necessary with iron-coated seeds because these<br />

seeds can be sown and establish plants successfully in the presence<br />

of water. The introduction of iron-coated seed technology<br />

may save water used for puddling. In addition, the flexibility<br />

of water control with iron-coated seeds would make<br />

herbicide application easier than in ordinary wet seeding.<br />

Water seeding is advantageous in the control of weeds,<br />

including weedy rice. Despite this advantage, water seeding<br />

210 <strong>Rice</strong> is life: scientific perspectives for the 21st century


has not yet been fully employed in direct seeding because of<br />

the unstable plant stand. Water seeding with iron-coated seeds<br />

provides an opportunity for ecologically sound weed control<br />

practices.<br />

Continuous application of iron to paddy fields may<br />

amend the soil and reduce the occurrence of physiological rice<br />

plant diseases, such as Akagare disease. In Japan, it is recommended<br />

to apply 340 kg Fe ha –1 annually to maintain the fertility<br />

of paddy soil. Seeding iron-coated seeds results in the<br />

application of 5–50 kg Fe ha –1 with each crop when the seed<br />

rate is 50 kg ha –1 . We confirmed that application of iron does<br />

not increase the ferrous iron concentration or cause any physiological<br />

problem. Thus, the introduction of iron-coated seed<br />

technology would be beneficial in maintaining soil fertility.<br />

Cost and labor requirement<br />

A new technology should be low-cost and labor-saving from<br />

the perspective of farmers. Granulation could be done manually<br />

if the coating ratio were low. Iron powder costs approximately<br />

US$1–3 kg –1 in Japan. Assuming a seed rate of 50 kg<br />

ha –1 and a coating ratio of 0.1, the cost for iron powder would<br />

be $5–15 ha –1 .<br />

In ordinary wet seeding, farmers have to follow a strict<br />

time schedule for seed preparation, land preparation, and seeding,<br />

watching the weather conditions for successful seeding.<br />

Because iron-coated seeds can be prepared in advance, avoiding<br />

the busy farming season, this method contributes to laborsaving.<br />

In Japan, many farmers are currently purchasing seedlings<br />

prepared for transplanting machines. We can imagine that<br />

once iron-coated seeds are produced commercially and sold<br />

on the market, part-time and weekend farmers could use such<br />

seeds so that they can save on labor for seed preparation.<br />

Conclusions and future research needs<br />

Because the technology of iron-coated seeds is new in Japan,<br />

we need to continue the evaluation. Furthermore, the feasibility<br />

of this technology in tropical Asia should be discussed.<br />

This technology could be advantageous for developing a sustainable<br />

technology oriented for water-saving, reducing the use<br />

of chemicals, and promoting ecological weed control.<br />

References<br />

Yamauchi M. 2002a. Reducing floating rice seedlings in wet direct<br />

sowing by increasing specific gravity of seeds with iron powder<br />

coating. Jpn. J. Crop Sci. 71(extra issue 1):150-151. (In<br />

Japanese.)<br />

Yamauchi M. 2002b. Production of rice seeds with increased vigor<br />

and their application to wet direct sowing. Jpn. J. Crop Sci.<br />

71(extra issue 1):152-153. (In Japanese.)<br />

Yamauchi M. 2003. Developing rice direct sowing technology with<br />

iron-coated dry seeds. Jpn. J. Crop Sci. 72(extra issue 1):4-5.<br />

(In Japanese.)<br />

Yamauchi M. 2004. <strong>Rice</strong> direct sowing with iron-coated dry seeds:<br />

coating and sowing methods. Jpn. J. Crop Sci. 73(extra issue<br />

1):10-11. (In Japanese.)<br />

Yamauchi M, Aragones DV, Casayuran PR, Sta. Cruz PC, Asis CA,<br />

Cruz RT. 2000. Seedling establishment and grain yield of tropical<br />

rice sown in puddled soil. Agron. J. 92:275-282.<br />

Yamauchi M, Tun Winn. 1996. <strong>Rice</strong> seed vigor and seedling establishment<br />

in anaerobic soil. Crop Sci. 36:680-686.<br />

Notes<br />

Author’s address: National Agricultural <strong>Research</strong> Center for Western<br />

Regions, NARO, Nishifukatsu 6-12-1, Fukuyama 721-<br />

8514, Japan, e-mail: myamauch@affric.go.jp.<br />

Issues for integrated weed management<br />

and decision support in direct-seeded rice<br />

D.E. Johnson and A.M. Mortimer<br />

<strong>Rice</strong> production has been transformed over much of Asia, with<br />

total harvest increasing by 2.4% per annum from 1968 to 1999<br />

(<strong>IRRI</strong> 2004) through the introduction of improved germplasm,<br />

agronomy, pest management, and, in many cases, mechanization.<br />

At the same time, the declining availability of labor for<br />

agriculture and increasing labor costs have required farmers<br />

to seek alternatives to manual weeding, which has long provided<br />

farmers with the means to limit losses to weeds. Herbicide<br />

use in rice grew dramatically in Asia from 1980 to 1995,<br />

with more than a threefold increase in sales, to more than $900<br />

million per annum (Naylor 1996), allowing a massive release<br />

of labor from agriculture that is expected to continue. The use<br />

of herbicides has been accompanied globally by the evolution<br />

of herbicide resistance in weeds, weed species population shifts,<br />

and concerns about environmental contamination and human<br />

health.<br />

In addition to labor, t<strong>here</strong> are increasing concerns over<br />

supplies of irrigation water. Farmers in many rice-growing areas<br />

are likely to have only limited availability of irrigation<br />

water and, in the future, most of the 22 million ha of dry-season<br />

rice in South and Southeast Asia will fall into an “economic<br />

water scarcity zone” (Bouman and Tuong 2003). Water<br />

scarcity threatens the sustainability of irrigated rice ecosystems<br />

since it may no longer be feasible for farmers to undertake<br />

wet cultivation and flood in fields to ensure good crop<br />

establishment and control weeds. The development and adoption<br />

of alternative irrigation strategies such as “alternate wetting<br />

and drying” and “aerobic rice” may enable good crop<br />

Session 6: Trends in crop establishment and management in Asia 211


growth but the lack of sustained flooding will greatly increase<br />

potential losses from weeds. These systems may integrate direct<br />

seeding and herbicide use, yet, to be sustainable, effective<br />

weed management strategies are required.<br />

In many areas of Asia, transplanting of rice is being replaced<br />

by direct seeding as farmers respond to increased costs<br />

or decreased availability of labor or water (Pandey and Velasco,<br />

this volume). Direct-seeded systems tend not to be as robust<br />

as transplanting as elements of soil moisture, irrigation, drainage,<br />

and weed control are more critical to successful crop establishment<br />

and growth. With management playing a more<br />

decisive role, as a practice, direct seeding could be described<br />

as “knowledge-intensive.”<br />

Technical constraints and economic demands are leading<br />

to change in production systems and are causing farmers<br />

to be increasingly dependent on information from outside<br />

sources. We discuss below some issues related to direct seeding,<br />

its adoption, and weedy rice and herbicide resistance, for<br />

which farmers could benefit from having a greater availability<br />

of current knowledge.<br />

Weed management issues related to direct seeding<br />

As described above, weed management is one of the major<br />

constraints to direct seeding. Studies in the rice-wheat system<br />

in India, in Malaysia, and in Bangladesh (this volume) have<br />

established a substantial knowledge base on weed management<br />

in some of the most productive rice systems in Asia. These<br />

systems have commonality in many of the weed species present<br />

but also reflect a continuum from transplanting to direct seeding.<br />

Four pertinent observations from this database can be<br />

made.<br />

First, t<strong>here</strong> is considerable variability in soil type, irrigation,<br />

and drainage, and at the farm level because of resources<br />

and cropping practices that affect the selection of direct-seeding<br />

options.<br />

Associated with direct seeding is an inevitable shift in<br />

the weed flora toward competitive grasses, including<br />

Echinochloa species, Leptochloa chinensis, and Ischaemum<br />

rugosum in wet-seeded rice and in dry-seeded rice the perennial<br />

sedge Cyperus rotundus. Management of such weeds requires<br />

farmers to have the ability to anticipate changes in weed<br />

populations and, to reduce losses, exploit integrated strategies<br />

comprising tillage, water, and crop management to complement<br />

herbicide application.<br />

Third, “weedy” rice (Oryza sativa) has become a relatively<br />

recent problem in Southeast Asia although “red” rice<br />

has been known in Latin America for decades. In the late 1980s,<br />

it was observed in direct-seeded rice of Malaysia and by the<br />

mid-1990s several of the major rice production schemes had<br />

infested areas (Azmi et al, this volume). In the Philippines,<br />

weedy rice was reported in 1990, in Vietnam in 1994, and it is<br />

now widespread in the central region of Thailand. Its vigorous<br />

growth results in serious yield losses, and its rapid spread makes<br />

it a considerable threat to direct-seeded rice production. Control<br />

strategies combining preventive and cultural measures,<br />

however, have been shown to be effective. Prevention is one<br />

of the immediate steps that should be implemented in many<br />

countries. This may involve sensitizing farmers to risks, closer<br />

inspection of seeds, and roguing at the initial appearance of<br />

weedy rice in fields.<br />

Finally, intensive herbicide use in rice has resulted in<br />

certain weed species, including Sphenoclea zeylanica and<br />

Fimbristylis miliacea, developing resistance to 2,4-D herbicide<br />

(Watanabe et al 1997). Lately, possible ALS (acetolactatesynthase)<br />

inhibitor-resistant biotypes of Bacopa rotundifolia<br />

and Limnophila erecta have been reported (Azmi and Baki<br />

2003). The risks of herbicide resistance evolving are known<br />

and strategies exist to mitigate the risks of occurrence. What is<br />

required is a greater awareness within farm communities of<br />

the resistance problem and suitable management strategies.<br />

Information needs for improved weed management systems<br />

As argued elsew<strong>here</strong> in this volume by various authors, the<br />

transition from traditional transplanting to direct seeding is<br />

knowledge-intensive and renders ineffective the experience of<br />

traditional rice production systems with their reliance on indigenous<br />

knowledge and manual inputs (often w<strong>here</strong> opportunity<br />

costs of labor are discounted). Information must be acquired<br />

from external agencies and uncertainty is often involved<br />

over the reliability of information and the implementation of<br />

actions. Decision rules or heuristics (see Heong and Escalada<br />

1997 for discussion) may address this difficulty but, to be successful,<br />

must focus appropriately and in context.<br />

Table 1 categorizes the issues that must be addressed in<br />

a decision support framework for weed management in directseeded<br />

rice. Since decision support frameworks may apply at<br />

different scales (regional, production system in locality, and<br />

individual farms) and have multiple target audiences<br />

(policymakers, researchers and extension personnel, and farmers),<br />

it is important to delineate the context with respect to<br />

production systems. Characterization of the existing cropping<br />

system(s) through constraint analyses enables identification of<br />

the magnitude and variance of yield gaps caused by the presence<br />

of weeds. In direct-seeded rice, these may be large (typically<br />

10–50% of attainable yield) and are often a consequence<br />

of an inability to implement timely weeding (20–30 DAS),<br />

which in turn may reflect difficulties in water management (irrigation<br />

and drainage), land leveling, and appropriate water<br />

management for selected herbicides. Constraints in credit,<br />

knowledge, and resources at the farm level contribute to poor<br />

agronomic practice. Characterization studies in weed management<br />

typically involve on-farm trials comparing yields from<br />

plots with intensive weed management as opposed to farmers’<br />

practices, coupled with focus-group interviews to describe<br />

farmer decision-making in weed management and to explore<br />

perceptions and the availability or lack of information.<br />

Comparative technology evaluation provides a partial<br />

budgeting analysis of system components and identifies intervention<br />

points for change. Typically, and at its simplest, a matrix<br />

of components versus systems is constructed and subjected to<br />

212 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. Issues to be considered in a decision support framework for direct-seeding options and weed management.<br />

Domains<br />

Policy adviser<br />

Focus<br />

Extension<br />

Farmer<br />

Socioeconomic<br />

Biophysical characteristics of production<br />

systems<br />

Weed managementtechnologies<br />

Implication of changes to establishment<br />

or weed management<br />

practices:<br />

Herbicide use<br />

Displacement of labor<br />

Patterns of land and water<br />

use<br />

Farm productivity<br />

Public/private partnerships<br />

Output: policy brief<br />

<br />

<br />

<br />

<br />

<br />

Yield potential<br />

Yield gaps because of weeds<br />

Stability of rice-based cropping<br />

systems<br />

Diversification of cropping<br />

systems<br />

Crop establishment methods<br />

Output: policy brief<br />

Choice of mechanical/chemical<br />

control<br />

Output: policy brief<br />

Cost-benefit analysis of component<br />

technologies and system<br />

profitability<br />

Output: technology options/knowledge<br />

banks<br />

Integration of weed management<br />

technologies, agronomic<br />

practices, and cultivar<br />

selection<br />

Prevention of herbicide resistance<br />

Preventive methods to prohibit<br />

weed species shifts<br />

Environmental protection<br />

Output: technology options/knowledge<br />

banks<br />

Information on individual component<br />

technologies<br />

Output: technology options/knowledge<br />

banks<br />

Choice of weed management<br />

methods in relation to<br />

labor<br />

knowledge<br />

resource availability<br />

input costs<br />

Output: leaflets, advice/decision<br />

trees<br />

Weed management options in<br />

relation to cropping systems,<br />

site location, water management,<br />

and other agronomic variables<br />

Output: leaflets, advice/decision<br />

trees<br />

Information on<br />

Target weed species<br />

Herbicide use<br />

Timing of application<br />

Output: leaflets, advice/decision<br />

trees<br />

sensitivity analysis by partial budgeting. Pandey and Velasco<br />

(2002) have pointed to the likelihood of tradeoffs. For instance,<br />

the introduction of direct seeding may have a negative impact<br />

on labor demand for the adoption of direct seeding in place of<br />

transplanting or a positive effect w<strong>here</strong> it allows for cropping<br />

intensification, both of which may have policy implications<br />

(Pandey and Velasco 2002). Likewise, improvements in water-use<br />

efficiency may be achievable only by a switch in herbicide<br />

product (e.g., butachlor to pretilachlor), which reduces<br />

the spectrum of control and necessitates more costs in later<br />

manual weeding.<br />

As a third framework component, decision trees provide<br />

farm-level information in the form of structured questions<br />

that enable answers in the form of options to be chosen.<br />

These trees specifically focus on technical issues related to<br />

the adoption of a particular system component and are most<br />

effective when heuristics are employed. The question “Are<br />

weeds that emerge early in the life of a rice crop the only ones<br />

to contribute to yield loss” may initiate a tree that can lead to<br />

the recognition of the risk of intransigent weeds that in practice<br />

require identification skills in scouting rice fields. For a<br />

farmer in the favorable rainfed environment, the question “What<br />

are my options for rice establishment” might initiate a tree<br />

involving several steps and covering the range of direct-seeding<br />

options (see Fig. 1 for an example).<br />

Conclusions<br />

Traditional and modern rice systems alike are complex, the<br />

management often sophisticated, and substantial information<br />

is required to enable farmers to judge objectively what the<br />

best technology options are. This is certainly true in the transition<br />

to direct seeding and the management of intractable weed<br />

problems. Gaining access to such information may present a<br />

major obstacle for potential adopters. The challenge for researchers<br />

is to adequately address the variability of rice-farming<br />

systems for which they are making recommendations and<br />

to synthesize the results in ways that will make the conclusions<br />

available to those who will use them. Only in this way<br />

will farmers obtain benefit from advances in technology and<br />

be able to meet the challenges of a changing production environment.<br />

Session 6: Trends in crop establishment and management in Asia 213


Crop establishment<br />

Can field be drained<br />

Yes<br />

No<br />

Can field be dry-cultivated<br />

Is Cynodon dactylon or Cyperus rotundus absent<br />

Transplant<br />

Yes<br />

No<br />

Dry seeding into a seedbed<br />

Wet seeding, sowing onto<br />

puddled saturated soil<br />

Are soil conditions suitable for line<br />

seeding by machinery<br />

Is t<strong>here</strong> a need for interow cultivation<br />

or substantial hand weeding<br />

Yes No Yes No<br />

Broacast Drill-seed Broacast Drum-seed<br />

Weed management<br />

Are annual grasses absent<br />

Good water management possible<br />

Yes<br />

No<br />

Apply herbicide<br />

+ limited manual weeding<br />

Apply herbicide<br />

+ limited manual weeding or<br />

interflow cultivation<br />

Fig. 1. Illustrative decision tree for adoption of direct seeding with respect to favorable rainfed lowland rice.<br />

References<br />

Azmi M, Baki BB. 2003. Weed species diversity and management<br />

practices in the Sekinchan Farm Block, Selangor’s South West<br />

Project—a highly productive rice area in Malaysia. In: Proceedings<br />

1, 19th Asian-Pacific Weed Science Society Conference,<br />

17-21 March 2003, Philippines. p 174-184.<br />

Bouman BAM, Tuong TP. 2003. Growing rice with less water. Issues<br />

of water management in agriculture: compilation of essays.<br />

Comprehensive Assessment Secretariat, IWMI, Colombo,<br />

Sri Lanka. p 49-54.<br />

Heong KL, Escalada MM. 1997. Perception change in rice pest<br />

management: a case study of farmers’ evaluation of conflict<br />

information. J. Appl. Comm. 81:3-17.<br />

<strong>IRRI</strong> (<strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>). 2004. World rice statistics.<br />

Manila (Philippines): <strong>IRRI</strong>. www.irri.org/science/<br />

ricestat.<br />

Naylor R, editor. 1996. Herbicides in Asian rice: transitions in weed<br />

management. Palo Alto, Calif. (USA): <strong>Institute</strong> for <strong>International</strong><br />

Studies, Stanford University, and Manila (Philippines):<br />

<strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>. 270 p.<br />

Pandey S, Velasco L. 2002. Economics of direct seeding in Asia:<br />

patterns of adoption and research priorities. In: Pandey S,<br />

Mortimer M, Wade L, Tuong TP, Lopez K, Hardy B, editors.<br />

Direct seeding: research issues and opportunities. Proceedings<br />

of the <strong>International</strong> Workshop on Direct Seeding in Asian<br />

<strong>Rice</strong> Systems: Strategic <strong>Research</strong> Issues and Opportunities,<br />

25-28 January 2000, Bangkok, Thailand. Los Baños (Philippines):<br />

<strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>. p 3-14.<br />

Watanabe H, Zuki MI, Ho NK. 1997. Response of 2,4-D resistant<br />

biotypes of Fimbristylis miliacea (L.) Vahl to 2,4-D<br />

dimethylamine and its distribution in Muda plain, Peninsular<br />

Malaysia. J. Weed Sci. Technol. 42(3):240-249.<br />

Notes<br />

Authors’ addresses: D.E. Johnson, <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>,<br />

DAPO Box 7777, Metro Manila, Philippines; A.M.<br />

Mortimer, School of Biological Sciences, University of<br />

Liverpool, Liverpool, UK.<br />

214 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Control of Leptochloa chinensis (L.) Nees<br />

in wet-seeded rice fields in Sri Lanka<br />

Anuruddhka S.K. Abeysekera and U.B. Wickrama<br />

Weeds are the major biotic stress in rice cultivation in Sri Lanka,<br />

causing yield losses of as much as 30–40% (Herath Banda et<br />

al 1999). Leptochloa chinensis (L.) Nees, Red Sprangletop, is<br />

becoming an important and serious threat to rice production in<br />

all rice ecosystems in Sri Lanka. It has the same outbreak level<br />

as Echinochloa crus-galli (L.) Beauv. (Abeysekera 1999).<br />

Chemical weed control is commonly practiced by rice farmers<br />

in Sri Lanka (90%) and propanil 36% EC was the most widely<br />

used grass-killer herbicide in rice fields before the introduction<br />

of bispyribac sodium (Abeysekera 1999, Amarasinghe and<br />

Marambe 1998). In 1998, bispyribac sodium was the leading<br />

herbicide and L. chinensis was selected as a serious weed in<br />

wetland rice fields. After it germinates, it grows profusely in<br />

waterlogged spots in rice fields because of very poor land leveling<br />

in farmers’ fields. At present, many herbicides have difficulty<br />

in controlling this weed. T<strong>here</strong>fore, the objective of<br />

this study was to evaluate the control efficacy of L. chinensis<br />

with postemergence herbicides in wet-seeded rice.<br />

Materials and methods<br />

A field experiment was conducted at the <strong>Rice</strong> <strong>Research</strong> and<br />

Development <strong>Institute</strong>, Sri Lanka, during the 1999 minor and<br />

1999-2000 major season. The soil type was red-yellow podsolic<br />

with pH 6.2 and annual rainfall of the region at 2,250–2,285<br />

mm, with an average temperature of 23–28 ºC. <strong>Rice</strong> (Oryza<br />

sativa) variety Bg 300a (3 months old) was used and broadcast<br />

at 100 kg ha –1 . The experimental design was a randomized<br />

complete block design with 3 replicates; plot size was 6 ×<br />

3 m 2 , each separated by 30-cm bunds. Six common<br />

postemergence herbicides were used: (1) clomozone + propanil<br />

60% EC (Cl + Pro) at 1.2 L ha –1 applied at 7–10 days after<br />

sowing (DAS), (2) cyhalofop-butyl 100% EC (Cy) at 1 L ha –1<br />

applied 7–10 DAS, (3) fentrazmide + propanil 44% WP (Fe +<br />

pro) at 3 kg ha –1 applied at 7–10 DAS, (4) propanil 36% EC<br />

(Pro) at 8.5 L ha –1 applied at 7–10 DAS, (5) quinclorac 250 g<br />

L –1 SC (Qui) at 0.6 kg ha –1 applied at 7–10 DAS, and (6)<br />

bispyribac sodium 10% SC (Bis) at 0.3 kg ha –1 applied at 10–<br />

12 DAS. These were evaluated with and without removing L.<br />

chinensis as the control treatment. MCPA was used to control<br />

broadleaf and sedge weeds at the experimental site and, except<br />

for L. chinensis, the other grasses were removed manually.<br />

All the other cultural practices and pest control followed<br />

Department of Agriculture recommendations. <strong>Rice</strong> germination<br />

count 2 weeks after sowing (WAS), visual phytotoxicity<br />

symptoms 2, 4, 6, and 8 d after herbicide application, the count<br />

of L. chinensis 4 and 6 WAS, dry weight of L. chinensis at 6<br />

WAS, yield, and yield components of rice were recorded at<br />

harvest time. The data were analyzed by ANOVA using the<br />

SAS computer package and the treatment means were compared<br />

by Duncan’s multiple range test.<br />

Results and discussion<br />

Grasses were the dominant weed group found at the experimental<br />

site, w<strong>here</strong> the grass L. chinensis was dominant.<br />

Echinochloa crus-galli, Isachne globosa, Paspalum distichum,<br />

and Ischaemum rugosum were also observed. None of the herbicides<br />

affected the germination and growth of rice seedlings.<br />

Phytotoxicity<br />

Cyhalofop-butyl, propanil, fentrazmide + propanil, quinclorac,<br />

and bispyribac sodium applied to rice plants did not show any<br />

visual phytotoxicity symptoms in rice plants. Clomozone +<br />

propanil–treated rice plants showed a slight whitening effect 2<br />

d after spraying. But these symptoms did not affect the grain<br />

yield of rice and were not visible after 7 d.<br />

Weed control efficacy<br />

The lowest L. chinensis dry weight and count were observed<br />

from the clomozone + propanil treatment and cyhalofop-butyl<br />

treatment, followed by fentrazmide + propanil, quinclorac, and<br />

propanil treatments during both seasons (Fig. 1). The highest<br />

L. chinensis dry weight was observed from the no-weeding<br />

treatment, followed by the bispyribac sodium treatment (Fig.<br />

1). All the herbicides gave excellent control of E. crus-galli<br />

and I. rugosum but were less effective on I. globosa and P.<br />

distichum.<br />

Yield<br />

The grain yield of rice was highly affected by the biomass<br />

production of L. chinensis. It showed significant differences<br />

among herbicide-treated plots and untreated plots. Weed competition<br />

was more severe in the dry season than in the wet<br />

season. In both seasons, the highest yield was obtained from<br />

clomozone + propanil, followed by cyhalofop-butyl,<br />

fentrazmide + propanil, propanil, quinclorac, and bispyribac<br />

sodium treatments, respectively (Fig. 2). Infestation of L.<br />

chinensis reduced rice yield significantly in the respective treatments.<br />

A significant linear relationship was found between the<br />

dry weight of L. chinensis and rice grain yield (Fig. 3A, B).<br />

The highest L. chinensis dry weight gave the lowest rice yield.<br />

Conclusions<br />

Cyhalofop-butyl 100% EC at 1 L ha –1 and clomozone +<br />

propanil 60% EC at 1.2 L ha –1 applied at 7–10 DAS gave excellent<br />

control efficacy (9% and 94%, respectively) of L.<br />

Session 6: Trends in crop establishment and management in Asia 215


Dry weight (g m –2 )<br />

40<br />

35<br />

30<br />

Minor<br />

Major<br />

a<br />

a<br />

a<br />

25<br />

20<br />

b<br />

15<br />

b<br />

bc<br />

10<br />

bc<br />

bc<br />

5<br />

c<br />

c<br />

d d<br />

d<br />

0<br />

Cl + pro Cy Fe + pro Qui Pro Bis Nw Hw<br />

Treatment<br />

Fig. 1. Dry weight of L. chinensis as affected by different herbicides at 6 weeks<br />

after sowing.<br />

Yield (t ha –2 )<br />

6<br />

5<br />

4<br />

3<br />

a<br />

a<br />

a<br />

a<br />

Minor<br />

Major<br />

b<br />

a<br />

b<br />

b<br />

b<br />

b<br />

b<br />

c<br />

a<br />

c<br />

d<br />

2<br />

a<br />

1<br />

0<br />

Cl + pro Cy Fe + pro Qui Pro Bis Nw Hw<br />

Treatment<br />

Fig. 2. Effect of different herbicides on rice grain yield.<br />

chinensis. Fentrazmide + propanil 44% WP at 3 kg ha –1 ,<br />

quinclorac 250 g L –1 SC at 0.6 kg ha –1 , and propanil 36% EC<br />

at 8.5 L ha –1 applied at 7–10 DAS gave moderate control efficacy<br />

(60%, 58%, and 40%, respectively) of L. chinensis. The<br />

lowest control efficacy of L. chinensis was observed with<br />

bispyribac sodium 10% SC at 0.3 kg ha –1 applied at 10–12<br />

DAS. No adverse effect was observed from all the tested herbicides<br />

on rice grain yield.<br />

References<br />

Abeysekera ASK. 1999. Current status of weed control in rice in Sri<br />

Lanka. Proceedings of the 17th Asian Pacific Weed Science<br />

Society Conference, Bangkok, Thailand, 22-27 November.<br />

p 174-179.<br />

Amarasinghe L, Marambe B. 1998. Trends in weed control of rice<br />

cultivation in Sri Lanka. Proceedings of a Multidisciplinary<br />

<strong>International</strong> Conference, University of Peradeniya, Sri Lanka.<br />

p 272-274.<br />

Bambaradeniya CNB, Gunatilaka CVS. 2002. Ecological aspects of<br />

weed flora in an irrigated rice field ecosystem in Sri Lanka.<br />

JNSF, Sri Lanka. 2 p.<br />

Herath Banda RM, Dhanapala MP, Silva GAC, Hossain M. 1998.<br />

Constraints to increase rice production in Sri Lanka. Workshop<br />

on the prioritization of rice research, <strong>International</strong> <strong>Rice</strong><br />

<strong>Research</strong> <strong>Institute</strong>, Los Baños, Philippines.<br />

Notes<br />

Authors’ address: <strong>Rice</strong> <strong>Research</strong> and Development <strong>Institute</strong>,<br />

Batalagoda, Ibbagamuwa, Sri Lanka, e-mail: anuru@sltnet.lk.<br />

216 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Yield (t ha –1 )<br />

6<br />

5<br />

4<br />

3<br />

2<br />

1<br />

Yield (t ha –1 )<br />

4.5<br />

4.0<br />

3.5<br />

3.0<br />

2.5<br />

2.0<br />

y = –0.0514x + 4.7006<br />

R 2 = 0.7528 1.5<br />

1.0<br />

y = –0.0741x + 3.7667<br />

R 2 = 0.9622<br />

0<br />

0 10 20 30 40<br />

Dry weight (g m –2 )<br />

0.5<br />

0.0<br />

0 5 10 15 20 25 30<br />

Dry weight (g m –2 )<br />

Fig. 3. <strong>Rice</strong> yield as affected by dry weight of Leptochloa chinensis. (A) minor season, (B) major season.<br />

Village-level modeling of environment-friendly<br />

and appropriate technologies and practices<br />

for direct seeding<br />

A<br />

Rowena G. Manalili, Bernard D. Tadeo, Emmanuel R. Tiongco, Wilfredo B. Collado, Rodolfo V. Bermudez, Constancio A. Asis, Jovino L. De Dios, Marvin<br />

F. Adap, Mario dela Cruz, Ulysses G. Duque, Leonardo V. Marquez, Cheryll B. Casiwan, Roy F. Tabalno, Placida C. Lanuza, and Belen C. Tejada<br />

B<br />

Direct seeding has increasingly become popular and adopted<br />

by farmers in many rice-growing areas in the Philippines, especially<br />

during the dry season. A recent survey of the Philippine<br />

<strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong> (Phil<strong>Rice</strong>) revealed that more than<br />

75% of the farmers in the major rice-producing areas are adopting<br />

direct seeding. Iloilo has the largest area devoted to directseeded<br />

rice, followed by Occidental Mindoro and Negros Occidental<br />

(Phil<strong>Rice</strong>-BAS 1997). Wet seeding of pregerminated<br />

seed in puddled soil is more common than dry seeding and<br />

more farmers wet-seed during the dry season.<br />

The economic advantages of this mode of crop establishment<br />

include reducing the labor requirement as a result of<br />

the elimination of the seedbed and transplanting operations,<br />

mitigating methane emissions, advancing harvesting by more<br />

than 1 week, and other advantages such as using less water to<br />

mitigate drought and allowing dryland tillage in relation to<br />

farm management techniques and practices.<br />

A gamut of mature technologies exists for the directseeding<br />

rice ecosystem. A strategy identified for more effective<br />

promotion of technologies is to develop a village into a<br />

community of farmers for direct seeding, w<strong>here</strong> indigenous<br />

and modern technologies and practices merge. The village<br />

model serves as a springboard for developed technologies before<br />

these are eventually promoted. It is w<strong>here</strong> technologies<br />

are fine-tuned with the participation of farmers. The community<br />

is envisioned to use ecologically sound, sustainable, and<br />

affordable practices and is closely monitored and supervised<br />

by an interdisciplinary team of research specialists and extension<br />

experts from the Philippine <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>. The<br />

project is piloted in the Agrarian Reform Community of<br />

Maragol, Science City of Muñoz, Nueva Ecija, Philippines.<br />

The objectives of the study were to (1) enhance the capacity<br />

of rice farmers, (2) increase the yield and income of<br />

rice farmer-partners by promoting improved rice production<br />

technologies, (3) link and network farm products to the mainstream<br />

and local market, and (4) assess the socioeconomic<br />

impact of technologies and provide insights for researchers.<br />

Methodology<br />

Site selection was conducted based on the accessibility of the<br />

area: large contiguous irrigated rice areas and farmers practicing<br />

direct seeding.<br />

A baseline survey and participatory rural appraisal were<br />

conducted to generate a location-specific database crucially<br />

important in the determination of rice farm households’ technology<br />

base, needs, and problems. Site mapping was also conducted<br />

using the global positioning system (GPS).<br />

Spatial and temporal pest dynamics in the area were<br />

monitored. Rat population dynamics were monitored using the<br />

trap barrier system + trap crop (TBS + TC) for four rice-cropping<br />

seasons in 2002-04 (Phil<strong>Rice</strong> 2000). The soil test kit<br />

Session 6: Trends in crop establishment and management in Asia 217


Site selection<br />

Support<br />

services<br />

Biophysical and<br />

socioeconomic<br />

characterization<br />

Technology<br />

adaptation,<br />

demonstration,<br />

and promotion<br />

Village-level<br />

adoption of<br />

technologies<br />

Monitoring and<br />

evaluation<br />

Fig. 1. Schematic diagram of the methodology in the direct-seeding rice village model.<br />

(STK), minus one element test (MOET), nutrient omission plot,<br />

and laboratory analysis were used to assess the nutrient status<br />

of various rice fields at the study site (Phil<strong>Rice</strong> 2002).<br />

<strong>Research</strong>ers and farmers identified technologies and<br />

adaptable farmers’ practices for direct-seeded rice. Demonstration<br />

trials on the package of technologies, which include<br />

the use of 40 kg ha –1 of certified seeds, the drum seeder, and<br />

carbonized rice hulls and organic fertilizer, were set up in the<br />

village. The performance of hand-tractor-drawn riding-type<br />

implements such as the harrow and leveler was also tested.<br />

The technologies introduced are being monitored through<br />

the farm record-keeping (FRK) approach. Farm record-keeping<br />

calendars were distributed to farmer-partners every cropping<br />

season for them to record their daily farm activities, expenses,<br />

and revenues. Monitoring, documentation, and copying<br />

of data were done on a weekly basis by technical staff to<br />

check whether farmers were religiously recording their daily<br />

farm activities, and problems encountered by the farmers were<br />

discussed. The gat<strong>here</strong>d data were coded and encoded using<br />

Microsoft Access. These were processed and analyzed using<br />

frequencies, means, averages, and costs and returns analysis.<br />

The profitability and productivity between direct-seeded and<br />

transplanted rice were also compared.<br />

Figure 1 shows the schematic diagram of the methodology<br />

for the direct-seeding rice village model.<br />

Results and discussion<br />

The project focused on about 200 ha of contiguous rice fields<br />

in the Agrarian Reform Community of Maragol. It is one of<br />

the 37 barangays in the Science City of Muñoz, Nueva Ecija.<br />

It has a population of 2,294 or around 480 households. It has a<br />

total land area of 520 ha, of which 490 ha is devoted to rice<br />

production. <strong>Rice</strong> is planted twice a year with the National Irrigation<br />

System (NIS) as the main source of irrigation. Direct<br />

seeding is practiced by 90% of the farmers during the dry season.<br />

However, 90% of the farmers practiced transplanting dur-<br />

ing the wet season because of drainage problems as a result of<br />

the difficulty of water control.<br />

The farmers’ association and organization are considered<br />

as an effective conduit in extending assistance to individual<br />

farmers. A farmers’ organization called Ugnayan ng<br />

Magsasaka Makabagong Teknolohiya at Yamang Kalikasan<br />

para sa Kaunlaran ng Maragol, Inc. (UMAYKAMI) was<br />

formed, and was officially registered at the Securities and Exchange<br />

Commission (SEC). Identified leaders were trained on<br />

basic leadership and community empowerment. Its members<br />

were taught about the technologies in direct seeding.<br />

The population of insect pests was higher during the late<br />

growth stages of the rice crop. Occurrence of major pests was<br />

prevented by the 2-month fallow period and the use of resistant<br />

varieties. Using the trap barrier system + trap crop (TBS<br />

+ TC), it was observed that fewer rats were trapped as soon as<br />

the TBS +TC was established. This increased a week after the<br />

start of the field operations because of flooding and the destruction<br />

of rat burrows in the levees and surrounding areas.<br />

More rats were trapped up to the early maximum tillering period<br />

than at the later rice growth stages. Community-wide physical<br />

rat control was recommended at the start of the cropping<br />

season. It was recommended that the time to use baits was<br />

during the early rice growth stages, not throughout the cropping<br />

period as is now being practiced.<br />

Relative grain yields of the nutrient omission plots ranged<br />

from 50% to 98% compared with those of the complete plots.<br />

Results showed that indigenous nitrogen (N) and potassium<br />

(K) were limited in supply but not phosphorus (P). The recommended<br />

rate of 90-40-40 kg NPK ha –1 provided an average<br />

grain yield of 5 t ha –1 . However, by increasing the yield target<br />

to 7 t ha –1 , the soil nutrient supply would be limited for all<br />

three nutrients (N>K>P) and a higher P application would be<br />

needed to attain that yield target.<br />

The indigenous nitrogen-supplying capacity (INS) and<br />

the agronomic efficiency of applied N (AEN) of the farmercooperators’<br />

fields ranged from 50 to 70 kg N ha –1 and 5 to 25<br />

218 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. Comparative costs and returns analysis of direct-seeded (DSR) and transplanted (TPR) rice production in Maragol, Science City of Muñoz, Nueva Ecija, Philippines, 2001-03.<br />

Indicator 2001 2002 2003<br />

Dry season Wet season Dry season Wet season Dry season Wet season<br />

TPR DSR TPR DSR TPR DSR TPR DSR TPR DSR TPR DSR<br />

Gross returns (pesos ha –1 ) 39,682 44,435 35,032 – 52,773 58,673 25,478 30,353 54,298 56,063 34,861 32,250<br />

Yield (t ha –1 ) 4.90 5.49 4.30 – 6.21 6.90 3.23 3.84 6.46 6.67 4.73 4.30<br />

Price (pesos kg –1 ) 8.10 8.10 8.15 – 8.50 8.50 7.90 7.90 8.41 8.41 7.64 7.50<br />

Production costs (pesos ha –1 )<br />

Materials 7,081 6,535 4,216 – 6,795 6,977 5,488 5,425 5,998 6,514 4,832 3,865<br />

Labor 14,173 11,997 11,940 – 16,950 14,785 10,944 10,639 15,445 13,044 11,538 7,324<br />

Other costs 2,066 5,407 6,306 – 7,080 7,446 7,908 3,664 4,966 5,879 6,308 4,679<br />

Total costs (pesos ha –1 ) 23,319 23,939 22,462 – 30,825 29,208 24,340 19,728 26,409 25,438 22,679 15,868<br />

Net income (pesos ha –1 ) 16,363 20,496 12,570 – 21,948 29,464 11,138 10,625 27,889 30,625 12,182 16,383<br />

Net profit-cost ratio 0.70 0.86 0.56 – 0.71 1.01 0.05 0.54 1.06 1.20 0.54 1.03<br />

Cost per kg (pesos ha –1 ) 4.76 4.36 5.23 – 4.96 4.23 7.55 5.13 4.09 3.82 4.79 3.69<br />

kg grain produced per kg N applied, respectively. These results<br />

showed that the areas tested have a high N-supplying<br />

capacity and that a small amount of N is needed as basal fertilizer<br />

or during the early vegetative stage.<br />

The minus one element test (MOET) showed that most<br />

of the fields were deficient in macronutrients but not in micronutrients.<br />

Farmers were encouraged and trained to optimize the<br />

use of biomass residue from the farm, for example, carbonization<br />

of rice hull (CRH) and animal manure as organic fertilizer<br />

and soil conditioner. The use of inorganic fertilizer was reduced.<br />

The performance of the ride-on tillage implements for<br />

hand tractors was tested in farmers’ fields. The technology for<br />

the 40–60 kg ha –1 of certified seeds was demonstrated with<br />

the use of the hand-tractor-drawn paddy seeder and the manually<br />

drawn drum seeder. The use of 40–60 kg ha –1 of certified<br />

seeds not only reduced the input costs in rice production but<br />

also helped save seeds for other farmers’ use. This also had a<br />

yield advantage of 10% over the use of ordinary seeds.<br />

Most of the farmers belonged to the medium- (3–5 t<br />

ha –1 ) and high-yield group (>5 t ha –1 ). Direct-seeded rice appeared<br />

to be more profitable than transplanted rice as indicated<br />

by its higher gross returns, net income, and net profitcost<br />

ratios and its lower cost of production. Table 1 shows the<br />

comparative costs and returns analysis between direct-seeded<br />

and transplanted rice production in the village.<br />

Conclusions<br />

Village-level integration is an effective strategy to verify and<br />

promote technologies for direct-seeding rice production. The<br />

strong collaboration among farmers, local government units,<br />

village officials, and researchers has contributed to the successful<br />

implementation of the project.<br />

The upcoming activities of the project include verification<br />

trials based on the results of the MOET and NOPT; provision<br />

of a fertilizer domain and delivery of nutrient management<br />

technologies; development of an integrated rat management<br />

system; linkage with support services such as inputs and<br />

product markets, and credit services; and impact evaluation of<br />

introduced technologies.<br />

References<br />

Phil<strong>Rice</strong>-BAS (Philippine <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>-Bureau of Agricultural<br />

Statistics). 1997. Survey, 1997. Maligaya, Science City<br />

of Muñoz, Nueva Ecija, Philippines.<br />

Phil<strong>Rice</strong> (Philippine <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>). 2000. Management<br />

of field rats. <strong>Rice</strong> Technology Bulletin No. 28. DA-Phil<strong>Rice</strong><br />

Maligaya, Science City of Muñoz, Nueva Ecija, Philippines.<br />

12 p.<br />

Phil<strong>Rice</strong> (Philippine <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>). 2002. Integrated nutrient<br />

management for rice production. Technology Bulletin<br />

No. 45. DA-Phil<strong>Rice</strong> Maligaya, Science City of Muñoz, Nueva<br />

Ecija, Philippines. 24 p.<br />

Session 6: Trends in crop establishment and management in Asia 219


Notes<br />

Authors’ addresses: R. Manalili, B. Tadeo, E. Tiongco, W. Collado,<br />

R. Bermudez, C. Asis, J. De Dios, M. Adap, M. Dela Cruz, U.<br />

Duque, and L. Marquez, Philippine <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>,<br />

Maligaya, Science City of Muñoz, Nueva Ecija 3119, Philippines;<br />

P. Lanuza and B. Tejad, Department of Agriculture-<br />

Local Government Unit, Science City of Muñoz, Nueva Ecija<br />

3119, Philippines, e-mail: rgmanalili@philrice.gov.ph;<br />

btadeo@philrice.gov.ph.<br />

Wrap-up of Session 6<br />

The change in rice crop establishment from transplanting to direct<br />

seeding has occurred in many Asian countries because of<br />

rapid economic growth, increasing labor costs, and shortages of<br />

water. In addition, t<strong>here</strong> is a need to reduce the costs of rice<br />

production in order to maintain profitability despite the declining<br />

market price, a trend that is expected to continue in the future. A<br />

change in cultivation methods could have a substantial influence<br />

on the environment; t<strong>here</strong>fore, a change from transplanting to<br />

direct seeding should be carried out with a focus on the sustainable<br />

use of water and concern regarding agricultural chemical<br />

use.<br />

Direct seeding is practiced in three main forms: dry seeding,<br />

wet seeding, and water seeding. In dry seeding,<br />

nongerminated seeds are sown beneath the soil surface. The<br />

plant stand is more consistent than in wet and water seeding as<br />

the soil is aerobic. Dry seeding is advantageous when the water<br />

supply is limited at the time of land preparation and crop establishment.<br />

The cultivation system of “aerobic rice” in China, which<br />

combines dry seeding with a “nonflooding” water regime, is suggested<br />

as a water-saving technology. As the land is not flooded<br />

and puddled, heavy weed infestation and high rates of water infiltration<br />

are problems in dry seeding.<br />

Wet seeding is a widely practiced form of direct seeding in<br />

which the land is flooded and puddled in the same way as in<br />

transplanting. Pregerminated seeds are sown on the puddled soil<br />

surface just after drainage. Drainage is important to achieve reliable<br />

crop establishment. In Malaysia, Vietnam, Thailand, the Philippines,<br />

and Korea, the repeated use of herbicides and limited<br />

irrigation water have seriously complicated weed problems with<br />

the rapid shift in weed populations to annual grasses (e.g.,<br />

Ischaemum rugosum and Leptochloa chinensis) and weedy rice<br />

(Oryza sativa) that are difficult to control.<br />

In Japan, wet seeding is practiced differently from the<br />

method used in other Asian countries. Pregerminated seeds are<br />

commonly coated with an “oxygen-supplier” based on calcium<br />

peroxide and seeded under the surface of puddled soil. As the<br />

coating alone is not sufficient to overcome anaerobic soil conditions,<br />

the field must be drained at the crop establishment stage.<br />

Seeding beneath the puddled soil surface has the advantage of<br />

reducing seedling float and bird damage. Further, “hill seeding”<br />

of coated seeds under the soil surface using a specialized seeder<br />

has been shown to reduce crop lodging.<br />

Sowing pregerminated seeds into standing water (water<br />

seeding) has advantages over wet seeding in terms of water savings<br />

and weed control. The water used for puddling is not drained<br />

and conserved in the field, w<strong>here</strong>as the presence of water in the<br />

paddy field, particularly at the time of rice crop establishment,<br />

efficiently suppresses weed growth. A major limitation of water<br />

seeding, however, is the tendency of seedlings to float, which<br />

causes uneven rice populations.<br />

Direct seeding in place of transplanting can have a positive<br />

impact on the productivity of cropping systems, particularly<br />

in rainfed systems w<strong>here</strong> water availability is limited. In the rainfed<br />

and drought-prone areas of Bangladesh, advancement of the rice<br />

crop harvest through direct seeding increases the chance of a<br />

second crop. Direct seeding also has advantages in the ricewheat<br />

cropping system of northern India, w<strong>here</strong> water availability<br />

and labor cost are the major determinants of successful farming.<br />

Weed infestation is a major threat to yield and the further expansion<br />

of direct seeding in Asia. W<strong>here</strong> direct seeding has been<br />

introduced, t<strong>here</strong> is commonly not only an increase in weed biomass<br />

but also a change in the weed species. Repeated use of<br />

the same herbicide or those with the same mode of action risks<br />

the occurrence of herbicide resistance in weeds, and biotypes<br />

with resistance to acetolactate synthase inhibitor have been reported.<br />

Furthermore, the control of weedy rice presents major<br />

challenges.<br />

With the high development costs for new herbicides, the<br />

agrochemical industry currently focuses on novel uses and mixtures<br />

of current active ingredients in order to solve new weed<br />

problems associated with direct-seeded rice. Water management<br />

in terms of timing, duration, and depth of flooding at the crop<br />

establishment stage is critical in determining the scope for the<br />

use of herbicides. Understanding the biology of weeds in relation<br />

to water profile is important in developing ecologically sound weed<br />

control methods and to enable the exploitation of flooding for<br />

weed control. A new technology that coats rice seeds with iron<br />

powder to increase the specific gravity would overcome the problem<br />

of seedling float and make water seeding possible. This may<br />

provide a means to control weedy rice and water seeding is suggested<br />

as a potential control measure. Thus, the weed problems<br />

associated with direct-seeded rice could be alleviated to some<br />

extent by greater emphasis on combined herbicide use and water<br />

management.<br />

220 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Crop and weed management are expected to become increasingly<br />

knowledge-intensive as direct seeding becomes widespread<br />

and as technology develops. To meet the challenges of<br />

the declining availability of labor and water, increasingly difficult<br />

weed problems, and growing concerns regarding sustainability,<br />

farmers require greater access to information and guidance to<br />

enable them to make more objective decisions for crop and weed<br />

management.<br />

Session 6: Trends in crop establishment and management in Asia 221


SESSION 7<br />

Improving efficiency through innovations<br />

in mechanization<br />

CONVENER: N. Itokawa (NARO)<br />

CO-CONVENER: J. Rickman (<strong>IRRI</strong>)


<strong>Rice</strong> as a key resource for saving our planet<br />

Nobutaka Ito<br />

<strong>Rice</strong> has become an extremely important crop being cultivated<br />

worldwide. In fact, the total production of rice in the world<br />

has reached almost 500 million tons and 90% of the total production<br />

comes from Asian countries. Taking into consideration<br />

the world population of 6.3 billion, food per capita per year<br />

has been estimated at 400 kg. This rough estimate was based<br />

on the total world production of rice in addition to that of other<br />

cereals (such as wheat, sorghum, soybean, and maize), almost<br />

equal to 2 billion tons, plus 400 million tons from vegetables,<br />

fruit, and meat. However, this amount is just enough for now<br />

and the Chinese government would like to increase production<br />

to satisfy a growing population. In this paper, basic data<br />

related to rice and its cultivation are discussed prior to developing<br />

solutions to increase rice production and protect the environment.<br />

<strong>Rice</strong> is cultivated basically for food consumption; however,<br />

it can also be used as energy in the form of an environment-friendly<br />

fuel. This is possible by using its biomass, for<br />

which production efficiency is the highest among agricultural<br />

crops. About 430 L of ethanol can be produced from 1 ton of<br />

rice biomass. Reliability is based on the fact that almost 17 to<br />

19 tons of carbon dioxide per hectare are absorbed by the growing<br />

rice plants, which is nearly equal to the amount of carbon<br />

dioxide absorbed by some forest trees. In addition, the rice<br />

maturity stage takes only 4 months, w<strong>here</strong>as trees take more<br />

than 10 years to reach maturity. In this case, ethanol from rice<br />

can easily be obtained as the demand for energy consumption<br />

increases. This will also help minimize the world’s dependency<br />

on fossil fuel. The most significant advantage of using ethanol<br />

produced from biogas is the clean emission of gas compared<br />

with that of fossil fuel during combustion.<br />

These facts illustrate the important role of rice in helping<br />

resolve four global issues (called tetralemma), particularly<br />

concerning the increased consumption of fossil fuel, which<br />

jeopardizes the environment. This condition will sooner or later<br />

result in fossil fuel exhaustion; t<strong>here</strong>fore, we must develop an<br />

alternative solution to combat this threat.<br />

New technology in rice mechanization<br />

Direct sowing by use of coated rice<br />

Direct sowing of rice is popularly accepted in many developing<br />

countries because of its low cost and energy-saving technology<br />

in planting; however, the yield per unit area is almost<br />

half that obtained in many developed countries. Only the United<br />

States practiced direct sowing of rice successfully, combined<br />

with low-cost production and high application of technology.<br />

Yield is almost 7.7 t ha –1 , which is 1.1 t ha –1 higher than in<br />

Japan’s case using the transplanting method. A new type of<br />

direct sowing by using calcium peroxide-coated rice seed has<br />

good potential because of its low production cost. An automatic<br />

coating machine has already been developed and commercialized.<br />

Coating technology will be expanded for the purpose<br />

of reducing some operations by the simultaneous application<br />

of herbicide, pesticide, and fertilizer.<br />

Combine harvester<br />

A special head-feeding-type self-propelled combine harvester<br />

was developed and is commercially available in Japan. This<br />

machine can harvest from two to six rows depending on the<br />

specified width of cut. I present new concepts of the machine’s<br />

functions below.<br />

Combine husker (named by the author)<br />

Normally, cutting of straw, threshing, winnowing, and cleaning<br />

of grains are the main functions of a commercial rice combine<br />

harvester. However, husking can be done simultaneously<br />

through an additional mechanism I designed. Using the combine<br />

husker, rice can be directly harvested as brown rice, throwing<br />

out other foreign materials such as rice chaff, husks, empty<br />

grains, and weeds after husking and scattering them on the<br />

paddy field. The following improvements can be made by introducing<br />

this type of harvester: first, a savings of energy for<br />

transportation because of the reduction in bulk density through<br />

removal of rice husks and other foreign materials during harvesting;<br />

second, a saving of drying space equal to almost half<br />

of the rice volume.<br />

The turntable combine harvester<br />

To improve operating efficiency, the total time for completing<br />

the harvesting operation and the total distance traveled to complete<br />

the harvesting operation are normally used for evaluating<br />

how much this could be improved. The turntable combine<br />

harvester turns normally using the turntable mounted on the<br />

main chassis. The shape ratio of the paddy field expressed by<br />

the ratio of length to width, the pattern of promoting harvesting<br />

operation, the operating speed, the operating width of the<br />

cutter bar, and the specifications of the machine must be considered<br />

as the factors for improvement. For the turntable combine<br />

harvester, the total distance required to complete harvesting<br />

could be reduced by 10% compared with that of the conventional<br />

commercial machine. The total distance under the<br />

same conditions could be reduced almost 25% at maximum.<br />

The turntable combine harvester can be recommended for its<br />

safety, automation, and energy savings.<br />

The combine harvester equipped<br />

with a pivot turn mechanism<br />

The improvement in turnability of the tracked vehicle can be<br />

achieved by applying the pivot turn mechanism. The ground<br />

224 <strong>Rice</strong> is life: scientific perspectives for the 21st century


contact length of the braked track has a key for that purpose<br />

because the width of the track cannot be changed or controlled<br />

once it has been mounted or equipped.<br />

Brown rice dryer<br />

As mentioned above, the removal of rice husks during harvesting<br />

can save dryer space and allow normal air to be used<br />

for efficient brown rice drying only. A prototype brown rice<br />

dryer has already been fabricated for the test. T<strong>here</strong> is no need<br />

to use hot air for drying, which produces carbon dioxide<br />

through kerosene burning of rice chaff.<br />

The rice transplanter using a long seedling mat<br />

In automated transplanting operations, time consumed for a<br />

frequent supply of nursery plants is one obstacle for continuous<br />

machine operation. The capacity for carrying a young nursery<br />

or rice seedlings should be big enough to eliminate such a<br />

problem. A long nursery plant mat is one alternative for solving<br />

this problem.<br />

Precision farming<br />

Precision farming can be characterized mainly by (1) hightechnology<br />

agricultural machinery, (2) large-scale farming, (3)<br />

combined application of a global positioning system and geographic<br />

information system, and so on. Precision farming is<br />

seemingly impossible to introduce in Japanese conditions.<br />

However, newly reclaimed national area can be used for possible<br />

validation. This possibility is intended for improving food<br />

self-sufficiency. Furthermore, this would assure safe food production<br />

with a satisfactory level of security. Precision farming<br />

contributes a lot as an environment-friendly technology.<br />

The world faces many threats. This paper has presented some<br />

suggestions to help overcome these threats. First, the world<br />

requires enough food, particularly rice, as the world population<br />

is increasing dramatically. Second, world dependency on<br />

fossil fuel must be minimized. Third, emissions of carbon dioxide<br />

must be controlled. We must improve rice production<br />

and consider the crop’s potential. Mechanization has a vital<br />

role in this endeavor as it functions as a force multiplier to<br />

compensate the human labor shortage for those engaged in<br />

food production. This includes developing new technologies<br />

to strengthen rice production and add more value to make the<br />

crop more competitive in the world market. Biomass derived<br />

from rice can provide us with ethanol to be used as an environment-friendly<br />

fuel. Thus, pollution from toxic gas emissions<br />

with fossil fuel will be lessened and a safe environment restored.<br />

However, in Japan, any increase in rice production is<br />

controlled politically to keep the price high and maintain the<br />

farmers’ standard of living. This condition protects farmers’<br />

lives but tends to neglect human welfare. This should not be<br />

the case because it is more important to produce enough to<br />

achieve a good distribution of food globally and keep the environment<br />

safe. <strong>Rice</strong> has the potential to overcome various<br />

global threats. I also hope that environmental protection will<br />

be given much more priority.<br />

Bibliography<br />

Ito N. 2002. Global tetralemma and its overcome through agri-techno<br />

fusion strategy. J. Electrification 55(5):7-12.<br />

Ito N. 2002. Global tetralemma and its overcome through agri-techno<br />

fusion strategy. J. Electrification. 55(6):8-13.<br />

Ito N. 2002. Global tetralemma and its overcome through agri-techno<br />

fusion strategy. J. Electrification 55(7):15-21.<br />

Ito N. 2000. Global tetralemma and its overcome through rice production.<br />

Presented at the 5th Regional Science and Technology<br />

Policy <strong>Research</strong> Symposium, 5-7 September, Mie, Japan.<br />

Conclusions<br />

Notes<br />

Mechanizing paddy rice cultivation in Korea<br />

Woo-Pung Park and Sang-Cheol Kim<br />

Author’s address: Laboratory of Energy Utilization Engineering,<br />

Department of Environmental Science and Technology, Faculty<br />

of Bio-resources, Mie University, e-mail: ito-n@bio.mieu.ac.jp.<br />

The field agricultural production system in Korea has focused<br />

on paddy rice and plot size is relatively small (less than 1 ha).<br />

Until the late 1950s, manual and animal power were used in<br />

rice production. With the execution of the Five-Year Economic<br />

Development Plans started in the early 1960s, agricultural<br />

machinery such as water pumps and pesticide applicators were<br />

disseminated for disaster-prevention purposes. In the 1970s,<br />

as a large portion of rural labor moved to factories in urban<br />

areas, full-scale agricultural mechanization projects began. The<br />

power tiller replaced animal power in the 1970s, and rice trans-<br />

planters and harvesters were distributed in the 1980s to overcome<br />

labor peaks and shortages.<br />

Agricultural mechanization technologies were developed<br />

and extended in the 1990s to improve the agricultural system<br />

and productivity. The change from manual and animal power<br />

to about 98% mechanization in rice production took place<br />

within only 30 years, which is regarded as a significant achievement<br />

by other developing countries.<br />

Session 7: Improving efficiency through innovations in mechanization 225


Table 1. Mechanization rate (%) in rice production.<br />

Year Tillage Transplanting Spraying Harvesting Drying<br />

1985 70 23 68 17 2.1<br />

1990 84 78 93 72 15<br />

1995 97 97 98 95 32<br />

2002 100 98 100 99 49<br />

Review of agricultural mechanization<br />

Population changes in the rural community<br />

The farm population was 58% of the national population in<br />

1960, but it gradually decreased as labor demand for other<br />

industries increased. The number of farmers decreased, from<br />

5.0 million in 1975 to 4.4 million in 1980, 3.1 million in 1990,<br />

and 2.2 million in 2000. The annual reduction rate is above<br />

3%. The current labor shortage is caused by (1) an increasing<br />

portion of old and female labor and (2) the higher labor wages<br />

in the rural community have promoted farm mechanization<br />

more actively.<br />

Farmers from 20 to 59 years old gradually decreased<br />

and farmers more than 60 years old gradually increased. In<br />

2000, farmers older than 60 made up 33.1% of the farm population.<br />

This is a big problem in Korea.<br />

Expanding farm size<br />

Farm size averaged 0.9 ha in 1965. It increased to 1.37 ha in<br />

2000. However, the farm size is not big enough to carry out<br />

farm-restructuring effects. A small farm is defined as a field<br />

less than 1.0 ha in size. Medium-sized farms from 1 to 2 ha<br />

have decreased rapidly.<br />

On the other hand, the number of large farms (more than<br />

2.0 ha) has been increasing. The ratio of small farms among<br />

total farms decreased slowly. Farmers gave up the profession<br />

during the industrialization period and were absorbed by the<br />

industrial sector.<br />

Number of agricultural machinery<br />

Since the 1960s, water pumps, two-wheel tractors, and pesticide<br />

applicators have been extended to farms. Two-wheel tractors<br />

were 11,884 in 1970, 289,779 in 1980, and 751,236 in<br />

1990. In 2003, the number reached 857,809.<br />

Four-wheel tractors have been propagated on a large scale<br />

since 1980, and their number reached 2,664 in 1980, 41,203<br />

in 1990, and 211,576 in 2003. With the rapid propagation of<br />

agricultural machinery, rice cultivation operations, including<br />

tillage, land preparation, transplanting, and harvesting, became<br />

mechanized almost completely (about 98%) as of 1998. This<br />

was enabled by the government’s strong enthusiasm for farm<br />

mechanization and concentrated financial support to attain selfsufficiency<br />

in major crops.<br />

Current progress in agricultural mechanization<br />

In 2002, the mechanization rate of tillage and land preparation<br />

was 100%, rice transplanting 98%, pest control 100%, harvesting<br />

99%, and paddy rice drying 49% (Table 1). Except for<br />

drying, all operations seem to be fully mechanized. Average<br />

tractor power was in the 45-hp (33.8 kW) class. Major attachments<br />

for tractors are the Irang-Janggi (plow), rotavator, trailer,<br />

and others, and the width of the rotavator for the 40-hp class<br />

tractor is 170 cm.<br />

Four-row walking-type and six-row riding-type transplanters<br />

are the main machines extended. Three- and four-row<br />

head-feed paddy rice combine harvesters are now the main<br />

rice combine harvester. The number of paddy rice dryers increases<br />

as the paddy rice combine harvester is being propagated,<br />

but sun drying is still practiced because of good weather<br />

during the harvest period. Drying in the rice-processing center,<br />

which reached 340 units in 2003, is another choice for rice<br />

drying.<br />

<strong>Research</strong> on and development of agricultural machinery<br />

for paddy rice<br />

The following machinery has been developed:<br />

Partial-tillage direct rice seeder (1999)<br />

Attachable to a tractor, 8 rows, operation width 2 m<br />

(tillage 0.6 m, no-tillage 1.3 m, drain ditch 0.1 m).<br />

Paddy-field leveling rotavator (1999)<br />

For preparing paddy fields before transplanting or direct<br />

seeding of rice, 3.4 m in width and less than ±35<br />

mm in unevenness.<br />

Unmanned tractor (2000)<br />

Autonomous travel technology based on a GPS navigation<br />

system and remote-control technology with a<br />

field monitoring system for the unmanned tractor.<br />

Paper-mulching rice transplanter (2003)<br />

Developed for sustainable agriculture and no herbicide<br />

application.<br />

Partial-tillage rice transplanter (2002)<br />

Developed after experiments considered important<br />

factors in untilled paddy fields and the design parameters<br />

of a rotary-type machine.<br />

A rice wet-seeding broadcaster (2003)<br />

To mechanize wet seeding, a broadcaster was developed<br />

for wet-seeding operations. The prototype is<br />

composed of a metering device, a blowing part, and a<br />

seeding part, which can be attached to a tractor.<br />

226 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Automatic hose winding device for power sprayers<br />

(2002)<br />

This study was conducted to develop the device for<br />

power sprayers, designed with a remote-control system.<br />

Criteria for securing parts for the rice transplanter and<br />

combine (2001)<br />

This study looked into the major repair parts for the<br />

rice transplanter and combine. It estimated the quantity<br />

of repair parts needed so that agricultural machinery<br />

agencies could secure the appropriate volume of<br />

parts. A computer program was developed for this<br />

purpose.<br />

A total information system for agricultural machinery<br />

(2001)<br />

A system that users could easily access through the<br />

Internet.<br />

Dry-type rice polisher (1999)<br />

Decreases rice turbidity by 7% versus the wet-type<br />

rice polisher.<br />

A grain circulating-type natural air in-bin dryer (1999)<br />

It took 10 days to dry 8 tons of paddy rice from 21.9%<br />

(wet basis) to 16.7% (w.b.) moisture content using<br />

the prototype dryer.<br />

<br />

A computer vision system to evaluate rice kernel quality<br />

(2001)<br />

The algorithm developed in this study was able to<br />

correctly classify rice features. For segmentation, an<br />

overall accuracy of 98.9% was achieved. Overall accuracy<br />

was 99.6% for milling rate, 99.5% for broken<br />

rice, 97.6% for cracked rice, and 94.7% for chalky<br />

rice.<br />

The processing system for prewashed rice (2002)<br />

Turbidity decreased significantly in response to increased<br />

amounts of water, and dropped to the target<br />

of 50 ppm or even lower when water increased to<br />

423 mL kg –1 of rice or higher. Turbidity varied from<br />

47.33 to 48.00 and 48.67 ppm, respectively, for water<br />

rates of 800, 1,000, and 1,200 kg h –1 , which meant<br />

successful rice processing free from prewashing.<br />

The far-infrared ray grain dryer (2002)<br />

Considering crack ratio, the inspection test of the drying<br />

simulation program indicated that optimum drying<br />

temperature should be decreased gradually<br />

(100→90→80→75→72 °C) for the concurrent-flow<br />

circulation dryer, w<strong>here</strong>as the cross-flow dryer performed<br />

better at 55 °C.<br />

Future research and development for farm mechanization<br />

Paddy rice is the major crop in Korea and is the staple food of<br />

most Korean people, who eat more than 240 g per day. Annual<br />

production is about 5 million metric tons from around 1 million<br />

hectares of paddy fields using mechanized farming. But<br />

Korean farmers have some problems:<br />

It is difficult to make profits from farming because<br />

farming is small-scale.<br />

More than 48% of Korean farmers are more than 50<br />

years old.<br />

Korean paddy rice farming is not strong enough for<br />

international competition because rice production<br />

costs and the market price are very high vis-à-vis<br />

imported products.<br />

To solve these problems, Korean rice farming needs new<br />

strategic studies of advanced technology development, such<br />

as reducing production costs through large-scale farming and<br />

rice production for products of high quality and excellent taste<br />

and appearance, including verification of food safety.<br />

The following need to be developed:<br />

<strong>Rice</strong> processing technology for keeping head rice,<br />

which makes an even taste, appearance, glutinousness,<br />

glossy surface, and color.<br />

A precision agricultural model for the small field plots<br />

in Korea, which is based on field information to decide<br />

the optimum amount of fertilizer and pesticide<br />

considering the conditions of soil and paddy rice.<br />

Traceability technology that offers information from<br />

seed to the table for human well-being (a flow route<br />

for farm products).<br />

Notes<br />

Authors’ address: National <strong>Institute</strong> of Agricultural Engineering,<br />

RDA, Suwon, Korea, e-mail: wppark@rda.go.kr.<br />

Session 7: Improving efficiency through innovations in mechanization 227


The status and prospects<br />

of rice production mechanization in China<br />

Li Yaoming<br />

The planting area of rice occupies nearly 31,000,000 hectares<br />

on the mainland of China, and field yields account for 39% of<br />

the total grain production. <strong>Rice</strong> is the largest grain crop, with<br />

the largest planting area, highest single yield, and most total<br />

production. China has 34.5% of the world’s grain yield, with<br />

only 21.4% of the rice planting area in the world. So China<br />

has played a major role in global rice production.<br />

The status of rice production mechanization in China<br />

Upon entering the 21st century, China had made great progress<br />

in major areas such as tillage, breeding and planting, field management,<br />

and harvest. By the end of 2003, China had doubled<br />

the area of rice under mechanization since 1995. Mechanized<br />

planting was 5.08% in 1995 and has increased nearly 3% per<br />

year since then. The mechanized area is 8 times more than that<br />

in 1995, whose level of rice mechanization reached 24%, with<br />

an increase of 21.6%.<br />

The status of rice production mechanization in China is<br />

such that the total level is relatively low, except for the level of<br />

tillage mechanization, which is higher. Mechanized planting<br />

and harvest are lower, and planting is the weakest operation<br />

and has the most difficulties. T<strong>here</strong> are many reasons why farm<br />

mechanization does not combine well with agronomy. China<br />

has a vast territory with complex agricultural situations, and a<br />

large population with limited arable lands. The weak agricultural<br />

economy, the large labor force, and expensive farm machinery<br />

have all contributed to the slow adoption of rice mechanization.<br />

Technical analysis of rice mechanization in China<br />

Tillage mechanization<br />

For the different steps in rice production mechanization, the<br />

level of tillage mechanization is highest. T<strong>here</strong> are many kinds<br />

of tillage machines: the plow, furrower, drive-disk plow, paddyfield<br />

harrow machine, and rotary machines that meet requirements<br />

for use in the main rice production areas.<br />

With the economic change, the most imminent technique<br />

is the straw-chopper.<br />

<strong>Rice</strong> planting mechanization<br />

Mechanized direct sowing of rice. China has two kinds of direct-sowing<br />

techniques for rice: wet direct sowing and dry direct<br />

sowing. The wet direct sowing is mainly aperture sowing,<br />

and some implements can sow the rice seed after it has been<br />

soaked and pregerminated. Other machines can sow sprouted<br />

rice seeds with a sprout of 3 mm. In contrast, the dry direct<br />

sowing is mainly drilling, which usually uses a wheat-drilling<br />

machine to directly sow seed in the paddy without irrigation,<br />

to a depth of 2 cm. This method is required for crop uniformity.<br />

China now increasingly uses direct sowing of rice.<br />

The rice factory-bred seedling technique. The rice factory-bred<br />

seedling is one means of mechanizing rice transplanting.<br />

According to the Chinese situation, in recent years, Chinese<br />

farmers have welcomed farm machinery and techniques<br />

such as bred seedlings, precision-sowing equipment, carpettype<br />

seedlings, and pan-type seedlings using a shallow-transplanting<br />

machine.<br />

Mechanized rice transplanting. T<strong>here</strong> are two ways:<br />

transplanting and throwing seedlings. The transplanter uses<br />

carpet-type seedlings. Throwing seedlings uses pan-type seedlings<br />

with soil having less-bruising roots, more rapid greening,<br />

and higher yield. Moreover, the efficiency of throwing<br />

seedlings is higher and costs less, so Chinese farmers welcome<br />

it.<br />

Transplanters mainly adopt the crank-swing-type capture-seedling<br />

mechanism and entire supporting slide plates with<br />

a single wheel. The row distance is generally 30 cm, with manipulation<br />

by three operators. The thrown seedling is broadcast<br />

or falls into a row. The broadcasting machine throws seedlings<br />

using a centrifugal disc mechanism.<br />

Harvest technology. In the past few years, mechanized<br />

rice harvesting in China has developed. Implements include<br />

the general-purpose wheel-type combine harvester for rice and<br />

wheat, as well as a cutting machine and binder. Recently, some<br />

new implements have been developed, such as the rubber-track<br />

crawler, full-fed and head-fed combine harvesters, and stripper<br />

combine harvester suitable for harvest operations, thus<br />

basically meeting needs in various areas.<br />

Dry farming technology. China has been slow in developing<br />

machines suitable for dry cultivation. Even today, the<br />

level of mechanization is low. <strong>Rice</strong> mechanization has now<br />

become more important, so suitable machines for dry farming<br />

technology have become important.<br />

Prospects<br />

T<strong>here</strong> is still much room for the development of new tillage<br />

technology, and also perfecting existing technology for sowing<br />

and applying fertilizer. This would add much value. Implements<br />

for returning straw to the field are urgently needed but<br />

are still in the development stage. Laser cultivation implements<br />

would be useful.<br />

Under controllable environmental conditions, factorybred<br />

seedlings are being provided to mechanized, large-scale,<br />

centralized commercial farms according to a standardized flow-<br />

228 <strong>Rice</strong> is life: scientific perspectives for the 21st century


chart. The goal of this technology is to upgrade planting techniques.<br />

Transplanting, throwing seedlings, and direct sowing in<br />

rice mechanization are now a mature technology for rice plant<br />

establishment. The technique chosen will depend on local conditions.<br />

The development of rice direct-sowing technology is<br />

now increasing. To improve the production rate of the labor<br />

force, save costs, and promote overall mechanization, we suggest<br />

that direct sowing is an ideal planting technique. For all<br />

of China, mechanized transplanting still plays a major role,<br />

thus developing into a combination of transplanting and manure<br />

application. Furthermore, technology is maturing with the<br />

further development of shallow transplanting. Swaying seedlings<br />

and sowing seedlings and precision-throwing-seedling<br />

machines are likely to obtain a good market share.<br />

<strong>Rice</strong> harvest mechanization has a good future. It will be<br />

a qualitative leap forward after overcoming problems of field<br />

transportation and grain cleaning in double cropping in southern<br />

China. A new-generation stripper combine harvester will<br />

have improved reliability, high efficiency, and less power consumption.<br />

Importance is increasingly given to using machinery for<br />

dry farming after solving problems of lower performance, meeting<br />

the special needs of rice, and enlarging the production scale.<br />

China will emphasize developing rice transplanting and machinery<br />

for dry farming, especially for the hybrid rice highspeed<br />

transplanter, bred-seedling technology and equipment,<br />

and hybrid rice precision seeding and small-quantity directsowing<br />

machines. The assembly, integration, and complete<br />

setup are speeded up, thus improving overall rice mechanization<br />

in various areas, and further strengthening international<br />

exchange and cooperation. This will promote technical renovation<br />

and lift the level of mechanized rice production in China.<br />

Bibliography<br />

Chen Zhi. 2003. Unique approach to develop the farm machinery<br />

industry by innovation of science and technology. Trans.<br />

CSAM 34(3):131-134.<br />

Editorial Committee of China Agricultural Machinery Yearbook.<br />

2000. China agricultural machinery yearbook 2000. Beijing<br />

(China): Editorial Committee of China Agricultural Machinery<br />

Yearbook. p 206-214.<br />

Liu Min. 2002. The development tactics and countermeasures of<br />

agricultural mechanization in the 21st century in China. Chinese<br />

Agric. Mechan. (6):3-5.<br />

Song Jiannong, Zhuang Naisheng, Wang Lichen. 2000. The development<br />

tendency of Chinese rice planting mechanization in<br />

the 21st century. J. China Agric. Univ. 5(2):30-33.<br />

Notes<br />

Author’s address: Jiangsu University, China, e-mail:<br />

ymli@ujs.edu.cn.<br />

The Phil<strong>Rice</strong>-JICA rotary rice reaper: redesigning<br />

a technology for Filipino farmers and manufacturers<br />

Eulito Bautista, Manuel Jose Regalado, Arnold Juliano, Shuji Ishihara, Hiroyuki Monobe, Joel Ramos, and Leo Molinawe<br />

Harvesting and related operations are among the most laborintensive<br />

operations in rice production in Asia. In the Philippines,<br />

harvesting and threshing consume roughly 60% of the<br />

total labor devoted to rice (Takahashi 1994). Harvesting alone<br />

costs around 6–8% of total produce, w<strong>here</strong>as losses (including<br />

gathering) can reach as high as 5% of total yield (Andales 1998).<br />

Back-breaking manual reaping alone requires 10–16 persondays<br />

ha –l (Juarez et al 1988).<br />

Attempts have been made to modernize rice harvesting<br />

in Asia, the most successful of which was reported by Ezaki<br />

(1970) on walking-type reapers in Japan. Later, modified versions<br />

of this design were locally produced in China, Thailand,<br />

India, and Pakistan. This design made use of a cutterbar assembly,<br />

composed of reciprocating triangular blades placed<br />

above a stationary ledger plate. This cutterbar mechanism reciprocates<br />

at low speed, requires low power, and is highly suitable<br />

for windrowing operations since the plants have practically<br />

no horizontal movement after cutting prior to conveying<br />

to one side of the machine.<br />

In 1980, the Los Baños-based <strong>International</strong> <strong>Rice</strong> <strong>Research</strong><br />

<strong>Institute</strong> (<strong>IRRI</strong>) developed with Chinese engineers a<br />

local version of this type of reaper for release to Asian countries.<br />

The <strong>IRRI</strong> reaper was a simplified version of the Japanese<br />

and Chinese designs and was released to small manufacturers<br />

in the Philippines and a few other countries (<strong>IRRI</strong> 1987).<br />

This design, however, was not as successful as the Japanese<br />

model released shortly afterward in the Philippines because of<br />

its durability problem as a result of poor blade tolerance<br />

(Stickney et al 1986), less convenient operation, and high walking<br />

speed. The imported model is more durable, lighter, and<br />

more convenient to use, with a slower forward speed and reverse<br />

gear that allows easy headland turning.<br />

Except for its high price, this imported reaper was found<br />

to be suitable to the variable field conditions in the Philippines.<br />

Eventually, it slowly replaced the <strong>IRRI</strong> models in most<br />

areas. No cheaper version was attempted locally to compete<br />

with this imported design because of a lack of alternative components<br />

such as light diecast components and a small trans-<br />

Session 7: Improving efficiency through innovations in mechanization 229


mission with forward and reverse options. Thus, we aimed to<br />

develop a cheaper design suitable to the field conditions in the<br />

Philippines and that could be locally manufactured with less<br />

precision.<br />

Development of a reaping mechanism<br />

Focus was directed to replacing the reciprocating cutterbar<br />

assembly with a rotary cutting system borrowed from grass<br />

cutters (Takahashi 1993). Such a rotary cutter would require<br />

fewer blades and less manufacturing tolerance. To minimize<br />

development work, some mechanisms of the <strong>IRRI</strong> reaper were<br />

adapted on the new design, such as the header-tiller-engine<br />

arrangement, windrowing mechanism, crop guides, and<br />

starwheels. For a simpler, low-cost, and easy-to-maintain power<br />

transmission, an open-carriage tiller unit was adopted.<br />

Laboratory studies<br />

A series of laboratory trials on potential rotary cutters combined<br />

with a starwheel and vertical flatbelt conveyor were made<br />

to determine the functionality and optimum operating parameters<br />

(blade number and tip speed, forward speed) with grain<br />

shattering, quality of cut, and power requirement as critical<br />

parameters.<br />

From these trials, the number of blades per disc was set<br />

at three, blade tip speed was set at 23–30 m s –1 , and forward<br />

speed could range from 2.8 to 3.3 km h –1 .<br />

Prototyping and field testing<br />

A series of prototypes was prepared to improve technical functionality<br />

and field performance. The basic design has three<br />

rotary discs with serrated blades, driven by one hexagonal belt<br />

through a bevel gear transmission at the drive shaft, a single<br />

flatbelt with sheetmetal lugs for conveying and windrowing, a<br />

plastic starwheel above each disc to hold the plants during<br />

cutting, and three inclined header plates in front for gathering<br />

prior to cutting (Fig. 1A). Power transmission for the carriage<br />

unit used an open-case chain-sprocket transmission mechanism<br />

connected by belt and pulley to the engine. A 3.7-kW gasoline<br />

engine was placed behind the tiller similar to previous designs<br />

for balance and operator access.<br />

Initially, we encountered problems of straw scattering<br />

and clogging, failure to attain orderly windrows, and belt slippage<br />

that limited power to the cutting and conveying components<br />

(Togasi 1994, Maeoka 1997). However, by properly<br />

positioning the starwheel relative to the cutting device and<br />

vertical conveyor, a prototype that successfully windrowed cut<br />

plants was finalized. This prototype, with an 80-cm cutting<br />

width, harvests at 0.11–0.16 ha h –1 , with grain losses of 1–<br />

1.5% and 70–90° windrow angles from machine direction.<br />

Commercialization<br />

Three commercial models were developed for the Philippine<br />

market by three cooperating manufacturers (Fig. 1B). Two of<br />

the designs were similar to our final prototype except for the<br />

Table 1. Comparison of the rotary reaper and the imported reaper<br />

models.<br />

Parameter Rotary reaper Imported reaper<br />

Overall length (cm) 244 239<br />

Overall width (cm) 138 147<br />

Overall height (cm) 118 90<br />

Weight (kg) 158–185 116<br />

Engine (kW) 4.5 1.7<br />

Cutting width (m) 1.1–1.3 1.2<br />

Traveling speed (km h –1 ) 2.6–3.2 2.6<br />

Cutting device<br />

38 cm dia., rotary 120 cm, reciprocating<br />

Minimum cutting height (cm) 8.0 10.0<br />

Field capacity (ha h –1 ) 0.22–0.34 0.29<br />

Shattering losses (%) 0.1–1.3 about 1–2<br />

cutting widths (1.1 and 1.3 m), while a third model followed<br />

the conveying system of the Japanese model employing chains<br />

for crop conveyance and windrowing.<br />

The commercial models were improvements of the final<br />

prototype. The hexagonal belt drive for the cutters was replaced<br />

by two sets of chains for durability. A reverse system employing<br />

belts and pulleys was also incorporated for easier headland<br />

turning. A bigger engine (4.5 kW) was installed to allow<br />

extra power for difficult soil conditions. The steel cagewheels<br />

replaceable by rubber tires have been changed into a combined<br />

tire-cagewheel system for operation in any type of soil<br />

surface.<br />

Field tests indicate that the commercial reapers have performances<br />

similar to those of the imported model (Table 1).<br />

However, in terms of harvesting ability in extreme field conditions<br />

such as tall crops, weedy fields, and soft soil conditions,<br />

the rotary reaper has better ability. In addition, repair and maintenance<br />

at village shops are easier and cheaper.<br />

Farmers’ feedback<br />

Central Luzon farmers found the new rotary reaper suitable to<br />

their conditions but also expected it to work in both transplanted<br />

and direct-seeded fields in any season. Because rice<br />

plots are generally small, maneuverability and transfer across<br />

levees were important and reverse motion was necessary. Adjustment<br />

for cutting height was also suggested in the commercial<br />

models since some farmers cut lower while others prefer<br />

higher cutting height for thresher efficiency.<br />

In addition, the new design was expected to work in<br />

weedy fields, with short, low-density crops, and beside levees<br />

without manual cutting of plant rows. Operators also suggested<br />

adopting a higher forward speed to increase field capacity,<br />

which is important for custom service.<br />

Economics<br />

Economic analysis indicated that using the new reaper design<br />

could incur a harvesting cost of US$22 ha –l versus $25 ha –l for<br />

the imported model. This is mainly due to the lower investment<br />

cost of the rotary reaper ($1,360 compared with $2,700<br />

per unit of the imported design). The rotary reaper has to work<br />

230 <strong>Rice</strong> is life: scientific perspectives for the 21st century


2,200<br />

1,200<br />

Gasoline<br />

engine<br />

Converter lug<br />

Cutter blade<br />

disc<br />

806<br />

Starwheel<br />

Cage wheel<br />

360<br />

Fig. 1. The Phil<strong>Rice</strong>-JICA rotary reaper prototype (A) and commercial model (B). (A) Schematic view of<br />

the prototype, (B) a commercial model during field operation.<br />

Session 7: Improving efficiency through innovations in mechanization 231


for 33 ha y –l while the imported unit has to complete 58 ha<br />

y –l at a benefit-cost ratio of 1.0.<br />

In a separate study, Yasunobo (2001) noted that the rotary<br />

reaper should be economical to own when harvesting at<br />

least 4.13 ha. In selected areas, farmers have greater incentives<br />

to own such a reaper because of the income-generating<br />

potential for rice harvesting (from custom fees and extra opportunities<br />

for thresher-owners).<br />

References<br />

Andales SC. 1998. Report on postharvest loss assessment. Muñoz,<br />

Nueva Ecija (Philippines): Bureau of Postharvest <strong>Research</strong><br />

and Extension.<br />

Ezaki H. 1970. Binders and combines. Tokyo: Agricultural Books<br />

Co. (In Japanese.)<br />

<strong>IRRI</strong> (<strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>). 1987. <strong>IRRI</strong> annual report.<br />

Los Baños (Philippines): <strong>IRRI</strong>. p 512-513.<br />

Juarez F, Te A, Duff B, Crissman L, Stickney RE, Manaligod HT,<br />

Salazar GC, Fernandez CP. 1988. The development and impact<br />

of mechanical reapers in the Philippines. Agric. Econ.<br />

Paper No. 88-23. Los Baños (Philippines): <strong>International</strong> <strong>Rice</strong><br />

<strong>Research</strong> <strong>Institute</strong>.<br />

Maeoka K. 1997. Report on the development of the Maligaya rice<br />

reaper. Report to JICA Technical Cooperation Project. <strong>Rice</strong><br />

Engineering and Mechanization Division, Phil<strong>Rice</strong>, Muñoz,<br />

Nueva Ecija.<br />

Stickney RE, Salazar GC, Manaligod HT, Juarez FS, Duff B, Bockhop<br />

CW, Fernandez CPo 1986. CAAMS-<strong>IRRI</strong> mechanical reaper:<br />

experiences in the Philippines. In: Small farm equipment for<br />

developing countries. Proceedings of the <strong>International</strong> Conference<br />

on Small Farm Equipment for Developing Countries:<br />

Past Experiences and Future Priorities. Los Baños (Philippines):<br />

<strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>. p 341-358.<br />

Takahashi H. 1993. Report on the development of the Maligaya<br />

reaper. Report to JICA Technical Cooperation Project. <strong>Rice</strong><br />

Engineering and Mechanization Division, Phil<strong>Rice</strong>, Muñoz,<br />

Nueva Ecija, Philippines.<br />

Takahashi H. 1994. Present situation and problems of rice production<br />

in the Philippines. Paper presented at the Workshop on<br />

Farming Management of <strong>Rice</strong>-Based Lowland Farms,<br />

Phil<strong>Rice</strong>, Muñoz, Nueva Ecija, 5 December 1994.<br />

Togasi T. 1994. Report on the test and evaluation of the Maligaya<br />

reaper. Report to JICA Technical Cooperation Project. <strong>Rice</strong><br />

Engineering and Mechanization Division, Phil<strong>Rice</strong>, Muñoz,<br />

Nueva Ecija.<br />

Yasunobo K, Casiwan C, Manalili R, Francisco S. 2000. Factors<br />

influencing farm mechanization in the Philippines: socioeconomic<br />

context. Report to JICA Technical Cooperation Project,<br />

Phil<strong>Rice</strong>, Maligaya, Muñoz, Nueva Ecija.<br />

Notes<br />

Authors’ address: Philippine <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>, e-mail:<br />

eubautista@philrice.gov.ph.<br />

Acknowledgments: We wish to acknowledge the support and suggestions<br />

of Dr. Santiago R. Obien and Dr. Hitoshi Takahashi<br />

in this Phil<strong>Rice</strong>-JICA collaborative project. The assistance of<br />

JICA short-term experts Hiroyuki Takahashi, Tatsusi Togashi,<br />

Kunihiko Maeoka, and Koji Inooku was crucial during<br />

prototyping and testing.<br />

Long-mat seedling culture and the transplanting system:<br />

an innovative one-person operational technology<br />

for mechanical rice transplanting<br />

Hisashi Kitagawa, Akio Ogura, Kouhei Tasaka, Hiroyuki Shiratsuchi, and Mikio Yashiro<br />

<strong>Rice</strong> transplanting was mechanized in the 1970s in Japan, and<br />

now more than 99% of paddy fields are cultivated by mechanized<br />

transplanting. Even large-scale transplanters with higher<br />

efficiency and precision are becoming common, and mechanical<br />

transplanting is assumed to have reached its technical perfection.<br />

But a problem remains.<br />

Usually, a plastic box (60 × 28 × 3 cm), called a “nursery<br />

box,” is used for raising rice seedlings. Soil is packed into<br />

it, and seeds are sown. Then, nursery boxes are arranged in<br />

vinyl houses and the seedlings are raised. When the seedlings<br />

grow up, the nursery boxes are put on a truck and taken to the<br />

paddy fields. The seedlings are then transplanted by a transplanter.<br />

This conventional soil-seedbed system (CSS) has major<br />

problems for the following reasons: (1) a nursery box filled<br />

with soil weighs about 6 kg, (2) 2,000 nursery boxes are necessary<br />

for paddy fields of 10 ha, and (3) it is necessary to carry<br />

nursery boxes many times from sowing to transplanting. The<br />

larger the farmer is, the harder it is to carry the nursery boxes.<br />

Our center developed the long-mat seedling culture system<br />

(long-mat system: LMS) to save labor and facilitate work in<br />

comparison with the CSS (Tasaka et al 1996, 1997), and has<br />

improved it further.<br />

In this paper, we introduce the general characteristics of<br />

this long-mat system and discuss the recent development of<br />

rolling-up equipment that enabled a one-person operation, and<br />

the improvement of the higher-precision transplanter for longmat<br />

seedlings.<br />

232 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Characteristics of the long-mat system<br />

Raising of seedlings by hydroponics<br />

The nursery device is composed of a nursery tray (60 × 28 × 5<br />

cm), a tank for liquid fertilizer, and a water-jet pump. A nonwoven<br />

cloth is put on the nursery tray, and germinated seeds<br />

are sown on it. The water pump circulates culture solution,<br />

and the seedlings are ready for transplanting in 2 weeks. The<br />

mat-shape seedlings about 6 m long grown <strong>here</strong> are called<br />

“long-mat seedlings (LS).”<br />

The length of the conventional nursery box in the CSS is<br />

60 cm. T<strong>here</strong>fore, the length of one LS is equivalent to that of<br />

ten nursery boxes in the CSS. T<strong>here</strong>fore, the number of LS is<br />

only one-tenth of that in the CSS. And, for the same amount of<br />

seedlings, the weight of LS is about one-fifth of that of the<br />

CSS, and t<strong>here</strong>fore it is easier to carry LS to the field.<br />

Rolling up seedlings<br />

Long-mat seedlings are too long to carry. So, the technology<br />

to roll up LS in a compact form was developed, which enabled<br />

farmers to set seedlings on the transplanter in a normal position<br />

(Fig. 1). The most marked aspect of this technology is the<br />

method of rolling up LS, which is called the “reverse roll<br />

method.” The details of this technology will be explained below.<br />

The normal roll method is not as good as the reverse roll<br />

method.<br />

Manual rolling up by two people using iron plates. Three<br />

steps are followed:<br />

1. By rolling a heavy iron roller on a long-mat seedling<br />

in one direction, the leaves of the seedlings are bent<br />

down.<br />

2. Ten sheets of iron plates (60 cm long) are placed on<br />

the seedlings, and pressed down.<br />

3. Two people are needed for rolling up. While one<br />

slowly shifts an iron plate, the other rolls up the LS<br />

using PVC pipe as a core.<br />

In this method, the cost is lower, but the labor requirement<br />

is higher. T<strong>here</strong>fore, this technology is suitable for smallscale<br />

farmers.<br />

Mechanical one-person rolling up. A machine to support<br />

the rolling up of raised long-mat seedlings was developed<br />

for use by large-scale farmers. Instead of pressing down seedlings<br />

with iron plates, this machine has a structure to draw<br />

seedlings into the front with a rotating rubber belt and to press<br />

the seedlings down. This machine is self-propelled with a motor<br />

driven by a battery. One person follows the machine, and rolls<br />

up the seedlings. Using this machine, LS can be rolled up easily<br />

with only one operator.<br />

The time required for rolling up was reduced to less than<br />

half of that using iron plates. This machine will soon come<br />

onto the market.<br />

Loading of the rolled seedlings. The volume of the rolled<br />

seedlings is about one-fifth that of the equivalent amount of<br />

seedlings in the CSS. The seedlings can be transported by a<br />

pickup truck, which many Japanese farmers have. A pickup<br />

truck can carry seedlings for a rice field of 1.5 ha at one time.<br />

Transplanting long-mat seedlings. For the long-mat<br />

transplanter, the folders for rolled seedlings and seedling press<br />

controls are attached to the normal transplanter on the market.<br />

However, because the root-mat of LS is softer and more flexible<br />

than that of the CSS, LS can be injured at the time of<br />

machine transplanting, and some seedlings die before rooting.<br />

The transplanter was improved to compress the seedling mat<br />

by force and to increase the density of the root-mat (Fig. 2).<br />

For precision of transplanting, t<strong>here</strong> is no inferiority in the<br />

transplanting of LS compared with that of the CSS with this<br />

easy adjustment.<br />

Labor savings and yield<br />

At the time of transplanting in the CSS, each nursery box should<br />

be handed over to the operator in the field. T<strong>here</strong>fore, both an<br />

operator and a helper are required. Mainly spouses and elderly<br />

people help with the loading of the nursery boxes, which<br />

is heavy labor.<br />

But, if long-mat technology is introduced, just one operator<br />

can do transplanting. Moreover, if the machine that supports<br />

rolling up is adopted, the whole operation from sowing<br />

to transplanting can be done completely by one person. The<br />

working hours for transplanting in LMS are less than one-third<br />

of those in the CSS. T<strong>here</strong>fore, LMS is an excellent laborsaving<br />

technology.<br />

The labor intensity of long-mat technology is less than<br />

half of that in the CSS. The typical working posture in the<br />

CSS, bending the waist to lift heavy nursery boxes, almost<br />

disappeared. The posture used in the LMS is much easier.<br />

It is estimated that the applicability of this technology is<br />

high because t<strong>here</strong> is no inferiority in growth and yield in comparison<br />

with growth and yield in the CSS. And, some largescale<br />

farmers in Kanto and Tohoku regions have already<br />

adopted this technology.<br />

Epilogue<br />

The National Agricultural <strong>Research</strong> Center (NARC) developed<br />

the basic technology of LMS. The basic equipment was developed<br />

by private companies in the project funded by the Biooriented<br />

Technology <strong>Research</strong> Advancement Institution<br />

(BRAIN). And, operational technologies such as raising and<br />

transplanting seedlings were developed by the agricultural<br />

experiment stations of Iwate, Saitama, Nagano, and Ibaraki<br />

prefectures in cooperation with NARC. NARC is now promoting<br />

the diffusion of long-mat technology to farmers in cooperation<br />

with the prefectural diffusion sections, private corporations,<br />

and the farmers who had introduced LMS.<br />

Long-mat technology makes the loading and transplanting<br />

of seedlings easy. So, it is effective not only in large fields<br />

on a flat plain but also in the small and scattered fields in<br />

middle-mountainous places. Hydroponic devices are used only<br />

in early spring. The technology to grow tulips and strawberry<br />

seedlings was developed to increase the effective use of the<br />

Session 7: Improving efficiency through innovations in mechanization 233


Normal roll method<br />

Reverse roll method<br />

Push down<br />

roller<br />

Core for rolling up<br />

Seedlings are cut<br />

off because leaves<br />

come out first<br />

Transplanting<br />

finger<br />

Running<br />

direction<br />

Running<br />

direction<br />

Iron weight<br />

plate<br />

Core for<br />

rolling up<br />

Seedlings fall down in this<br />

direction<br />

Running<br />

direction<br />

Motor<br />

Belt<br />

Nursery tray<br />

Fig. 1. The principle of rolling up (upper right), manual rolling up by two people (middle), and mechanical<br />

one-person rolling up (below).<br />

facilities, too. It is expected that the long-mat technology will<br />

spread to stimulate agriculture in the region.<br />

References<br />

Tasaka K, Ogura A, Karahashi M. 1996. Development of hydroponic<br />

raising and transplanting technology for mat type rice<br />

seedlings. Part 1. Raising test of seedlings. J. Jpn. Soc. Agric.<br />

Mach. 58:89-99.<br />

Tasaka K, Ogura A, Karahashi M, Niiyama H, Namoto H, Kaneko T.<br />

1997. Development of hydroponic raising and transplanting<br />

technology for mat type rice seedlings. Part 2. Development<br />

and field test of rice transplanters for long mat type hydroponic<br />

rice seedlings. J. Jpn. Soc. Agric. Mach. 59:87-98.<br />

Notes<br />

Author’s address: National Agricultural <strong>Research</strong> Center, e-mail:<br />

kitaga@narc.affrc.go.jp.<br />

234 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Seedling press<br />

controls<br />

Folders for rolled<br />

seedlings<br />

Seedlings<br />

Planting finger<br />

Guides to gather<br />

seedlings<br />

Fig. 2. The outline of the long-mat transplanter (left) and remodeling for higher precision transplanting<br />

(right).<br />

High-precision autonomous operation using<br />

an unmanned rice transplanter<br />

Yoshisada Nagasaka, Yutaka Kanetani, Naonobu Umeda, and Takuo Kokuryu<br />

With farm size increasing and the number of farmers decreasing,<br />

more efficient agricultural practices are needed. However,<br />

in Japan, fields are not as yet sufficiently consolidated. They<br />

are frequently dispersed and it is difficult to use large machines<br />

in areas that would be unable to bear their weight. This efficiency<br />

problem would be solved, however, if one operator were<br />

able to control several lightweight machines simultaneously.<br />

The goal of our research is to develop an autonomous operating<br />

system for paddy fields that would permit one operator to<br />

control multiple machines. The objective of this study is to<br />

develop an autonomous navigation system for the rice transplanter.<br />

Several pieces of research on autonomous agricultural<br />

machinery have been published (Reid et al 2000). Recently,<br />

an autonomous tractor using an optical surveying device and a<br />

terrestrial magnetism sensor for plowing was developed<br />

(Matsuo et al 2002). These researchers obtained good results<br />

but found it difficult to control multiple machines because each<br />

vehicle required its own optical surveying device. Some researchers<br />

used a differential global positioning system (DGPS)<br />

(Cho and Lee 2002). Kalman filtering of DGPS can effectively<br />

correct DGPS position error (Han et al 2002), but it does not<br />

provide enough precision for operation in paddy fields.<br />

Noguchi et al (2002) developed a robot tractor and Nagasaka<br />

et al (2000) developed an automated rice transplanter. Both of<br />

them employed RTKGPS and FOG sensors that established<br />

precise operations. In this paper, the results of automated rice<br />

transplanting operation experiments are reported. We first describe<br />

the sensors, actuators, and controllers used for the automated<br />

rice transplanter and how data are processed. Then we<br />

describe the vehicle control methods and how the desired operating<br />

path is chosen. The experimental results are discussed,<br />

and the final section gives conclusions.<br />

Materials and methods<br />

Vehicle, sensors, actuators, and controllers<br />

We modified a commercial 6-row rice transplanter (PH-6, Iseki<br />

Co., Ehime, Japan). Figure 1 shows the modified rice transplanter<br />

controlled by a computer with a 486-compatible 66<br />

MHz central processing unit. Figure 2 is a schematic for an<br />

automated rice transplanting system. An RTKGPS (MS750,<br />

Trimble Navigation Ltd., Sunnyvale, California) with 2-cm<br />

precision at 10 Hz data output was used to locate the position<br />

of the rice transplanter. For communication between the<br />

RTKGPS reference station and the rover station, 5-mW output<br />

wireless radio modems (YRM211, Vertex Standard Co.,<br />

Ltd., Japan) were used with baud rates set at 9,600 bps. A FOG<br />

sensor (JG-35FD, Japan Aviation Electronics Ind., Ltd., Tokyo)<br />

was used to measure the yaw angle, and an inclinationmeasuring<br />

apparatus (JCS-7401, Japan Aviation Electronics<br />

Ind., Ltd., Tokyo) composed of three FOG sensors and three<br />

accelerometers was used to measure the roll and pitch angles.<br />

The GPS position data, yaw, and roll and pitch angle<br />

data were transferred to a computer through an RS232C interface.<br />

The sampling rate was 10 Hz for the GPS, 20 Hz for the<br />

yaw angle, and 25 Hz for the roll and pitch angles. The main<br />

computer corrected the GPS position data, which were influenced<br />

by the vehicle inclination, and calculated the control<br />

parameters, then sent them to an industrial programmable logic<br />

Session 7: Improving efficiency through innovations in mechanization 235


Fig. 1. Unmanned rice transplanter.<br />

Data<br />

Modem<br />

Modem<br />

RTKGPS base station<br />

RTKGPS rover station<br />

RS232C<br />

Main computer<br />

RS232C<br />

Steering<br />

HST<br />

Clutch<br />

Brake (L, R)<br />

Engine throttle<br />

Attachment up-down<br />

Encoder<br />

Limit switch<br />

Motor<br />

Controller<br />

PLC<br />

R5232C<br />

Yaw<br />

Roll<br />

Pitch<br />

Fig. 2. A schematic for an automated rice transplanting system.<br />

236 <strong>Rice</strong> is life: scientific perspectives for the 21st century


controller (PLC) (KZ-350, Keyence CO., Osaka) through the<br />

serial port every 100 milliseconds. The PLC receives control<br />

parameters from the main computer through the RS232C interface<br />

link unit to control the actuators. The steering angle is<br />

sensed by means of an absolute rotary encoder and is controlled<br />

by a DC motor. Proximity sensors detect the clutch and<br />

brake positions and electrical linear cylinders control the clutch<br />

and brake pedals. The positions of the transplanting instrument<br />

control levers, engine throttle, and hydrostatic transmission<br />

(HST) lever were measured using absolute rotary encoders<br />

and operated by electrical linear cylinders. The PLC control<br />

loop was 2 milliseconds.<br />

Path planning<br />

Before starting operation, the computer must create a desired<br />

path along which the rice transplanter travels. In this study, the<br />

paddy field was assumed to be rectangular. The four corners<br />

in the field were measured beforehand. The sowing width of a<br />

6-row rice transplanter is 1.8 m. Since a paddy field usually<br />

has only one entrance, the desired path depends on the width<br />

of the field.<br />

Vehicle control<br />

In paddy fields, it is thought that the paddy ground is flimsier<br />

than upland fields. Several papers discuss steering control in<br />

upland fields. O’Connor et al (1996) used a steering controller<br />

based on a set of linear motion equations. Cho and Lee (2000)<br />

used a fuzzy controller for autonomous operation for an orchard<br />

speed sprayer. Kise et al (2002) developed an optimal<br />

steering controller and obtained good curved-path guidance<br />

results. Inoue et al (1997) developed an adaptive steering controller<br />

that corrected steering system delay. Most of these researchers<br />

analyzed vehicle dynamics and made a dynamic<br />

model, then decided on the control parameters.<br />

In this study, we used a simple proportional controller<br />

for steering control before evaluating the effectiveness of advanced<br />

controllers in loose-ground-like paddy fields.<br />

At the headland, the rice transplanter moves forward and<br />

backward during a turn so as to minimize the headland space.<br />

When the rice transplanter reaches the edge of the field, it first<br />

stops transplanting and lifts the transplanting attachment, then<br />

the HST lever is set to the forward position. While the rice<br />

transplanter is turning and the yaw angle is less than 160 degrees,<br />

only the yaw angle is obtained. Under these conditions,<br />

the steering angle is kept at 40 degrees and the brake is applied<br />

on one side. If the yaw angle exceeds 160 degrees, the<br />

rice transplanter is moved as close as possible to the next desired<br />

path. Then it moves backward.<br />

Results and discussion<br />

The experiment was conducted 4 days after puddling. The field<br />

size is a 20 m × 100 m square. When the operating program<br />

started, the transplanter moved into the paddy field and reached<br />

the starting point. Then it started operation and went forward<br />

and backward in the field 4 times. Finally, it planted the seedlings<br />

around the headland. After finishing operation, it went<br />

out from the field and stopped automatically. The deviation<br />

from the desired straight path was less than 12 cm at a traveling<br />

speed of 0.6 m s –1 during operation. As the turning radius<br />

of the vehicle at the headland was around 2 m, it was easy to<br />

get back as close as possible to the new desired path after turning.<br />

The operating efficiency was about 0.3 ha h –1 when long<br />

mat-type hydroponic seedlings (Tasaka 1998) were used.<br />

When the data communication between the RTKGPS<br />

base and rover station via radio link was disconnected, the<br />

clutch was released and operation was interrupted. Then, as<br />

soon as the radio link was connected, operation started again.<br />

Conclusions<br />

An automated rice transplanter was developed and autonomous<br />

guidance operation was conducted. The maximum deviation<br />

from the desired straight path is 12 cm and RMS deviation is<br />

5.5 cm at a 0.6 m s –1 operating speed. This is only accuracy<br />

enough for rice transplanting operations, and not enough for<br />

spraying and mechanical weeding operations after rice transplanting.<br />

Since it is necessary to drive an autonomous vehicle<br />

between the crop row to do spraying and mechanical weeding<br />

operations, the maximum deviation must be reduced to less<br />

than 5 cm. It is also necessary to evaluate the control algorithms.<br />

References<br />

Cho SI, Lee JH. 2000. Autonomous speed sprayer using differential<br />

global positioning system, genetic algorithm and fuzzy control.<br />

J. Agric. Eng. Res. 76:111-119.<br />

Han S, Zhang Q, Noh H. 2002. Kalman filtering of DGPS position<br />

for a parallel tracking application. Trans. ASAE 45(3):553-<br />

559.<br />

Inoue K, Otuka K, Sugimoto M, Murakami N. 1997. Estimation of<br />

place of tractor and adaptive control method of autonomous<br />

tractor using INS and GPS. Preprints of the <strong>International</strong><br />

Workshop on Robotics and Automated Machinery for Bio-<br />

Productions, 27-36, EurAgEng, Gandía, Spain.<br />

Kise M, Noguchi N, Ishii K, Terao H. 2002. The development of the<br />

autonomous tractor with steering controller applied by optimal<br />

control. Proceedings of Automation Technology for Off-<br />

Road Equipment. Chicago, Ill. (USA): ASAE. p 367-373.<br />

Matsuo Y, Yamamoto S, Yukumoto O. 2002. Development of tilling<br />

robot and operation software. Proceedings of Automation<br />

Technology for Off-Road Equipment. Chicago, Ill. (USA):<br />

ASAE. p 184-189.<br />

Nagasaka Y, Otani R, Shigeta K, Taniwaki K. 2000. A study about<br />

an automated rice transplanter with GPS and FOG. ASAE<br />

Paper No.00-1045. Milwaukee, Wis. (USA): ASAE.<br />

Noguchi N, Kise M, Ishii K, Terao H. 2002. Field automation using<br />

robot tractor. Proceedings of Automation Technology for Off-<br />

Road Equipment. Chicago, Ill. (USA): ASAE. p 239-245.<br />

O’Connor M, Bell T, Elkaim G, Parkinson B. 1996. Automatic steering<br />

of farm vehicles using GPS. Paper presented at the 3rd<br />

<strong>International</strong> Conference on Precision Agriculture. Madison,<br />

Wis. (USA): ASA, CSSA, and SSSA.<br />

Session 7: Improving efficiency through innovations in mechanization 237


Reid JF, Zhang Q, Noguchi N, Dickson M. 2000. Agricultural automatic<br />

guidance research in North America, Comput. Electron.<br />

Agric. 25(1/2):155-167.<br />

Tasaka K. 1998. Outline of raising and transplanting technology for<br />

long mat type hydroponic rice seedlings. Agric. Eng. Paper<br />

98-A-061. EurAgEng, Oslo, Norway.<br />

Notes<br />

Authors’ address: National Agricultural <strong>Research</strong> Center, e-mail:<br />

zentei@affrc.go.jp.<br />

Precision-drilling methods for the direct sowing<br />

of rice in flooded paddy fields<br />

Yoh Nishimura, Kazunobu Hayashi, Takashi Goto, and Mitsuhiro Horio<br />

Dry seeding is the most common direct-sowing method used<br />

in Japanese rice paddy fields. In 1996, before this study began,<br />

only 7,000 ha (< 0.5%) of the rice fields in Japan relied<br />

on direct-sowing methods, and dry seeding accounted for approximately<br />

70% of the total. However, considering the climatic<br />

conditions in Japan and the working system available<br />

for rice production, we believe that wet seeding could considerably<br />

improve rice productivity. Because wet seeding relies<br />

on cultivating methods similar to rice transplanting, however,<br />

it is generally considered to be more expensive than dry seeding,<br />

in terms of both labor and machinery requirements.<br />

The major challenge related to implementing wet seeding<br />

in Japan has been crop stabilization and minimizing the<br />

occurrence of lodging. Most rice varieties that are currently<br />

grown in Japan have been selectively bred for eating quality,<br />

and, as a result, few varieties are specifically suited for directsowing<br />

methods and are also resistant to low temperatures and<br />

lodging. However, several studies have been carried out investigating<br />

direct-sowing methods using several different rice<br />

varieties. Japanese rice farmers have expressed a desire to produce<br />

high-quality rice (Koshihikari, etc.) that can attain the<br />

highest market prices. As a result, it is not broadcast seeding<br />

that places seeds on the soil surface but the sowing method<br />

that buries seeds in the soil absolutely that could be the best<br />

option.<br />

Traditional wet seeding in flooded paddy fields<br />

An improved technology, aimed at stabilizing crop growth and<br />

improving the efficiency of crop establishment by burying seeds<br />

in the soil, was developed in the 1980s. A method involving<br />

the coating of seeds with CaO 3 was found to improve both<br />

crop emergence and establishment. Furthermore, a riding-type<br />

drill seeder, which could be used to open shallow furrows on<br />

the puddled soil surface and re-cover the furrow after seeding,<br />

was also developed. Although these machines were available<br />

on the market, their widespread use was limited, with the majority<br />

of growers continuing to use more conventional transplanting<br />

methods.<br />

Commercial success of this machinery was limited because<br />

of several problems. First, the coating machine required<br />

a high level of skill for its operation, especially for calculating<br />

the appropriate doses of chemical powder and water. This process<br />

required constant observation to control the coating efficiency<br />

after adding rice seeds to the inclined-rotator drum.<br />

High concentrations of chemical dust in the working environment<br />

also caused a significant problem and a potential health<br />

risk. The drill seeder was found to have poor accuracy for the<br />

control of seeding depth affected by the hardness of the soil<br />

surface. Several mechanical problems also occurred related to<br />

the stability of the furrow-opener and the covering plate.<br />

Development of a precision-drilling method<br />

for flooded paddy fields<br />

Following the Uruguay Round agreement in 1994, it was decided<br />

that t<strong>here</strong> should be a gradual reduction in the tariff placed<br />

on imported rice. This agreement encouraged the production<br />

of low-cost rice that could be produced with minimum labor.<br />

<strong>Research</strong> carried out in our laboratory led to the development<br />

of a direct-sowing machine, with financial assistance from an<br />

“Urgent Development of Agricultural Machinery and Its Commercial<br />

Enterprise” project aimed at facilitating improvements<br />

in agricultural machinery. This research led to the development<br />

of an automatic coating machine for rice paddy seeds,<br />

and a precision drill seeder.<br />

<br />

Automatic coating machine for paddy seed<br />

Design. The coating machine has several characteristics that<br />

lead to improved efficiency.<br />

The machine uses dewatered, dipped seeds to stabilize<br />

the moisture content.<br />

Although the coating machine employs the same<br />

working principles as the earlier developed models<br />

(consecutive water input and intermittent chemical<br />

input after seed input), the rotator drum has a much<br />

greater capacity. Water and chemical inputs are controlled<br />

automatically.<br />

The coating mix can be set to ratios of 1:2 and 2:2<br />

(seeds to chemical, dry weight). Seed input modes<br />

can be set to 15 kg or 10 kg for 1:2 mixing or 15 kg or<br />

20 kg for 1:1 mixing.<br />

238 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Chemical hopper<br />

Water nozzle<br />

Agitator<br />

Cover<br />

Inclined-rotator<br />

drum<br />

Screw feeder<br />

Vent for products<br />

Water pump<br />

Controller<br />

Fig. 1. Side view of a developed automatic coating machine.<br />

<br />

<br />

The machine is contained within a shatterproof cover<br />

and was designed to be resistant to chemical dust<br />

particles.<br />

A vent on the side of the rotator drum enables the<br />

easy removal of the coated seeds.<br />

Overview of the coating machine. The coating machine,<br />

as shown in Figure 1, is composed of an inclined-rotator drum,<br />

a screw-type chemical feeder, a constant-pressure water nozzle<br />

with associated pump system, and a program-sequence controller.<br />

Combining a large-diameter agitator and a screw-type<br />

feeder, a stable chemical feeding performance was achieved.<br />

Several research experiments were carried out to test different<br />

input patterns of water and coating chemicals. Based on the<br />

results of these experiments, a prototype machine was produced.<br />

This prototype was equipped with an automatic sequencing<br />

system to control the input of water and chemicals into the<br />

inclined-rotator drum. Several performance tests were then<br />

carried out.<br />

Performance of the coating machine. The efficiency of<br />

the newly developed coating machine was compared with that<br />

of other more traditional models. Efficiency was evaluated<br />

based on the output of coated seeds, the mass of one coated<br />

seed, the hardness of the coating layer, and germination. The<br />

results of these tests showed that, in most respects, the newly<br />

developed coating machine performed similarly to the earlier<br />

models. Although differences were few between the models<br />

for coating time, the newly developed coating machine had<br />

double the capacity and was t<strong>here</strong>fore much faster. Much of<br />

the preparation work such as dewatering, preparation of chemicals,<br />

drying of coated seed, and packing of the coated product<br />

needed to be carried out either before or after coating using<br />

the old model. However, using the newly developed coating<br />

machine, all of these tasks could be carried out simultaneously.<br />

The precision drill seeder in flooded paddy fields<br />

Design. The depth at which the seeds were sown was known<br />

to be affected by the hardness of the soil surface in the field.<br />

<strong>Research</strong> was t<strong>here</strong>fore carried out to improve the seeding<br />

characteristics of the traditional drill seeder.<br />

The drill seeder mounts on a paddy vehicle had a<br />

working width of eight rows or more.<br />

A float is used to improve the accuracy of placing<br />

seeds at depth. A function was also provided to accurately<br />

control the angle of the covering plate.<br />

Seeding depth is adjusted depending on soil characteristics<br />

and the rice variety being planted.<br />

The machine adds fertilizer to the planted seeds.<br />

Overview of the seeding machine. The seeder, as shown<br />

in Figure 2, consists of an 8-row seeder mounted on a paddy<br />

vehicle. The seeder consists of a seeding part and a fertilizing<br />

part. This seeding machine was designed to improve seeding<br />

accuracy. As a high-performance fertilizing part is already in<br />

commercial use, commercial items were employed. The basic<br />

components of the furrow-opener and the covering plate are<br />

also commercially available, as is the traditional drill seeder.<br />

To overcome some of the problems associated with variations<br />

in soil-surface hardness, it was decided that the seeder<br />

Session 7: Improving efficiency through innovations in mechanization 239


Fig. 2. Developed drill seeder in a flooded paddy field.<br />

should be equipped with a soil-surface hardness sensor. Several<br />

experiments were carried out to investigate soil-surface<br />

hardness in relation to covering-plate angle. The results of these<br />

experiments showed that control of the covering-plate angle<br />

with a sensor could be used to overcome some of the soilcovering<br />

problems associated with differences in soil-surface<br />

hardness. The drill seeder was found to be more accurate for<br />

seeding depth than other traditional drill seeders. A float was<br />

also installed to increase the area of ground-surface contact,<br />

which significantly improved efficiency. The precision drill<br />

seeder was t<strong>here</strong>fore provided with a mechanism to control<br />

the covering-plate angle, a sensor for soil-surface hardness,<br />

and a large float with a two-step adjustable furrow-opener.<br />

Performance of the seeding machine. Field tests using<br />

the newly developed seeder were conducted at 14 sites in Japan.<br />

The results of these tests showed that the seeder was much<br />

more efficient than traditional seeding machines and led to a<br />

33% decrease in the number of surface seedlings and a 40%<br />

decrease in the number of lodged and floating seedlings. In<br />

addition, the working capacity was improved by 30% as a result<br />

of the wider working width and the higher operation speed<br />

compared with those of other traditional seeders.<br />

Commercialization and diffusion<br />

Since the development of an improved automatic coating machine,<br />

its use has increased dramatically. This machine, which<br />

assists with the direct sowing of rice, was found to improve<br />

crop emergence and establishment. The development of a precision<br />

drill seeder also contributes to crop emergence and establishment<br />

by decreasing the number of surface seedlings and<br />

floating seedlings, and decreasing lodging. Moreover, these<br />

newly developed machines have working properties similar to<br />

those of rice transplanters and will undoubtedly lead to more<br />

efficient rice fields because of the application of direct-sowing<br />

techniques in flooded paddy fields.<br />

The automatic coating machine has been marketed since<br />

1999 by HATSUTA Industrial Co., Ltd. and Yanmar Agricultural<br />

Equipment Co., Ltd. A precision drill seeder for use in<br />

flooded paddy fields has been available and marketed since<br />

2000 by Iseki & Co., Ltd.; Kubota Corporation; Mitsubishi<br />

Agricultural Machinery Co., Ltd.; and Yanmar Agricultural<br />

Equipment Co., Ltd. The use of these machines has increased<br />

dramatically in recent years. Some 250 coating machines and<br />

300 drill seeders are now being used. As a result of the increased<br />

use of these machines, the amount of land that can be<br />

used for direct sowing in flooded paddy fields will likely increase<br />

to three times the area that was available in 1998 (3,600<br />

ha).<br />

Notes<br />

Authors’ address: IAM, Bio-oriented Technology <strong>Research</strong> Advancement<br />

Institution, e-mail: Y_nishimura@affrc.go.jp.<br />

240 <strong>Rice</strong> is life: scientific perspectives for the 21st century


The rice direct-seeding system using multiple seed pellets<br />

in northern Tohoku<br />

Hiroyuki Sekiya, Hitoshi Ogiwara, Shoichi Kimura, Ryuji Otani, Yukio Yaji, Satoshi Morita, Tatsushi Togashi, and Hiroaki Watanabe<br />

In Japan, direct-seeding methods of rice are now being introduced<br />

to lower rice production costs. However, in the northeast<br />

area, direct seeding did not spread easily. Under chilly<br />

spring weather conditions, seed establishment in direct seeding<br />

was unstable in wet-seeded fields. Also, growth of broadcast<br />

rice is difficult to control. Moreover, good-tasting varieties,<br />

such as Akitakomachi (Oryza sativa L.), suffer from lodging.<br />

Recently, to solve these problems, a precise direct-seeding<br />

system was developed that stabilizes seedling establishment<br />

and lodging resistance in wet-seeded fields. We developed<br />

this new rice direct-seeding system with multiple seed<br />

pellets as one type of hill-seeding cultivation. This paper discusses<br />

the granulation method of multiple seed pellets, and<br />

paddy field cultivation tests using multiple seed pellets in wetseeded<br />

rice.<br />

Developing the granulation method of multiple seed pellets<br />

Developing a granulation method<br />

of a clay-rod cutting system<br />

We developed a granulation method of a clay-rod cutting system<br />

as a high-precision new granulation method (Fig. 1, Togashi<br />

et al 2004b). The clay-rod cutting method follows these steps:<br />

clay rods are injected from nozzles by a compressing pump,<br />

rice seeds are spread over the rods, reciprocating movement is<br />

given to the rods and seeds, and the rods are cut between cutting<br />

boards after the seeds are attached to the rod surface. The<br />

pellets are coated in Calper Fine Granule (an oxygen-generating<br />

product) using a coating machine. The round-shaped pellet<br />

of about 10 mm in diameter contains 5–7 seeds, made by<br />

the clay-rod cutting method. The working efficiency of the<br />

granulation instrument is about 60,000 pellets h –1 (0.3 ha h –1 ).<br />

This work needs about 1–2 people. The seeds used for granulation<br />

of multiple seed pellets are pregerminated to about 30%<br />

in pigeon-breasted conditions. The coated multiple seed pellets<br />

are put in a sealed plastic bag, and have been stored for<br />

about 1 month in refrigeration conditions (Ogiwara et al 2003).<br />

Before seeding work, 48 h of warm processing (25 °C) of<br />

multiple seed pellets were effective for bud stabilization under<br />

low-air-temperature conditions. Moreover, we have made<br />

a small and simple experimental granulation instrument of the<br />

clay-rod cutting system for general marketing by joint research<br />

with a private corporation. This granulation instrument was<br />

sharply miniaturized by simplifying the clay feeding device.<br />

However, the clay feeding unit needs to be improved for continuous<br />

operation. At present, no granulation instrument for<br />

multiple seed pellets is on the market.<br />

Clay supply device<br />

(A) Seed adhesion process<br />

Seed supply device<br />

Seeds are ad<strong>here</strong>d to the clay rod<br />

Sorting device<br />

(B) Granulation process<br />

Clay-rod cut device<br />

Ditch board conveyor<br />

Cloth belt for conveyance<br />

The clay rod is cut and rolled to the ditch<br />

board conveyor and seeds are rounded<br />

Fig. 1. The machine for manufacturing multiple seed pellets by the clay-rod cutting method (Togashi et al 2004a).<br />

Session 7: Improving efficiency through innovations in mechanization 241


Table 1. Yield components and lodging index for planted multiple seed pellets of cultivar Akitakomachi. a<br />

Seeding method Fertilizer application Yield Panicle no. Culm length Lodging index Pushing resistance<br />

(g N m –2 ) (g m –2 ) (m –2 ) (cm) (0–4) (g × cm)<br />

Seeding multiple Standard 5-3-2-2 610 434 80.3 0.83 1,635<br />

seed pellets<br />

Seeding multiple Large quantity 7-3-2-2 638* 451 84.6* 1.33 2,594<br />

seed pellets<br />

Drilling Standard 5-3-2-2 578 431 78.7 1.17 525<br />

Drilling Large quantity 7-3-2-2 638* 465 84.2* 2.17* 0<br />

Broadcast seeding Standard 5-3-2-2 548 387 80.3 2.08* 31<br />

Hill-seeding Standard 5-3-2-2 588 436 78.3 0.67 1,760<br />

Transplanting Standard 5-3-2-2 586 441 73.7* 0* 2,729<br />

a<br />

Multiple-seed-pellet seeding, hill-seeding, and transplanting were used with about 15-cm interrow spacing and 30-cm row spacing. Drilling was done with about 30-cm row<br />

spacing. Hill-seeding was done every five grains within 6 cm of the direction of a rider and 4-cm width. Seeding depth was about 10 mm. The multiple seed pellets of a clayrod<br />

cutting system were used for the test. Large-quantity fertilization added 2 g N m –2 using LP30 (coated urea-N). This was adjusted at 4 wk after seeding to seedling<br />

establishment at 22 shares m –2 , 5 seedlings per share, and 111 seedlings m –2 . Data are means of 3 sections. Yield is the weight of brown rice graded by grain size (>1.85<br />

mm in thickness) at 15% moisture. Pushing resistance was measured at 20-cm height at 18–20 d after heading. * indicates a significant difference as opposed to multipleseed-pellet<br />

seeding at 0.05 according to the Dunnet method (Morita et al 2004).<br />

Developing the granulation method<br />

using clay-powder<br />

To granulate more simply, we developed an alternative production<br />

method for multiple seed pellets. With this method,<br />

seeds and clay-powder were rounded together between a wet<br />

cellulose spongy sheet and a sponge-plastic mat on which hemispherical<br />

hollows were arranged. Seeds and clay-powder were<br />

made to condense and a spherical pellet was fabricated (Sekiya<br />

et al 2004b). The granulation instrument made as an experiment<br />

can be continuously granulating seed pellets by moving<br />

conveyor belts with a spongy sheet and a sponge plastic mat.<br />

Clay-powder for ceramic art is mixed with an oxygen-generating<br />

product (Calper) used for a binder by a weight ratio of 1:1.<br />

This granulation method is as efficient as the clay-rod cutting<br />

method. The pellet was about 9 mm in diameter and contained<br />

4 seeds (CV 49%) on average. This method is expected to be<br />

less costly than the clay-rod cutting method.<br />

Developing the seeding method of multiple seed pellets<br />

We developed a precision hill-seeding cultivation method using<br />

multiple seed pellets. Multiple seed pellets are sown by a<br />

planter, which is an improved commercial inclined-belt-type<br />

planter attached to a 4WD tractor or a transplanter (Togashi et<br />

al 2002). The inclined-belt-type planter drops multiple seed<br />

pellets on puddled soil with about 15-cm interrow spacing and<br />

30-cm row spacing. The multiple seed pellets were precisely<br />

hill-seeded at about 5-mm depth. Planting efficiency of an eightrow<br />

planter is about 0.35 ha h –1 . After seeding, water is drained<br />

for 1 to 2 wk depending on soil conditions. Then, water is<br />

refilled and the usual cultural management is practiced. This<br />

planter can be used for soybean and wheat seeding, and seeding<br />

accuracy is good.<br />

Multiple seed pellets could be broadcast by a duster or a<br />

radio-controlled helicopter (Togashi et al 2004a). However,<br />

the broadcasting method sometimes made a block of seeds and<br />

cracked pellets. In direct seeding by a duster, the unevenness<br />

of multiple seed pellets was also large compared with singlecoated<br />

seeds. The granulation method needs to be improved<br />

for the broadcasting method.<br />

Field experiments<br />

In precision cultivation tests in which the number of seedlings<br />

to be established was arranged, the resistance to lodging of<br />

multiple seed pellets was improved compared with broadcast<br />

seeding or drilling (Table 1, Morita et al 2004). In a large number<br />

of fertilization conditions, the difference between multipleseed-pellet<br />

seedling cultivation and drilling cultivation was<br />

remarkable. For labor-saving fertilizing work, we experimentally<br />

produced a sidedressing fertilizer for a planter and carried<br />

out cultivation tests by a single application of the fertilizer<br />

(Sekiya et al 2004a). A sidedressing fertilizer application<br />

showed that sufficient yield was obtained with a single fertilizer<br />

application by this machine.<br />

In 6 years of field cultivating, results of multiple-seedpellet<br />

seeding in Ohta test fields in Akita Prefecture indicated<br />

a stable brown rice harvest of 4.58–6.84 t ha –1 and less lodging<br />

using Akitakomachi (Sekiya et al 2004b). Since the amount<br />

of fertilization is decreasing now, t<strong>here</strong> were small lodging<br />

resistance differences in seeding multiple seed pellets and drilling,<br />

and t<strong>here</strong> were also small yield differences. When culm<br />

length was comparable in multiple-seed-pellet seeding, lodging<br />

was mitigated compared with drilling.<br />

As the farmers introduced the multiple-seed-pellet direct-seeding<br />

system, labor expenses, seedling materials, and<br />

fertilizer expenses could be reduced. However, the entire materials<br />

expense had only a small difference in multiple-seedpellet<br />

seeding and transplanting with the increase in the expense<br />

of Calper or additional herbicide. The merit of the multiple-seed-pellet<br />

seeding system for farmers was that it was as<br />

easy to manage as transplanting. On the other hand, farmers<br />

seldom felt a difference in resistance to lodging between the<br />

multiple-seed-pellet seeding system and the drilling system,<br />

242 <strong>Rice</strong> is life: scientific perspectives for the 21st century


according to the improvement in water and fertilizer management<br />

techniques, and the direct-seeding managerial technique.<br />

Conclusions<br />

We established the direct-seeding system, which employed the<br />

characteristics of multiple seed pellets efficiently. Farmers who<br />

use a type of direct seeding that is weak in lodging resistance<br />

can be provided with stable direct-seeding technology by introducing<br />

the precision hill-seeding cultivation method using<br />

multiple seed pellets (Yaji et al 2001). However, this cultivation<br />

method has not spread up to now. The reasons are considered<br />

to be that t<strong>here</strong> is still no commercial granulation instrument,<br />

t<strong>here</strong> is little cost reduction, the seeding efficiency of an<br />

inclined-belt-type planter is somewhat low, and t<strong>here</strong> are few<br />

differences in resistance to lodging with a drilling method for<br />

the present low yield level. Farmers who cooperated in cultivation<br />

tests mentioned that direct planting with very high seeding<br />

efficiency and high resistance to lodging was done by introducing<br />

multiple seed pellets into the broadcast-seeding system.<br />

Now, we are continuing to develop a simple and inexpensive<br />

granulation instrument suitable for the broadcast-seeding<br />

system and broadcast-seeding cultivation system tests using<br />

multiple seed pellets.<br />

References<br />

Morita S, Sekiya H, Yaji Y, Ogiwara H. 2004. Evaluation of lodging<br />

resistance by the chain method and improvement of the cultivation<br />

method. Report of integrated research for agriculture<br />

(NARCT). 18:32-33.<br />

Ogiwara H, Otani R, Yaji Y, Sekiya H. 2003. Emergence and seedling<br />

establishment of rice multiple seed pellet. Jpn. J. Tohoku<br />

Crop Sci. 46:7-8.<br />

Sekiya H, Kimura S, Ogiwara H, Otani R, Nisiwaki K, Watanabe H.<br />

2004b. Development of granulation method of the multiple<br />

seed pellet using clay-powder. Jpn. J. Farm Work <strong>Research</strong><br />

39 (extra issue) 1:47-48.<br />

Sekiya H, Ogiwara H, Morita S, Suzuki Y, Yaji Y, Watanabe H. 2004a.<br />

Result of a direct-seeding cultivation examination at Ohta test<br />

field in Akita prefecture. Report of integrated research for<br />

agriculture (NARCT). 18:38-44.<br />

Togashi T, Amaha K, Nishiwaki K, Yaji Y, Kimura S, Kikuchi Y.<br />

2002. Development of the granulation and seeding technology<br />

of rice multiple seed pellet. Part 5. Jpn. J. Tohoku Agric.<br />

Implem. Mach. 49:15-18.<br />

Togashi T, Ito N, Nishiwaki K, Kimura S, Amaha K, Matuo K, Otani<br />

R, 2004a. Development of seeding method of multiple seed<br />

pellet. Report of integrated research for agriculture (NARCT).<br />

18:50-53.<br />

Togashi T, Ito N, Nishiwaki K, Kimura S, Amaha K, Otani R. 2004b.<br />

Development of simple granulation method of multiple seed<br />

pellet at low cost. Report of integrated research for agriculture<br />

(NARCT). 18:45-49.<br />

Yaji Y, Togashi T, Morita S, Sekiya H. 2001. <strong>Rice</strong> direct-seeding<br />

system using multiple seed pellet in a cold district. Jpn. J.<br />

Agric. Hort. 76:46-54.<br />

Notes<br />

Authors’ addresses: Hiroyuki Sekiya, Shoichi Kimura, and Ryuji<br />

Otani, National Agricultural <strong>Research</strong> Center for Tohoku Region<br />

(NARCT), NARO, Japan, e-mail: sekiya@affrc.go.jp;<br />

Hitoshi Ogiwara, Agriculture, Forestry, and Fisheries <strong>Research</strong><br />

Council; Yukio Yaji, headquarters of NARO; Satoshi Morita,<br />

National Agricultural <strong>Research</strong> Center for Kyushu Okinawa<br />

Region (KONARC); Tatsushi Togashi and Hiroaki Watanabe,<br />

National Agricultural <strong>Research</strong> Center (NARC).<br />

Wrap-up of Session 7<br />

This session covered specific concerns related to the improvement<br />

of efficiency through innovations in mechanization for boosting<br />

rice production. Some 90% of the total rice production is<br />

produced from Asian countries. Invited speakers came from Korea,<br />

China, and the Philippines.<br />

Professor N. Ito discussed the important role of rice as a<br />

key resource to save our planet. He said that the world faces<br />

various global issues, or tetralemma. The rice world requires a<br />

sufficient food supply, particularly including rice, because the world<br />

population is increasing markedly. On the other hand, globalscale<br />

dependency on fossil fuel must be minimized to prevent<br />

global warming. These problems can be solved only by improving<br />

rice production; hence, mechanization plays a vital role in this<br />

endeavor as a force multiplier compensating for the labor shortage.<br />

In addition, N. Ito introduced new, unique technologies: a<br />

combine husker, combine harvester equipped with a pivot turn<br />

mechanism, brown rice dryer, and others. Finally, he stressed<br />

that rice has good potential to reduce tetralemma as an environmentally<br />

friendly fuel.<br />

W.P. Park reviewed the current status of agricultural mechanization,<br />

which progressed rapidly in paddy rice production. As a<br />

result, Korean agricultural policy has contributed to self-sufficiency<br />

in food and improvement of welfare in rural society. But, Korean<br />

farmers have some problems to be solved because of the small<br />

farming scale and aging society. To solve these problems, Korean<br />

rice farming needs new strategic studies of advanced technology<br />

development to lower production costs, enhance the quality of<br />

products, and use precision agriculture and farm robots.<br />

Professor Y. Li analyzed the development of rice mechanization,<br />

and noted that mechanization of planting and harvesting<br />

is relatively less since farm mechanization does not go well with<br />

agronomy because of vast territory with complex agricultural situations.<br />

China will concentrate on developing rice planting and<br />

drying mechanization techniques, especially for new equipment,<br />

Session 7: Improving efficiency through innovations in mechanization 243


including the high-speed transplanter and small-quantity directsowing<br />

machine for hybrid rice.<br />

E. Bautista explained the rotary rice reaper to be developed<br />

in the Phil<strong>Rice</strong>-JICA collaborative project. <strong>Rice</strong> harvesting<br />

using the traditional sickle remains a laborious activity. Owing to<br />

its simple design and ease of manufacture and maintenance,<br />

the new reaper design has high potential in the Philippines and<br />

in other Asian countries. Though the engine output is higher than<br />

that of imported units, it is the most realistic selection when<br />

considering repairs. It was compatible with other technologies<br />

that have been proven effective for farmers and friendly to the<br />

rice communities in the village. He also mentioned the challenge<br />

to develop a tractor-mounted type.<br />

Following the invited speakers, four Japanese researchers<br />

introduced newly developed technologies.<br />

H. Kitagawa explained the long-mat seedling culture system<br />

for labor-saving and comfortable work. The weight of the<br />

long-mat is around one-fifth that of a conventional soil seedbed.<br />

Accordingly, the long-mat system eliminates the need to carry<br />

nursery boxes many times from sowing to transplanting. Longmat<br />

technology makes loading and transplanting processes for<br />

seedlings easy. The required working hours for transplanting decreased<br />

to one-half, and this enabled a one-person operation.<br />

Y. Nagasaka discussed an automated rice transplanter and<br />

autonomous guidance system equipped with a GPS and fiberoptic<br />

gyro-sensor to achieve more efficient unmanned operation.<br />

Accuracy was enough for rice transplanting operations, but was<br />

not always enough for doing other work. A newly designed transplanter<br />

could be applicable, but, for seedling recovery and traveling<br />

on the road, and especially production costs, the adoption of<br />

a commercialized transplanter is recommendable.<br />

Y. Nishimura explained a new rice seed-coating machine<br />

and high-precision drilling machine. As for the direct-sowing machine,<br />

the precision drill seeder equipped with a soil-surface hardness<br />

sensor was able to stabilize seeding depth. These two machines<br />

have already been commercialized and they helped to<br />

extend the direct-sowing area.<br />

Finally, a general discussion covered direct sowing of rice,<br />

precision farming, autonomous technologies, and energy use of<br />

rice. The following points were highlighted:<br />

1. The proportion of direct-sowing area is about 6–7% in<br />

Korea, and that of Japan is less than 1%. China will<br />

tend to increase this area. However, the development<br />

of a new precision drilling machine or demand for cost<br />

reduction will probably promote a further increase in<br />

direct-sowing area.<br />

2. In Korea, precision farming (PF) research is conducted<br />

in collaboration with a U.S. university as well as counterparts<br />

in Japan. The effectiveness of PF had already<br />

been demonstrated on large-scale farms like those in<br />

the U.S., w<strong>here</strong>as the compatibility of environmental<br />

conservation and profitability for farmers was not entirely<br />

clarified in small-scale farming, including that of<br />

Japan. It is better to cooperate among Asian countries<br />

to create an Asian model for enhancing value-added<br />

productivity.<br />

3. For robot research, most participants, except Korea and<br />

Japan, have less concern about autonomous technologies.<br />

But, these technologies are expected as measures<br />

to cope with the labor shortage, or to eliminate laborious<br />

work in agriculture. <strong>Research</strong> on and development<br />

of this type of agricultural machinery will be accelerated<br />

in Korea and Japan.<br />

4. In Japan, rice policy reform is being steadily promoted<br />

since rice consumption per capita is decreasing. Although<br />

the use of rice as an energy crop was not discussed<br />

in the session, it seems to be one alternative<br />

besides an adjustment in rice production.<br />

5. From a global viewpoint, the amount of rice consumption<br />

exceeds that of production, which causes an imbalance<br />

between supply and demand. In addition, because<br />

of meteorological disasters such as droughts and<br />

floods, we need to realize the importance of stabilizing<br />

rice supply and enhancing productivity. Mechanization<br />

will play a major role in this in the future as well.<br />

As a whole, this session examined the wide diversity in<br />

Asian rice farming. This discussion proved to be a good opportunity<br />

to exchange information for international collaborative research<br />

activities. We appreciate the cooperation of Professor<br />

Koike, the chairperson from the Japanese Society of Agricultural<br />

Machinery, and all the participants.<br />

244 <strong>Rice</strong> is life: scientific perspectives for the 21st century


SESSION 8<br />

Improving rice quality<br />

CONVENER: U. Matsukura (NARO


The chemical basis of rice end-use quality<br />

Kshirod R. Bhattacharya<br />

<strong>Rice</strong> is among the top food grains in the world and is the most<br />

important one as human food. It is grown widely on all continents<br />

and under all agroclimatic conditions. This wide adaptation<br />

has led to the evolution of thousands of varieties of rice<br />

having diverse cooking, eating, and product-making characteristics.<br />

<strong>Rice</strong> palatable to one ethnic group or suitable for one<br />

product may not be so for others. One striking example of this<br />

diversity is the unique geographical shift in the quality of rice<br />

in Asia, the home of the world’s rice. <strong>Rice</strong> grown in northern<br />

and eastern Asia cooks soft and sticky, while that in southern<br />

Asia is completely different, for it cooks firm and fluffy, with<br />

that in Southeast Asia coming in between.<br />

<strong>Research</strong> on divergence in rice quality<br />

This wide varietal divergence in rice quality has attracted the<br />

attention of researchers for close to a century. In fact, this subject<br />

has been one of the most intensively investigated topics in<br />

cereal chemistry. The work can be divided into three phases.<br />

The first phase, up to the end of the 1940s, was merely a period<br />

of initiation. The work, carried out mostly in India, was<br />

sporadic and confined largely to studying the absorption of<br />

water by rice during cooking.<br />

The second phase, the period of data accumulation,<br />

started soon after World War II, when t<strong>here</strong> was a sudden spurt<br />

of research activity in the subject in the United States, Japan,<br />

Germany, Italy, Spain, and France. This was followed shortly<br />

afterward by intensive and sustained research at the newly set<br />

up <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong> (<strong>IRRI</strong>) in the Philippines<br />

as well as at the Central Food Technological <strong>Research</strong><br />

<strong>Institute</strong> (CFTRI) in Mysore, India.<br />

This work led to a mass of data. The main conclusion<br />

was that the amylose starch content of rice was the single largest<br />

determinant of its end-use quality. The greater the amylose,<br />

the firmer was the rice texture when cooked and viceversa.<br />

However, it was also realized that amylose, though necessary,<br />

was not sufficient; other secondary factors were involved.<br />

In fact, pinpointing these secondary factors was the<br />

main brunt of research during this phase. Many factors were<br />

suggested: hydration power, starch-iodine blue value, gelatinization<br />

temperature (GT), alkali digestion score, Brabender<br />

viscograph pattern, mobility of an alkaline rice-flour gel (gel<br />

consistency), as well as hot-water-insoluble amylose. This last<br />

item has an interesting history. While investigating the starchiodine<br />

blue value of rice varieties, my school at CFTRI realized<br />

that it was nothing but the water-soluble amylose of rice.<br />

<strong>Research</strong>ers then observed that the solubility of amylose of<br />

rice varieties fell into three distinct groups. The Taiwanese<br />

high-amylose, low-GT, dwarfing-gene donors and many of their<br />

progenies had an amylose solubility of only about 35%; many<br />

high-amylose, intermediate-GT varieties of South Asia had<br />

about 45%; all other varieties showed about 55% solubility.<br />

The calculated insoluble amylose content of rice on this basis<br />

(total minus soluble amylose) showed a striking correlation<br />

with rice texture, particularly in the high-amylose group, which<br />

was t<strong>here</strong>by divided into three distinct subgroups showing distinct<br />

texture after cooking (Bhattacharya et al 1978).<br />

Taking the above secondary factors into consideration,<br />

it appeared by the mid-1980s that the Brabender paste breakdown,<br />

gel consistency, and insoluble amylose, along with amylose<br />

content of rice, could characterize its end-use quality very<br />

well (Sowbhagya et al 1987). But the chemical basis was unclear.<br />

Evidently, these approaches had reached the limit of their<br />

potential and a new approach was necessary.<br />

A new approach<br />

The third phase started at this juncture in the mid-1980s with a<br />

complete shift in the prevailing paradigm. Chemists’ understanding<br />

of the structure of starch, especially amylopectin, has<br />

been all along going through a metamorphosis. The chain structure<br />

of amylopectin came under serious reexamination from<br />

the end of the 1970s with the use of various starch-hydrolyzing<br />

enzymes and of gel permeation chromatography (GPC).<br />

Biliaderis et al (1981), for example, showed that the chain profile<br />

of legume starches varied significantly from one species<br />

to another. Again, Professors Fuwa and Hizukuri in Japan<br />

showed significant variation in amylopectin chain structure<br />

among various starches. Chinnaswamy in my laboratory at<br />

CFTRI at this time observed with surprise that the GPC-separated<br />

amylopectins of rice starch gave a varying shade of blue<br />

color with iodine. What is more, the absorption maxima (λmax)<br />

of these iodine complexes showed excellent correlation with<br />

the texture of the corresponding rice varieties after cooking<br />

(Fig. 1). These results showed that (1) unlike as so far believed,<br />

amylopectin also bound iodine, (2) this binding was<br />

apparently caused by the presence of some very long chains in<br />

it, (3) rice varieties t<strong>here</strong>fore apparently differed in their amylopectin<br />

chain structure, and (4) the apparent amylose content<br />

of starch as determined by reaction with iodine was always an<br />

overestimation, part of the value being contributed by amylopectin.<br />

Hizukuri in collaboration with <strong>IRRI</strong> scientists shortly<br />

t<strong>here</strong>after showed that the chain profile of rice amylopectin<br />

indeed differed from variety to variety, with high-amylose rice<br />

having more very long chains than low-amylose rice, with intermediate-amylose<br />

rice coming in between (Hizukuri et at<br />

1989). Radhika Reddy et al (1993) later confirmed these findings<br />

and also showed that high insoluble-amylose rice amylopectin<br />

not only had more long chains but also that these chains<br />

seemed to be largely located externally in the molecule and<br />

246 <strong>Rice</strong> is life: scientific perspectives for the 21st century


lmax of fraction 1 (iodine) (nm)<br />

r = 0.983***<br />

600<br />

580<br />

A<br />

Jaya<br />

(I)<br />

0 min 60 min 0 min 60 min<br />

I<br />

B<br />

560<br />

S317<br />

(III)<br />

III<br />

540<br />

Intan<br />

(V)<br />

V<br />

520<br />

0 5 10 15 20<br />

Insoluble amylose in rice (% d.b.)<br />

Cooked-rice hardness<br />

T65<br />

(VII)<br />

VII<br />

Fig. 1. Variation in λmax of rice amylopectiniodine<br />

complex. Thirteen rice varieties having<br />

different insoluble amylose contents were fractionated<br />

over Sepharose 2B and the gel-excluded<br />

fraction 1 (amylopectin) was reacted<br />

with iodine. The absorption maxima of the blue<br />

complexes were read. d.b. = dry basis. (Adapted<br />

from Chinnaswamy and Bhattacharya 1986.)<br />

Fig. 2. Photomicrographs of starch granules in 12% rice-flour pastes<br />

of four varieties (types I, III, V, VII, having from very high to low<br />

insoluble amylose). Flours were pasted by heating up to 95 °C. (A)<br />

Light microscopy, (B) scanning electron microscopy. For each, left<br />

column: just pasted (0 min); right column: maintained at 95 °C for<br />

another 60 min. After 60 min, the granules are hardly affected in<br />

type I but are completely degraded in type VII. (Reproduced from<br />

Sandhya Rani and Bhattacharya 1995.)<br />

vice-versa. Work in many laboratories worldwide (Korea, UK,<br />

Japan, Taiwan-China) subsequently confirmed these findings.<br />

The influence of amylopectin<br />

Clearly, the texture of cooked rice was closely correlated with<br />

the relative abundance of long chains in its amylopectin. The<br />

more long chains, the firmer was the rice when cooked and<br />

vice-versa. The rationale was explained by rheological and<br />

microscopical studies in my laboratory. It was shown that the<br />

presence of abundant long chains in the amylopectin led, apparently<br />

by mutual interaction, to strong and resilient starch<br />

granules that resisted swelling and breakdown, w<strong>here</strong>as their<br />

absence led to weak and fragile granules that broke down easily<br />

during cooking (Fig. 2).<br />

Thus, after more than 50 years of intensive research, the<br />

texture of cooked rice and other rice end-use quality has been<br />

attributed primarily to the relative abundance of long chains<br />

in its amylopectin. Interestingly, other work has shown that<br />

the bulk of rice starch consists of amylopectin, true amylose<br />

being not more than about 10% in it (Ramesh et al 1999).<br />

Other factors<br />

Very recent work, primarily in Japan, has shown that the GT<br />

of rice starch, too, is correlated with the chain structure of<br />

amylopectin. The proportion of very short chains among the<br />

overall short chains in amylopectin is negatively correlated<br />

with the GT (Umemoto et at 2002). However, the implication<br />

of this finding in terms of rice quality is uncertain. From all<br />

accounts, rice GT does not seem to have a significant influence<br />

on its cooking-eating characteristics.<br />

A few other factors may affect rice-use value in a small<br />

way. Protein content of rice has long been thought to influence<br />

rice-use quality. This was first proposed by Spanish workers<br />

in the 1950s and 1960s. Subsequently, Japanese and other<br />

workers supported this contention. Recently, Ohtsubo and his<br />

group at the Food <strong>Research</strong> <strong>Institute</strong> in Japan have shown that<br />

the surface hardness of cooked rice especially is related to protein<br />

(Okadome et al 1999). American scientists have shown<br />

that rice protein may have some relationship to its paste properties.<br />

In addition, the content of free amino acids and sugars<br />

in rice has been suggested by Japanese scientists to affect the<br />

palatability and flavor of rice after cooking.<br />

References<br />

Bhattacharya KR, Sowbhagya CM, Indudhara Swamy YM. 1978.<br />

Importance of insoluble amylose as a determinant of rice quality.<br />

J. Sci. Food Agric. 29:359-364.<br />

Biliaderis CG, Grant DR, Vose JR. 1981. Structural characterization<br />

of legume starches. 1. Studies on amylose, amylopectin and<br />

beta-limit dextrins. Cereal Chem. 58:496-502.<br />

Chinnaswamy R, Bhattacharya KR. 1986. Characteristics of gel-chromatographic<br />

fractions of starch in relation to rice and expanded<br />

rice-product qualities. Staerke 38:51-57.<br />

Session 8: Improving rice quality 247


Hizukuri S, Takeda Y, Maruta N, Juliano BO. 1989. Molecular structures<br />

of rice starch. Carbohydr. Res. 189:227-235.<br />

Okadome H, Toyoshima H, Ohtsubo K. 1999. Multiple measurements<br />

of physical properties of individual cooked rice grains<br />

with a single apparatus. Cereal Chem. 76:855-860.<br />

Radhika Reddy K, Ali SZ, Bhattacharya KR. 1993. The fine structure<br />

of rice-starch amylopectin and its relation to the texture<br />

of cooked rice. Carbohydr. Polym. 22:267-275.<br />

Ramesh M, Ali SZ, Bhattacharya KR. 1999. Structure of rice starch<br />

and its relation to cooked-rice texture. Carbohydr. Polym.<br />

38:337-347.<br />

Sandhya Rani MR, Bhattacharya KR. 1995. Microscopy of rice starch<br />

granules during cooking. Staerke 47:334-337.<br />

Sowbhagya CM, Ramesh BS, Bhattacharya KR. 1987. The relationship<br />

between cooked-rice texture and the physicochemical<br />

characteristics of rice. J. Cereal Sci. 5:287-297.<br />

Umemoto T, Yano M, Satoh H, Shomura A, Nakamura Y. 2002.<br />

Mapping of a gene responsible for the difference in amylopectin<br />

structure between japonica-type and indica-type rice varieties.<br />

Theor. Appl. Genet. 104:1-8.<br />

Notes<br />

Improving rice grain quality in Thailand<br />

Kunya Cheaupun, Sunantha Wongpiyachon, and Ngamchuen Kongseree<br />

Author’s address: <strong>Rice</strong> <strong>Research</strong> and Development Centre, 2633, II<br />

Main Road, V.V. Mohalla, Mysore 570002, India, e-mail:<br />

krb@rrdc.net.<br />

<strong>Rice</strong>, the most important crop in Thailand, was expected to<br />

alleviate the economic problem of jobless people in 1998.<br />

During 1998-2003, rice production obtained from main and<br />

second crops was 22–26 million tons annually. About 6.8–7.3<br />

million t of milled rice were exported in 1999-2003. Approximately<br />

50% of the commodity was used domestically, and the<br />

surplus exported to foreign markets. In 2003, Thai rice exports<br />

made up about 27% of the world market. Among this<br />

proportion of exports, good-quality rice represented 46%. This<br />

included Thai aromatic rice or Jasmine rice. Thus, Thailand’s<br />

rice program is projected to enhance production, sufficient for<br />

self-consumption and for export. <strong>Rice</strong> with good grain quality<br />

must aim to meet the requirements of both domestic and foreign<br />

consumers.<br />

Improving quality<br />

<strong>Rice</strong> quality is considered to have two general aspects:<br />

1. Milling, cooking, and processing qualities, which refer<br />

to suitability of the grain for a particular end-use.<br />

2. Physical quality, which means cleanliness, soundness,<br />

and being free from foreign materials. Usually, physical<br />

quality and milling, cooking, and processing qualities<br />

are interrelated in that certain market grades of<br />

rice are more suitable than others for consumer products.<br />

The quality of Thai rice has long been well known in<br />

international markets. The quality of rice is mainly defined as<br />

long and slender. Breeding selection has incorporated grain<br />

quality into varietal improvement with other agronomic characters.<br />

<strong>Rice</strong> with long, slender, and translucent grain is preferable.<br />

Different varieties produce a different quality of cooked<br />

rice; glutinous rice is very sticky, and steaming is always applied<br />

to prepare the cooked product. Nonglutinous rice may<br />

be soft and slightly sticky before cooking, and rather soft or<br />

hard in its texture when cooked. The main factor influencing<br />

this property is amylose content. The low-amylose type (less<br />

than 20% amylose) always has a soft texture and is sticky when<br />

cooked. The intermediate-amylose type (21–25%) produces<br />

rather soft cooked rice, w<strong>here</strong>as the high-amylose type has a<br />

hard texture. To obtain an optimum cooked-rice quality, highamylose<br />

milled rice requires more cooking water than that<br />

having a lower amylose content. To cook rice, the cooking<br />

time depends on the gelatinization temperature of the starch<br />

(gel. temp.) in milled grain. On the basis of gel temperature,<br />

rice varieties can be classified into three groups: low, intermediate,<br />

and high. Thai rice has a great variation in cooked-rice<br />

(Table 1). We have glutinous rice and various types of<br />

nonglutinous rice, providing an advantage to satisfy the preferences<br />

of different groups of rice consumers. Aroma is a special<br />

characteristic and is considered to be a special quality.<br />

Quality testing is t<strong>here</strong>fore primarily a matter of determining<br />

whether the rice is suitable for a particular use and whether it<br />

meets specific requirements of cleanliness and purity.<br />

Furthermore, milling yields are based on the amount of<br />

whole milled kernels and all sizes of broken kernels obtainable<br />

from a unit of rough rice. Many factors influence milling<br />

yield; the miller must also judge the quality of rice for milling<br />

on the basis of variety, moisture content, the presence of red<br />

rice, peckiness (parboiled kernels with obviously black or dark<br />

brown area) and other kernel damage, foreign seeds and other<br />

material, chalky kernels, and mustiness or other undesirable<br />

odors (Webb and Stermer 1972).<br />

The world rice market classifies the commodity into six<br />

basic types: (1) predominantly indica, high-quality, long-grain<br />

raw milled rice; (2) predominantly indica, medium-quality,<br />

long-grain raw milled rice; (3) japonica short- or medium-grain,<br />

raw milled rice; (4) parboiled rice; (5) aromatic (fragrant) rice;<br />

and (6) waxy (glutinous) rice. Among these types, five have a<br />

significant role in the international market. These groups can<br />

also be subdivided depending on consumer preferences. Each<br />

type has different markets and, within each type, t<strong>here</strong> are spe-<br />

248 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. Grain characteristics of some Thai rice varieties.<br />

Varieties Grain length % amylose Gelatinization<br />

(mm)<br />

temp.<br />

Soft-sticky cooked rice<br />

KDML 105 a 7.4 12–18 Low<br />

RD 15 a 7.5 14–18 Low<br />

RD 21 7.3 17–19 Low<br />

Khao’ Jow Hawm 7.8 18–19 Low<br />

Khlong Luang1 a – – –<br />

Khao’ Jow Hawm 7.7 18–19 Low<br />

Suphan Buri a – – –<br />

Pathum Thani1 a 7.6 14–19 Low<br />

Rather soft cooked rice<br />

Khao Pahk Maw 148 7.7 24–26 Intermediate<br />

RD23 7.3 23–27 Intermediate<br />

Suphanburi 60 7.5 20–26 Low<br />

Hard cooked rice<br />

Leuang Pratew 123 7.4 28–32 Low-intermediate<br />

Suphanburi 1 7.3 29 Intermediate<br />

Suphanburi 90 7.4 27–30 Low-intermediate<br />

Chai Nat 1 7.4 27–30 Intermediate<br />

Pathum Thani 60 a 7.5 27–32 Low<br />

a<br />

Aromatic rice.<br />

cial quality demands for specific uses. In general, consumers<br />

view rice in an uncooked or unprocessed state and make judgments<br />

on its quality. To meet market standards, major rice exporters<br />

and importers have established official grades to identify<br />

the relative quality of the commodity.<br />

Thai rice standards<br />

As the major rice exporter, Thailand established Thai <strong>Rice</strong><br />

Standards B.E. 2540. These standards were revised in 1997<br />

through a notification by the Ministry of Commerce. These<br />

rice standards described the minimum specifications of rice in<br />

each type and grade for domestic and international trade. They<br />

include white rice (milled rice), cargo rice (Loonzain rice,<br />

brown rice, or husked rice), white glutinous rice (milled waxy<br />

rice), and parboiled rice. The judgment is based on physical<br />

examination of the grain considering the following categories.<br />

<strong>Rice</strong> classification<br />

Classes of rice refer to the unbroken kernels of various length,<br />

which are a mixture in accordance to the proportion. They can<br />

be divided into four groups as follows:<br />

Class 1 long grain more than 7.0 mm<br />

Class 2 long grain 6.6–7.0 mm<br />

Class 3 long grain 6.2–6.6 mm<br />

Short grain Less than 6.2 mm<br />

High-quality rice is composed of class 1 long grain in a<br />

greater proportion than that of the lower grades. The percentage<br />

of this grain becomes less as the grade becomes lower.<br />

Grain composition<br />

Grain composition is whole kernels, head rice, and broken rice.<br />

Whole kernels are unbroken kernels and kernels retaining<br />

9/10 of the grain unbroken. The size of the broken rice depends<br />

on the rice grade.<br />

High-quality rice not only contains a higher proportion<br />

of class 1 long grain than that of other lower grades, but the<br />

sizes of head rice and broken kernels are also longer. Small<br />

broken rice (C1) that passed through a round-hole metal sieve<br />

no. 7 (0.79 mm in diameter and 1.75 mm in thickness) is not<br />

allowed to mix with 100% class white rice.<br />

<strong>Rice</strong> and other matter<br />

Some allowances are specified for each grade of rice, as follows.<br />

Red kernel: rice having red bran covering the kernel<br />

wholly or partly.<br />

Yellow kernel: rice having some parts of the kernels<br />

obviously turned yellow.<br />

Chalky kernel: nonglutinous rice having an opaque<br />

area of more than 50% of the kernel.<br />

Damaged kernel: rice kernels obviously damaged by<br />

moisture, heat, insects, or something else.<br />

Foreign matter: including underdeveloped grain, immature<br />

kernels, excess kernels, other seeds, rice husk,<br />

and bran.<br />

Black kernels (whole kernels), partly black kernels<br />

(more than 25% of the kernel becomes black), and<br />

pecked kernels (less than 25% become pecked) are<br />

limited in the parboiled rice standard.<br />

Paddy: glutinous rice in nonglutinous rice or<br />

nonglutinous rice in glutinous rice is also specified in<br />

all types of rice standards.<br />

Milling degree<br />

This is divided into four levels: extra well milled, well milled,<br />

reasonably well milled, and ordinarily well milled.<br />

Moisture content<br />

The moisture content of rice of all types and grades is specified<br />

as not exceeding 14%.<br />

The adulteration problem of Thai Jasmine rice<br />

The popularity of Thai aromatic or Jasmine rice increased remarkably<br />

from 1992 to 1997. The annual export quantities of<br />

aromatic rice were as high as 1.06–1.45 million t. It represented<br />

20–27% of the total quantity exported. The commodity<br />

was produced from varieties KDML 105 and RD15. Production<br />

was only 3–4 million t of paddy, which was not enough<br />

for market demand. This brought about an increase in the paddy<br />

price. The grains of these two varieties result in soft and sticky<br />

cooked rice that is too sticky for some consumers. The high<br />

price and this unfavorable cooked-rice texture brought about<br />

a blending of grain of aromatic rice with that of other varieties<br />

having a similar grain appearance. In general, these practices<br />

Session 8: Improving rice quality 249


are in accordance with agreements between buyers and sellers.<br />

The grain of rice varieties used for blending comes from<br />

RD23 (intermediate amylose content, intermediate gelatinization<br />

temperature) and Chai Nat 1 (high amylose content, intermediate<br />

gel temperature). Blended rice resulted in changes in<br />

cooked-rice quality and introduced complaints from some customers<br />

who expected to have soft-texture aromatic cooked rice.<br />

To satisfy Thai aromatic rice consumers, the government took<br />

the following action.<br />

Establishment of Thai Hom Mali <strong>Rice</strong> Standards B.E. 2544<br />

Thai aromatic rice is always exported using the name Thai<br />

Hom Mali <strong>Rice</strong>, Jasmine <strong>Rice</strong>, or Thai Fragrant <strong>Rice</strong>. The commodity<br />

was certified in accordance with Thai <strong>Rice</strong> Standards<br />

through physical measurements. It is difficult to classify aromatic<br />

rice grain separate from other white rice. For the benefit<br />

of Thai exporters, the Ministry of Commerce, with cooperation<br />

from the Ministry of Agriculture, cooperatives, and the<br />

private sector, established a notification on the subject: Thai<br />

Hom Mali <strong>Rice</strong> Standards B.E. 2544. These standards comprised<br />

both physical and chemical analyses. The name Hom<br />

Mali was chosen and is well known among Thais in the domestic<br />

market. The standards disclose the name of Thai Hom<br />

Mali to the public, like Basmati of India and Pakistan. The<br />

standards concern the following categories:<br />

1. Thai Hom Mali <strong>Rice</strong> means cargo rice and white<br />

rice obtained from paddy of nonglutinous fragrant rice<br />

varieties that are produced in Thailand, and certified<br />

by the Ministry of Agriculture and Cooperatives, such<br />

as Khao Dowk Mali 105 and RD15. This rice has a<br />

natural fragrant aroma depending on whether it is new<br />

or aged rice. The cooked rice kernels have a tender<br />

texture.<br />

2. Characteristics and size of rice kernels. The rice<br />

kernels are long grain: the average length of unbroken<br />

kernels shall not be less than 7.00 mm, with a<br />

length/width ratio not less than 3.2.<br />

3. Chemical properties of the grain indicate its amylose<br />

content, 13–18%, at 14% moisture content.<br />

4. Types of rice. T<strong>here</strong> are two types: white rice and<br />

cargo rice.<br />

5. Quality of Thai Hom Mali <strong>Rice</strong>. If it has a mixture<br />

of other rice, the other rice shall not exceed 8.0% by<br />

weight.<br />

6. Grades of rice are defined in accordance with a notification<br />

from the Ministry of Consumer Subjects:<br />

<strong>Rice</strong> Standards 2540, except for grain classifications,<br />

which are divided as follows:<br />

White rice: 100% grade A, 100% grade B, 100%<br />

grade C, 5%, 10%, and 15% broken rice A1 extra<br />

super, and broken rice A1 super.<br />

Cargo rice: 100% grade A, 100% grade B, 100%<br />

grade C, and 5%, 10%, and 15%.<br />

7. White rice and cargo rice that have mixtures of<br />

other rice exceeding 8.0% by weight shall not be<br />

considered as Thai Hom Mali <strong>Rice</strong>. Using other or<br />

previous trade names, exporters can still do business.<br />

The advantage of these standards is to ensure that both<br />

exporters and importers meet the standards for rice quality of<br />

Thai Hom Mali. Amylose content for low-amylose rice is 15–<br />

19%. This refers to soft and sticky cooked rice. Testing for<br />

other rice based on alkali spreading value is used to detect<br />

grain of RD 23 and Chai Nat 1.<br />

Bibliography<br />

Agricultural statistics of Thailand, crop year 2003/2004. Center for<br />

Agricultural Information, Office of Agricultural Economics,<br />

Ministry of Agriculture and Cooperatives, Bangkok, Thailand.<br />

www.oae.go.th.<br />

Department of Foreign Trade 2545. Thai <strong>Rice</strong> Standards. Notification<br />

of Ministry of Commerce. The Royal Gazette, Vol. 114,<br />

Section 31D,17 April, B.E. 2540, 1997.<br />

Department of Foreign Trade 2545. Thai Hom Mali <strong>Rice</strong> Standards.<br />

Notification of Ministry of Commerce. The Royal Gazette,<br />

Vol. 119, Special Part 55d, 21 June, B.E. 2545, 2002.<br />

Webb BD, Stermer RA. 1972. Criteria of rice quality. In: Houston<br />

DF, editor. <strong>Rice</strong>: chemistry and technology. St. Paul, Minn.<br />

(USA): American Association of Cereal Chemists. p 102-139.<br />

Notes<br />

Authors’ addresses: Kunya Cheaupun and Sunantha Wongpiyachon,<br />

Pathumthani <strong>Rice</strong> <strong>Research</strong> Center, Thanyaburi, Pathumthani<br />

12110, Thailand; Ngamchuen Kongseree, Office of the Senior<br />

Experts, Department of Agriculture, Bangkok 10900,<br />

Thailand, e-mail: ckunya@hotmail.com.<br />

250 <strong>Rice</strong> is life: scientific perspectives for the 21st century


New tools for understanding starch synthesis<br />

Melissa Fitzgerald, Jeffrey Castro, Rosa Paula Cuevas, and Robert Gilbert<br />

Starch is the major component of rice grain, and its structure<br />

contributes significantly to the “quality” of cooked rice. Starch<br />

structure can be described on several levels—ranging from<br />

the organization of compound starch granules (Whistler and<br />

BeMiller 1997) within the cells of the endosperm down to the<br />

connectivity of the chains in the individual molecules.<br />

Amylopectin and amylose are accumulated in the developing<br />

grains of all cereals. Amylopectin is deposited in semicrystalline<br />

growth rings, in alternating zones of crystalline and<br />

amorphous regions (French 1984). It is unclear whether amylose<br />

is interspersed within the amorphous lamella of the semicrystalline<br />

rings, or if it is deposited within the amorphous<br />

growth rings. The amorphous growth rings are known to contain<br />

carbohydrates linked by both alpha 1-4 and alpha 1-6 bonds<br />

(Atkin et al 1999), but the exact contents of those growth rings<br />

are unknown.<br />

The semicrystalline growth rings of starch are understood<br />

much more than are the amorphous growth rings. For amylopectin,<br />

crystalline lamellae alternate with amorphous lamellae.<br />

The synthesis of amylopectin occurs through the agency<br />

of a suite of enzymes, many of which have been identified,<br />

cloned, and sequenced, showing that the biosynthesis of starch<br />

has been strongly conserved throughout the plant kingdom.<br />

However, the exact function of each enzyme is not so well<br />

understood. Attempts to understand function have been mostly<br />

undertaken by comparing the molecular weight distribution<br />

(MWD) of the amylopectin chains of wild types with that of<br />

mutants or antisense lines that lack the activity of one enzyme<br />

in the pathway of starch synthesis (Myers et al 2000). Here we<br />

introduce a new technique for understanding the full MWD of<br />

debranched amylopectin, using methods that have been developed<br />

for quantitatively interpreting MWDs in synthetic polymers<br />

(Clay and Gilbert 1995). In brief, if the only events occurring<br />

during synthesis are random chain growth and stoppage,<br />

then the number of chains of degree of polymerization<br />

N, P(N), has the form ln[P(N)] ∝N, w<strong>here</strong> the constant of proportionality<br />

is the ratio of the stoppage and growth rates. This<br />

starting point suggests that mechanistic inferences can be made<br />

from a plot of lnP(N) against N. Castro et al (submitted) have<br />

described the validation of the application of this model to<br />

starch, and mathematical proof of the model.<br />

Methods<br />

Starch was isolated from rice, wheat, barley, maize, and potato<br />

by established techniques. The starches were gelatinized,<br />

debranched, and labeled with 8-amino-1,3,6-pyrenetrisulfonic<br />

acid (APTS) and analyzed by capillary eElectrophoresis<br />

(O’Shea et al 1998).<br />

To investigate the structure of the amorphous material,<br />

flour (250 mg) from 16 waxy varieties of rice was mixed with<br />

25 g MilliQ water. The slurries were gelatinized with a Rapid<br />

Visco Analyser (RVA, Newport Scientific) (AACC method 61-<br />

02). The mixture was centrifuged immediately (10,000 g, 10<br />

min). The supernatant contained the hot water soluble (HWS)<br />

starch. The HWS material was debranched, labeled with APTS,<br />

and analyzed as described above.<br />

Results<br />

Figure 1A shows the logarithmic plots for the range of species.<br />

All the higher plants studied exhibit similar logarithmic<br />

MWD plots: an initial increasing nonlinear region (which we<br />

define as Region 1), followed by two distinct decreasing linear<br />

regions (Regions 2 and 4) separated by a nonlinear region<br />

(Region 3). Seven metrics of the plots have been defined (Fig.<br />

1B): four slopes and three intersects of the slopes. The slopes<br />

and position of the regions on the logarithmic plots are independent<br />

of the normalization of the original data. Comparing<br />

the various species, the slopes of the linear regions (2 and 4)<br />

clearly vary, but all the intersects are similar (Fig. 1A).<br />

Figure 2 shows the logarithmic plot of the debranched<br />

HWS starch and full flour for one representative from the collection<br />

of 16 varieties of waxy rice. All intersects differ and<br />

the slope of both Regions 2 and 4 differs. The logarithmic plots<br />

of the full flour and HWS starch for all 16 varieties showed<br />

the same differences, but these are not shown <strong>here</strong>.<br />

Discussion<br />

Starch synthesis is a multistep process, containing both random<br />

and nonrandom elements (Thompson 2000, Caldwell and<br />

Matheson 2003). Plotting the MWDs of the debranched starch<br />

as logarithmic plots (Fig. 1) allows the identification of these<br />

random and nonrandom elements. Monotonically decreasing<br />

functions (Regions 2 and 4) indicate random elements (Clay<br />

and Gilbert 1995). The monotonically increasing nonlinear<br />

regions of the lnP curves (Regions 1 and 3) are of particular<br />

interest—if all chains began at DP 1 and grew until a random<br />

stopping event, then P(N), and hence lnP(N), must necessarily<br />

be a decreasing function. Two decreasing functions added together<br />

still produce a decreasing function. This implies that<br />

some nonrandom event must be involved in generating Regions<br />

1 and 3. Region 1 chains are between DP 6 and 10 and<br />

are probably remnants of branching enzyme events (chain stoppage)<br />

rather than originating from controlled synthesis.<br />

Regions 2 and 4 appear to define two populations of<br />

chains. The longer chains (Region 4) must originate from the<br />

shorter chains (Region 2), as t<strong>here</strong> is no evidence for a mecha-<br />

Session 8: Improving rice quality 251


InP(N) + offset<br />

3<br />

A<br />

2<br />

InP(N)<br />

18<br />

17<br />

HWS<br />

Full flour<br />

1<br />

16<br />

0<br />

–1<br />

–2<br />

–3<br />

15<br />

14<br />

13<br />

12<br />

11<br />

–4<br />

10<br />

0 20 40 60 80<br />

–5<br />

0<br />

InP(N)<br />

20 40 60 80 100<br />

N<br />

Fig. 2. lnP(N) plots of the debranched hot water soluble (HWS)<br />

and full flour starch of chains from DP 6 to DP


fer between the plots, and the difference is consistent among<br />

the collection of 16 varieties. This shows that the kinetics of<br />

the synthesis of these HWS molecules differ, suggesting<br />

strongly that the HWS molecules composed of branches between<br />

DP 6 and 70 (consistent with being amylopectin) are<br />

actually synthesized by different processes from amylopectin<br />

molecules. Further analysis of the metrics of these plots is required<br />

to determine whether these HWS molecules account<br />

for the chains between DP 33 and 47, but we cautiously support<br />

the possibility of a third fraction of starch that could exist<br />

in the amorphous growth rings. Further, we suggest that this<br />

molecule could account for all the reasons behind the term<br />

“apparent amylose” and account for the alpha 1-6 linkages<br />

observed by Atkin et al (1999) in the amorphous growth rings.<br />

We propose that these molecules are an intrinsic part of the<br />

starch granule and, to reflect this, we propose that this fraction<br />

be called amyloglycan.<br />

References<br />

Atkin NJ, Cheng SL, Abeysekera RM, Robards AW. 1999.<br />

Localisation of amylose and amylopectin in starch granules<br />

using enzyme-gold labeling. Starch-Starke 51:163-172.<br />

Chinnaswamy R, Bhattacharya KR.1986. Characteristics of gel-chromatographic<br />

fractions of starch in relation to rice and expanded<br />

rice-product qualities. Starch-Starke 38:51-57.<br />

Clay PA, Gilbert RG. 1995. Molecular weight distributions in freeradical<br />

polymerizations. 1. Model development and implications<br />

for data interpretation. Macromolecules 28:552-569.<br />

French D. 1984. Organization of the starch granules. In: Whistler<br />

RL, Bemiller JN, Pasehall JF, editors. Starch: chemistry and<br />

technology. Orlando, Fla. (USA): Academic Press.<br />

Hizukuri S, Takeda Y, Maruta N, Juliano BO. 1989. Molecular structures<br />

of rice starch. Carb. Res. 189:227-235.<br />

Imberty A, Buleon A, Vinh T, Perez S. 1991. Recent advances in<br />

knowledge on starch structure. Starch-Starke 43:375-384.<br />

Myers AM, Morell MK, James MG, Ball SG. 2000. Recent progress<br />

toward understanding biosynthesis of the amylopectin crystal.<br />

Plant Physiol. 122:989-997.<br />

O’Shea MG, Samuel MS, Konik CM, Morell MK. 1998.<br />

Fluorophore-assisted carbohydrate electrophoresis (face) of<br />

oligosaccharides: efficiency of labelling and high-resolution<br />

separation. Carb. Res. 307:1-12.<br />

Thompson DB. 2000. On the non-random nature of amylopectin<br />

branching. Carb. Polymers 43:223-229.<br />

Whistler RL, BeMiller JN. 1997. Carbohydrate chemistry for food<br />

scientists. St. Paul, Minn. (USA): American Association of<br />

Cereal Chemists, Inc.<br />

Notes<br />

Authors’ addresses: Melissa Fitzgerald and Rosa Paula Cuevas, <strong>International</strong><br />

<strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>, DAPO Box 7777, Metro<br />

Manila, Philippines; Melissa Fitzgerald and Jeffrey Castro,<br />

CRC for Sustainable <strong>Rice</strong> Production, PMB, Yanco 2703,<br />

NSW, Australia; Melissa Fitzgerald, NSW Department of Primary<br />

Industries, PMB, Yanco 2703, NSW, Australia; Jeffrey<br />

Castro and Robert Gilbert, Key Centre for Polymer Colloids,<br />

School of Chemistry, The University of Sydney 2006, NSW,<br />

Australia, e-mail: m.fitzgerald@cgiar.org.<br />

Textural differences between indica<br />

and japonica varieties in cooked rice<br />

Keiko Hatae, Sonoko Ayabe, and Midori Kasai<br />

Indica rice varieties are popular worldwide. Cooked indica rice<br />

is hard but not sticky. However, Japanese people are fond of<br />

japonica cooked rice because of its moderate elasticity and<br />

stickiness. It is generally said that the amylose content contributes<br />

to the hardness and stickiness of cooked rice. Japonica<br />

rice has lower amylose content and moderate elasticity and<br />

stickiness.<br />

This study was carried out to confirm the textural difference<br />

between cooked indica and japonica rice and to know the<br />

reasons for the difference. Among indica varieties, Khao Dawk<br />

Mali is known to contain less amylose; thus, Khao Dawk Mali<br />

and a higher amylose Thai rice and japonica Nipponbare were<br />

used to compare their texture and some physicochemical properties.<br />

Materials and methods<br />

Two cultivars of Oryza sativa L. indica (Khao Dawk Mali 105<br />

and unknown high-amylose Thai rice) obtained from Thailand<br />

in 2001 were used. They were stored at 4 °C. Japonica rice,<br />

Oryza sativa L. japonica (Nipponbare), grown in Shiga Prefecture,<br />

Japan (2001), was used. Khao Dawk Mali 105 and<br />

Nipponbare were 90% milled in a polishing machine before<br />

use.<br />

Milled rice grain was ground with an electric miller, and<br />

the resulting flour was passed through a 100-mesh sieve. Starch<br />

was isolated from milled rice flour by using cold 0.2% NaOH<br />

according to the alkali method of Yamamoto et al (1973) with<br />

modifications. The precipitate was washed with distilled water<br />

until the pH decreased to 7.0. After rinsing with ethanol,<br />

the starch was air-dried and passed through a 100-mesh sieve.<br />

Milled rice grains were washed three times with distilled wa-<br />

Session 8: Improving rice quality 253


Table 1. Textural properties of cooked rice from three varieties. a<br />

How cooked Textural property Nipponbare Khao Dawk Mali High-amylose rice<br />

Cooked with 1.4 Hardness (kgf) 2.19 ± 0.22 a 2.45 ± 0.15 a 3.74 ± 0.38 b<br />

times water Stickiness (kgf) 0.34 ± 0.04 a 0.10 ± 0.01 b 0.03 ± 0.04 c<br />

Cooked with 1.9 Hardness (kgf) 1.98 ± 0.19 a 2.18 ± 0.30 a 3.17 ± 0.16 b<br />

times water Stickiness (kgf) 0.41 ± 0.03 a 0.14 ± 0.06 b 0.04 ± 0.01 c<br />

a<br />

Mean ±SD of ten measurements. For letters a, b, and c, the same letter in the same row is not significantly<br />

different (P λ max ≥600 nm; Fr. II: 600 nm > λ max<br />

≥525 nm; Fr. III: 525 nm > λ max).<br />

Results and discussion<br />

Proximate analysis<br />

The moisture contents of the three rice flours ranged from<br />

13.4% to 14.5% and crude protein from 5.34% to 7.62%. Apparent<br />

amylose contents were almost the same (16%) in Khao<br />

Dawk Mali and Nipponbare, which were different from highamylose<br />

Thai rice (27%). This confirmed that indica variety<br />

Khao Dawk Mali and japonica variety Nipponbare have the<br />

same level of amylose.<br />

Textural properties<br />

Table 1 shows the hardness and stickiness of rice cooked with<br />

1.4 times water or 1.9 times water. The hardness of Nipponbare<br />

and Khao Dawk Mali was the same, but the stickiness was<br />

different. And those of high-amylose Thai rice were quite different<br />

from those of other rice varieties. Thus, the textural difference<br />

of cooked rice could not be explained by only the difference<br />

in amylose content.<br />

Degree of gelatinization<br />

The degree of gelatinization was almost 100% in Nipponbare<br />

and Khao Dawk Mali, both cooked with 1.4 and 1.9 times<br />

water. In contrast, the value of the high-amylose Thai rice was<br />

84% even when cooked with 1.9 times water. The degree of<br />

gelatinization is not enough to explain the textural difference<br />

of cooked rice.<br />

254 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Total saccharide ratio ( )<br />

12<br />

Nipponbare<br />

40<br />

12<br />

Khao Dawk Mali<br />

40<br />

Average degree of polymerization (d.p.)<br />

12<br />

High-amylose rice<br />

40<br />

10<br />

10<br />

10<br />

30<br />

30<br />

30<br />

8<br />

8<br />

8<br />

6<br />

20<br />

6<br />

20<br />

6<br />

20<br />

4<br />

4<br />

4<br />

10<br />

10<br />

10<br />

2<br />

2<br />

2<br />

0<br />

0 0<br />

0 0<br />

0<br />

25 30 35 40 45 50 55 25 30 35 40 45 50 55 25 30 35 40 45 50 55<br />

Fraction no.<br />

Fraction no.<br />

Fraction no.<br />

Fig. 1. GFC patterns of extracts from three kinds of cooked rice surface after isoamylase treatment.<br />

Weight of precipitates and sugar and protein<br />

contents of supernatant of cooked-rice extracts<br />

The weight of precipitates was the largest in Nipponbare, followed<br />

by Khao Dawk Mali, and the smallest in high-amylose<br />

Thai rice. The same order in the contents of total sugar, reducing<br />

sugar, and protein of supernatant was obtained. It seemed<br />

that the large amount of sugar in the supernatant was an important<br />

factor, especially in the stickiness of cooked rice.<br />

FT-IR spectrometry<br />

FT-IR is a useful tool to determine intermolecular interaction.<br />

This time, the difference in intermolecular interaction of the<br />

three kinds of rice starches (flour with 50% w/w of water) was<br />

measured. A wave length of 1,000–1,100 cm –1 is known to<br />

denote the interaction between C and O and C and C, and 1,020<br />

cm –1 is also known to show the absorption of sugar. Thus, we<br />

used a wave length of around 1,000 cm –1 .<br />

Three FT-IR patterns for each three kinds of rice were<br />

obtained, that is, raw rice starch, cooked rice, and extracts of<br />

the surface of cooked rice. Moreover, a difference in IR spectrum<br />

of the cooked rice and the extracts was found. From the<br />

results, the difference in IR spectrum of this approximate wave<br />

length was negatively larger in Nipponbare, followed by Khao<br />

Dawk Mali. On the other hand, high-amylose Thai rice was<br />

positively larger. This negatively large difference in cooked<br />

rice and the extracts means that a larger amount of sugar was<br />

in the surface layer than inside the cooked rice. This may be<br />

one reason to explain the textural difference of the cooked<br />

rice.<br />

Gel permeation chromatography<br />

Figure 1 shows the gel permeation patterns of rice starch after<br />

iso-amylase treatment. For raw rice, the patterns of Nipponbare<br />

and Khao Dawk Mali were similar and that of high-amylose<br />

Thai rice was different. The long-chain fraction was largest in<br />

high-amylose Thai rice.<br />

When three kinds of rice were cooked, Nipponbare decreased<br />

its amylose fraction, but its short-chain (about 15 dp)<br />

amylopectin fraction increased slightly. The pattern of the<br />

Nipponbare extracts was almost the same as with cooked rice.<br />

In Khao Dawk Mali, the amylose fraction decreased to the<br />

same level as Nipponbare when cooked. However, this amylose<br />

fraction increased in the extracts. In high-amylose rice,<br />

the amylose fraction decreased largely after cooking, w<strong>here</strong>as<br />

the short-chain fraction increased. And, in the extracts, the longchain<br />

fraction (amylose fraction) increased even much more<br />

than raw starch.<br />

From these findings, we assumed that the distribution of<br />

amylose and amylopectin was almost equal in Nipponbare, but<br />

not in the indica varieties.<br />

Conclusions<br />

It is suggested that the stickiness of cooked rice is related to<br />

the sugar content in the surface layer of cooked rice extracts.<br />

These extracts also contained a lower amount of amylose fraction<br />

and larger amount of short-chain amylopectin fraction.<br />

These components are once eluted from the rice during cooking<br />

and finally absorbed into the surface layer, thus giving<br />

stickiness to rice.<br />

References<br />

Hizukuri S, Takeda Y, Yasuda M, Suzuki A. 1981. Multi branched<br />

nature of amylose and the action of debranching enzymes.<br />

Carbohydr. Res. 147:342-347.<br />

Session 8: Improving rice quality 255


Inouchi N, Glover DV, Takaya T, Fuwa H. 1987. Chain length distribution<br />

of amylopectin of several single mutants and the normal<br />

counterpart, and sugary-1 phytoglycogen in maize (Zea<br />

mays L.). Starch 39:259-266.<br />

Itoh T, Yoshio N, Teranishi K, Hisamatsu M, Yamada T. 1994. Saccharides<br />

extracted from rice grains during cooking process<br />

and effect of monoglyceride on them. Nippon Sholuhin Kogyo<br />

Gakkaishi 41:871-877.<br />

Juliano BO. 1971. A simplified assay for milled rice amylose. Cereal<br />

Sci. Today 16:334-338,340,360.<br />

Lowry OH, Rosenbrough GJ, Farr AL, Randall RJ. 1951. Protein<br />

measurement with the folin phenol reagent. J. Biol. Chem.<br />

193:265-275.<br />

Matsunaga A, Kainuma K. 1981. Studies on the retrogradation of<br />

starchy foods (Part 1). Retrogradation of cooked rice. J. Home<br />

Econ. Jpn. 32:653-659.<br />

Okabe M. 1977. <strong>Research</strong> on the taste of cooked rice. New Food<br />

Industry 19:65-71.<br />

Yamamoto K, Sawada S, Onogaki T. 1973. Properties of rice starch<br />

prepared by alkali method with various conditions. Denpun<br />

Kagaku 20:99-104.<br />

Notes<br />

Authors’ address: Department of Food and Nutrition, Ochanomizu<br />

University, e-mail: hatae@cc.ocha.ac.jp.<br />

Biological efficacy of consuming rice biofortified with iron<br />

J. Haas, J. Beard, A. Del Mundo, G. Gregorio, L.M. Kolb, and A. Felix<br />

The World Health Organization estimates that 3.5 billion people<br />

in the developing world are affected by iron-deficiency anemia.<br />

Given the need for a sustainable solution to reduce this<br />

number, biofortified rice (variety IR68144) was used to test<br />

the feasibility of high-iron rice as a source of dietary iron. We<br />

conducted a double-blind longitudinal (9 months) intervention<br />

study with religious sisters from 10 convents in and around<br />

Manila, Philippines. Some 317 religious sisters were randomly<br />

assigned to consume either an iron-enhanced (high-iron) rice<br />

or a local variety of rice (control). <strong>Rice</strong> preparation and distribution<br />

were standardized. The sisters consumed their assigned<br />

rice at every meal and food intakes were weighed on 3 days<br />

every 2 weeks for each woman. Blood samples were collected<br />

at baseline, mid-point, and end-point and used to determine<br />

serum ferritin, the transferring receptor, and hemoglobin,<br />

among other indicators of iron status. The efficacy trial indicated<br />

that the high-iron rice provided an additional 1.41 mg of<br />

iron per day, representing a 17% increase in dietary iron in the<br />

diets of these women. Ferritin and body iron levels were sig-<br />

nificantly different at the end of the 9-month trial for the<br />

nonanemic women who consumed the high-iron rice instead<br />

of the control after controlling for baseline values, amount of<br />

rice consumed, and convent. The greatest changes in ferritin<br />

and body iron were observed in the women who consumed the<br />

most biofortified rice and the calculation of the amount of iron<br />

transferred from the diet to iron stores is consistent with the<br />

observed changes in body iron. T<strong>here</strong>fore, it is possible to<br />

conclude that t<strong>here</strong> was a significantly positive effect of consuming<br />

biofortified rice on the iron status of women with an<br />

iron-poor diet.<br />

Notes<br />

Authors’ addresses: J. Haas, J. Beard, and L.M. Kolb, Cornell University,<br />

USA; G. Gregorio, <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>,<br />

Los Baños, Philippines; A. Del Mundo and A. Felix,<br />

University of the Philippines Los Baños, Los Baños, Philippines.<br />

Radical-scavenging activity of red and black rice<br />

Tomoyuki Oki, Mami Masuda, Saki Nagai, Miwako Take’ichi, Mio Kobayashi, Yoichi Nishiba, Terumi Sugawara, Ikuo Suda, and Tetsuo Sato<br />

<strong>Rice</strong> (Oryza sativa) is widely consumed in the world, and the<br />

most common type (>85%) has a white pericarp. Other types<br />

have a colored pericarp, and the most common are green, black,<br />

and red. The black and red varieties are planted mainly in South<br />

Asia and other countries, such as Italy, Greece, and the United<br />

States (Simmons and Williams 1997). <strong>Rice</strong> with a colored pericarp<br />

has long been consumed in Japan and China and is considered<br />

to be a healthy food. We are especially interested in<br />

the antioxidative and radical-scavenging properties of rice<br />

because of their potential to provide health protection against<br />

reactive oxygen species and free radicals, which have been<br />

implicated in more than 100 diseases (Halliwell 1992).<br />

On the other hand, t<strong>here</strong> have also been some reports<br />

concerning the antioxidative compounds found in rice. Gammaoryzanol,<br />

which is a mixture of ferulate esters of triterpene<br />

alcohol, is well known as an antioxidant in rice bran (Xu et al<br />

256 <strong>Rice</strong> is life: scientific perspectives for the 21st century


2001). In black rice, cyanidin-3-glucoside (Cy-3-Glc) has been<br />

reported to be one of the major antioxidant compounds (Osawa<br />

1999). However, little information exists on the antioxidative<br />

effects of red rice, although the existence of catechin and tannin<br />

has been reported (Nawa and Ohtani 1992).<br />

In this report, extracts from rice with pericarp of three<br />

different colors (white, black, and red) were prepared by using<br />

solvents with various polarities and subjected to a radicalscavenging<br />

assay. Furthermore, we determined the major radical-scavenging<br />

components in black and red rice.<br />

Materials and methods<br />

<strong>Rice</strong><br />

Three rice cultivars, Hinohikari, Saikai-225, and Beniroman,<br />

which have white, black, and red pericarp, respectively, were<br />

harvested at KONARC (Chikugo Branch, Fukuoka, Japan) in<br />

1998. The authors also used Beniroman, Tsukushiakamochi,<br />

Tsushimazairai, and Tanegashimazairai, which have red pericarp.<br />

Each cultivar was milled with an ultra centrifugal mill<br />

(type ZM1000, Retsch GmbH & Co., KG, Germany). The<br />

milled rice was stored at 4 °C and used within 2 days of milling.<br />

Preparation of rice extract<br />

Extraction 1. Milled rice powder (2.0 g) was sequentially extracted<br />

with six different polar solvents already reported by<br />

Oki et al (2002a). Extraction was done using 5.0 mL of solvent<br />

and the following sequence of solvents with increasing<br />

polarity: n-hexane, diethylether, ethyl acetate, acetone, methanol,<br />

and deionized water. After each extraction, the residue<br />

was dried under reduced pressure at ambient temperature for<br />

1 hour to remove the residual solvent. Each extract was filled<br />

up to 5.0 mL with the extraction solvent. An aliquot (1.0 mL)<br />

was dried under reduced pressure at 35 °C, and the residue<br />

was redissolved in 1.0 mL of dimethyl sulfoxide.<br />

Extraction 2. Milled rice powder (1.0 or 2.0 g) was extracted<br />

twice with 5.0 mL of a 70% acetone/0.5% acetic acid<br />

solution (red rice) and a 5% acetic acid solution (black rice)<br />

for 16 hours at ambient temperature in the dark. The supernatant<br />

obtained by centrifugation (1,200x g, 10 min, 4 °C) was<br />

combined and filled up to 10 mL with the same extraction solution.<br />

For black rice, an aliquot (2.0 mL) of the extract was<br />

applied on an Amberlite XAD-2000 column (10 × 40 mm)<br />

and eluted stepwise with 15 mL of distilled water and a 70%<br />

ethanol solution. The ethanol fraction was evaporated to dryness<br />

under reduced pressure and redissolved in 2.0 mL of deionized<br />

water.<br />

Assay for DPPH • and t-BuOO • scavenging activity<br />

The 1,1-diphenyl-2-picrylhydrazyl radical (DPPH • ) and the<br />

tert-butyl hydroperoxide radical (t-BuOO • ) scavenging activities<br />

were measured by the methods already reported (Oki et al<br />

2002a, 2002b). The radical-scavenging activity was expressed<br />

as a Trolox, water-soluble alpha-tocopherol equivalent.<br />

Determination of polyphenol, anthocyanin,<br />

and proanthocyanidin content<br />

The polyphenol and anthocyanin content were detemined by<br />

the methods already reported (Oki et al 2002b). The polyphenol<br />

and anthocyanin content were expressed as a gallic acid<br />

and Cy-3-Glc equivalent, respectively.<br />

The proanthocyanidin content was determined by the<br />

vanillin-sulfuric acid assay already reported (Oki et al 2002a).<br />

The proanthocyanidin content was expressed as a (+)-catechin<br />

equivalent.<br />

Results and discussion<br />

Comparison of radical-scavenging activity<br />

among three different-colored pericarps<br />

<strong>Rice</strong> powder was sequentially extracted with n-hexane, diethyl<br />

ether, ethyl acetate, acetone, methanol, and deionized water,<br />

and the DPPH • scavenging activity of each extract is shown in<br />

Figure 1A. The total DPPH • scavenging activity, which was<br />

calculated from the sum of the activity in each extract, varied<br />

according to the pericarp color. The highest activity was observed<br />

in red rice (2.77 µmol-Trolox equiv. mL –1 ), followed<br />

by black (0.92) and white (0.26) rice. In all varieties, the extracts<br />

prepared with high polar solvents, methanol, and deionized<br />

water showed radical-scavenging activity. In rice with<br />

black and white pericarp, the sum of the activities in two extracts<br />

corresponded to more than 90% of the total DPPH • scavenging<br />

activity. In red rice, high radical-scavenging activity<br />

(1.22 µmol-Trolox equiv. mL –1 ) was observed in the acetone<br />

extract in addition to the methanol and deionized water extracts.<br />

The t-BuOO • scavenging activity was estimated by the<br />

decrease in luminance measured with an analyzer equipped<br />

with a charge-coupled device camera (type CLA-IMG2,<br />

Tohoku Electronic Industrial Co., Sendai, Japan). As the activities<br />

were calculated as a Trolox equivalent per assay, it could<br />

be observed that the extracts prepared with high polar solvents<br />

exhibited higher t-BuOO • scavenging activity, which was similar<br />

to the results of the DPPH • scavenging activity (Fig. 1B).<br />

The total t-BuOO • scavenging activity, which was calculated<br />

from the sum of the activity in each extract, decreased in the<br />

order of rice with red pericarp (4.15 nmol-Trolox equiv. assay<br />

–1 ), black (2.83), and white (2.09). In addition, the acetone<br />

extract from red rice exhibited a high t-BuOO • scavenging activity,<br />

while no such activities of the other cultivars (white and<br />

black rice) were detected.<br />

Radical-scavenging components in red rice<br />

To obtain useful information about the radical-scavenging components<br />

in the acetone extract prepared from red rice, the extract<br />

was subjected to hydrochloric acid hydrolysis and a vanillin-sulfuric<br />

acid assay. In both reactions, the tested solution<br />

turned red, indicating the presence of proanthocyanidin in the<br />

extract. In the acid hydrolysate, only cyanidin was identified<br />

as an anthocyanidin by reverse-phase high-performance liquid<br />

chromatography (RP-HPLC). This result revealed that the<br />

Session 8: Improving rice quality 257


DPPH • scavenging activity (mmol-Trolox equiv. mL –1 )<br />

1.5<br />

White rice<br />

1.0<br />

0.5<br />

A<br />

t-BuOO • scavenging activity (nmol-Trolox equiv. assay –1 )<br />

2.0<br />

White rice<br />

B<br />

1.5<br />

1.0<br />

0.5<br />

0<br />

ND<br />

ND<br />

0<br />

ND<br />

ND<br />

ND<br />

1.5<br />

Black rice<br />

2.0<br />

Black rice<br />

1.0<br />

1.5<br />

1.0<br />

0.5<br />

0.5<br />

0<br />

ND<br />

ND<br />

ND<br />

0<br />

ND<br />

ND<br />

ND<br />

1.5<br />

Red rice<br />

2.0<br />

Red rice<br />

1.0<br />

1.5<br />

1.0<br />

0.5<br />

0.5<br />

0<br />

n-hexane<br />

Diethylether<br />

ND<br />

Ethyl acetate<br />

Acetone<br />

Methanol<br />

Deionized water<br />

0<br />

n-hexane<br />

ND<br />

Diethylether<br />

ND<br />

Ethyl acetate<br />

Acetone<br />

Methanol<br />

Deionized water<br />

Fig. 1. DPPH • (A) and t-BuOO • (B) scavenging activities of extracts prepared from rice with red, black,<br />

and white pericarp by using solvents with various polarities. ND = not detected.<br />

proanthocyanidin in the extract from red rice was the<br />

procyanidin type, that is, (+)-catechin and/or (–)-epicatechin<br />

derivatives. The gel permeation chromatography of the acetylated<br />

proanthocyanidin revealed that the average molecular<br />

weight is about 5,000, in a range of about 500 to 18,000 after<br />

proanthocyanidin was purified from the acetone extract by<br />

using a Sephadex LH-20 column chromatography.<br />

We also examined DPPH • scavenging activity, polyphenol<br />

content, and proanthocyanidin content in various rice cultivars<br />

with red pericarp. The DPPH • scavenging activity varied<br />

according to the cultivars (1.4 to 46.7 µmol-Trolox equiv.<br />

g –1 ), and Tanegashimazairai, a traditional wild type of red rice<br />

in Japan, showed very high radical-scavenging activity. The<br />

DPPH • scavenging activity was highly correlated to polyphenol<br />

content and proanthocyanidin content, with correlation<br />

coefficients of 0.982 and 0.944, respectively (Fig. 2). This result<br />

indicated that the major radical-scavenging component in<br />

red rice was proanthocyanidin.<br />

Radical-scavenging components in black rice<br />

The black rice extracts were prepared from eight varieties purchased<br />

at the local market in the Kyushu and Okinawa regions.<br />

DPPH • scavenging activity of the extracts ranged from 3.1 to<br />

10.8 µmol-Trolox equiv. mL –1 of the extract. The radical-scavenging<br />

activity increased with the increase in anthocyanin content,<br />

and the correlation coefficient was 0.987. By RP-HPLC<br />

of the extracts, two major peaks were observed in all eight<br />

black rice varieties, and these peaks were identified as peonidin-<br />

3-glucoside (Pn-3-Glc) in addition to Cy-3-Glc. A slight compositional<br />

difference in anthocyanin was observed, however.<br />

The sum of Cy-3-Glc and Pn-3-Glc constituted more than 85%<br />

of the total anthocyanin. T<strong>here</strong>fore, it was revealed that the<br />

dominant radical-scavengers in black rice were Cy-3-Glc and<br />

Pn-3-Glc.<br />

We have already found that two anthocyanins (Cy-3-Glc<br />

and Pn-3-Glc) were detected in rat plasma after oral administration<br />

of the anthocyanin-rich concentrate prepared from black<br />

rice (BR-ANT) (Oki et al 2002c). Furthermore, the BR-ANT<br />

258 <strong>Rice</strong> is life: scientific perspectives for the 21st century


DPPH • scavenging activity (mmol-Trolox equiv. g –1 )<br />

50<br />

A<br />

B<br />

40<br />

30<br />

20<br />

10<br />

R = 0.982<br />

R = 0.994<br />

0<br />

0 10 20 30 40 50<br />

Polyphenol content<br />

(mmol-gallic acid equiv. g –1 )<br />

0 10 20 30 40 50<br />

Proanthocyanidin content<br />

(mmol-(+)-catechin equiv. g –1 )<br />

Fig. 2. Correlation of polyphenol content (A) and proanthocyanidin content (B) with DPPH • scavenging<br />

activity in various rice cultivars with red pericarp.<br />

suppressed hemolysis and the oxidation of LDL (Oki et al<br />

2002c). The BR-ANT also inhibited lipid peroxidation induced<br />

by four different radical generation systems (Oki et al 2002c).<br />

These results suggested that dietary consumption of black rice<br />

might prevent many diseases related to lipid peroxidation<br />

caused by free radicals.<br />

On the other hand, t<strong>here</strong> is currently no satisfactory explanation<br />

for how the polymeric proanthocyanidin is absorbed<br />

into the bloodstream. Ling et al (2001) have reported that, when<br />

a hypercholesterolemia rabbit had red rice as a part of its diet,<br />

the total antioxidative properties of the serum and liver increased.<br />

They suggested that constituents with antioxidative<br />

activity could be responsible for the increased antioxidative<br />

properties in the body; however, they did not identify the antioxidant<br />

compounds in red rice. This report suggests that, after<br />

proanthocyanidin in red rice is consumed, it could be absorbed<br />

by the body directly and/or indirectly (i.e., structural change<br />

or degradation), which would elevate the antioxidative capacity.<br />

Now, we are investigating the physiological functions of<br />

red rice in vivo and elucidating the mechanisms at work in<br />

these functions.<br />

References<br />

Halliwell B. 1992. The role of oxygen radicals in human disease,<br />

with particular reference to the vascular system. Haemostasis<br />

23(suppl. 1):118-126.<br />

Ling WH, Cheng QX, Wang JMT. 2001. Red and black rice decrease<br />

artherosclerotic plaque formation and increase antioxidant<br />

status in rabbits. J. Nutr. 131:1421-1426.<br />

Nawa Y, Ohtani T. 1992. Property of pigments in rice hulls of various<br />

colors. Food Industry 11:28-33. (In Japanese.)<br />

Oki T, Masuda M, Kobayashi M, Nishiba Y, Furuta S, Suda I, Sato<br />

T. 2002a. Polymeric procyanidins as radical scavenging components<br />

in red-hulled rice. J. Agric. Food Chem. 50:7524-<br />

7529.<br />

Oki T, Masuda M, Furuta S, Nishiba Y, Suda I. 2002b. Involvement<br />

of anthocyanins and other phenolic compounds in radical-scavenging<br />

activity of purple-fleshed sweet potato cultivars. J. Food<br />

Sci. 67:1752-1756.<br />

Oki T, Masuda M, Ikuo S. 2002c. Antioxidative activity of black<br />

rice commercially available in Kyushu and Okinawa region.<br />

In: Noguchi T, editor. The 56th Annual Scientific Meeting,<br />

19-21 July 2002. Hokkaido University (Japan): The Japanese<br />

Society of Nutrition and Food Science. p 230. (In Japanese.)<br />

Osawa T. 1999. Protective role of rice polyphenols in oxidative stress.<br />

Anticancer Res. 19:3645-3650. (In Japanese.)<br />

Simmons D, Williams R. 1997. Dietary practices among Europeans<br />

and different South Asian groups in Coventry. Br. J. Nutr.<br />

78:5-14.<br />

Xu Z, Hua N, Godber JS. 2001. Antioxidant activity of tocopherols,<br />

tocotrienols, and γ-oryzanol components from rice bran against<br />

cholesterol oxidation accelerated by 2,2′-azobis (2-<br />

methylpropionamidine) dihydrochloride. J. Agric. Food Chem.<br />

49:2077-2081.<br />

Notes<br />

Authors’ addresses: Department of Crop and Food Science, National<br />

Agricultural <strong>Research</strong> Center for Kyushu Okinawa Region<br />

(KONARC), National Agriculture and Bio-oriented <strong>Research</strong><br />

Organization (NARO), 2421 Suya, Nishigoshi, Kikuchi,<br />

Kumamoto 861-1192, Japan, e-mail: tomooki@affrc.go.jp.<br />

Session 8: Improving rice quality 259


A rice mutant with enhanced amylose content in endosperm<br />

derived from low-amylose variety Snow Pearl: isolation<br />

and characterization<br />

Yasuhiro Suzuki, Hiro-Yuki Hirano, Yoshio Sano, Kazuo Ise, Ushio Matsukura, Noriaki Aoki, and Hiroyuki Sato<br />

Amylose content of endosperm starch is an important characteristic<br />

of rice in determining eating and cooking quality. Amylose<br />

content is genetically controlled by a major gene, the Waxy<br />

(Wx) gene (Nelson and Pan 1995). In addition, amylose content<br />

is also affected by several modifying genes and environmental<br />

factors such as temperature. The Wx gene encodes the<br />

granule-bound starch synthase that is responsible for amylose<br />

synthesis in the endosperm. <strong>Rice</strong> strains having the Wx b gene<br />

contain 15–20% amylose, w<strong>here</strong>as rice strains having the Wx a<br />

gene contain 20–25% amylose (Sano 1984). The du loci modify<br />

amylose content by controlling expression of the Wx b gene<br />

and mutations at the du loci cause a reduction in amylose content<br />

(Okuno et al 1983, Hirano 1993). Although the amyloseextender<br />

(ae) mutant shows increasing levels of apparent amylose<br />

content, this increase is caused by the altered amylopectin<br />

structure, and the ae mutation is found in the gene for starchbranching<br />

enzyme IIb (Nishi et al 2001). While t<strong>here</strong> are many<br />

mutants in starch composition, t<strong>here</strong> is no report about a gene<br />

whose mutation gives rise to an increase in amylose content in<br />

the endosperm. In this paper, we describe the isolation and<br />

characterization of a rice mutant with enhanced amylose content<br />

in the endosperm that does not affect the amylopectin structure.<br />

To screen mutants with enhanced amylose content, we<br />

used a low-amylose rice variety, Snow Pearl (Higashi et al<br />

1999). In this variety, amylose content was very low (about<br />

5%) and the endosperm appeared chalky when seeds matured<br />

at a normal temperature (26 o C) (Table 1). On the other hand,<br />

when seeds matured at a cool temperature (20 o C), amylose<br />

content was about 18% and the endosperm appeared<br />

semitranslucent. Because amylose content in rice seed influences<br />

the degree of transparency (Suzuki et al 2002), a mutant<br />

with enhanced amylose content in (semitranslucent) seeds<br />

matured at a normal temperature could be easily distinguished<br />

from the original variety with low-amylose (chalky) seeds.<br />

Dry seeds of Snow Pearl rice were treated with 1 mM<br />

sodium azide in 0.1 M sodium phosphate buffer (pH 3.0) for 6<br />

h at room temperature, following washing with tap water. The<br />

first screening used 7,200 M 1 plants that matured at an average<br />

temperature of 24–26 o C. Although the panicles of almost<br />

all of these plants contained exclusively chalky seeds, one of<br />

these plants contained a mixture of chalky and semitranslucent<br />

seeds, 41 and 6 seeds, respectively. Next, semitranslucent M 2<br />

seeds were chosen as a candidate (designated as SP14) for a<br />

mutant with enhanced amylose content. The M 2 seeds were<br />

Table 1. Effect of temperature on the accumulation of amylose during<br />

seed development. a<br />

Strain 20 o C 26 o C Difference (20–26 o C)<br />

Snow Pearl 18.3 ± 0.8 5.2 ± 0.5 13.1<br />

SP14 24.7 ± 0.3 11.7 ± 0.6 13.0<br />

Koshihikari 25.1 ± 0.8 17.0 ± 0.3 8.1<br />

a<br />

Snow Pearl, SP14, and Koshihikari seeds matured at 20 or 26 o C. The amylose<br />

content of the samples was analyzed based on an iodine colorimetric assay (Juliano<br />

1971) with slight modifications (Suzuki et al 2002). Data (amylose content, %) are<br />

mean values ± SE from 5 trials. Twenty mg of white rice powder was used for each<br />

trial.<br />

seeded, and amylose content of SP14 (M 3 seeds) was compared<br />

with that of Snow Pearl and Koshihikari using a temperature-controlled<br />

growth chamber. The amylose content in<br />

mature seeds of SP14 was about 12% at 26 o C and 25% at 20<br />

o C (Table 1), indicating that amylose content of SP14 is responding<br />

to maturation temperatures and is 6–7% higher than<br />

that of Snow Pearl. Furthermore, to clarify whether amylose<br />

content in SP14 was increased by the ae locus or not, the amylopectin<br />

chain-length distribution in rice endosperm was analyzed<br />

by high-performance anion exchange chromatography<br />

with a pulsed amperometric detector, as previously described<br />

(Suzuki et al 2003). The chain-length distributions of amylopectin<br />

were almost the same between the two strains matured<br />

at both temperatures (data not shown). In addition, while<br />

endosperm appearance of EM10 (ae mutant) was floury, that<br />

of SP14 as well as that of Snow Pearl and Koshihikari was not<br />

floury (i.e., wild type = normal). These results indicated that<br />

the mutation in SP14 would not be the ae mutation, but a new<br />

mutation that enhances amylose content in rice endosperm.<br />

It should also be noted whether SP14 is derived from<br />

Snow Pearl or not. As Snow Pearl has a single nucleotide polymorphism<br />

(SNP) on the 3rd exon of the Wx gene (Nippon<br />

Suisan Kaisha, Ltd. 2000), a part of the SP14 Wx gene (344<br />

base pairs) containing the SNP was compared with that of Snow<br />

Pearl and Koshihikari. SNP of SP14 was identical with that of<br />

Snow Pearl, but not with that of Koshihikari, indicating that<br />

SP14 is a mutant derived from Snow Pearl. Furthermore, the<br />

nucleotide sequences of the wx locus (6,800 base pairs: Wx<br />

gene and promoter region) of SP14 and Snow Pearl were identical.<br />

These results suggested that the mutation from Wx b to<br />

Wx a in SP14 would not occur and that the mutation in SP14<br />

would not be on the wx locus.<br />

260 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 2. Segregation of amylose content of F 2 seeds from selfed F 1 rice plants. a<br />

Seed number<br />

Chi-square value<br />

Strain Amylose content Total for 15:1 ratio Probability<br />

< 8% ≥ 8%<br />

SP14/Snow Pearl 92 8 100 0.523 0.4 < P < 0.5<br />

Snow Pearl 10 0 10<br />

SP14 0 10 10<br />

a<br />

Snow Pearl, SP14, and F 2 rice seeds (SP14/Snow Pearl) matured at 26 o C. The amylose content of white rice<br />

seeds (15–25 mg) was analyzed based on an iodine colorimetric assay (Juliano 1971) with slight modifications<br />

(Suzuki et al 2002).<br />

Next, the mode of inheritance of the character was analyzed<br />

by crossing SP14 with Snow Pearl. The seeds of F 1 , Snow<br />

Pearl, and SP14 plants matured at 26 o C. As segregation of<br />

amylose content in F 2 seeds derived from the cross fit the ratio<br />

of 15 Snow Pearl-type seeds:1 SP14-type seed, the mutation<br />

is controlled by two recessive genes (Table 2). Thus, we have<br />

isolated a new rice mutant (SP14) in which amylose content in<br />

the endosperm was enhanced compared with the original variety.<br />

This mutant should be useful in breeding programs designed<br />

to produce rice of a high quality and in understanding<br />

genetic and molecular mechanisms for amylose synthesis.<br />

References<br />

Higashi T, Saitoh S, Takita T, Yamaguchi M, Sunohara Y, Yokogami<br />

N, Ikeda R, Tamura Y, Oyamada Z, Kowata H, Inoue M,<br />

Matsumoto S, Kataoka T. 1999. Breeding of a new rice cultivar<br />

with low amylose contents, “Snow pearl”. Bull. Tohoku<br />

Natl. Agric. Exp. Stn. 95:1-12.<br />

Hirano H-Y. 1993. Genetic variation and gene regulation at the wx<br />

locus in rice. Gamma-Field Symp. 24:63-79.<br />

Juliano BO. 1971. A simplified assay for milled-rice amylose. Cereal<br />

Sci. Today 16:334-340.<br />

Nelson O, Pan D. 1995. Starch synthesis in maize endosperms. Annu.<br />

Rev. Plant Physiol. Plant Mol. Biol. 46:475-496.<br />

Nippon Suisan Kaisha, Ltd. 2000. Method to distinguish a specific<br />

low-amylose-rice variety. Japan patent exhibition 2000-<br />

201679.<br />

Nishi A, Nakamura Y, Tanaka N, Satoh H. 2001. Biochemical and<br />

genetic analysis of the effects of amylose-extender mutation<br />

in rice endosperm. Plant Physiol. 127:459-472.<br />

Okuno K, Fuwa H, Yano M. 1983. A new mutant gene lowering<br />

amylose content in endosperm starch of rice, Oryza sativa L.<br />

Jpn. J. Breed. 33:387-394.<br />

Sano Y. 1984. Differential regulation of waxy gene expression in<br />

rice endosperm. Theor. Appl. Genet. 68:467-473.<br />

Suzuki Y, Sano Y, Hirano H-Y. 2002. Isolation and characterization<br />

of a rice mutant insensitive to cool temperatures on amylose<br />

synthesis. Euphytica 123:95-100.<br />

Suzuki Y, Sano Y, Ishikawa T, Sasaki T, Matsukura U, Hirano H-Y.<br />

2003. Starch characteristics of the rice mutant du2-2 Taichung<br />

65 highly affected by environmental temperatures during seed<br />

development. Cereal Chem. 80:184-187.<br />

Notes<br />

The role of the water-soluble fraction<br />

in rice pasting behavior<br />

Tadashi Yoshihashi, Eizo Tatsumi, Vipa Surojanametakul, Patcharee Tungtrakul, and Warunee Varanyanond<br />

Authors’ addresses: Yasuhiro Suzuki, Ushio Matsukura, Noriaki<br />

Aoki, and Hiroyuki Sato, National <strong>Institute</strong> of Crop Science,<br />

Kannondai, Tsukuba, Ibaraki 305-8518; Hiro-Yuki Hirano,<br />

Graduate School of Sciences, The University of Tokyo, Yayoi,<br />

Bunkyo-ku, Tokyo 113-8657; Yoshio Sano, Graduate School<br />

of Agriculture, Hokkaido University, Kita 9, Nishi 9, Kita-ku,<br />

Sapporo 060-8589; Kazuo Ise, Japan <strong>International</strong> <strong>Research</strong><br />

Center for Agricultural Sciences, Ohwashi, Tsukuba, Ibaraki<br />

305-8686, Japan, e-mail: suzuyasu@affrc.go.jp.<br />

Pasting behavior was widely used to estimate the physical<br />

properties of various cereals or starch-based products, including<br />

rice products. The components of rice, such as amylose<br />

content, protein, and enzymes, especially amylase activity,<br />

were known as the factors affecting pasting behavior. T<strong>here</strong><br />

were several reports on the effect of amylase activity on rapid<br />

visco analyzer (RVA) profiles in nonglutinous and glutinous<br />

rice varieties. Especially, the inhibition of amylase activity<br />

using copper sulfate or mercury chloride in Japanese glutinous<br />

rice varieties increased peak viscosity and could express<br />

the variety difference of glutinous rice varieties (Kikuchi 1998).<br />

However, the effects of amylase inhibitor in Thai high-amy-<br />

Session 8: Improving rice quality 261


lose varieties were opposite compared to those in glutinous<br />

rice varieties: lower peak viscosity and higher final viscosity<br />

(Tungtrakul and Yoshihashi 2001). Also, Matsukura et al (2004)<br />

reported that endogenous amylase activity among genetically<br />

isolated lines between nonglutinous and glutinous rice varieties<br />

did not show clear differences. T<strong>here</strong>fore, these changes in<br />

pasting behavior might be caused by an unknown factor or<br />

component in glutinous rice varieties, which are sensitive for<br />

amylase activity. The existence of water-soluble polysaccharide<br />

in rice has been reported (Horino et al 1988), and the<br />

amount of the polysaccharide was reported to be higher in glutinous<br />

rice varieties.<br />

Since polysaccharide contains a water-soluble fraction<br />

in rice, information about the water-soluble fraction in pasting<br />

behavior is important. However, the report showed only its<br />

existence, and t<strong>here</strong> is no information on its properties or role<br />

in rice properties. Generally, it is difficult to digest or react<br />

with raw starch from rice flour, without gelatinization for the<br />

usual amylase. Thus, we expected that the water-soluble fraction,<br />

which contains water-soluble polysaccharide, might be a<br />

novel factor in rice pasting behavior. T<strong>here</strong>fore, this study examines<br />

such an approach to understand the role of water-soluble<br />

polysaccharide in rice flour in rice pasting behavior through<br />

amylase inhibition.<br />

Materials and methods<br />

Four rice varieties, low-amylose variety Koshihikari (japonica,<br />

Japan), high-amylose variety Chainat 1 (indica, Thailand), and<br />

two glutinous rice varieties (RD6, indica, Thailand, and<br />

Hakuchoumochi, japonica, Hokkaido, Japan), were ground<br />

using an Ultracentrifugal Mill (ZM100, Retch, Germany) attached<br />

with a 0.5-mm screen. <strong>Rice</strong> flour was stored in a refrigerator<br />

until used.<br />

The effect of the water-soluble fraction on the pasting<br />

behavior of rice flour was examined using an RVA (RVA-super<br />

3, Newport Scientific, New South Wales, Australia) with a<br />

temperature program of AACC method No. 61-2. Various treatments<br />

with the rice flour used the following procedures:<br />

G1—the flour suspensions were prepared by adding<br />

25 mL of distilled water or 10 mM CuSO 4 to rice<br />

flour (3 g) in an RVA canister. The mixture underwent<br />

RVA analysis.<br />

G2—the flour suspension prepared as G1 was held at<br />

37 ºC for 60 min with stirring at 160 rpm to allow<br />

time for extraction of the water-soluble fraction by<br />

the RVA, and then the mixture immediately underwent<br />

an RVA analysis.<br />

G3—the water-soluble fraction was removed by centrifugation<br />

after the G2 procedure and the precipitate<br />

was then added to 25 mL of distilled water. Then, the<br />

mixture underwent RVA analysis.<br />

G4—the water-soluble fraction was removed following<br />

the G3 procedure and the precipitate was resuspended<br />

in 25 mL of distilled water or 10 mM CuSO 4<br />

solution. Then, the mixture underwent RVA analysis.<br />

<strong>Rice</strong> flour suspensions were prepared by weighing rice<br />

flour (3 g) in an RVA canister and adding 25 mL of distilled<br />

water or 10 mM CuSO 4 as amylase inhibitor. Also, suspensions<br />

were prepared from heated rice flour (110 ºC, 1 h). The<br />

suspensions were held at 37 ºC for 30 min with stirring at 160<br />

rpm by the RVA to allow extraction of the water-soluble fraction<br />

and digestion with in<strong>here</strong>nt rice amylase. A suspension<br />

was added with 1M CuSO 4 (250 mL) to inhibit further amylase<br />

digestion. Each water-soluble fraction was removed by<br />

centrifugation and supernatants were subjected to gel permeation<br />

chromatography (GPC). GPC was conducted with the<br />

Tosoh PS-8020 system equipped with the evaporative lightscattering<br />

detector (ELSD; Sedex-55, Sedex, France). The<br />

column used was a Tosoh G6000PWXL (250 × 6 mm I.D.).<br />

For GPC analysis, 20 mL of water-soluble fraction was injected<br />

and eluted with 1 mL min –1 of water. The ELSD conditions<br />

were 70 °C for inlet temperature, 2.3 bars for nitrogen<br />

flow, and gain 8.<br />

Milled broken rice was prepared by breaking milled rice<br />

by a hammer. Broken rice was heated (110 °C, 1 h) and 3 g of<br />

sample was suspended into water (25 mL). The suspension<br />

was stirred by a magnetic stirrer for 2 h at room temperature.<br />

The supernatant was separated by centrifuging (5 ºC, 8,000<br />

rpm, 30 min). GPC analysis was performed in the same manner.<br />

Ethanol precipitate of the water-soluble fraction (10 mg)<br />

and water (50 mL) were prepared in a sealed silver pan for<br />

differential scanning calorimetry (DSC) and kept in a refrigerator<br />

overnight for reaching equilibrium. The sealed sample<br />

was scanned by a differential scanning calorimeter (SII<br />

DSC5100, Japan) from 30 to 120 °C at 0.5 °C min –1 . Also,<br />

water-insoluble powder of rice was analyzed in the same manner.<br />

Ethanol precipitate of the water-soluble fraction was dissolved<br />

into 90% formic acid (1% w/v) in a screw-capped vial<br />

and heated at 100 °C for 3 h. Hydrolysates were dried up in<br />

vacuo and resuspended into 10% trifluoroacetic acid and heated<br />

at 100 °C for 3 h. Complete hydrolysates were dried up in<br />

vacuo, then reduced by NaBH 4 and acetylated by acetic<br />

anhydrate. The obtained alditol acetates underwent GC-MS<br />

analysis to obtain constituent sugars.<br />

Results and discussion<br />

Effect of the water-soluble fraction<br />

on pasting properties of rice flour<br />

Under conventional RVA conditions (G1), Hakuchoumochi had<br />

a lower peak viscosity. When the soaking time was prolonged<br />

(G2), peak viscosity was the lowest. The presence of copper<br />

sulfate, as an amylase inhibitor, dramatically increased the peak<br />

viscosity of glutinous varieties. However, Koshihikari was less<br />

affected by the addition of copper sulfate. The results suggested<br />

that an endogenous component, which was sensitive<br />

for in<strong>here</strong>nt amylase activity in rice, affected rice pasting behavior.<br />

In glutinous varieties, the amylase-sensitive component<br />

might be present in a larger amount. Removal of the wa-<br />

262 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Viscosity (cP)<br />

G1 with CuSO 4<br />

2,400<br />

1,800<br />

G4 with CuSO 4<br />

1,200<br />

G3 with CuSO 4<br />

G4 with water<br />

G1 with water<br />

600<br />

G3 with water<br />

0<br />

0 3 6 9 12<br />

Time (min)<br />

Fig. 1. RVA profile of rice flour (with and without water-soluble fraction) in water and in CuSO 4 solution.<br />

ter-soluble fraction (G3 and G4) showed no peak increasing<br />

even with an amylase inhibitor. T<strong>here</strong>fore, it is suspected that<br />

the water-soluble fraction contains the substance, which affects<br />

pasting properties and is sensitive for in<strong>here</strong>nt amylase<br />

activity.<br />

Effect of amylase activities on the water-soluble<br />

fraction<br />

Figure 2 shows an example of a GPC profile of the watersoluble<br />

fraction. The water-soluble fraction contained an expected<br />

peak as water-soluble polysaccharide, when in<strong>here</strong>nt<br />

amylase activities were inhibited by copper sulfate or heating.<br />

The peak disappeared when suspensions were allowed to mix<br />

for 30 min by RVA. However, when an amylase inhibitor such<br />

as copper sulfate was added after 10 min, the peak remained,<br />

which corresponds to the water-soluble polysaccharide. These<br />

results suggested that water-soluble polysaccharide was extremely<br />

sensitive to in<strong>here</strong>nt rice amylase. Since the heating<br />

procedure inhibited in<strong>here</strong>nt amylase activities, high-temperature<br />

drying might control the digestion of water-soluble<br />

polysaccharide through denaturation of in<strong>here</strong>nt amylase.<br />

Elution of water-soluble polysaccharide<br />

from broken rice<br />

Even less physical force was applied on the rice kernel for the<br />

preparation of broken rice. Water-soluble polysaccharide was<br />

eluted in GPC analysis. T<strong>here</strong>fore, water-soluble polysaccharide<br />

was not categorized as “damaged starch,” which might be<br />

produced during longer grinding (Chen et al 1988, 1999).<br />

Obtained DSC thermograms of water-soluble polysaccharide,<br />

water-insoluble powder, and original rice flour of<br />

Hakuchoumochi indicated that the water-soluble fraction never<br />

gelatinized, and the thermal properties of rice may be represented<br />

by water-insoluble powder. Water-insoluble powder is<br />

considered to represent “wet-milled” rice flour. T<strong>here</strong>fore, the<br />

wet-milling process might be a process to remove water-soluble<br />

polysaccharide, which might affect gelatinization (Chen et al<br />

1988, 1999).<br />

Constituent analysis of water-soluble<br />

polysaccharides<br />

All samples showed constituents as glucose only. Thus, watersoluble<br />

polysaccharide in rice was expected as a homoglycan<br />

built from glucose.<br />

With these properties, water-soluble polysaccharide was<br />

easily digested by in<strong>here</strong>nt rice amylase, then released oligosaccharides,<br />

which show lower viscosity in RVA and “stickiness”<br />

Session 8: Improving rice quality 263


Water-soluble polysaccharide<br />

Oligosaccharide<br />

Copper sulfate<br />

Water<br />

V 0<br />

CuSO 4 , 10 min<br />

CuSO 4<br />

Heated<br />

0 2.5 5.0 7.5 10.0 12.5<br />

Min<br />

Fig. 2. GPC profile of water-soluble fraction on amylase digestion (Hakuchoumochi).<br />

on the surface of products. T<strong>here</strong>fore, the polysaccharide might<br />

work like “cement” in rice gel, which is considered as “concrete.”<br />

These results might be a clue to understanding pasting<br />

of rice, and this is needed to understand rice gel, not only starch,<br />

but also polysaccharides. However, further studies are needed<br />

to elucidate more detailed properties of polysaccharide.<br />

References<br />

Chen JJ, Lu S, Lii CY. 1988. Thermal characteristics and microstructure<br />

changes in waxy rice flours by different milling<br />

methods. Food Sci. 25:314-330.<br />

Chen JJ, Lu S, Lii CY. 1999. Effects of milling on the physicochemical<br />

characteristics of waxy rice in Taiwan. Cereal Chem.<br />

76:796-799.<br />

Horino T, Ondona A, Kusumoto K, Soegusa T, Mori Y. 1988. Novel<br />

water-soluble polysaccharide from rice. <strong>Research</strong> highlights<br />

on food research, NFRI. (In Japanese.)<br />

Kikuchi H. 1998. Studies on chemical components in rice kernel for<br />

breeding. Hokkaido Pref. Agric. Res Report. 1998:1-68.<br />

Matsukura U, Suzuki Y, Iwai Y, Monma M, Kaneko N. 2004. Comparison<br />

of α-amylase activity in rice grains of nonglutinous<br />

and glutinous varieties and effect of α-amylase activity on<br />

rice pasting property. Nippon Shokuhin Kagaku Kougaku<br />

Kaishi. 51(10):554-558. (In Japanese.)<br />

Tungtrakul P, Yoshihashi T. 2001. Elucidation of amylase effect on<br />

amylopectin chain distribution in various rice flour. Report<br />

submitted to JIRCAS. 8 p.<br />

Notes<br />

Authors’ addresses: Tadashi Yoshihashi and Eizo Tatsumi, Japan<br />

<strong>International</strong> <strong>Research</strong> Center for Agricultural Sciences<br />

(JIRCAS), Tsukuba 305-8686, Japan; Vipa Surojanametakul,<br />

Patcharee Tungtrakul, and Warunee Varanyanond, <strong>Institute</strong> of<br />

Food <strong>Research</strong> and Product Development (IFRPD), Kasetsart<br />

University, 50 Phahonyothin Road, Chatuchak, Bangkok<br />

10900, Thailand, e-mail: tadashi@jircas.affrc.go.jp.<br />

264 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Wrap-up of Session 8<br />

Session 8 featured six oral presentations on rice quality. Four<br />

related to the chemistry of rice, grain quality, and eating quality,<br />

and two related to human health.<br />

K.R. Bhattacharya from the <strong>Rice</strong> <strong>Research</strong> and Development<br />

Center, India, covered “The chemical basis of rice end-use<br />

quality.” He gave an overview and history of research on rice<br />

quality worldwide. Amylose was the single largest determinant of<br />

rice end-use quality, but was not sufficient. The texture of cooked<br />

rice and other rice end-use qualities is now attributed mainly to<br />

the relative abundance of long chains in its amylopectin. The<br />

author said that the true amylose content in rice starch was less<br />

than 10%. But B. Juliano said that amylose content was at least<br />

15%. So, we need further investigation on true amylose content.<br />

The length (degree of polymerization) of the long chains of amylopectin<br />

was also discussed.<br />

The second speaker, K. Cheaupun from the Pathumthani<br />

<strong>Rice</strong> <strong>Research</strong> Center, Thailand, discussed “<strong>Rice</strong> grain quality<br />

improvement in Thailand.” She explained the classification and<br />

standards of Thai rice. The standards for white rice are grades,<br />

grain classification (length), grain composition, defects, and milling<br />

degree. For Thai aromatic rice (Thai Hom Mali <strong>Rice</strong>), the standards<br />

are Thai Hom Mali <strong>Rice</strong> content, average grain length,<br />

amylose content, and alkali spreading value. She explained the<br />

recommended rice varieties and their main production areas.<br />

Physical grain quality is determined by grain dimension, chalkiness,<br />

and milling quality. Cooking quality is determined by amylose content,<br />

gelatinization temperature, and aroma. Finally, she explained<br />

inspections and postharvest management.<br />

M. Fitzgerald from <strong>IRRI</strong> explained “New tools for understanding<br />

starch synthesis.” She told of the starch synthesis that<br />

affects starch structure. She analyzed the molecular weight distribution<br />

of debranched starch and explained the synthesis of<br />

amylopectin chains (control of chains and random growth) and<br />

amylopectin architecture (amorphous and crystalline lamellae).<br />

In addition, she suggested that t<strong>here</strong> was a third starch that<br />

differed from amylopectin in its size and its spatial separation in<br />

the amorphous growth rings. She proposed calling this starch<br />

“amyloglycan.” After her talk, T. Yoshihashi said that he had found<br />

a similar new starch component susceptible to amylase.<br />

Professor K. Hatae from Ochanomizu University, Japan,<br />

discussed “Textural differences between indica and japonica varieties<br />

in cooked rice.” She used a japonica variety, Nipponbare,<br />

an indica variety, Khao Dawk Mali, and an unknown high-amylose<br />

Thai rice that had a different texture of cooked rice. The<br />

results indicated that the higher the solid content and amylopec-<br />

tin of the extract from the surface layer of the cooked rice, the<br />

more sticky the cooked rice. Moreover, the distribution of amylose<br />

in the rice grain was also an important factor in the stickiness<br />

of cooked rice.<br />

These four presentations indicated that amylose is an important<br />

factor but not enough to explain the eating quality of rice.<br />

The structure of amylopectin (chain length distribution) is also an<br />

important factor. Additionally, the existence of a third component,<br />

amyloglycan, is suggested and it is interesting to consider<br />

how amyloglycan contributes to rice quality.<br />

The next two presentations related to human health. Professor<br />

J. Haas from Cornell University (USA) covered the “Biological<br />

efficacy of consuming rice biofortified with iron.” The authors<br />

conducted a double-blind, longitudinal (9 months), and intervention<br />

study with religious sisters in the Philippines. The provision<br />

of additional dietary iron from biofortified rice contributed<br />

to a 20% increase in daily iron intake for diets that were ironpoor.<br />

The additional iron from biofortified rice was insufficient,<br />

but it significantly reduced the number of women who had deficient<br />

iron intakes. T<strong>here</strong> was a biologically significant effect of<br />

consuming rice biofortified with iron on increases in plasma ferritin<br />

and total body iron for women who were initially not anemic.<br />

This was the first demonstration that plant breeding for enhanced<br />

micronutrient quality had a positive biological impact on the individuals<br />

who consumed the rice. One question addressed whether<br />

milling affected iron content. The answer was that milling did<br />

reduce iron content because most of the iron was in the bran<br />

that was removed by milling and polishing. The high-iron variety<br />

seemed to retain more iron in the endosperm than other varieties.<br />

The final presentation was given by T. Sato from the National<br />

Agricultural <strong>Research</strong> Center for Kyushu Okinawa Region,<br />

Japan, on “Radical-scavenging activity of red and black rice.”<br />

The author told us that red rice contained the highest activity.<br />

Results from sequential extraction with six different polar solvents<br />

showed that the highly polar solvents, methanol, and deionized<br />

water extracts from all red, black, and white rice had 1,1-<br />

diphenyl-2-picrylhydrazyl radical- and tert-butyl hydroperoxyl radical-scavenging<br />

activity. In addition, the acetone extract from only<br />

red rice had the highest activity. The major component responsible<br />

for the radical scavenging in the acetone extract from red<br />

rice was proanthocyanidin. It would be interesting to study whether<br />

consuming red rice is good for human health. Now, the authors<br />

are investigating the physiological functions of red rice in vivo<br />

and elucidating the mechanisms at work in these functions.<br />

Session 8: Improving rice quality 265


SESSION 9<br />

Developing new uses of rice<br />

CONVENER: K. Ohtsubo (NFRI)


Overview of rice and rice-based products<br />

Bienvenido O. Juliano<br />

<strong>Rice</strong> (Oryza sativa L.) and rice-based products derived from<br />

rice grain and rice flour include parboiled rice; quick-cooking<br />

rice and ready-to-eat convenience foods; rice flours; rice starch;<br />

cakes and puddings; baked breads and crackers; breakfast cereals<br />

and expanded rice products; extrusion-cooked and puffedrice<br />

snacks; noodles, paper, and pasta; baby/weaning foods;<br />

fermented foods and beverages; pet foods; and bran products<br />

(Juliano 2003). The rice ingredient is preferably aged to have<br />

predictable, stable functional properties, and freshly milled and<br />

well-milled for minimal initial fat rancidity and long shelf life.<br />

The rice ingredient in most of these products has the same<br />

apparent amylose content (AC) type as that of the preferred<br />

table rice in the country. Milled rice AC (on a dry-weight basis)<br />

is classified into waxy (0–2% dry basis) and nonwaxy:<br />

low (12–20%), intermediate (20–25%), and high (25–33%).<br />

Waxy and low-AC rice are used for alcoholic beverages because<br />

of the higher enzymic conversion of starch to glucose<br />

than high-AC rice, and for products requiring starch-gel stability<br />

of wet products. High-amylose rice is preferred for products<br />

requiring an intact cooked product, resistant to disintegration,<br />

although it may be harder in texture.<br />

Traditional rice products in developing countries are<br />

small-scale and poorly packaged, and have a short shelf life.<br />

Improvement of value-added traditional rice products, selected<br />

based on marketability and profitability, will create jobs in rural<br />

areas and make a country’s products compete globally as import<br />

substitutes or as exports to niche markets.<br />

Semiwet-milled rice flour<br />

The availability of a semiwet (semidry)-milled rice flour of<br />

specified AC (waxy, intermediate-AC, and high-AC) is crucial<br />

to the development of the rice products industry in the<br />

Philippines, since a dry-milled flour cannot be used in many<br />

baked and steamed products requiring a fine flour with little<br />

starch damage. By contrast, wet-milled and semiwet-milled<br />

rice flours can be used in all rice products and are whiter than<br />

dry-milled flour. However, wet-milling is tedious and a source<br />

of environmental pollution. Yeh (2004) considered semidry-/<br />

semiwet-milled rice flour as that produced from steeped milled<br />

rice (30% water) with a roller mill, a stamp mill, and a pin<br />

mill, without water added during milling. Its starch is reported<br />

to be 40% gelatinized from heat generated during milling,<br />

which may affect its functional properties. It has lower contents<br />

of protein, lipids, ash, and reducing sugars than dry-milled<br />

flour. The development and production of semiwet rice flour<br />

of uniform properties (specified AC) to replace wet-milled flour<br />

should improve the efficiency of small and medium rice enterprises<br />

since the tedious wet-milling step can be dispensed with.<br />

Starch properties<br />

Thermal properties of starch of importance to product quality<br />

include gelatinization temperature (GT) and degree of gelatinization,<br />

amylose-lipid complex I (melting at temperatures<br />

100°C), and staledamylopectin<br />

melting (45–60 °C). Final GT represents the temperature<br />

when at least 90% of the starch granules have swollen<br />

in hot water with loss of crystallinity. Residual ungelatinized<br />

starch may affect product properties. Parboiling studies showed<br />

that low-GT samples tended to have amylose-lipid complex I,<br />

and intermediate-high-GT rice tended to have amylose-lipid<br />

complex II in parboiled rice (Biliaderis et al 1993). The presence<br />

of amylose-lipid complex II in pressure-parboiled rice<br />

(>100 °C) may explain the hard texture of its cooked rice since<br />

amylose-lipid complex II does not melt during rice cooking.<br />

<strong>Rice</strong> noodles and corn starch noodles have a similar texture<br />

when freshly cooked. However, the cooked rice noodles<br />

are more stable, even on reheating, and have a better shelf life,<br />

w<strong>here</strong>as the corn starch noodles become mushy on reheating<br />

and readily spoil. Is this because of the greater stability of starch<br />

gels of high-AC rice relative to nonwaxy corn Or is it because<br />

of the presence of more protein in milled rice (7%) that<br />

is reported to contribute to the stability of rice starch gel (C.R.<br />

Mitchell, California Natural Products, 1994, unpublished<br />

data) Corn starch has only 0.7–1.0% protein.<br />

The glycemic index is the relative increase in plasma<br />

glucose within 3 h after a fasted subject ingests 50 g of carbohydrate,<br />

with white bread or glucose taken as 100%. It is used<br />

as a guide for diets of noninsulin-dependent diabetes mellitus<br />

patients. The glycemic index tends to be higher for cooked<br />

waxy and low-AC rice than for cooked intermediate- and high-<br />

AC rice (Table 1) (Panlasigui 1989, Foster-Powell and Brand-<br />

Miller 1995, Juliano 2003). Cooking processes that allow<br />

amylose staling such as parboiling and noodle extrusion further<br />

reduce the glycemic index of intermediate- to high-AC<br />

rice. Processes that suppress amylose staling such as puffing<br />

and precooking increase the glycemic index of all rice. However,<br />

varietal differences in glycemic index are shown in<br />

molded puffed brown rice cake.<br />

Filipino consumers (laborers) prefer rice that is more<br />

filling (Unnevehr et al 1992), for example, high-AC PSBRc10.<br />

Satiety is defined as the state of being fed or gratified to capacity.<br />

Boiled rice and molded puffed brown rice cake with a<br />

higher glycemic index and lower AC tended to have less perceived<br />

satiety and greater subsequent food intake than high-<br />

AC rice (Holt and Brand Miller 1995, Tetens et al 2003). The<br />

satiety situation for waxy and intermediate-AC rice should be<br />

determined. The glycemic index of intermediate-AC rice tended<br />

268 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. Effect of apparent amylose content (AC) and processing on the glycemic index in humans of rice<br />

and rice products (Panlasigui 1989, Foster-Powell and Brand-Miller 1995, Juliano 2003).<br />

<strong>Rice</strong> product<br />

Glycemic index a (% of white bread)<br />

Waxy/low AC (0–20%) Intermediate/high AC (20–33%)<br />

Milled rice 116 ± 23, 126 ± 16/126 ± 4 (2) 81 ± 3 (13)/83 ± 11 (2)<br />

Brown rice 112 ± 11/116 ± 10 (2) –/94 ±10, 83 ± 12<br />

<strong>Rice</strong> bran –/27 ± 4 –/–<br />

Parboiled milled rice 133 ± 12/124 ± 10 68 ± 4 (13)/69 ± 9, 66 ± 8<br />

Noodles/pasta –/131 ± 11 –/50 ± 10, 58 ± 12, 83 ± 5<br />

Precooked/instant rice –/128 ± 10 –/132 ± 10<br />

<strong>Rice</strong> bubbles/krispies –/126 ± 10 (2), 117 ± 5 –/–<br />

Puffed brown rice cake, molded –/117 ± 16, 128 ± 10 –/85 ± 7<br />

a<br />

Mean ± standard deviation. Numbers of samples in parentheses, if mean of more than one sample. The glycemic index based on<br />

glucose is 0.70 of the glycemic index based on white bread.<br />

Table 2. In vivo resistant starch in cooked rice and rice products of various amylose<br />

(AC) and gelatinization temperature (GT) types as measured in five growing rats (Eggum<br />

et al 1993) and in an ileostomate (Jenkins et al 1987).<br />

AC type Resistant starch a (%)<br />

<strong>Rice</strong> product (%)<br />

Low GT<br />

Interm.-high GT<br />

Boiled rice Waxy and low (0–20%) R 0.0 a<br />

Intermediate (20–25%) R 1.5 b, H 3.9<br />

High (25–33%) R 0.4 a R 3.4 c<br />

Very high (40%)<br />

R 1.7 b<br />

Parboiled (100 °C) High (25–33%) R 3.7 c R 1.7 b<br />

Very high (40%)<br />

R 1.2 b<br />

Pressure-parboiled Intermediate (20–25%) H 3.6 ± 0.9 (4)<br />

High (25–33%) R 4.9 d R 2.1 b<br />

Instant rice Intermediate (20–25%) H 5.1<br />

<strong>Rice</strong> noodles High (25–33%) R 2.7 bc<br />

<strong>Rice</strong> Chex Low (10–20%) H 2.9<br />

a R = rat, H = human. Values followed by the same letter are not significantly different at the 5% level by<br />

Duncan’s multiple range test. Mean ± standard deviation.<br />

to overlap with that of high-AC rice, and waxy and low-AC<br />

rice have a similar glycemic index (Table 1).<br />

The resistant starch (staled amylose) in boiled rice is<br />

low at 0–4% in milled rice and tends to increase with AC, GT,<br />

and cooking time (Table 2) (Jenkins et al 1987, Eggum et al<br />

1993). The total dietary fiber (TDF)/neutral detergent fiber is<br />

0.7–2.3% of milled rice and 2.9–4.0% of brown rice. Brown<br />

rice has a lower TDF content than whole-wheat grain, with a<br />

minimum TDF of 5.6%. The increase in TDF during cooking<br />

of nonwaxy rice is due to the formation of resistant starch. The<br />

IR36-based amylose extender mutant with 40% AC can still<br />

be cooked in boiling water and was not lower in glycemic index<br />

than the high-AC intermediate-GT parent. It contains both<br />

elongated (B type) and normal polyhedral starch granules. Its<br />

in vivo resistant starch in rats was surprisingly lower than that<br />

of high-AC intermediate-GT rice (Table 2). Its TDF was also<br />

lower (7.5%) than that reported for high-amylose corn mutants<br />

(30–40%) that are cooked only by autoclaving (>100 °C).<br />

Other nutritional concerns<br />

The effects of food processing on protein quality, mycotoxin<br />

level, acrylamide content, and level of antioxidants have to be<br />

monitored to ensure maintenance of the nutritive value of the<br />

rice product (Juliano 2003). The amino acids lysine and cysteine<br />

are sensitive to heat, particularly during toasting of expanded<br />

rice. Hydrogen sulfide is produced during extrusion<br />

cooking of rice. Alkaline treatment may induce the formation<br />

of lysinoalanine, a carcinogen. Mycotoxin is a problem with<br />

wet grain, including delayed drying after harvest and parboiled<br />

rice. It is concentrated in the bran layer.<br />

Acrylamide, a carcinogen, was analyzed in 2002 because<br />

of its presence in high levels in baked and fried cereals and<br />

potato, but absence in boiled cereals, including rice (NFA<br />

2002). Acrylamide is produced by the Maillard reaction of free<br />

asparagine with free sugars. Developments in research on high<br />

acrylamide levels in foods should be closely monitored as they<br />

relate to baked, fried, and toasted rice products.<br />

Session 9: Developing new uses of rice 269


The high level of antioxidants in rice bran—γ-oryzanols,<br />

tocopherols, and tocotrienols—as reflected in high (3–7%)<br />

unsaponifiable matter in bran oil contributes to the<br />

hypocholesterolemic effect and other health benefits of fullfat<br />

bran. γ-oryzanols are a group of ferulic acid esters of sterols<br />

and triterpenoid alcohols (4,4-dimethylsterols). <strong>Rice</strong> bran<br />

is also rich in the water-soluble antioxidant phytic acid. Significant<br />

amounts of antioxidants are lost during the various<br />

steps of rice-bran oil processing. With the popularity of virgin<br />

coconut oil in the region, the production of virgin rice-bran oil<br />

with superior levels of antioxidants as a functional food/<br />

nutraceutical could be considered as a cottage industry near<br />

rice mills. However, oil extraction may be a problem since<br />

rice bran has a lower fat content (15%) than coconut meat<br />

(33%). Virgin rice-bran oil may be blended with virgin coconut<br />

oil with a high content of medium-chain fatty acids (8:0 to<br />

12:0) to combine the healing properties of coconut oil with the<br />

antioxidant properties of rice-bran oil.<br />

These are important considerations in the formulation<br />

of new rice products.<br />

References<br />

Biliaderis CG, Tonogai JR, Perez CM, Juliano BO. 1993.<br />

Thermophysical properties of milled rice starch as influenced<br />

by variety and parboiling method. Cereal Chem. 70:512-516.<br />

Eggum BO, Juliano BO, Perez CM, Acedo EF. 1993. The resistant<br />

starch, undigestible energy and undigestible protein contents<br />

of raw and cooked milled rice. J. Cereal Sci. 18:159-170.<br />

Foster-Powell K, Brand-Miller J. 1995. <strong>International</strong> tables of glycemic<br />

index. Am. J. Clin. Nutr. 62:869S-893S.<br />

Holt SHA, Brand Miller J. 1995. Increased insulin response to ingested<br />

foods is associated with lessened satiety. Appetite 24:43-<br />

54.<br />

Jenkins DJA, Cuff D, Wolever TMS, Knowland D, Thompson L,<br />

Cohen Z, Prokipchuk E. 1987. Digestibility of carbohydrate<br />

foods in an ileostomate: relationship to dietary fiber, in vitro<br />

digestibility, and glycemic response. Am. J. Gastroenterol.<br />

82:709-717.<br />

Juliano BO. 2003. <strong>Rice</strong> chemistry and quality. Muñoz, Nueva Ecija<br />

(Philippines): Philippine <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>. 480 p.<br />

NFA (National Food Administration). 2002. Analytical methodology<br />

and survey results for acrylamide in foods. Uppsala (Sweden):<br />

NFA. 2 p.<br />

Panlasigui LN. 1989. Glycemic response to rice. PhD dissertation.<br />

Toronto, Ontario (Canada): Department of Nutritional Sciences,<br />

University of Toronto. 171 p.<br />

Tetens I, Kabir KA, Parvin S, Thilsted SH. 2003. Differential rates<br />

of energy release from rice and effects on satiety. In: Mew<br />

TM, Brar DS, Dawe D, Hardy B, editors. <strong>Rice</strong> science: innovations<br />

and impact for livelihood. Proceedings of the <strong>International</strong><br />

<strong>Rice</strong> <strong>Research</strong> Conference, 16-19 September 2002,<br />

Beijing, China. Los Baños (Philippines): <strong>International</strong> <strong>Rice</strong><br />

<strong>Research</strong> <strong>Institute</strong>. p 421-430.<br />

Unnevehr LJ, Duff B, Juliano BO, editors. 1992. Consumer demand<br />

for rice grain quality. Terminal Report IDRC Projects. National<br />

Grain Quality (Asia) and <strong>International</strong> Grain Quality<br />

Economics (Asia). Manila (Philippines): <strong>International</strong> <strong>Rice</strong><br />

<strong>Research</strong> <strong>Institute</strong>, and Ottawa (Canada): <strong>International</strong> Development<br />

<strong>Research</strong> Centre. 248 p.<br />

Yeh A-I. 2004. Preparation and applications of rice flour. In: Champagne<br />

ET, editor. <strong>Rice</strong> chemistry and technology. 3rd ed. St.<br />

Paul, Minn. (USA): American Association of Cereal Chemists.<br />

p 495-539.<br />

Notes<br />

Author’s address: Philippine <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>, Los Baños,<br />

College Laguna 4031, Philippines, e-mail:<br />

bjuliano@laguna.net.<br />

Sterilization effect of electrolyzed water on rice food<br />

Seiichiro Isobe, Chang-yong Lee, and Kyoichiro Yoshida<br />

Recently, a lot of instant foods have been made from rice. The<br />

main categories are aseptic packaged rice and rice cookies. In<br />

this food process, the control of microorganisms, especially<br />

heat-resistant spores from raw materials to products, is the most<br />

important point to confirm safety in product flow. If the heatresistant<br />

spores can be controlled by pretreatment before cooking,<br />

excess heat should be omitted to make long shelf-life rice<br />

products, thus improving the quality of the products. Several<br />

papers have demonstrated the sterilization effects of electrolyzed<br />

water on food ingredients (Koseki et al 2004a,b).<br />

In this paper, we try to confirm the sterilization effect on<br />

rice using electrolyzed water and check the quality of rice during<br />

pretreatment.<br />

Materials and methods<br />

Electrolyzed water is produced by electrolyzing tap water with<br />

the addition of a small quantity of NaCl. Acidic electrolyzed<br />

water (AcEW) created at the anode has been observed to have<br />

sterilization effects on microorganisms, and alkaline electrolyzed<br />

water (AlEW) created at the cathode has been observed<br />

to have a rinsing effect on organic compounds. In Japan, AcEW<br />

already was approved as an indirect food additive in 2002.<br />

The principle of electrolyzed water is shown in Figure 1.<br />

We used a flow-type electrolyzed water producer (Rox-<br />

20TA: Hoshizaki Electric Co., Japan). This apparatus generates<br />

electrolyzed water by the electrolysis of a dilute (0.1%)<br />

saline solution in an electrolytic cell separated into an anode<br />

and cathode region with a diaphragm. The current passing<br />

270 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Acid-electrolyzed<br />

water for<br />

sterilization<br />

Alkalineelectrolyzed<br />

water<br />

Survival number (Log cfu g –1 )<br />

5<br />

HCl<br />

HClO<br />

NaOH<br />

+<br />

Cl 2<br />

H 2<br />

–<br />

H + OH –<br />

Cl – Na +<br />

~Chemical reaction~<br />

:<br />

2OH – ®H 2<br />

O+1/2O 2<br />

+<br />

2e –<br />

2Cl – ®Cl 2<br />

+2e –<br />

Cl 2<br />

+H 2<br />

®HClO+HCl<br />

(low pH condition)<br />

HClO®H + +ClO –<br />

(high pH condition)<br />

:<br />

2H + +2e – ®H 2<br />

4<br />

3<br />

2<br />

1<br />

NaCl<br />

Tap water<br />

with NaCl<br />

NaCl<br />

Separation<br />

membrane<br />

Fig. 1. Principle of acidic electrolyzed water. Left: process<br />

flow of apparatus, right: chemical reaction during electrolyzing<br />

process.<br />

0<br />

A B C D<br />

Fig. 2. Sterilization effects of combination of<br />

electrolyzed water on rice preparation. (A) Control<br />

rice, (B) washing with AlEW (5 min), (C)<br />

soaking with AcEW (30 min) after B treatment,<br />

(D) soaking with D/W (30 min) after C treatment.<br />

through the electrolysis apparatus and voltage between the electrodes<br />

were set at 14A and 18V, respectively. AcEW was prepared<br />

within the anode region of the electrolytic cell, and AlEW<br />

was prepared within the cathode region. The physicochemical<br />

properties of electrolyzed water are as follows:<br />

AcEW: pH 2.7, oxidation reduction potential (ORP)<br />

1,481 mV, available chlorine concentration 51.5 ppm.<br />

AlEW: pH 11.6, ORP –576 mV.<br />

We used distilled water as a control processing solution.<br />

Polished rice (Kinuhikari) was purchased and used as a<br />

sample. Prepared Bacillus subtillis PCI219 was used as a heatresistant<br />

spore sample.<br />

Some 1 mL of spore solution (10 9 cfu mL) was added to<br />

9 mL of AcEW and mixed. The sample was collected from the<br />

mixed solution every 1 min and the survival number counted<br />

in each sample after cultivation.<br />

Some 100 g of polished rice were prepared for each<br />

preparation test. We devised a preparation process with 3 stages<br />

(washing: 5 min, soaking 1 ½ min, soaking 2 ½ min). We used<br />

AcEW, AlEW, and distilled water, respectively, as each stage<br />

solution. pH and color of rice were measured by a conventional<br />

pH meter and color meter.<br />

To confirm the microorganism control effect, we added<br />

the B. subtillis spore into the rice and we counted the survival<br />

number in each sample of the preparation test.<br />

Results and discussion<br />

We examined several tests to prove the influence on the microorganism<br />

and the change in the raw rice.<br />

AcEW and AlEW changed the color and pH of rice rapidly.<br />

But, when the rice was treated with a combination of electrolyzed<br />

water (washing with AlEW, soaking with AcEW, and<br />

soaking with distilled water), pH and color of the treated rice<br />

were no different from conventional washing and soaking with<br />

distilled water.<br />

AcEW showed a strong effect on microorganism control,<br />

even on heat-resistant spores in vitro. However, in the<br />

rice preparation test, AcEW could not kill B. subtillis spores<br />

on the rice completely. But, after washing by AlEW, AcEW<br />

could kill completely. So, finally, we set the optimum method<br />

of combination of electrolyzed water as follows. To remove<br />

rice bran powder and other foreign materials that coat the surface<br />

of the raw rice, at first we washed the rice with AlEW for<br />

5 min and soaked it with AcEW to sterilize microorganisms<br />

for 30 min. Then, to remove the odor of chlorine and to revert<br />

the pH level, we resoaked the rice with distilled water for 30<br />

min. Figure 2 shows the effects against microorganisms using<br />

the combination process of each electrolyzed water.<br />

In this experiment, we could confirm the effect of the<br />

combination of electrolyzed water on microorganism control.<br />

This effect can be considered the result of available chlorine<br />

concentration and the rapid change in pH and it raises the sen-<br />

Session 9: Developing new uses of rice 271


sibility on the microorganism. From this experiment we can<br />

see the importance of the contact condition of the microorganism<br />

with the electrolyzed water, which increased the effect of<br />

sterilization.<br />

We concluded that the combination of electrolyzed water<br />

for rice preparation before cooking (washing and soaking)<br />

is efficient in reducing heat-resistant microorganisms; t<strong>here</strong>fore,<br />

this process will be able to help make rice products with<br />

a long shelf-life without excess heat treatment to keep the quality<br />

of these products.<br />

In this experiment, we did not evaluate the quality (texture,<br />

flavor, chemical components, and so on) of the cooked<br />

rice. We must consider this quality before introducing this pretreatment.<br />

References<br />

Koseki S, Yoshida K, Isobe S, Itoh K. 2004a. Efficacy of acidic<br />

electrolyzed water for microbial decontamination of cucumbers<br />

and strawberries. J. Food Prot. 67(6):1247-1251.<br />

Koseki S, Yoshida K, Kamitani Y, Isobe S, Itoh K. 2004b. Effect of<br />

mild heat pre-treatment with alkaline electrolyzed water on<br />

the efficacy of acidic electrolyzed water against Escherichia<br />

coli O157:H7 and Salmonella on lettuce. Food Microbiol.<br />

21:559-566.<br />

Notes<br />

Authors’addresses: Seiichiro Isobe, National Food <strong>Research</strong> <strong>Institute</strong>,<br />

2-1-12 Kannodai, Tsukuba, Ibaraki 305-8642, Japan, e-<br />

mail: seiichi@nfri.affrc.go.jp; Chang-yong Lee, Cheiljedang<br />

Corporation Korea; Kyoichiro Yoshida, Hoshizaki Electric<br />

Co., Japan.<br />

Current status of varietal improvement<br />

and use of specialty rice in Korea<br />

Hae Chune Choi<br />

Korea has maintained self-sufficiency in rice production since<br />

1975, except during severely cold years. However, self-sufficiency<br />

in total cereal food supply, including other cereals, is<br />

still limited to about 54% and to about 30% for total consumption,<br />

including livestock feeds. <strong>Rice</strong> products, the staple food<br />

in Korea, cover 23% of farmers’ income and 41% of total agricultural<br />

resources, and provide 35% of caloric intake and<br />

21% of protein intake per capita at present.<br />

Historically, the continuous improvement of Tongil-type<br />

high-yielding rice cultivars greatly contributed to self-sufficiency<br />

in rice production through the so-called Green Revolution<br />

during the 1970-1980s. Moreover, the development of<br />

high-yielding and high-quality japonica rice cultivars during<br />

the 1980-1990s played a major role both in ensuring self-sufficiency<br />

of rice production and in enhancing the competitiveness<br />

of rice products under free trade. We believe that we have<br />

the most advanced techniques in rice breeding and maintain<br />

the highest level of rice yield potential per hectare while producing<br />

the best-quality rice in the world. However, Korea is<br />

still lagging behind in the international competitiveness of rice<br />

goods primarily because the size of rice farm land is so small<br />

and the production cost is still very high (Choi 2001). It should<br />

also be noted that per capita rice consumption in Korea has<br />

decreased dramatically from 120 kg in 1990 to 83 kg in 2003.<br />

The development of high-quality and specialty rice varieties<br />

should continue to be an important element in rice research.<br />

By developing a variety of rice products other than ordinary<br />

cooked rice, we can increase rice consumption and international<br />

competitiveness.<br />

Achievement of varietal improvement in specialty rice<br />

The target of rice breeding in Korea is to develop high-quality<br />

and high-yielding rice cultivars suitable for labor-saving, lowcost,<br />

and safe grain production under different environmental<br />

conditions. The main direction of the country’s rice breeding<br />

program was on how to increase yield potential and safe grain<br />

production and how to improve marketability and palatability.<br />

Also, efforts to develop various specialty rice varieties started<br />

in the mid-1980s to support an increase in rice consumption<br />

and use through food processing (Choi 2001).<br />

Since 1990, 23 specialty rice cultivars, including glutinous<br />

rice, have been developed. The first specialty rice cultivar<br />

was a large-kernel variety, Daeribbyeo 1, developed in<br />

1993. It has about 1.7 times heavier 1,000-grain weight of 34.8<br />

g than ordinary ones. It showed a good usability for popping<br />

and brewing. In the same year, high-yielding and semidwarf<br />

indica scented rice, Hyangmibyeo 1, was developed. It has a<br />

considerably strong aroma and a good flavor in cooked rice or<br />

processed rice foods such as traditional rice cakes and saccharified<br />

rice beverage. A high-quality japonica scented rice,<br />

Hyangnambyeo, was developed in 1995. Another high-yielding<br />

Tongil-type scented rice, Hyangmibyeo 2, was developed<br />

in 1996. Since then, two scented glutinous rice varieties,<br />

Aranghyangchalbyeo and Seolhyangbyeo, a premium scented<br />

rice, Mihyangbyeo, and a blackish purple-scented rice,<br />

Heughyangbyeo, were developed successively (Table 1).<br />

In 1994, a medium-sized, chalky-kernel rice variety having<br />

suitability for brewing, Yangjobyeo, was developed. An<br />

opaque nonglutinous rice, Seolgaeng, a 9% low-amylose dull<br />

272 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. Development of specialty rice cultivars suitable for food processing. a<br />

Bred Culm Milled 1,000- Chalkiness Color of<br />

Cultivar in Heading length rice yield kernel L/W (WC/WB) seed Aroma Amylose<br />

year date (cm) (t ha –1 ) weight ratio (0–9) coat (0–9) (%)<br />

(g)<br />

Daeribbyeo 1 1993 15 Aug 88 4.45 34.8 1.94 1/0 YW 0 19.5<br />

Hyangmibyeo 1 1993 15 Aug 72 4.93 20.6 2.46 1/1 YW 5 18.3<br />

Hyangnambyeo 1995 11 Aug 82 5.03 21.3 1.81 0/0 YW 3 17.7<br />

Hangmibyeo 2 1996 4 Aug 77 6.14 22.8 2.44 1/2 YW 3 19.0<br />

Yangjobyeo 1994 14 Aug 71 5.11 25.4 1.78 7/0 YW 0 20.2<br />

Aranghyangchalbyeo 1997 13 Aug 88 5.37 20.5 1.90 – YW 3 0.0<br />

Heugjinjubyeo 1997 25 July 80 4.05 17.0 2.22 – BP 1 15.1<br />

Heugnambyeo 1997 13 Aug 73 4.97 23.5 2.14 – BP 1 16.7<br />

Mihyangbyeo 1998 16 Aug 79 5.57 22.6 1.86 0/0 YW 3 19.0<br />

Seolhyangchalbyeo 1999 8 Aug 89 5.23 24.2 2.10 – YW 3 0.0<br />

Goamibyeo 2000 18 Aug 85 5.38 20.8 1.77 0/2 YW 0 26.7<br />

Heughyangbyeo 2000 23 Aug 77 5.28 23.1 1.96 – BP 3 18.0<br />

Jeogjinjubyeo 2000 26 July 81 5.54 22.1 1.79 – RB 0 18.3<br />

Baegjinju 2001 21 Aug 77 5.18 19.2 1.62 Dull YW 0 9.1<br />

Seolgaeng 2001 19 Aug 83 5.27 20.3 1.63 Opaque YW 0 19.3<br />

Yeongan 2001 13 Aug 83 5.45 22.4 1.79 0/1 YW HL 18.9<br />

Goami 2 2002 22 Aug 75 4.24 14.6 1.89 4/4 YW HF 28.1<br />

Manmi 2002 17 Aug 86 4.46 19.9 1.84 0/0 YW 0 12.9<br />

Heugkwang 2003 14 Aug 89 5.05 14.8 1.73 – BP 0 18.0<br />

a<br />

L/W ratio = length/width ratio of brown rice, YW = yellowish white, BP = blackish purple, RB = reddish brown, HL = high lysine, HF = high fiber.<br />

Source: Choi (2004).<br />

mutant rice, Baegjinju, and a high-fiber and high-amylose rice,<br />

Goami 2, were developed through mutation breeding by MNU<br />

(N-methyl-N-nitrosourea) treatment on a premium-quality<br />

japonica rice variety, Ilpumbyeo. Another semiglutinous rice,<br />

Manmi, which has 12.9% amylose content, was developed by<br />

a conventional breeding method using a dull mutant as a parent.<br />

Some colored rice varieties having reddish brown or<br />

blackish purple pericarp were also developed (Table 1). In<br />

2001, a premium-quality rice variety with high lysine content,<br />

Yeongan, was developed. Some specialty rice varieties, such<br />

as blackish purple or reddish brown glutinous rice and giantembryo<br />

glutinous rice, were bred by mutation or from weedy<br />

rice collections (Choi 2004).<br />

The cultivation area of specialty rice, including glutinous<br />

rice, is only about 1.5% of the total rice cultivation area<br />

since its usability and processing have not been fully developed.<br />

Use of specialty rice<br />

The large-kernel and low-amylose rice varieties revealed both<br />

improved popping and brewing characteristics. Their softer<br />

gel consistency and lower amylose content were closely related<br />

to the higher ratio of popped rice grains and also to the<br />

lower bulk density of popped grain in either brown or milled<br />

rice (Choi 2002).<br />

Of the high-amylose and high-protein rice varieties, some<br />

showed a desirable quality of processed rice noodles or rice<br />

bread. The acceptability for noodle formation and eating qual-<br />

ity of cooked noodles might be due to some factors independent<br />

of each other in rice. The potassium and magnesium contents<br />

of milled rice were negatively related to the gross score<br />

of noodle making when mixed with wheat flour half and half<br />

(Choi 2002).<br />

Batters for making brown rice bread had more volume<br />

expansion, better loaf formation, and more springiness in rice<br />

bread. The higher the protein content in rice, the more moist<br />

milled rice bread resulted. The springiness of rice bread was<br />

significantly correlated with high amylose content and hard<br />

gel consistency. A considerably different tendency of acceptability<br />

for rice bread baking among tested rice varieties was<br />

revealed between brown and polished rice (Kang et al 1997).<br />

T<strong>here</strong> was a large varietal difference in suitability for koji<br />

(malted rice) fermentation by either Aspergillus oryzae or<br />

Monascus anka. The nonglutinous rice having opaque endosperm,<br />

Seolgaeng, showed better rooting density of mycelia<br />

and higher saccharogenic power in A. oryzae-fermented<br />

rice, and higher pigment concentration in Monascus anka-fermented<br />

rice when compared with dull or ordinary nonglutinous<br />

rice. The chalky and large-grain rice showed better suitability<br />

for fermentation and brewing than less chalky and smaller rice<br />

(Choi 2002).<br />

Colored rice can be used as natural functional pigments.<br />

The anthocyanin pigment of blackish purple rice showed significantly<br />

high antioxidant and antimutagenic reaction (Kang<br />

2002). The pigments of colored rice are very useful for traditional<br />

colored rice cakes or for brewing colored rice wines.<br />

The extracted anthocyanin pigment can be used for diverse<br />

processed rice foods or for beauty products (Choi 2002).<br />

Session 9: Developing new uses of rice 273


The mutant rice, Goami 2, which has extreme contrasts<br />

in cooking quality and physicochemical and ultrastructural<br />

properties from those of its original variety, Ilpumbyeo (Kang<br />

et al 2003, Kim et al 2004), revealed a considerable “health<br />

effect” by reducing blood glucose and insulin levels in both<br />

normal and obese or diabetic participants after feeding the rice<br />

orally (Lee and Shin 2002). In addition, Goami 2 also demonstrated<br />

an ability to lower the levels of serum triglycerides and<br />

C-peptides in obese persons. However, the diabetic participants<br />

showed no significant reduction in plasma glucose and<br />

BMI (body mass index) after 4 weeks of eating the fiber-rich<br />

Goami 2 rice diet (Lee and Shin 2002, RDA 2004). Goami 2<br />

has low-digestible and high-amylose starch, and has approximately<br />

three times more crude fiber and three-plus times higher<br />

arabinose and xylose contents than the original variety. It has<br />

a significantly low proportion of short-chain frequency in amylopectin<br />

structure compared with its original variety (Kang et<br />

al 2003, Cheong et al 2004). It also showed significantly low<br />

activity in branching enzymes, but remarkably high activity in<br />

ADP-glucose pyrophosphorylase and total starch synthase as<br />

well as UDP-glucose pyrophosphorylase in rice grain during<br />

the rapid filling period (Cheong et al 2004). On the basis of<br />

these data, it is proposed that Goami 2 should be an excellent<br />

candidate for processing a variety of low-digestible, low-calorie<br />

“healthy” food products other than ordinary cooked rice.<br />

Regarding the soaking or germination treatment of brown<br />

rice, the production of γ-aminobutyric acid (GABA), a chemical<br />

that has been shown to contribute diverse health-related<br />

functions to the human body, increased two to three times more<br />

than that in untreated brown rice. Especially, brown rice with<br />

giant-embryo generally exhibited 6–8 times increases in GABA<br />

concentration compared with nonsoaked giant-embryo brown<br />

rice when soaked for 4 hours. This soaked and/or germinated<br />

giant-embryo brown rice may be useful for producing various<br />

foods processed with high “healthy” elements (Nemoto 2001).<br />

Glutinous rice varieties revealed significantly larger<br />

variations in viscogram characteristics, amylopectin structure,<br />

and physical as well as retrogradation properties of cooked<br />

rice. They were classified into nine different varietal groups<br />

based on 11 physicochemical and structural characteristics of<br />

rice endosperm (Fig. 1). Significant positive or negative correlations<br />

were noted in water absorption rates of rice grain,<br />

physical properties of cooked rice, and viscogram characteristics<br />

of rice flour. Especially in japonica glutinous rice, the<br />

breakdown and setback viscosities of rice flour were closely<br />

related to alkali digestibility of milled rice and the stickiness<br />

of cooked rice. The frequency ratio of short glucose chains<br />

(A-chains) to intermediate chains (B-chains), the ratio of B-<br />

chain to long-chain (C-chain) fractions, and the relative frequency<br />

of A- or B-chain fractions in debranched rice starch<br />

were closely related to the breakdown and setback viscosities<br />

of rice flour. T<strong>here</strong> were some close associations between some<br />

of the grain properties in glutinous rice and the respective suitability<br />

for processing various kinds of traditional rice foods<br />

(Choi et al 1999).<br />

1<br />

0<br />

–1<br />

I<br />

III<br />

II<br />

IV<br />

Z 2<br />

VI<br />

V<br />

–1 0 1 2<br />

Fig. 1. Classification of glutinous rice varieties using principal component<br />

analysis, based on physicochemical and structural characteristics<br />

of rice endosperm (11 quality properties). = indica,<br />

= japonica, = javanica. I–IX = varietal groups, Z 1 and Z 2 are<br />

1st and 2nd principal components, respectively, derived from 11<br />

grain quality properties by principal component analysis. (Based<br />

on Choi et al 1999.)<br />

Prospects for specialty rice breeding<br />

Unstable environmental conditions caused by the global greenhouse<br />

effect and unexpected local meteorological disasters may<br />

be continuous problems in rice production. The deterioration<br />

of paddy soil is also expected with the increased air and water<br />

pollution, and the shortage of irrigation water may become<br />

more serious in the future. It is obvious that the greenhouse<br />

effect will result in increased disease incidence and insect pests.<br />

In addition, the pressure of the rice market opening from some<br />

export countries may become increasingly serious, resulting<br />

in an unfavorable situation for maintaining self-sufficiency in<br />

domestic rice supply and demand.<br />

It is urged, t<strong>here</strong>fore, that rice breeders must come to<br />

terms with the outlook of the rice industry and be ready for<br />

unexpected changes in environmental and socioeconomic situations<br />

as well as the trend in world trade. Fortunately, an effective<br />

selection and introduction of useful agronomic target<br />

genes has been made possible recently through the use of DNA<br />

markers linked with target genes and genetic engineering, following<br />

the biochemical pathway and mechanism of the gene<br />

expression being elucidated. Moreover, the possibility of desirable<br />

recombination and the enhancement of useful gene<br />

expression may be gradually realized through the identification<br />

of target gene loci, gene cloning, and transformation. The<br />

genetic variation of rice breeding materials may become further<br />

diversified through the introduction of various useful alien<br />

genes by using biotechnological procedures in the future, and<br />

these may be further helpful for increasing the stability of rice<br />

production and enhancing the healthy competitiveness of rice<br />

products.<br />

The yield potential of milled rice is expected to increase<br />

to 6.5 t ha –1 in specialty japonica rice and to 10.0 t ha –1 in<br />

super-yielding specialty rice in the next ten years. Breeding<br />

efforts for diversification and physicochemical characteristics<br />

VII<br />

VIII<br />

IX<br />

Z 1<br />

274 <strong>Rice</strong> is life: scientific perspectives for the 21st century


in specialty rice grain will be continuously intensified to enhance<br />

the usability for various food-processing and health-related<br />

purposes. Specifically, breeding efforts to enhance healthrelated<br />

functions will focus on developing specialty rice suitable<br />

for particular needs, such as low-allergen rice helpful for<br />

atopic dermatitis patients, low-protein rice beneficial to nephritis<br />

patients, high-lysine or high-sulfur-containing aminoacid<br />

rice, high procarotenoid rice, giant-embryo rice, etc., for<br />

other health-related subjects (Choi 2004).<br />

Multiple resistance to major pests and environmental<br />

stresses suitable for each relevant region must be gradually<br />

strengthened in specialty rice by introducing new gene sources<br />

from wild species and through in situ selection breeding adaptable<br />

to global climatic change.<br />

References<br />

Cheong MY, Park YM, Choi HC, Park YI, Kim SI, Chung YH, Kim<br />

SH. 2004. A rice mutant with altered polysaccharides in grain.<br />

(Unpublished.)<br />

Choi HC, Hong HC, Kim YG, Nahm BH. 1999. Varietal variations<br />

in physicochemcial characteristics and amylopectin structure<br />

of grain in glutinous rice. Korean J. Crop Sci. 44(3):207-213.<br />

Choi HC. 2001. Achievements and advanced technology of rice production<br />

in Korea. In: <strong>Rice</strong> culture in Asia: KCD and ICID,<br />

Seoul. p 55-80.<br />

Choi HC.2002. Current status and perspectives in varietal improvement<br />

of rice cultivars for high-quality and value-added products.<br />

Korean J. Crop Sci. 47(S):15-32.<br />

Choi HC.2004. Principal characteristics of specialty rice cultivars<br />

and regarding cultivation management. Lecture note for advanced<br />

course of elite farmers. 17 p.<br />

Kang HJ, Hwang IK, Kim KS, Choi HC. 2003. Comparative structure<br />

and physicochemical properties of Ilpumbyeo, a highquality<br />

japonica rice, and its mutant Suweon 464. J. Agric.<br />

Food Chem. 51:6598-6603.<br />

Kang MY, Choi YH, Choi HC. 1997. Comparison of some characteristics<br />

relevant to rice bread processing between brown and<br />

milled rice. Korean J. Soc. Food Sci. 13(1):64-69.<br />

Kang MY. 2002. Functional components and efficacy of rice. In:<br />

Illumination of hygienic function in rice and strategy for functional<br />

rice foods. Proceedings of 2002 Spring Symposium of<br />

the Korea Industrial Food Engineering Society. p 35-50.<br />

Kim KS, Kang HJ, Hwang IK, Hwang HG, Kim TY, Choi HC. 2004.<br />

Comparative ultrastructure of Ilpumbyeo, a high-quality<br />

japonica rice, and its mutant Suweon 464: scanning and transmission<br />

electron microscopy studies. J. Agric. Food Chem.<br />

52:3876-3883.<br />

Lee C, Shin JS. 2002. Effects of different fiber content of rice on<br />

blood glucose and triglyceride levels in normal subjects. J.<br />

Korean Soc. Food Sci. Nutr. 31(6):1048-1051.<br />

Nemoto H. 2001. Current status and perspectives of high value-added<br />

and specialty rice production in Japan. Book Series No. 11 of<br />

the Korea <strong>Rice</strong> Technical Working Group. p 97-104.<br />

RDA (Rural Development Administration). 2004. Effect of newly<br />

developed naturally fiber-rich rice (Goami 2) on body weight<br />

and lipid metabolism in Korea. Final report. 41 p.<br />

Notes<br />

Author’s address: National <strong>Institute</strong> of Crop Science, Rural Development<br />

Administration, 209 Seodun, Suwon 441-857, Republic<br />

of Korea, e-mail: hcchoi@rda.go.kr.<br />

Processed novel foodstuffs from pregerminated brown rice<br />

by a twin-screw extruder<br />

Ken’ichi Ohtsubo, Tomoya Okunishi, and Keitaro Suzuki<br />

<strong>Rice</strong> is one of the most important cereals in the world in addition<br />

to wheat and maize. <strong>Rice</strong> production is more than 500<br />

million tons (as paddy per year) in the world and about 90% of<br />

it is produced and consumed as a major staple food in the<br />

densely populated Asian countries.<br />

Processing of rice grains in Japan<br />

<strong>Rice</strong> is processed and used as various kinds of foodstuffs besides<br />

direct food use, such as parboiled rice, fermented rice<br />

wine, rice noodles, rice crackers, rice cakes, rice snacks, rice<br />

flour, and other fermented rice products.<br />

Traditional rice-based convenience foods in Japan<br />

One of the most famous traditional rice-based convenience<br />

foods in Japan is sushi. Sushi originated as a preservative food<br />

of fish using natural fermentation (narezushi). In this case,<br />

cooked rice was used as a substrate with salt for Lactobacillus<br />

bacteria. Nowadays, nigirizushi was invented as an easily prepared<br />

rice dish by pressing cooked rice balls manually and<br />

topping them with sliced raw fish in Tokyo in the 1800s.<br />

(Cooked rice becomes tastier by adding salt, sugar, and vinegar<br />

after cooking.) Soy sauce and grated horseradish (wasabi)<br />

are necessary to enjoy the original taste of sushi.<br />

Onigiri or omusubi is another traditional rice-based convenience<br />

food in Japan. These cooked rice balls wrapped with<br />

bamboo leaves were used as a box lunch for many years.<br />

Breakfast cereals from rice<br />

Breakfast rice cereals are made from rice grains, milled rice<br />

flour, or cooked rice dough. These rice materials are precooked,<br />

dried, flaked, then expanded or puffed and toasted. Examples<br />

Session 9: Developing new uses of rice 275


are puffed rice, rice flakes, and shredded rice cereals. Various<br />

kinds of breakfast cereals were developed and consumed in<br />

the United States, China, Korea, Thailand, Vietnam, and many<br />

other Pacific countries.<br />

Retort rice<br />

Retort rice was developed in the early 1970s in Japan. <strong>Rice</strong><br />

and water are packed in a laminated plastic container and pasteurized<br />

at 120 ºC. Consumers soak this in hot water for 15<br />

min or heat it in a microwave oven for a couple of minutes. Its<br />

shelf-life is more than half a year without refrigeration. The<br />

price is reasonable. Its problems are off-flavor by the excess<br />

heating and the texture of cooked rice grains. Retort rice represented<br />

22,000 tons in Japan in 1996.<br />

Canned rice<br />

Canned rice has a long history of more than 50 years. Milled<br />

rice and water are placed in tin cans, steamed for 30 min, and<br />

sealed and sterilized in a retort at 112 ºC for 80 min. Consumers<br />

heat it in hot water for 15 min before eating. Canned rice<br />

can be stored for several years under natural conditions.<br />

Pregelatinized rice<br />

Cooked and dried rice or pregelatinized rice is prepared by<br />

usual cooking followed by abrupt drying. As its moisture content<br />

is very low, it can be preserved for several years under<br />

natural conditions. It is easy to cook as its starch is<br />

pregelatinized and prevented from retrogradation because of<br />

its low moisture content.<br />

Instant rice, such as Cup <strong>Rice</strong>, is a kind of high-quality<br />

pregelatinized rice. Consumers can eat it by only adding hot<br />

water and keeping it warm for several minutes.<br />

Recently, pregelatinized and packaged rice without excess<br />

drying has been developed in Japan (hayadakimai or<br />

“quick-cooking rice”). Consumers only have to add the tasty<br />

cooking soup or water and cook for about 15 minutes. They<br />

can omit the time-consuming washing of rice, soaking it, and<br />

keeping it warm after cooking. Compared with “instant rice,”<br />

quick-cooking rice is improved in terms of taste and texture.<br />

Although its moisture content is more than 35%, it can be stored<br />

for several months without refrigeration by pasteurization or<br />

by the oxygen absorber. Quality evaluation of these various<br />

kinds of quick-cooking rice, sensory test, gelatinization properties<br />

test, and physical properties measurement were carried<br />

out in our laboratory as a collaborative research activity with<br />

Kiewpie Co. Ltd.<br />

Frozen cooked rice<br />

The market for frozen cooked rice in Japan expanded to<br />

138,000 tons in 1996. Frozen cooked rice is convenient to prepare<br />

with a microwave oven at home and its high quality is<br />

preserved in a freezer for a long time. Its price is higher than<br />

that of other processed rice, but frozen roasted cooked rice<br />

balls or frozen pilaf are very popular among Japanese consumers.<br />

In cooperative research work with a manufacturer of<br />

freezer systems, Mayekawa Co. Ltd., we developed a new<br />

freezing method, “medium-rate freezing,” for frozen cooked<br />

rice balls. Frozen cooked rice balls prepared at a medium rate<br />

had better palatability than those frozen at a slow rate or quick<br />

rate. In addition, their physical properties, hardness, and stickiness<br />

were maintained better than those of others.<br />

Aseptic cooked rice<br />

Aseptic cooked rice was developed within one decade in Japan.<br />

<strong>Rice</strong> grains are washed well to remove bacteria, followed<br />

by cooking and packaging. Because contamination by microorganisms<br />

is very low, this product can be stored for half a<br />

year under natural conditions. As the rice is not heated excessively<br />

as is retort-pouched rice, its eating quality is very good.<br />

Cooked rice distributed at low temperature<br />

Cooked rice and packaged rice in a plastic container are sometimes<br />

shipped and distributed under low temperature (lower<br />

than 18 ºC). This is recommended for sanitation, but the problem<br />

is the retrogradation of rice starch. Its market is expanding<br />

year by year.<br />

“New characteristic rice” research project<br />

The Ministry of Agriculture, Forestry, and Fisheries supported<br />

the research project “New characteristic rice” from 1990 to<br />

1995. To enhance rice consumption, Japanese breeders tried<br />

to develop various kinds of new rice varieties, such as big<br />

grains, long grains, aromatic rice, pigmented rice, low-amylose<br />

rice, etc. In addition to national institutes, many universities,<br />

prefectural research institutes, and private companies took<br />

part in the project.<br />

Using pressurization in rice processing<br />

High-pressure treatment was applied to the manufacturing of<br />

rice crackers and rice cakes. It is well known that rice crackers<br />

are made in many processing steps. High-pressure treatment<br />

made it possible to simplify the manufacturing procedure.<br />

According to Dr. A. Yamasaki, starch of nonglutinous rice was<br />

gelatinized by high-pressure treatment of 700 MPa at 35 ºC.<br />

He also succeeded in developing low-allergenic rice, which is<br />

useful for preparing low-allergenic bread and low-allergenic<br />

cooked rice. These rice products are promising because many<br />

people suffer from allergy.<br />

Pregerminated brown rice and extrusion cooking<br />

Pregerminated brown rice has become popular in Japan. It is<br />

believed that pregerminated brown rice is good for health. It<br />

was reported that the content of gamma-aminobutyric acid<br />

(GABA) in pregerminated brown rice is higher than in ordinary<br />

milled rice or ungerminated brown rice. The development<br />

of a novel foodstuff from pregerminated brown rice by a<br />

twin-screw extruder was investigated. The characteristics of<br />

the components of the materials and the products are as follows.<br />

276 <strong>Rice</strong> is life: scientific perspectives for the 21st century


1. Pregerminated brown rice was prepared by soaking<br />

in water for 72 h at 30 ºC followed by drying to 13%<br />

to 15% moisture content at 15 ºC in a low-humidity<br />

artificial weather-control room. Total dietary fiber,<br />

total ferulic acid, and GABA contents of the<br />

pregerminated brown rice were higher than those of<br />

ordinary brown rice or polished rice.<br />

2. The pregerminated brown rice was processed with a<br />

twin-screw extruder. The puffed pregerminated brown<br />

rice contained more oryzanol, inositol, total ferulic<br />

acid, and total dietary fibers than the unpuffed polished<br />

rice. And the product prepared by the co-extrusion<br />

of pregerminated brown rice (90%) and beer<br />

yeast (10%) contained more free amino acids, such<br />

as GABA, glycine, alanine, aspartic acid, and glutamic<br />

acid, than polished rice, brown rice, and puffed<br />

pregerminated brown rice.<br />

3. Extrusion cooking was shown to sterilize the germinated<br />

brown rice by the incubation test, which would<br />

lead to the development of consumer-oriented rice<br />

products following food safety procedures.<br />

4. Wheat bread prepared with 30% puffed pregerminated<br />

brown rice contained more GABA and free sugars,<br />

such as maltose, than ordinary wheat bread. The<br />

extrudate bread was shown to be sweeter (P


Ohtsubo K, Nakamura S, Imamura T. 2002. Development of primer<br />

sets for identification of a rice cultivar, Koshihikari, by PCR.<br />

Nippon Nogeikagaku Kaishi 76:388-397. (In Japanese with<br />

English summary.)<br />

Notes<br />

Authors’ address: National Food <strong>Research</strong> <strong>Institute</strong>, Tsukuba, Ibaraki<br />

305-8642, Japan, e-mail: kenohtsu@nfri.affrc.go.jp.<br />

High-pressure food processing of rice and starch foods<br />

Rikimaru Hayashi<br />

The use of pressure (P) in addition to temperature (T) (Hayashi<br />

1987, Hayashi et al 1987) has been accepted in the field of<br />

food science and technology over the past 15 years, and research<br />

and development are now under way in the food industry,<br />

universities, and government institutes (Hayashi 2002).<br />

Several commercial products are now on the market that are<br />

prepared using high-pressure techniques.<br />

This paper describes the principle of high-pressure treatment<br />

and the effects of high pressure on foods, with emphasis<br />

on the high-pressure effects on starches. Finally, recent successes<br />

of the Echigo Seika Company in the application of highpressure<br />

techniques to rice and rice products are discussed.<br />

Principle and method<br />

High pressure means high hydrostatic pressure generated by<br />

the compression of water. A pressure of 100 MPa or higher<br />

(usually lower than 1,000 MPa) is used under temperatures<br />

below 100 °C. A unit of pressure is expressed in kg cm –2 , bar,<br />

or pounds in –2 , but now the international Pascal unit is commonly<br />

used. T<strong>here</strong>fore, 1,000 bar or 1,000 kg cm –2 almost<br />

equals 100 MPa.<br />

Food, which is contained in a plastic bag and sealed by<br />

carefully removing air, is placed in a pressure vessel filled with<br />

water and high pressure is then generated in the vessel by a<br />

pressure pump.<br />

Pressurization of food<br />

An egg is not crushed by compression at 600 MPa, but the egg<br />

white and yolk are coagulated. The color of egg yolk of a pressurized<br />

egg is naturally yellow, w<strong>here</strong>as a boiled egg changes<br />

to a faded yellow. The color difference is attributed to changes<br />

associated with pressurization: pressure affects only<br />

noncovalent bonding and coagulates proteins without splitting<br />

covalent bonds, thus keeping the color and smell intact.<br />

High pressure induces protein denaturation in the same<br />

way as high temperature.<br />

Meat protein is also denatured by pressure treatment at<br />

400 MPa, preserving the properties of raw meats. An example<br />

of prawns or shrimp is interesting: although a boiled prawn<br />

turns red and the meat coagulates, the appearance of a pressurized<br />

prawn is the same as that of raw shrimp, but the meat<br />

coagulates after pressurization at 400 MPa for 10 min.<br />

High pressure also has an effect on starches: a thick suspension<br />

of rice starch forms a ball by standing against its own<br />

weight after pressurization at 700 MPa, indicating that starches<br />

are gelatinized by the pressure treatment.<br />

Versatile utility of high pressure<br />

A high-pressure treatment generally coagulates protein, t<strong>here</strong>by<br />

inactivating the enzymes, gelatinizing the starches, and killing<br />

microorganisms. Thus, the use of high pressure promises to be<br />

a versatile process in food science and technology. Pressure<br />

produces a new texture in meats and starch-based foods, while<br />

keeping the original nutrients, flavor, and color.<br />

High-pressure effects on pure starches<br />

High-pressure-induced gelatinization of starch<br />

Effect of pressure on amylase digestibility of starches. The<br />

starches of potato, maize, and wheat are gelatinized by pressure<br />

treatment at warm conditions of 45–50 °C. The pressurization<br />

produces unique properties that are different from those<br />

of heat-gelatinization: heat-treatment destroys starch granules,<br />

resulting in a transparent solution, but a pressure-treatment<br />

swells the granules while maintaining the granular structure.<br />

Nevertheless, amylolytic enzymes such as α-, β-, and glc-amylases<br />

digest the pressurized starches well, being similar to the<br />

phenomenon in which the pressure-treatment of proteins increases<br />

protease digestibility (Hayashi and Hayashida 1989).<br />

The pressure-induced gelatinization of starches exhibits<br />

a sigmoid curve, suggesting that a two-state transition is involved,<br />

as in heat-induced gelatinization (see below).<br />

Effect of pressurization time on amylase digestibility of<br />

starches. To attain full amylase digestibility of starches, pressurization<br />

under warm conditions for 2 to 6 h is necessary.<br />

Interestingly, pressurization of starches for a longer time<br />

makes amylase digestion difficult: the amylase digestibility of<br />

starches decreased by 20–50% after pressurization for 17 h<br />

compared with the maximum digestibility obtained after pressurization<br />

for 2 to 6 h.<br />

These observations suggest that pressure induces gelatinization<br />

of starches, similar to heating, but prolonged pressurization<br />

produces a new stable structure of starches, which is<br />

not susceptible to attack by amylase (Ezaki and Hayashi 1992).<br />

Birefringence of starches after pressurization. The birefringence<br />

of starches is lost as increasing pressure is applied.<br />

278 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Wheat starch is sensitive to pressure and birefringence is lost<br />

at 200 MPa.<br />

In the pressurization of starches, the number of granules<br />

exhibiting complete birefringence decreases without increasing<br />

the incomplete birefringent granules. This loss of birefringence<br />

shows that the crystalline structure is destroyed by high<br />

pressure as well as by high temperature and that the high-pressure-induced<br />

gelatinization of starches follows a two-state transition<br />

without an intermediate state of destruction.<br />

Physical properties of pressurized starches<br />

When a 50% water suspension of starches is pressurized at<br />

100 to 500 MPa and at 45 °C for 1 h and air-dried, followed<br />

by analyses of their physical properties, the results are as follows.<br />

According to X-ray crystal analysis, the crystalline structure<br />

of potato, waxy maize, and maize starches decreases with<br />

an increase in pressure, although the crystalline structure of<br />

potato starch does not change up to 500 MPa. The decrease in<br />

the high-pressure-induced crystalline structure is parallel with<br />

the increase in amylase susceptibility.<br />

Amylograms show that the transition temperature of pressurized<br />

starches is elevated, thus decreasing the viscosity.<br />

Interestingly, differential-scanning calorimetry (DSC) of<br />

pressurized starches shows that the peak temperature of the<br />

DSC patterns increases while the peak area decreases, indicating<br />

that some pressure-induced structural state of the pressurized<br />

starches is perturbed by low energy at higher temperatures.<br />

Summary of pressure-induced changes in starches<br />

The structure of pressurized starches changes accompanying<br />

the increase in amylase digestibility, a loss of birefringence,<br />

and a loss of crystallinity. These unique structural properties,<br />

which are somewhat different from those of heat-gelatinized<br />

starches, should be analyzed in detail for effective applications<br />

of high pressure to starch and related foods.<br />

<strong>Rice</strong>-based foods produced by high-pressure processing<br />

Dr. Akira Yamazaki, of Echigo Seika Company Ltd., studied<br />

the properties of pressurized rice in detail to introduce the use<br />

of high pressure to the food industry (Kinefuchi et al 1999,<br />

Sasagawa and Yamazaki 2002). He equipped several large highpressure<br />

machines in his own factory and succeeded in sending<br />

rice and rice products to the market by introducing the<br />

high-pressure technique to the manufacturing process of rice<br />

products, cooked rice (gohan), rice crackers (osembei), and<br />

rice cakes (omochi).<br />

High-pressure effects on rice grains<br />

Traditionally cooked-rice grains change their shape and develop<br />

some cracks, but rice grains after high-pressure pretreatment<br />

followed by heat-cooking swell, and their original shape<br />

is maintained without cracks.<br />

High-pressure cooked rice for microwave ovens<br />

Bread is purchased in the store and toasted just before eating.<br />

This is a typical life style, especially on a busy morning. However,<br />

45 min are required to cook rice. Cooked rice tastes best<br />

and has its best texture just after steaming. Warming of cold<br />

cooked rice makes the taste worse. In general, heating a starchbased<br />

food twice leads to an unpalatable food. In history, instant-rice<br />

is a dream of Japanese consumers.<br />

Dr. Yamazaki succeeded in producing oven-cooked rice<br />

with a good taste and texture for consumers, although the production<br />

scale is only enough to fulfill the requirement of a<br />

small city. He also succeeded in producing instant rice containing<br />

miscellaneous cereals. These instant cooked-rice cereals<br />

exhibited good taste and good texture by a 3-min heating<br />

in a microwave oven.<br />

When high-pressure pretreated and successively heatcooked<br />

rice is compared with traditionally cooked rice, its properties<br />

are as follows: first, it is more gelatinized; second, it is<br />

more slowly retrograded; and third, it is gelatinized to a greater<br />

extent by heating just before serving. Japanese consumers who<br />

are particularly sensitive to rice accept these properties.<br />

High-pressure rice cakes<br />

During New-Year days, the Japanese public is freed from the<br />

kitchen and enjoys the New-Year cerebrations, eating rice cakes<br />

(omochi) every day, which are a preserved food. The company<br />

introduced the high-pressure technique for producing the traditional<br />

rice cake and a special kind of omochi, which contains<br />

herbs with a natural color, smell, and taste, and this is<br />

now available on the market.<br />

Merits of high-pressure food processing<br />

High-pressure processing is useful not only for producing highquality<br />

food, but also for improving the manufacturing process.<br />

The production time for rice crackers is shortened by<br />

introducing a high-pressure technique into the traditional processing<br />

system and the total energy cost is decreased by 10%<br />

and the labor force by 56%.<br />

Conclusions<br />

The use of high pressure for food processing and cooking, in<br />

addition to heating and cooling, is now in our hands. Two factors,<br />

T and P, are useful for the manufacturing of good foods,<br />

including starch-based foods. Although T and P are used independently,<br />

their combined use is also important for the optimal<br />

use of high pressure. For example, heat-tolerant bacterial<br />

spores are inactivated by pressurization under elevated temperature.<br />

References<br />

Ezaki S, Hayashi R. 1992. High-pressure effects on starch: structural<br />

change and retrogradation. In: Balny C, Hayashi R,<br />

Heremans K, Masson P, editors. High pressure and biotechnology.<br />

France: John Libbey Eurotext. p 163-165.<br />

Session 9: Developing new uses of rice 279


Hayashi R. 1987. Possibility of high-pressure technology for cooking,<br />

sterilization, processing, and storage of foods. Food Dev.<br />

(Shokuhin to Kaihatu) 22(7):55-62.<br />

Hayashi R, Kawamura Y, Kunugi S. 1987. Introduction of high pressure<br />

to food processing: preferential proteolysis of â-lactoglobulin<br />

in milk whey. J. Food Sci. 52:1107-1108.<br />

Hayashi R, Hayashida A. 1989. Increased amylase digestibility of<br />

pressure-treated starch. Agric. Biol. Chem. 53:2543-2544.<br />

Hayashi R, editor. 2002. Trends in high-pressure bioscience and biotechnology.<br />

Netherlands: Elsevier.<br />

Kinefuchi M, Watanabe K, Komiya S, Yamazaki A, Yamamoto K.<br />

1999. Characteristic of retrogradation of pressure-treated<br />

cooked rice. J. Appl. Glycosci. 46:31-38.<br />

Sasagawa A, Yamazaki A. 2002. Development and industrialization<br />

of pressure-processed foods. In: Hayashi R, editor. Trends in<br />

high-pressure bioscience and biotechnology. Netherlands:<br />

Elsevier. p 375-384.<br />

Notes<br />

Author’s address: Food Science and Technology, College of<br />

Bioresource Science, Nihon University, Kamenoi 1866,<br />

Fujisawa, Kanagawa 252-8502, Japan, e-mail:<br />

hayashi2@brs.nihon-u.ac.jp.<br />

Acknowledgments and sympathy: The author expresses his thanks<br />

to Miss Atsuko Hayashida, Kyoto University, and Dr. Souji<br />

Suzuki, Ajinomote Company, who performed a part of the<br />

experiments of high-pressure effects on starches, and sincere<br />

gratitude to Dr. Akira Yamazaki, manager of Echigo Seika<br />

Food Company, who gave me permission to use his data on<br />

high-pressure rice and rice products.<br />

On the evening of 23 October 2004, a huge earthquake<br />

struck Niigata Prefecture, especially Ojiya City. This city, the<br />

location of Echigo Seika Company Ltd., was the seismic center.<br />

I express my sincere sympathy to the people t<strong>here</strong>, and, as<br />

it is now a very busy season for the coming New Year, I regret<br />

the damage to the rice-processing systems of the company,<br />

including the high-pressure machines, resulting from this earthquake.<br />

Developing novel processes for incorporating<br />

the unique nutritional and functional properties<br />

of rice into value-added products<br />

Elaine T. Champagne, Harmeet S. Guraya, Frederick F. Shih, and Ranjit S. Kadan<br />

An expanding global rice market and diet diversification have<br />

presented the rice industry in the United States and other developed<br />

countries challenges and opportunities to develop new<br />

markets for rice. Global trade has expanded with advances in<br />

technologies leading to record yields of high-quality rice. Countries<br />

that at one time were importers or had only a small share<br />

of the export market are now major exporters. The United<br />

States, once the lead exporter of high-quality rice, has been hit<br />

hard by this shrinking export market. Outside of the U.S., countries<br />

such as Brazil, China, Japan, Taiwan, and India have been<br />

faced with declining per-capita consumption because of diet<br />

diversification. Value-added rice products that capture the<br />

unique nutritional and functional attributes of rice offer a means<br />

to keep rice as a mainstay of the diet and to expand domestic<br />

markets. This paper will highlight new product introductions<br />

in the U.S. and technologies recently developed at the USDA-<br />

ARS Southern Regional <strong>Research</strong> Center for value-added rice<br />

products.<br />

New product introductions<br />

Domestic usage of rice in the United States has tripled in the<br />

last ten years in response to consumer demand for more healthful<br />

foods, more convenient products, and a growing interest in<br />

ethnic foods. The market has been flooded with new product<br />

introductions. Foods that use rice now include baby food, bak-<br />

ery goods, breakfast cereals, candy, desserts, beverages and<br />

dairy items, side dishes, package mixes, entrees (frozen, shelfstable,<br />

chilled), meats and meat substitutes, sauces and spreads,<br />

snacks, soups, and pet foods.<br />

<strong>Rice</strong> usage in entrees has increased 10-fold in the last 20<br />

years. Interest in ethnic foods has boosted this growth. Frozen<br />

ethnic entrees represented a $2.2 billion industry in 2000<br />

(Brandt 2001). A popular new addition is bowl meals—a frozen<br />

entree in a microwaveable bowl usually containing individually<br />

quick-frozen rice, meat or poultry, and vegetables.<br />

They have contributed largely to the growth of the entree market.<br />

Package rice mixes to serve as side dishes combine rice<br />

with seasonings, dehydrated vegetables, and other ingredients.<br />

The use of rice in packaged mixes doubled during the 1990s<br />

(USA <strong>Rice</strong> Federation 2000). Mixes for Louisiana Cajun and<br />

Creole foods, such as jambalaya, gumbo, and etouffee, and<br />

difficult-to-make dishes, such as risotto, are popular. <strong>Rice</strong> for<br />

mixes is either regular or parboiled, with a low moisture content<br />

around 6.5%. For a product in which distinct grains are<br />

important, such as a pilaf, or when a sauce will add moisture,<br />

parboiled rice often performs better than regular rice.<br />

Snack bars using rice include granola, breakfast, and<br />

energy bars. Energy bars, introduced in the 1990s, account for<br />

80 to 100 new product launches a year and represented about<br />

$500–700 million in sales in 2000 (Kreuzer 2001, Mintel In-<br />

280 <strong>Rice</strong> is life: scientific perspectives for the 21st century


ternational Group Ltd. 2003). Snack bars target the healthconscious<br />

consumer and are often enriched. A breakfast bar<br />

introduced in 2003 contains milk infused into the grains composing<br />

the bar to give one the taste of a bowl of cereal. Crisped<br />

rice is used in granola, breakfast, and energy bars. High-pressure<br />

extrusion processing is generally used for the manufacture<br />

of crisped rice for these snack bars.<br />

Desserts with rice emerged in the late 1990s with waxy<br />

rice serving as a fat replacer in ice cream. The addition of<br />

1.5% waxy rice starch improves the creamy mouthfeel and<br />

overall texture, allowing the product to mimic premium (higher<br />

fat) ice cream. The excellent freeze-thaw stability of waxy rice<br />

starch helps reduce iciness during storage (Bakal 1994,<br />

Wilkinson and Champagne 2004). Crisped rice provides texture<br />

to a number of chocolate dessert products.<br />

<strong>Rice</strong> incorporated into a meat product can help reduce<br />

fat content, for example, in the manufacture of “light” sausages.<br />

<strong>Rice</strong> starch can be used to bind water in poultry products<br />

during vacuum tumbling or injection. <strong>Rice</strong> and rice protein<br />

are used in meat analogs to help bind the other ingredients.<br />

<strong>Rice</strong> has also found new applications in dairy alternatives<br />

and electrolyte-replacement drinks. <strong>Rice</strong> offers a lactosefree,<br />

hypoallergenic alternative to cow and soy milk products.<br />

In soy milk, rice flour and syrup can be used to help mask<br />

beany flavors and keep insoluble proteins suspended in solution<br />

(Burrington 2002). In electrolyte-replacement drinks, the<br />

long-chain carbohydrates and proteins of rice enhance the absorption<br />

of fluid and electrolyte salts into the body’s cells<br />

(Greenough 1998).<br />

Novel processes developed at the Southern Regional<br />

<strong>Research</strong> Center<br />

The postharvest rice research program at the Southern Regional<br />

<strong>Research</strong> Center is directed at (1) obtaining a fuller understanding<br />

of component structure-function relationships in rice<br />

and its coproducts that contribute to their unique nutritional<br />

and functional properties and (2) developing new technologies<br />

for converting rice components, in situ and isolated, into<br />

high-value, high-demand products that capture these unique<br />

properties. Technologies resulting from this research are highlighted.<br />

Physical process for rice starch<br />

and protein separation<br />

<strong>Rice</strong> starch has not been produced in the United States since<br />

1943, except on a small scale in recent years. Seventy-five<br />

percent of the world’s 25,000 metric tons of rice starch produced<br />

annually is made in Europe. The classical, commercial<br />

rice starch operation employed in Europe requires extensive<br />

soaking in dilute sodium hydroxide prior to the separation of<br />

starch and protein. This wet-milling process is water, energy,<br />

and time intensive and requires costly wastewater treatments.<br />

The usage of alkali results in a salt disposal problem and can<br />

impart bitterness to the protein component. The environmental<br />

and energy issues associated with this process have hindered<br />

the comeback of a rice starch industry in the U.S.<br />

Dr. Harmeet Guraya under a Cooperative <strong>Research</strong> and<br />

Development Agreement (CRADA) and Small Business Initiative<br />

<strong>Research</strong> (SBIR) grant with Sage V Foods (Los Angeles,<br />

California) has developed a physical process for separating<br />

rice flour into starch and protein. In this process, proteinstarch<br />

agglomerates of rice are physically disrupted in the presence<br />

of water by the use of high-pressure homogenization, as<br />

achieved by the use of a microfluidizer. The deagglomeration<br />

leads to better density-based separation of rice starch and protein.<br />

This process yields starch with low damage (5–6% versus<br />

12% in commercial starches) and low protein content<br />

(< 0.5%). The protein has high solubility compared with that<br />

of commercially available protein concentrates, making it suitable<br />

for beverage applications. Sage V Foods has been granted<br />

an exclusive license for U.S. Patent 6,737,099 (18 May 2004),<br />

“Process for the Deagglomeration and Homogeneous Dispersion<br />

of Starch Particles.” The company has scaled-up the process<br />

and will shortly begin manufacturing the starch product.<br />

This technology has the potential of reducing imports of rice<br />

starch and increasing profits for the U.S. rice industry.<br />

Physical process for quick-cooking brown rice<br />

Brown rice is rich in minerals and vitamins, making it a nutritionally<br />

valuable food. Consumption of brown rice, however,<br />

is low. A major drawback for brown rice is its long cooking<br />

time (45–50 min) because of the slow rate of hydration. This<br />

long cooking time produces an undesirable sticky, soft texture<br />

on the surface of the kernel. Existing commercial methods for<br />

producing quick-cooking brown and white rice involve precooking<br />

the rice, followed by drying. These methods require a<br />

significant input of water and energy, which, in turn, creates<br />

significant expense.<br />

Dr. Guraya has invented a dry instantization process that<br />

reduces the cooking time of brown and wild rice from 45–50<br />

min to that of white rice (20 min). This process “sandblasts”<br />

brown rice with parboiled rice flour. The bombardment creates<br />

microperforations in the waxy layer of the bran, allowing<br />

the kernel to absorb water more readily and cook more rapidly.<br />

Visually, the uncooked kernel looks the same as an untreated<br />

kernel. The cooked kernel has a texture similar to that<br />

of white rice and is not soft and mealy like that of untreated<br />

brown rice. The U.S. Patent 6,586,036 (1 July 2003), “Process<br />

for Increasing Rate of Hydration of Food Crop Seeds,”<br />

has been licensed by three companies. One licensee, Progressive<br />

Technologies (Grand Rapids, Michigan), has manufactured<br />

a continuous system for production of these products by<br />

the other two licensees. The process cost is approximately 2 to<br />

4 cents per kg of brown rice. The invented process reduces the<br />

cost of processing to make quick-cooking rice, reduces environmental<br />

pollution, and will make nutritious brown rice more<br />

appealing to consumers.<br />

Session 9: Developing new uses of rice 281


Gluten-free rice bread<br />

Economical rice bread products are needed for consumers with<br />

Celiac Sprue disease and other disorders that prevent consumption<br />

of gluten-containing grain (e.g., wheat) products. Dr. Ranjit<br />

Kadan has developed formulations for rice bread using a home<br />

bread machine. The prototype bread has desirable flavor and<br />

texture comparable with those of wheat bread. A U.S. patent<br />

application has been submitted. The developed process will<br />

allow consumers to readily and economically prepare glutenfree<br />

bread. Ingredients cost $0.65 kg –1 loaf –1 , with marketing<br />

cost 2–3 times this cost. This compares with $4–5 loaf –1 for<br />

commercial wheat bread.<br />

Low-oil-uptake rice batter and donuts<br />

Fried batters may enhance the sensory quality of the coated<br />

food, but they may also contain high amounts of oil and contribute<br />

to oil-related health problems such as obesity and heart<br />

disease. T<strong>here</strong>fore, in spite of their popularity, fried foods with<br />

excessively elevated oil are undesirable and should be avoided.<br />

Dr. Fred Shih and Ms. Kim Daigle (1999) found rice flour to<br />

have better oil resistance than wheat flour when formulated as<br />

a batter. However, rice-flour slurries, at concentrations such<br />

that the viscosity is appropriate for a batter, become brittle<br />

and hard during frying. These observations led them to discover<br />

that gelatinized long-grain rice flour and phosphorylated<br />

long-grain rice starch esters can be effective in enhancing both<br />

the viscosity and oil-lowering properties of rice-flour batters.<br />

These batters, when applied to chicken, absorb up to 60% less<br />

oil than a traditional wheat-based batter. U.S. Patent 6,224,921<br />

(1 May 2001), “<strong>Rice</strong> flour-based low oil-uptake frying batters,”<br />

was issued.<br />

Following an approach similar to that taken for the batter<br />

development, Shih and Daigle (2002) developed low-oiluptake<br />

rice donuts. The product formulated with long-grain<br />

rice flour and pregelatinized long-grain rice flour (30%) absorbed<br />

as much as 54% less oil than traditional wheat-flour<br />

donuts.<br />

Fungi-free rice straw<br />

Japan desires to import rice straw from the United States for<br />

cattle feed and requires that the straw be free of fungi. Dr.<br />

Guraya has invented an economical process for fungi-free rice<br />

straw. <strong>Research</strong> is under way, in collaboration with an industry<br />

partner through a CRADA, to make the process continuous<br />

and scale it up for a commercial operation. This process will<br />

allow the U.S. to export rice straw to Japan, which currently<br />

imports 2 million tons of forage other than that from rice.<br />

New research thrusts<br />

Current research efforts are directed at developing novel technologies<br />

for health-beneficial products from rice bran and hulls.<br />

These technologies include processes for (1) protein concentrates<br />

and isolates for infant formulas, beverages, and ingredient<br />

applications; and (2) fractions (rice wax, wax-rich fractions,<br />

hull and bran extracts) with cholesterol-lowering and<br />

antioxidative activity for various food applications. Technologies<br />

for new low-oil-uptake rice and sweet potato–rice products<br />

that suit the need of health-conscious consumers are also<br />

being developed. All of these applications target the unique<br />

nutritional and functional attributes of rice co-products and<br />

their components. The processes being pursued to achieve these<br />

products are efficient, environmentally friendly, and commercially<br />

viable.<br />

References<br />

Bakal A. 1994. The lowdown on formulating lowfat. Prep Foods<br />

163:75-78.<br />

Brandt LA. 2001. Entrees take the orient express. Prep Foods 170:65-<br />

68.<br />

Burrington KJ. 2002. More than just milk. Food Prod. Design 12:37-<br />

64.<br />

Greenough WB. III. 1998. Oral hydration therapy: something new,<br />

something old. Infec. Dis. Clin. Pract. 7:97-100.<br />

Kreuzer H. 2001. High-octane bars and beverages. Food Prod. Design<br />

11:33-58.<br />

Mintel <strong>International</strong> Group Ltd. 2003. Global new products database:<br />

category review. At www.gnpd.com. (See categories<br />

snack bars, snack mixes, and energy bars; cold cereal; rice;<br />

soup.)<br />

Shih FF, Daigle KW. 1999. Oil uptake properties of fried batters<br />

from rice flour. J. Agric. Food Chem. 47:1611-1615.<br />

Shih FF, Daigle KW. 2002. Preparation and characterization of low<br />

oil uptake rice cake donuts. Cereal Chem. 79:745-748.<br />

USA <strong>Rice</strong> Federation. 2000. U.S. rice distribution patterns, 1999-<br />

2000 report. The Federation, Houston, TX. (Also 1996 and<br />

other rice distribution pattern reports through 2001.)<br />

Wilkinson HC, Champagne ET. 2004. Value-added rice products.<br />

In: Champagne ET, editor. <strong>Rice</strong> chemistry and technology.<br />

3rd edition. St. Paul, Minn. (USA): American Association of<br />

Cereal Chemists. p 473-493.<br />

Notes<br />

Authors’ address: USDA-ARS Southern Regional <strong>Research</strong> Center,<br />

New Orleans, Louisiana, USA, e-mail:<br />

etchamp@srrc.ars.usda.gov.<br />

282 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Dehydrin proteins in rice bran<br />

Michiko Momma<br />

Dehydrin is a group of late embryogenesis-abundant (LEA)<br />

proteins, which accumulate in the maturing seed of many plants.<br />

Dehydrins are reported to protect protein or membranes in plant<br />

tissue under abiotic stress such as desiccation or low temperature<br />

(Close 1997). Besides the biological function, application<br />

for preservation of food quality is expected, similar to<br />

antifreeze proteins in fish (Breton et al 2000). Since rice bran<br />

could be a good source of dehydrin for nonfood usage, we<br />

tried to characterize rice dehydrin in this study. <strong>Rice</strong> bran protein<br />

was analyzed by two-dimensional (2D) electrophoresis,<br />

and dehydrins in the protein fraction were detected by<br />

immunoblotting using antibody against the conserved motifstructure<br />

in order. A major rice dehydrin was partially purified<br />

from rice bran and its cryoprotective activity was estimated to<br />

assess the function of the protein.<br />

Materials and methods<br />

Fractionation and partial purification of proteins<br />

<strong>Rice</strong> bran was obtained in the process of refining 1 kg of rice<br />

(cv. Koshihikari) to 90%. Fifty grams of the rice bran was defatted<br />

with 500 mL of hexane three times and kept at –20 o C<br />

before use. The defatted rice bran (20 g) was mixed with 20<br />

mM HEPES-NaOH, pH 7.0, for 3 min by a hiscotron mixer<br />

(NS-50, Nichi-On), centrifuged twice at 8,000x g for 20 min.<br />

Supernatant was collected as a water-soluble fraction of rice<br />

bran. The heat-tolerable protein fraction was prepared by heating<br />

the water-soluble fraction in boiling water for 10 min and<br />

removing precipitate by centrifugation at 12,000x g for 20 min.<br />

<strong>Rice</strong> dehydrin was partially purified by modifying the<br />

method of purification of soybean dehydrin (Momma et al<br />

2003). From 20 g of defatted rice bran, a 10–50% saturated<br />

ammonium sulfate fraction was isolated, dialyzed, heated in<br />

boiling water, and then centrifuged. Supernatant was put onto<br />

an S Sepharose Fast Flow column (2 × 35 cm), and eluted with<br />

a linear gradient of 0–300 mM NaCl. The dehydrin fraction<br />

was collected based on detection by SDS-PAGE and<br />

immunoblotting with antiserum against the conserved lysinemotif<br />

of dehydrin. The water-soluble fraction, heat-tolerable<br />

fraction, and partially purified dehydrin were dialyzed against<br />

distilled water and freeze-dried and used to assess cryoprotective<br />

activity.<br />

Electrophoresis of rice bran proteins<br />

SDS-PAGE was carried out on 5–20% polyacrylamide gradient<br />

gel (PAGEL, NPG-520L, ATTO) by the method of Laemmli<br />

(1970). Gels were stained with Coomassie Brilliant Blue (CBB)<br />

R-250. Two-dimensional electrophoresis of protein fractions<br />

isolated from rice bran was conducted with the Multiphore II<br />

System (Amersham Pharmacia Biotech) following the<br />

supplier’s instructions. Protein fractions were mixed with<br />

sample buffer (3-10NL) and IPG strips (pH3-10NL, 7 cm) were<br />

soaked in the sample solution for 15 h. The IPG strips were set<br />

on the system, and electrophoresis was carried out at 200–<br />

3,500 V for 90 min and at 3,500 V for 65 min. IPG strips were<br />

then equilibrated in 50 mM Tris-HCl, pH 8.8, containing 6 M<br />

urea, 30% (w/v) glycerol, 2% SDS, 10 mg mL –1 dithiothreitol,<br />

and a trace of bromophenol blue for 20 min. Second-dimensional<br />

electrophoresis (SDS-PAGE) was carried out on a 5–<br />

20% polyacrylamide gradient gel. Gels were stained with CBB<br />

R-250.<br />

Immunoblot analysis<br />

Electrophoresis gels were incubated in a blotting buffer (25<br />

mM Tris-HCl, pH 9.5, containing 40 mM ε-aminocaproic acid,<br />

20% methanol, 0.05% SDS) for 20 min, and then protein on<br />

the gel was blotted onto a PVDF membrane (Immun-Blot,<br />

Biorad) at 2.5 mA for 30 min. The PVDF membrane was kept<br />

overnight in 3% BSA-TBS (Tris-buffered saline, 20 mM Tris-<br />

HCl, pH 7.5, 500 mM NaCl, containing 3% bovine serum albumin).<br />

Dehydrin protein was detected by polyclonal antiserum<br />

raised against conserved lysine-motif sequence<br />

(DQNEKKGIMDKIKEKLPGGH) conjugated with ovalbumin.<br />

The PVDF membrane was incubated for 60 min in the<br />

antiserum of rabbits diluted to 1:200 with 1% BSA-TBS, then<br />

washed with TBS-t (Tris-buffered saline containing 0.05%<br />

tween 20) for 20 min three times, and with TBS for 20 min.<br />

The washed membrane was incubated with peroxydase-conjugated<br />

antirabbit goat antibody diluted to 1:2,000 with 1%<br />

BSA-TBS, washed with TBS-t for 20 min three times, and<br />

washed with TBS for 20 min. Reacted polypeptides were detected<br />

by a detection kit (Immunostain HRP1000, Konica).<br />

Cryoprotective activity on lactate dehydrogenase<br />

Cryoprotective activities of dehydrins in comparison with bovine<br />

serum albumin (BSA, A4378, Sigma) on freeze/thaw inactivation<br />

of lactate dehydrogenase were assayed following<br />

the method of Lin (1992). Lactate dehydrogenase from rabbit<br />

muscle (L5132, Sigma) was dissolved in 10 mM sodium phosphate<br />

buffer, pH 7.5, at a concentration of 2.5 µg mL –1 . The<br />

enzyme solution (0.1 mL) was mixed with equal amounts of<br />

test compounds dissolved in the same buffer at a concentration<br />

of 2 × 10 2 – 2 × 10 –4 µM. The solutions were frozen at<br />

–20 o C for 24 h and thawed at room temperature for 5 min.<br />

Enzyme activity was measured with the change of absorbance<br />

at 340 nm at 25 o C using an assay kit (DG1340K, Sigma). All<br />

samples were assayed twice in triplicate. Residual activity was<br />

shown as the percentage of the control activity assayed immediately<br />

after mixing of enzyme and protein solution.<br />

Session 9: Developing new uses of rice 283


A<br />

– 3-10NL +<br />

B<br />

– 3-10NL +<br />

C<br />

– 3-10NL +<br />

97.4<br />

106.0<br />

97.4<br />

66.2<br />

80.0<br />

66.2<br />

45.0<br />

49.5<br />

45.0<br />

31.0<br />

21.5<br />

14.4<br />

kDa<br />

32.5<br />

27.5<br />

18.5<br />

kDa<br />

Fig. 1. Two-dimensional electrophoresis and immunoblotting. (A) 2D electrophoresis of water-soluble fraction, (B) immunoblot of watersoluble<br />

fraction, (C) 2D electrophoresis of heat-tolerable fraction. = spots reacted with antibody.<br />

31.0<br />

21.5<br />

14.4<br />

kDa<br />

Results and discussion<br />

In the results of SDS-PAGE analysis, two bands of dehydrinlike<br />

protein were detected in water-soluble and heat-tolerable<br />

fractions of rice bran by immunoblotting for the conserved<br />

motif-sequence of dehydrin. Two major bands of 44 kDa and<br />

23 kDa were detected with similar intensity in this experiment.<br />

Still et al (1994) had investigated the accumulation of dehydrin<br />

in the course of seed development of rice using an antiserum<br />

similar to the one we used. They detected a polypeptide estimated<br />

to be 21 kDa as a major dehydrin-like protein in the<br />

seeds of 15–39 DAF along with a small amount of 38-kDa<br />

polypeptide, which also cross-reacted with the antibody. It had<br />

been known that dehydrin with low molecular weight (about<br />

20 kDa) also accumulated in rice seedlings under desiccation<br />

stress. They concluded that the 21-kDa polypeptide was the<br />

major dehydrin protein in rice seed. As for the dehydrin-like<br />

proteins with higher molecular weight, besides the 38-kDa<br />

polypeptide in developing seed, Jayaprakash et al (1998) found<br />

a trace amount of 60-kDa and 45-kDa polypeptides in desiccated<br />

rice seedlings. Dehydrin cognates with a higher molecular<br />

weight than the major one were detected in other plant seeds<br />

such as pea or wheat. They have often been found to lack the<br />

N-terminal motif sequence consisting of DEYGNP (Danyluk<br />

et al 1994). From findings in previous publications, the 23-<br />

kDa polypeptide detected by the immunoblot analysis was<br />

supposed to be the major dehydrin in rice seed and seedlings<br />

under abiotic stress, and that 45-kDa polypeptide would be<br />

one of the dehydrin-cognate proteins.<br />

Two-dimensional electrophoresis profiles of rice bran<br />

proteins are shown in Figure 1. In the results of immunoblotting<br />

for dehydrin motif, 3 spots around 44 kDa and 5 spots around<br />

23 kDa were detected. Though no clear difference was observed<br />

in the SDS-PAGE pattern of the water-soluble and heattolerable<br />

protein fraction, their 2D-electrophoresis patterns<br />

were considerably different. In general, the number of detected<br />

spots decreased with the heat treatment, but some of the spots<br />

on the acidic side seemed to be concentrated in the heated<br />

sample. In the heat-tolerable fraction, cross-reacted spots were<br />

shifted to the acidic side and the separation of the spots became<br />

obscure, implying that they might interact with other<br />

components in rice bran.<br />

Remaining activity (%)<br />

120<br />

100<br />

80<br />

60<br />

40<br />

20<br />

Bovine serum abumin<br />

Sucrose<br />

Ovalbumin<br />

<strong>Rice</strong> dehydrin<br />

Soybean dehydrin<br />

0<br />

10 –6 10 –4 10 –2 1 10 2 10 4<br />

Concentration (mg m –1 )<br />

Fig. 2. Cryoprotective activity of 23-kDa dehydrin.<br />

The cryoprotective activity of partially purified 23-kDa<br />

dehydrin from rice bran on the freeze/thaw inactivation of lactate<br />

dehydrogenase was estimated (Fig. 2). The CP 50 values,<br />

protein amounts necessary to keep 50% activity of lactate dehydrogenase,<br />

of the water-soluble fraction, heat-tolerable fraction,<br />

and dehydrin were 43, 29, and 15.6 µg mL –1 (0.78 µM),<br />

respectively. In our previous study, we assayed the activities<br />

of two types of purified soy dehydrins (Momma 1997, 2003).<br />

The CP 50 of soybean 26-kDa dehydrin had been 5.2 µg mL –1<br />

(0.2 µM). Compared with the soy protein and other commercially<br />

available proteins, rice 23-kDa dehydrin had a level of<br />

cryoprotective activity similar to that of ovalbumin and lacto<br />

albumin, and about one-third the activity of 26-kDa soybean<br />

dehydrin.<br />

Lin and Thomashow (1992) showed that in vitro-translated<br />

COR15 from Arabidopsis had cryoprotective activity on<br />

freeze/thaw inactivation of lactate dehydrogenase. This was<br />

the first report indicating a function of LEA-related proteins.<br />

This cryoprotective activity was found in Chlorella HIC6, a<br />

group 3 LEA protein (Honjoh et al 2000), and a protein from<br />

284 <strong>Rice</strong> is life: scientific perspectives for the 21st century


an ice-nucleating bacterium and others as well. It is presumed<br />

that the extreme hydrophilic property of LEA proteins relates<br />

to their protective function on protein denaturation. The cryoprotective<br />

activity is considered as an index of function of protein<br />

induced by stress such as low temperature or desiccation.<br />

Breton et al (2000) suggested the possibility that the cryoprotective<br />

activity of LEA protein would be applicable to preserve<br />

the quality of frozen food or prevent frostbite. In this<br />

study, we found multiple dehydrin proteins in water-soluble<br />

and heat-tolerable proteins of rice bran. In the results of in<br />

vitro assay, rice dehydrin was found to preserve enzyme activity<br />

against freeze/thaw damage. The fact that the rice dehydrin<br />

has cryoprotective activity is encouraging for novel usage of<br />

rice bran protein, but further characterization of the protein<br />

would be necessary for the development of applications.<br />

References<br />

Breton G, Danyluk J, Ouellet F, Sarhan F. 2000. Biotechnological<br />

applications of plant freezing associated proteins. Biotechnol.<br />

Annu. Rev. 6:59-101.<br />

Close TJ. 1997. Dehydrins: a commonality in the response of plants<br />

to dehydration and low temperature. Physiol. Plant. 100:291-<br />

296.<br />

Danyluk J, Houde M, Rassart E, Sarhan F. 1994. Differential expression<br />

of a gene encoding an acidic dehydrin in chilling<br />

sensitive and freezing tolerant gramineae species. FEBS Lett.<br />

344:20-24.<br />

Honjoh K, Matsumoto H., Shimizu H, Ooyama K, Tanaka K, Oda Y,<br />

Tanaka R, Joh T, Suga K, Miyamoto T, Iio M, Hatano S. 2000.<br />

Cryoprotective activities of group 3 late embryogenesis abundant<br />

protein from Chlorella vulgaris C-27. Biosci. Biotechnol.<br />

Biochem. 64:1656-1663.<br />

Jayaprakash TL, Ramamohan G, Krishnaprasad BT, Ganeshkumar,<br />

Prasad TG, Mathew MK, Udayakumar M. 1998. Genotypic<br />

variability in differential expression of lea2 and lea3 genes<br />

and proteins in response to salinity stress in fingermillet<br />

(Eleusine coracana Gaertn.) and rice (Oryza sativa L.) seedlings.<br />

Ann. Bot. 82:513-522.<br />

Laemmli UK. 1970. Cleavage of structural proteins during the assembly<br />

of the head of bacteriophage T4. Nature 227:680-685.<br />

Lin C, Thomashow MF. 1992. A cold-regulated Arabidopsis gene<br />

encodes a polypeptide having potent cryoprotective activity.<br />

Biochem. Biophys. Res. Commun. 183:1103-1108.<br />

Momma M, Haraguchi K, Saito M, Chikuni K, Harada K. 1997.<br />

Purification and characterization of the acid soluble 26-kDa<br />

polypeptide from soybean seeds. Biosci. Biotechnol. Biochem.<br />

61:1286-1291.<br />

Momma M, Kaneko S, Haraguchi K, Matsukura U. 2003. Peptide<br />

mapping and assessment of cryoprotective activity of 26/27-<br />

kDa dehydrin from soybean seeds. Biosci. Biotechnol.<br />

Biochem. 67:1832-1835.<br />

Still DW, Kovach A, Bradford KJ. 1994. Development of desiccation<br />

tolerance during embryogenesis in rice (Oryza sativa)<br />

and wild rice (Zizania palustris) dehydrin expression, abscisic<br />

acid content, and sucrose accumulation. Plant Physiol.<br />

104:431-438.<br />

Notes<br />

Author’s address: National Food <strong>Research</strong> <strong>Institute</strong>,2-1-12 Kannodai,<br />

Tsukuba, Ibaraki 305-8642, Japan.<br />

Physicochemical properties of modified rice flour<br />

and its use for processed food<br />

T. Takahashi, M. Miura, N. Ohisa, K. Mori, and S. Kobayashi<br />

<strong>Rice</strong> is an important grain. Most of it is consumed as milled<br />

rice. Interest in rice-based products and their processing technologies<br />

has increased despite higher costs than for either maize<br />

or wheat. Modified (by a physical or chemical treatment)<br />

starches and cereal flours have become important in processed<br />

food because the functional properties of the starches and flours<br />

are improved over the gelatinization properties of native<br />

starches and cereal flours. Numerous studies have explored<br />

the physical properties of rice flour from treated kernels, but<br />

few studies have addressed modified rice flour’s characteristics<br />

of cooking and processing. Our study aims to clarify the<br />

effects of heat treatments on gelatinization property and cooking<br />

quality.<br />

Materials and methods<br />

Preparation of heat-treated rice flour<br />

The moisture content of milled rice (japonica, nonglutinous<br />

type) was 12.4% (w/w), determined by the drying method.<br />

Amylose content was determined to be 17.7% (w/w) by the<br />

method of Juliano (1971). The milled rice was heated at 120<br />

°C for 60 min by an autoclave. The moisture content was 20.6%<br />

after autoclaving and 12.9% after drying at room temperature<br />

(25 ± 1 °C) for 24 h. The milled rice was heated at 160 °C for<br />

60 min by an air-oven. The moisture content was 2.2% after<br />

oven treatment. Untreated rice flour (UTR), heat-moisturetreated<br />

rice flour (HMR), and heat-dry-treated rice flour (HDR)<br />

Session 9: Developing new uses of rice 285


Table 1. Dynamic viscoelastic characteristics of 10.0% (w/w) rice flour suspensions during gelatinization. a<br />

Samples G´o/°C G´p/Pa G´95 /Pa G2 BD /Pa tan δ/-<br />

UTR 63.9 ± 0.8 a 1396 ± 55 c 611 ± 55a b 784 ± 69 b 0.12 ± 0.01 a<br />

HDR 65.5 ± 0.4 b 778 ± 40 b 660 ± 30 b 117 ± 29 a 0.13 ± 0.01 a<br />

HMR 79.8 ± 2.1 c n.d. 519 ± 26 a n.d. 0.26 ± 0.01 a<br />

a G´o, onset temperature; G´p, peak G´; G´95 , G´ at 95 °C; G´ BD , breakdown (= G´ p – G´ 95 ). n.d., not detectable. Mean ±<br />

standard deviation (n = 3). Values followed by the same letter in the same column are not significantly different (P85<br />

°C) increased slightly. HMR paste exhibited weak gel because<br />

the tan δ of HMR was greater than that of UTR and HDR. It is<br />

recognized that a rigid starch granule formed with the interaction<br />

of both amorphous and crystallite regions during heatmoisture<br />

treatment. The rheological behavior of rice flour paste<br />

was primarily attributed to interaction in the system, such as<br />

contact between the granules directly and between the granules<br />

and glucose chains (Hoover and Vasanthan 2000).<br />

Table 2 shows the DSC characteristics of 30% (w/w)<br />

rice flour suspensions. The T o of HMR was 8 °C higher than<br />

that of UTR and HDR (Table 2). Other endothermic peaks<br />

(T p2 and T p3 ) in the DSC corresponding to amylose-lipid complexes<br />

were observed at temperatures of 100–120 °C (Table<br />

2). The peak transition for HMR was at a higher temperature<br />

(112 °C) than for UTR and HDR (102 °C). Lai (2000) reported<br />

that increases in gelatinization (T o ) and the peak of<br />

amylose-lipid complex (T p2 ) temperature were observed in DSC<br />

curves of parboiled rice flour. It was also reported that the<br />

peak of the amylose-lipid complexes shifted to a higher temperature<br />

with heat-moisture treatment. Changes in DSC parameters<br />

of HMR indicate that rearrangement of starch chains<br />

occurs during heat-moisture treatment, and leads to the formation<br />

of crystallites of different thermal stabilities. T<strong>here</strong>fore,<br />

the modification of G´ p and T o of HMR is attributed to more<br />

thermally stable crystallites in starch after heat-moisture treatment.<br />

The intensities of the major peaks of HMR were weaker<br />

than that of UTR and HDR measured by X-ray diffractometry.<br />

However, the diffraction peak of HMR at 19.5° (2θ) became<br />

much sharper and another feature peak at 13° (2θ) was also<br />

286 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 2. Effect of heat treatments on differential scanning calorimetry characteristics of rice flours in excess water. a<br />

Samples<br />

Gelatinization<br />

Amylose-lipid complex<br />

T o /°C T p1 /°C T c /°C ∆H/kJ·kg -1 T p2 /°C ∆H 2 /kJ·kg -1 T p3 /°C ∆H 3 /kJ·kg -1<br />

UTR 60.2 ± 0.3b 68.1 ± 0.1 b 78.4 ± 0.3 b 8.6 ± 0.4 b 101.4 ± 0.6 a 0.5 ± 0.0 a – –<br />

HDR 58.1 ± 0.3 a 66.5 ± 0.2 a 76.8 ± 0.2 a 9.6 ± 0.2 c 102.4 ± 1.9 a 0.8 ± 0.1 b – –<br />

HMR 68.3 ± 0.0 c 76.2 ± 0.2 c 86.7 ± 0.5 c 5.2 ± 0.1 a – – 111.9 ± 0.0 0.7 ± 0.0<br />

a<br />

T o , onset temperature; T p , peak temperature; T c , conclusion temperature; ∆H, gelatinization enthalpy. Values followed by the same letter in the same column are not significantly<br />

different (P


Introducing soybean β-conglycinin genes into rice<br />

to improve nutritional and physiological value<br />

Takayasu Motoyama, Nobuyuki Maruyama, Takahiko Higasa, Masaaki Yoshikawa, Fumio Takaiwa, and Shigeru Utsumi<br />

In advanced countries, the aging of society is becoming a serious<br />

problem. Especially in Japan, elderly people over age 65<br />

account for 14.5% of the population, and it is estimated that<br />

they will increase to 24.7% by 2025 and 32.3% by 2050. In<br />

such an ultra-aged society, lifestyle-related diseases such as<br />

hypertension, hyperlipemia, and diabetes could spread. Further,<br />

our immune system weakens against various viruses as<br />

we age. T<strong>here</strong>fore, demand for food that can prevent lifestylerelated<br />

disease and stimulate the immune system will become<br />

larger and larger in advanced countries.<br />

Soybean β-conglycinin, composed of α, α′, and β subunits,<br />

is reported to have many physiological functions such<br />

as cholesterol-lowering activity in human serum (Sirtori et al<br />

1995), serum triglyceride-lowering activity (Aoyama et al<br />

2001), LDL-cholesterol-lowering activity (Manzoni et al 1998),<br />

and phagocytosis-stimulating activity in the α′ subunit (Tsuruki<br />

et al 2001). On the other hand, rice seed storage proteins, glutelin,<br />

prolamin, and globulin, do not have any significant physiological<br />

functions. Furthermore, they are deficient in lysine,<br />

w<strong>here</strong>as β-conglycinin, especially the α′ subunit, is rich in<br />

lysine. T<strong>here</strong>fore, in this study, we attempted to develop<br />

transgenic rice containing the α′ subunit for conferring high<br />

nutritional value, the modified β subunit having improved phagocytosis-stimulating<br />

activity (Maruyama et al 2003) for<br />

physiological property, and the β subunit for control of phagocytosis-stimulating<br />

activity.<br />

Transformation of rice with chimeric α′ and β genes<br />

β-conglycinin α′ and β cDNAs were connected with GluB-1<br />

and GluB-2 promoter regions in the pGTV-HPT vector (Becker<br />

et al 1992), respectively. The resultant pGTV-HPT/α′ and<br />

pGTV-HPT/β were introduced into rice calli by Agrobacterium<br />

tumefaciens-mediated transformation. Eleven and 22 lines<br />

expressing α′ and β were regenerated, respectively. Total proteins<br />

extracted by SDS buffer from T 1 seeds were spotted onto<br />

nitrocellulose membranes and the accumulation levels of α′<br />

and β were estimated immunologically. The accumulation level<br />

of α′ was basically higher than that of β. The average and highest<br />

accumulation levels of α′ and β were 3.9% and 1.9%, and<br />

8.5% and 4.3%, respectively. The lines with the highest accumulation<br />

underwent subsequent analyses. To investigate the<br />

reason for this difference, we compared the transcription level<br />

of α′ and β in rice seeds. The transcription level of α′ was<br />

close to that of β. This suggests that the difference in accumulation<br />

level between α′ and β did not depend on the transcriptional<br />

step, but depended on the posttranscriptional step.<br />

Interaction of α′ and β with rice seed storage proteins<br />

To investigate whether α′ and β interacted with rice seed storage<br />

proteins glutelin and prolamin, sequential extraction of<br />

proteins from transgenic rice seeds and western blotting using<br />

anti-α′ and β sera were conducted (Fig. 1-I). β contains no<br />

Cys residue, w<strong>here</strong>as α′ contains four Cys residues in the pro<br />

region and one near the N-terminus of the mature region. Most<br />

of the β was extracted with buffer without 2-mercaptoethernol,<br />

2-ME (fraction 1), but not by buffer with 2-ME (fraction 5)<br />

(Fig. 1-IB). On the other hand, α′ was extracted by buffer without<br />

and with 2-ME (Fig. 1-IA). In this case, fraction 5 contained<br />

acidic polypeptide of glutelin (data not shown), suggesting<br />

that α′ interacted with glutelin by disulfide bonds. Fractions<br />

9–16 containing glutelin extracted by lactic acid gave<br />

bands of α′ and β, corresponding to 19% and 20% of their<br />

total amounts, respectively, and t<strong>here</strong> was no difference in their<br />

distributions in each fraction. T<strong>here</strong>fore, α′ and β in fractions<br />

9–16 probably interacted with glutelin by hydrophobic interaction.<br />

Fraction17 containing prolamin extracted by SDS buffer<br />

also gave the bands of α′ and β, corresponding to about 10%<br />

of their total amounts. This indicates that α′ and β interacted<br />

with prolamin by disulfide bonds or hydrophobic interaction.<br />

Subcellular localization of β-conglycinin<br />

in mature transgenic seeds<br />

Subcellular localizations of α′ and β in transgenic rice endosperm<br />

were analyzed by immunocytochemical analysis using<br />

immunoelectron microscopy (IEM). <strong>Rice</strong> seeds have two<br />

types of protein bodies (Tanaka et al 1980). Protein body I<br />

(PB-I) is derived from ER, mainly accumulating prolamin, and<br />

protein body II (PB-II) is derived from vacuole, mainly accumulating<br />

glutelin and globulin. A morphological difference was<br />

not observed between nontransgenic and α′-transgenic rice<br />

seeds. When ultra-thin sections of α′-transgenic rice seed were<br />

labeled with anti-α′ antiserum conjugated with gold particles,<br />

these particles were mainly detected in the peripheral region<br />

of PB-II (Fig. 1-IIA), and nonspecific adsorption was not observed<br />

in the nontransgenic rice seeds under the same conditions.<br />

On the other hand, t<strong>here</strong> was an obvious morphological<br />

difference between nontransgenic and β-transgenic rice seeds<br />

(Fig. 1-IIB). The electron density of PB-II was uniform in<br />

nontransgenic rice seed, but PB-II in β-transgenic rice seed<br />

contained a slightly low electron density region. When this<br />

seed was reacted with anti-β serum, the gold particles were<br />

288 <strong>Rice</strong> is life: scientific perspectives for the 21st century


I<br />

–2-ME +2-ME Lactic acid<br />

A<br />

M 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17<br />

–2-ME +2-ME Lactic acid<br />

B<br />

M 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17<br />

II<br />

A<br />

C<br />

E<br />

B<br />

D<br />

F<br />

Fig. 1. Accumulation of α′ and β-conglycinin in rice seeds. (I) Sequential extraction of α′ (A) and β (B) from individual transgenic rice<br />

seeds. At first, proteins were extracted from ground rice seeds four times by buffer without 2-ME (lanes 1 to 4), then four times by<br />

buffer with 2-ME (lanes 5 to 8), subsequently eight times by lactic acid (lanes 9 to 16), finally by SDS buffer (lane 17). (II) Electron<br />

micrographs of α′- (A, B, C) and β- (B, D, F) transgenic rice seeds. A and B, mature seeds; C to F, developing seeds.<br />

observed only in the low electron density regions, and no nonspecific<br />

adsorption was observed in the nontransgenic rice<br />

seeds. Anti-glutelin gold particles were not observed in this<br />

region. These results indicate that β and glutelin were separately<br />

accumulated in a different region of PB-II. Around 10%<br />

of α′ and β expressed in the rice seeds was accumulated in<br />

PB-I.<br />

Subcellular localization of β-conglycinin in developing seeds<br />

<strong>Rice</strong> storage proteins are basically synthesized on the ER, then<br />

assembled in the ER lumen, transported to the Golgi apparatus,<br />

and sorted into the vacuoles (Krishnan et al 1986). To<br />

investigate the trafficking pathway of α′ in rice seeds, the developing<br />

seeds of α′-transgenic rice were observed immunologically<br />

by EM. T<strong>here</strong> was no morphological difference between<br />

α′-transgenic and nontransgenic rice seeds. In the early<br />

stage of PB-II formation, α′ was already localized in the peripheral<br />

region (Fig. 1-IIC). Vesicles budding from the Golgi<br />

apparatus were observed, and anti-α′ gold particles recognized<br />

these vesicles (Fig. 1-IIE). This suggests that the α′ subunit<br />

was transported to the vacuoles via the Golgi apparatus.<br />

In the β-transgenic rice seeds, some PB-II had two regions,<br />

high and low electron densities (Fig. 1-IID). The low<br />

electron density region of PB-II was not seen in immature α′-<br />

transgenic and nontransgenic rice seeds. Anti-β gold particles<br />

mainly existed in low electron density regions of PB-II. On<br />

the other hand, anti-glutelin gold particles did not exist in the<br />

low electron density regions of PB-II. Moreover, morphologically<br />

different vesicles were observed (Fig. 1-IIF, arrow).<br />

Though the size of these vesicles was analogous with that of<br />

conventional vesicles (Fig. 1-IIE, arrowhead), with a diameter<br />

of 100 to 500 nm and uniform smooth density surface (Oparka<br />

and Harris 1982), the morphologically different vesicles were<br />

surrounded by ribosome membrane-like precursor-accumulating<br />

(PAC) vesicles, observed in pumpkin seeds (Hara-<br />

Nishimura et al 1998). It has been reported that PAC vesicles<br />

serve to carry storage proteins from the ER to the vacuole,<br />

bypassing the Golgi apparatus. So, rice seeds may possess the<br />

same trafficking pathway. To investigate whether the PAC-like<br />

Session 9: Developing new uses of rice 289


A<br />

I 135 - VNPHDHQNLKIIWKAIPVNKPGRYDDFFLSSTQAQQ - 170<br />

II 135 - VNPHDHQNLKMIWLAIPVNKPGRYDDFFLSSTQAQQ - 170<br />

B<br />

1 2 3<br />

C<br />

Phagocytotic index<br />

4.0<br />

3.5<br />

3.0<br />

2.5<br />

2.0<br />

1.5<br />

1.0<br />

0.5<br />

0 0 0.01 0.1 1.0 10<br />

Concentration (mM)<br />

Fig. 2. Development of rice to stimulate human phagocytotic activity. (A) Substitution of amino<br />

acids of β subunit to confer the phagocytotic activity. I, β subunit; II, I122M/K124W. (B) SDS-<br />

PAGE of proteins extracted by buffer from β and I122M/K124W transgenic rice seeds. Lane 1,<br />

nontransgenic rice; lane 2, β transgenic rice; lane 3, I122M/K124W-transgenic rice. (C) Phagocytotic<br />

assay of I122M/K124W and β. Solid line, I122M/K124W; dotted line, β.<br />

vesicles are derived from the ER, we observed immunologically<br />

with anti-serum against binding protein (BiP) the ERlocated<br />

chaperon protein. Consequently, BiP was located in<br />

the PAC-like vesicles (data not shown), suggesting that the β<br />

subunit was transported to the vacuoles not only from the Golgi<br />

apparatus but also from the ER, bypassing the Golgi apparatus.<br />

Developing rice to stimulate human phagocytotic activity<br />

We also aimed to develop rice to stimulate human phagocytotic<br />

activity. For this, we had substituted two amino acid residues<br />

of the β subunit to confer the phagocytotic activity (Fig.<br />

2A) to produce I122M/K124W (Maruyama et al 2003). Subsequently,<br />

we connected I122M/K124W cDNA with the GluB-<br />

2 promoter, and introduced it into rice seeds. The accumulation<br />

level of I122M/K124W was similar to that of native β.<br />

We extracted and purified I122M/K124W and native β from<br />

individual transgenic rice seeds (Fig. 2B), and subjected them<br />

to a phagocytotic assay. At first, neutrophils were purified from<br />

heparinized human blood. Fluorescent beads were opsonized<br />

with human serum, and these beads were then added into neutrophils.<br />

The intensity of phagocytosis was shown as the phagocytic<br />

index, which is presented as the number of incorporated<br />

fluorescent beads per 100 neutrophils. The phagocytotic<br />

activity of human neutrophils of I122M/K124W after digestion<br />

by trypsin was about three times higher than that of native<br />

β (Fig. 2C).<br />

Conclusions<br />

In this study, we succeeded in developing transgenic rice accumulating<br />

α′ and β. α′ accumulated in seeds about twice as<br />

much as β. It was presumed that the difference in the accumulation<br />

level was dependent on whether they interact with glutelin<br />

through disulfide bonds or not. When we observed these<br />

transgenic rice seeds by EM, it was suggested that α′ and β<br />

were transported to the vacuole through the Golgi apparatus.<br />

In addition, a part of β was transported from the ER to the<br />

vacuoles, bypassing the Golgi apparatus.<br />

I122M/K124W was accumulated similarly to native β.<br />

The phagocytotic activity of I122M/K124W was about three<br />

times higher than that of native β.<br />

References<br />

Aoyama T, Kohno M, Saito T, Fukui K, Takamatsu K, Hashimoto T,<br />

Yamamoto Y, Hirotsuka M, Kito M. 2001. Reduction by<br />

phytate-reduced soybean beta-conglycinin of plasma triglyceride<br />

level of young and adult rats. Biosci. Biotechnol.<br />

Biochem. 65:1071-1075.<br />

Becker D, Kemper E, Schell J, Masterson R. 1992. New plant binary<br />

vectors with selectable markers located proximal to the<br />

left T-DNA border. Plant Mol. Biol. 20:1195-1197.<br />

Hara-Nishimura I, Shimada T, Hatano K, Takeuchi Y, Nishimura M.<br />

1998. Transport of storage proteins to protein storage vacuoles<br />

is mediated by large precursor-accumulating vesicles.<br />

Plant Cell 10:825-836.<br />

290 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Krishnan HB, Franceschi VR, Okita TW. 1986. Immunochemical<br />

studies on the role of the Golgi complex in protein body formation<br />

in rice seeds. Planta 169:471-480.<br />

Manzoni C, Lovati MR, Ggianazza E, Morita Y, Sirtori CR. 1998.<br />

Soybean protein products as regulators of liver low-density<br />

lipoprotein receptors. II. α-α′ rich commercial soy concentrate<br />

and α′ deficient mutant differently affect low-density lipoprotein<br />

receptor activation. J. Agric. Food Chem. 46:2481-<br />

2484.<br />

Maruyama N, Maruyama Y, Tsuruki T, Okuda E, Yoshikawa M,<br />

Utsumi S. 2003. Creation of soybean β-conglycinin β with<br />

strong phagocytosis-stimulating activity. Biochim. Biophys.<br />

Acta 1648:99-104.<br />

Oparka KJ, Harris N. 1982. <strong>Rice</strong> protein-body formation: all types<br />

are initiated by dilation of the endoplasmicreticulum. Planta<br />

154:184-188.<br />

Sirtori CR, Lovati MR, Manzoni C, Monetti M, Pazzucconi F, Gatti<br />

E. 1995. Soy and cholesterol reduction: clinical experience.<br />

J. Nutr. 125:598S-605S.<br />

Tanaka K, Sugimoto T, Ogawa M, Kasai Z. 1980. Isolation and characterization<br />

of two types of protein bodies in the rice endosperm<br />

glutelin and prolamin. Cereal Chem. 48:169-181.<br />

Tsuruki T, Takagata K, Yoshikawa M. 2001. Soymetide, an<br />

immunostimulating peptide derived from soybean β-<br />

conglycinin, is an fMLP agonist. FEBS Lett. 540:206-210.<br />

Notes<br />

Authors’ addresses: Takayasu Motoyama, Nobuyuki Maruyama,<br />

Takahiko Higasa, Masaaki Yoshikawa, and Shigeru Utsumi,<br />

Graduate School of Agriculture, Kyoto University, Japan, e-<br />

mail: mtaka@kais.kyoto-u.ac.jp; Fumio Takaiwa, Department<br />

of Plant Biotechnology, National <strong>Institute</strong> of Agrobiological<br />

Sciences, Japan.<br />

Wrap-up of Session 9<br />

B.O. Juliano of the Philippine <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong> gave an<br />

“Overview of rice and rice-based products.” He pointed out the<br />

importance of the amylose content of rice as table rice, for example,<br />

in relation to palatability and glycemic index. For materials<br />

for baked and steamed products, the milling method was<br />

shown to be important. He indicated that the effect of food processing<br />

on protein quality, level of antioxidants, mycotoxin level,<br />

and acrylamide content has to be monitored. Finally, he concluded<br />

that the high level of antioxidants in rice bran, oryzanol,<br />

tocopherols, and tocotrienols, as reflected in high unsaponifiable<br />

matter in bran oil, contributes, in addition to phytic acid, to the<br />

hypocholesterolemic effect and other health benefits of full-fat<br />

bran.<br />

S. Isobe of the National Food <strong>Research</strong> <strong>Institute</strong>, Japan,<br />

discussed the “Sterilization effect of electrolyzed water on rice<br />

food.” He pointed out that controlling microorganisms from raw<br />

materials to products and confirming safety in product distribution<br />

are most important for enhancing rice consumption in the<br />

development of new rice products, such as aseptic packaged<br />

rice and rice cookies. He found that the combination of acidicelectrolyzed<br />

water and alkaline-electrolyzed water is very effective<br />

for controlling microorganisms without a change in color and<br />

pH. He reported the effect of electrolyzed water on preventing<br />

raw rice from microorganism infestation by an in vitro test using<br />

Bacillus subtillis spores.<br />

H.C. Choi of the National <strong>Institute</strong> of Crop Science, Korea,<br />

covered the “Current status of varietal improvement and use of<br />

specialty rice in Korea.” He mentioned various kinds of newly<br />

developed specialty rice varieties, such as low-amylose dull,<br />

opaque endosperm, or high-fiber mutants, and high-amylose and<br />

high-lysine rice in Korea. He explained the relationship between<br />

the physicochemical properties and processing suitabilities for<br />

rice snacks, rice noodles, rice bread, and fermented products.<br />

High-fiber and low-digestible rice was revealed to have a considerable<br />

dietetic effect and to lower the blood-sugar level. He concluded<br />

that breeding to improve the utility and nutritional function<br />

in rice for the future should focus on diversification in the<br />

morphological, physicochemical, and nutritional characteristics<br />

of rice grain suitable for processing various value-added rice foods.<br />

K. Ohtsubo of the National Food <strong>Research</strong> <strong>Institute</strong>, Japan,<br />

discussed “Processed novel foodstuffs from pregerminated<br />

brown rice by a twin-screw extruder.” He mentioned various kinds<br />

of Japanese processed rice products, such as retort-pouched<br />

rice, dried cooked rice, aseptic cooked rice, and pregerminated<br />

brown rice. He developed a novel foodstuff from pregerminated<br />

brown rice by a twin-screw extruder. The pregerminated brown<br />

rice was rich in gamma-aminobutyric acid (GABA). The extruded<br />

pregerminated brown rice contained more oryzanol, inositol, ferulic<br />

acid, and dietary fibers than polished rice. Wheat bread prepared<br />

with 30% of the extruded pregerminated brown rice contained<br />

more GABA, free sugars, and amino acids than ordinary bread.<br />

These results showed that a novel foodstuff from extruded<br />

pregerminated brown rice would be acceptable to consumers or<br />

the food industry as a promising foodstuff that contains more<br />

bio-functional components than ordinary rice products.<br />

Professor R. Hayashi of Nihon University covered “Highpressure<br />

food processing of rice and starchy foods.” He pointed<br />

out that high pressure is used for food processing at high temperature.<br />

When starch is pressurized at 200 MPa or higher, it<br />

changes its physical properties, including loss of birefringence<br />

and increases in amylase digestibility and crystalline properties.<br />

Thus, high-pressure food processing is now applied in rice and<br />

its related food industry in Japan. He explained the high-pressure<br />

effects on starches and mentioned the recent development<br />

of the high-pressure technique in the food industry.<br />

Session 9: Developing new uses of rice 291


E. Champagne of the Southern Regional <strong>Research</strong> Center,<br />

USDA/ARS, USA, reported on “Developing novel processes for<br />

incorporating the unique nutritional and functional properties of<br />

rice into value-added products.” She pointed out that, with more<br />

efficient production and milling and with value-added applications<br />

for rice, its components and co-products are necessary to<br />

prosper in both the domestic and export arena. She highlighted<br />

novel processes developed by Southern Regional <strong>Research</strong> Center<br />

scientists, such as (1) a cost-effective, environment-friendly<br />

rapid technology for separating rice starch and protein using physical<br />

means, (2) a dry instantization process for quick-cooking brown<br />

rice, (3) rice batter that absorbs 60% less oil than wheat batter,<br />

(4) rice donuts with textural properties of wheat donuts, but substantially<br />

lower oil uptake, and (5) rice bread developed for preparation<br />

using a home bread machine.<br />

Posters included ones such as “Dehydrin proteins in rice<br />

bran” by M. Momma of the National Food <strong>Research</strong> <strong>Institute</strong>,<br />

“Physicochemical properties of modified flour and its use for processed<br />

food” by T. Takahashi of the Akita Prefectural Food <strong>Research</strong><br />

<strong>Institute</strong>, and “Introduction of soybean beta-conglycinin<br />

into rice to improve nutritional and physiological values” by T.<br />

Motoyama of Kyoto University. Other topics covered were the<br />

breeding of novel-pigmented rice, giant-embryo rice, high-yielding<br />

rice for cattle feed, and new technology for the preparation of<br />

pregerminated brown rice.<br />

292 <strong>Rice</strong> is life: scientific perspectives for the 21st century


SESSION 10<br />

Postharvest technology for efficient processing<br />

and distribution of rice<br />

CONVENER: T. Kimura (Univ. of Tsukuba)<br />

CO-CONVENER: J. Rickman (<strong>IRRI</strong>)


Postharvest technology for rice in India: a changing scenario<br />

Pallab Kumar Chattopadhyay<br />

India produces about 93 million tons of rice, which is about<br />

one-fifth of world production. India is the second-largest riceproducing<br />

country in the world. More than 200 commercial<br />

rice varieties of indica subspecies are grown on an area of<br />

about 45 million hectares, with 25% irrigated area. Yield averages<br />

2,086 kg ha –1 (FAI 2003). <strong>Rice</strong> provides an occupation<br />

for more laborers than any other industry in India. About twothirds<br />

of the production is retained by producers for their own<br />

consumption and for seed. Of the total quantity of rice available,<br />

about 10% is processed into products such as beaten rice,<br />

puffed rice, puffed paddy, and deep-fried products such as<br />

papads and chakli, and fermented products such as idli, dosa,<br />

and uthapam. India exports rice valued at about US$1.4 billion,<br />

of which Basmati is $420 million and non-Basmati is<br />

$980 million (MFPI 2003).<br />

Development of a modernization program<br />

In 1955, the government of India set up a committee to examine<br />

the problems concerning the development of a rice-milling<br />

industry. It recommended that preference be given to shellertype<br />

mills over the existing metallic huller. On the basis of<br />

these recommendations, the government promulgated the <strong>Rice</strong><br />

Milling Industry (Regulation and Licensing) Act and the Rules<br />

t<strong>here</strong>of for regulating the industry. In 1963, the government,<br />

under the Intensive Agricultural Development Program, along<br />

with the Ford Foundation, undertook a study on the rice-milling<br />

industry. Seven modern rice mills of rubber-roll sheller<br />

type were imported from Japan and Germany and were set up<br />

in seven rice-growing states. The remaining components,<br />

namely, parboiling plants, mechanical dryers, silos, and mechanical<br />

handling and conveying equipment, were constructed<br />

and fabricated in the country. A report submitted in 1968 (MA<br />

1971) showed that modern mills gave a substantial increase in<br />

total rice outturn and head-rice yield for both raw and parboiled<br />

paddy over existing sheller mills and a much higher<br />

increase over existing huller mills (Table 1). Further, modern<br />

mills yielded by-products (husk and bran) separately for better<br />

end uses. Mechanical drying increased yield by 1–2%, and<br />

the improved technique of parboiling in conjunction with mechanical<br />

drying increased yield by 2%. With silo storage, estimated<br />

additional yield ranged from 2% to 4%.<br />

The government of India recognized that t<strong>here</strong> was vast<br />

potential for improving the entire postharvest technology of<br />

the paddy/rice system. Accordingly, the <strong>Rice</strong> Milling Industry<br />

(Regulation) Act, 1958, and <strong>Rice</strong> Milling Industry (Regulation<br />

and Licensing) Rules, 1959, were amended in 1968 and<br />

1970, respectively. In the initial phase, a battery of hullers,<br />

huller-cum-sheller combinations, and shellers in the organized<br />

sector was brought under the purview of modernization. The<br />

Table 1. Mean average percentages of additional outturns of total<br />

rice and head rice obtained in modern mills versus conventional<br />

mills for raw and parboiled paddy.<br />

Mean average percentage of additional outturns<br />

of rice in modern mills versus conventional mills<br />

Type of paddy<br />

milled Total rice Head rice<br />

Sheller Huller Sheller Huller<br />

Raw 2.5 6.6 6.1 15.1<br />

(0.8–4.2) a (1.8–12.5) (1.9–12.9) (6.9–24.7)<br />

Parboiled 0.8 1.6 1.3 4.1<br />

(0.0–1.3) (0.3–2.5) (0.8–2.5) (1.0–8.5)<br />

a<br />

Numbers in parentheses represent the variations of actual additional outturns from<br />

different varieties of paddy and over different mills. Source: MA (1971).<br />

single hullers were left out for the pending development and<br />

supply of modern equipment of the same capacity (250 to 300<br />

kg h –1 ) in the country.<br />

Apart from the seven modern rice mills initially set up<br />

in the pilot study, the Food Corporation of India established<br />

25 modern rice mills without including silo storage. In addition,<br />

the cooperative and private sector together established<br />

55 modern rice mills and modernized 51 existing mills.<br />

Modernization of huller rice mills<br />

Over the years, several designs of low-cost mini rice mills became<br />

available in the country. In July 1976, by an amendment<br />

to the <strong>Rice</strong> Mill Industry Rules, provision was made for the<br />

gradual modernization of single-huller mills by adding rubber-roll<br />

shellers or centrifugal dehuskers, paddy cleaners, and<br />

separators. A huller subsidy scheme with 50% of the cost of<br />

modernization provided to each beneficiary was being implemented<br />

in six states to encourage the modernization of huller<br />

mills.<br />

Modernization of paddy parboiling<br />

During the 1950s, the Indian Council of Medical <strong>Research</strong><br />

sponsored research at the Central Food Technological <strong>Research</strong><br />

<strong>Institute</strong> (CFTRI), Mysore, and Jadavpur University, Calcutta,<br />

for improving the parboiling and drying processes as well as<br />

nutritional and cooking quality of rice. In 1957-58, the Ministry<br />

of Food and Agriculture recommended the new technique<br />

of parboiling developed by CFTRI for popularization.<br />

Modernization of paddy/rice storage<br />

In 1965-66, the “Save Grain Campaign” was organized by the<br />

government, covering 19 states/union territories to popularize<br />

an effective method of grain storage among farmers, traders,<br />

294 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Number of modern mills<br />

30,100<br />

32,200<br />

33,557 34,110 34,668 34,668 34,668 35,088<br />

25,000<br />

1991 1992 1993 1994 1995 1996 1997 1998 1999<br />

Year<br />

Fig. 1. Growth of modern rice mills. Source: MFPI (2003).<br />

etc. The Indian Grain Storage <strong>Institute</strong> was established at Hapur,<br />

with two substations at Ludhiana and Bapatla for conducting<br />

applied research, development, and training in grain storage<br />

with the assistance of the United Nations Development<br />

Programme. Storage structures made of steel, concrete, and<br />

metal-plastic combinations at the farmers’ level were being<br />

popularized, initiated through assistance received from the<br />

United Kingdom and Netherlands Freedom From Hunger Campaign,<br />

and USAID.<br />

Training, research, and extension<br />

The government established in 1970 a full-fledged <strong>Rice</strong> Process<br />

Engineering Centre (presently, Post Harvest Technology<br />

Centre) at the Indian <strong>Institute</strong> of Technology, Kharagpur, to<br />

provide training facilities at the Bachelor, Masters, and Ph.D.<br />

levels, and short-term training courses for rice mill engineers,<br />

managers, and operators. The Ministry of Food Processing<br />

Industries (MFPI) has been sponsoring various research and<br />

development activities through this Centre as well as the Paddy<br />

Processing <strong>Research</strong> Centre, Thanjavur. MFPI has also set up<br />

a technical cell to assist the industry by providing technical<br />

assistance and consultancy service. In addition, extension and<br />

training work was undertaken through a network of ten regional<br />

extension service centers. Grant-in-aid is being provided to<br />

various institutions to promote research and development, extension,<br />

and training work on postharvest technology for rice.<br />

Development of modern equipment<br />

Realizing that the country would require modern rice-milling<br />

equipment on a large scale, three manufacturers were initially<br />

given licenses to manufacture machinery with suitable modifications<br />

in collaboration with the companies from w<strong>here</strong> seven<br />

modern mills were imported for the pilot study.<br />

To encourage the production of good-quality rice mills<br />

and allied machinery by various manufacturers, four testing<br />

centers were set up in four different regions of the country to<br />

undertake testing of mill machinery according to standards<br />

prescribed by the Bureau of Indian Standards.<br />

Present position of the industry<br />

<strong>Rice</strong> postharvest technology in India has come a long way over<br />

the past three decades. Now, more than 50% of the overall rice<br />

production is processed by modern mills, with a steady growth<br />

in numbers (Fig. 1), about 40% by traditional mills, and about<br />

10% by hand pounding. T<strong>here</strong> are now 35,088 modern/modernized<br />

mills (0.5–4 t h –1 ), 4,538 under-runner disc shellers,<br />

8,385 hullers-cum-shellers, and 91,287 metallic hullers (MFPI<br />

2003).<br />

Fifty percent of the total paddy production is parboiled.<br />

The CFTRI method of parboiling is used mostly by modern<br />

mills to drastically reduce soaking time and improve rice quality.<br />

However, the age-old practices of premilling treatments at<br />

the village level and traditional parboiling methods are still<br />

being followed in some commercial mills.<br />

Drying of paddy is carried out by sun drying in open<br />

drying yards and/or by mechanical drying in L.S.U.-type dryers<br />

in commercial mills.<br />

The estimated losses in storage and handling are about<br />

10%. About 70% of the produce is stored by farmers in small<br />

indigenous storage structures with some modifications and<br />

made of locally available materials. The commercial-scale use<br />

of bag storage of paddy/rice in godowns is common.<br />

Out of a potential availability of 1 million t of bran oil,<br />

only 0.5 million t is produced from 3.4 million t of bran, twothirds<br />

of which is of edible grade and the rest is of industrial<br />

grade. A part of the edible quality is consumed via root blending<br />

or hydrogenation. About 70,000–80,000 t of the oil are<br />

used for direct cooking purposes. De-oiled bran is mainly used<br />

for cattle feed.<br />

<strong>Rice</strong> husks are primarily used as fuel in husk-fired furnaces<br />

to produce steam through a boiler for parboiling, run-<br />

Session 10: Postharvest technology for efficient processing and distribution of rice 295


ning the mill using a steam engine and hot air for drying. Producer<br />

gas is being produced from husks as fuel for a diesel<br />

engine to run the mill and to generate electricity. Husks are<br />

also being used commercially to produce furfural.<br />

At present in India, a large number of trained technical<br />

personnel are available. Many research workers are actively<br />

involved in rice postharvest technology research. India manufactures<br />

and also exports all types of rice-processing machinery<br />

and equipment. India also provides training to foreign personnel.<br />

Constraints and concerns<br />

T<strong>here</strong> have been several problems with the modern large-capacity<br />

rice mills: the inadequate supply of paddy for continuous<br />

operation throughout the year, controls and restrictions<br />

imposed by the government with regard to price, a levy, and<br />

movement for paddy and rice. The high capital cost for silos<br />

prohibits the use of integrated units. Because of the unavailability<br />

of good-quality rice bran and its inadequate timely collection<br />

from the mills, the use of bran is very poor. A genuine<br />

need exists for efficient low-cost mini rice mills to replace the<br />

existing metallic hullers.<br />

Even though sufficient systematic development has been<br />

made and experience has been gained, much remains to be<br />

done for rice postharvest technology to play an important role<br />

in the proper use of valuable resources and in contributing<br />

substantially toward Indian economic growth.<br />

References<br />

FAI (Fertilizer Association of India). 2003. Fertilizer statistics. New<br />

Delhi (India): FAI.<br />

MA (Ministry of Agriculture, Government of India). 1971. Modern<br />

versus traditional rice mills—a performance study. Delhi (India):<br />

MA.<br />

MFPI (Ministry of Food Processing Industries, Government of India).<br />

2003. Annual report. New Delhi (India): MFPI.<br />

Notes<br />

Author’s address: Professor, Post Harvest Technology Centre, Agricultural<br />

and Food Engineering Department, Indian <strong>Institute</strong><br />

of Technology, Kharagpur 721302, India.<br />

Development of a far-infrared radiation dryer for grain<br />

Yasuyuki Hidaka, Kotaro Kubota, and Tomohiko Ichikawa<br />

Drying, especially for rice, is an important postharvest process<br />

in monsoon climate areas such as Japan, w<strong>here</strong> t<strong>here</strong> is<br />

much precipitation during the harvest period. The Japanese<br />

Ministry of Agriculture, Forestry, and Fisheries has taught farmers<br />

to dry crops within 8 hours after harvest.<br />

Currently in Japan, heated-air (HA) drying by burning<br />

kerosene is regularly used for artificial grain drying. However,<br />

to maintain grain quality, the combustion heat is mixed with<br />

ambient air and its temperature is lowered to about 40 to 50<br />

°C. Heat energy cannot be used effectively because of the need<br />

to maintain grain quality. Although the HA dryer has evolved,<br />

its capability is limited from the energy viewpoint.<br />

The applicability of far-infrared radiation (FIR) to grain<br />

drying was investigated earlier by Harry and David (1959) and<br />

then by Faulkner and Wratten (1969). FIR radiation can efficiently<br />

transfer energy to an object. Moreover, the wavelength<br />

of FIR is 2.5 to 1,000 µm, and grain has an infrared absorption<br />

wavelength in this range. For this reason, FIR can be used to<br />

heat grain efficiently. Heat emission causes very little energy<br />

loss in transmitting drying energy to the grain.<br />

In Japan, the possibility of FIR drying for rough rice<br />

was also evaluated by Bekki (1991) and Matusoka (1990). Itoh<br />

et al (1994) and Mouri and Huoqing (1996) also explored the<br />

possible application of FIR to other agricultural products. In<br />

their studies, they acquired basic drying data for rough rice<br />

using an electric heater. However, they needed to change the<br />

dryer structure and modify it to use an FIR electric heater, so<br />

that it was difficult to develop commercial models.<br />

We decided to use a design including the FIR body with<br />

a kerosene burner in the recirculating batch dryer because it is<br />

widely used in Japan.<br />

Schematic of the FIR dryer<br />

The concept of an FIR dryer and an HA dryer is shown in<br />

Figure 1. The HA dryer heats the air to 40 to 50 °C by mixing<br />

the flame and the ambient air, and passes the heated air through<br />

the grain layer. The FIR dryer converted thermal energy by<br />

heating an FIR body with a kerosene burner. Moreover, exhaust<br />

heat was reused for drying to increase drying efficiency.<br />

The FIR body was made from a stainless-steel pipe coated<br />

with silicone resin. FIR body surface areas were 1.6 to 3.6 m 2 .<br />

The rate of radiation was 0.9, and the FIR body surface temperature<br />

was 300 to 500 °C. The center of the wavelength was<br />

4.3 to 5.2 µm as determined by Wien’s displacement law. An<br />

electromagnetic wave containing far-infrared radiation is generated.<br />

These spectra are the absorption band of water. Moreover,<br />

30–50% of the input energy was converted into FIR.<br />

The FIR body was useful w<strong>here</strong>ver installed. Two types<br />

of dryers are used, one with the FIR body installed in the drying<br />

chamber and the other with it installed in the space be-<br />

296 <strong>Rice</strong> is life: scientific perspectives for the 21st century


FIR dryer<br />

Ambient air<br />

HA dryer<br />

Ambient air<br />

Exhaust<br />

heat<br />

Heated air<br />

Fig. 1. Concept of the FIR dryer.<br />

FIR body<br />

Grain layer<br />

tween the rotary valve and the under-screw conveyer, considering<br />

development costs.<br />

FIR<br />

Burner<br />

Suction fan<br />

Burner Heated air Grain layer Suction fan<br />

the ratio that compared FIR and HA represented the rate of<br />

energy reduction.<br />

Rough rice was husked by hand before and after drying,<br />

and the cracked grain was judged visually using a grain scope<br />

(Shizuoka Seiki Co. Ltd., DC-50). The difference in the cracking<br />

rate before and after drying represented the increase in<br />

cracking rate.<br />

Noise measurements. The A-weighted sound pressure<br />

level was measured based on JIS Z8731. The sound level meter<br />

was located 1.0 m from the dryer at a height of 1.2 m. The<br />

average level of noise for a fixed period of drying time was<br />

measured. We measured the A-weighted sound pressure level<br />

when the difference between the background noise and the real<br />

A-weighted sound pressure level was 10 dB or more.<br />

Quality tests. The germination tests were performed<br />

based on the Japanese Food Agency method. The palatability<br />

tests were performed using the rice dried by HA and FIR.<br />

Twenty panelists evaluated palatability based on six criteria:<br />

appearance, flavor, taste, viscosity, hardness, and total evaluation.<br />

The palatability tests were performed by the Japan Grain<br />

Inspection Association.<br />

Materials and methods<br />

Materials<br />

Nine varieties of rough rice (Hinohikari, Koshihikari,<br />

Akitakomachi, Haenuki, Kinuhikari, Yumeminori,<br />

Tukinohikari, Akiroman, and Asanihikari) and five varieties<br />

of wheat (Nourinn61, Kitakami, Chikugoizumi, Chihoku, and<br />

Bandouwase) were used.<br />

Initial moisture content (MC) was 18% w.b. to 29% w.b.<br />

for rough rice and 15% w.b. to 39% w.b. for wheat. Final MC<br />

was 15% w.b. for rice and 12.5% w.b. for wheat. Grain weight<br />

was 1.2 to 6 t, with an average of 3.5 t.<br />

Methods<br />

Drying tests. To compare drying performance, we prepared<br />

FIR and HA dryers with identical capacities as in the drying<br />

test. We used grain from the same field so that drying characteristics<br />

did not change. When grain was taken into or discharged<br />

from the dryer, we took 20 samples that were 1 kg per<br />

sample. And we measured MC and grain quality using these<br />

samples.<br />

Drying time was calculated from start time to finish time,<br />

when the moisture meter attached to the dryer measured 15%<br />

w.b. The true MC was measured by the air-oven method and<br />

drying rate was calculated.<br />

Heated-air temperature, exhaust-air temperature, FIR<br />

body surface temperature, grain temperature, atmosp<strong>here</strong> temperature,<br />

and humidity were automatically measured at 10-min<br />

intervals during drying using a data logger and thermocouple.<br />

The amount of water removed was measured automatically by<br />

load cells in the bottom of a dryer. Fuel consumption was calculated<br />

automatically by a balance and the amount of electricity<br />

used was measured by a wattmeter. The moisture extracted<br />

by 1 kg kerosene and 1 kWh electricity was calculated, and<br />

Results and discussion<br />

Drying tests<br />

The average drying rate was 0.75% h –1 , the same as for the<br />

HA dryer. Under some conditions, the drying rate was 1.2%<br />

h –1 . Furthermore, the increase in cracking rate of rice was satisfactory<br />

at 2% or less. Although the cracking rate of rice dried<br />

by HA was increased at drying rates exceeding 1% h –1 , t<strong>here</strong><br />

was no increase in cracking rate by FIR drying. We thus demonstrated<br />

the possibility of high-speed drying using the FIR<br />

dryer.<br />

The FIR dryer’s energy efficiency averaged 5.11 MJ<br />

kg –1 H 2 O, which is 10% better than that of the HA dryer. To<br />

perform more practical evaluations, specific moisture extraction<br />

rates by kerosene and electricity were averaged and found<br />

to be 9.43 kg H 2 O kg –1 and 14.6 kg H 2 O kWh –1 . We could<br />

thus reduce electricity consumption by 30% and kerosene consumption<br />

by 10% vis-à-vis the HA dryers (Table 1).<br />

Noise measurements<br />

Because the kerosene was burned in the FIR body with a burner,<br />

combustion noise was low. Moreover, the FIR dryer could<br />

operate with a 10% reduction in fan RPM compared with the<br />

HA dryer. T<strong>here</strong>fore, the A-weighted sound pressure level was<br />

reduced by an average of 3 dB.<br />

Drying is actually performed at night in many cases, and<br />

so a low noise level is highly desirable.<br />

Quality tests<br />

The germination rate averaged 98.3%. FIR drying t<strong>here</strong>fore<br />

did not decrease the germination rate compared with HA drying.<br />

Palatability testing revealed that rice dried by the FIR<br />

dryer tended to have greater viscosity and better palatability.<br />

Session 10: Postharvest technology for efficient processing and distribution of rice 297


Table 1. Results of drying tests.<br />

Item<br />

Unit<br />

Rough rice<br />

Wheat<br />

FIR a HA FIR HA<br />

Moisture content w.b. Before 21.7 21.7 21.8 21.8<br />

After 14.8 14.9 12.4 12.3<br />

Grain temperature °C 30.5 28.8 33.8 33.0<br />

Heated air temperature °C 48.4 43.4 52.8 52.7<br />

Exhaust air temperature °C 29.4 27.6 32.0 31.1<br />

Ambient air: Temperature °C 20.3 22.3<br />

Humidity % 79.9 71.3<br />

Air flow rate m 3 s –1 t –1 0.36 0.51 0.27 0.34<br />

Drying rate % h –1 0.72 0.69 0.78 0.79<br />

Consumption of kerosene Kg 27.2 29.2 40.7 43.1<br />

Consumption of electricity kWh 18.5 25.4 24.0 28.6<br />

Energy efficiency MJ kg –1 H 2 O 4.98 5.65 5.24 5.71<br />

FIR/HA ratio % 88.1 91.8<br />

Specific moisture extraction kg H 2 O kg –1 9.72 8.86 9.14 8.47<br />

rate by kerosene<br />

FIR/HA ratio % 110 108<br />

Specific moisture extraction kg H 2 O kWh –1 14.6 10.4 14.6 12.0<br />

rate by electricity<br />

FIR/HA ratio % 140 122<br />

a FIR = far-infrared radiation, HA = heated air.<br />

Although the mechanism is not yet perfected, we demonstrated<br />

the potential of high-quality drying using an FIR dryer.<br />

Conclusions<br />

The FIR dryer developed has satisfactory drying, energy efficiency,<br />

and energy conservation compared with the HA dryer.<br />

The reduced noise level will be comfortable to work with. In<br />

addition, palatability tended to improve. Thus, the potential<br />

for high-quality drying was demonstrated.<br />

These dryers have been produced with commercial models<br />

from cooperating research companies since 1998, and the<br />

34,000 FIR dryers so far produced were distributed among<br />

individual farmers in Japan. We now have a series of FIR dryers<br />

with a capacity of 1 to 30 t for a drying facility.<br />

References<br />

Bekki E. 1991. Rough rice drying with a far-infrared panel heater.<br />

JSAM 53(1):55-63.<br />

Faulkner MD, Wratten FT. 1969. The Louisiana State University<br />

infrared preheat rice drier. 61st Annual Progress Report, <strong>Rice</strong><br />

<strong>Research</strong> Station, Louisiana State University Agricultural<br />

Center, Crowley, Louisiana.<br />

Harry WS, David WR. 1959. Drying rough rice with infra-red radiation.<br />

<strong>Rice</strong> J. June, p 16-38.<br />

Itoh K, Chung SH. 1994. Drying of agricultural products using long<br />

wave infrared radiation. Part 1. Fundamental heating characteristics<br />

of long wave infrared radiation. SASJ 25(1):39-45.<br />

Matsuoka T. 1990. Drying characteristics of rough rice by far-infrared<br />

radiation heating. SASJ 21(2):85-93.<br />

Mouri K, Huoqing L. 1996. Study on the drying of agricultural products<br />

by using far-infrared ray. Part 1. The performance of the<br />

drying device and the heating properties of agricultural products.<br />

SASJ 27(2):57-63.<br />

Notes<br />

Authors’ address: Bio-oriented Technology <strong>Research</strong> Advancement<br />

Institution (BRAIN), <strong>Institute</strong> of Agricultural Machinery<br />

(IAM), 1-40-2 Nisshin, Kita-ku, Saitama, 331-8537 Japan, e-<br />

mail: yhidaka@affrc.go.jp.<br />

Acknowledgments: We are very grateful for the cooperation of the<br />

research companies Iseki Co., Ltd.; Kaneko Agricultural Machinery<br />

Co., Ltd.; Satake Corporation; Shizuoka Seiki Co.,<br />

Ltd.; and Yamamoto Co., Ltd.<br />

298 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Status of rice milling and use of by-products<br />

Naoto Shimizu, Yuji Katsuragi, and Toshinori Kimura<br />

In addition to energy, materials can be recovered from biomass,<br />

and it is clear that the world must, from now on, substantially<br />

increase the use of biomass as a source of both energy<br />

and materials by optimizing biomass production, conversion,<br />

and use technologies.<br />

<strong>Rice</strong> milling and processing need to be part of this effort,<br />

given that the rice-milling process generates by-products,<br />

such as husks, bran, and broken kernels. Here, we report on<br />

several aspects of rice milling and processing: (1) the use industry<br />

and new rice products, (2) the application of the dosa<br />

fermentation process to indica-type rice use, (3) a finishing<br />

system for manufacturing prewashed rice, and (4) an overview<br />

of rice milling and processing in developing countries.<br />

The use industry and new rice products<br />

Figure 1 presents uses of rice and by-products in the rice industry.<br />

In Japan, 1,200,000 tons of rice are used for processing<br />

raw materials. This is about 12% of the total consumption.<br />

The main application is for sake (600,000 t), rice confectionary<br />

(200,000 t), miso (180,000 t), and other purposes (200,000 t).<br />

The product of processed rice consists mainly of whole-milled<br />

rice grain and its directly processed materials. Sake, miso,<br />

packed rice-cake, and arare are produced directly by kojimaking<br />

and rice-cake making from whole-milled rice grain.<br />

Flour and starch-making rarely occur by milling and wet-milling<br />

such as are done with wheat and maize. A very small amount<br />

of rice flour and starch has been distributed and used.<br />

Paddy<br />

Parboiling<br />

Parboiled rice<br />

Husking process<br />

Brown rice<br />

<strong>Rice</strong> milling<br />

Husk<br />

SteamingBrewing<br />

Pressurization/steamingDrying<br />

Roasting<br />

<strong>Rice</strong> bran<br />

Sake<br />

NEO-unpolished brown rice<br />

Brown rice tea<br />

Grading<br />

Broken rice<br />

Animal feed, for beer, noodles, confectionery<br />

White rice<br />

Prewashed rice<br />

Enriched rice-vitamin, mineral<br />

Steaming<br />

Fermentation<br />

Brewing<br />

Sake, beer, vinegar, alcohol<br />

Roasting<br />

Roasted rice<br />

For milling<br />

For confectionery<br />

Puffing<br />

Puffed rice<br />

Pressurization puffing<br />

SteamingFlaking<br />

Puffed rice crackers<br />

<strong>Rice</strong> flakes<br />

Roasting<br />

Drying<br />

Flour milling<br />

Pulverize<br />

Flour for confectionery<br />

Flour for confectionery<br />

Flour milling<br />

CookingFreezing<br />

Drying<br />

Solidifying<br />

Steamed rice<br />

For bread, dosa<br />

Frozen food<br />

Instant rice<br />

Sushi/rice, ball/rice, burger<br />

Fig. 1. Uses of rice and by-products in the rice industry.<br />

Session 10: Postharvest technology for efficient processing and distribution of rice 299


<strong>Rice</strong> grits and their processing by wet-milling<br />

<strong>Rice</strong> grits or broken rice kernels are used for brewing. Generally,<br />

wet-milled rice flour is superior to dry-milled flour for<br />

making baked products. Adjuncts (usually 20–40% of the total<br />

ingredients) are used to obtain fermentable sugars at a lower<br />

cost, and play a very important and specific role in giving a<br />

characteristic quality to beer to attract consumers. All-malt beer<br />

is richer in flavor and has more fullness of body and a darker<br />

color. On the other hand, beer with adjuncts has a lighter color<br />

and taste, so that consumers drink more because of its less<br />

satiating taste. Also, beer with adjuncts has a higher colloidal<br />

stability because of its lower nitrogen content (Yoshizawa and<br />

Kishi 1985).<br />

Application of the dosa fermentation process<br />

to indica-type rice use<br />

Dosa is a spongy pancake that has a desirable flavor, texture,<br />

and sourness. The Japanese are receptive to the characteristics<br />

of dosa. A new food product is expected to have a desirable<br />

flavor, texture, and function through fermentation. We examined<br />

the lactobacillus identification and physical-biochemical<br />

parameters of dosa and tofu-by-product-additive dosa batter.<br />

Dosa and tofu-by-product-additive dosa were measured using<br />

the creep compliance test, and antioxidant activity was measured<br />

by the DHHP method. The fermentation characteristics<br />

and texture of tofu-by-product-additive dosa (additive ratio<br />

less than 60%) were similar to those of dosa produced by conventional<br />

fermentation. Tofu-by-product-additive dosa had<br />

improved antioxidant activity, although the tofu-by-productadditive<br />

ratio was more than 60%, yielding a poor texture<br />

(Shimizu et al 2003).<br />

The finishing system<br />

Facility for manufacturing prewashed rice<br />

A new manufacturing facility aims to polish conventional milled<br />

rice to a condition good enough to be cooked without prior<br />

washing. Today, facilities for manufacturing prewashed rice<br />

can be broken down broadly into three types: (1) a dry-polishing<br />

and finishing system, (2) a wet-milling and finishing system,<br />

and (3) a special processing and finishing system. Facilities<br />

of all these types finish the milled rice to a prewash rice<br />

state by removing the surface portion of rice by 1–2% by weight<br />

of the rice. These facilities are designed to process japonica<br />

rice.<br />

The dry-polishing and finishing system<br />

Kapika and Rifure are major ones of this type. Kapika has a<br />

long roller, 1.7 times longer than the roller of an ordinary friction<br />

rice-milling machine, with three extrusions on the mixing<br />

roller. The screen has a dodecagon shape. The milled rice flows<br />

downward from the top of the machine and rice grains are<br />

milled by grain-to-grain friction. The machine comes in four<br />

models, with capacities of 0.3, 1, 1.8, and 3 t h –1 .<br />

Rifure was developed by converting a rice-milling machine<br />

into a dry-polishing machine. The machine has brush<br />

knives, on which are plated fine nylon fiber 0.275 mm across,<br />

containing 800-mesh carbon silicate particles at 15% weight.<br />

<strong>Rice</strong> is fed into the lower portion of the machine and is pushed<br />

upward to the roller, w<strong>here</strong> rice is polished by the brushes<br />

embedded on the roller. Rifure comes in two capacities, 1 and<br />

1.5 t h –1 , the former in two lines and the latter in three lines.<br />

The wet-milling and finishing system<br />

The Super jiff rice (SJR) consists of two stages of processing,<br />

the first being wet-milled and the second being finishing. The<br />

milled rice is fed from the top of the wet-milling section, or<br />

the first stage, and rice flows downward to the milling roller,<br />

w<strong>here</strong> the rice is wet-milled. The retention time of the rice in<br />

the first stage is about 3 seconds. Water is added at about 50%<br />

by weight to the feed rice, and heated to 20 to 30 °C by the<br />

heat exchanger on the water tank. Subsequently, rice undergoes<br />

dehydration by centrifugation, and then is fed into the<br />

finishing process, w<strong>here</strong> the rice is finished by air heated to<br />

about 45 °C. The water discharged from the wet-milling section<br />

is sent to a dryer, w<strong>here</strong> water is evaporated by the heated<br />

air from the boiler, which then leaves flakes of suspended solids.<br />

The special processing and finishing system<br />

The Neo Tasty White Process (NTWP), a new special processing<br />

and finishing system, has been adopted by large rice<br />

milling plants since 2000. This system consists of three sections:<br />

the moist pressurized milling section, the heated adhesion<br />

low-pressure mixing section, and the drying and separation<br />

system. The moist pressurized milling section mixes the<br />

grain after adding water at a rate of 5% of the milled rice. The<br />

retention time of milled rice in this section is about 10 seconds.<br />

The subsequent secondary process in the heated adhesion<br />

low-pressure mixing section adds tapioca starch, heated<br />

to about 85 °C, to the grain at a rate of 50% of the milled rice.<br />

Here, tapioca starch acts as a heated adhesive agent. The tapioca<br />

starch removes the remaining bran layer from the milled<br />

rice while being mixed with the latter. The retention time of<br />

the milled rice in this section is about 10 seconds. The tertiary<br />

process separates the tapioca starch agent from the bran by the<br />

bag filter and the separator installed separately, and tapioca<br />

starch is recycled back to the system after being heated by a<br />

boiler.<br />

Overview of rice milling and processing in the Philippines<br />

The following factors have been highlighted by many reports<br />

as the main causes of loss through the various stages from harvest<br />

to consumption.<br />

1. Characteristics of the rice variety. High-yielding varieties,<br />

especially IR64, are the main rice crop these<br />

days. These varieties are characterized by a high shattering<br />

loss because of the delayed harvesting and<br />

threshing time.<br />

300 <strong>Rice</strong> is life: scientific perspectives for the 21st century


2. Equipment and facilities. The use of machinery is still<br />

very limited at all stages. The lack of dryers among<br />

farmers especially causes a considerable loss of paddy.<br />

3. Unsuitable milling equipment. This is the cause of<br />

low yield among custom mills in rural villages.<br />

4. Inadequate facility management. Poor management<br />

of small and medium storage facilities in particular<br />

results in a considerable loss to vermin and spoilage<br />

by microorganisms.<br />

5. Socioeconomic factors. Poor roads, including farm<br />

roads, cause losses during handling and transportation<br />

(Yoshizaki 2002).<br />

Table 1 shows the level of postproduction losses in the<br />

Philippines. A postproduction assessment was conducted by<br />

NAPHIRE (present-day BPRE) in 1994-95 with the cooperation<br />

of 13 universities using a common survey methodology.<br />

The total loss (percentage) is t<strong>here</strong>fore considered to be higher<br />

than these numbers indicate.<br />

References<br />

Shimizu N, Seimiya H, Toyoki A, Kimura T. 2003. Application of<br />

the dosa fermentation process to tofu-byproduct utilization in<br />

food industry. 5th <strong>International</strong> Food Convention, 5-8 December<br />

2003. Mysore (India): Central Food Technological<br />

<strong>Research</strong> <strong>Institute</strong>. p 50-51.<br />

Yoshizaki S. 2002. Report on the local survey on rice distribution<br />

and management in the Philippines. ODA Project for Improving<br />

<strong>Rice</strong> Distribution in Asia. Japan Grain Inspection Association.<br />

p 9-10.<br />

Yoshizawa K, Kishi S. 1985. <strong>Rice</strong> in brewing. In: Juliano BO, editor.<br />

<strong>Rice</strong>: chemistry and technology. St. Paul, Minn. (USA):<br />

American Association of Cereal Chemists, Inc. p 638.<br />

Table 1. Postproduction losses in the Philippines (%).<br />

Process 1994-95 1988 1974<br />

(NAPHIRE) (NAPHIRE) (<strong>IRRI</strong>)<br />

Harvesting Trace–4.85 (1.81) a Trace–4.8 1–3<br />

Piling Trace–1.77 (0.54) Trace–1.0 2–7<br />

Threshing and winnowing 0.04–5.09 (2.17) 0.1–5.4 2–6<br />

Drying 0.74–8.70 (4.50) Trace–0.7 1–5<br />

Storage 0.35–5.20 (2.72) 2.6–5.0 2–6<br />

Milling 0.00–6.33 (3.10) 6.3–8.3 2–10<br />

Total loss 1.13–31.94 9.1–23.0 10–37<br />

Average 14.84 16 23.5<br />

a Numbers in parentheses show the average.<br />

Notes<br />

Authors’ addresses: Naoto Shimizu and Toshinori Kimura, Graduate<br />

School of Life and Environmental Sciences, University of<br />

Tsukuba, Tennodai 1-1-1, Tsukuba 305-8572, Ibaraki-ken,<br />

Japan; Yuji Katsuragi, Japan <strong>Rice</strong> Millers Association,<br />

Kojimachi 3-3-6, Chiyoda-ku 102-0083, Tokyo, Japan, e-mail:<br />

shimizu@sakura.cc.tsukuba.ac.jp.<br />

Acknowledgments: We express our gratitude to the Ministry of Agriculture,<br />

Forestry, and Fisheries, Japanese Grain Inspection<br />

Association, and KOKKEN. Especially, the overview of rice<br />

milling and processing in the Philippines is a result of the<br />

ODA project on “Improving <strong>Rice</strong> Distribution in Asia.”<br />

Advanced application technology of rice bran:<br />

preparation of ferulic acid and its applications<br />

Hisaji Taniguchi, Eisaku Nomura, and Asao Hosoda<br />

The production of brown rice in the world is about 560 million<br />

tons a year. Japan produced about ten million tons. Brown<br />

rice is usually polished before eating, and 10% of its weight is<br />

discharged as rice bran. Thus, 1 million tons of rice bran are<br />

discharged in Japan. About 40% of the rice bran is used to<br />

produce rice edible oil in Japan, by extraction. In the course of<br />

production of rice edible oil, rice bran pitch is discharged. This<br />

is a dark and viscous oil and it is a waste material. We prepared<br />

ferulic acid from rice bran pitch (Taniguchi et al 1994).<br />

Ferulic acid was produced from petroleum before. Petroleum,<br />

however, is predicted to be used up in the future, after about<br />

40 years. So far, the cost of ferulic acid has been about<br />

US$2,500 per kg. No one could use this as a chemical material<br />

because of its expensiveness. In the method we have developed,<br />

the cost of ferulic acid is about $100 per kg. Thus,<br />

ferulic acid has become a very important chemical material.<br />

The carbon resource of ferulic acid is carbon dioxide in the<br />

air. Further, ferulic acid will be obtained forever as long as<br />

humankind keeps on producing rice. T<strong>here</strong>fore, ferulic acid<br />

can become a renewable resource of the future chemical industry.<br />

This development is an environmentally friendly one.<br />

Figure 1 illustrates the concept of renewable resource usage<br />

with a system flowchart of the organic chemical industry using<br />

ferulic acid obtained from rice bran.<br />

Preparation of ferulic acid<br />

Ferulic acid and rice bran pitch<br />

It is well known that ferulic acid can be prepared by the condensation<br />

reaction of vanillin with malonic acid (Adams 1942).<br />

Session 10: Postharvest technology for efficient processing and distribution of rice 301


Sun<br />

Renewable resource<br />

Light<br />

<strong>Rice</strong> plant Brown rice <strong>Rice</strong> bran <strong>Rice</strong> salad oil<br />

Synthetic methods<br />

— Organic chemistry<br />

— Biochemistry<br />

Evaluation studies<br />

Cancer prevention<br />

Antioxidant activity<br />

<strong>Rice</strong> bran pitch<br />

CO 2 ,<br />

water<br />

Ferulic acid<br />

Preparation of new<br />

compounds<br />

Ferulic acid is a starting<br />

material<br />

Compounds<br />

to maintain health<br />

Fossil resource<br />

(Petroleum-coal)<br />

Consumers<br />

Organic chemical industry<br />

Public demand<br />

Ecorecycle<br />

CO 2 , water<br />

Fig. 1. A system flowchart for the organic chemical industry using ferulic acid obtained from rice bran.<br />

This produces ferulic acid at a high yield, but takes as long as<br />

3 weeks. In addition, the product is a mixture of trans- and<br />

cis-isomers. A vigorous search has t<strong>here</strong>fore been made for a<br />

commercial method for manufacturing high-purity trans-ferulic<br />

acid.<br />

In the manufacture of rice edible oil, a blackish brown<br />

waste oil having a high viscosity, called rice bran pitch, an<br />

alkaline oil cake rich in oil components, called soap stock,<br />

and a by-product rich in crude fatty acids, called dark oil, are<br />

discharged. These waste materials are known to contain useful<br />

components but they have generally been disposed of as useless<br />

industrial by-products, for example, by burning, because<br />

of the lack of techniques for effective use.<br />

We have investigated the components of rice bran pitch<br />

and found by chromatography that about 30% by weight is γ-<br />

oryzanol itself. Because other components are contained in<br />

large amounts, it is very difficult to recover γ-oryzanol alone,<br />

leading to a high manufacturing cost. Thus, it is economically<br />

not feasible to recover γ-oryzanol from rice bran pitch. However,<br />

hydrolysis under certain conditions must make it possible<br />

for us to produce ferulic acid, as illustrated in Figure 2.<br />

Yet, because γ-oryzanol was included within various oil<br />

components of rice bran pitch, hydrolysis under usual conditions<br />

did not proceed at all. It should be noted that rice bran<br />

pitch is quite immiscible with water so that a suitable alcohol<br />

must be applied as a solvent. With a simple alcohol having a<br />

small number of carbon atoms, which can be infinitely dissolved<br />

in water, the alkaline compound and rice bran pitch can<br />

also be dissolved without difficulty.<br />

In our procedure, hydrolysis was carried out at 90–<br />

100 °C for 8 hours under an atmospheric pressure, resulting in<br />

crude ferulic acid with a purity of about 70–90%. The crude<br />

ferulic acid was purified by the recrystallization from a cosolvent<br />

of ethyl alcohol and water. Ferulic acid was obtained<br />

in a 100% yield based on γ-oryzanol that existed in rice bran<br />

pitch (Taniguchi et al 1999).<br />

EGMP and ferulic acid, which act as anticarcinogens<br />

The synthesis of EGMP<br />

It is known that many kinds of chemopreventive agents are<br />

present in a diverse range of edible plants and herbs. It is difficult,<br />

however, to isolate or extract chemically pure substances<br />

from plants because these substances are present in very small<br />

amounts in plants.<br />

However, ferulic acid can now be obtained easily in a<br />

large amount from rice bran. This development prompted us<br />

to synthesize potential cancer chemopreventive agents. On<br />

searching for an appropriate target compound that should be<br />

synthesized by the reaction of ferulic acid with other reagents,<br />

we found that aurapten, a citrus coumarin, is an excellent cancer<br />

chemopreventive agent. Recently, Koshimizu et al (1997)<br />

have isolated aurapten from citrus natudaidai (natsumikan in<br />

Japanese) and showed that aurapten inhibited 12-Otetradecanoylphorbol-13-acetate<br />

(TPA)-induced skin tumor<br />

promotion in mice.<br />

Aurapten consists of 7-hydroxycoumarin and a geranyl<br />

group. 7-hydroxycoumarin has one phenolic hydroxyl group,<br />

one carbon-carbon double bond, and one carbonyl group in its<br />

molecule. Ferulic acid also has these functional groups in its<br />

molecule. T<strong>here</strong>fore, we synthesized many compounds in which<br />

ethyl 3-(4-geranyloxy-3-methoxyphenyl)-2-propenpate<br />

(EGMP) was contained, resembling the chemical structure of<br />

aurapten using ferulic acid. Especially, for EGMP, the geranyl<br />

group is attached to the phenolic hydroxyl group of ethyl<br />

ferulate.<br />

302 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Extraction<br />

<strong>Rice</strong> edible oil<br />

Brown rice<br />

<strong>Rice</strong> bran<br />

<strong>Rice</strong> bran pitch<br />

COOH<br />

HO<br />

H 3 CO<br />

COO<br />

Ca. 30%<br />

MOH<br />

ROH<br />

OH<br />

OCH 3<br />

γ-oryzanol<br />

Ferulic acid<br />

Fig. 2. Preparation of ferulic acid.<br />

Anticolon carcinogenesis of ferulic acid and EGMP<br />

Among compounds we synthesized, ferulic acid itself and<br />

EGMP showed anticarcinogenesis. The anticarcinogenesis of<br />

these compounds has been studied by Tsuda et al (1999).<br />

The inhibitory influence of ferulic acid and EGMP on<br />

the postinitiation stage of azoxymethane (AOM)-induced colon<br />

carcinogenesis was investigated in male F344 rats given<br />

two s.c. injections of AOM (15 mg kg –1 body weight) during<br />

week 1. Diets containing ferulic acid or EGMP at doses of<br />

0.1% or 0.2% were then fed for 3 weeks from weeks 2 to 5,<br />

when the animals were sacrificed. The numbers of aberrant<br />

crypt foci (ACF) and aberrant crypts (AC) per rat in the group<br />

given 0.2% ferulic acid decreased significantly (P


is an excellent UV absorbent, it is not stable at high temperatures.<br />

Thus, we have developed a facile preparation method of<br />

the ferulic acid dimer, that is, bis-4,4′-(2-ethoxycarbonyl-1-<br />

ethenyl)-2,2′-methoxyphenoxymethane, which can become a<br />

better UV absorbent than available UV absorbents such as<br />

benzophenone and salicylic acid. The compound absorbs light<br />

at about 260–370 nm and exhibits two absorption maxima<br />

(λ max ) at 321 nm (ε max : 3.28 × 10 4 ) and 292 nm (ε max : 3.21 ×<br />

10 4 ). The decomposition temperature is 359 °C. This temperature<br />

is far higher than that of ferulic acid, which decomposes<br />

a<br />

t<br />

176 °C. Based on these results, the compound is able to become<br />

a thermally stable absorbent of UV light for plastics.<br />

Other applications<br />

Ferulic acid is used as the starting material for the preparation<br />

of reagents having antibacterial activity, fragrances, food additives,<br />

control of germination, and cosmetics (Taniguchi at al<br />

2003).<br />

References<br />

Nomura E, Kashiwada A, Hosoda A, Nakamura K, Morishita H,<br />

Tsuno T, Taniguchi H. 2003. Synthesis of amide compounds<br />

of ferulic acid, and their stimulatory effects on insulin secretion<br />

in vitro. Bioorg. Med. Chem. 11:3807-3813.<br />

Taniguchi H, Hosoda A, Tsuno T, Maruta Y, Nomua E. 1999. Preparation<br />

of ferulic acid and its application for the synthesis of<br />

cancer chemopreventive agents. Anticancer Res. 19:3757-<br />

3762.<br />

Taniguchi H, Nomura E, Hosoda A. 2003. Useful application of ferulic<br />

acid produced from rice bran. Yukigouseikagakukyoukaishi<br />

61:310-321.<br />

Taniguchi H, Nomura E, Tsuno T, Mimami S, Kato K, Hayashi C.<br />

1994. Method of manufacturing ferulic acid. US Patent No.<br />

5,288,902. Japanese Patent No. 2095088.<br />

Tsuda H, Park CE, Takasuka N, Baba-Toriyama H, Sekine K, Moore<br />

MA, Nomura E, Taniguchi H. 1999. Influence of ethyl 3-(4-<br />

geranyloxy-3-methoxyphenyl)-2-propenpate (EGMP) on early<br />

stage colon cacinogenesis in rats treated with azoxymethane<br />

(AOM). Anticancer Res. 19:3779-3782.<br />

Tsuno T, Maruta Y, Hosoda A, Nomura E, Taniguchi H. 2001. Preparation<br />

of a novel thermally stable UV absorbent from natural<br />

resources. ITE Letters on Batteries, New Technologies &<br />

Medicine 2C6:808-811.<br />

Notes<br />

New movements regarding the safety of rice<br />

and residual agrochemical inspection<br />

Yukio Hosaka<br />

Authors’ address: Industrial Technology Center of Wakayama Prefecture,<br />

60 Ogura, Wakayama 649-6261, Japan, e-<br />

mail:taniguti@wakayama-kg.go.jp.<br />

Recently, t<strong>here</strong> have been new movements in the Japanese rice<br />

market to inspect residual agrochemicals before harvesting,<br />

that is, the crops are checked for residual agrochemicals for<br />

each farm or each harvesting lot. If agrochemicals are not detected,<br />

the crop will be harvested and sent to a large-scale drying<br />

facility, but, when agrochemicals are detected, harvesting<br />

will be postponed until the sun and rain dissolve the chemicals,<br />

and the crop will be harvested later, after another residual<br />

agrochemical inspection.<br />

The reason for this preharvest inspection is that, when<br />

crops are sent to a large-scale drying facility, they are mixed<br />

with other crops within a storage silo. If a part of the crop has<br />

residual agrochemicals, the whole grains will be contaminated<br />

by the agrochemicals and it will be impossible to separate sound<br />

grains and contaminated grains afterward.<br />

Raw paddy is collected from standing plants and threshed<br />

by simple threshing equipment to make a 130-g sample, and<br />

then taken to a large-scale drying facility to be processed with<br />

a test dryer and test husker to make brown rice, 25 g of which<br />

are used for checking residual agrochemicals. This method was<br />

introduced to all of Fukuoka Prefecture in Japan starting in<br />

2004, under the guidelines of JA Central Fukuoka.<br />

Background of the new movements<br />

I will explain the background of these new movements. For<br />

each agrochemical, the maximum permissible level is determined<br />

by a law, which is set based on studies of the medical<br />

effect of agrochemicals on the human body. However, in the<br />

market, it is not so simple to judge that residual agrochemicals<br />

under the standard are acceptable and that residual agrochemicals<br />

over the standard are not.<br />

Suppose that t<strong>here</strong> are two rice products, one of which<br />

is almost certain not to exceed the legal level of residual agrochemicals<br />

from past experience and the way of cultivation but<br />

not confirmed with measuring equipment, and the other is<br />

checked for confirmation. Which rice will customers buy if<br />

other commercial factors such as price, taste, and appearance<br />

are the same At least, in a culturally mature society, the latter<br />

will be chosen. Or, suppose two samples are checked by an<br />

304 <strong>Rice</strong> is life: scientific perspectives for the 21st century


ACA2000 analyzing flow<br />

Activate toxicity<br />

of enzyme<br />

Add enzyme<br />

Preprocessing<br />

2–3 hours<br />

ChE<br />

Grind Shake Filter Column Evaporate<br />

chromatography<br />

Dissolve<br />

Measurement<br />

Acetylcholine<br />

Add substrate<br />

15 min<br />

Measuring principal enzyme inhibition method<br />

H 2 O<br />

ChE<br />

Agrochemical<br />

2H 2 O<br />

(Oxidant)<br />

POD<br />

(Reductant)<br />

M<br />

(Red.)<br />

e –<br />

Current detection<br />

Choline ChOD H 2 O 2<br />

H 2 O + O 2<br />

Fig. 1. Measuring procedures.<br />

POD<br />

(Red.)<br />

M<br />

(Ox.)<br />

M: electron-transfer<br />

Electrode mediator<br />

POD: peroxidase<br />

agrochemical inspector, one of which has near but under the<br />

regulatory level of residual agrochemical, and the other contains<br />

no residual agrochemicals. As before, if other factors are<br />

the same, the latter rice will be chosen. Even when the level of<br />

residual agrochemicals is under the standard, the product’s<br />

value still differs widely in human society because of actually<br />

checking the residues or confirming whether the level of residue<br />

is near the standard or almost zero. T<strong>here</strong>fore, the issue of<br />

residual agrochemical in the recent market is not that of a legal<br />

or a medical problem, but more of a cultural or human<br />

nature matter.<br />

In recent rice trading in the market, this cultural or human<br />

nature aspect is claimed in competitions. This is clear<br />

because agrochemical-free production is promoted in the market.<br />

Another reason that rice producers are becoming sensitive<br />

to residual agrochemicals is that, if their rice products are<br />

found to contain residues over the standard, because of the<br />

abovementioned cultural and human nature aspects, the brand<br />

name could suffer critical damage through news reports.<br />

The new movements regarding residual agrochemical inspection<br />

started from this background, and are attempting to<br />

achieve a higher level of residue-free rice production.<br />

A new residual agrochemical detector to study the trend<br />

Because of this new trend, we need to check residual agrochemicals<br />

for each farm or harvesting lot in a short period of<br />

time; thus, a large number of agrochemical detectors must be<br />

placed among rice-producing areas. T<strong>here</strong>fore, a low-cost detecting<br />

system is indispensable.<br />

Moreover, it is also requested that the system be able to<br />

process a large amount of samples in a short period of time,<br />

and that it produce test results rapidly, since the test is conducted<br />

right before harvesting.<br />

Also, the system must be able to check not only that residues<br />

are under the regulatory level, but it must have a high<br />

sensitivity to confirm that residual agrochemicals do not really<br />

exist. To meet these demands, we have developed a measuring<br />

system using the enzyme inhibition method.<br />

Many agrochemicals have the effect of inhibiting the<br />

neural transmission of insects, so this system measures the<br />

degree to which the components of agrochemicals inhibit cholinesterase,<br />

an important factor for neural transmission function.<br />

Acetylcholinesterase (ACHE) is known as a hydrolytic<br />

enzyme of excitatory neurotransmitter acetylcholine that exists<br />

widely from invertebrates to Pisces and mammals, and<br />

activity is inhibited by organophosphorus compounds and carbamate<br />

compounds.<br />

Figure 1 shows the measuring procedures. First is a preprocessing<br />

to collect the possibly contained residual agrochemicals,<br />

and then the toxicity of agrochemicals to the enzyme is<br />

activated before adding the enzyme cholinesterase. After adding<br />

the enzyme, acetylcholine is added as a substrate. This<br />

acetylcholine is transformed to choline by the effect of cholinesterase.<br />

The amount of the generated choline is measured<br />

by transforming the choline into hydrogen peroxide and check-<br />

Session 10: Postharvest technology for efficient processing and distribution of rice 305


Measuring principle<br />

A method to measure the amount of agrochemicals from the enzyme inactivities by<br />

agrochemicals = enzyme inhibition method<br />

Reference<br />

Current/nA<br />

300<br />

250<br />

The generation of H 2 O 2 is fast since<br />

cholinesterase is intact<br />

Rapid increase of electric current<br />

Without agrochemical<br />

H 2 O 2<br />

Acetylcholine<br />

ChE<br />

Acetylcholine<br />

Choline<br />

ChE Agrochemical<br />

ChOD<br />

Choline<br />

200<br />

V R<br />

H 2 O 2<br />

ChOD<br />

150<br />

V S<br />

Sample<br />

100<br />

The generation of H 2 O 2 is slow since<br />

cholinesterase is affected<br />

Slow increase of electric current<br />

50<br />

With agrochemical<br />

0<br />

2 3 4 5 6 7 8<br />

Time (min)<br />

Fig. 2. The measuring principle.<br />

ing by a hydrogen peroxide sensor. The resulting output is in<br />

the form of an electrical current. During this process, the<br />

amount of generated choline is influenced by the inhibition of<br />

the activity of cholinesterase by agrochemicals, which in turn<br />

affect the amount of hydrogen peroxide and change the electrical<br />

current. The amount of electrical current is determined<br />

by the degree to which residual agrochemicals inhibit the effect<br />

of cholinesterase. T<strong>here</strong>fore, the electrical current is affected<br />

by the amount of agrochemicals, so the residual agrochemicals<br />

can be measured by using a hydrogen peroxide sensor.<br />

To be more specific, as shown in Figure 2, if t<strong>here</strong> are<br />

no agrochemicals, the generation of hydrogen peroxide is fast,<br />

so the increase in electrical current is faster. On the other hand,<br />

if t<strong>here</strong> are residual agrochemicals, the generation of hydrogen<br />

peroxide is slow, thus the increase in electrical current is<br />

slower. T<strong>here</strong>fore, the amount of residual agrochemicals can<br />

be measured by the differential V R or V S . This method cannot<br />

specify the type of agrochemical component, but it can detect<br />

the agrochemicals that inhibit the cholinesterase as a whole.<br />

In the case of DDVP (dichlorovinyl dimethyl phosphate),<br />

which is an organophosphorus insecticide, sensitivity is high<br />

enough compared with the legal standard.<br />

T<strong>here</strong>fore, this method can be considered as a high-accuracy<br />

screening method. According to data of several years<br />

ago, residual agrochemicals are actually detected in one out of<br />

300 samples in Japan, but they contain only a minute amount<br />

of agrochemicals and the residues barely exceed the legal standard.<br />

In the conventional legal method, all 300 samples must<br />

be checked by liquid chromatography and mass spectrometer,<br />

etc. However, this legal method is high in cost and the measuring<br />

efficiency, the number of samples that can be checked per<br />

day, is low. What if screening tests are done by using our simple,<br />

inexpensive, high-efficiency and low-measuring-cost method,<br />

and the legal method is performed only on the samples that are<br />

picked up by this screening test If the legal method detects<br />

one out of 300 samples, our high-accuracy screening will detect<br />

about two samples that contain residual agrochemicals.<br />

T<strong>here</strong>fore, while the conventional method needed the inefficient<br />

legal method to be performed on all 300 samples, this<br />

high-accuracy screening allows you to use the legal method<br />

on only two samples. The measuring efficiency and the cost<br />

for measuring residual agrochemicals are significantly improved<br />

in this total system with the new technology and legal<br />

method combined.<br />

The idea of screening before the legal method is not new;<br />

however, the point is how far you can reduce the number of<br />

samples using the screening method. If the degree of narrowing<br />

down by a screening is small, and the dependence on the<br />

legal method is still high, the screening will make the measurement<br />

inefficient. However, because of its high measuring<br />

sensitivity, our new screening method can significantly reduce<br />

the number of samples to be checked by the legal method, and<br />

can well be called a high-accuracy screening method.<br />

The theory of agrochemical measurement by the enzyme<br />

inhibition method existed from before, although this may be<br />

the first practical system that allows for a high-accuracy measurement.<br />

306 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Furthermore, our newly developed system can be called<br />

an expanded enzyme inhibition method, which means that it<br />

uses not only the traditional cholinesterase inhibition theory,<br />

but also tries to apply a new principle of transforming the agrochemical<br />

component that originally did not inhibit enzyme<br />

activity to inhibit the enzyme, and widens the variety of agrochemicals<br />

that can be measured. Because of the development<br />

based on this new principle, some of the agrochemicals that<br />

could not be detected by conventional methods now can be<br />

detected by the system, and, furthermore, not only insecticides<br />

but a part of the bactericides can also be measured. We will<br />

make further progress in this area, while also considering the<br />

use of other enzymes.<br />

Notes<br />

Author’s address: e-mail: y-hosaka@satake-japan.co.jp.<br />

Impact of infrastructure on profitability and global<br />

competitiveness of rice production in the Philippines<br />

Rowena G. Manalili and Leonardo A. Gonzales<br />

One of the constraints to the growth of Philippine rice production<br />

is the lack of appropriate and adequate infrastructure. This<br />

includes marketing and distribution infrastructure such as farmto-market<br />

roads; limited access to credit, processing, and storage<br />

facilities; and the lack of effective irrigation systems. Several<br />

policy studies had pointed out the importance of these<br />

facilities, but studies that look into the impact of infrastructure<br />

on profitability and global competitiveness are still lacking. It<br />

is t<strong>here</strong>fore important to evaluate and measure the impact of<br />

irrigation and road infrastructure on rice profitability.<br />

Our study evaluated the impact of infrastructure (roads<br />

and irrigation) development on farm productivity, rural income,<br />

technology adoption, and transaction costs in rice farming, and<br />

compared the profitability and global competitiveness of rice<br />

farmers who have access to good infrastructure and those who<br />

do not.<br />

Methodology<br />

The study used the 1996 wet season (WS) and 1997 dry season<br />

(DS) farm-level and barangay-level data of the Regular<br />

Monitoring of <strong>Rice</strong>-Based Farm Household Survey (RBFHS)<br />

project of the Philippine <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>’s (Phil<strong>Rice</strong>)<br />

Socioeconomic Division (SED) and the Bureau of Agricultural<br />

Statistics (BAS). The farm-level data included production<br />

costs and returns and socioeconomic and technological<br />

profiles of 2,500 rice farmers from 281 barangays (villages)<br />

of 30 selected provinces in the Philippines. Sample barangays<br />

were classified according to their state of road infrastructure<br />

development. A barangay with good infrastructure was characterized<br />

by its year-round accessibility owing to asphalt or<br />

concrete roads and sufficient transport facilities. On the other<br />

hand, a barangay with poor road infrastructure was characterized<br />

by a lack of all-weather roads, making it barely accessible,<br />

and having insufficient transportation vehicles.<br />

The methods employed in the analysis were the costs<br />

and returns analyses, competitive advantage analysis using do-<br />

mestic resource cost (DRC), and the seemingly unrelated regression<br />

(SUR) analysis.<br />

The rice-based farm households across ecosystems, seasons,<br />

and infrastructure with yield as the major indicator were<br />

regressed to measure the impact of infrastructure indicators<br />

on total productivity, output prices, input prices, technology<br />

adoption, and net farm income. The models were estimated<br />

using the SUR analysis. The models were as follows:<br />

1. Output = f (production inputs, infra indicators)<br />

2. Output price = f (yield, infra indicators)<br />

3. Input price = f (inputs, infra indicators)<br />

4. Technology adoption = f (inputs, infra indicators)<br />

5. Farm income = f (inputs, infra indicators)<br />

The explanatory variables for the regression model were<br />

the inputs of production that include farm size (ha), seed use<br />

(kg ha –1 ), fertilizers—nitrogen, phosphorus, and potassium (kg<br />

ha –l ), pesticides (active ingredients in kg), and preharvest labor<br />

(person-days), as well as infrastructure indicators such as<br />

road classification, distance and travel time to major wholesale<br />

markets, transport cost of rough rice from farm to major<br />

wholesale market, availability of transportation vehicles, number<br />

of input/output dealers, number of business establishments,<br />

and number of communication facilities.<br />

Results and discussion<br />

Yield and profitability<br />

Irrigated versus nonirrigated farms. Table 1 shows the yield<br />

performance and relative profitability of farmers from irrigated<br />

and nonirrigated environments. Data in both seasons showed<br />

a substantial yield advantage of irrigated over nonirrigated<br />

farms. The average yield for irrigated farms during the WS<br />

was 3.54 t ha –l , w<strong>here</strong>as the yield for nonirrigated rice was<br />

2.55 t ha –l . Similarly, in the DS, yield of irrigated rice farms<br />

averaged 3.66 t ha –l , while yield of nonirrigated farms averaged<br />

2.34 t ha –l , or around a 1 t ha –l (56%) yield difference.<br />

Session 10: Postharvest technology for efficient processing and distribution of rice 307


Table 1. Average costs and returns of rice production in the Philippines, 1996<br />

WS and 1997 DS by agroecological system.<br />

Item Wet season Dry season<br />

Irrigated Nonirrigated Irrigated Nonirrigated<br />

Yield (t ha –1 ) 3.54 2.55 3.66 2.34<br />

Price of paddy ($ t –1 ) 290 290 300 300<br />

Gross returns ($ ha –1 ) 1,027 740 1,098 702<br />

Production costs ($ ha –1 )<br />

Seeds 47 43 47 42<br />

Fertilizer 86 60 75 52<br />

Pesticides a 50 47 48 46<br />

Irrigation fee 35 – 38 –<br />

Transportation 3 3 4 3<br />

Fuel and oil 18 11 20 12<br />

Labor costs 324 328 343 309<br />

Depreciation 23 19 23 18<br />

Land (rental value) 27 14 27 15<br />

Other costs b 38 33 30 25<br />

Total production costs ($ ha –1 ) 651 558 655 522<br />

Net farm income ($ ha –1 ) 375 182 443 180<br />

Net profit-cost ratio 0.58 0.33 0.68 0.35<br />

Cost per ton ($) 184 219 179 223<br />

a Includes herbicides, insecticides, fungicides, molluscicides, and rodenticides. b Includes food costs,<br />

interest expenses, and land tax. Official exchange rate: P26.30 = US$1.<br />

Source: Department of Agriculture-Phil<strong>Rice</strong> <strong>Rice</strong>-Based Farm Household Survey, 1997.<br />

Costs and returns analysis showed that irrigated farms<br />

were more profitable than nonirrigated farms in both seasons.<br />

The higher production cost incurred by irrigated rice farms<br />

was offset by their higher yield gains. Net farm income realized<br />

from irrigated farms was higher at US$375 ha –l for the<br />

WS and $443 ha –l for the DS versus $182 ha –l for the WS and<br />

$180 ha –l for the DS obtained from nonirrigated farms. Moreover,<br />

net profit-to-cost ratios were better for irrigated farms.<br />

Good versus poor infrastructure. Table 2 shows the comparative<br />

productivity and profitability of farmers with access<br />

to good and poor road infrastructure. <strong>Rice</strong> yield of farmers on<br />

irrigated farms with access to good road infrastructure was<br />

higher at 3.61 t ha –l for the WS and 3.77 t ha –l for the DS than<br />

that of farms with poor infrastructure at 3.31 t ha –l for the WS<br />

and 3.24 t ha –l for the DS. Results of the analysis showed that,<br />

except for the nonirrigated farms during the DS, farms with<br />

good infrastructure appeared to be more profitable as indicated<br />

by their higher gross returns, net income, and net profitto-cost<br />

ratios. Net incomes from farms with good road infrastructure<br />

were higher by 14–40% for all seasons.<br />

Competitive advantage analysis<br />

Results of the competitive advantage analysis showed that the<br />

Philippines has no competitive advantage under the export trade<br />

scenario. The country has no competitive advantage in domestically<br />

producing rice for export as indicated by the resource<br />

cost ratios greater than 1. A major reason for this export<br />

noncompetitiveness was the high per unit cost of rice production<br />

shown in the costs and returns analyses.<br />

Under the import trade scenario, t<strong>here</strong> is a competitive<br />

advantage in domestically producing rice only on irrigated<br />

farms. For infrastructure development, farmers with access to<br />

good infrastructure had higher levels of competitive advantage.<br />

Seemingly unrelated regression analysis<br />

Results of the SUR analysis showed that nitrogen fertilizer,<br />

pesticides, and irrigation were positively correlated with yield<br />

and showed a very high level of significance. These indicate<br />

that an increase in one of these explanatory variables will positively<br />

and significantly affect rice yield. Road structure affected<br />

the price of urea fertilizer. Urea fertilizer was more expensive<br />

in areas with poor road conditions owing to higher transportation<br />

costs incurred in the purchase of this input.<br />

Another major finding of the study is that road structure<br />

and vehicle density positively and significantly affected the<br />

quantity of nitrogen fertilizer used in rice production. Farmers<br />

would apply more nitrogen fertilizer to their crops because of<br />

its lower price brought about by lower transaction costs, good<br />

road conditions, and the availability of sufficient transport facilities<br />

in the area.<br />

The major determinants of farm income were the major<br />

inputs of production such as nitrogen fertilizer, pesticides,<br />

preharvest labor, as well as infrastructure indicators such as<br />

irrigation, road structure, and transportation costs.<br />

308 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 2. Average costs and returns of rice production in the Philippines, 1996 WS and 1997<br />

DS by state of infrastructure development.<br />

Wet season<br />

Dry season<br />

Item Irrigated Nonirrigated Irrigated Nonirrigated<br />

Good Poor Good Poor Good Poor Good Poor<br />

Yield (t ha –1 ) 3.61 3.31 2.61 2.39 3.77 3.24 2.26 2.32<br />

Price of output ($ t –1 ) 290 290 290 290 300 300 300 300<br />

Gross returns ($ ha –1 ) 1,047 960 757 693 1,131 972 678 696<br />

Production costs ($ ha –1 )<br />

Seeds 49 42 46 40 48 43 43 38<br />

Fertilizer 87 79 53 52 90 80 58 47<br />

Pesticides a 52 45 48 38 49 43 45 40<br />

Irrigation fee 34 0 – – 37 40 – –<br />

Transportation 3 3 3 3 3 3 3 3<br />

Fuel and oil 18 19 10 13 21 19 10 14<br />

Labor costs 339 353 289 285 346 336 296 297<br />

Depreciation 24 24 20 17 24 23 17 17<br />

Land (rental value) 27 27 14 14 27 27 15 15<br />

Other costs b 38 35 32 27 34 34 28 23<br />

Total production costs ($ ha –1 ) 670 629 515 490 679 648 514 493<br />

Net farm income ($ ha –1 ) 377 331 242 203 452 324 164 203<br />

Net profit-cost ratio 0.56 0.53 0.47 0.41 0.67 0.50 0.32 0.41<br />

Cost per metric ton ($ t –1 ) 186 190 197 205 180 200 227 213<br />

a<br />

Includes herbicides, insecticides, fungicides, molluscicides, and rodenticides. b Includes food costs, interest expenses,<br />

and land tax.<br />

Source: Department of Agriculture-Phil<strong>Rice</strong> <strong>Rice</strong>-Based Farm Household Survey, 1997.<br />

Policy implications<br />

Results of the study generally imply that good infrastructure<br />

improves farm profitability and productivity. T<strong>here</strong>fore, t<strong>here</strong><br />

is a need to evolve an infrastructure development strategy in<br />

irrigation and farm-to-market roads for the rice sector.<br />

Public investment policy for irrigation<br />

Irrigation increases the cropping intensity of farmers. The<br />

Department of Agriculture (DA) should fast-track the construction<br />

of additional irrigation systems because of their high interaction<br />

effect in terms of efficiency in the use of water and<br />

other inputs such as fertilizer and seeds to sustain productivity<br />

and reduce risks in the rice sector. Irrigation also provides a<br />

safety net from distortion caused by natural agro-climatic phenomena<br />

such as drought, as indicated by the higher net farm<br />

income of farmers in irrigated areas.<br />

Public investment policy for farm-to-market roads<br />

Inadequate farm-to-market roads generally increase the transaction<br />

costs of inputs and outputs. According to Gonzales<br />

(2000a,b), inadequate infrastructure in marketing and distribution<br />

accounts for 35–40% of the total costs of production<br />

from the farm to the wholesale market in the grain sector. It<br />

also restricts the adoption of technology because of the relatively<br />

higher cost on-farm of yield-shifter inputs such as fertil-<br />

izer and certified seeds. The restriction in the use of these yieldenhancing<br />

inputs results in lower farm productivity and consequently<br />

lowers farm income.<br />

The dismal condition of rural roads has been cited as the<br />

major reason (1) traders are able to dictate farm-gate prices,<br />

(2) transportation costs are exorbitant, and (3) agricultural<br />

growth did not lead to growth of the nonagricultural sector as<br />

it did in the newly industrializing economies (AGRICOM<br />

1997). Given the long gestation period in investment in public<br />

infrastructure, strategic alliances among agricultural stakeholders<br />

should always advocate the inclusion of public infrastructure<br />

investment in the budgetary process.<br />

The open trade regime in agricultural products has made<br />

the Philippines vulnerable to globalization. Given the state of<br />

noncompetitiveness of the rice sector, t<strong>here</strong> is a need to focus<br />

on key result areas, some of which are proposed by Gonzales<br />

(2000a,b), following the agribusiness framework to cushion<br />

the impact of globalization.<br />

Accelerate farmers’ access to good-quality seeds<br />

Results of this study showed that only a very small percentage<br />

of Philippine rice farmers use good-quality seeds. Since goodquality<br />

seeds enhance yield by 10–15% over ordinary seeds,<br />

full adoption of good-quality seeds can partly enhance productivity<br />

in the rice sector.<br />

Session 10: Postharvest technology for efficient processing and distribution of rice 309


Improvements in postharvest facilities<br />

Postharvest losses account for a substantial portion in the production-distribution<br />

chain and should t<strong>here</strong>fore be minimized,<br />

if not totally eradicated, to enhance productivity.<br />

Promote a higher rate of fertilizer use<br />

The complementarity of fertilizer use, availability of irrigation<br />

water, and adoption of high-yielding varieties should be<br />

considered in promoting higher rates of fertilizer use. Provision<br />

of other services such as credit and marketing services as<br />

well as improvement in infrastructure such as irrigation and<br />

transportation will encourage farmers to apply the right amount<br />

of fertilizer.<br />

References<br />

AGRICOM (Congressional Commission on Agricultural Modernization).<br />

1997. Modernizing agriculture. Manila (Philippines):<br />

Congress of the Philippines.<br />

Gonzales LA. 2000a. Philippine agriculture in the next millennium:<br />

some strategic issues and directions. Proceedings of the Aventis<br />

Launch Conference, 4 February 2000, Makati City, Philippines.<br />

Gonzales LA. 2000b. The Philippine rice industry: strategic issues<br />

and directions. STRIVE Foundation, Putho, Tuntungin, Los<br />

Baños, Laguna, Philippines.<br />

Notes<br />

Authors’ addresses: Rowena G. Manalili, Philippine <strong>Rice</strong> <strong>Research</strong><br />

<strong>Institute</strong>, Maligaya, Science City of Muñoz, 3119 Nueva Ecija,<br />

Philippines, e-mail: rgmanalili@philrice.gov.ph; Leonardo A.<br />

Gonzales, SIKAP/STRIVE Foundation, One Tepeyac Place,<br />

Gov. San Luis Road, Putho, Tuntungin, Los Baños, Laguna,<br />

Philippines, e-mail: lag@strivefoundation.com.<br />

Development of an on-farm rice storage technique<br />

using fresh chilly air and preservation of high-quality rice<br />

Shuso Kawamura, Kazuhiro Takekura, and Kazuhiko Itoh<br />

T<strong>here</strong> are two commercial brown-rice storage systems in Japan:<br />

an environment-temperature storage system, in which the<br />

temperature during storage is not controlled, and a low-temperature<br />

storage system, in which the temperature is maintained<br />

below 15 °C during storage. The low-temperature storage system<br />

minimizes insect activities and mold growth, and fumigants<br />

are t<strong>here</strong>fore not required during storage. However, this<br />

system requires electricity to cool the stored brown rice.<br />

A previous basic study (Kawamura et al 1997) revealed<br />

that the quality of rice stored at a temperature below ice point<br />

is comparable with that of newly harvested rice. Kawamura et<br />

al (2004) reported that rice with moisture content of less than<br />

17.8% does not freeze at a temperature of –80 °C and that a<br />

temperature below ice point minimizes the physiological activities<br />

in rice and hence minimizes the deterioration of rice<br />

quality. <strong>Rice</strong> storage at a temperature below ice point was<br />

named “super-low-temperature storage” by Kawamura because<br />

the storage temperature was much lower than that of low-temperature<br />

storage.<br />

Based on the results of the studies mentioned above, we<br />

conducted an on-farm experiment to develop a new rice storage<br />

technique using ambient fresh chilly air in winter and to<br />

preserve the quality of rice.<br />

Materials and methods<br />

Storage structure<br />

Two of 12 silos of a grain elevator constructed in Hokkaido,<br />

Japan, were used for the on-farm experiment. Each silo had a<br />

diameter of 7.4 m and a height of 23.2 m. Each silo was made<br />

of steel with a 75-mm insulation layer on the outside of the<br />

wall. An automatic system was installed for aeration from the<br />

bottom through to the top of the silo, and an automatic system<br />

was installed for ventilation in the upper vacant space of the<br />

silo.<br />

<strong>Rice</strong> samples<br />

Kirara397 and Hoshinoyume varieties were used for the storage<br />

experiment. The moisture content of each rough rice sample<br />

was 15.4%.<br />

Storage conditions<br />

Five hundred tons of Kirara397 rough rice was stored in one<br />

silo and 494 t of Hoshinoyume rough rice was stored in the<br />

other silo. The storage period was from the end of November<br />

1999 until the end of July 2000. The rough rice in the two silos<br />

was simultaneously aerated in January 2000. Aeration was<br />

automatically carried out when the temperature of the fresh air<br />

was below –7 °C and it was continued until the cooling front<br />

had moved through all of the rough rice in the silos. Total aerating<br />

time (fan time) was 91 h.<br />

310 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Grain temperature (ºC)<br />

30<br />

Mean temperature in parentheses<br />

20<br />

Room-temperature storage (20.2 ºC)<br />

Silo storage<br />

10 cm from silo wall (5.8 ºC)<br />

10<br />

Aeration<br />

Low-temperature<br />

storage (7.6 ºC)<br />

0<br />

Silo storage in<br />

center of silo (1.5 ºC)<br />

Minus 5 ºC storage (–5.0 ºC)<br />

–10<br />

10 Nov 10 Dec 10 Jan 9 Feb 11 Mar 10 Apr 11 May 10 Jun 11 Jul 10 Aug<br />

Period (1999-2000)<br />

Fig. 1. <strong>Rice</strong> grain temperatures during on-farm silo storage and control storage (Kirara397).<br />

Three control storage experiments were also carried out<br />

at the same time: a room-temperature storage, in which rice<br />

samples were stored in a laboratory room; a low-temperature<br />

storage, in which rice samples were stored in a commercial<br />

rice warehouse and kept at a temperature below 15 °C; and a<br />

storage experiment at –5 °C, in which rice samples were stored<br />

in a refrigerator and kept at –5 °C. About 15 kg each of rough<br />

rice and brown rice were stored in polyethylene containers in<br />

each control experiment.<br />

Temperature measurement and sampling<br />

The temperatures of rough rice in the center of the silo and at<br />

10 cm from the silo wall were measured by thermocouples set<br />

at 2.2-m intervals from the bottom to the top of the silo. The<br />

temperatures of rough rice and brown rice in each container in<br />

the control storage experiments were also measured.<br />

<strong>Rice</strong> was sampled and tested for quality before, during,<br />

and after storage. Rough rice samples were taken from the<br />

center of the silo and at four points 15 cm from the silo wall<br />

(north, west, south, and east in the silo) at the end of the storage<br />

period. Sampling depths below the surface of the rough<br />

rice were 0.1, 0.5, 1.0, 2.0, and 4.0 m.<br />

Quality assessment<br />

Moisture content, germination rate, free-fat acidity, and<br />

texturogram property were determined to assess rice quality.<br />

Results and discussion<br />

Grain temperature during storage<br />

The range of grain temperatures in the vertical direction in<br />

each silo was less than 3 °C, and t<strong>here</strong> was no tendency in the<br />

grain temperature distribution. The temperatures recorded in<br />

the center and near the wall of each silo were averaged, and<br />

the average values were used as indicators of changes in grain<br />

temperature during on-farm storage (Fig. 1).<br />

The grain temperature was 10 °C at the beginning of<br />

storage. The temperature of rice grains near the wall gradually<br />

decreased as the ambient temperature fell. The minimum grain<br />

temperature near the wall in the middle of February was<br />

–2 °C. From the end of March until the end of the storage<br />

period (at the end of July), the grain temperature near the wall<br />

gradually increased. The maximum grain temperature near the<br />

wall in the middle of July was 21 °C. The grain temperature in<br />

the center of the silo remained constant (10 °C) at the beginning<br />

of storage and fell to –2 °C when the silo was aerated at<br />

the end of January. The grain temperature in the center of the<br />

silo remained below ice point until the end of July. After aeration,<br />

the grain temperature throughout the silo remained below<br />

ice point until the end of March. These results indicate<br />

that super-low-temperature storage of rice in a farm-scale silo<br />

can be achieved by using aeration and chilly fresh air in winter.<br />

Session 10: Postharvest technology for efficient processing and distribution of rice 311


The thermal conductivity of rough rice (about 0.09 W<br />

m –1 K –1 ) is nearly equal to that of lumber (0.15 W m –1 K –1 )<br />

and glass wool (0.04 W m –1 K –1 ). This means that rough rice<br />

is a thermal insulating material. On the other hand, the specific<br />

heat of rough rice (about 1.7 J K –1 g –1 ) is larger than that<br />

of lumber (1.3 J K –1 g –1 ) and concrete (0.8 J K –1 g –1 ). This<br />

means that rough rice is a refrigerant material. Because of these<br />

physical properties of rough rice, the grain temperature in the<br />

center of the silo remained below ice point until the end of<br />

July despite the increase in outside temperature in summer.<br />

Quality of rice sampled from different parts<br />

of the silo<br />

<strong>Rice</strong> samples were collected from different parts of the silo at<br />

the end of the storage period and were examined for quality.<br />

The germination rates of all samples were more than 97%.<br />

Free-fat acidities of all samples ranged from 12 to 15 mg. A<br />

germination rate of rice grains of more than 90% and free-fat<br />

acidity of rice grains of less than 20 mg mean that t<strong>here</strong> has<br />

been no deterioration in the quality of the rice. The temperature<br />

of rice grains near the silo wall increased to about 20 °C<br />

in July. However, the temperature of rice grains near the wall<br />

was below ice point during winter, and the mean temperature<br />

of rice grains near the silo wall during storage was 5.8 °C (Fig.<br />

1). The results of quality measurements showed that t<strong>here</strong> was<br />

no deterioration in the quality of rice grains near the silo wall.<br />

Quality assessment of rice before and after storage<br />

The germination rates of rice subjected to the silo, –5 °C, and<br />

low-temperature storage were more than 98% after storage, as<br />

high as that of samples taken before storage. On the other hand,<br />

the germination rate of rice subjected to room-temperature storage<br />

decreased to about 50%, indicating that the rice had lost<br />

vitality during room-temperature storage. The free-fat acidities<br />

of rice increased in all of the storage experiments. However,<br />

t<strong>here</strong> were differences in the rates of increase in free-fat<br />

acidity: the rate of increase in rough rice during storage was<br />

less than that of brown rice. Moreover, the rate of increase in<br />

free-fat acidity was highest for rice stored at a room temperature,<br />

next highest for rice stored at a low temperature and in<br />

the silo, and lowest for rice stored at –5 °C. These results indicate<br />

that the decomposition process of fat is slower in rough<br />

rice during storage and in rice during storage at lower temperatures.<br />

Changes in the texture of cooked rice were minimized<br />

by silo storage and –5 °C storage and by storage of<br />

rough rice.<br />

The results of quality assessment indicate that storage<br />

of rice at temperatures below ice point (silo storage and –5 °C<br />

storage in this study), which is called super-low-temperature<br />

storage, preserves the quality of rice at a much higher level<br />

than that of rice stored at higher temperatures.<br />

Storage capacity of rough rice (000 t)<br />

120<br />

100<br />

80<br />

60<br />

Number of newly<br />

constructed facilities<br />

Each year<br />

Total<br />

47<br />

64<br />

79<br />

104<br />

111<br />

115<br />

40<br />

(3) (6)<br />

(4)<br />

19<br />

20<br />

(2)<br />

28 (5) (4)<br />

25<br />

8<br />

17<br />

0<br />

16<br />

(1)<br />

11<br />

(2)<br />

6 5<br />

0<br />

1995 1996 1997 1998 1999 2000 2001 2002 2003<br />

Year of construction<br />

Fig. 2. Storage capacity of rough rice in Hokkaido, Japan.<br />

use of fresh chilly air enables the quality of rice to be preserved<br />

at a high level without requiring a cooling unit or electricity.<br />

The use of the super-low-temperature storage technique<br />

has been increasing in cold regions of Japan in recent years. In<br />

Hokkaido, the northernmost island in Japan, 26 grain-elevators<br />

have been constructed since 1996. The storage capacity<br />

of rough rice in Hokkaido was 115,000 t at the end of 2003<br />

(Fig. 2).<br />

References<br />

Kawamura S, Natsuga M, Kouno S, Itoh K. 1997. Super-low temperature<br />

storage for preserving rice quality. Proceedings of<br />

the Joint <strong>International</strong> Conference on Agricultural Engineering<br />

& Technology, Volume III, 15-18 December 1997, Dhaka,<br />

Bangladesh. p 820-824.<br />

Kawamura S, Takekura K, Itoh K. 2004. <strong>Rice</strong> quality preservation<br />

during on-farm storage using fresh chilly air. Proceedings of<br />

the 2004 <strong>International</strong> Quality Grains Conference, 19-22 July<br />

2004, Indianapolis, Ind. (USA). p 1-17.<br />

Notes<br />

Authors’ addresses: Shuso Kawamura, Graduate School of Agricultural<br />

Science, Hokkaido University, Kita 9, Nishi 9, Sapporo<br />

060-8589, e-mail: shuso@bpe.agr.hokudai.ac.jp; Kazuhiro<br />

Takekura, National Agricultural <strong>Research</strong> Center, 3-1-1<br />

Kannondai, Tsukuba, Ibaraki 305-8666, e-mail:<br />

takekura@affrc.go.jp; Kazuhiko Itoh, Graduate School of<br />

Agricultural Science, Hokkaido University, Kita 9, Nishi 9,<br />

Sapporo 060-8589, Japan, e-mail:<br />

kazu@bpe.agr.hokudai.ac.jp.<br />

Extension of super-low-temperature storage of rice<br />

A new technique for storing rice at a temperature below ice<br />

point using fresh chilly air in winter was developed. A combination<br />

of rice storage at a temperature below ice point and the<br />

312 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Life-cycle inventory analysis of local parboiling processes<br />

Poritosh Roy, Naoto Shimizu, Takeo Shiina, and Toshinori Kimura<br />

Parboiled rice is the staple food in some developing countries,<br />

including Bangladesh. In Bangladesh, per capita consumption<br />

is reported to be 168 kg year –1 (FAO STAT 2001). Kar et al<br />

(1999) reported that one-fourth of the world’s paddy is parboiled.<br />

Parboiled rice has been produced by both traditional<br />

and modern methods. Modern methods are energy- and capital-intensive,<br />

and are not suitable for small-scale operation at<br />

the village level. In rural areas, various methods are being used<br />

to produce rice and these consume different amounts of energy.<br />

The commonly used local parboiling processes are vessel<br />

(0.5–1.2 t batch –1 ), small-boiler (2–4 t batch –1 ), and medium-boiler<br />

(5–10 t batch –1 ). Biomass, that is, rice husk, is the<br />

main source of energy for parboiling. In Bangladesh, 63% of<br />

the total energy consumption is met by biomass fuel and 37%<br />

is commercial fuel. The household sector consumes 80% of<br />

total biomass energy and rural households use it almost exclusively<br />

for cooking (Bari et al 1998). It is reported that biomass<br />

combustion contributes as much as 20–50% of global greenhouse<br />

gas emissions, of which one-third may come from households.<br />

This has an adverse effect on human health and the environment<br />

(Smith 1999). With the growing concern about environmental<br />

pollution and health risks, it is very important to<br />

find a sustainable rice-processing method. T<strong>here</strong>fore, this study<br />

attempts to evaluate the environmental effects of different riceprocessing<br />

methods using the life-cycle assessment (LCA)<br />

methodology.<br />

Methodology<br />

LCA is a methodology to assess all the environmental impacts<br />

associated with a product, process, or activity throughout its<br />

life cycle by accounting for and evaluating resource consumption<br />

and emissions. This concept consists of four major steps:<br />

goal definition and scoping, inventory analysis, impact assessment,<br />

and improvement assessment (SETAC 1993).<br />

Goal definition and scoping<br />

This stage defines the purpose of the study, the expected product<br />

of the study, the boundary conditions, and the assumption.<br />

Furthermore, a reference unit (functional unit, FU), to which<br />

all the environmental impacts are related, has to be defined.<br />

The goal of this study was to investigate the life cycle of rice<br />

produced by the vessel, small-boiler, medium-boiler, and untreated<br />

process. Figure 1 shows the life cycle of rice under<br />

different processing methods and the boundary of this study,<br />

which is encircled by a broken line.<br />

It has been reported that agricultural LCAs often exclude<br />

production processes of medicine and insecticides, machines,<br />

buildings, and roads because of a lack of data (Cederberg and<br />

Mattsson 2000). In this study, environmental releases related<br />

to the cultivation of paddy and construction of the parboiling<br />

facilities were not considered because of the unavailability of<br />

data. Usually, the paddy and rice are marketed at the nearby<br />

market or at the mill-gate in local areas. Manually operated<br />

three-wheeled rickshaw-vans are the main transportation used<br />

in local parboiling processes. T<strong>here</strong>fore, energy consumption<br />

and environmental releases from transportation were also not<br />

considered. The FU has been defined as the mass of the product,<br />

that is, 1 ton of head rice.<br />

Inventory analysis<br />

The life-cycle inventory (LCI) analysis quantifies resource use,<br />

energy consumption, and environmental releases associated<br />

with the system being evaluated. The energy consumption in<br />

the parboiling processes, dehusking, milling, and cooking, was<br />

taken from our own study (Roy 2003). Energy consumption<br />

during drying of parboiled paddy was derived from the literature<br />

(Palipane et al 1988). Energy consumption in dehusking,<br />

milling, and cooking was considered to be the same for parboiled<br />

rice produced by different processing methods.<br />

Seedling<br />

Cultivation<br />

Parboiling<br />

PresteamingSoakingSteaming DryingDehuskingMilling<br />

Parboiled<br />

Harvesting<br />

Paddy<br />

Fresh<br />

Untreated DehuskingMilling <strong>Rice</strong><br />

CookingConsumption<br />

Parboiling<br />

PresteamingSoakingSteaming Drying DehuskingMilling<br />

Parboiled<br />

Fig. 1. Life cycle of rice and the system boundary of this study (marked by the broken line).<br />

Session 10: Postharvest technology for efficient processing and distribution of rice 313


Table 1. Inventory results (inputs and outputs) of the rice life cycle produced by different<br />

processes. a<br />

Inputs and outputs per t<br />

of head rice<br />

Process<br />

Vessel Small-boiler Medium-boiler Untreated<br />

Input Paddy (kg) 1,517.5 1,445.1 1,501.5 1,666.7<br />

Biomass energy (kg) 1,275.7 1,286.2 1,170.0 885.1<br />

Diesel energy (L) – – 0.1 –<br />

Output Biomass energy (kg) 440.1 419.1 435.4 483.3<br />

Atmospheric emissions (kg)<br />

CO 2 1,349.0 1,360.0 1,237.9 938.2<br />

CO 94.1 94.2 93.3 82.8<br />

CH 4 3.0 3.0 2.8 2.0<br />

TSP 18.3 18.6 15.3 8.9<br />

SO x 4.1 4.1 3.7 2.8<br />

NO x 3.6 3.6 3.5 2.9<br />

VOC – – 0.00077 –<br />

Water emissions (g)<br />

BOD 426.8 406.5 422.3 –<br />

COD 1,114.4 1,061.3 1,102.7 –<br />

Amino nitrogen 113.6 108.2 112.4 –<br />

Phenol 70.0 67.0 69.0 –<br />

Solid waste (ash) (kg) 261.7 263.8 241.4 185.1<br />

a The head-rice yield of the vessel, small-boiler, medium-boiler, and untreated process was 65.9%, 69.2%,<br />

66.6%, and 60%, respectively.<br />

It was assumed that the energy requirement in the life<br />

cycle of rice was met by biomass energy and that biomass (rice<br />

husk) was the source of primary energy for all types of energy<br />

consumed in the rice life cycle, except diesel energy. The biomass<br />

used in parboiling and electricity generation is considered<br />

to be the industrial use of biomass and an improved domestic<br />

cook-stove was used for cooking. It has been reported<br />

that the electricity efficiency of IGCC (integrated gasification<br />

combined cycles, biomass option) is 43% (Gustavsson 1997).<br />

The efficiency of an improved cook-stove (ASTRA) is reported<br />

to be 30% (Bhattacharya et al 1999). Based on these factors,<br />

the primary energy, atmospheric emissions (CO 2 , CO, TSP,<br />

CH 4 , NO x , SO x , and VOC), water emissions (amino nitrogen,<br />

phenol, BOD, and COD), and production of final solid waste<br />

(ash) were determined.<br />

Results and discussion<br />

Although the inventory results consist of an exhaustive list of<br />

parameters, the only parameters discussed in this study are<br />

resource use, energy use, environmental emissions, and solid<br />

waste (ash) production. The inventory results (inputs and outputs)<br />

of the rice life cycle are reported in Table 1.<br />

Energy consumption<br />

The rice-processing industry consumes some energy and at the<br />

same time produces some energy in the form of a by-product<br />

(rice husk). Based on this assumption, an energy inventory was<br />

worked out and expressed in terms of primary energy (rice<br />

husk). In the case of parboiled rice, the energy inventory was<br />

lower for the medium-boiler than for the vessel and small-boiler<br />

process. Fresh rice consumes less energy than parboiled rice,<br />

but it consumes more resource (paddy) because of low headrice<br />

yield (Table 1).<br />

Atmospheric emissions<br />

The environmental load was found to be lower for untreated<br />

rice than for parboiled rice. Parboiled rice produced by the<br />

medium-boiler process had a lower environmental load than<br />

that produced by the vessel and small-boiler. The atmospheric<br />

emission inventory indicates a need to switch methods to reduce<br />

air emissions.<br />

Water emissions<br />

The excess soak-water drains after the soaking treatment in<br />

the parboiling process and is the main source of water emissions<br />

in the life cycle of parboiled rice. T<strong>here</strong> is no soaking<br />

treatment in the untreated process and hence no water emissions<br />

were reported for fresh rice.<br />

Solid waste (ash)<br />

Untreated rice produces the lowest amount of solid waste compared<br />

with the other processes. For parboiled rice, solid waste<br />

was lower for the medium-boiler process (Table 1).<br />

LCI analysis of rice reveals that all the processes have a<br />

negative effect on the environment and the environmental load<br />

depends on the production process. The results showed a<br />

gradual decrease in inventory (energy consumption, atmospheric<br />

emissions, and solid waste) from the small-boiler to<br />

the untreated process (small-boiler>vessel>mediumboiler>untreated)<br />

and t<strong>here</strong> are no waterborne emissions in<br />

the case of the untreated process. The environmental load is<br />

314 <strong>Rice</strong> is life: scientific perspectives for the 21st century


lowest for untreated rice; however, it consumes more resource<br />

(paddy) because of the lowest head rice. This study indicates<br />

that a switch in rice production processes is required to reduce<br />

energy and resource consumption, and environmental pollution.<br />

If fresh rice is considered to be a sustainable energy consumption<br />

option (the energy shortage would be overcome by<br />

agri-residues, animal wastes, and tree leaves and twigs), then<br />

the other processes might be responsible for deforestation.<br />

Considering the head-rice yield and consumption pattern, it<br />

would be wise to produce parboiled rice by adopting the medium-boiler<br />

process even though it requires a higher initial<br />

installation cost than the vessel and small-boiler process, and<br />

consumes more energy than the untreated process.<br />

Conclusions<br />

This study makes it possible to compare the environmental<br />

load of different types of rice and it reveals that all the processes<br />

are responsible for environmental pollution, although<br />

the intensity of pollution varies from process to process. Thus,<br />

a change in the rice production process and consumption pattern<br />

would reduce energy consumption, atmospheric emissions,<br />

waterborne emissions, and solid waste in the rice life cycle. A<br />

nominal incentive, motivation, and awareness of the environment<br />

and health are required for method switching. Method<br />

switching would reduce environmental pollution, deforestation,<br />

and global warming.<br />

References<br />

Bari MN, Hall DO, Lucas NJD, Hossain SMA. 1998. Biomass energy<br />

use at the household level in two villages of Bangladesh:<br />

assessment of field methods. Biomass Bioenergy 15(2):171-<br />

180.<br />

Bhattacharya SC, Attalage RA, Augustus Leon M, Amur GQ, Abdul<br />

Salam P, Thanawat C. 1999. Potential of biomass fuel conversion<br />

in selected Asian countries. Energy Conver. Manage.<br />

40:1141-1162.<br />

Cederberg C, Mattsson B. 2000. Life cycle assessment of milk production:<br />

a comparison of conventional and organic farming.<br />

J. Cleaner Prod. 8:49-60.<br />

FAOSTAT. 2001. Food and Agriculture Organization of the United<br />

Nations, Rome Italy, FAO statistical databases, available online<br />

at http://apps.fao.org/.<br />

Gustavsson L. 1997. Energy efficiency and competitiveness of biomass<br />

based energy systems. Energy 22(10):959-967.<br />

Kar N, Jain RK, Srivastav PP. 1999. Parboiling of dehusked rice. J.<br />

Food Eng. 39:17-22.<br />

Palipane KB, Adhikarinayake TB, Watson WR, Thorpe GR,<br />

Ilangantilleke SG, Senanayake DP. 1988. Fluidized bed drying<br />

of parboiled rice. Sri Lankan J. Post Harvest Technol.<br />

1(1):1-9.<br />

Roy P. 2003. Improvement of energy requirement in traditional parboiling<br />

process. PhD thesis. University of Tsukuba, Japan.<br />

(Unpublished.)<br />

SETAC. 1993. A conceptual framework for life-cycle impact assessment.<br />

Workshop (1-7 February 1992) Report, The Society of<br />

Environmental Toxicology and Chemistry, Pensacola, Fla.<br />

(USA).<br />

Smith KR. 1999. Fuel emission, health and global warming. Regional<br />

Wood Energy Development Programme in Asia (FAO). Wood<br />

Energy News 14(3):4-5.<br />

Notes<br />

Authors’ addresses: Poritosh Roy and Takeo Shiina, Distribution<br />

Engineering Laboratory, National Food <strong>Research</strong> <strong>Institute</strong>,<br />

Tsukuba, Japan; Naoto Shimizu and Toshinori Kimura, Graduate<br />

School of Life and Environmental Sciences, University of<br />

Tsukuba, Japan, e-mail: shimizu@sakura.cc.tsukuba.ac.jp.<br />

Using genetics to create changes in rice cooking,<br />

processing, storage, and health-beneficial properties<br />

Christine Bergman<br />

A great deal of improvement in rice grain end-use quality has<br />

occurred over the past decades using postharvest technology.<br />

For example, a method has been developed to fabricate rice<br />

flour into grain-like shapes possessing superior mineral content.<br />

Preharvest technology, however, has been used to a lesser<br />

degree to affect rice end-use quality. To date, only traditional<br />

breeding methods combined with molecular markers and relatively<br />

simple physical and biochemical tools have been used<br />

to change the end-use quality of rice cultivars. The few traits<br />

that have been modified using these tools are amylose content,<br />

gelatinization temperature, kernel morphology, bran color,<br />

chalkiness, and milling quality. Changing rice end-use quality<br />

characteristics using preharvest techniques has an advantage<br />

over postharvest methods because they create permanent<br />

change. On the contrary, changes made using postharvest methodology<br />

must be made to each rice harvest.<br />

Advancement in genetics methods and biochemical separation<br />

and identification tools have lagged behind the technological<br />

advancements underpinning postharvest methods used<br />

to modify rice end-use quality. But, the gap between the tools<br />

of pre- and postharvest technology is closing. Consequently,<br />

some research programs across the world are using these tools<br />

to evaluate the potential of developing cultivars with modified<br />

traits such as storage, cooking, processing, and health-beneficial<br />

properties. These programs consist of collaboration among<br />

geneticists, breeders, food scientists, nutritionists, and chemists.<br />

Below is a review of research efforts using the tools of<br />

Session 10: Postharvest technology for efficient processing and distribution of rice 315


genetics to modify rice end-use quality, including traditional,<br />

mutation, and molecular breeding techniques.<br />

Traditional breeding<br />

To use traditional breeding to modify rice traits, genetic diversity<br />

for the trait must exist. Nearly 420,500 Oryza samples are<br />

maintained in germplasm collections across the world. Most<br />

of this genetic material has yet to be explored for its variation<br />

in any aspects of end-use quality. T<strong>here</strong> is an increasing interest<br />

by some breeding programs around the world in using these<br />

genetic resources to develop rice cultivars with modified kernel<br />

characteristics. As an example of this, work by my colleagues<br />

and me at the U.S. Department of Agriculture is discussed<br />

below.<br />

A germplasm collection was chosen to contain as much<br />

genetic diversity as possible. More than 200 rice cultivars and<br />

exotic accessions from over 25 countries were grown using<br />

the same cultural management practices during two growing<br />

seasons. The collection has been used to evaluate the potential<br />

for developing cultivars with a reduced need for postharvest<br />

bran stabilization and enhanced levels or ratios of bran<br />

phytochemicals using genetic diversity and cross-pollination<br />

techniques.<br />

Oil content (twofold) and fatty acid profiles in the collection<br />

varied a great deal (Goffman et al 2003). Significant<br />

genotypic differences in bran E vitamer (i.e., tocopherols and<br />

tocotrienols) content (twofold) and gamma-oryzanol (threefold)<br />

content were also found (Chen and Bergman, unreported<br />

data). Total gamma-oryzanol content and the three primary<br />

gamma-oryzanol compounds were not correlated with the level<br />

of E vitamers across the germplasm collection. The three<br />

gamma-oryzanol compounds were not correlated with each<br />

other. Nor was the tocopherol content correlated with the<br />

tocotrienol content. The lines with white or light brown bran<br />

had low phenolic contents, w<strong>here</strong>as those with darker bran<br />

(dark brown, red, and black) showed a much greater range in<br />

phenolic concentration (23-fold) and antiradical efficiency<br />

(Goffman and Bergman 2003). The rate of hydrolytic rancidity<br />

in this collection was well correlated with esterase activity,<br />

which varied approximately fourfold (Goffman and Bergman<br />

2003). These results suggest that it will be possible to use traditional<br />

breeding methods to increase the oil and various antioxidant<br />

fractions of rice bran, as well as to modify the bran’s<br />

fatty acid profile and reduce its susceptibility to becoming rancid.<br />

Mutation breeding<br />

When an end-use quality trait is desired, but does not exist in<br />

rice germplasm or it varies little, then mutation or molecular<br />

breeding must be used. Mutation breeding becomes the method<br />

of choice when the genes controlling the trait have not been<br />

cloned, or if transgenic technology is not desired. Mutation<br />

breeding has recently been used successfully to create new<br />

rice kernel traits. A few examples are described below.<br />

Located primarily in the aleurone layer, phytic acid, when<br />

consumed by humans, is thought to reduce mineral<br />

bioavailability. Also, when fed to animals, the phosphorus in<br />

this molecule is excreted in their feces and rain takes it to waterways,<br />

w<strong>here</strong> the algae growth that occurs as a result depletes<br />

the oxygen and other aquatic life dies. Thus, bran low in<br />

phytic acid is desired, but little genetic variation for this trait<br />

has been found in rice germplasm.<br />

A low-phytic-acid mutant has been reported by Larson<br />

et al (2000). Gamma radiation mutagenesis was used to create<br />

the nonlethal low-phytic-acid mutant. The mutation was designated<br />

low phytic acid 1-1 (lpa1-1). Homozygosity for rice<br />

lpa-1 changed the wild-type portion of seed phosphorus in<br />

phytic acid from 71% to 39%. The inorganic portion of phosphorus<br />

increased from 5% to 32%, w<strong>here</strong>as the total phosphorus<br />

content of the seeds was unchanged.<br />

Cool temperatures during grain maturation can interact<br />

with some genotypes to cause greater amylose content and thus<br />

firmer rice may ensue. Variability in textural properties is a<br />

problem for the food-processing industry. T<strong>here</strong>fore, cultivars<br />

that are insensitive to low growing temperatures would be advantageous.<br />

Suzuki et al (2002) set out to create such a genotype<br />

by mutating a temperature-sensitive low-amylose type.<br />

This genotype had a mutation at the du2 locus and, as a result,<br />

the seeds could be visibly distinguished depending on whether<br />

they matured at cool or warmer temperatures. A mutant that<br />

was insensitive to cool temperature was identified based on its<br />

semitranslucent phenotype. Amylose synthesis in the mutant<br />

and wild type was not significantly different. The authors are<br />

now confident that the effect of the mutation is not limited to<br />

the du2 mutant background. They are now incorporating the<br />

mutation into locally adapted germplasm (personal communication).<br />

As with other cereal grains, rice is lower in the essential<br />

amino acid lysine than other sources of protein consumed by<br />

humans. Elevated lysine levels in rice could help reduce humans’<br />

reliance on animal protein, which is in shorter supply<br />

than grain protein and its production is considered to be less<br />

sustainable. Kim et al (2004) irradiated calli of a cultivar with<br />

gamma-rays and mutant cell lines resistant to growth inhibition<br />

by S-(2-aminoethyl)-cysteine (AEC) were selected. The<br />

AEC-resistant M 3 lines had lysine levels from 1.58 to 2.66<br />

times higher than the wild type.<br />

Molecular plant breeding<br />

Some characteristics that are desired in rice kernels will have<br />

to be created using genetic transformation techniques. These<br />

are generally traits that do not exist, vary too little or too much<br />

in rice germplasm, or are unlikely to be found using mutation<br />

methods. The creation of enhanced levels of iron, zinc, and<br />

beta-carotene in rice using molecular breeding techniques has<br />

been well described (Beyer et al 2002, Vasconcelos et al 2003).<br />

Described below are examples of other efforts to use transformation<br />

technology to change rice end-use quality.<br />

316 <strong>Rice</strong> is life: scientific perspectives for the 21st century


A family of plant phenolic compounds that are derivatives<br />

of the neurotransmitter, serotonin, has been hypothesized<br />

to have an array of health-beneficial effects, such as antioxidant<br />

activity. Kang et al (2004) transformed rice to have enhanced<br />

levels of pepper hydroxycinnamoyl-CoA:serotonin N-<br />

(hydroxycinnamoyl) transferase. The transformed seeds had<br />

on average ninefold higher amounts of serotonin derivatives<br />

than the wild type. The radical scavenging activity of the<br />

transgenic rice was also higher and showed concentration dependence<br />

on the serotonin derivatives.<br />

Puroindolines are thought to be involved in creating<br />

variation in wheat grain texture, but are absent in rice. Mutations<br />

in the genes that code for puroindolines are associated<br />

with wheat kernel hardness. Transgenic rice was produced with<br />

the puroindoline genes under the control of a maize promoter<br />

(Krishnamurthy and Giroux 2001). Textural analysis of the<br />

transgenic rice seeds provided evidence that the expression of<br />

these genes is able to reduce rice grain hardness. After milling,<br />

flour prepared from these softer seeds had reduced starch<br />

damage and an increased percentage of fine flour particles.<br />

The authors suggested that these characteristics could have<br />

utility in designing new rice-based products. Interestingly, this<br />

transformation also resulted in increased rice plant resistance<br />

to several fungal diseases.<br />

A fifth or more of stored grain in less developed countries<br />

is lost because of insect and disease damage. The primary<br />

source of storage loss (i.e., weight and sensory quality)<br />

for rice is the rice weevil (Sitophilus oryzae). These insects<br />

depend on serine proteinases to metabolize protein and, consequently,<br />

consumption of proteinase inhibitors decreases their<br />

survival rate. Alfonso-Rubi et al (2003) reported the transformation<br />

of rice with the Itr1 gene, which encodes the barley<br />

trypsin inhibitor. The gene was controlled by its own promoter<br />

that confers endosperm specificity and the maize ubiquitin<br />

promoter. The authors reported a significant reduction in the<br />

survival rate of rice weevils fed the transgenic rice seeds expressing<br />

the inhibitor compared with the controls. This confirmed<br />

the potential utility of this proteinase inhibitor gene to<br />

decrease rice storage losses caused by the rice weevil.<br />

Conclusions<br />

None of the research efforts described above have yet resulted<br />

in the release of a new cultivar. The traits need to be moved<br />

into superior-yielding germplasm and its agronomic performance<br />

evaluated. Also, producers must be convinced of a<br />

cultivar’s agronomic superiority before they will replace the<br />

cultivars they are currently planting. An alternative is for an<br />

interested party to have a cultivar with a unique end-use property<br />

grown under contract, regardless of its agronomic quality.<br />

In some instances, mechanisms also need to be in place to segregate<br />

harvests of the modified cultivar from those of other<br />

cultivars. When these hurdles are overcome, consumers will<br />

be closer to having access to rice with a plethora of enhanced<br />

end-use quality characteristics.<br />

References<br />

Alfonso-Rubi J, Ortego F, Castanera P, Carbonero P, Diaz I. 2003.<br />

Transgenic expression of trypsin inhibitor CMe from barley<br />

in indica and japonica rice confers resistance to the rice weevil<br />

Sitophilus oryzae. Transgenic Res. 12:23-31.<br />

Beyer P, Al-Babili S, Ye X, Lucca P, Schaub P, Welsch R, Potrykus<br />

I. 2002. Golden <strong>Rice</strong>: introducing the ß-carotene biosynthesis<br />

pathway into rice endosperm by genetic engineering to<br />

defeat vitamin A deficiency. J. Nutr. 132:506S-510S.<br />

Goffman FD, Pinson SR, Bergman CJ. 2003. Genetic diversity for<br />

lipid content and fatty acid profile in rice bran. J. Am. Oil<br />

Chem. Soc. 80:485-490.<br />

Goffman FD, Bergman CJ. 2003. Relationship between hydrolytic<br />

rancidity, oil concentration and esterase activity in rice cultivars.<br />

Cereal Chem. 80:446-449.<br />

Kang K, Jang S-M, Kang S, Back K. 2004. Enhanced neutraceutical<br />

serotonin derivatives of rice seed by hydroxycinnamoyl-<br />

CoA:serotonin N-(hydroxycinnamoyl) transferase. Plant Sci.<br />

(In press.)<br />

Kim DS, Lee IS, Jang CS, Lee SJ, Song HS, Lee YI, Seo YW. 2004.<br />

AEC resistant rice mutants induced by gamma-ray irradiation<br />

may include both elevated lysine production and increased<br />

activity of stress related enzymes. Plant Sci. 167:305-316.<br />

Krishnamurthy K, Giroux MJ. 2001. Expression of wheat<br />

puroindoline genes in transgenic rice enhances grain softness.<br />

Nat. Biotechnol. 19:162-166.<br />

Larson SR, Rutger JN, Young KA, Raboy V. 2000. Isolation and<br />

genetic mapping of a non-lethal rice (Oryza sativa L.) low<br />

phytic acid 1 mutation. Crop Sci. 40:1397-1405.<br />

Suzuki Y, Sano Y, Hiro-Yuki H. 2002. Isolation and characterization<br />

of a rice mutant insensitive to cool temperatures on amylase<br />

synthesis. Euphytica 123:95-100.<br />

Vasconcelos M, Datta K, Oliva N, Khalekuzzaman M, Torrizo L,<br />

Krishnan S, Margarida O, Goto F, Datta S. 2003. Enhanced<br />

iron and zinc accumulation in transgenic rice with the ferritin<br />

gene. Plant Sci. 164:371-378.<br />

Notes<br />

Author’s address: University of Nevada, Las Vegas, Departments of<br />

Food and Beverage and Nutrition Sciences, 4505 Maryland<br />

Parkway, Las Vegas, NV 89154, USA, e-mail:<br />

bergman5@unlv.nevada.edu.<br />

Session 10: Postharvest technology for efficient processing and distribution of rice 317


The role of proteins in textural changes in aged rice<br />

Toshihisa Ohno, Takahiro Kaneko, and Naganori Ohisa<br />

The texture of cooked rice from aged grains is generally hard<br />

and nonsticky. Japanese people prefer cooked rice from newly<br />

harvested grains because of its highly sticky and soft texture.<br />

Many factors have been identified as the cause of these changes<br />

in cooking properties, including the increase in free fatty acids<br />

during storage and their inhibitory effect on the gelatinization<br />

of rice starch, changes in the physicochemical properties of<br />

rice starch itself, and changes in the structure-maintaining components<br />

(Shibuya and Iwasaki 1982).<br />

Some investigators have specifically studied the proteins<br />

associated with these changes. Moritaka and Yasumatsu (1972)<br />

suggested that disulfide bond formation is responsible for the<br />

textural changes in cooked rice during storage, and Arai and<br />

Watanabe (1993) reported that denatured proteins were associated<br />

with these changes. Furthermore, Hamaker and Griffin<br />

(1990) reported that reducing agents influence the texture of<br />

cooked rice.<br />

We t<strong>here</strong>fore aimed to clarify the role of proteins in the<br />

textural changes in cooked rice seen after storage.<br />

Materials and methods<br />

Experimental materials<br />

A japonica-type rice (Oryza sativa L. japonica, cultivar<br />

Akitakomachi) harvested in Akita Prefecture was used in the<br />

experiments. After brown rice grains harvested in 2001 were<br />

polished to wash-free grade, they were used as New <strong>Rice</strong> A.<br />

New <strong>Rice</strong> A grains, stored for 2 months at 30 °C in a closed<br />

aluminum pouch, were used as Aged <strong>Rice</strong> A. Brown rice grains<br />

harvested in 2001 were normally polished and used as New<br />

<strong>Rice</strong> B. After the brown rice grains harvested in 1999 had been<br />

stored for 3 years at 15 °C in a paper bag, they were normally<br />

polished and used as Aged <strong>Rice</strong> B. T<strong>here</strong>after, all samples were<br />

stored at below –5 °C until use in the experiments.<br />

Cooking and texture measurement<br />

Ten-gram samples of polished rice were not washed and then<br />

soaked in 16 mL of distilled water for 1 h in an aluminum cup<br />

covered with aluminum foil. Next, they were cooked in an electric<br />

rice cooker (National, SR-W100, with 75 mL of water<br />

added to the outer pan) for about 12 min. After steaming for<br />

30 min, the cooked rice was transferred to a closed dish and<br />

kept at 25 °C for 90 min.<br />

The hardness (H) and stickiness (S) of the individual<br />

cooked rice grains were then measured by 90% deformation<br />

with a compression tester (Taketomo, Tensipresser, TTP-<br />

50BX2). The most important parameter, stickiness/hardness<br />

(S/H) ratio, was worked out. More than 40 cooked rice grains<br />

of every type were measured. Conditions for the measurement<br />

were as follows: plunger and stage, aluminum; bite speed, 2<br />

mm sec –1 ; and sample temperature at the time of measurement,<br />

25 °C.<br />

The influence of the addition of an oxidizing or reducing<br />

agent on the S/H ratio was also investigated. Instead of<br />

distilled water, an aqueous solution of 5 mM potassium iodate<br />

(an oxidizing agent) or 8 mM sodium sulfite or 10 mM cysteine<br />

(reducing agents) was used as the cooking water. The<br />

method of cooking and measuring S/H ratio was the same as<br />

described above.<br />

Removal of external layer of polished rice<br />

After the rice samples were further polished in a mill (Grain<br />

Testing Mill, Satake or HS-4 Mill, Tiyoda Engineering), they<br />

were cooked. The rate of removal of the external layer of the<br />

polished rice was 7–20%. The method of cooking and measuring<br />

S/H ratio was the same as described above.<br />

Electrophoresis<br />

The rice flour derived from the external layer of the rice grains<br />

was mixed with distilled water or an aqueous solution of 5<br />

mM potassium iodate for 30 min. After the mixture had been<br />

centrifuged, the pellet was rinsed in distilled water and centrifuged<br />

again. The precipitate was mixed with Solution A (10<br />

mM sodium hydroxide, 1% SDS) and incubated for 2 h.<br />

The mixtures were then centrifuged and the resulting supernatants<br />

subjected to electrophoresis. The native-PAGE using<br />

0.1% SDS was performed on 5–20% gradient polyacrylamide<br />

gels. Coomassie brilliant blue was used as the staining<br />

agent.<br />

Results and discussion<br />

We evaluated the textures of cooked rice. Figure 1 shows the<br />

S/H ratios of the various types of cooked rice. The S/H ratio of<br />

aged rice cooked in water was low. Since Japanese people generally<br />

prefer cooked rice with a high S/H ratio (Fuke et al 1991),<br />

Aged <strong>Rice</strong> A and B were inferior to New <strong>Rice</strong> A and B. These<br />

changes have been observed in numerous previous reports (e.g.,<br />

Fuke et al 1991).<br />

Next, the influence of the addition of an oxidizing or<br />

reducing agent on the S/H ratio was investigated (Fig. 1). The<br />

addition of 5 mM potassium iodate to the cooking water lowered<br />

the S/H ratio. On the other hand, the addition of a reducing<br />

agent to the cooking water raised it. The S/H ratio of aged<br />

rice was low as described above, and the addition of the oxidizing<br />

agent brought the S/H ratio of New <strong>Rice</strong> down. We t<strong>here</strong>fore<br />

estimated that the textural changes in the aged rice are<br />

attributable to oxidation.<br />

318 <strong>Rice</strong> is life: scientific perspectives for the 21st century


S/H ratio<br />

0.5<br />

0.4<br />

Cooked in water<br />

Cooked in water with oxidizing agent<br />

Cooked in water with reducing agent<br />

The rate of removed external layer to the polished rice was 7%, cooked in water<br />

The rate of removed external layer to the polished rice was 1% or 20%, cooked in water<br />

0.3<br />

0.2<br />

0.1<br />

0<br />

New <strong>Rice</strong> A Aged <strong>Rice</strong> A New <strong>Rice</strong> B Aged <strong>Rice</strong> B<br />

Fig. 1. The S/H ratio of various types of cooked rice.<br />

After the polished rice had been further polished in a<br />

mill, it was cooked. Figure 1 also shows the S/H ratio of<br />

samples. After the removal of 7% of the external layer from<br />

the polished rice, the S/H ratio of Aged <strong>Rice</strong> A increased to<br />

slightly higher than that of New <strong>Rice</strong> A. Distinct differences<br />

were seen between the S/H ratio of Aged <strong>Rice</strong> B and that of<br />

New <strong>Rice</strong> B after the removal of 7% of the external layer, but<br />

these differences disappeared completely after the removal of<br />

1% or 20% of the external layer. Since the S/H ratio of Aged<br />

<strong>Rice</strong> B was not sufficiently improved by the removal of 7% of<br />

its external layer, Aged <strong>Rice</strong> B is likely to have been in an<br />

advanced stage of deterioration. These improvements to the<br />

S/H ratio in aged rice by the removal of the external layer<br />

suggest that the external layer of the aged rice caused the decreased<br />

S/H ratio.<br />

Finally, the native-PAGE results for rice flours treated<br />

with the oxidizing agent are shown in Figure 2. The native-<br />

PAGE of rice flour treated with the oxidizing agent revealed a<br />

decrease in low-molecular proteins (21, 23, and 32 kDa) and<br />

an increase in high-molecular proteins (larger than 46 kDa).<br />

These facts suggest that intermolecular disulfide linkages of<br />

rice proteins were easily formed in the presence of an oxidizing<br />

agent.<br />

Our results indicate that proteins may be polymerized<br />

by disulfide linkage in the external layer of aged rice, and that<br />

some of these proteins influence its texture. Further investigations<br />

need to be made to clarify this supposition.<br />

Positions of molecular<br />

weight markers<br />

97.0 k<br />

66.0 k<br />

45.0 k<br />

30.0 k<br />

20.1 k<br />

14.4 k<br />

1 2<br />

Fig. 2. Native-PAGE of rice flours treated with water or<br />

oxidizing agent. Lane 1: treated with distilled water;<br />

lane 2: treated with aqueous solution of 5 mM potassium<br />

iodate.<br />

Session 10: Postharvest technology for efficient processing and distribution of rice 319


References<br />

Arai E, Watanabe M. 1993. Enzymatic improvement of the cooking<br />

quality of aged rice: a main mode of protease action. Biosci.<br />

Biotech. Biochem. 57:911-914.<br />

Hamaker BR, Griffin VK. 1990. Changing the viscoelastic properties<br />

of cooked rice through protein disruption. Cereal Chem.<br />

67:261-264.<br />

Moritaka S, Yasumatsu K. 1972. The effect of sulfhydryl groups on<br />

storage deterioration of milled rice: studies on cereals (part<br />

10). Eiyo Syokuryo 25(2):59-62.<br />

Shibuya N, Iwasaki T. 1982. Effect of the enzymatic removal of endosperm<br />

cell wall on the gelatinization properties of aged and<br />

unaged rice flours. Starch/Staerke 34:300-303.<br />

Notes<br />

Authors’ address: Akita <strong>Research</strong> <strong>Institute</strong> of Food and Brewing, 4-<br />

26, Aza-sanuki, Araya-machi, Akita 010-1623, Japan, e-mail:<br />

ohno@arif.pref.akita.jp.<br />

Acknowledgments: This work was financially supported by the Iijima<br />

Food Science Foundation.<br />

Postharvest technology of rice: the role of farm women<br />

in storing grains with different storage practices<br />

P. Sumathi and M.N. Budhar<br />

India has increased rice production markedly during the past<br />

50 years by enhancing production from 22 to 93 million t. On<br />

the other hand, because of severe and unprecedented drought<br />

conditions during 2002-03, the total annual rice production<br />

had a shortfall of 17 million t. However, rice demand in 2010<br />

and 2025 will be 100 and 140 million t, respectively (Mishra<br />

2004). Hence, the shortfall in unexpected years and the projected<br />

demand to feed the growing population have to be met<br />

by proper handling of produced rice besides increasing production.<br />

The importance of storage is often ignored in rice<br />

production ventures. Inadequate storage facilities and improper<br />

storage can cause considerable losses to rice farmers. Total<br />

postharvest losses of food grains account for 9.3% and the<br />

losses during storage alone account for 6.5% (Gandhi 1983).<br />

Unless losses of food grains in the postharvest phase are satisfactorily<br />

minimized, the problem of feeding hungry millions<br />

could continue even with a substantial increase in production.<br />

Thus, farmers must learn the proper way of storing rice for a<br />

transitory period on the farm and the local market and for a<br />

seasonal/national reserve or buffer stock, besides protecting<br />

grains against weather and insects. Preventing grain discoloration<br />

and a bad odor to maintain rice quality for feeding and<br />

marketing is essential.<br />

The majority of the world’s agricultural producers are<br />

women: they produce more than 50% of the food that is grown<br />

worldwide. Women are usually responsible for food processing<br />

and make a major contribution to food storage. Women<br />

farmers play a distinct and well-accepted role in all activities<br />

of rice cultivation and 93% of the farm women are actively<br />

involved themselves in storing rice grains (Sumathi and Budhar<br />

2003). Women farmers receive less than 5% of extension services<br />

worldwide and the priorities of women farmers are rarely<br />

reflected in agricultural research or national policies, and the<br />

role of women as agricultural producers is still largely unrecognized<br />

and has not been addressed (LEISA 2002). Hence, we<br />

conducted a study among women farmers to find out their role<br />

in storing paddy grains with different storage practices and<br />

also to find out their needs for effective storing of grains.<br />

Materials and methods<br />

The study was conducted in Vellore District of Tamil Nadu,<br />

India, w<strong>here</strong> rice is grown on about 72,000 ha and t<strong>here</strong> are 20<br />

blocks in this district. Among these blocks, Tirupattur block<br />

was randomly selected for collection of data. This block consists<br />

of 32 revenue villages w<strong>here</strong>in agriculture is the main<br />

source of livelihood and rice is grown in three distinct seasons:<br />

the dry (Jul-Nov), wet (Dec-Mar), and summer season<br />

(Feb-May). Employing a proportionate sampling method, 100<br />

respondents (farm women) representing small farms (0.1 to 1<br />

ha) and big farms (>1 ha) were selected, out of which 50 were<br />

small-farm women and another 50 big-farm women. Thus, a<br />

sample of 100 women farmers (20 from each village) was selected<br />

randomly from five randomly selected villages. Most<br />

of the women farmers cultivate relatively small farms (0.1 to 1<br />

ha) and some who have more land (>1 ha) live in clusters.<br />

Through a well-structured interview schedule, the data on adoption<br />

of women farmers for storing rice grains in different storage<br />

methods and feedback on suggestions to overcome problems<br />

in adoption were collected. The relevant data gat<strong>here</strong>d<br />

were tabulated, processed, and subjected to statistical tests of<br />

percentage analysis.<br />

Results and discussion<br />

Adoption level of storage methods<br />

Among 12 practices, four (Table 1)—drying grains before storage,<br />

keeping bags horizontally, keeping bags on planks and<br />

leaving passages, and using metal traps for rodent control—<br />

were found to have been adopted by a majority of the farm<br />

women. Upadhay and Gupta (1987) also stated that the majority<br />

of rural women possessed sufficient knowledge of grain<br />

320 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. Distribution of respondents according to their practice in the adoption<br />

of storage methods.<br />

Small-farm Big-farm Total<br />

Recommended practices women women<br />

(no.) (%) (no.) (%) (no.) (%)<br />

Drying grains before storage 50 100 50 100 100 100<br />

Impregnated bags – – 6 12 6 6<br />

Polythene-lined bags 26 52 25 50 51 51<br />

Keeping bags on planks and 36 72 40 80 76 76<br />

leaving passages<br />

Pretreatment of storage 5 10 15 30 20 20<br />

structures<br />

Keeping bags horizontally 50 100 50 100 100 100<br />

Metal storage bins 15 30 3 6 18 18<br />

Tin-cone plates for storage 9 18 21 42 30 30<br />

structures<br />

Fumigation by ethylene 1 2 4 8 5 5<br />

dibromide ampules<br />

Metal traps for rodent control 43 86 45 90 88 88<br />

Anticoagulants for rat control 7 14 18 36 25 25<br />

Prebaiting and poison baiting<br />

for rats with zinc phosphide 21 42 34 68 55 55<br />

storage. All these practices required less cost and skill, which<br />

might be the reason for their better adoption. Nearly 50% of<br />

the farm women followed the use of polythene-lined bags and<br />

prebaiting and poison baiting with zinc phosphide against rats.<br />

This practice is dangerous to domestic animals, has a high cost<br />

of technology, and has no technical guidance. The rest of the<br />

practices had a very low level of adoption because they were<br />

capital-intensive and demanded skill in practicing them. A<br />

considerably higher percentage of nonadoption was found in<br />

other storage practices for paddy grains because these practices<br />

had a high cost, were complex, a local substitute was<br />

available, and knowledge on storage structures and technical<br />

guidance were lacking.<br />

The big-farm women had a higher percentage of adoption<br />

of storage practices such as impregnated bags, pretreatment<br />

of storage structures, tin-cone plates for storage structures,<br />

and anticoagulants for rat control since the big-farm<br />

women can afford the costs of these storage methods. However,<br />

the percentage of usage by small-farm women of metal<br />

storage bins was high since these structures were given to the<br />

small-farm women only at the subsidized rate.<br />

Suggestions for increasing the efficiency<br />

of storing grains<br />

The majority of the small-farm women (76%) suggested providing<br />

financial assistance on a credit basis for the purchase of<br />

better storage structures such as metal bins. Also, 72% of the<br />

farm women suggested having subsidized facilities for the same<br />

purpose and 34% of the respondents wanted special campaigns<br />

on storage structures (Table 2) since the percentage of suggestions<br />

was more than with big-farm women. On the other hand,<br />

the big-farm women suggested an adequate (70%) and timely<br />

supply of materials (64%). Half of the farm women needed<br />

timely technical guidance on postharvest technology of paddy<br />

(52%) since these women farmers are economically stable and<br />

hence need a timely supply of materials as well as technical<br />

guidance.<br />

In general, most of the farm women suggested financial<br />

assistance on a credit basis (54%) and a timely supply of materials<br />

(52%), followed by providing a subsidized facility<br />

(48%), an adequate supply of materials (47%), and timely technical<br />

guidance (44%). Less than 30% of the farm women<br />

wanted the research system to develop low-cost storage structures<br />

to prevent grain losses from infestation and arrange campaigns<br />

on scientific storage structures.<br />

The results imply that, in many parts of the world, t<strong>here</strong><br />

is an increasing trend in the involvement of farm women in<br />

agriculture and other allied sectors and these women farmers<br />

have more responsibilities, especially in the Indian agricultural<br />

system. Rural women who are contributing to the rural<br />

economy should be supported by the government (Narayana<br />

2002). Hence, for a balanced and sustainable growth of rural<br />

India, women’s role in the developmental process and activities<br />

should be recognized and they should be adequately supported<br />

as were the men farmers to achieve gender democracy<br />

and guarantee food security.<br />

References<br />

Gandhi NK. 1983. Stepping up rural warehousing. Kurukshetra<br />

31(22):18-20.<br />

LEISA. 2002. Women in agriculture. Magazine on Low External<br />

Input Sustainable Agriculture (LEISA) India 4(4):4-5.<br />

Mishra B. 2004. Exploring new opportunities: survey of Indian agriculture.<br />

The Hindu. p 29-31.<br />

Session 10: Postharvest technology for efficient processing and distribution of rice 321


Table 2. Distribution of respondents according to their suggestions to overcome<br />

problems in adoption.<br />

Small-farm Big-farm Total<br />

Suggestions a women women<br />

(no.) (%) (no.) (%) (no.) (%)<br />

Financial assistance on a credit 38 76 16 32 54 54<br />

basis<br />

Providing a subsidized facility 36 72 12 24 48 48<br />

Timely supply of materials 20 40 32 64 52 52<br />

Timely technical guidance 18 36 26 52 44 44<br />

Arranging special campaigns 17 34 8 16 25 25<br />

on storage structures<br />

Adequate supply of materials 12 24 35 70 47 47<br />

Developing low-cost storage 10 20 13 26 23 23<br />

structures<br />

a Multiple responses.<br />

Narayana RL. 2002. Women in agriculture. Magazine on Low External<br />

Input Sustainable Agriculture (LEISA) India 4(4):30.<br />

Sumathi P, Budhar MN. 2003. Extent of women’s involvement in<br />

Indian rice cultivation. Int. <strong>Rice</strong> Res. Notes 28(1):74-76.<br />

Upadhay M, Gupta P. 1987. Adoption of selected home making by<br />

rural women. Indian J. Extn. Edn. 23(1&2):76-78.<br />

Wrap-up of Session 10<br />

Session 10 included a wide range of interests from conditioning<br />

or primary processing of rice to safety and environmental matters.<br />

Professor P. Chattopadhyay from India reported on the<br />

changing scenario in postharvest technology in India, whose rice<br />

production and economy are growing rapidly. From Japan, the<br />

latest technological information on drying, milling, and storage<br />

facilities was introduced. Relatively new topics such as the use<br />

of by-products, residual agrochemical inspection, life-cycle inventory<br />

analysis, and so forth were also presented. To meet these<br />

global needs, the importance of new concepts for rice breeding<br />

was pointed out from the U.S. R.G. Manalili from the Philippines<br />

mentioned that the infrastructure surrounding rice production was<br />

essential for improving international competitiveness in rice production<br />

as well as in technological renovations.<br />

Session participants reached the following conclusions:<br />

1. The covering area of postharvest or postproduction technology<br />

is becoming wider. This includes safety, environmental,<br />

and socioeconomic issues.<br />

Notes<br />

Authors’ address: Regional <strong>Research</strong> Station, Tamil Nadu Agricultural<br />

University, Paiyur 635112, Krishnagiri Dist., Tamil Nadu,<br />

India, e-mail: mnbudhar@rediffmail.com.<br />

2. Postharvest technology can improve production efficiency<br />

more easily than other preharvest measures such<br />

as the development of new arable land or a new variety.<br />

3. T<strong>here</strong>fore, more emphasis should be given to postharvest<br />

technology and related matters to achieve well-balanced<br />

production after examining productivity, quality, safety,<br />

economic, and environmental issues.<br />

Two outstanding posters were chosen: “Postharvest of rice:<br />

the role of farm women in storing grains by different storage practices”<br />

by P. Sumathi from India and “The role of proteins in textural<br />

changes of cooked rice during rice storage” by T. Ohno from<br />

Japan. The first dealt with women’s labor in postharvest practices<br />

during the storage of rice in rural areas of India. It was<br />

understood that the role of women’s labor would strongly affect<br />

the future improvement of postharvest practices in developing<br />

countries.<br />

322 <strong>Rice</strong> is life: scientific perspectives for the 21st century


SESSION 11<br />

Enhancing the multifunctionality<br />

of rice systems<br />

CONVENER: Y. Tsutsui (NIRE)<br />

CO-CONVENER: K. Yamaoka (NIRE)


Multifunctional roles of paddy irrigation in monsoon Asia<br />

Takao Masumoto<br />

Approximately 54% of the world’s population is thought to<br />

live in the regions known as humid Asia or the Asian monsoon<br />

region, which constitute only approximately 14% of the world’s<br />

land area. The majority of Asia’s massive population is supported<br />

by intensive paddy rice cultivation, which originates<br />

from the warm and humid environment and offers high land<br />

productivity because of irrigation.<br />

Paddy rice cultivation in the Asian monsoon region is<br />

not only an excellent form of agriculture offering high land<br />

productivity; it is also seen as a sustainable and environmentally<br />

friendly economic activity that suits the climatic and topographical<br />

conditions of this region. This economic activity<br />

has continued to evolve for thousands of years across various<br />

regions, as witnessed by the archaeological traces of 7,000-<br />

year-old rice cultivation obtained in China. Even today, paddy<br />

rice cultivation is a unique way of life supported by the endeavors<br />

of people living in harmony with water. Moreover,<br />

paddies also make life more convenient for city dwellers by<br />

reducing floods, fostering groundwater, etc. These “products”<br />

cannot be sold in any market, and their functions have been<br />

referred to as “the multifunctional roles of paddy irrigation”<br />

in this study.<br />

In this paper, the multifunctional roles of paddy irrigation<br />

are illustrated by comparing the hydrological environments,<br />

forms of irrigation practiced, and characteristics of paddies<br />

in humid regions with those in the arid and semiarid regions.<br />

Further, the paper examines the quantitative or economic<br />

methods for evaluating these multifunctional roles and formulates<br />

policy proposals for Japan and the rest of the world with<br />

a view toward solving water-related problems.<br />

Characteristics of paddy irrigation in monsoon Asia<br />

Definition of Monsoon Asia and characteristics<br />

of climatologic and hydrologic environment<br />

Musiake (2001) asserts that regions such as monsoon Asia<br />

should be characterized by the region’s uniqueness (including<br />

the nature of human activity), in addition to the climatic conditions<br />

that have been emphasized in the past. Thus, this paper<br />

follows his new classification. The Asia monsoon region embraces<br />

the Indian Ocean to the south, the expansive region of<br />

Tibet, the Himalayan mountain mass and continental China to<br />

the north, and the Pacific Ocean to the east. Most of it consists<br />

of high-precipitation warm regions that have annual rainfall in<br />

excess of 1,500 mm, influenced by low pressure and monsoons<br />

accompanied by westerly winds. Meanwhile, the water balance<br />

(calculated by subtracting annual potential evapotranspiration<br />

from annual precipitation) generally exceeds 500 mm.<br />

Characteristics of paddy irrigation in monsoon Asia<br />

The principal grain crop in monsoon Asia is rice. In fact, nearly<br />

90% of the world’s rice is produced in the countries of this<br />

region. Monsoon Asia could be called a virtually homogeneous<br />

region in that paddy rice cultivation extends over almost the<br />

whole of its area. Generally speaking, regions with annual precipitation<br />

of less than 400 mm are classified as perennial irrigation<br />

zones, those with precipitation from 400 to 1,000 mm<br />

as unstable irrigation zones, and those with more than 1,000<br />

mm as replenishment irrigation zones. Of these, the whole of<br />

monsoon Asia belongs to the last classification. What is more,<br />

the Asian monsoon region is also characterized by large seasonal<br />

and short-term fluctuations in the supply of water resources,<br />

as evident in the distinct dry and rainy seasons.<br />

Paddy irrigation in arid and semiarid regions<br />

Overview<br />

As characteristics of paddy irrigation in the world’s arid and<br />

semiarid regions, cases from the United States and Australia<br />

are discussed. In the U.S., paddy zones extend along the Mississippi<br />

River and in five southern states as well as California.<br />

The rice cultivated area changes from year to year, from<br />

300,000 to 1,500,000 ha. In Australia, about 100,000 ha of<br />

paddy fields are concentrated in the Murray and Murrumbidgee<br />

River basins. With annual precipitation of about 400 mm, paddy<br />

irrigation is practiced t<strong>here</strong>.<br />

Examples<br />

The state of California in the U.S. is a semiarid region with<br />

rainfall in winter but little in summer. The average annual precipitation<br />

is 575 mm, and agriculture t<strong>here</strong> would be impossible<br />

without irrigation facilities. Paddies and water-supply<br />

channels are used as retarding basins and diversion channels<br />

for floodwater. Paddies also provide sanctuaries for migrating<br />

birds as well as for duck hunting. Although some features of<br />

paddy rice culture in California are similar to those of monsoon<br />

Asia, the California paddies and water distribution and<br />

the drainage system do not have the all-encompassing multifunctional<br />

roles of paddy irrigation in monsoon Asia. In the<br />

rice cultivation zones along the Murray River in Australia,<br />

meanwhile, some floodwater is stored during high flows. However,<br />

paddies are not seen as having a function for relief from<br />

flooding. Furthermore, groundwater percolation from paddies<br />

causes an accumulation of soil salinity in surrounding nonrice<br />

arable land because the shallow groundwater is saline. In terms<br />

of the sustainability of agriculture, this could be seen as an<br />

example of a negative impact being exerted on a region’s water<br />

resources.<br />

324 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Paddy storage capacity, S (mm)<br />

200<br />

Catherine typhoon<br />

Status quo<br />

S 0<br />

D 0<br />

Irrigation period<br />

Fukuoka headwork<br />

Category<br />

150<br />

1/100-y return period<br />

L<br />

Block by gates<br />

B 1 and drops<br />

Characteristics<br />

100<br />

50<br />

0<br />

0<br />

1/50-y RP<br />

1/10-y RP<br />

2,000<br />

4,000<br />

Drainage (conveying) capacity, D (m 3 s –1 )<br />

Fig. 1. Drainage capacity (urban area) and<br />

storage capacity of paddies (Kinu River),<br />

(Masumoto 2002).<br />

St.2<br />

G<br />

C<br />

U 1<br />

I 3<br />

S mv<br />

A<br />

Main irrigation<br />

channel 1<br />

G s A Ecosystem in<br />

plateaus<br />

G<br />

C<br />

U 1<br />

D 3<br />

of channel unit<br />

S mv<br />

A<br />

5 4 3 2 1 0<br />

Ecosystem<br />

evaluation by<br />

hydrologic<br />

indices<br />

Evaluated points<br />

U 5<br />

I 3<br />

Methods of quantifying the multifunctional roles<br />

of paddy irrigation<br />

Kokai<br />

River<br />

U 2<br />

D 3<br />

S mv<br />

A<br />

Branch<br />

channel<br />

C<br />

A<br />

Definition of multifunctional roles<br />

In 2001, the Science Council of Japan delivered a report on<br />

the multifunctional roles of agriculture and forests to the Minister<br />

of Agriculture, Forestry, and Fisheries. The report included<br />

a list of categories connected with the multifunctional roles of<br />

paddy irrigation. Based on this, the multifunctional roles of<br />

paddy field irrigation are defined as (1) water cycle control<br />

functions (flood prevention, groundwater recharge, prevention<br />

of soil erosion), (2) environmental load control functions (water<br />

purification, processing of organic waste, climate modification),<br />

(3) nature formation functions (biodiversity, landscapes),<br />

and (4) social culture formation functions (health and<br />

recreation, participatory learning).<br />

Specific examples<br />

Each function mentioned above is summarized in the report<br />

(Masumoto 2004). Discussions on the multifunctional roles of<br />

agriculture are also under way and attempts are being made<br />

not only to define multifunctional roles qualitatively but also<br />

to evaluate them quantitatively. Here, some of the latest results<br />

are introduced below.<br />

Flood prevention function. When changes in runoff volume<br />

due to the abandonment of paddy farming were measured<br />

in mountainous parts of the Hokuriku region, an increase in<br />

total runoff and peak runoff for all observed floods was observed<br />

at times when paddy fields were wet (Masumoto et al<br />

1997). Meanwhile, as examples in which low-lying paddy zones<br />

contribute to flood prevention in river basins, research has been<br />

done on the Ogura basin in Kyoto, the Tomari basin of the<br />

Natsu River system in Miyagi Prefecture, and the Mekong River<br />

basin (Masumoto 1998, 2003a, Masumoto et al 2002).<br />

Attempts have been made to evaluate the<br />

abovementioned functions at the basin level to propose meth-<br />

Oka<br />

headwork<br />

St.1<br />

Main irrigation<br />

channel 3<br />

Drainage river<br />

(Nakadori River)<br />

U 3<br />

G<br />

A<br />

Branch<br />

irrigation<br />

channel<br />

Iatami<br />

gate<br />

Branch<br />

drainage<br />

channel<br />

Fig. 2. Evaluation of irrigation and drainage network for fish ecosystem<br />

(Fukuoka headwork area, irrigation period), (Masumoto et<br />

al 2004).<br />

ods of evaluating flood prevention functions at the basin level<br />

in macro scales. The relationship between discharge in urban<br />

rivers and flood prevention capability of suburban paddies can<br />

be defined as the relation between drainage and storage capabilities<br />

(Masumoto 2003b). Figure 1 shows an example of this<br />

evaluation method applied to the basin of the Kinu River, a<br />

tributary of the Tone River in the north of the Kanto region.<br />

Ecosystem preservation function. A survey has been<br />

made of the ecosystem maintenance functions in<strong>here</strong>nt in paddy<br />

irrigation in the Kokai River of the Tone River system in Japan<br />

(Masumoto et al 2004). For this, a network map for ecosystem<br />

evaluation was created using, among other indicators,<br />

the state of connection of each channel in a network of irrigation<br />

and drainage channels (Fig. 2). The condition of fish in<br />

the target area was also evaluated by using time and space<br />

hydrologic indices proposed.<br />

D<br />

B 1<br />

G<br />

A<br />

Main irrigation<br />

channel 2<br />

U 4<br />

D 1 Ecosystem<br />

in<br />

C m<br />

B 1 plateaus<br />

Session 11: Enhancing the multifunctionality of rice systems 325


Economic evaluation of the multifunctional roles<br />

of paddy irrigation<br />

The benefits brought about by the external economy intrinsic<br />

to the economic activity of agriculture are public properties to<br />

be enjoyed by all the people of a nation. Methods applied to<br />

evaluate the scale of these benefits in economic terms are the<br />

substitution method, CVM (contingent valuation method), the<br />

hedonic method, the travel cost method, and the direct method.<br />

When evaluation is difficult to achieve by these methods, the<br />

tendency has been for the CVM and other methods to be<br />

adopted.<br />

So far, the multifunctional roles of paddies, upland fields,<br />

and rural areas throughout Japan were evaluated and their results<br />

produced values ranging from 4.1 to 11.9 trillion yen for<br />

functions that can be quantified. The following functions, not<br />

included in these calculation results, are calculated through<br />

economic evaluation.<br />

As a method of economic evaluation for flood prevention<br />

functions, attempts have been made to evaluate the flood<br />

storage capability of a paddy area by substituting it with the<br />

volume of a retarding basin. Using a method based on questionnaire<br />

surveys (stated choice method), meanwhile, methods<br />

of analysis are moving toward greater refinement by increasing<br />

the targeted range (functions), and t<strong>here</strong> is a progressive<br />

shift from CVM toward choice experiments (choice-based<br />

conjoint analysis: contingent ranking method). With choice<br />

experiments, however, several situations are evaluated for comparison.<br />

Policy proposals for Japan and the international community<br />

Development, economic activity (e.g., agriculture),<br />

and environmental preservation<br />

Agriculture, of course, is a type of economic activity, but the<br />

water supply and drainage systems that exist in rural regions<br />

could also help protect a region’s ecosystems, for example, by<br />

providing nursery grounds for fish in connecting rivers. Many<br />

examples are demonstrating that agricultural development is<br />

not necessarily in opposition to environmental preservation.<br />

Rather, we would assert that several points still require improvement<br />

in terms of protecting ecosystems. The reason for<br />

this is that drainage channels fed by urban drainage continue<br />

to flow throughout the year, while water supply channels have<br />

no flow of water outside the irrigation period.<br />

Sustainable water-recycling agriculture<br />

The difference between paddy field agriculture in arid regions<br />

and that in monsoon Asia needs to be clarified. Namely, t<strong>here</strong><br />

are huge differences in paddy irrigation between those regions.<br />

For paddy fields in the arid and/or semiarid regions, excessive<br />

irrigation to cope with arid climates causes salt damage due to<br />

a rise in groundwater levels and this in turns leads to external<br />

diseconomy. In Japan and other highly humid zones, on the<br />

other hand, the supply of groundwater from paddy fields can<br />

be evaluated as an external economy in that it builds up groundwater<br />

resources.<br />

Introduction of external economic evaluation<br />

(basin management) and sharing of water<br />

management costs<br />

Studies should be made from the perspective of the basin as a<br />

whole, rather than just being aimed at the direct beneficiaries<br />

to agriculture. If this, a case of external economic evaluation,<br />

were studied in terms of the basin as a whole, it could also be<br />

considered from the perspective of the internal economy.<br />

Numerous facilities have been developed in agricultural<br />

and rural development projects to date. In the past, facilities<br />

for water management in regions and basins mainly concerned<br />

with agriculture used to be developed upon applications from<br />

agricultural concerns. The development was mainly undertaken<br />

by farmers and land improvement districts, which also bore<br />

the maintenance and management costs. However, urbanization<br />

has opened its way to all parts of the country in recent<br />

years. In many cases, farmers also bear the costs for operating<br />

and maintaining district drainage and drainage channels in<br />

suburban agricultural zones. These costs should ordinarily be<br />

borne by urban residents. In other words, t<strong>here</strong> should be a<br />

sharing of management costs commensurate with the manifestation<br />

of multifunctional roles of paddy irrigation, partly as a<br />

consideration for providing comfort to local residents in urbanized<br />

areas. Legal support systems also need to be developed<br />

to address this.<br />

Basin management during excessive flooding<br />

In paddy-dominant basins w<strong>here</strong> pump drainage is practiced<br />

in low-lying areas, flood plains for its connecting main river<br />

are designed for the capacities on a 100-year probability scale.<br />

The maximum drainage volume for agricultural facilities is<br />

normally assumed on a 10-year probability scale (in some recent<br />

cases, 20–30 years). Thus, runoff that exceeds the drainage<br />

capacity on a scale of 10 years cannot drain outside the<br />

basin, and is forcibly stored in drainage channels and/or paddies.<br />

In other words, farmlands that include agricultural drainage<br />

channels and paddies have the function of storing floodwater<br />

for drainage rivers, and, as a result, could be said to help<br />

reduce the risk of flooding in main rivers downstream w<strong>here</strong><br />

urban areas extend.<br />

References<br />

Masumoto T. 1998. Paradigm shift in the evaluation of water storage<br />

function of paddies and in watershed management. J. Jpn.<br />

Soc. Hydrol. Water Res. 11(7):711-722. (In Japanese with<br />

English abstract.)<br />

Masumoto T. 2003a. Flood prevention function of paddies in monsoon<br />

Asia. Proceedings of Japan/OECD Expert Meeting on<br />

Agriculture and Land Conservation: Developing Indicators<br />

for Policy Analysis, Kyoto, Japan, May 2003. p 91-98.<br />

326 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Masumoto T. 2003b. Indices to evaluate flood prevention function<br />

of paddies. Proceedings of Japan/OECD Expert Meeting on<br />

Agriculture and Land Conservation: Developing Indicators<br />

for Policy Analysis, Kyoto, Japan, May 2003. p 159-164.<br />

Masumoto T. 2004. Multi-functional roles of paddy irrigation in<br />

monsoon Asia. J. JSIDRE. 72(7):11-16. (In Japanese.)<br />

Masumoto T, Kubota T, Matsuda S. 2002. An integrated approach to<br />

use multifunctional roles of paddies in basin-wide flood and<br />

water-use management. Electric Transactions of the 18th <strong>International</strong><br />

Congress on Irrigation and Drainage (ICID).<br />

Q51R12.07:1-16.<br />

Masumoto T, Kubota T, Matsuda S, Takagi, A. 2004. An evaluation<br />

method of water resources in paddy regions to preserve ecological<br />

environments. Technical Report of the National <strong>Institute</strong><br />

for Rural Engineering. No. 202:81-90. (In Japanese with<br />

English abstract.)<br />

Masumoto T, Takaki K, Yoshida S. Adachi K. 1997. Effects of abandoned<br />

paddies in hilly rural areas on runoff. Trans. JSIDRE.<br />

189:59-68. (In Japanese with English abstract.)<br />

Musiake K. 2001. Hydrology and water resources in monsoon Asia:<br />

a consideration of necessity to organize “Asian Association<br />

of Hydrology and Water Resources.” In the Proceedings of<br />

the Symposium on Innovation Approaches for Hydrology and<br />

Water Resources Management in Monsoon Asia, Tokyo, Japan.<br />

p 1-11.<br />

Notes<br />

Author’s address: National <strong>Institute</strong> for Rural Engineering, 2-1-6<br />

Kan-nondai, Tsukuba, Ibaraki 305-8609, Japan, e-mail:<br />

matsumoto@nkk.affrc.go.jp.<br />

Accounting for culture in paddy cultivation:<br />

toward a broader definition of “livelihood”<br />

David Groenfeldt<br />

Paddy cultivation forms the basis of traditional Southeast Asian<br />

societies and the livelihoods of the people who comprise those<br />

societies. Historically speaking, paddy cultivation has always<br />

(at least for several millennia) been multifunctional—providing<br />

not only the raw material for subsistence and trade but also<br />

serving as the central focus for family and community life as<br />

well as spiritual and religious expression. While times have<br />

certainly changed, this paper suggests that the multifunctional<br />

nature of paddy cultivation continues to be important, and that<br />

our concept of rural “livelihood” should incorporate these cultural<br />

dimensions.<br />

Traditional versus modern paddy cultivation<br />

Twentieth-century economic developments changed the wellintegrated<br />

world of paddy farmers and imposed new pressures<br />

while offering new options from modern agriculture. In Bali,<br />

for example, farmers no longer had to follow the traditional<br />

cropping calendar imposed by the temple priests. Thanks to<br />

new crop varieties from the <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong><br />

(<strong>IRRI</strong>) and new infrastructure from the Asian Development<br />

Bank (ADB)-financed Bali Irrigation Project, farmers<br />

were encouraged to adopt modern methods that treat farming<br />

more as agri-business rather than agri-culture.<br />

The Balinese case has become a symbol of the dangers<br />

of ignorantly tinkering with a carefully evolved agricultural<br />

system. The disruption of coordinated planting times allowed<br />

insect populations to spike, causing severe crop losses (Lansing<br />

1991). The project-imposed diversion weirs were incompatible<br />

with customary water rights, resulting in conflicts among<br />

farmers (ADB 1998). The lesson from Bali, and from many<br />

other cases of externally imposed agricultural strategies, is that<br />

traditional farming systems are often highly evolved sociotechnical<br />

systems, and the introduction of any improvements<br />

must be attempted very carefully, taking into account the potential<br />

cascade of multiplier effects from seemingly small<br />

changes.<br />

Respect for the technical sophistication of traditional<br />

farming systems has now become an accepted tenet within the<br />

current paradigm of agricultural development. Indigenous technical<br />

knowledge even has its own acronym—ITK. And the<br />

concept of rural livelihoods goes even further in capturing the<br />

complex interactions of the farming system with the larger<br />

economic context of handicrafts, wage labor, remittances from<br />

abroad, etc. The legitimacy that the development profession<br />

has grudgingly accorded to the economic strategies of rural<br />

farm families, however, has not been extended to the overall<br />

cultural “lifeways” of the people themselves. Traditional beliefs<br />

in river spirits and rice gods are dismissed as superstitions.<br />

Local customs about diet, nutrition, and health are viewed<br />

with suspicion, if not ridicule. And traditional values referring<br />

to time and money are met with exasperation by Western advisers<br />

preaching the virtues of market-based capitalism.<br />

The conventional model<br />

According to the conventional model of development, traditional<br />

family and community-based modes of paddy cultivation<br />

are doomed to an eventual demise in the face of competition<br />

from industrial-style producers. While many observers of<br />

economic development—myself included—are uncomfortable<br />

with the social and cultural costs of economic change, the process<br />

is generally accepted as both necessary and inevitable.<br />

Session 11: Enhancing the multifunctionality of rice systems 327


After all, the growing population of the world needs to be fed,<br />

and the most efficient arrangements for producing food must<br />

be followed.<br />

This conventional model of development is applied to<br />

paddy cultivation and rural livelihoods as a sort of economic<br />

determinism that requires changes in cultural values toward<br />

more economic thinking. Traditional societies are advised to<br />

“get with the program,” give up their traditional customs, and<br />

adopt Western-style materialism. The only alternative is poverty.<br />

Another approach: happiness<br />

The message of this paper is that t<strong>here</strong> is a middle way, and it<br />

is a far more interesting way to live than the materialistic extremism<br />

advocated by conventional development experts. Life<br />

is more than money, and livelihoods are more than economics.<br />

Paddy cultivation is not only an economic strategy; it is a part<br />

of a way of life that needs to be considered in those very broad<br />

terms.<br />

The concept of gross national happiness (GNH), which<br />

forms the center-piece of Bhutan’s development policies, captures<br />

the broad dimensions of life that I feel need to be incorporated<br />

into our concept of livelihoods. T<strong>here</strong> are four pillars<br />

to the concept of GNH as defined in the Bhutan context: (1)<br />

economic development, (2) cultural heritage, (3) preservation<br />

and sustainable use of the environment, and (4) good governance.<br />

It is significant that economic development is listed<br />

first. The dominance of economics is natural and justified, but<br />

as a means, and not an end in itself. The dimension I will focus<br />

on in this paper is that of cultural heritage. The dimension of<br />

environment is addressed in other conference papers. The governance<br />

dimension is also relevant to paddy cultivation (e.g.,<br />

irrigator associations as a type of local governance) but is<br />

omitted from this discussion in the interest of maintaining focus.<br />

Let me now turn to cultural heritage, which I will gloss<br />

with the more general term “culture.”<br />

Culture and livelihoods<br />

How does paddy agriculture contribute to the cultural dimensions<br />

of rural life I will subdivide these dimensions into four<br />

categories: (1) rural social structure at the family and community<br />

level, (2) cultural identity, (3) spiritual and religious life,<br />

and (4) aesthetic beauty.<br />

Social structure<br />

The irrigation systems used for paddy cultivation largely determine<br />

the location of village settlements. In Sri Lanka, villages<br />

grew up around the reservoirs (tanks) constructed for<br />

irrigating paddy and other crops. In Bali, village lands are defined<br />

by irrigation canals that are linked to larger networks<br />

supervised by priests. In Bhutan, the villages typically take<br />

water from a stream diversion built and maintained by farmers<br />

from that village. The paddy irrigation infrastructure serves as<br />

a physical representation of the village community. Family and<br />

community life are organized around the cultivation cycle, with<br />

periodic labor exchange for transplanting and harvesting, and<br />

social gatherings tied to agricultural rituals. This dimension<br />

can be thought of as the social capital of paddy agriculture.<br />

The organizational depth of these social interactions serves<br />

multiple functions beyond paddy cultivation (e.g., credit circles,<br />

political action, etc.) while also providing social “happiness”<br />

directly through the satisfaction of social interaction.<br />

Cultural identity<br />

The interconnectedness of food, farming, and identity is fundamental<br />

to traditional societies as well as modern ones. An<br />

American Indian farmer explained this relationship in kinship<br />

terms: “The [traditional crops of] corn, beans, and squash plants<br />

are like our children. We don’t have to live with our children,<br />

but life is much richer and happier when we do.” Traditional<br />

cultural identities are often seen as a luxury that modernity can<br />

no longer support, or even as a threat to national integration.<br />

The importance of traditional identity is typically appreciated<br />

only under the looming cloud of cultural extinction. Yet, from<br />

a psychological perspective, cultural identity is fundamental<br />

to emotional balance and personal happiness. Traditional foods<br />

and crop varieties are a key part of this happiness. What is a<br />

Sri Lankan—or Bhutanese, or Balinese—meal without rice<br />

And, more specifically, local varieties of rice, prepared in certain<br />

traditional ways Even in many industrial societies (such<br />

as Japan and France), w<strong>here</strong> the farming population has been<br />

reduced to a fraction of the work force, the identity with particular<br />

foods and farming practices continues to be valued.<br />

Religion<br />

The tasks of farming itself can be a spiritual practice. The interaction<br />

with plants and animals, the preparation of the soil,<br />

diverting of water, all have meanings that are systematized<br />

through rituals and ceremonies throughout Asia. The Water<br />

Temples of Bali are famous examples of merging religion and<br />

paddy cultivation, but less dramatic illustrations are everyw<strong>here</strong>,<br />

from the Hanuman deity guarding a tubewell in India<br />

to prayers on the threshing floor in Sri Lanka. The daily experience<br />

of spiritual life is tied to the cultivation process.<br />

Aesthetic<br />

The landscape value of paddy fields is important to both rural<br />

producers and urban consumers. In some cases, these values<br />

may be harnessed through eco-tourism (as some resorts in Bali<br />

have attempted to do), but, in most other cases, the agrarian<br />

beauty of the landscape is a type of common resource provided<br />

free to the observer. Another type of aesthetic benefit<br />

provided by traditional paddy cultivation is the rice itself, which<br />

may be valued for its culinary qualities (taste, texture) as well<br />

as for its cultural heritage value (as a symbol of a particular<br />

region or ethnic group). This is why farmers often grow one<br />

variety of rice for selling, while growing lower-yielding traditional<br />

varieties for home consumption.<br />

328 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Implications for agricultural policy<br />

Both farmers and urban food consumers share an interest in<br />

preserving certain dimensions of traditional paddy cultivation,<br />

for the simple reason that these aspects contribute to their happiness.<br />

Is this a valid basis for selecting among development<br />

options The idea that development is exclusively the domain<br />

of economics has emerged for historical reasons, not logical<br />

ones. What would development policies look like if psychologists,<br />

or priests, were employed as the advisers The policies<br />

would probably be quite similar to Bhutan’s policy of gross<br />

national happiness, which closely reflects the Buddhist heritage<br />

of that country.<br />

Happy paddy farmers Happy rice consumers Are these<br />

realistic objectives for agricultural policy Perhaps we should<br />

turn the question around: If agricultural policy is not oriented<br />

toward increasing general happiness, then what is its purpose<br />

And if policies are indeed oriented to increasing happiness,<br />

then the dimensions of happiness need to be addressed.<br />

References<br />

ADB (Asian Development Bank). 1998. Re-evaluation of the Bali<br />

Irrigation Sector Project in Indonesia. December.<br />

Lansing SJ. 1991. Priests and programmers. Princeton, N.J. (USA):<br />

Princeton University Press.<br />

Notes<br />

Author’s address: Independent Consultant, Santa Fe, New Mexico<br />

(USA), e-mail: DGroenfeldt@aol.com.<br />

The need to keep irrigated rice culture sustainable<br />

Nyoman Sutawan<br />

<strong>Rice</strong> is the most important staple crop for many people in Asia,<br />

especially in East and Southeast Asia. It has a long history of<br />

cultivation, probably for more than seven millennia. Its cultivation<br />

plays a significant role in Asia’s customs and religions.<br />

In the year 2000, the world rice harvest area was around 152.0<br />

million hectares. Of this, Asia contributed nearly 90%. Global<br />

rice production was 597.2 million tons of rough rice and Asia<br />

as a whole produced more than 91% (Kim 2001).<br />

For many countries, rice is not merely an economic good;<br />

it is also a social, cultural, religious, and even political good.<br />

A rice shortage could create national instability. Moreover, the<br />

world rice market is highly volatile and relying upon such an<br />

unstable rice market could be quite risky for national food security.<br />

No wonder that many countries still insist on adopting<br />

a rice self-sufficiency policy. This implies that preserving rice<br />

culture seems to be of primary importance.<br />

This paper tries to (1) propose a concept of sustainable<br />

irrigated rice culture, (2) raise arguments for preserving irrigated<br />

rice culture, and (3) recommend relevant policy measures<br />

to preserve irrigated rice culture.<br />

Proposed concept of sustainable irrigated rice culture<br />

T<strong>here</strong> are a lot of definitions or concepts of sustainable agriculture.<br />

Pakpahan (1995) has cited several definitions of sustainable<br />

agriculture but those will not be repeated <strong>here</strong>. Suffice<br />

it to say that most of the definitions seem to merely emphasize<br />

more the environmental and agro-technological aspects.<br />

Since land and irrigation water are indispensable for<br />

irrigated agriculture, it seems necessary to see sustainability<br />

of agriculture, especially irrigated rice culture, from a rather<br />

different point of view.<br />

Irrigated rice culture getting water from an irrigation<br />

system can be viewed to possess several interrelated elements.<br />

Sustainable irrigated rice culture should be perceived <strong>here</strong> as<br />

a prolonged existence and functioning of several important<br />

interrelated elements of irrigated rice culture. In other words,<br />

sustainability of irrigated rice culture should encompass the<br />

sustainability of the following: (1) the irrigators’ association<br />

or institution (institutional sustainability), (2) irrigation networks<br />

(technical sustainability), (3) agricultural production<br />

(economic sustainability), (4) irrigated land ecosystem (ecological<br />

sustainability), and (5) socio-cultural values linked to<br />

rice cultivation (socio-cultural sustainability).<br />

However, the sustainability of those five elements of irrigated<br />

rice culture also largely depends on the local natural<br />

environment, especially the upstream watershed and the quality<br />

of river water upstream (environmental sustainability),<br />

which are external to the irrigated rice culture concerned. An<br />

individual irrigation system for rice cultivation is also an element<br />

or subsystem of the entire system along a river course.<br />

This implies that the performance of the individual irrigation<br />

system or irrigated paddy culture getting water from a lower<br />

stream may also be affected by the system getting water from<br />

the upper stream. The sustainability of the local environment<br />

of the system along the water course as well as the individual<br />

irrigation system is also affected by various external forces<br />

such as demographic, social, economic, cultural, political, industrial<br />

development, tourism, government policy, etc.<br />

Session 11: Enhancing the multifunctionality of rice systems 329


Arguments for preserving irrigated rice culture<br />

Multifunctionality of irrigated agriculture,<br />

particularly irrigated rice culture<br />

Irrigated agriculture, irrigated paddy cultivation in particular,<br />

possesses multifunctional roles with positive externalities. Irrigated<br />

agriculture produces not only food and fiber but also<br />

other intangible “goods” that are quite difficult to evaluate in<br />

economic terms. The multifunctional roles of irrigated agriculture<br />

are the provision of agricultural products to ensure food<br />

security, flood preservation, soil erosion control, groundwater<br />

recharge, water purification, and air-cooling effect; provision<br />

of habitat for various tiny living creatures that can create ecological<br />

balance or biodiversity preservation; provision of beautiful<br />

landscape that can have good potential for eco-tourism;<br />

provision of drinking water for rural people and domesticated<br />

animals; provision of an additional source of water plant and<br />

animal protein; provision of a place for duck raising; provision<br />

of a place for religious rituals and rural festivals; and many<br />

others (Mizutani 2002, Kwun 2002, Groenfeldt 2003).<br />

We cannot imagine how much money we need to combat<br />

flood and soil erosion, to purify water, to clean the air, and<br />

to solve the numerous problems that could emerge if the next<br />

generation abandons rice farming. Kwun (2002) provides important<br />

information on estimates of economic values of several<br />

multifunctional benefits of irrigated agriculture in Korea<br />

and Japan. For example, just for the flood control function of<br />

paddy farming, the value ranges from US$16.27 billion to<br />

$23.99 billion in Japan and from $1.11 billion to $1.32 billion<br />

in Korea. Thus, rice farmers deserve to be honored and praised<br />

as national heroes in environmental and biodiversity preservation.<br />

This is because they produce unmarketable multifunctional<br />

benefits that are reaped and enjoyed by other people not<br />

directly involved in rice-farming activities.<br />

Local wisdom and socio-cultural values attached<br />

to irrigated rice culture<br />

Local wisdom or indigenous knowledge and socio-cultural<br />

values are in<strong>here</strong>nt in rice cultivation. Rural traditions and<br />

various kinds of rituals and festivals associated with rice farming<br />

can bring social stability and social harmony. Before the<br />

advent of the Green Revolution, irrigated agriculture in many<br />

developing countries was rich in a wide variety of genetic resources.<br />

Local rice varieties were numerous. Modern agriculture<br />

has replaced local varieties with their associated local<br />

wisdom by modern rice varieties requiring expensive agrochemical<br />

inputs, which in many cases are beyond the capacity<br />

of local farmers to purchase.<br />

Moreover, the trade-related intellectual property rights<br />

recently implemented through international trade arrangements<br />

have pushed the farmers of developing countries into further<br />

difficulties. They would not have access to such costly technology<br />

crucial to enhancing agricultural development in their<br />

countries.<br />

Technical, managerial, and financial constraints<br />

faced by rice farmers<br />

After the implementation of an irrigation management transfer<br />

program in many countries, the farmers must be responsible<br />

for shouldering the cost burden for repairs, operation,<br />

and maintenance of the systems that were formerly managed<br />

by the government. However, many rice farmers lack technical,<br />

managerial, and financial capacity. They still need external<br />

support to be able to manage the irrigation system properly.<br />

Threats to the sustainability of irrigated rice culture<br />

Several conditions or factors may severely threaten the<br />

sustainability of irrigated rice culture: (1) declining interest of<br />

rural youth to work as farmers, particularly as rice farmers, (2)<br />

declining irrigated land area because of conversion for nonagricultural<br />

uses, (3) increasing conflict in the use of water resources,<br />

and (4) deforestation and pollution of irrigation water.<br />

Recommended measures for maintaining irrigated rice<br />

culture sustainable<br />

Minimizing irrigated paddy land conversion<br />

This can be done through (1) careful spatial and land-use planning<br />

taking water resource availability into consideration, and<br />

(2) creation of a legal framework prohibiting the use of paddy<br />

land within the prescribed zone for nonfarming activities, with<br />

strict law enforcement in its implementation.<br />

Narrowing the rural-urban gap<br />

This can be achieved through (1) pro-paddy farmers’ agricultural<br />

policies that ensure the enhancement of farmers’ income<br />

and terms of trade of farm products, (2) agricultural-based rural<br />

industrial development efforts for rural employment and<br />

income generation, and (3) improvement of rural infrastructure.<br />

Empowering irrigators’ associations (IAs)<br />

The following methods can be employed: (1) provision of support<br />

services such as agricultural credit, market information,<br />

and so on; (2) provision of training and education to increase<br />

farmers’ skills and knowledge in various fields; (3) facilitating<br />

and motivating the potential IAs to perform income-generating<br />

activities beyond irrigation management; (4) external support<br />

for selected IAs that are badly in need of major rehabilitation<br />

through a participatory approach; (5) government recognition<br />

for IAs as a legal entity so that they can make economic<br />

transactions and receive credit from financial institutions.<br />

Reducing water conflict<br />

This can be endeavored through (1) creating a legal framework<br />

for clearly defined water rights for different users, (2)<br />

330 <strong>Rice</strong> is life: scientific perspectives for the 21st century


promoting good coordination among existing IAs both within<br />

a single “large-scale” irrigation system and intersystem coordination<br />

along the watershed for equitable water allocation and<br />

distribution, (3) mobilizing and organizing dialog among water<br />

users of different sectors to develop a mutual understanding<br />

on how to use water as a common property for the benefit<br />

of the community as a whole, and (5) promoting more efficient<br />

use of the available water.<br />

Protecting upstream watershed and water quality<br />

from further degradation<br />

This can done through the following measures: (1) imposing<br />

strict punishment for water polluters and illegal woodcutters<br />

in the protected watershed; (2) refusing the issuance of a permit<br />

for any project investment for which, from an environmental<br />

impact, assessment criteria are not feasible; (3) implementing<br />

a “polluters pay principle”; (5) strengthening the roles<br />

of existing “community-based” forestry; (6) exploring the possibility<br />

of transferring government-managed forestry to local<br />

communities; (7) reducing the excessive use of chemical farm<br />

inputs and applying organic farming; and (8) strengthening<br />

interagency coordination in handling water problems.<br />

Closing notes<br />

Sustainability of irrigated rice culture should encompass technical,<br />

institutional, economic, ecological, socio-cultural, and<br />

environmental sustainability. In this way, it would enable us to<br />

(1) better understand the location-specific nature of greatly<br />

diverse irrigated rice culture in a rather holistic perspective,<br />

and (2) formulate irrigation and rice policy best suited to the<br />

specific conditions of a given country. This concept of<br />

sustainability, however, may be applicable mainly to irrigated<br />

agriculture getting water from farmer-managed irrigation systems<br />

but might not quite be relevant for those receiving water<br />

from government-managed irrigation systems.<br />

One of the greatest threats to the sustainability of irrigated<br />

rice culture is the rapid conversion of paddy fields to<br />

nonagricultural uses. As rice culture plays multifunctional roles<br />

with positive externalities, it must be preserved. Effective and<br />

appropriate policy measures need to be taken to restrict the<br />

changing uses of irrigated paddy fields.<br />

References<br />

Groenfeldt D. 2003. Multi-functional roles of irrigation with special<br />

reference to paddy cultivation. Proceedings of Sessions on<br />

Agriculture, Food, and Water for the Third World Water Forum<br />

(WWF3), 19-21 March 2003. Kyoto (Japan): World Water<br />

Council 3rd World Water Forum. p 71-82.<br />

Kim KH. 2001. <strong>Rice</strong> production and consumption. In: Kwun S-K,<br />

Choi HC, Chung S-O, Kim J-C, Kim TC, Heu M-H, Lee BW,<br />

Lee K-H, editors. <strong>Rice</strong> culture in Asia. Gyeonggi-do (Korea):<br />

Korean National Committee on Irrigation and Drainage, and<br />

<strong>International</strong> Commission on Irrigation and Drainage. p 14-<br />

19.<br />

Kwun S-K. 2002. Multi-functional roles in paddy fields and on-farm<br />

irrigation. Proceedings of the Pre-Symposium for the Third<br />

World Water Forum (WWF3), 20-21 March 2002. Otsu, Shiga<br />

(Japan): World Water Council 3rd World Water Forum. p 55-<br />

68.<br />

Mizutani M. 2002. Multi-functional roles of paddy field irrigation<br />

in the Asia monsoon region. Proceedings of the Pre-Symposium<br />

for the Third World Water Forum, 20-21 March 2002.<br />

Otsu, Shiga (Japan): World Water Council 3rd World Water<br />

Forum. p 37-54.<br />

Pakpahan A. 1995. Fundamental issues toward sustainable agriculture.<br />

Perencanaan Pembangunan. Nomor 03/1995:83-91.<br />

Notes<br />

Author’s address: Professor Emeritus, Udayana University, Bali,<br />

Indonesia, e- mail:stw_trisula@yahoo.com.<br />

Multifunctional roles of irrigation water<br />

and rice fields in Dujiangyan, China<br />

Liu Yulong, Yamaoka Kazumi, and Ren Yonghuai<br />

As a developing country, China has made outstanding progress<br />

in economic growth during the past 55 years. Especially in the<br />

last two decades, China has emerged as one of the fastest-growing<br />

economies in the world (Anderson and Peng 1998). From<br />

1949 to 2003, grain production in China increased from 113.2<br />

million to 430.7 million tons and peaked at 504.5 million tons<br />

in 1996. Meanwhile, the Chinese population has increased from<br />

0.4 billion to 1.3 billion. China feeds 25% of the world’s people<br />

with 7% of the total cultivated land in the world.<br />

However, since 1998, Chinese total rice production has<br />

declined continuously, from 200 million to 170 million tons.<br />

Although huge changes in agriculture with the development of<br />

a social economy and a population peak of 1.6 billion are expected<br />

in the next two decades, China faces increasing food<br />

demand and limited arable land and water resources (Liu et al<br />

2001). From 1996 to 2003, Chinese total cereal production<br />

declined by 14.6%. The main reasons influencing this decline<br />

in Chinese cereal production are attributed to a shift in peasants’<br />

willingness to cultivate grain crops instead of other economic<br />

crops, a price fluctuation in the international grain market,<br />

and the limited land and water. China affects the international<br />

grain market because of its huge population and<br />

Session 11: Enhancing the multifunctionality of rice systems 331


economy. China cannot rely on the international grain market<br />

for grain supply, w<strong>here</strong>as other developing countries can.<br />

Efficient ways to increase the production of the staple<br />

food crop rice are to enlarge the planted area and increase<br />

yield by improving arable land with affluent water resources.<br />

This environment provides the water-loving rice plant with the<br />

fundamental conditions necessary to achieve a high yield when<br />

combined with crossbreeding and gene-mapping technologies.<br />

More attractive and efficient ways to use water are now crucial<br />

for farmers in order to encourage them to plant rice because<br />

rapid economic growth in China has led to high competition<br />

among water users and requires the introduction of effective<br />

systems for water charging. Farmers need to wisely<br />

develop multifunctional uses of paddy fields and water to harvest<br />

more rice based on hydrologic conditions. Economic externalities<br />

generated by the multifunctional uses of paddy fields<br />

and water should be incorporated when the efficiency and<br />

sustainability of water use is addressed in rice paddy agriculture<br />

in the Asian monsoon region (Yamaoka et al 2004).<br />

This paper emphasizes the multifunctional roles of paddy<br />

fields and irrigation water, and introduces the multifunctional<br />

social roles of wise water management in the Dujiangyan irrigation<br />

area.<br />

Multifunctional roles of paddy fields and irrigation water<br />

Multifunctional roles are typically involved with fisheries in<br />

two aspects in the Dujiangyan irrigation area. One aspect is<br />

the role of irrigation water in fisheries. In most of southern<br />

China, especially in the Huai, Yangtze, and Pearl river basins,<br />

farmers have developed irrigation water for both paddy fields<br />

and fisheries. In the process of irrigation and drainage, farmers<br />

at the hamlet level have cooperatively built bypassed water-cycle<br />

courses adjacent to the channels with permission from<br />

rural authorities and used fishery drainage water to irrigate<br />

paddy fields (see Fig. 1.).<br />

These fisheries do not require the digging of ridges in<br />

the paddy field, but only require the building of fishponds beside<br />

the irrigation channel. In those areas of Dujiangyan w<strong>here</strong><br />

paddy fields are influenced by unstable water supplies because<br />

of the hilly topography, farmers build fishery ponds upstream<br />

beside the channel and irrigate rice fields downstream.<br />

The main construction and management steps are to (1)<br />

survey the scope of the fishpond beside the channel and calculate<br />

the differences in water levels between upstream and downstream,<br />

(2) design the size of the fishpond with the connecting<br />

water channels, gates, and pipes, (3) lay clay or concrete on<br />

the bottom and sides of the fishpond to prevent water leakage,<br />

(4) disinfect the fishpond, and (5) fill the fishpond with water<br />

and monitor the quality of the water body.<br />

The fishery pond also works as a retaining reservoir,<br />

jointly owned by a farmers’ group, for rice paddy fields downstream<br />

in case of water shortage such as during transplanting.<br />

A person who wants to manage the fishery does not pay a water<br />

charge but pays a rental fee for the fishery pond, about<br />

Channel<br />

Gate<br />

Gate<br />

Gate<br />

Fig. 1. Fishery beside the channel.<br />

Gate<br />

Fishpond<br />

Irrigated water<br />

<strong>Rice</strong> field<br />

US$400 ha –1 year –1 , to the farmers’ group. This person must<br />

follow the group’s instructions on water management. In fact,<br />

this multifunctional water use improves the efficiency of the<br />

irrigation water and also helps to strengthen farmers’ cooperative<br />

water management autonomy.<br />

Another aspect of the role of paddy fields and irrigation<br />

water is reconstruction of the paddy field with ridges and fossae.<br />

The ridges need to be about 70 cm wide. The depth of the<br />

fossae must be in the range of 20–25 cm and all the fossae<br />

need to be connected. Paddy rice grows on the surface of the<br />

ridges and fish live in the water in the fossae (see Fig. 2).<br />

The main processes for accomplishing this role are reconstructing<br />

the rice field, disinfecting the water and field,<br />

feeding fish fry, monitoring water volume and quality, managing<br />

the rice field, and harvesting.<br />

The fisheries beside the irrigation channels mainly feed<br />

herring, mandarin fish, crucian, carp, catfish, etc. In the paddy<br />

fields, the multifunctional technologies mainly provide breeding<br />

places for the rice field eel, loach, shrimp, crabs, giant<br />

spiny-frogs, ducks, and golden-fish. Statistical data show that,<br />

with these wise skills, the farmers get both high rice production<br />

and a relevant effective income. Compared with<br />

nonbreeding fields, multifunctional fields harvest more rice,<br />

approximately 750 kg ha –1 , and produce an economic commodity<br />

of fish, about 450 kg ha –1 . All these technologies alleviate<br />

grain shortages and produce extra income for the farmers.<br />

In addition, farmers are encouraged to be enthusiastic about<br />

planting rice.<br />

332 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Soil<br />

<strong>Rice</strong> <strong>Rice</strong> <strong>Rice</strong><br />

Ridge Ridge Ridge<br />

Fishing water<br />

Fig. 2. Fishery among rice fields.<br />

Soil<br />

Multifunctional social roles of the Dujiangyan irrigation<br />

system<br />

Besides technologies for irrigation water management and<br />

cultivated paddy fields, the irrigation water also fulfills multifunctional<br />

social roles in the irrigation areas. The Dujiangyan<br />

Irrigation System has been designated as a World Heritage by<br />

UNESCO, and its multifunctional social roles provide many<br />

revelations. This system is a gigantic water project built 2,260<br />

years ago on the upper reaches of the Minjiang River. The<br />

Dujiangyan diversion dam lies only 57 km from Chengdu, the<br />

capital of Sichuan Province, which has a population of approximately<br />

9 million, and it provides water for cities as well<br />

as for agriculture. This system is a good example of the development<br />

of efficient and sustainable water-use management<br />

through multifunctional social roles from ancient to modern<br />

times.<br />

The multifunctional social roles are outlined below:<br />

1. Economic benefit. At present, this system boasts a<br />

673,333-ha gravitation irrigation area, not only providing<br />

the irrigation water to produce 31% of the total<br />

provincial rice production, but also providing functions<br />

for urban living, industry, flood prevention, fishery,<br />

etc., for 30% of the total population of approximately<br />

85 million in Sichuan Province. The<br />

Dujiangyan Irrigation System brings prosperity to the<br />

Chengdu Plain and protects this plain against drought<br />

and waterlogging. This system has contributed to the<br />

development of Sichuan’s economy.<br />

2. Cultural development. The Dujiangyan Irrigation System<br />

and Mount Qingcheng have been put on the World<br />

Heritage List. Mount Qingcheng was the birthplace<br />

of Taoism, which is celebrated in a series of ancient<br />

temples (UNESCO 2000). It is well known that Taoism<br />

is the traditional Chinese religious culture. Even<br />

now, Taoism still influences the behavior of many<br />

people. In addition, Taoism has provided water management<br />

ideas and the apotheosis of ancient water<br />

treatment experiences that have become the base of<br />

the sustainable modern water management institution.<br />

This civilization was based on irrigation water and<br />

reflects the long-term social functions of irrigation<br />

water. People realized that the “unification of humans<br />

and nature” is a rule of cultural development.<br />

3. Biodiversity maintenance. After thousands of years<br />

of development, the Dujiangyan area formed five<br />

types of ecosystems: urban, agricultural, forest, high<br />

and cold, and river. In this area are 3,284 species,<br />

13% of the total species of Chinese advanced plants<br />

(Zhuang et al 2004). The unique humid environment<br />

throughout the vast alluvial fan allows many species<br />

of animals and plants to survive only in this area. This<br />

provides a rare biodiversity and gene pool in the<br />

Dujiangyan area, even for the world. The irrigation<br />

water provides the environment for this biodiversity.<br />

On the other hand, the biodiversity also maintains the<br />

whole water system to produce benefits and a civilization<br />

resulting in the unification of humans and nature.<br />

4. Sustainable development revelation. Many world<br />

heritages are no longer active in history and their thrilling<br />

stories are reserved in a book for the memory of<br />

humankind, but Dujiangyan is still active. The combination<br />

of ancient wisdom and modern technology<br />

is the sustainable condition for this system. The coordination<br />

of use, construction, and conservancy is important<br />

for the development of water resources and<br />

environmental protection. The administrative authority<br />

of the Dujiangyan Irrigation System has the ambition<br />

to expand its irrigation area to 1 million ha. This<br />

will bring sustainable developmental challenges to the<br />

irrigation system.<br />

References<br />

Anderson K, Peng C. 1998. Feeding and fueling China in the 21st<br />

century. World Dev. 26(8):1413-1429.<br />

UNESCO. 2000. Report of twenty-fourth session, World Heritage<br />

Committee, Cairns, Australia, 27 November-2 December 2000.<br />

p 45.<br />

Yamaoka K, Horikawa N, Tomosho T. 2004. Water productivity and<br />

economic externalities of rice paddy agriculture in the Asian<br />

monsoon region. The collection of theses of the <strong>International</strong><br />

Academic Forum for 2,260th Anniversary of the Founding of<br />

the Dujiangyan Irrigation System. p 303-311.<br />

Yulong L, Yukuo A, Minjian C, Yibin C. 2001. Multi-regression<br />

analysis of China’s grain production from 1949 to 2050.<br />

Biosyst. Stud. 1(1):29-36.<br />

Zhuang Ping, Gao Xianming, Feng Jinbo, Jing Changwei. 2004.<br />

Biodiversity research and conservation, Dujiangyan. In: General<br />

situation and characteristics of biodiversity in Dujiangyan.<br />

Sichuang Science and Technology Press. www.wwfchina.org/<br />

csis/shengwudyx2/djy/px12.htm.<br />

Session 11: Enhancing the multifunctionality of rice systems 333


Notes<br />

Authors’ addresses: Liu Yulong, Department of Water Resources,<br />

China <strong>Institute</strong> of Water Resources and Hydropower <strong>Research</strong><br />

(IWHR), 20 Chegongzhuang Xilu, Beijing 100044, China,<br />

liuyl@iwhr.com; Yamaoka Kazumi, Laboratory of Agricultural<br />

Water Management, National <strong>Institute</strong> for Rural Engineering<br />

(NIRE), 2-1-6 Kan-non-dai, Tsukuba, Ibaraki 305-<br />

8609, Japan, kyamaoka@nkk.affrc.go.jp; Ren Yonghuai,<br />

Laboratory of Agricultural Water Management, National <strong>Institute</strong><br />

for Rural Engineering (NIRE), 2-1-6 Kan-non-dai,<br />

Tsukuba, Ibaraki 305-8609, Japan, ren@nkk.affrc.go.jp.<br />

Decommissioning of paddy lands in the Wet Zone<br />

of Sri Lanka: some effects on food security and ecosystems<br />

Kusum Athukorala and Missaka Hettiarachchi<br />

<strong>Rice</strong> is the staple food and main agricultural commodity of Sri<br />

Lanka, w<strong>here</strong> 17.7% of the gross domestic product comes from<br />

the agricultural sector. Highly water-intensive rice cultivation<br />

consumes more than 70% of the total water allocated for food<br />

production in the country.<br />

Paddy lands in Sri Lanka can be categorized into three<br />

major types depending on the water usage:<br />

Major and medium irrigated systems—264,602 ha in<br />

1999-2000, 50% of the total area sown<br />

Minor irrigated systems—129,604 ha in 1999-2000,<br />

<br />

23% of the total area sown<br />

Rainfed systems—155,040 ha in 1999-2000, 28% of<br />

the total area sown<br />

Out of this, the rainfed systems are mainly found in the<br />

Wet Zone of the country. The Wet Zone is a climatic subdivision<br />

in the southwestern part of the country, which gets up to<br />

2,000–2,500 mm of annual rainfall. It constitutes about onethird<br />

of the country’s total area and accommodates about 63%<br />

of the population. The major part of heavily urbanized areas,<br />

including the cities of Colombo, Kandy, and Galle, is situated<br />

in the Wet Zone. Because of the high population density and<br />

high level of urbanization, demand is overwhelming for land<br />

in the Wet Zone. The population density in Colombo District<br />

is 3,305 persons per km 2 versus 957 persons per km 2 in the<br />

Wet Zone. In the Dry Zone, this decreases to 163 persons per<br />

km 2 . Competition for land is t<strong>here</strong>fore strong and, because of<br />

the availability of other employment, labor costs are increasingly<br />

high.<br />

In recent years, rice or paddy farmers (as they are termed<br />

in Sri Lanka) were either attracted by more lucrative alternatives<br />

or demotivated by the competition from rice imported<br />

from Pakistan, Vietnam, or Thailand, and tended to abandon<br />

rice farming. Table 1 shows rice imports by quantity and as a<br />

percentage of total national consumption.<br />

The inevitable consequence of this pressure is that most<br />

of the traditional Wet Zone farmers are pushed toward selling<br />

their paddy lands in lucrative deals for real estate development.<br />

This has significantly decreased the total area of rainfed<br />

paddy cultivation schemes during recent times (see Fig. 1).<br />

From the statistics, it is apparent that the percentage of<br />

rainfed paddy fields, which was as high as 45% of the total<br />

cultivated area in the early 1960s, had dropped to about 28%<br />

by 2000.<br />

The impact of the loss of rainfed paddy land<br />

on national food security<br />

A study of rice imports in the past few years showed a significant<br />

growth of rice imports in 1996-2000. This could be mainly<br />

attributed to the severe shortfall of rain that the country had to<br />

face intermittently during this period. Importing water-intensive<br />

goods to a country w<strong>here</strong> the water stress is high from<br />

another country w<strong>here</strong> the water stress is comparatively less is<br />

a form of virtual water trade, and it is a practice encouraged<br />

by most of the modern water ideologues since the Dublin-Rio<br />

conference onward.<br />

But, unfortunately in the Sri Lankan situation, most paddy<br />

lands affected by a shortage of rain are in the irrigated systems<br />

in the Dry Zone, w<strong>here</strong>as water stress in the Wet Zone is much<br />

less even during drought; t<strong>here</strong>fore, the rainfed systems in the<br />

Wet Zone could be cultivated to a certain extent even during<br />

relatively dry years. Because of the loss of paddy cultivation<br />

Table 1. <strong>Rice</strong> imports by year.<br />

Item<br />

Year<br />

1994 1995 1996 1997 1998 1999 2000 2001 2002<br />

<strong>Rice</strong> imports in million SLR 655 122 5,118 4,331 2,621 3,290 288 969 1,732<br />

Imports as a percentage 2 0.3 16.5 13.7 6.2 7.5 0.5 2.0 3.3<br />

of total local production<br />

Source: www.statistics.gov.lk.<br />

334 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Sown area (ha)<br />

250,000<br />

200,000<br />

Season 1<br />

Season 2<br />

150,000<br />

100,000<br />

50,000<br />

0<br />

1961-62<br />

1963-64<br />

1965-66<br />

1967-68<br />

1969-70<br />

1971-72<br />

1973-74<br />

1975-76<br />

1977-78<br />

1979-80<br />

1981-82<br />

1983-84<br />

Years<br />

1985-86<br />

1987-88<br />

1989-90<br />

1991-92<br />

1993-94<br />

1995-96<br />

1997-98<br />

1999-2000<br />

Fig. 1. Variation in total sown area in the rainfed system from 1961 to 2002.<br />

External debt and trade balance (billion US$)<br />

10<br />

8<br />

External debt<br />

Trade balance<br />

6<br />

4<br />

2<br />

0<br />

–2<br />

–4<br />

1990 1991 1992 19931994 1995 1996 1997 1998 1999 2000 2001 2002<br />

Year<br />

Fig. 2. External debt and trade balance.<br />

in the Wet Zone, Sri Lanka is pushed toward dependency on<br />

imported rice, hence the import of virtual water, placing a heavy<br />

burden on the already precarious balance of payments while a<br />

significant amount of real water is being lost as runoff because<br />

of the limitation of cultivable land in the Wet Zone. T<strong>here</strong>fore,<br />

this is more akin to a trade of virtual land than virtual water. In<br />

this process, not only is t<strong>here</strong> a loss of water, but also food<br />

security and the trade balance of the country are at stake. Because<br />

of the competition from cheap rice imports, small-scale<br />

farmers in the rainfed system are further discouraged and are<br />

tempted by high land prices to decommission their paddy land,<br />

thus creating a vicious circle (Fig. 2).<br />

The impact of the loss of rainfed paddy land<br />

on the water sector<br />

From the above section, it is clear how the decommissioning<br />

of rainfed paddy lands contributes to wastage of a significant<br />

volume of water that could have been used for cultivation. In<br />

all the recent environmental resolutions from Dublin-Rio to<br />

Rio+10 conferences, it has been stipulated that uses of water<br />

Session 11: Enhancing the multifunctionality of rice systems 335


are further defined as water for people, and water for food and<br />

ecosystems. The immediate repercussion of decommissioning<br />

a paddy land will be an impact on water for the food sector.<br />

With further investigation, it becomes apparent that t<strong>here</strong> are<br />

negative effects on water for people and water for ecosystems,<br />

too.<br />

T<strong>here</strong> are two types of rainfed paddy lands in Sri Lanka:<br />

the lowland rainfed paddy lands and the up-country terraced<br />

paddy fields. Because of the cultivation methods used traditionally<br />

for centuries in Sri Lanka, paddy lands act as sponges<br />

that absorb and retain water, thus enhancing groundwater recharge.<br />

When paddy lands are sold as real estate, w<strong>here</strong> the<br />

land will be filled, separated into small blocks, and sold for<br />

urban housing, more than 70% of the land is paved, which<br />

reduces groundwater recharge significantly. Housing also encroaches<br />

on the neighboring watersheds. Groundwater reduction<br />

for this reason is mainly felt in the up-country mountainous<br />

regions w<strong>here</strong> many water supply schemes are supplied<br />

by small streams. In valley areas such as Peradeniya, Gelioya,<br />

and Kundasale in the Central Province, w<strong>here</strong> t<strong>here</strong> had been<br />

significant filling of traditional paddy lands, t<strong>here</strong> are major<br />

flow fluctuations in small streams and springs that used to be<br />

perennial (e.g., Nanu Oya, Kandy District, Central Province).<br />

This has a direct negative effect on drinking water since water-supply<br />

authorities have begun to experience difficulties in<br />

maintaining the minor stream-fed supply points.<br />

The result could be that the water-supply authorities<br />

would have to pump water from a distance with greater treatment<br />

and conveyance costs. This would be a major economic<br />

implication for the nation because of the loss of groundwater.<br />

The effects in the lowlands take on a different twist. Filling of<br />

paddy lands increases runoff; hence, in sudden storms, runoff<br />

surpasses the flood limit, quite frequently causing severe flash<br />

floods. This is exacerbated in the high-intensity rains currently<br />

experienced because of El Niño. Economic implications in this<br />

case are much more intense than merely the loss of groundwater.<br />

In low-lying areas of Colombo District such as Kotte and<br />

Kollonnawa, w<strong>here</strong> a significant amount of paddy land was<br />

filled for urban housing, flash floods have become a major<br />

and regular problem. Even the Parliament of Sri Lanka in the<br />

low-lying area of Sri Jayewardenepura Kotte has been flooded<br />

twice. The Greater Colombo Flood Control and Environmental<br />

Improvement Project (1993-2004) has identified the filling<br />

of paddy land as one of the major causes of urban floods. The<br />

total cost of the project is about 15,000 million SLRs (US$150<br />

million) and it has had to resettle about 900 families, creating<br />

another set of significant socioeconomic and environmental<br />

problems.<br />

Remedies<br />

From the above facts and statistics, it is obvious that t<strong>here</strong> are<br />

significant economic implications of decommissioning rainfed<br />

paddy lands that need to be reviewed. Since most of these lands<br />

are used for urban housing, a direct prohibition on selling paddy<br />

land might cause conflicts in other sectors. T<strong>here</strong>fore, it is<br />

necessary that mitigatory measures such as local authorities<br />

imposing an extra tax on paddy land transactions or filling be<br />

considered. This could be based on the expense of commissioning<br />

a similar piece of land in the Dry Zone irrigated systems.<br />

It should also include an allowance for damage from<br />

groundwater loss and flash floods. The estimation for this total<br />

loss is about $1,700–2,000 per ha; policymakers could arrive<br />

at their rates based on the above value. A participatory<br />

awareness program, introducing alternate high-value crops<br />

(such as orchids) to encourage Wet Zone farmers, must be put<br />

in place immediately to continue with the maintenance of rice<br />

paddies in an ecologically appropriate manner. This could be<br />

useful in mitigating the negative impacts of decommissioning<br />

paddy lands.<br />

References<br />

Official Web site of the Central Bank of Sri Lanka.<br />

www.centralbanklanka.org.<br />

Department of Census and Statistics, Sri Lanka Web site,<br />

www.statistics.gov.lk.<br />

Greater Colombo Flood Control and Environmental Improvement<br />

Project (1993-2004): Report on the Badovita Resettlement<br />

Project.<br />

Notes<br />

Authors’ addresses: Kusum Athukorala, Netwater, No. 7, St. Mary’s<br />

Lane, Colombo 15, Sri Lanka, e-mail: kusum@itmin.net;<br />

Missaka Hettiarachchi, Department of Earth Resources, University<br />

of Moratuwa, Moratuwa, Sri Lanka, e-mail:<br />

nadalochana@yahoo.co.uk.<br />

336 <strong>Rice</strong> is life: scientific perspectives for the 21st century


True agro-biodiversity depending on irrigated rice cultivation<br />

as a multifunction of paddy fields<br />

Kazumasa Hidaka<br />

As one of the multifunctions of irrigated rice cultivation, biological<br />

diversity in rice paddies has been a critical issue in<br />

Japan and some Asian countries under free marketing of the<br />

WTO. Especially, in Japan, conservation of biodiversity and<br />

ecosystems in agriculture has been an important issue in agricultural<br />

and environmental policy since 1999, when a changed<br />

agricultural foundation law stimulated progress by the Japanese<br />

government and EU. Agro-biodiversity has now become<br />

a popular password in many nations, and the Internet now has<br />

30,000 articles on it.<br />

According to the literature before, about 2,000 species<br />

of plants and animals associated with rice paddy fields have<br />

been recorded in Japan (Hidaka 1998). This biodiversity in<br />

species richness can be regarded as a general characteristic in<br />

the rice paddy ecosystem. Actually, 645 animal species were<br />

recorded in the Philippines (Cohen et al 1994) and 765 species<br />

of arthropods were examined in Indonesia (Settle et al<br />

1996), for example. For rice, 212 species were recorded in the<br />

Philippines (Heong et al 1991).<br />

We must not ignore, however, that t<strong>here</strong> are actually two<br />

types of agro-biodiversity in rice paddies: one is “apparent<br />

agro-biodiversity” and the other is “true agro-biodiversity.”<br />

Usually, we have been evaluating agro-biodiversity as a value<br />

for the number of species collected in arable land, but not all<br />

species of plants and animals truly depend on the agricultural<br />

ecosystem. In the case of rice paddy fields, some species may<br />

be stranger species or may depend on other wetland habitats.<br />

T<strong>here</strong> are many kinds in natural or managed ecosystems with<br />

the exception of rice paddy fields: ponds, lakes, rivers, streams,<br />

and reservoirs in the limnological viewpoint. Furthermore,<br />

species components of agro-biodiversity in rice paddies may<br />

vary depending on the preserved situation of natural wetlands.<br />

Approaches toward evaluating true agro-biodiversity<br />

To discriminate the true species depending on rice cultivation<br />

as true agro-biodiversity, t<strong>here</strong> are three ways to examine this:<br />

natural history, review work, and field work in ecology and<br />

systematics:<br />

1. Review work in the literature (classical natural history).<br />

2. Collection of specimens attached to a living habitat<br />

(new natural history) (Mineta, Hidaka, and Enomoto,<br />

in preparation).<br />

3. Ecological field work of each species population associated<br />

with agricultural practices (agroecological<br />

field work).<br />

In this presentation, some typical studies, which we or<br />

other pioneers have conducted, will be reviewed from the viewpoint<br />

of agroecological principles.<br />

Case studies<br />

Examining natural history<br />

More than 200 plant species, 20 species of amphibians and<br />

reptiles, 30 species of fish and birds, and more than 1,000 species<br />

of arthropods can be reviewed as apparent agrobiodiversity<br />

in rice paddies (Hidaka 1998). A few collecting<br />

studies were conducted with scientifically appropriate methods<br />

of sampling. Kobayashi et al (1973) examined in detail<br />

the biodiversity of arthropods using sweeping methods in rice<br />

paddies of several sites of Tokushima Prefecture in the late<br />

1950s. More than 450 species of insects, spiders, and mites<br />

could be recorded in spite of the methodological faults of<br />

sweeping methods that can mainly collect arthropods only on<br />

rice plants. Nowadays, if we had a chance to examine arthropod<br />

fauna in the same fields, it might be difficult to collect a<br />

closed number of species in rice paddies such as in the 1950s.<br />

An example of this examination for species number must be<br />

significant and important to evaluate the agro-biodiversity level<br />

as a first step. But many species are stranger species in rice<br />

paddies, which the authors pointed out. We have to examine<br />

the fauna in other wetland ecosystems as well as rice paddies<br />

to evaluate true agro-biodiversity. Recently, Saijo (2001, 2002)<br />

tried to examine aquatic insect fauna in both rice paddies and<br />

irrigated ponds in Shimane Prefecture to make a clear reproduction<br />

of each species site. These studies are significant in<br />

the ecological sciences to reveal the dependency of each species<br />

on rice paddy ecosystems and to evaluate true agrobiodiversity.<br />

For botanists, Kasahara (1947) examined a list of rice<br />

paddy weed specimens in 25 prefectures over Japan and recorded<br />

174 plant species. All botanical species could be classified<br />

as serious harmful weeds (96 species) and semiwild<br />

weeds (78 species) in rice paddy ecosystems.<br />

Habitat records of specimens<br />

Recording habitat when collecting specimens in natural history<br />

work is important information for evaluating the agricultural<br />

dependency of each species as true-biodiversity. Although<br />

t<strong>here</strong> are very few cases that recorded the habitat of collected<br />

specimens, the same specimen wetland plants had details on<br />

the collecting place such as rice paddy, pond, irrigation way,<br />

or natural wetland. Some botanists had been recording habitats,<br />

such as Kasahara’s collection and Fujii (2001). So many<br />

Session 11: Enhancing the multifunctionality of rice systems 337


25<br />

L. indica subsp.<br />

incnopnyiia<br />

N. coreana<br />

75<br />

25<br />

M. quadrifolia<br />

R. extorris G. japonica<br />

50<br />

R. cantoniensis A. japonica<br />

50<br />

M.korsakowii<br />

V. undulata<br />

A. imbricata<br />

R. nipponicus<br />

<strong>Rice</strong> paddy fields<br />

H. oliganthum<br />

(%)<br />

100 R. leptopetala var. littorea<br />

R. pusilla, M. minima<br />

A. humidum<br />

N. indica<br />

Irrigation ponds<br />

P. chinense<br />

S. natans Blyxa spp.<br />

U. minor<br />

Isoetes spp.<br />

0<br />

100 75 50 25<br />

100<br />

0<br />

Food plains in rivers<br />

Fig. 1. Frequency of habitat records among endangered aquatic<br />

weeds in Okayama Prefecture according to botanical specimen<br />

collections (Mineta, Hidaka, and Enomoto, in preparation).<br />

data were accumulated so that dependency on rice paddies<br />

could be demonstrated in weed species in irrigated rice cultivation<br />

(Fig. 1; Mineta, Hidaka, and Enomoto, in preparation).<br />

Constructing a database of specimen habitat records using a<br />

GPS system is a key methodology for evaluating true agrobiodiversity.<br />

75<br />

Agroecological study of local populations<br />

and communities<br />

The most evidential and practical methods among these three<br />

approaches are agroecological field work at the population or<br />

community level for each species. For the community level,<br />

generally, examinations of an assembly of biological species<br />

on grown rice plants such as Kobayashi et al (1973), Heong et<br />

al (1991), and Une et al (1989) are correctly regarded as agrobiodiversity.<br />

T<strong>here</strong> is another assembly of aquatic animals following<br />

the irrigation system in rice paddies for agrobiodiversity<br />

such as Katano (2001) in fish or Saijo (2002) in<br />

insects.<br />

At the population level, it is difficult for all species, one<br />

by one or gene by gene, to reveal their dependency on rice<br />

cultivation by analyzing basic data, which used to require tasks<br />

such as genetic analysis of one local population. If we could<br />

make their dependency on paddy fields clear for a particular<br />

species population, we could use the most practical tactics for<br />

the population in agricultural policy. T<strong>here</strong>fore, it is reasonable<br />

to start from an emergent case such as endangered species,<br />

which need to conserve their population soon in an environmental<br />

policy (Hidaka 1998). Recently, some ecological<br />

field workers have started detailed studies of population biology<br />

for RDB animals and plants to demonstrate their habitat<br />

use quantitatively. Some species, including endangered populations,<br />

depend on agricultural practices in rice paddy fields.<br />

To make agricultural dependency clear, all wetlands in not only<br />

rice paddies but also in ditches, ponds, or streams and rivers<br />

and other natural wetlands should be examined in detail over<br />

several years. Many species may use several kinds of ecosystems<br />

to round out their life cycles as their indispensable habitats.<br />

Our examinations for the giant water bug Lethocerus<br />

deyrollei (Hemiptera) and the diving beetle Cybister japonicus<br />

(Coleoptera), representative endangered aquatic insects, have<br />

been conducted in hotspots to reveal their life history and agricultural<br />

dependency on rice paddy fields since 2000. These<br />

local populations of each species depend on irrigated rice fields<br />

and agricultural practices for their reproduction, according to<br />

results from our field work (Fig. 2). Furthermore, L. deyrollei<br />

populations depend on frogs, which strongly depend on the<br />

rice paddy ecosystem as a reproductive habitat (Hirai and<br />

Hidaka 2002). Their dependency on irrigated rice cultivation,<br />

however, might not be permanent. It is necessary for their agricultural<br />

dependency to conduct similar field examinations in<br />

different places and different climatic conditions. Often, the<br />

habitat use pattern of a species population has changed in a<br />

fluctuating environment. For more adequate conservation management,<br />

it is necessary to conduct ecological field work that<br />

can evaluate the habitat use of each local population quantitatively,<br />

such as ornithologists’ work (Elphick 2000, Fujioka et<br />

al 2001, Maeda 2001).<br />

Integrating conservation and agricultural production<br />

For endangered species in rural areas w<strong>here</strong> rice has been cultivated,<br />

some conservation practices are necessary immediately<br />

to recover or sustain the population level so that it won’t<br />

become threatened. For other conservation practices, we have<br />

to sustain agricultural production. Especially in the case of<br />

conserving agriculturally dependent species such as the giant<br />

water bug, maintaining agricultural activity is necessary in some<br />

hotspots of true agro-biodiversity. T<strong>here</strong>fore, integration of the<br />

conservation of biodiversity and agricultural production is<br />

important and necessary. Recently, a new concept, IBM (integrated<br />

biodiversity management), has been proposed in Japan<br />

(Kiritani 2002). Practically, to manage biodiversity well in<br />

agroecosystems, finding and making devices that can buffer a<br />

conflict between biodiversity and food production are desirable<br />

for both hardware and software.<br />

In our research field, some IBM trials have started to<br />

manage an endangered population of the giant water bug associated<br />

with biodiversity and sustainable agriculture in several<br />

practices of agricultural, educational, and scientific research.<br />

For our scientific researchers in agroecology, quantitative<br />

analyses of population dynamics can produce optimal results<br />

for the management of endangered species populations. Analyzing<br />

an endangered population by genetic methods at the<br />

molecular level, furthermore, must result in not only management<br />

of the population but mitigation for its appropriate conservation.<br />

In addition to studies of an intrapopulation, impor-<br />

338 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Conventional rice cultivation practices<br />

Tillage and<br />

puddling fertilizer<br />

Transplanting and<br />

pesticides<br />

Drainage<br />

Pesticide<br />

with IPM<br />

Harvest<br />

Tillage<br />

MAR APR MAY JUN JUL AUG SEP OCT NOV DEC JAN<br />

Overwintering Immigration In rice paddy<br />

Movement among paddy fields<br />

Mating and reproduction<br />

Overwintering<br />

Almost disappearing<br />

from aquatic habitats<br />

Dispersal and repeated reproduction<br />

Larval development<br />

Emigration with drainage<br />

Other wetland habitats<br />

(ditches, ponds, rivers)<br />

Water level of irrigation<br />

Higher<br />

Irrigation<br />

start<br />

New adults<br />

Dispersal<br />

Emigration<br />

Life stages of the paddy bug<br />

Fig. 2. A schematic description of the life cycle of the giant water bug, Lethocerus deyrollei, rice<br />

cultivation practices, and irrigation water level in a hotspot field of agro-biodiversity.<br />

tant research at the interpopulation level is necessary for the<br />

conservation of endangered species. Generally, each species<br />

coexists with more than 20 species, at least for sustaining their<br />

lives. T<strong>here</strong>fore, examinations of population dynamics should<br />

be included in community ecology for optimal conservation<br />

planning. It was demonstrated that diverse amphibian species<br />

are important for supporting food resources for a carnivorous<br />

species of the giant water bug (Hirai and Hidaka 2002). On<br />

the other hand, educational work must be important for villagers<br />

and consumers in the city to promote the significance of<br />

biodiversity in agriculture. In 1960s Japan, some fish, snails,<br />

and insects such as grasshoppers in rice fields were sold and<br />

eaten. Good devices often lurk behind our traditional life style.<br />

Recently, several ecological workers have been conducting<br />

a detailed population analysis in a residual population of<br />

threatened animals and plant species and conservation with<br />

villagers in Japan. However, conservation biologists are not<br />

enough to produce a successful regeneration of an endangered<br />

species, although it is in emergency for its conservation.<br />

Conclusions<br />

To understand and manage true agro-biodiversity in rice paddies,<br />

we need to organize an integrated ecosystem management<br />

system such as IBM as soon as possible. First of all, it is<br />

necessary to answer a question about what kinds of species<br />

depend on the rice paddy ecosystem in not only negotiations<br />

with the WTO but also in building up a consensus of many<br />

people in villages on management practices for agrobiodiversity.<br />

For this, the integration of scientific research and<br />

education must always be the most practical.<br />

References<br />

Elphick CS. 2000. Functional equivalency between rice fields and<br />

seminatural wetland habitats. Conserv. Biol. 14(1):181-191.<br />

Heong KL, Aquino GB, Barrion AT. 1991. Arthropod community<br />

structures of rice ecosystems in the Philippines. Bull. Entomol.<br />

Res. 8:407-416.<br />

Hidaka K. 1998. Biodiversity conservation and environmentally regenerated<br />

farming system in rice paddy fields. Jpn. Ecol.<br />

48:167-178.<br />

Session 11: Enhancing the multifunctionality of rice systems 339


Hirai T, Hidaka K. 2002. Anuran-dependent predation by the giant<br />

water bug Lethocerus deyrollei (Hemiptera: Belostomatidae),<br />

in rice fields of Japan. Ecol. Res. 17:661-665.<br />

Kasahara Y. 1947. Studies on the characteristics of weeds and their<br />

geographical distribution (1). Nogaku Kenkyu 37(1):8-9.<br />

Kiritani K. 2000. Integrated biodiversity management in paddy fields:<br />

shift of paradigm from IPM toward IBM. Int. Pest Manage.<br />

Rev. 5:175-183<br />

Kobayashi T, Noguchi Y, Hiwada T, Kanayama K, Maruoka N. 1973.<br />

Studies on the arthropod associations in paddy fields, with a<br />

particular reference to insecticidal effect on them. 1. General<br />

composition of the arthropod fauna in paddy fields revealed<br />

by net-sweeping in Tokushima Prefecture. Konchu 41(3):359-<br />

373.<br />

Maeda T. 2001. Patterns of bird abundance and habitat use in rice<br />

fields of the Kanto Plain, central Japan. Ecol. Res. 16(3):569-<br />

585.<br />

Saijo H. 2002. The role of loach-farming paddy on the life cycle of<br />

aquatic insects inhabiting lentic habitats. Jpn. J. Ecol. 51(1):1-<br />

12.<br />

Une Y, Hidaka K, Akamatsu T. 1989. A field guide of paddy insects<br />

for reduced farmers. Tokyo (Japan): Nobunkyo Pub. Co.<br />

86 p.<br />

Notes<br />

Author’s address: College of Agriculture, Ehime University, Japan,<br />

e-mail:sunhwkaz@agr.ehime-u.ac.jp.<br />

Enhancing the multifunctionality of floating-rice farming<br />

in the Chao Phraya delta of Thailand<br />

Yuyama Yoshito, Ogawa Shigeo, and Ueda Tatsuki<br />

Paddy farming in the Asian monsoon area is closely connected<br />

to the rural social system. Paddy farming has important roles<br />

and functions. Recently, energetic efforts have been made to<br />

spread such recognition worldwide and to evaluate it quantitatively<br />

(Japanese National Committee of ICID 2003, MAFF<br />

2003, JIID 2003). In this paper, we introduce the<br />

multifunctionality of floating rice farming in the Chao Phraya<br />

delta of Thailand and its possibility for enhancement by water<br />

management.<br />

Farming and water management in the Chao Phraya delta<br />

The Chao Phraya River basin has a catchment area of 162,000<br />

km 2 , including 1.34 million ha of low-lying delta area. The<br />

Greater Chao Phraya Project drastically changed farming and<br />

water management in the delta. Only one crop per year was<br />

possible t<strong>here</strong> before the project. The original purpose of the<br />

project was supplementary irrigation in the rainy season. Its<br />

purpose has now expanded to irrigation in the dry season and<br />

domestic water supply, among others. The delta area has become<br />

one of the largest rice granaries in the Asian monsoon<br />

area.<br />

The present irrigable area in the delta is 1.08 million ha.<br />

<strong>Rice</strong> cultivation for more than five times per two years is possible<br />

w<strong>here</strong> water accessibility is good. New trials of rice cultivation<br />

in the dry season started only about 30 years ago. The<br />

rice cultivation area increased rapidly, but soon reached its<br />

limit because of a shortage of water resources and insufficient<br />

capacity of existing irrigation facilities. Farming and land use<br />

changed rapidly again in the last 15 years. Water management<br />

became more complicated than before because water demand<br />

increased and competition among water users became more<br />

serious (Francois et al 1999, 2001). The problems of water<br />

shortage (Roongrueng et al 1996) and flooding (Pramote 1999)<br />

have to be examined in parallel.<br />

Water management is mainly carried out under the authority<br />

of the Royal Irrigation Department (RID). To prevent<br />

water conflict, water allocation in the dry season from January<br />

to June is very important. Hereafter, the period from January<br />

to June is referred to as “WM (water management) dry season,”<br />

while the period from July to December is referred to as<br />

“WM wet season.”<br />

Multifunctionality of floating-rice farming<br />

Floating-rice farming in the delta has played important roles.<br />

It can be summarized as having low input and low yield but<br />

sustainable farming. Cultivated floating-rice area decreased<br />

from 228,000 ha in 1987 to 114,000 ha in 1997 (CTI et al<br />

1999). Floating rice can grow flexibly according to irregular<br />

increases in water level. It grows in a dry field with weeds at<br />

the beginning stage. Then, the stem increases in length from 2<br />

to 5 m according to water conditions. The cultivation calendar<br />

matches the natural water conditions. It takes 7–9 months from<br />

planting to harvest. The harvest starts in December or January<br />

after the stored water in the field is drained.<br />

In the past, people in the delta had to follow natural water<br />

conditions. Recently, the water level and flow conditions of<br />

the main rivers and canals have been controlled to some degree<br />

by the operation of diversion dams and regulators along<br />

both the main irrigation and drainage canals. A unit of floating<br />

rice area is from a few thousand to 10,000 ha. Each unit has a<br />

so-called “drainage box” that has a drainage regulator to control<br />

the water level upstream. Newly constructed big roads<br />

function as embankments. T<strong>here</strong>fore, the location of flooding<br />

areas is also partially regulated by water operation. Scattered<br />

340 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Specific volume of standing floodwater<br />

Paddy fields located in low-lying area<br />

Paddy fields located in comparatively<br />

elevated area<br />

Residential area located in low-lying<br />

area<br />

Forest<br />

Allowable limit<br />

for paddy fields<br />

1 2 5 10 20 50 100 200<br />

Flood prevention function<br />

Damage from flood<br />

Return period of rainfall (y)<br />

Flood mitigation function that<br />

paddy fields potentially have<br />

Design return period for<br />

drainage of paddy fields<br />

Flood mitigation function<br />

Paddy rice w<strong>here</strong> drainage improvement was implemented<br />

Residential area with paddy fields in upstream side<br />

Residential area without paddy fields in upstream side<br />

1 2 5 10 20 50 100 200<br />

Return period of rainfall (y)<br />

Fig. 1. Volume of standingflood water and flood disaster damage<br />

in respective land use under different rainfall magnitudes.<br />

inundation prevents serious flood damage. Figure 1 represents<br />

the general image of flood mitigation function by the paddy<br />

field.<br />

Problems of flooding in the delta often occur in October<br />

and November. A paddy field cultivating a high-yielding variety<br />

cannot receive too much water during the flood. However,<br />

floating-rice area has a great possibility to receive surplus water,<br />

which contributes to flood mitigation at the regional level. The<br />

storage volume of the floating-rice area can be estimated at<br />

2,280 million m 3 by assuming that the area is 114,000 ha and<br />

the water depth is 2.0 m. The volume would be almost the<br />

same as the storage in the remaining paddy fields in the WM<br />

wet season, assuming the water depth were 0.2 m.<br />

If we could convey surplus water to the floating-rice area<br />

to decrease the peak flood discharge with a depth of 25 cm (5<br />

cm day –1 for 5 days), the total storage capacity would become<br />

285 million m 3 . We can call this the buffer function. That volume<br />

is equal to the inflow discharge of 660 m 3 s –1 for 5 days.<br />

This is compared with the storage volume of dams and the<br />

discharge of water allocation in the WM dry season. It is impossible<br />

to protect metropolitan Bangkok from flooding without<br />

paddy fields.<br />

In addition, the river and canal network also has a buffer<br />

function for flood mitigation. If the rivers or canals upstream<br />

and midstream can store surplus water temporarily, they help<br />

to limit a peak discharge. If a river or canal with a length of<br />

100 km and width of 200 m could increase the water level by<br />

30 cm without any damage from overflow or breaking of an<br />

embankment, the storage volume would become 6 million m 3 .<br />

This volume is equivalent to 70 m 3 s –1 , but it is effective on<br />

only one day. That is achieved by conveying surplus water in<br />

the Chao Phraya River to the Lopburi River, the Noi River,<br />

and the main irrigation and drainage canals. This function to<br />

control the timing of release of surplus water to the downstream<br />

of the Chao Phraya River is significant because the<br />

lower delta is a more serious flood-prone area affected by high<br />

tide. Moreover, the function of the river and canal network<br />

that conveys surplus water to the floating-rice area is important.<br />

Water released from the floating-rice area can be used<br />

in downstream areas and it contributes to decreasing the salinity<br />

concentration at the beginning of the WM dry season. EC<br />

(electrical conductivity) in the irrigation and drainage canals<br />

of the upper east bank of the delta ranged from 15 to 30 mS<br />

m –1 . Compared with the EC standard for irrigation of 70 mS<br />

m –1 , the measured values were relatively low. The released<br />

water also functions to increase the water level and discharge<br />

in the Chao Phraya River. It is important for navigation and<br />

the tap-water supply. In other words, it can decrease the release<br />

discharge from the Chao Phraya diversion dam and save<br />

water resources at upstream storage dams. The floating-rice<br />

field is also a living place for fish. It provides aquatic products.<br />

Ducks are sometimes kept in the floating-rice field after<br />

it is harvested. T<strong>here</strong> is little soil erosion in this kind of farming.<br />

It produces oxygen. The landscape of the floating-rice area<br />

provides opportunities for eco-tourism.<br />

Enhancing multifunctionality by water management<br />

The positive multifunctionality of floating-rice farming can<br />

be enhanced by water management because the floating-rice<br />

area is a buffer space in terms of water flow. The RID is daily<br />

monitoring hydrology, meteorology, and water operation information<br />

at many stations and facilities. Monitored information<br />

should be effectively used for decision making on water<br />

operations. In the decision support system for water operations,<br />

the monitoring of existing conditions, their summary,<br />

and the judging of facility operations learned from past records<br />

and experience are essential. Many proposals at the planning<br />

stage of water allocation and at the practical water operation<br />

stage as well as remarks on flood control were made (Yuyama<br />

et al 2003a,b). Table 1 shows the methods to enhance three<br />

functions of floating-rice farming and possible impact. New<br />

methods to enhance the existing function must match technology<br />

development and public agreements. A quantitative study<br />

is needed to clarify the relationship among release discharge<br />

from the dams, tidal level, water levels along the river, and<br />

salinity concentration. Moreover, we have to keep in mind that<br />

one preferential enhancement function often has a negative<br />

impact on other functions.<br />

Session 11: Enhancing the multifunctionality of rice systems 341


Table 1. Methods to enhance the functions of floating-rice farming and possible impacts.<br />

Preferential<br />

enhancement function<br />

Flood mitigation Development of water resources Food production<br />

Method (how)<br />

Induced<br />

positive<br />

impact<br />

What<br />

When<br />

W<strong>here</strong><br />

For whom<br />

Induced negative impact<br />

or remarks<br />

Preliminary release of standing water<br />

from floating-rice area<br />

Conveyance of floodwater into floatingrice<br />

area<br />

Insurance contract between government<br />

and farmer for receiving surplus floodwater<br />

Heightening of embankment<br />

Advanced operation of drainage regulator<br />

Development of decision support system<br />

of infrastructure for information and<br />

communication technology<br />

Peak period of flood discharge<br />

Flooding period (October, November)<br />

Downstream delta, especially Bangkok<br />

People in downstream delta<br />

Increase in risk in farming and harvest<br />

yield<br />

Release of standing water considering the<br />

timing of water use downstream<br />

Change of drainage point to use water<br />

resources more effectively<br />

Arrangement of new facility such as<br />

pump, regulator, and regulating pond<br />

Modification of cultivation pattern in<br />

downstream fields<br />

Development of a decision support system<br />

Provision of new water resources<br />

From middle of December to end of January<br />

Downstream fields<br />

Whole basin<br />

Farmers of downstream fields<br />

People in the basin<br />

Increase in salinity in the Chao Phraya<br />

River<br />

Decrease in water level in the downstream<br />

Chao Phraya River (it is sometimes<br />

unsuitable for navigation and intake<br />

for tap water)<br />

Introduction of new farming technology<br />

for dry-season cultivation<br />

Drainage improvement<br />

Arrangement of irrigation facility<br />

New water allocation<br />

New farm products<br />

From February to May<br />

Floating-rice field<br />

Farmers<br />

Consumers<br />

Deterioration of water quality and soil<br />

Increase in water demand<br />

New water conflict might occur<br />

Change in ecological environment<br />

Conclusions<br />

Whether the people are aware or not, multifunctionality of floating-rice<br />

farming in the Chao Phraya delta of Thailand really<br />

exists. The functions of flood mitigation and cultivation of water<br />

resources for downstream areas are obvious. If we could limit<br />

the flood peak discharge of 285 million m 3 , new dam construction<br />

would not be needed. In addition, we could obtain<br />

new water resources of 2,280 million m 3 . This is equivalent to<br />

the water demand for a rice cultivation area of 11,000–22,000<br />

ha. This would help to increase the flexibility of water operations.<br />

Other functions such as water quality conservation, contribution<br />

to salinity control, maintaining navigation, and provision<br />

of eco-tourism opportunities are also important.<br />

Multifunctionality would be enhanced by water management<br />

accompanied by a decision support system for water operations.<br />

References<br />

CTI Engineering Co., Ltd. and INA Corporation. 1999. The study<br />

on integrated plan for flood mitigation in Chao Phraya River<br />

basin. Final Main Report, RID, JICA.<br />

Francois M, Sripen D, Chatchom C, Alexandre J, Yuphaa L. 1999.<br />

Improvement of rice cultivation and water management in the<br />

flooded area of the Central Plain of Thailand. DORAS Center.<br />

Francois M, Chatchom C, Thippawal S, Jesda K. 2001. Dry-season<br />

water allocation and management in the Chao Phraya Delta.<br />

DORAS Center.<br />

Japanese National Committee of ICID. 2003. Proceedings of WWF3<br />

Agriculture, Food, and Water.<br />

JIID. 2003. A message from Japan and Asia to the world water discussions.<br />

MAFF. 2003. The global diversity of irrigation.<br />

Pramote M. 1999. Development and achievements in flood control<br />

and management in Thailand, regional cooperation in the<br />

twenty-first century on flood control and management in Asia<br />

and the Pacific. New York, N.Y. (USA): ESCAP, UN. p 59-<br />

111.<br />

Roongrueng C, Charoon K, Siripong H, Natha H. 1996. Master planning<br />

of water resources development in Thailand (1994-2006).<br />

Trans. of 16th ICID Congress. Cairo, Q. 47, R.1.05. p 55-67.<br />

Yuyama Y, Pongsak A, Phonchai K, Chatchom C, Athaporn P, Shioda<br />

K. 2003a. Strategy to improve water management in the Chao<br />

Phraya delta. Rural Environ. Eng. 44:42-59.<br />

YuyamaY, Pongsak A, Shioda K, Onimaru T, Nakazawa N, Fujisaki<br />

T. 2003b. Improvement of water allocation planning and practical<br />

operation in the upper east bank of the Chao Phraya delta.<br />

Technical Report of the National <strong>Institute</strong> for Rural Engineering.<br />

No. 201. p 93-124.<br />

342 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Notes<br />

Authors’ address: National <strong>Institute</strong> for Rural Engineering, 2-1-6,<br />

Kannondai, Tsukuba, Ibaraki 305-8609, Japan, e-mail:<br />

yuya@nkk.affrc.go.jp.<br />

Acknowledgments: The authors worked for the Modernization of<br />

Water Management System Project (MWMS) at RID. This<br />

project is under implementation facilitated by the Japan <strong>International</strong><br />

Cooperation Agency (JICA). The authors greatly appreciate<br />

all the people involved in the project.<br />

Demonstration program on multifunctionality of paddy fields<br />

in the northeastern region of Thailand<br />

Chatchai Boonlue<br />

The principal grain crop in the Lower Mekong River Basin<br />

(LMB) is rice. In fact, nearly 90% of the world’s rice is produced<br />

in the Asian countries including this region. It is commonly<br />

recognized that “paddy fields” have many functions and<br />

advantages or disadvantages but consume a large amount of<br />

water. The value of irrigation water encompasses more than<br />

the net economic returns of the rice produced. The multiple<br />

values of irrigation are particularly evident in paddy cultivation<br />

w<strong>here</strong> water supports a sustainable and ecological water<br />

cycle control, which is the basis for the characteristic sociocultural<br />

system of Southeast Asia.<br />

Northeast Thailand has an area within the LMB of<br />

513,113 km 2 and runoff showing as much fluctuation as 80–<br />

85% in the wet season but very scarce in the dry season. Accordingly,<br />

water control functions (flood prevention, groundwater<br />

recharge, prevention of soil erosion) are essentially required<br />

to control flood and drought problems.<br />

In this connection, we need to know more precise information<br />

about the multifunctional roles and multipurpose uses<br />

of paddy-field irrigation. For this region, the Demonstration<br />

Program on Multifunctionality of Paddy Fields over the<br />

Mekong River Basin (DMPF) is developed by the Mekong<br />

River Committee (MRC) member countries to collect data and<br />

information on the area that help to demonstrate the<br />

multifunctionality of paddy fields in the LMB.<br />

Thailand has expected that the outputs of DMPF will<br />

provide useful information for the effective use of water to<br />

achieve high production in paddy fields under appropriate<br />

water, soil, and crop management.<br />

The overall concept of the DMPF aims at promoting<br />

agriculture and irrigation development within the MRB in a<br />

sustainable and environmentally sound manner, and with good<br />

participation and cooperation of all concerned. This will serve<br />

as a practical and integrated approach for agricultural development<br />

at the farm, subbasin, and basin levels. Achievement<br />

of this program will benefit local people, scientists, and managers<br />

of relevant agencies. Local farmers would learn how to<br />

cultivate rice with an optimum or minimum use of water and<br />

how to manage the consequent impact from rice growing. Scientists<br />

would gain further insight into such aspects as the rice<br />

cultivation system and the possible impact of actual water use<br />

for paddy growing, the balance of water use, surface and un-<br />

derground water quality, and the relationships of various factors<br />

in paddy growing. Results at the farm level will be extrapolated<br />

to the subbasin (or catchments) and, ultimately, to<br />

the whole basin. The expected outputs will provide useful information<br />

for the optimum use of water to obtain higher paddy<br />

yields under appropriate soil, crop, and water management.<br />

Summary study of the DMPF<br />

The total timeframe of the DMPF is proposed for 5 years. In<br />

the first and second year, activities will concentrate on data<br />

collection in the subbasin and experimental plot. A demonstration<br />

model for the multifunctionality of paddy fields will<br />

be established in the third year and will be improved and applied<br />

to a wider area in the fourth year. Finally, analysis and<br />

demonstration will be done.<br />

Demonstration will be done through simulation of a logical<br />

model and a small experimental study. Through the study<br />

for the demonstration of paddy fields in northeastern Thailand,<br />

two types of models will be developed, at the field level<br />

and at the subbasin level.<br />

Field-level model<br />

The field-level model shows mainly the inflow/outflow of water<br />

in the field for agricultural land (paddy and upland). In addition,<br />

if possible, it is better to reflect some other aspects, such<br />

as field conditions (topography, soil, meteorology), farming<br />

practices, and infrastructure (irrigation/drainage, roads).<br />

The preliminary field-level model will be studied, based<br />

on the schematic model shown in Figure 1, and on other factors.<br />

To evaluate the multifunctionality of paddy fields at the<br />

sub-/entire basin levels, it is necessary to consider the impact<br />

of upland crops. The model can be applied for both paddy and<br />

upland by changing the coefficients of several factors.<br />

Subbasin level<br />

In this study, the subbasin is defined as one of the areas assuming<br />

a unit block from the viewpoints of conditions of hydrology,<br />

topography, land use, water use, flooding, and environment.<br />

It may include one or more rivers/tributaries of the<br />

Mekong. The model at the subbasin level (Fig. 2) will be in<br />

conflict because of factors such as other water use (urban,<br />

Session 11: Enhancing the multifunctionality of rice systems 343


Evaporation<br />

Methane emissions<br />

Rainfall<br />

Landscape/amenity<br />

Bund<br />

Flood<br />

mitigation<br />

Soil erosion<br />

control<br />

Irrigation<br />

water<br />

Biodiversity<br />

Ponded wetland ecology<br />

Return flow to the river<br />

Nitrate<br />

Groundwater recharge<br />

Groundwater<br />

Fig. 1. Basic idea of preliminary model for field level.<br />

Measuring station<br />

Headwork<br />

Paddy field<br />

Water intake<br />

Return flow<br />

Paddy field<br />

Paddy field<br />

Other water use<br />

Fig. 2. Basic idea of preliminary model for the subbasin level.<br />

domestic, industrial), environmental impact on the area beyond<br />

the field, flood damage, etc. In the case of including reservoirs<br />

in a subbasin, it is necessary to consider the operation<br />

of the reservoirs and conditions for hydropower generation.<br />

To accommodate the model subbasin-wide, three options<br />

are proposed for data collection. The subbasin consisting of<br />

rice ecosystems as designed will be selected. These ecosystems<br />

are rainfed and the irrigated wet and dry seasons. Within<br />

the selected subbasin, a farmer-field experiment will be conducted<br />

to collect data as needed.<br />

Proposed data to be collected<br />

Subbasin level<br />

Subbasin conditions. The data on subbasin boundary, administrative<br />

conditions, infrastructure, irrigation, and land use are<br />

selected for basic items on the respective subbasin conditions.<br />

These data are available for designing the basic framework of<br />

the subbasin model and for clarifying the present conditions<br />

of the subbasin. The entire LMB levels will be clarified by<br />

compiling the information on the subbasin.<br />

Natural conditions. The data on climate, topography,<br />

geology, hydrogeology, soil, hydrology, drainage, and flood<br />

are selected for the natural conditions in the subbasin. These<br />

data are basic calculation data of the entire LMB and the<br />

subbasin model and actual observation data will be used for<br />

calibration and improvement of both models.<br />

<strong>Rice</strong> ecosystem. The data on rice ecosystem, paddy area,<br />

soil moisture, rice crop, and agro-economy are selected for<br />

the rice ecosystem of the subbasin. These data will be used<br />

mainly for analysis of direct impacts of the multifunctionality<br />

of paddy fields.<br />

Other conditions. The data related to socioeconomics,<br />

water use, community, and environment are selected for the<br />

344 <strong>Rice</strong> is life: scientific perspectives for the 21st century


other conditions of the respective subbasin. Indirect impacts<br />

will be analyzed mainly based on these data.<br />

On-farm level<br />

General conditions. The data on irrigation, rice area, landholdings,<br />

infrastructure, nearby drainage, topography, soil, land<br />

use, and climate are selected for the general conditions for the<br />

on-farm level. These data are required for designing the basic<br />

framework of the on-farm level model and for clarifying the<br />

present conditions at the field level. These data are also basic<br />

calculation data of the field-level model and actual observation<br />

data will be used for calibration and improvement of the<br />

model.<br />

<strong>Rice</strong> ecosystem. The data on the rice ecosystem, rice crop,<br />

and farming practices are selected for the rice ecosystem at<br />

the on-farm level. These data will be used mainly for analysis<br />

of direct impacts of the multifunctionality of paddy fields.<br />

Water and other conditions. The data on water inflow,<br />

water outflow, water table, underground water, and environment<br />

are selected for the water and other conditions of the onfarm<br />

level. These data will be used for analyses of water inflow<br />

and outflow and the main multifunctionality.<br />

Progress at the subbasin level<br />

The data on irrigation projects and reservoirs, soil and land<br />

use, and rice crops to be collected are basically in the form of<br />

an attribute table that will be linked subsequently with existing<br />

point data in a GIS file.<br />

The following results have been obtained.<br />

Irrigation data T<strong>here</strong> are 8,764 irrigation projects,<br />

as follows: 5,125 reservoir projects, 1,347 weir<br />

projects, 1,192 pumping projects, and 1,100 other<br />

headwork projects (those are 17 large-, 1,335 medium-,<br />

and 7,412 small-scale projects).<br />

Land-use data. The total area of the Mae Kong<br />

subbasin is 186,221 km 2 . The major land uses are<br />

paddy fields (45%), forest (18%), and other agricultural<br />

land (20%).<br />

<strong>Rice</strong> crop data. Rainfed lowland rice on bunded fields<br />

occupies a large portion of the rice area. In northeastern<br />

Thailand, it is grown on rainfed area of about 3.3<br />

million ha and on irrigated area of about 0.3 million<br />

ha.<br />

Progress of the on-farm experiments<br />

The on-farm experiment in the dry season was selected at two<br />

different locations, as site I in Udon Thani and site II in Roi<br />

Et. Site I covered 2.5 ha, elevation 395 m, located at the lateral<br />

canal of the Huai Luang Irrigation Project. Site II covered<br />

4 ha, using water from the Seoi Yai Irrigation Project.<br />

Both on-farm experiments are preferably nearby the<br />

meteorological station, which is the site of the main source of<br />

data for the site: rainfall, temperature, and other climatic data<br />

needed to be collected. For the wet season, two more meteorological<br />

stations for on-farm experiments in the rainfed area<br />

will be established and an automatic rain gauge is already installed<br />

at the sites.<br />

The land use in the on-farm and surrounding sites was<br />

evaluated and soil samples were collected. The data on water<br />

inflow, water outflow, water depth, and water table are recorded<br />

daily by the staff of the Royal Irrigation Department (RID).<br />

Actually, the daily data record began in mid-March 2004.<br />

Some results<br />

A hook gauge is used for measuring the water level from an<br />

installed apparatus such as an N-type and water-requirement<br />

measuring apparatus. Daily data recorded by the N-type apparatus<br />

indicated a decrease in value because of the rate of water<br />

consumption by both percolation and evapotranspiration. The<br />

rate of percolation in the experimental area at the Huai Luang<br />

site is about 3–5 mm d –1 (average 3.57 mm d –1 ), evapotranspiration<br />

is 7–15 mm d –1 (average 11.13 mm d –1 ), and evaporation<br />

is 5–7 mm d –1 (average 5.77 mm d –1 ). The water-depth<br />

fluctuation in the paddy field was about 110–160 mm in the<br />

on-farm experiment.<br />

The on-farm experiment for the wet season started in<br />

August. T<strong>here</strong> are two sites in irrigation projects and two sites<br />

in the rainfed area.<br />

Bibliography<br />

Mekong River Commission. 2003. Inception report. Program to<br />

Demonstrate Multifunctionality of Paddy Fields.<br />

Thai National Mekong Committee. 2004. Interim report. DMPF.<br />

Notes<br />

Author’s address: Royal Irrigation Department, Bangkok, Thailand,<br />

e-mail: ffpd@mail.rid.go.th.<br />

Session 11: Enhancing the multifunctionality of rice systems 345


Remediation effect of rice terraces for strong acidic<br />

and nitrate-rich effluent water from tea bush areas<br />

in the Makinohara plateau of Shizuoka, Japan<br />

Kiyoshi Matsuo, Yuhei Hirono, and Kunihiko Nonaka<br />

To meet the demand for high-quality green tea products, Japanese<br />

tea farmers have applied excess nitrogen fertilizer (over<br />

1 t N ha –1 y –1 ) for a long time. As a result, heavy groundwater<br />

pollution by nitrate occurred in tea areas. Nitrate pollution is<br />

associated with strong acidity because of severe soil acidification<br />

in tea fields. T<strong>here</strong>fore, we evaluated the bioremediation<br />

effect of traditional small-scale rice terraces on effluent water<br />

from tea fields. Many small rice terraces have been used by<br />

farmers for a long time to cultivate rice for their home consumption<br />

near tea plantation areas in the Makinohara plateau<br />

of Shizuoka, Japan. The water remediation effect of those rice<br />

terraces on strong acidic and nitrate-rich effluent water from<br />

tea areas was investigated by a field survey and a field experiment.<br />

For the survey in two rice terrace areas in a traditional<br />

land-use region in Kurasawa, water quality (water temperature,<br />

pH, nitrate concentration, EC) was investigated from<br />

upstream to downstream. Farmers used those rice terraces for<br />

rice cultivation. Results are summarized in Table 1.<br />

A fallow rice terrace at Tann-no-pond, Ogasa-cho,<br />

Shizuoka, was used for an experiment without rice plants. The<br />

effect of paddy on water quality was investigated from June to<br />

October 2001. The experimental area was 180 m 2 and vegetation<br />

was paddy weed = no rice plant. Water management was<br />

submergence and total irrigated water to the plot was 1,946 t<br />

(surface effluent water was only 56 t). The effluent water from<br />

tea bushes was poured into the experimental paddy plot. Water<br />

quality (water temperature, pH, nitrate concentration, EC)<br />

was monitored once a week and some mineral elements ware<br />

measured by ICP or AAS. Table 2 summarizes the results.<br />

Original effluent water from tea bush areas is strongly<br />

acidic at pH 4 to 5 and has high nitrate content, 20 ppm or<br />

more as nitrogen. Occasionally, aluminum was as high as 7<br />

ppm. <strong>Rice</strong> terraces had a marked effect on remediating water<br />

quality. After passing the paddy soil, water pH was neutralized<br />

and nitrate was reduced to half. Aluminum was reduced<br />

below 0.5 ppm. Some field surveys were conducted at the same<br />

Table 1. Water quality in rice terraces farmed at Kurasawa,<br />

Shizuoka.<br />

Sampling point pH Nitrate N a Al Mg<br />

<strong>Rice</strong> terraces A (in) 4.44 33.5 2.2 17.5<br />

<strong>Rice</strong> terraces A (out) 6.09 23.1 0.4 15.8<br />

<strong>Rice</strong> terraces B (in) 5.44 29.3 0.5 16.9<br />

<strong>Rice</strong> terraces B (out) 6.85 13.8 0.5 14.8<br />

Original groundwater 4.28 27.2 5.7 17.4<br />

a Nitrate, aluminum, and magnesium concentrations are in ppm. Data were<br />

gat<strong>here</strong>d in mid-summer 2000. <strong>Rice</strong> terrace A is about 2,500 m 2 with 7<br />

terraces, including slopes, and rice terrace B is about 5,000 m 2 , with 13<br />

terraces. The rice terraces were continuously irrigated. The original groundwater<br />

was measured at a water spring on the upper slope of Makinohara<br />

plateau.<br />

site in Makinohara. We confirmed the remediation effect of<br />

rice terraces for improving local water quality in heavily fertilized<br />

tea plantation areas in Shizuoka, Japan.<br />

Notes<br />

Table 2. Water remediation effect of rice terrace<br />

fields (experimental data in a fallow field).<br />

Sampling point pH Nitrate a Aluminum<br />

Influent water 4.70 24.6 2.74<br />

Paddy water 5.77 17.4 0.99<br />

Groundwater 6.60 9.9 0.31<br />

a Nitrate and aluminum concentrations are in ppm. Aluminum<br />

was measured on 6 different dates, pH and nitrate were measured<br />

once a week from 27 June to 27 October in 2001.<br />

Authors’ address: National <strong>Institute</strong> of Vegetables and Tea Science,<br />

e-mail: matuok@affrc.go.jp.<br />

346 <strong>Rice</strong> is life: scientific perspectives for the 21st century


W<strong>here</strong> are the hot spots of RDB plants in rice paddy fields<br />

A GIS-based analysis using information accumulated<br />

at a natural history museum<br />

Takuya Mineta, Kenji Ishida, and Takashi Iijima<br />

<strong>Rice</strong> paddy fields that occupy artificial wetland maintained by<br />

agricultural practices continue to occupy about 7% of the land<br />

area in Japan. In recent years, rice paddy fields were expected<br />

to be an alternative natural wetland for rapidly decreasing marsh<br />

and moorland caused by development. Numerous aquatic organisms,<br />

which depend on wetland habitat, are threatened with<br />

extinction. T<strong>here</strong> are 191 species of 43 families, including<br />

natural wetland plants with origin in paddy fields, in the entire<br />

region (Kasahara 1954). Now, 49 species of 25 families in<br />

paddy fields are registered with the Red Data Book (RDB) in<br />

the Kanto region as endangered aquatic plants. These plants<br />

are considered as species dependent on the rice culture environment<br />

(= agro-dependent species), although information is<br />

lacking about characteristics of the habitat and distribution.<br />

We should be enhancing multifunctionality such as the<br />

preservation of both biodiversity and productivity in paddy<br />

fields to ensure a sustainable rice-cropping system in the world.<br />

On the other hand, Myers et al (2000) suggested “biodiversity<br />

hot spots,” w<strong>here</strong> exceptional concentrations of endemic species<br />

are undergoing an exceptional loss of habitat, to support<br />

the most species. To enable us to pinpoint conservation priorities,<br />

we need knowledge of hot spots w<strong>here</strong> endangered and<br />

agro-dependent species are concentrated in rural areas. We<br />

attempt to find a hot spot of endangered aquatic plants using<br />

information accumulated at a natural history museum on geographic<br />

information systems (GIS).<br />

This paper attempts to provide useful information on sustainable<br />

agriculture for the harmonious co-existence of<br />

biodiversity.<br />

Extraction of a hot spot of<br />

RDB plants<br />

GSIS process<br />

Analysis of characteristics<br />

of the habitat of each species<br />

Selection of endangered plants<br />

Specimen data input into database<br />

Creation of positional information<br />

(Low accuracy)<br />

Meshing<br />

Mapping<br />

Extraction of hot spots<br />

(High accuracy)<br />

Pointing<br />

Habitat information on specimens<br />

(Digital National Land Information)<br />

Land-use chart<br />

Extraction of<br />

paddy use<br />

Developing a database<br />

Habitat classification of plants<br />

Soil classification<br />

Extraction of<br />

ill-drained paddy<br />

How can we find a hot spot<br />

Figure 1 describes the process to find a hot spot of aquatic<br />

endangered plants and to understand the characteristics of their<br />

habitat. A detailed procedure follows.<br />

A survey was conducted in Tochigi Prefecture, which is<br />

located in the northern Kanto region (within 100 km of Tokyo)<br />

and occupies approximately 640,000 ha. Tochigi Prefecture<br />

has been accumulating geographic information on wildlife<br />

in standard grid squares (approximately 1 × 1 km). First,<br />

31 species of endangered hygrophilous plants were targeted in<br />

this study: they are selected based on records on paddy environment<br />

and natural wetland although their population has been<br />

decreasing rapidly. Second, we obtained a database with information<br />

such as collection location, date, and habitat information<br />

from botanical specimens stored at the Tochigi Prefectural<br />

Museum (at Ustunomiya City, Tochigi Prefecture). Then,<br />

Grasp of distribution pattern<br />

Fig. 1. Flow chart to find hot spots of endangered plants, and to<br />

analyze distribution pattern based on GIS, using the habitat data<br />

of botanical specimens.<br />

the database of a collection location of select RDB plants was<br />

arranged by standard grid squares to be able to analyze the<br />

distribution in detail. Furthermore, if we know a site w<strong>here</strong><br />

RDB plants were collected with higher precision, we could<br />

obtain point data and analyze habitat with more information<br />

about endangered species.<br />

From information on RDB plants in Tochigi Prefecture,<br />

we were able to make a map of 197 grids, which observed the<br />

RDB plants on GIS. Multiple endangered species were observed<br />

on 75 grids, particularly at the Watarase Retarding Ba-<br />

Session 11: Enhancing the multifunctionality of rice systems 347


Paddy field<br />

dominance type<br />

River<br />

dominance type<br />

Hill-bottom<br />

dominance type<br />

Endangered species 0 20 40 60 80 100 (%)<br />

Rotala leptopetala<br />

Blyxa echinosperma<br />

Azolla japonica<br />

Eusteralis stellata<br />

Utricularia multispinosa<br />

Ceratopteris thalictroides<br />

Rorippa cantoniensis<br />

Eriocaulon cinereum<br />

Microcarpaea minima<br />

Salvinia natans<br />

Tillaea aquatica<br />

Gratiola japonica<br />

Monochoria korsakowii<br />

Inula britannica<br />

Rumex nipponicus<br />

Salvia plebeia<br />

Penthorum chinense<br />

Deinostema adenocaulum<br />

Najas foveolata<br />

Blyxa japonica<br />

Sagittaria aginashi<br />

Najas japonica<br />

Eriocaulon hondoense<br />

Ottelia japonica<br />

Isoetes japonica<br />

Utricularia australis<br />

Polygonum taquetii<br />

Ixeris makinoana<br />

Rotala pusilla<br />

Ludwigia greatrexii<br />

Eusteralis yatabeana<br />

Paddy fields Upland fields Rivers or lakes<br />

Forests Residence Others<br />

Fig. 2. Land use of areas around which RDB plants appeared. *Among plants in each type,<br />

significant differences were found as to their habitat (χ 2 test, χ 2 = 161.74, P


1. Paddy field dominance type (the majority of land is<br />

used for paddy fields).<br />

2. River or lake dominance type (consists mainly of riverside<br />

land and riverbanks).<br />

3. Hill-bottom dominance type (consists mainly of forests<br />

and small paddy fields).<br />

These data suggest that each group of RDB plants has a<br />

different habitat. The majority of hot spots were observed in<br />

the hill-bottom-type area, w<strong>here</strong> forests accounted for more<br />

than 50% of the land. We call such small rice fields yachida or<br />

yatsuda spreading out over the hill-bottom.<br />

Discussion<br />

From the overlying data on land use, plants collected, and performed<br />

agricultural development projects, we understood that<br />

RDB plants were preserved under stable land use. In addition,<br />

we were able to confirm a few RDB plants such as Isoetes<br />

japonica, Eusteralis stellata, and Microcarpaea minima in the<br />

area w<strong>here</strong> agricultural development took place. For harmony<br />

with an improvement in infrastructure and conservation of<br />

biodiversity in the rural environment, we could obtain the necessary<br />

information by detailed analysis of a habitat in the future.<br />

However, most current hot spots are places w<strong>here</strong> agricultural<br />

development projects have not yet been carried out.<br />

We can use information about the hot spots of threatened<br />

aquatic plants that have different habitats depending on<br />

land use as indices for agricultural development projects that<br />

consider the environment.<br />

When using specimen information, data on botanical<br />

specimens should be handled carefully because information<br />

about collected areas and years may be biased, or t<strong>here</strong> might<br />

be a lack or nonuniformity of information about the collection<br />

location and the habitats of plants. The following are issues.<br />

To use specimen information, it is important to develop a database<br />

with enormous amounts of information on specimens<br />

stored in a museum of the whole country. In addition, information<br />

on latitude, longitude, and altitude has to be unified. Detailed<br />

habitat descriptions are also important for site information,<br />

since analysis on habitat and distribution needs various<br />

sources of information.<br />

We describe how to find a hot spot of endangered plants<br />

by using the habitat data of botanical specimens in combination<br />

with GIS. Then, by overlapping a land-use chart with the<br />

GIS, we can understand the characteristics of their habitat.<br />

References<br />

Kasahara Y. 1954. Studies on the weeds of arable land in Japan, with<br />

special reference to kinds of harmful weeds, their geographic<br />

distribution, abundance, life-length, origin and history. Ber.<br />

Ohara Inst. Landw. Forsch. 10:72-116.<br />

Myers N, Mittermeier RA, Mittermeier CG, da Fonseca GAB, Kent<br />

J. 2000. Biodiversity hotspots for conservation priorities.<br />

Nature 403:853-858.<br />

Notes<br />

Authors’ address: National <strong>Institute</strong> for Rural Engineering, Japan,<br />

e-mail: minetaku@nkk.affrc.go.jp; ishida@nkk.affrc.go.jp;<br />

tiijima@affrc.go.jp.<br />

Wrap-up of Session 11<br />

Session 11 featured discussion on the various values and roles<br />

in our lives as a whole fulfilled by rice cultivation with paddy fields<br />

and irrigation under the designated theme. A welcome was given<br />

by H. Satoh, president of the National <strong>Institute</strong> for Rural Engineering<br />

(NIRE), K. Miyamaoto, executive director of NIRE, and Y.<br />

Tsutsui, convener. The session, with about 200 participants from<br />

various countries, discussed the subject of inquiry raised by Professor<br />

R. Nakamura in his earlier keynote speech. K. Yamaoka,<br />

co-convener, proposed recalling the following arguments summed<br />

up by Professor Nakamura.<br />

1. Water is indispensable to rice cultivation. Sustainable<br />

irrigated rice paddy agriculture is crucial for developing humans’<br />

future.<br />

2. Increasing water-use efficiency, namely, water productivity,<br />

is in fashion and seems to be our universal mission.<br />

3. However, we have to note that in humid regions it is<br />

rational to use ample water to substitute for farmers’ labor,<br />

w<strong>here</strong>as in arid regions constantly valuable water cannot be replaced<br />

by other resources. (In humid regions, developing appropriate<br />

water resource allocation systems for occasional dry spells<br />

is most important to increase real water-use efficiency.)<br />

4. Ample agricultural water in humid regions generates vast<br />

externalities that cannot be priced through market mechanisms.<br />

5. Significance of the externalities has been maintained<br />

but has shifted its weight from benefits to farmers to those for<br />

the public (town dwellers) according to the socioeconomic development<br />

of the country.<br />

6. Policy implications for publicly facilitating sustainable<br />

irrigated rice paddy agriculture in restoring a natural balance should<br />

be further promoted in various development stages of countries<br />

in the Asian monsoon region.<br />

K. Yamaoka also presented the background and purpose<br />

of the session. It was expected to feature discussions to endorse<br />

the arguments and to sum up the main points of the arguments<br />

to be contributed to discussions at the OECD, the Fourth World<br />

Water Forum, and relevant international conferences. Eight contributors<br />

made presentations from various interdisciplinary aspects.<br />

The first contributor, T. Masumoto from Japan, stated that<br />

the geographical, climatological, and hydrological characteristics<br />

Session 11: Enhancing the multifunctionality of rice systems 349


of the region have led to paddy rice farming having an advantage<br />

in environmentally friendly characters as well as crop productivity<br />

over other types of farming anyw<strong>here</strong> in the Asian monsoon region.<br />

He contrasted paddy rice farming with farming in upland<br />

fields in an arid climate and reviewed the major methodologies<br />

and results for assessing various socioeconomic externalities<br />

generated by paddy rice-farming activities, including quantitative<br />

and monetary assessment.<br />

D. Groenfeldt from the United States stressed the importance<br />

of intangible benefits to social, cultural, spiritual, and aesthetic<br />

life contributed by paddy cultivation to rural livelihoods in<br />

the broadest sense. He criticized the negative effects of the Green<br />

Revolution on cultural ways of life in rice paddy cultivation introduced<br />

by modern materialism and professional aspirations and<br />

identified the roles of paddy rice cultivation in rural quality of life<br />

as social structure, cultural identity, religion and spirituality, and<br />

aesthetic beauty. He concluded that a participatory methodology<br />

for studying livelihood happiness should be developed for describing<br />

people’s vision of their life, taking into consideration four<br />

pillars of happiness: economic development, cultural heritage,<br />

environment, and governance.<br />

N. Sutawan from Indonesia emphasized the need to preserve<br />

irrigated rice culture because of its multifunctional roles<br />

with invaluable positive externalities. He pointed out the rapid<br />

conversion of paddy fields to other nonfarming usage as one of<br />

the greatest threats to the sustainability of irrigated rice culture.<br />

He concluded that sustainability depends on sustainable water<br />

circulation at a basin scale, including several irrigation systems<br />

as well as sustainability of irrigation institutions and networks,<br />

rice production, ecosystems, and socio-cultural values featured<br />

by each independent irrigation system.<br />

L. Yulong from China mentioned that current Chinese food<br />

production, including rice, has declined by 15% and he pointed<br />

out the difficulty in expanding farm land because of the limitation<br />

of land and water resources. He illustrated the multifunctional<br />

roles and technologies of the Dujiangyan Irrigation Area, China’s<br />

oldest and biggest irrigation area, including a case study for aquaculture<br />

in and beside paddy fields, contributing to poverty alleviation,<br />

the regional economy, indigenous culture, biodiversity, and<br />

system sustainability.<br />

K. Athukorala from Sri Lanka described the terrible situation<br />

brought about by the decommissioning of rainfed paddy fields<br />

in southern Sri Lanka with abundant precipitation. She mentioned<br />

that the soil of the decommissioned paddies acted like a sponge<br />

in absorbing moisture. She concluded that the situation causes<br />

groundwater aquifers to deteriorate for water of city dwellers and<br />

increases floods downstream even around the parliament building<br />

in the capital city as well as threatening food security of people<br />

in Sri Lanka.<br />

K. Hidaka from Japan proposed a definition of true<br />

biodiversity depending upon rice ecosystems as different from<br />

that of conventional apparent biodiversity. He also proposed integrated<br />

research for organizing the three methods of collecting<br />

specimens, reviewing records in the literature, and ecological fieldwork.<br />

He emphasized a need for integration between the conservation<br />

of biodiversity and agricultural production, with a new concept<br />

of integrated biodiversity management for managing agricultural<br />

activity in hotspot villages for species such as the giant<br />

water bug.<br />

Y. Yuyama from Japan introduced floating-rice cultivation<br />

in regularly inundated areas in Thailand. He assessed its potential<br />

function for mitigating flood and providing water resources in<br />

Bangkok, located downstream, taking into consideration the development<br />

of facilities such as diversion dams and drainage regulators<br />

controlling water level in the area. He concluded that the<br />

monitoring of water flow, water operations, and cultivation conditions<br />

is essential and the decision support system for water operations<br />

is a key technology.<br />

Finally, C. Boonlue from Thailand introduced a new challenging<br />

program used to measure and improve the<br />

multifunctionality of paddy fields in the northeastern region of<br />

Thailand. He mentioned the intensive experiments to collect data<br />

in paddy fields on evaporation, transpiration, percolation, and<br />

infiltration as well as data on runoff at the subbasin and wholebasin<br />

level. He anticipated the development of a model to describe<br />

water use of paddy cultivation and its effects on surface<br />

and underground water and return flow in the basin as well as on<br />

various rice ecosystems.<br />

Many valuable comments were made after each presentation.<br />

The discussions are summarized as follows.<br />

The significance of rice systems in the Asian monsoon region<br />

was attributed to centuries of sustainability of paddy farming,<br />

which has produced different socioeconomic externalities as<br />

well as food for people. The excellent power of rice farming to<br />

feed people and to form sustainable and harmonious societies is<br />

evidenced by the fact that, in this region, 54% of the world’s<br />

population survives on only 14% of the world’s land area. People’s<br />

ceaselessly striving to produce rice under extreme water conditions<br />

such as frequent flood and occasional water shortage has<br />

molded their stable and mutually dependent communities as well<br />

as their basic lifestyle and culture closely connected with water.<br />

Paddy rice farming in the Asian monsoon region now accounts<br />

for about 90% of the world’s rice production and about half of<br />

the world’s freshwater use. Centuries of sustainability of paddy<br />

farming with broad socioeconomic externalities have gone by with<br />

massive water use.<br />

However, the broad positive externalities of rice paddy farming<br />

and irrigation for such ecosystems, sound water circulation,<br />

and socioeconomic stability have deteriorated with the development<br />

of the market economy because nobody pays compensation<br />

for the externalities through market mechanisms. Though it<br />

is important to improve water-use efficiency, namely, economic<br />

water productivity in farming in water-deficient regions, we should<br />

also promote enhancing the multifunctionality of rice systems,<br />

not only for sustainable rice paddy farming in the Asian monsoon<br />

region but also for sustaining and making optimal use of global<br />

water resources.<br />

We were satisfied with the interdisciplinary discussions with<br />

the selected speakers from various fields in international research.<br />

We are strongly convinced that we need to promote further research<br />

activities in this area.<br />

350 <strong>Rice</strong> is life: scientific perspectives for the 21st century


SESSION 12<br />

Conservation of soil, water,<br />

and environment in rice cultures<br />

CONVENER: M. Saito (NARO)<br />

CO-CONVENERS: S. Itoh (NIAES) and T. Nozoe (<strong>IRRI</strong>)


Paddy soils around the world<br />

K. Kyuma<br />

The world’s annual rice production reached 589 million tons<br />

in 2003 (FAO 2004). It exceeded that of wheat and amounted<br />

to 28.4% of the world’s total cereal output. Maize production<br />

has recently surpassed that of rice, but its increase is mainly to<br />

meet the demand for animal feed and not for immediate human<br />

consumption. Thus, rice as the staple for the human diet<br />

is becoming increasingly important in Asia and in some parts<br />

of Africa and the Americas, feeding nearly half of the world’s<br />

population today.<br />

According to <strong>IRRI</strong> (2002), some 11% of the total area<br />

cultivated for rice worldwide is in uplands, the rest being in<br />

wetlands, either as rainfed, deepwater, or irrigated paddies.<br />

As upland rice is generally much less productive, rice production<br />

in paddy soils should definitely exceed 90% or even 95%<br />

of the total global output. This justifies my confining this discussion<br />

to only paddy soils.<br />

Natural settings of paddy lands<br />

T<strong>here</strong> are some 135 million ha of paddy lands in the world, of<br />

which 126 million ha, or 93%, are in monsoon Asia, or in humid<br />

East, Southeast, and South Asia (<strong>IRRI</strong> 2002). Climate and<br />

landforms are the two determinants for this strongly biased<br />

distribution of paddy lands (Kyuma 2004). Monsoon climate<br />

is characterized by a yearly inversion of wind direction and<br />

this accompanies alternating rainy and dry seasons. T<strong>here</strong>fore,<br />

rainfall is concentrated during the rainy season, often bringing<br />

more than 1,000 mm of rain in less than half a year, thus enabling<br />

cultivation of a rice crop. In terms of landforms, monsoon<br />

Asia features an exceptional abundance of lowlands (Table<br />

1). Being in the region of active orogeny and volcanism, in<br />

combination with high rainfall, monsoon Asia undergoes severe<br />

erosion in its high mountainous lands and deposition in<br />

its riparian and coastal lowlands, producing extensive floodplains<br />

and deltas in the middle and lower reaches of gigantic<br />

rivers such as the Yangtze, Mekong, Brahmaputra, and Ganges.<br />

These lowlands are naturally inundated with monsoon rains<br />

during the rainy season.<br />

As depicted above, monsoon Asia, with its high seasonal<br />

concentration of rainfall and its exceptionally extensive area<br />

of lowlands, provides Oryza sativa, a plant species native to<br />

the region, with the most adapted natural habitat. Thus, rice<br />

culture originated as an adaptation to the given natural settings<br />

of monsoon Asia. Later expansion of paddy lands has<br />

been made possible mainly by the provision of irrigation.<br />

A small share of indigenous rice culture with O.<br />

glaberrima is known to exist in West Africa, but it has been<br />

narrowly confined to its place of origin throughout history, for<br />

the climate and landforms of the region are not favorable for<br />

its propagation.<br />

Table 1. Importance of alluvial land (in 10 6 ha).<br />

Region<br />

Land area<br />

Characteristics of paddy soils<br />

Alluvial soil area<br />

Total Potentially Total Potentially<br />

arable<br />

arable<br />

World 13,000 3,152 588 316<br />

Asia a 2,704 620 – 192<br />

Tropics 4,893 1,652 365 172<br />

Tropical Asia 987 344 168 114<br />

a<br />

Excluding the former USSR.<br />

Source: White House (1967).<br />

Any soil that is used for growing aquatic rice can be called a<br />

paddy soil. Paddy soil in this definition is related directly to<br />

land use, but not to any particular type of soil in a pedological<br />

sense. Paddy soils occur basically in lands with an aquic (note:<br />

this is a technical term used in U.S. Soil Taxonomy and widely<br />

recognized as a term to denote hydromorphic conditions) moisture<br />

regime, in floodplains, deltaic plains, fans, and terraces.<br />

Fluvisols, Gleysols, and Cambisols are the most common pedological<br />

members of paddy soils, but some other members,<br />

such as Acrisols and Luvisols, occur among paddy soils on<br />

older land surfaces. Eswaran et al (2001) also listed all the soil<br />

orders of soil taxonomy except Gelisols as soils used for aquatic<br />

rice cultivation, but they also indicated that Inceptisols and<br />

Ultisols are the most frequently used.<br />

Irrespective of their pedological nature, all paddy soils<br />

are submerged for at least a few months a year, either naturally<br />

or artificially. Managing paddy soils under water is entirely<br />

different from managing other soils used for upland crops, and<br />

this produces important differences, particularly in chemical<br />

and biochemical or microbiological processes. However, paddy<br />

soils are also kept drained for the rest of the year, again naturally<br />

or artificially. This cyclic change in micro-environmental<br />

conditions exhibits properties not encountered in other soils<br />

and differentiates paddy soils from most other soil systems.<br />

The most important change upon submerging a soil is a<br />

decrease in oxygen partial pressure, which accompanies a lowering<br />

of redox potential (Eh), reduction of chemical species<br />

[O 2 →H 2 O, NO 3 – →N 2 , Mn(IV)→Mn(II), Fe(III)→Fe(II),<br />

SO 4 2– →S 2– , CO 2 →CH 4 ], elevation of soil pH, and changes in<br />

biotic composition (aerobic to anaerobic) (Table 2). All these<br />

changes further induce enhanced nitrogen availability and its<br />

fixation, solubilization of soil phosphates, and so forth.<br />

Draining a paddy soil reverses most of the above processes:<br />

Eh rises, chemical species are oxidized, soil pH decreases,<br />

and aerobic soil biota recover. However, some of the<br />

352 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 2. Reduction processes and microbial metabolism in submerged soils.<br />

Stage of Chemical Initial Eh 7 Expected pattern of Formation of Formation of Formation of Hypothetical pattern of Redox state<br />

reduction transformation in soil, V energy metabolism NH 4 -N CO 2 organic acids organic matter decomposition<br />

First Disappearance of 0.5 Aerobic respiration Rapid process Rapid process Usually not accumulated Aerobic and semianaerobic Oxidized<br />

molecular oxygen without fresh organic matter decomposition process<br />

Disappearance of nitrate 0.4 Nitrate reduction Weakly reduced<br />

Formation of Mn II 0.4 (Mn III, IV reduction) Moderately<br />

reduced<br />

Formation of Fe II 0.2 (Fe III reduction)<br />

Second Formation of S –II 0 Sulfate reduction Slow process Slow to stagnant Early stage: rapid accumulation Anaerobic decomposition Strongly reduced<br />

process process<br />

Formation of methane –0.2 Methane fermentation Advanced stage: rapid decrease<br />

Formation of hydrogen –0.2 Fermentation Formation and decomposition<br />

of formic acid<br />

Source: Takai (1978, partly modified).<br />

changes are irreversible, for example, “ferrolysis” proceeds in<br />

every cycle of submergence and drainage, impoverishing soil<br />

basic cations and leading to Al-interlayering and eventual destruction<br />

of smectitic clay lattices (Kyuma 2004).<br />

Intrinsic merits and demerits of the paddy soil/rice system<br />

In comparison with the soils used for growing upland crops,<br />

paddy soils cropped to aquatic rice have many intrinsic merits<br />

and some demerits. Among the merits, the following can be<br />

enumerated: (1) a higher natural supply of nitrogen, bases, and<br />

silica; (2) higher availability of soil phosphorus; (3) relative<br />

indifference to soil physical properties; (4) detoxification of<br />

excessive nutrients; (5) detoxification of many agrochemicals;<br />

(6) perfect resistance to soil erosion; (7) relative ease of weeding;<br />

(8) tolerance for monoculture; and (9) carbon sequestration<br />

(Kyuma 2004).<br />

Some of these merits contribute to higher land productivity<br />

of rice relative to upland cereals, and others contribute<br />

to higher stability of rice farming. It deserves a special mention<br />

that routine production techniques such as land leveling<br />

and bund construction for submerging the rice field simultaneously<br />

serve to protect the land from erosion and degradation.<br />

All in all, these intrinsic merits confer upon the paddy<br />

soil/rice system the highest sustainability among existing food<br />

production systems in the world.<br />

Some demerits, however, are also intrinsic to paddy rice<br />

cultivation, such as potential pollution hazards for water and<br />

air. In countries with a high fertilizer use, paddy fields are considered<br />

to be the largest potential nonpoint source of pollutants,<br />

particularly nitrogen and phosphorus, for water bodies.<br />

Globally, paddy soils are said to be responsible for 11% of<br />

total annual methane emissions (IPCC 1995). For researchers<br />

of the paddy soil/rice system, it is imperative to strive to lessen<br />

these local as well as global environmental hazards incurred<br />

by paddy rice cultivation.<br />

Conclusions<br />

The world population is still increasing and it is forecast to<br />

reach nine billion by 2050. If demand for rice increases proportionally,<br />

the total production will have to increase by as<br />

much as 50% by mid-century. Taking into consideration the<br />

requirements for climate and landforms in making paddy lands,<br />

prospects will not be great for further expansion of rice area.<br />

The only way to attain the target would be to develop infrastructure<br />

for irrigation and drainage. Even in many traditional<br />

rice-growing countries, irrigated paddies are often less than<br />

half of the total. Provision of better irrigation and drainage<br />

would both enhance the productivity of rice and help to negate<br />

the major demerit of methane emissions from paddy lands.<br />

Session 12: Conservation of soil, water, and environment in rice cultures 353


References<br />

Eswaran H, Moncharoen P, Reich P, Padmanaban E. 2001. <strong>Rice</strong>,<br />

land and people: the faltering nexus in Asia. Proceedings of<br />

the 5th Conference of the East and Southeast Asia Federation<br />

of Soil Science Societies, Krabi, Thailand. Bangkok (Thailand):<br />

Department of Agriculture. p 38-66.<br />

FAO (Food and Agriculture Organization). 2004. FAOSTAT. Rome<br />

(Italy): FAO.<br />

IPCC (Intergovernmental Panel on Climate Change). 1995. Climate<br />

change 1994, radiative forcing of climate change and an evaluation<br />

of the IPCC 1992 IS92 emission scenarios. New York,<br />

N.Y. (USA): Cambridge University Press.<br />

<strong>IRRI</strong> (<strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>). 2002.World rice statistics,<br />

2002. Los Baños (Philippines): <strong>IRRI</strong>.<br />

Kyuma K. 2004. Paddy soil science. Kyoto (Japan): Kyoto University<br />

Press. 280 p.<br />

Takai Y. 1978. Redox processes in the soil under submergence. In:<br />

Kawaguchi K, editor. Suiden-dojyogaku (Paddy soil science).<br />

Tokyo (Japan): Kodan-sha. p 23-55. (In Japanese.)<br />

White House. 1967. World food problem: a report of the president’s<br />

Science Advisory Committee. Vol. II. Report of the Panel on<br />

the World Food Supply. Washington, D.C. (USA): White<br />

House.<br />

Notes<br />

Author’s address: Professor Emeritus, Kyoto University and the<br />

University of Shiga Prefecture, 1-79 Nagatanicho, Iwakura,<br />

Sakyoku, Kyoto 606-0026, Japan.<br />

Sustainability of paddy soil fertility in Vietnam<br />

Ngo Ngoc Hung, Nguyen Bao Ve, Roland J. Buresh, Mark Bayley, and Takeshi Watanabe<br />

Although the Lower Mekong Delta (LMD) covers only 12%<br />

of Vietnam’s total land area, it is the main source of agricultural<br />

products of the country, supplying more than 50% of the<br />

staple food. Among the diverse range of agricultural products<br />

in the Delta, rice is the main crop. It is planted in irrigated<br />

lowlands with three major cropping seasons: winter-spring<br />

(November to February), spring-summer (March to June), and<br />

summer-autumn (July to October), which produce about 56%<br />

of the nation’s total production. Some soils in the Mekong Delta<br />

receive high amounts of fertilizer, either because of the production<br />

of three crops per year or because soils such as acid<br />

sulfate soils require much fertilizer to support production.<br />

Yield of summer-autumn rice in the LMD is usually low<br />

(3–4 t ha –1 ). T<strong>here</strong>fore, the government and farmers are interested<br />

in diversifying continuous lowland rice culture to multiple<br />

cropping. Urea is the main N fertilizer applied to lowland<br />

rice in the Mekong Delta. Phosphorus fertilizers have been<br />

used on some soils in Mekong Delta agriculture for more than<br />

30 years. Especially, along the main rivers, soils have received<br />

P fertilizer for more than 20 years.<br />

The objectives of this research are to (1) determine the<br />

effects of the previous crop on rice yield and the economic<br />

merits of crop rotation, (2) determine phytoplankton activity<br />

in nitrogen fertilizer-use efficiency, and (3) assess the effects<br />

of long-term P fertilization in intensive rice production on cadmium<br />

contamination of soils.<br />

Effects of crop rotations on rice<br />

Field experiments to assess crop rotations with three consecutive<br />

crops per year were conducted on alluvial soils in 2002<br />

and 2003 at Can Tho. Five crops (rice, soybean, maize, sweet<br />

potato, and sesame) were grown in spring-summer and rice<br />

was then grown in winter-spring and summer-autumn seasons.<br />

The experiment was a randomized complete block design<br />

with four replications. All crops received 60 kg P 2 O 5<br />

ha –1 as single superphosphate. The application of N and K 2 O<br />

fertilizer for each crop was 100-30 for rice, 30-60 for soybean,<br />

100-60 for maize, 50-90 for sweet potato, and 60-30 for<br />

sesame. Nitrogen was applied as urea in three equal splits: 1/3<br />

at 10 days after planting (DAP), 1/3 at 20 DAP, and 1/3 at 45<br />

DAP. Potassium was applied as KCl. <strong>Rice</strong> variety IR66 was<br />

used. Soil properties in the top 25 cm were pH = 4.2, organic<br />

C = 2.8%, total N = 0.25%, CEC = 16 cmol c kg –1 , clay = 42%,<br />

and silt = 56%.<br />

A rotation of rice with other crops in nearly all cases<br />

significantly improved rice yield (Table 1). Yield and the apparent<br />

recovery of N fertilizer by summer-autumn rice were<br />

the greatest following sweet potato, and they were greater for<br />

rice following soybean and maize than following rice. Nitrogen<br />

fertilizer-use efficiency was higher following sweet potato<br />

than rice. The decomposition of sweet potato residues in<br />

raised beds after harvesting provided N and potentially improved<br />

soil physical, biological, and chemical processes. In<br />

addition, a symbiotic combination of N 2 -fixing microorganisms<br />

of Azospirillum brasilense with sweet potato roots was<br />

found (Hill et al 1983).<br />

The profit for each cropping system was determined from<br />

grain yield and market price. The profit (US$ ha –1 year –1 ) of<br />

the cropping systems was rice-soybean-rice = 644, rice-sweet<br />

potato-rice = 612, rice-sesame-rice = 586, rice-maize-rice =<br />

503, and rice-rice-rice = 421 (Ngo Ngoc Hung and Nguyen<br />

Bao Ve 2004). Additional research conducted at four locations<br />

during summer-autumn 2001 and 2002 showed that, in all the<br />

cases, rice yield was higher after a 3-month fallow (average:<br />

4.1 t ha -1 ) than with continuous rice cropping (average: 3.8 t<br />

ha –1 ) (Nguyen Bao Ve et al 2002).<br />

354 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. Effect of crop rotation on rice grain yield and N efficiency for 100 kg N ha –1<br />

applied to rice at Can Tho, southern Vietnam. a<br />

Previous crops Summer-autumn Summer-autumn season (2003)<br />

(spring-summer season (2002)<br />

season) (rice grain yield, <strong>Rice</strong> grain AFRN b Ndff % c NUE d<br />

t ha –1 ) yield (t ha –1 )<br />

<strong>Rice</strong> 3.4 a 4.4 a 23 15 19<br />

Soybean 4.2 bc 5.5 c 37 – –<br />

Maize 3.9 ab 4.9 b 33 – –<br />

Sweet potato 4.6 c 6.3 d 52 32 29<br />

Sesame 3.6 ab 4.7 ab 26 – –<br />

LSD 5% 0.67 0.56<br />

a<br />

Numbers followed by the same letter in a column are significant at the 5% level. b Apparent fertilizer N<br />

recovery. c Plant N derived from fertilizer. d Nitrogen fertilizer-use efficiency.<br />

Phytoplankton activity and nitrogen losses in rice fields<br />

The design was a randomized complete block with four replications.<br />

Floodwater pH, urea, ammonium, and biomass of phytoplankton<br />

were monitored after N fertilizer application. Fertilizer<br />

was applied to rice as urea or ammonium sulfate, superphosphate,<br />

and potassium chloride.<br />

The biomass of phytoplankton (dominated by Diatom,<br />

Chlorophyta, Cyanophyta, and Euglenophyta) reached a maximum<br />

within 2–4 days after urea application. During summerautumn,<br />

at 3 days after N fertilizer application, the biomass<br />

reached 8.0 g m –2 in urea plots versus 5.0 g m –2 in ammonium<br />

sulfate plots. Because of daytime consumption by algae of CO 2<br />

dissolved in the floodwater, the floodwater pH rose to > 8 on<br />

some days at the first and second N application. However, t<strong>here</strong><br />

was no significant difference in biomass of phytoplankton or<br />

pH of floodwater between these two treatments after the second<br />

fertilizer application (Watanabe et al 2003). This was conducive<br />

to a rapid conversion of NH 4<br />

+<br />

to gaseous NH 3 .<br />

15 Nitrogen balance research during the dry season of<br />

1990 at Can Tho showed that the fraction of added urea-N not<br />

recovered in the plant and soil, and presumably lost, depended<br />

on the timing of urea application. The estimated N loss for N<br />

applied at 10 DAS was very high (49% of applied N). It decreased<br />

to 25% of the applied N at 20 DAS and 11% of the<br />

applied N at 44 DAS. The distribution of 15 N in the soil plus<br />

roots suggested that leaching was not an important loss mechanism,<br />

and t<strong>here</strong>fore the N loss in this case was presumed to be<br />

due to NH 3 volatilization and denitrification (Ngo Ngoc Hung<br />

et al 1995).<br />

Cadmium content in flooded rice soils<br />

Soil samples from the top 20 cm, which covered three major<br />

soil groups (alluvial soils, acid sulfate soils, and saline soils)<br />

in the LMD, were collected. In addition, P fertilizers used in<br />

the LMD were collected.<br />

Cadmium content in P fertilizers ranged from 0.02 to<br />

2.76 mg kg –1 . The highest content was in imported NPK fertilizer<br />

(2.76 mg kg –1 ), w<strong>here</strong>as some domestic P fertilizers had a<br />

lower Cd content (1.73 mg kg –1 ). Cadmium content in LMD<br />

rice soils ranged from 0.01 to 0.56 mg kg –1 . Generally, the<br />

maximum value of Cd (0.56 mg kg –1 ) in rice soils was lower<br />

than the standard limit of Vietnam (2.0 mg kg –1 ), the EC Directive<br />

(1–3 mg kg –1 ), and Canada (1.4 mg kg –1 ) for Cd in<br />

agricultural soils.<br />

The correlation between duration of P fertilizer use and<br />

Cd content in soil is well recorded (Fig. 1). Cadmium content<br />

was highest in alluvial and acid sulfate soils and relatively lower<br />

in saline soils. This can be attributed to the more intensive<br />

crop cultivation on alluvial soils (3–4 crops year –1 ) than on<br />

saline soils (1–2 crops year –1 ). Although crop cultivation is<br />

not as great on acid sulfate soils (usually 2 crops year –1 ) as on<br />

alluvial soils, the rate of P fertilizer application is higher on<br />

acid sulfate soils (60–90 kg P 2 O 5 ha –1 ) than on alluvial soils<br />

(50–60 kg P 2 O 5 ha –1 ).<br />

In serious cases, increasing soil Cd content could decrease<br />

soil health, reduce crop yield (Steve 1994), and affect<br />

humans by Cd contamination in food. Recent research has<br />

shown that the Cd uptake in crops depends largely on soil and<br />

climatic factors, plant genotype, and agronomic management.<br />

While plant breeding and agronomic management can minimize<br />

soil-plant transfer of Cd, and maximize concentrations<br />

of antagonists to Cd assimilation in humans, implications of<br />

the studies are that inputs of this metal to soil can be minimized<br />

(McLaughlin et al 1999).<br />

Conclusions<br />

The rotation of rice with other crops in nearly all cases significantly<br />

improved rice yield. <strong>Rice</strong> yield was highest after sweet<br />

potato, and the N fertilizer-use efficiency of rice was higher<br />

following sweet potato (29%) than rice (19%). The rotation of<br />

rice with soybean attained the highest profit because soybean<br />

had a high market price.<br />

Floodwater pH is a major factor affecting NH 3 volatilization,<br />

and photosynthetic aquatic biomass has a key role in<br />

increasing floodwater pH. The biomass of phytoplankton,<br />

dominated by Diatom, Chlorophyta, Cyanophyta, and<br />

Euglenophyta, reached a maximum within 2–4 days after urea<br />

Session 12: Conservation of soil, water, and environment in rice cultures 355


Soil Cd content (mg kg –1 )<br />

0.6<br />

0.5<br />

y = 0.0066x + 0.0306, R 2 = 0.32*<br />

0.4<br />

0.3<br />

0.2<br />

0.1<br />

0.0<br />

0 10 20 30 40<br />

Duration of P application (y)<br />

Fig. 1. The correlation between years of P fertilizer application and soil Cd content.<br />

application. Management practices to reduce floodwater N<br />

concentration can help minimize N losses.<br />

Some soils in the Mekong Delta received high amounts<br />

of P fertilizer, which can contain varying degrees of contaminants,<br />

including cadmium. The concentrations were lower than<br />

critical values considered by Vietnamese and some international<br />

levels, but the results indicate an anthropogenic impact<br />

on soil cadmium levels. Concerns about food-chain contamination<br />

should be evaluated.<br />

References<br />

Hill WA, Bacon-Hill P, Crosman SM, Steven C. 1983. Characterization<br />

of N 2 -fixing bacteria associated with sweet potato roots.<br />

Can. J. Microbiol. 29:860-862.<br />

McLaughlin MJ, Parker DR, Clarke JM. 1999. Metals and micronutrients:<br />

food safety issues. Field Crops Res. 60:143-163.<br />

Ngo Ngoc Hung, Singh U, Vo Tong Xuan, Buresh RJ, Padilla JL,<br />

Tran Thanh Lap, Truong Thi Nga. 1995. Improving nitrogenuse<br />

efficiency of direct-seeded rice on alluvial soils of the<br />

Mekong River Delta. In: Denning GL, Vo Tong Xuan, editors.<br />

Vietnam and <strong>IRRI</strong>: a partnership in rice research. Los<br />

Baños (Philippines): <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>.<br />

p 137-149.<br />

Ngo Ngoc Hung, Nguyen Bao Ve. 2004. Effect of crop rotation on<br />

nitrogen use efficiency and yield of summer-autumn rice. Vietnam<br />

Sci. Technol. J. Agric. Rural Dev. 5(2004):634-636.<br />

Nguyen Bao Ve, Ngo Ngoc Hung, Nguyen Thanh Hoi, Pham Duc<br />

Tri, Nguyen Van Nhieu Em. 2002. Effect of soil fertility and<br />

farming practices on rice growth and yield of summer-autumn<br />

rice in the Mekong Delta. Vietnam Soil Sci. J. 16(2002):76-<br />

83.<br />

Steve PM. 1994. Case study 6: effects of heavy metals from sewage<br />

sludge on soil microbes in agricultural ecosystems. In: Ross<br />

SM, editor. Toxic metals in soil-plant systems. John Wiley<br />

and Sons. 247 p.<br />

Watanabe T, Ngo Ngoc Hung, Nguyen Do Chau Giang, Vo Thi Yen<br />

Phi, Tran Chan Bac. 2003. Changes of nitrogen in floodwater<br />

after fertilizer application. In: Development of new technologies<br />

and their practice for sustainable farming systems in the<br />

Mekong Delta. Proceedings of the Final Workshop of JIRCAS<br />

Mekong Delta Project, 25-26 November 2003. Can Tho (Vietnam):<br />

College of Agriculture, Can Tho University. p 373-382.<br />

Notes<br />

Authors’ addresses: Ngo Ngoc Hung and Nguyen Bao Ve, Can Tho<br />

University, Vietnam; Roland J. Buresh, <strong>International</strong> <strong>Rice</strong><br />

<strong>Research</strong> <strong>Institute</strong> (<strong>IRRI</strong>), Philippines; Mark Bayley, University<br />

of Aarhus, Denmark; Takeshi Watanabe, Japan <strong>International</strong><br />

<strong>Research</strong> Center for Agricultural Sciences (JIRCAS),<br />

Japan, e-mail: ngochung@ctu.edu.vn.<br />

Acknowledgments: This research was supported in part by grants<br />

from the projects of CAULES, funded by DANIDA (Danish<br />

<strong>International</strong> Development Agency), and JIRCAS (Japan <strong>International</strong><br />

<strong>Research</strong> Center for Agricultural Sciences).<br />

356 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Managing soil fertility for sustainable rice production<br />

in northeast Thailand<br />

Kunnika Naklang<br />

Thailand is divided geographically into four main regions:<br />

northern, northeast (NE), Central Plain, and southern. Northern<br />

Thailand, with about 22% of the total rice area, contributes<br />

about 26% of the rice production. The NE has 57% of the<br />

total area and 46% of the total production. In the Central Plain,<br />

the rice-growing area is 17% and rice production is 24%. In<br />

southern Thailand, the corresponding percentages are only 4%<br />

and 4%.<br />

Rainfed rice is grown on approximately 4.66 million<br />

hectares or about 92% of the total rice-growing area in northeast<br />

Thailand. The average paddy yield in the 2003 crop season<br />

was 1.81 t ha –1 , versus 3.21 t ha –1 for irrigated lowland<br />

rice in the Central Plain. Among the four regions, rice yield in<br />

the northeast is the lowest because of at least two major constraints,<br />

poor soil and the unpredictable amount and distribution<br />

of rainfall. Low soil fertility recurs every year in the rainfed<br />

lowlands in this region, but the problem of drought does not<br />

occur in the same manner every year (Fukai et al 1995, Ragland<br />

1997).<br />

The quantity of organic matter in the soil is a major indicator<br />

of its quality. To achieve higher grain yield, we should<br />

apply chemical and organic fertilizer. For sustainability, it is<br />

important to incorporate organic matter into the soil. Koopmans<br />

and Goldstein (2001) stated that to improve soil quality we<br />

should treat our organic matter like a bank account. A bank<br />

account lets us deposit, save, and withdraw something we value.<br />

For sustainability, it is important to deposit in the account of<br />

active organic matter in the soil on a regular basis, t<strong>here</strong>by<br />

building cultural fertility. Poulton (1995) summarized that longterm<br />

experiments are essential in determining the factors affecting<br />

soil fertility and sustainable production.<br />

Experiments<br />

Effects of chemical fertilizer and farmyard manure<br />

on grain yield of rice in NE Thailand<br />

Twenty-six experiments were conducted at eight sites in NE<br />

Thailand from 1995 to 1997 to determine the effects of farmyard<br />

manure (FYM) and chemical fertilizers on rice yield in<br />

rainfed areas. Out of eight sites, the experiments were separated<br />

into two experimental plots: one was rainfed and the other<br />

under irrigated conditions. The soil texture was loamy sand at<br />

three sites, sandy loam at three sites, and clayey loam and clay<br />

at one site each. The soil’s pH varied from 4.0 to 5.7. Organic<br />

matter varied from 0.39% to 1.57% and Bray-II P ranged from<br />

7 to 38 mg kg –1 . Nonglutinous, photosensitive, and tall cultivars<br />

RD 15, harvested in mid-November, and KDML 105,<br />

harvested in late November, were used in these experiments.<br />

The fertilizer treatments were nil, FYM (cattle dung at 6.25 t<br />

ha –1 ), PK, NPK, CR-NPK (controlled-release N), all (NPK +<br />

micronutrients), N, and FYM + NPK. The rates of N, P 2 O 5 ,<br />

and K 2 O were all 50 kg ha –1 . <strong>Rice</strong> seedlings were transplanted<br />

at a spacing of 25 × 25 cm at almost all sites except in Tung<br />

Kula Ronghai 1996, w<strong>here</strong> dry seed was broadcast at 62.5 kg<br />

ha –1 .<br />

Soil properties indicate that soil productivity was controlled<br />

by many factors, including soil fertility, environment,<br />

and cultural management. The decline in grain yield under<br />

rainfed loamy sand soil at Ubon was lower than under irrigated<br />

conditions. Late dry-seeded sowing and late transplanting<br />

reduced the growth and yield of rice (Naklang et al 1998).<br />

The results indicated that the most effective fertilizer was N,<br />

which made the average grain yield increase over all sites by<br />

39%. This result reflected that N was the most limiting nutrient<br />

in NE Thailand. The application of PK was effective only<br />

when it was applied with N. The application of NPK gave a<br />

higher grain yield than N applied alone: but only 8%. In loamy<br />

sand soil, the addition of some micronutrients together with<br />

NPK (all) increased grain yield from 2% to 21% compared<br />

with applied NPK. The application of FYM increased grain<br />

yield in many experiments. Average grain yield of FYM was<br />

only 7.5% less than the yield of NPK (mean yield of NPK was<br />

2,425 kg ha –1 ). The additional role of FYM in contributing<br />

NPK was found in some sandy soils. The grain yield of rice<br />

was higher in clay soil than in loamy sand soil when chemical<br />

fertilizer was applied (Table 1).<br />

Long-term effects of rice straw compost<br />

and chemical fertilizer on rice yield<br />

and their residual effects<br />

An experiment has been conducted at the Surin <strong>Rice</strong> <strong>Research</strong><br />

Center since 1976. <strong>Rice</strong> straw compost (RSC) at 0, 3.125, 6.25,<br />

9.375, and 12.5 t ha –1 with and without chemical fertilizer (CF)<br />

at the rate of 50-50-50 kg of N-P 2 O 5 -K 2 O ha –1 was applied for<br />

25 consecutive years (1976-2000). During the first 25 years,<br />

the rice variety used was RD 7, short, nonglutinous, and<br />

nonphotoperiod-sensitive. From 2001 to 2003, residual effects<br />

of 25 years’ application of RSC and CF were also investigated<br />

without any addition of RSC or CF. The rice variety used was<br />

KDML 105.<br />

The results showed that average rice grain yield over 25<br />

years of application of RSC with CF was higher than grain<br />

yield of the application of RSC without CF. <strong>Rice</strong> yield increased<br />

when the rate of RSC increased. The residual effects also<br />

showed that the higher the RSC rate applied, the higher the<br />

rice grain yield obtained (Table 2).<br />

Session 12: Conservation of soil, water, and environment in rice cultures 357


Table 1. <strong>Rice</strong> grain yield average for 3 years (kg ha –1 ) as affected by the application of chemical fertilizer and farmyard manure in different locations in northeast<br />

Thailand. a Loamy sand soil Sandy loam soil Clay soil<br />

Treatment Ubon Ubon Tung Kula Sakon Khon Udon Surin Chumpae Phimai Treatment<br />

irrigated rainfed Ronghai Nakorn Kaen mean<br />

pH 4.2, pH 4.1, pH 4.6, pH 7.1, pH 4.5, pH 5.7, pH 4.0, pH 4.2, pH 4.6,<br />

OM 0.52% OM 0.60% OM 0.77% OM 0.96% OM 0.39% OM 1.32% OM 0.59% OM 1.18% OM 1.57%<br />

Nil 1,316 b 857 cd 1,154 b 1,632 de 1,310 c 2,674 2,271 c 1,993 d 1,426 c 1,634 d<br />

FYM 2,234 a 928 cd 2,016 a 2,488 ab 1,669 bc 2,636 3,192 ab 2,876 c 2,371 b 2,264 c<br />

PK 1,423 b 689 d 1,272 b 1,428 e 1,312 c 2,605 2,314 c 2,206 d 1,639 c 1,655 d<br />

NPK 2,408 a 1,318 abc 1,602 ab 1,981 c 2,224 ab 3,005 2,896 ab 3,473 a 3,168 a 2,425 bc<br />

CR-NPK 2,129 a 1,458 ab 1,638 ab 1,907 cd 2,286 a 3,020 3,045 ab 3,012 bc 3,262 a 2,385 bc<br />

All 2,454 a 1,661 a 2,005 a 2,341 b 2,195 ab 2,773 3,244 a 3,350 ab 3,225 a 2,559 ab<br />

N 2,204 a 1,158 bc 1,252 b 1,990 c 2,152 ab 2,957 2,626 bc 3,077 abc 2,992 a 2,240 c<br />

FYM+NPK 2,624 a 1,424 ab 2,221 a 2,696 a 2,467 a 2,812 3,290 a 3,503 a 3,288 a 2,680 a<br />

Location mean 2,099 1,186 1,645 2,058 1,952 2,810 2,859 2,936 2,681 2,230<br />

a At each site, means followed by a common letter are not significantly different at the 5% level by Duncan’s multiple range test.<br />

Source: Naklang et al (1998).<br />

Table 2. <strong>Rice</strong> grain yield (kg ha –1 ) as affected by rice straw compost (RSC) with and without<br />

chemical fertilizer (CF) and their residual effects (RSC and CF were applied annually from<br />

1976 to 2000 and their residual effects were evaluated from 2001 to 2003). a<br />

Effects of RSC and CF applied Residual effects of RSC and CF<br />

for 25 years on RD 7 grain yield on KDML 105 grain yield<br />

RSC rate<br />

(kg ha –1 ) CF rate (kg of N-P 2 O 5 -K 2 O ha –1 ) CF rate (kg of N-P 2 O 5 -K 2 O ha –1 )<br />

0-0-0 50-50-50 RSC mean 0-0-0 50-50-50 RSC mean<br />

0 2,409 3,308 2,858 e 2,498 2,961 2,728 c<br />

3,125 2,831 3,877 3,354 d 3,040 3,215 3,127 b<br />

6,250 3,161 3,999 3,580 c 2,983 3,410 3,197 b<br />

9,375 3,344 4,188 3,766 b 3,436 3,675 3,555 a<br />

12,500 3,527 4,360 3,944 a 3,542 3,656 3,598 a<br />

CF-mean 3,054 B 3,946 A 3,099 B 3,383 A<br />

a In each column, means followed by a common letter are not significantly different at the 5% level by Duncan’s<br />

multiple range test.<br />

Naklang and Rojanakusol (1992) also reported the longterm<br />

effects of compost, green manure (sunnhemp: Crotalaria<br />

juncea Linn.), and dry rice straw incorporated into soil at 0,<br />

6.25, 12.5, 18.75, and 25 t ha –1 for 8 years and 5 years without<br />

any organic or inorganic fertilizer. The rice varieties were<br />

KDML 105 and RD 7. Grain yield of KDML 105 increased<br />

with an increasing rate of compost, w<strong>here</strong>as RD 7 gave the<br />

highest response to green manure followed by compost. The<br />

application of green manure up to 18.75 t ha –1 gave a higher<br />

grain yield of KDML 105 and then dropped at the rate of 25 t<br />

ha –1 . Dry rice straw gave the lowest yield among three materials.<br />

The residual effects of dry rice straw and compost gave no<br />

difference in grain yield and obtained a higher rice yield than<br />

the residual effects of green manure.<br />

The annual application of 1.5 kg dry matter ha –1 of leaf<br />

litter differed in the breakdown rate from a legume crop and<br />

three kinds of trees for five seasons resulted in an increase in<br />

rice grain yield of 23–48% above the no-leaf-litter control<br />

(Whitbread et al 1999) and increased the total and labile carbon<br />

pool in the soil by 24–37% (Naklang et al 1999). A higher<br />

rate of chemical fertilizer did not result in increased soil carbon.<br />

Crop residue, leaf litter, and green manure with slow breakdown<br />

rates are needed to rehabilitate soil C and nutrients, which<br />

will benefit the following crop. In the NE Thailand climate,<br />

t<strong>here</strong> is significant potential for a rapid breakdown of any re-<br />

358 <strong>Rice</strong> is life: scientific perspectives for the 21st century


maining residue during the first rain of the next season, but<br />

before the crop can use the nutrients that are released (Naklang<br />

et al 1999).<br />

Supapoj et al (1998) reported on some long-term experiments<br />

conducted in the sandy soils of NE Thailand. The<br />

application of rice husks at 3.13 t ha –1 annually for 17 years<br />

showed that the application of rice husks alone and plus chemical<br />

fertilizer produced grain yield about 15% and 74% higher<br />

than the no-fertilizer control treatment (1.97 t ha –1 ). In dryseeded<br />

rice cultivation, straw mulching gave better grain yield.<br />

The effects of integrating mungbean (Vigna radiata) with rice<br />

(mungbean seeds were broadcast together with rice seed) on<br />

rice yield were less because mungbean did not establish well<br />

under water-saturated acid infertile soil.<br />

The importance of both organic and inorganic (chemical<br />

or synthetic) fertilizer has been recognized for the supply<br />

of plant nutrients to ensure efficient crop production. These<br />

fertilizers have some weak and strong points.<br />

Although the application rate of organic materials was<br />

higher than that of chemical fertilizer and they needed more<br />

labor to prepare and apply to or incorporate into the soil, they<br />

decomposed and served as a very important source of plant<br />

nutrients and also accumulated as organic matter to maintain<br />

long-term soil fertility. To avoid hard work and the transportation<br />

of organic fertilizer, field crops, trees, and shrub legumes<br />

could be introduced to grow in rice fields for producing biomass.<br />

Recently, many countries have become interested in organic<br />

agriculture. Also, the Thai government announced Surin<br />

as an Organic Farming Model Pilot Project in November 2001.<br />

Some of the principles of organic crop production are to protect<br />

and minimize all forms of pollution of soil water and air<br />

as a result of agricultural practices, to develop and implement<br />

a soil improvement program and maintain long-term soil fertility,<br />

to maintain biodiversity within the farming system, to<br />

recycle plant materials and resources within the farm, and to<br />

handle products and processing methods to maintain the organic<br />

integrity and vital qualities of produce from harvesting<br />

to consumption.<br />

Many research results can be applied and introduced to<br />

farmers and can support some principles in sustainable and<br />

organic crop production. In the future, research will focus on<br />

green manure and organic fertilizer management, develop cropping<br />

systems in organic rice fields, and evaluate the effects of<br />

organic rice production on soil quality.<br />

Conclusions<br />

<strong>Rice</strong> productivity and paddy soil fertility in northeast Thailand<br />

can be improved by using chemical fertilizer and organic<br />

fertilizer such as compost, farmyard manure, rice straw, rice<br />

husk, and leaf litter. Apart from management of the cropping<br />

system, the use of perennial shrubs or tree legumes as a source<br />

of leaf litter has been recommended by planting these trees<br />

near (or on the bund of) the paddy field.<br />

References<br />

Fukai S, Rajatasereekul S, Boonjung H, Skulkhu E. 1995. Simulation<br />

modeling to quantify the effect of drought for rainfed<br />

lowland rice in northest Thailand. In: Fragile lives in fragile<br />

ecosystems. Proceedings of the <strong>International</strong> <strong>Rice</strong> <strong>Research</strong><br />

Conference, 13-17 Feb. 1995. Manila (Philippines): <strong>International</strong><br />

<strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>. 976 p.<br />

Koopmans C, Goldstein W. 2001. Soil organic matter budgeting in<br />

sustainable farming with applications to southeastern Wisconsin<br />

and northern Illinois. Bulletin No. 7. Michael Fields Agricultural<br />

<strong>Institute</strong>. 39 p.<br />

Naklang K, Rojanakusol S. 1992. Long-term effect of compost, green<br />

manure and rice straw on rice yield and their residual effects.<br />

<strong>Rice</strong> Res. J. 1:31-41. (In Thai, English abstract.)<br />

Naklang K, Harnpichitvitaya D, Wade LJ, Jearakongman S, Ekasit<br />

Skulkhu E, Romyen P, Phasopa S, Suriya-arunroj D,<br />

Khunthasuvon S, Kraisorakul D, Youngsuk P. 1998. Management<br />

× environment interaction and quantification of factors<br />

limiting productivity of rainfed lowland rice in Northeast<br />

Thailand. In: Annual rice research report for 1998. Bangkok<br />

(Thailand): <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>. p 639-666.<br />

Naklang K, Whitbread A, Lefroy R, Blair G, Wonprasaid S, Konboon<br />

Y, Suriya-arunroj D. 1999. The management of rice straw,<br />

fertilizers and leaf litter in rice cropping systems in Northeast<br />

Thailand. 1. Soil carbon dynamics. Plant Soil 209:21-28.<br />

Poulton PR. 1995. The importance of long-term trials in understanding<br />

sustainable farming systems: the Rothamsted experience.<br />

Austr. J. Exp. Agric. 35:825-834.<br />

Ragland JL. 1997. Managing soil acidity in northest Thailand. In:<br />

Fukai S, Cooper M, Salisbury J, editors. Breeding strategies<br />

for rainfed lowland rice in drought-prone environments. Proceedings<br />

of an <strong>International</strong> Workshop held at Ubon<br />

Ratchathani, Thailand, 5-8 November 1996. ACIAR Proceedings<br />

No. 77. p 286-299.<br />

Supapoj N, Naklang K, Konboon Y. 1998. Using organic material to<br />

improve soil productivity in rainfed lowland rice soils. In:<br />

Ladha JK, Wade LJ, Dobermann A, Reichardt W, Kirk GJD,<br />

Piggin C, editors. 1998. Rainfed lowland rice: advances in<br />

nutrient management research. Proceedings of the <strong>International</strong><br />

Workshop on Nutrient Reserch in Rainfed Lowlands, 12-15<br />

Oct. 1998, Ubon Ratchathani, Thailand. Manila (Philippines):<br />

<strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>. p 161-168.<br />

Whitbread A, Blair G, Naklang K, Lefroy R, Wonprasaid S, Konboon<br />

Y, Suriya-arunroj D. 1999. The management of rice straw,<br />

fertilizers and leaf litter in rice cropping systems in northeast<br />

Thailand. 2. <strong>Rice</strong> yield and nutrient balance. Plant Soil 209:29-<br />

36.<br />

Notes<br />

Author’s address: Surin <strong>Rice</strong> <strong>Research</strong> Center, Surin, Thailand,<br />

32000, e-mail: kunnika_naklang@hotmail.com.<br />

Session 12: Conservation of soil, water, and environment in rice cultures 359


Site-specific nutrient management and the sustainability<br />

of phosphorus and potassium supply in irrigated rice soils<br />

of Asia<br />

C. Witt, A. Dobermann, R. Buresh, S. Abdulrachman, H.C. Gines, R. Nagarajan, S. Ramanathan, P.S. Tan, and G.H. Wang<br />

The management of soil phosphorus (P) and potassium (K) is<br />

receiving greater attention in intensive irrigated lowland rice<br />

systems of Asia because of concerns that fertilizer P and K<br />

rates are not optimally adjusted to long-term needs (Greenland<br />

1997, Johnston and Syers 1998). Breeding offers limited opportunities<br />

to change plant nutrient requirements or uptake<br />

efficiencies so that long-term management strategies must focus<br />

on overcoming immediate nutrient deficiencies and maintaining<br />

adequate nutrient balances in the top-soil layer. Current<br />

fertilizer P and K strategies in Asia are still mostly based<br />

on soil tests that have shown little correlation with the effective<br />

nutrient supply to the irrigated rice crop (Dobermann et al<br />

2003b). Site-specific nutrient management (SSNM) allows an<br />

effective management of indigenous P and K supplies by estimating<br />

fertilizer requirements based on yield level, yield response<br />

to fertilizer P and K application, and a nutrient balance<br />

model (Witt et al 2002, 2004). In that approach, fertilizer P<br />

and K maintenance rates are commonly developed based on<br />

only two seasons of on-farm experiments, which may be insufficient<br />

to develop long-term strategies. In this paper, we<br />

evaluate SSNM strategies to prevent soil nutrient depletion<br />

using data from five long-term experiments established from<br />

1968 to 1995 in China, India, Indonesia, the Philippines, and<br />

Vietnam.<br />

Indigenous nutrient supplies<br />

Nutrient supplies from indigenous sources can be estimated<br />

by measuring plant nutrient uptake or grain yield in nutrient<br />

omission plots, which receive all nutrients applied as fertilizer<br />

except for the omitted nutrient of interest (Dobermann et al<br />

2003a). In a large multinational research project, omission plots<br />

have been used for several seasons to estimate the spatial and<br />

temporal variation in indigenous nutrient supplies in farmers’<br />

fields (Dobermann et al 2004). These on-farm experiments have<br />

confirmed for a wide range of soils and growing environments<br />

that farmers’ current fertilizer P and K management causes<br />

slightly positive P balances at a number of sites, while fertilizer<br />

K application is commonly insufficient to balance K removal<br />

with grain and straw. Apart from unavoidable inaccuracies<br />

in the estimation, nutrient balances probably supply limited<br />

information regarding the risk of nutrient depletion, unless<br />

combined with estimates of medium- or long-term changes<br />

in indigenous nutrient supplies. In our past on-farm research,<br />

however, the location of the omission plots was changed every<br />

season in individual farmers’ fields to avoid residual effects<br />

that occur when fertilizer is omitted for longer periods. In the<br />

following, we will re-evaluate this strategy.<br />

Long-term P and K management strategies<br />

In the SSNM approach, fertilizer P and K rates are based on<br />

the yield difference between treatments with optimal fertilizer<br />

use of N, P, and K (NPK) and omission plots that receive all<br />

nutrients except for the omitted one (0P, 0K). Recommended<br />

fertilizer rates would increase with an increasing yield gap<br />

between NPK and 0P or 0K treatments to overcome greater<br />

nutrient limitations. Maintenance fertilizer P and K rates are<br />

suggested w<strong>here</strong> a yield response to P or K application is lacking,<br />

and fertilizer rates would increase with increasing yield<br />

level to balance greater nutrient removal with grain and straw<br />

(Witt et al 2002, Witt and Dobermann 2004). The NPK, 0P,<br />

and 0K treatments were also included in five long-term experiments<br />

with two rice crops per year, and the cumulative<br />

yield differences between NPK and omission plots for a period<br />

of up to 15 seasons are plotted in Figure 1. Differences<br />

were substantial in short- and long-term yield responses to fertilizer<br />

P and K application among sites. Yields were not affected<br />

by K application in India or P application in China in<br />

the first two seasons, and initial yield responses to fertilizer<br />

application were generally small except for Vietnam (P) and<br />

China (K). However, yield responses developed within a few<br />

seasons at all sites except for K application at Omon in the<br />

Mekong River Delta of Vietnam, w<strong>here</strong> annual flooding supplies<br />

a large K load through sedimentation (Nguyen 2003).<br />

Yield responses developed linearly except for China, w<strong>here</strong><br />

yield responses to P but not K application developed exponentially<br />

within eight seasons or four years. Long-term fertilizer<br />

requirements would generally be underestimated if fertilizer<br />

requirements were based only on short-term yield responses<br />

without considering nutrient removal with grain and<br />

straw and the overall input-output balance.<br />

In the absence of a yield response to fertilizer P and K<br />

application, SSNM recommends fertilizer P and K maintenance<br />

rates that are calculated based on a nutrient input-output model<br />

(Witt and Dobermann 2004). Since initial yield responses appear<br />

to be generally small based on the data presented from<br />

long-term experiments, fertilizer requirements with SSNM<br />

could, to a larger extent, follow maintenance strategies. At issue<br />

is whether SSNM recommendations would need to be adjusted<br />

if yield responses to fertilizer P and K application were<br />

evaluated for longer periods. Table 1 shows fertilizer require-<br />

360 <strong>Rice</strong> is life: scientific perspectives for the 21st century


SD Grain yield (t ha –1 )<br />

20<br />

Philippines<br />

(Phil<strong>Rice</strong>)<br />

S. Vietnam<br />

(CLRRI)<br />

Indonesia<br />

(IIRR)<br />

15<br />

10<br />

5<br />

0<br />

20<br />

1 3 5 7 9 11 13 15<br />

India<br />

(TNRRI)<br />

1 3 5 7 9 11 13 15<br />

China<br />

(ARS)<br />

1 3 5 7 9 11 13 15<br />

Season<br />

15<br />

(NPK) – (OP)<br />

(NPK) – (OK)<br />

10<br />

5<br />

0<br />

1 3 5 7 9 11 13 15 1 3 5 7 9 11 13 15<br />

Season<br />

Season<br />

Fig. 1. Cumulative grain yield increase in fully fertilized plots (NPK) over plots without fertilizer P (0P) and K (0K) application<br />

in long-term experiments at five sites in Asia, 1995-2002. Phil<strong>Rice</strong> = Philippine <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>, Muñoz, Philippines;<br />

CLRRI = Cuu Long <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>, Omon, Vietnam; IIRR = Indonesian <strong>Institute</strong> for <strong>Rice</strong> <strong>Research</strong>, Sukamandi,<br />

Indonesia; TNRRI = Tamil Nadu <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>, Tamil Nadu, India; ARS = Agricultural <strong>Research</strong> Station, Zhejiang,<br />

China.<br />

ments calculated with SSNM based on data from two and eight<br />

cropping seasons in the long-term experiments. Note that the<br />

actual fertilizer P and K rates were several times higher than<br />

the recommended rates with SSNM. High fertilizer P and K<br />

rates in long-term experiments are usually chosen to ensure<br />

that these nutrients are not limiting.<br />

Considering two seasons of data, recommended fertilizer<br />

rates ranged from 21 to 32 kg P 2 O 5 ha –1 and from 20 to 48<br />

kg K 2 O ha –1 . Suggested rates were highest w<strong>here</strong> both yield<br />

and yield responses to fertilizer application were high (Philippines,<br />

India, China). Fertilizer rates changed at some but not<br />

all sites when eight instead of two seasons of data were considered<br />

in the calculation of fertilizer rates. Fertilizer rates<br />

needed little adjustment at sites w<strong>here</strong> yield responses developed<br />

steadily and yields in NPK treatments remained more or<br />

less constant (e.g., Philippines). Adjustments in fertilizer rates<br />

were needed w<strong>here</strong> yield levels in the first year were not representative<br />

for a longer time period, as in Indonesia, w<strong>here</strong><br />

yields increased with time. Adjustments were also needed<br />

w<strong>here</strong> average yield responses to fertilizer application were<br />

either lacking or very strong over the four-year period. A lacking<br />

yield response over a long period indicates a strong soil<br />

nutrient-supplying power, while a strong yield response developed<br />

within a few seasons is a sign of a low soil buffering<br />

capacity for nutrient depletion. For example, four years of data<br />

from Omon revealed greater P but lower K requirements than<br />

the rates calculated after one year. Despite these adjustments,<br />

the initial estimates of fertilizer requirements showed a good<br />

congruence with the fertilizer rates that were based on several<br />

seasons of data.<br />

Conclusions<br />

Two-season estimates of indigenous P and K supplies provide<br />

a first, sufficiently robust estimate of fertilizer P and K requirements.<br />

However, on-farm monitoring of indigenous nutrient<br />

supplies for longer time periods is essential to fine-tune<br />

fertilizer P and K recommendations based on historical trends<br />

in soil fertility. Omission plots embedded in farmers’ fields<br />

should be continued at the same location for several seasons if<br />

data from representative long-term experiments are not available<br />

to identify the response pattern that develops with time.<br />

Session 12: Conservation of soil, water, and environment in rice cultures 361


Table 1. Average fertilizer rates and fertilizer requirements with SSNM (Witt et al<br />

2002, 2004) based on the average yield increase (response) in N-, P-, and K-fertilized<br />

plots (NPK) over plots without fertilizer P (0P) and K (0K) application during two and<br />

eight cropping seasons in five long-term experiments in Asia.<br />

Parameter<br />

Unit<br />

Sites<br />

Philippines Vietnam Indonesia India China<br />

(Phil<strong>Rice</strong>) (CLRRI) (IIRR) (TNRRI) (ARS)<br />

Fertilizer rates<br />

Starting year 1968 1995 1995 1995 1997<br />

Fertilizer P 2 O 5 kg ha –1 60 57 57 57 57<br />

Fertilizer K 2 O kg ha –1 60 90 120 120 120<br />

Short-term fertilizer requirements<br />

Number of seasons 2 2 2 2 2<br />

Grain yield (NPK) t ha –1 6.3 5.0 5.2 7.0 6.0<br />

Yield response to P t ha –1 0.5 0.8 0.1 0.5 0.0<br />

Yield response to K t ha –1 0.2 0.2 0.4 0.0 0.7<br />

Fertilizer P 2 O 5 kg ha –1 28 23 21 32 24<br />

Fertilizer K 2 O kg ha –1 40 20 28 48 44<br />

Long-term fertilizer requirements<br />

Number of seasons 8 8 8 8 8<br />

Grain yield (NPK) t ha –1 6.0 4.7 6.0 6.3 5.6<br />

Yield response to P t ha –1 0.7 1.5 0.2 0.5 1.5<br />

Yield response to K t ha –1 0.4 0.1 0.3 0.5 0.8<br />

Fertilizer P 2 O 5 kg ha –1 27 30 25 28 29<br />

Fertilizer K 2 O kg ha –1 38 13 37 45 38<br />

References<br />

Dobermann A, Witt C, Abdulrachman S, Gines HC, Nagarajan R,<br />

Son TT, Tan PS, Wang GH, Chien NV, Thoa VTK, Phung CV,<br />

Stalin P, Muthukrishnan P, Ravi V, Babu M, Simbahan GC,<br />

Adviento MA. 2003a. Soil fertility and indigenous nutrient<br />

supply in irrigated rice domains of Asia. Agron. J. 95:913-<br />

923.<br />

Dobermann A, Witt C, Abdulrachman S, Gines HC, Nagarajan R,<br />

Son TT, Tan PS, Wang GH, Chien NV, Thoa VTK, Phung CV,<br />

Stalin P, Muthukrishnan P, Ravi V, Babu M, Simbahan GC,<br />

Adviento MA, Bartolome V. 2003b. Estimating indigenous<br />

nutrient supplies for site-specific nutrient management in irrigated<br />

rice. Agron. J. 95:924-935.<br />

Dobermann A, Witt C, Dawe D, editors. 2004. Increasing productivity<br />

of intensive rice systems through site-specific nutrient<br />

management. Enfield, NH (USA) and Los Baños (Philippines):<br />

Science Publishers, Inc., and <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong><br />

(<strong>IRRI</strong>). p 1-410.<br />

Greenland DJ. 1997. The sustainability of rice farming. Wallingford<br />

(UK) and Manila (Philippines): CAB <strong>International</strong> and <strong>International</strong><br />

<strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>. p 1-273.<br />

Johnston AE, Syers JK, editors. 1998. Nutrient management for sustainable<br />

crop production in Asia. Wallingford (UK): CAB <strong>International</strong>.<br />

p 1-394.<br />

Nguyen MH. 2003. Soil potassium dynamics under intensive rice<br />

cropping: a case study in the Mekong Delta, Vietnam.<br />

Wageningen University, Netherlands. p 1-203.<br />

Witt C, Balasubramanian V, Dobermann A, Buresh RJ. 2002. Nutrient<br />

management. In: Fairhurst T, Witt C, editors. <strong>Rice</strong>: a practical<br />

guide for nutrient management. Singapore and Los Baños:<br />

Potash and Phosphate <strong>Institute</strong> & Potash and Phosphate <strong>Institute</strong><br />

of Canada and <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>.<br />

p 1-45.<br />

Witt C, Buresh RJ, Balasubramanian V, Dawe D, Dobermann A.<br />

2004. Principles and promotion of site-specific nutrient management.<br />

In: Dobermann A, Witt C, Dawe D, editors. Increasing<br />

productivity of intensive rice systems through site-specific<br />

nutrient management. Enfield, NH (USA) and Los Baños<br />

(Philippines): Science Publishers, Inc., and <strong>International</strong> <strong>Rice</strong><br />

<strong>Research</strong> <strong>Institute</strong>. p 397-410.<br />

Witt C , Dobermann A. 2004. Toward a decision support system for<br />

site-specific nutrient management. In: Dobermann A, Witt C,<br />

Dawe D, editors. Increasing productivity of intensive rice systems<br />

through site-specific nutrient management. Enfield, NH<br />

(USA) and Los Baños (Philippines): Science Publishers, Inc.,<br />

and <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>. p 359-396.<br />

362 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Notes<br />

Authors’ addresses: C. Witt and R. Buresh, <strong>International</strong> <strong>Rice</strong> <strong>Research</strong><br />

<strong>Institute</strong> (<strong>IRRI</strong>), DAPO Box 7777, Metro Manila, Philippines;<br />

A. Dobermann, University of Nebraska, Lincoln, NE<br />

68583-0915; S. Abdulrachman, Indonesian <strong>Institute</strong> for <strong>Rice</strong><br />

<strong>Research</strong> (IIRR), Sukamandi, West Java 41256, Indonesia;<br />

H.C. Gines, Philippine <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong> (Phil<strong>Rice</strong>),<br />

Muñoz, Nueva Ecija 3119, Philippines; R. Nagarajan, Soil<br />

and Water Management <strong>Research</strong> <strong>Institute</strong> (SWMRI),<br />

Thanjavar, Tamil Nadu 613501, India; S. Ramanathan, Tamil<br />

Nadu Agricultural University (TNAU), Coimbatore 641003,<br />

India; P.S. Tan, Cuu Long Delta <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong><br />

(CLRRI), Omon, Vietnam; G.H. Wang, Zhejiang Agricultural<br />

University, Hangzhou, Zhejiang 310029, China. Current address:<br />

C. Witt, Potash & Phosphate <strong>Institute</strong>/Potash & Phosphate<br />

<strong>Institute</strong> of Canada and <strong>International</strong> Potash <strong>Institute</strong>,<br />

Southeast Asia Program, 126 Watten Estate Road, Singapore<br />

287599, e-mail: cwitt@ppi-ppic-ipi.org.<br />

Acknowledgments: The <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong> (<strong>IRRI</strong>),<br />

the Swiss Agency for Development and Cooperation (SDC),<br />

the Potash and Phosphate <strong>Institute</strong>/Potash and Phosphate <strong>Institute</strong><br />

of Canada (PPI/PPIC), and the <strong>International</strong> Potash<br />

<strong>Institute</strong> (IPI) provided funding for this research.<br />

Ecological engineering for sustainable rice production<br />

and the restoration of degraded watersheds in West Africa<br />

Toshiyuki Wakatsuki, Md. Moro Buri, and Oluwarotimi O. Fashola<br />

During 1970-2000, although rice production increased from<br />

2.4 to 7.4 million tons in West Africa (WA), consumption per<br />

capita increased from 15 to 30 kg and imports increased from<br />

0.7 to 4.3 million tons. Yield, however, has been stagnant at<br />

1.3–1.7 t ha –1 during the past 30 years in this region. More<br />

than 100 high-yielding varieties for various rice ecologies are<br />

available and another 6 NERICA varieties are in the pipeline<br />

for upland areas. The lowland elite varieties under the sawah 1<br />

system with good management could yield up to 6 t ha –1 . But<br />

these potentials are never achieved in farmers’ fields because<br />

of poor water control and bad soil management systems. This<br />

is why a renewed call for a concerted effort needs to be made<br />

for better water and soil management systems, referred to in<br />

this paper as the sawah system (Wakatsuki et al 1998), and<br />

correct policies for rice development.<br />

Why has the Green Revolution not yet occurred in West<br />

Africa in spite of its successes in Asia in the 1960s The Green<br />

Revolution laid the foundation for the rapidly growing economies<br />

of Asia today. As our team revealed, the ecological environment<br />

of soil and water conditions in this region is very severe.<br />

Lowland soil fertility in WA may be the lowest among<br />

the major tropical areas in the world (Issaka et al 1997, Buri et<br />

al 2000, Hirose and Wakatsuki 2002). The main cause of the<br />

present agricultural and environmental crises in WA, however,<br />

may be the underdevelopment of lowland agriculture. Environmentally<br />

creative technology, or ecological engineering<br />

technology, such as lowland sawah farming, is not traditionally<br />

practiced in WA. Sawah is a multifunctional constructed<br />

wetland, which is the prerequisite for realizing the Green Revolution<br />

as well as for preserving and even restoring ecological<br />

environments. Irrigation and drainage without farmers’ sawah<br />

farming technologies have proved inefficient or even damaging<br />

because of accelerated erosion processes. Thus, the development<br />

of irrigation has been slow. In the absence of water<br />

control, fertilizers cannot be used efficiently. Consequently,<br />

the high-yielding varieties perform poorly and soil fertility<br />

cannot be sustained. Hence, the Green Revolution cannot take<br />

place.<br />

The sawah system and integrated watershed approach<br />

The upper part of Figure 1 shows a concept of macroscale<br />

ecological engineering, that is, watershed ecological engineering.<br />

The soils formed in uplands and the nutrients released<br />

during rock weathering and soil formation processes in uplands<br />

are accumulated in lowlands (geological fertilization).<br />

If the sawah system exists in the lowlands, it can store and<br />

effectively use the nutrient-rich water and fertile topsoils eroded<br />

from the uplands. Watershed agroforestry through the integration<br />

of upland forestry and lowland sawah systems in a unit<br />

watershed as seen in the upper part of Figure 1 is a typical<br />

model of watershed ecological engineering. Optimum landuse<br />

patterns and landscape management practices optimize<br />

geological fertilization through optimum hydrology in a given<br />

watershed. This is an eco-environmental basis for the longterm<br />

intensive sustainability of sawah-based rice farming in<br />

Asia.<br />

1 The sawah system is the rice farmers’ basic infrastructure for intensive and<br />

sustainable rice production. The term “sawah” refers to a leveled rice field<br />

surrounded by bunds with inlet and outlet connections to irrigation and drainage<br />

canals. The term originates from Malayo-Indonesian. The English term<br />

“paddy or paddi” also originates from the Malayo-Indonesian term “padi,”<br />

which means rice plant. However, the term “paddy” refers to rice grain with<br />

husk in West Africa as a whole. The paddy field is almost equivalent to the<br />

sawah for Asian scientists. However, the term “paddy fields” refers to just a<br />

rice field, including an upland rice field in West Africa. T<strong>here</strong>fore, to avoid<br />

confusion among the terms “rice plant,” “paddy,” and the improved manmade<br />

rice-growing environment through ecological engineering, the authors<br />

propose to use the term “sawah.”<br />

Session 12: Conservation of soil, water, and environment in rice cultures 363


(A) Optimum land-use patterns and landscape management practices optimize geological<br />

fertilization through the control of optimum hydrology in the watershed<br />

Rainfall<br />

Watershed<br />

agroforestry<br />

Application of various types<br />

of humified organic matter<br />

Intensive sustainability in uplands<br />

= combination with stock raising<br />

Uplands: 1,000–5,000 ha<br />

Nutrient cycle<br />

Rock weathering, soil formation,<br />

and nutrient release<br />

Topsoil<br />

Geological fertilization<br />

Nutrient-rich water<br />

Topsoil erosion<br />

Village<br />

Small irrigation canal<br />

Sedimentation<br />

Stream discharge<br />

Small reservoir<br />

Fish culture pond<br />

Lowlands = about 5%<br />

Supply of<br />

nutrients by<br />

animals<br />

Sawah hypothesis: 1 ha of sawah fields<br />

is equivalent to 10–15 ha of uplands<br />

Geological<br />

fertilization<br />

A few mm<br />

to 2 cm<br />

10–20 cm<br />

O 2 + N 2 CH 4<br />

CO 2<br />

emission<br />

Technology development for nitrogen fixation through<br />

integrated management of soil, water, algae, and rice<br />

N 2<br />

biological<br />

nitrogen<br />

N 2 O N2 (N 2 O, NO)<br />

fixation Algae<br />

Submerged<br />

Algae<br />

Nitrificaton Denitrificaton water<br />

CH 4 →CO 2 NH 3 →NO 2 →NO 3 +400–500 mV Oxidized<br />

layer<br />

Organic N 2<br />

NO 3 N 2 (N 2 O, NO)<br />

NO Mn (IV)<br />

3 ←NO 2 ←NH 4 -N<br />

Mn (II) –100 mV<br />

CO 2 CH 4<br />

Fe (III)<br />

SO 4<br />

N 2 NH 4<br />

CO 2 CH 4<br />

CH 3 COOH CH 4<br />

Fe (II)<br />

H 2 S<br />

–250 mV<br />

(Eh)<br />

Reduced<br />

layer<br />

Plow layer<br />

O 2 , N 2<br />

CH 4 →CO 2<br />

Accumulating layer Fe 2 CO 3 ⋅ nH 2 O<br />

Accumulating layer MnO 2 ⋅ nH 2 O<br />

(B) The sawah system as multifunctional constructed wetlands<br />

Fig. 1. Macro- and microscale ecological mechanisms of intensive sustainability of the lowland<br />

sawah system: (A) geological fertilization through watershed ecological engineering and<br />

(B) multifunctional constructed wetlands for enhanced supply of N, P, Si, and other nutrients.<br />

Although the rate of soil formation, and thus also soil<br />

erosion, is much higher in Asia than in Africa, suppose that the<br />

soil formation rate in uplands, which make up 95% of the total<br />

area in the example of a watershed shown in Figure 1, is 1 t<br />

ha –1 y –1 . In a stable ecosystem in a watershed, the rates of soil<br />

formation and erosion should be well balanced; t<strong>here</strong>fore, the<br />

topsoils formed in uplands—which account for 95% of the<br />

area—and the nutrients produced in the process will be concentrated<br />

in lowlands, which make up 5% of the area. Thus,<br />

the soil formation rate in the lowlands equals 20 t ha –1 y –1<br />

(Hirose and Wakatsuki 2002). Though it will be impossible to<br />

use all of the rich soils and nutrient-rich water from the uplands<br />

effectively, the sawah farming system could artificially<br />

reinforce the geological fertilization processes. The quantitative<br />

scientific evaluation of the geological fertilization processes<br />

in a watershed will be an important future research subject.<br />

The excessive decomposition of organic matter in tropical<br />

soils is another problem. T<strong>here</strong>fore, organic matter management<br />

through agroforestry and cover-crop systems is important<br />

for sustaining soil fertility. Sustainability under intensive<br />

cultivation of uplands is possible through integration with<br />

stock raising. Animals can accumulate nutrients on upland<br />

farms and lowlands. However, except for lowland sawah farming,<br />

these options are not successful enough to make tropical<br />

upland farming sustainable under intensive cultivation. The<br />

sawah system can also control such excessive organic matter<br />

decomposition (Kyuma 2003). Another possibility to restore<br />

364 <strong>Rice</strong> is life: scientific perspectives for the 21st century


upland soil fertility is the application of various refractory humified<br />

materials to soil (Wakatsuki et al 2003).<br />

When the unit yields of upland slash-and-burn rice cultivation<br />

are compared with that of lowland sawah rice cultivation,<br />

the latter (2.5 t ha –1 ) is approximately 2.5 times higher<br />

than the former (1 t ha –1 ) under conditions of no-fertilizer application.<br />

In addition, the planting of rice in rainfed upland<br />

areas must be followed by a fallow period of at least 4–5 years<br />

to allow restoration of soil fertility, that is, to sustain 1 ha of<br />

upland rice cultivation based on slash and burn, 4–5 ha of upland<br />

are necessary. In comparison, continuous cultivation is<br />

possible with sawah fields.<br />

T<strong>here</strong>fore, when these two types of cultivation are compared<br />

for a long period of 10-plus years, which are necessary<br />

to sustain a complete cycle of slash-and-burn cultivation, taking<br />

the above facts into consideration, the difference in<br />

sustainability per unit of productivity can be more than tenfold,<br />

that is, the yield difference (2.5) times the difference in<br />

required area (4–5 times) for sustainable production.<br />

Accordingly, the development of 1 ha of sawah field<br />

enables the conservation or regeneration of 10 ha or more of<br />

forest area. Sawah fields can t<strong>here</strong>fore contribute to not only<br />

increased food production but also conservation of the forest<br />

environment as well as soil and water conservation in the whole<br />

watershed, resulting in enhanced sustainability of an intensive<br />

lowland sawah field system. Furthermore, these fields can contribute<br />

to the alleviation of global warming and other global<br />

environmental problems through the fixation of carbon to forests<br />

and forest soil.<br />

The sawah system as multifunctional wetland<br />

The lower part of Figure 1 shows the microscale mechanisms<br />

of intensive sustainability of the sawah system. The sawah system<br />

can be managed by multifunctional constructed wetlands.<br />

It is well known that weeds can be controlled by means of<br />

water. But it is not well evaluated that the nitrogen fixation<br />

amount of soil microbes under a submerged sawah system<br />

reaches 20–100 kg ha –1 year –1 in Japan and 20–200 kg ha –1<br />

year –1 in the tropics depending on the level of soil fertility and<br />

water management (Greenland 1997, Kyuma 2003, Hirose and<br />

Wakatsuki 2002). This amount is comparable with the nitrogen<br />

fixation amount of leguminous plants. Rainfed upland farming<br />

has no such option but to rely on the use of leguminous<br />

plants, animal dung, other organic fertilizer, and/or chemical<br />

fertilizer. Under submerged conditions, because of reduction<br />

of ferric iron to ferrous iron, phosphorus availability is increased<br />

and acid pH is neutralized; hence, micronutrient availability is<br />

also increased (Kyuma 2003). These are the other benefits of<br />

the sawah system. These eutrophication mechanisms not only<br />

encourage the growth of the rice plant but also encourage the<br />

growth of various algae that increase nitrogen fixation. The<br />

quantitative evaluation of nitrogen fixation in the sawah system,<br />

including the role of algae, will also be an important future<br />

research topic. Under nitrate-rich submerged water conditions,<br />

the sawah system encourages the denitrification process.<br />

Easily decomposable organic materials become substrate<br />

of various denitrifiers. Another function of the sawah system<br />

is the purification of nitrate-polluted water.<br />

State of rice cultivation in West Africa<br />

<strong>Rice</strong> is the only crop that can be grown in all the agroecological<br />

zones of WA: (1) rainfed upland, (2) rainfed lowland, (3) irrigated<br />

lowland, and (4) deepwater/mangrove swamp. According<br />

to a recent survey by WARDA (1988, 1999), the percentage<br />

of area under rice by ecology is as follows: 31% for upland,<br />

47% for lowland, 16% for irrigated, and 5% for deep<br />

water. The percentages of upland rice area and production<br />

decreased dramatically in 1990-2000, 57% to 31% and 42%<br />

to 25%, respectively. <strong>Rice</strong> cultivation in WA was traditionally<br />

an extension of upland farming. However, following the pioneering<br />

technical cooperation activities of Taiwanese teams<br />

regarding widespread and intensive sawah-based farming for<br />

some 10 years in the 1960s and 1970s, the number of rice<br />

farmers who are consciously conducting water management<br />

has steadily increased over the last 30–40 years (Hsieh 2001).<br />

Such management involves the introduction of bunding, leveling,<br />

construction of dams, dikes, and weirs, and extension of<br />

water canals. Consequently, t<strong>here</strong> are now many types of rice<br />

cultivation in WA in terms of water control, ranging from upland<br />

rice cultivation to irrigated lowland sawah (Fig. 2).<br />

Restoration of degraded inland valley watersheds<br />

in West Africa: a case study of an ecological engineering<br />

project<br />

In the past 16 years, the authors’ group carried out various<br />

surveys and trials for on-farm research and participatory as<br />

well as farmers’ self-support development at two benchmark<br />

watersheds in the Guinea Savanna Zone (Nigeria) and Forest<br />

Transitional Zone (Ghana). The major target was to develop<br />

sustainable eco-technologies to increase food, especially rice,<br />

and at the same time restore the degraded watershed. The results<br />

showed that various sawah-based rice farming activities<br />

in lowlands are a key technology (Wakatsuki et al 1998, 2001,<br />

Hirose and Wakatsuki 2002).<br />

In 2003, a new but continuing five-year research project<br />

had started under the title “Watershed Ecological Engineering<br />

for Sustainable Increase of Food Production and Restoration<br />

of Degraded Environment in West Africa” (Wakatsuki 2004).<br />

The major outcome will be to consolidate the long-term comprehensive<br />

plan for sustainable development of 10–20 million<br />

ha of the lowland sawah system in WA. Based on the sustainable<br />

increase in food production through sawah development,<br />

our final target is to regenerate 100–200 million ha of forest in<br />

WA.<br />

Reference<br />

Buri MM, Ishida F, Kubota D, Masunaga T, Wakatsuki T. 2000. Sulfur<br />

and zinc levels as limiting factors to rice production in West<br />

Africa lowlands. Geoderma 94:23-42.<br />

Session 12: Conservation of soil, water, and environment in rice cultures 365


Forest destruction induced<br />

savannization<br />

Upland-lowland<br />

continuum<br />

Intensified rainfed to irrigated<br />

lowland sawah system<br />

NERICA with<br />

bunding, leveling<br />

Water table<br />

Geological<br />

fertilization<br />

Drought<br />

Flood<br />

Some level of water control<br />

Functional constructed<br />

wetland<br />

Nitrogen fixation<br />

(20–200 kg ha –1 y –1 )<br />

Geological fertilization and enhanced<br />

supply of Si, Ca, Mg, K, P<br />

Spring irrigation<br />

Bunding<br />

Evaporation<br />

Stabilized<br />

Fragile:<br />

no sustainable upland<br />

rice including NERICA<br />

Leveling<br />

Leaching runoff<br />

Humid zone<br />

Sahel zone<br />

Upland<br />

Soil conservation<br />

Slope upland<br />

No soil conservation<br />

Hydromorphic<br />

slopes (fringe)<br />

Lowland<br />

(valley bottom)<br />

Intensified<br />

lowland<br />

Irrigated<br />

lowland<br />

Main water supply:<br />

rainfall<br />

Rainfall Rainfall +<br />

water table<br />

seepage in<br />

spring<br />

Rainfall +<br />

water table +<br />

floodwater in spring<br />

Regulated<br />

floodwater in spring<br />

Irrigation dams,<br />

wells, pumps<br />

Agroecological zone:<br />

Guinea savanna to<br />

humid forest zone<br />

Guinea savanna to<br />

humid forest zone<br />

Guinea savanna<br />

to humid forest<br />

zone<br />

Sudan savanna to<br />

humid forest zone<br />

Sudan savanna to<br />

humid forest zone<br />

Sahel to<br />

humid forest zone<br />

Rudimentary sawah Rainfed sawah Irrigated sawah<br />

Rainfed upland<br />

Rainfed lowland<br />

Fig. 2. <strong>Rice</strong> ecologies along a continuum of inland valley watersheds and floodplains in West Africa (excluding the ecologies of deepwater<br />

and mangrove swamp rice).<br />

Irrigated<br />

Greenland DJ. 1997. The sustainability of rice farming. Wallingford<br />

(UK): CAB <strong>International</strong>, in association with the <strong>International</strong><br />

<strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>. 273 p.<br />

Hirose S, Wakatsuki T. 2002. Restoration of inland valley ecosystems<br />

in West Africa. Tokyo (Japan): Norin Tokei Kyokai. 600<br />

p.<br />

Hsieh S-C. 2001. Agricultural reform in Africa, with special focus<br />

on Taiwan-assisted rice production in Africa, past, present and<br />

future perspectives. Tropics 11:33-58.<br />

Issaka RF, Ishida F, Kubota D, Wakatsuki T. 1997. Geographic distribution<br />

of selected soil parameters of inland valleys in West<br />

Africa. Geoderma 75:99-116.<br />

Kyuma K. 2003. Paddy soil science. Kyoto (Japan): Kyoto University<br />

Press. 305 p.<br />

Wakatsuki T. 2004. Watershed ecological engineering for sustainable<br />

increase for food production and resoration of degraded<br />

environment in West Africa. www.kindai-ecotech.jp.<br />

Wakatsuki T, Shinmura Y, Otto E, Olanian G. 1998. African-based<br />

sawah system for the integrated watershed management of<br />

small inland valley in West Africa. Water Reports 17. Institutional<br />

and technical opinion in the development and management<br />

of small-scale irrigation. Rome (Italy): FAO. p 56-79.<br />

Wakatsuki T, Otto E, Andah WEI, Cobbina J, Buri MM, Kubota D,<br />

editors. 2001. Integrated watershed management of inland<br />

valley in Ghana and West Africa: ecotechnology approach.<br />

Final Report on JICA/CRI joint study project, CRI, Kumashi,<br />

Ghana, and JICA, Tokyo. 337 p.<br />

Wakatsuki T, Matsui K, Shibata K, Matsuoka K, Masunaga T. 2003.<br />

A method for organic fertilizer production. Japanese Patent<br />

Application No. 2002-338185.<br />

WARDA (West Africa <strong>Rice</strong> Development Association). 1988. Strategic<br />

plan. Bouaké (Côte d’Ivoire): WARDA.<br />

WARDA (West Africa <strong>Rice</strong> Development Association). 1999. African<br />

rice initiative report. Bouaké (Côte d’Ivoire): WARDA.<br />

Notes<br />

Authors’ addresses: Toshiyuki Wakatsuki, Faculty of Agriculture,<br />

Kinki University, 3327-204 Nakamachi, Nara 631-8505, Japan,<br />

e-mail: wakatuki@nara.kindai.ac.jp; Md. Moro Buri, Soil<br />

<strong>Research</strong> <strong>Institute</strong>-CSIR, Kumasi, Ghana, e-mail:<br />

sawahksi@ghana.com; Oluwarotimi O. Fashola, Watershed<br />

Initiative of Nigeria, WIN2001, <strong>International</strong> <strong>Institute</strong> of Tropical<br />

Agriculture, Ibadan, Nigeria, e-mail: r.fashola@cgiar.org.<br />

366 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Nitrogen cycling under the rice-wheat rotation<br />

and environmental effects<br />

Jian-guo Zhu, Xiaozhi Wang, Zu-cong Cai, Ren Gao, and Yasukazu Hosen<br />

Nitrogen fertilizer efficiency in flooded rice fields is usually<br />

poor. Upland crops frequently use 40–60% of the applied N,<br />

w<strong>here</strong>as flooded rice crops typically use only 20–40% (Vlek<br />

and Byrens 1986). This means that about 60% of the applied<br />

nitrogen in the rice season is released from the soil to a water<br />

body (surface water and groundwater) and to the atmosp<strong>here</strong>.<br />

For these reasons, sustainable forms of agricultural systems<br />

that are more stable and friendly to the environment are now<br />

gradually recognized by the government as a long-term policy.<br />

Meanwhile, to develop corresponding technologies and evaluate<br />

their environmental impact have become important for<br />

agroenvironmental researchers. Much research has been done<br />

in the area of NO 3<br />

–<br />

movement, N 2 O emission, and NH 3 volatilization,<br />

but generally only one or a few components are involved<br />

in one experiment. As we know, the processes in N<br />

cycling are correlated and they interact. T<strong>here</strong>fore, t<strong>here</strong> is a<br />

need to determine as much as possible measurable items for N<br />

cycling at one time in one experiment.<br />

A field experiment on monolithic lysimeters was carried<br />

out in the 2001 rice season in the Tai-hu Lake region. The<br />

objective of our studies was to investigate nitrogen cycling<br />

data for urea applied in paddy fields managed according to the<br />

prevailing practices of local farmers, including losses through<br />

surface runoff, percolation loss, and ammonia volatilization,<br />

and to evaluate their impact on the environment.<br />

Materials and methods<br />

The experiments were carried out at the Changshu Agro-ecological<br />

Experiment Station (31º32′45″N and 120º41′57″E). The<br />

soil was classified as a Wushan soil, a waterlogged soil developed<br />

from a parent material of lacustrine deposit, with the following<br />

characteristics in the surface 0.15-m layer: pH 7.36<br />

(H 2 O); total N 1.79 g kg –1 ; organic carbon 20.0 g kg –1 ; texture<br />

silty sandy clay loam; bulk density 1.22 g cm –3 ; and CEC 20.20<br />

cmol kg –1 .<br />

Ten profile-undisturbed lysimeters each had an 800-mm<br />

inner diameter and 1,000-mm height. One percolate outlet was<br />

drilled at the center of the bottom. Each lysimeter was installed<br />

with two runoff outlets in the column wall, one at 60 mm above<br />

and one at 100 mm below the top surface.<br />

The experiment included three treatments: U550 (urea<br />

at 300 and 250 kg N ha –1 for rice and wheat, respectively; conventional<br />

level), U275 (urea at 150 and 125 kg N ha –1 for rice<br />

and wheat, respectively); and a control (no N). The treatments<br />

(3 replicates) and control (4 replicates) were arranged randomly.<br />

For U275 and U550 treatments, readily available urea<br />

was applied as basal, tillering, and booting fertilizer, with 40%,<br />

20%, and 40% of N applied in the whole rice season, respectively.<br />

All treatments received 100 kg K 2 O ha –1 and 100 kg<br />

P 2 O 5 ha –1 as basal fertilizer. Fertilizers for basal application<br />

were scattered evenly on the wet soil surface and flooded and<br />

puddled for transplanting. The other two applications adopted<br />

the topdressing method.<br />

For each irrigation, the soil was kept flooded at 5-cm<br />

depth, and supplemental irrigation water was added according<br />

to local practices. Meanwhile, the percolation rate was artificially<br />

controlled at 5 mm day –1 continuously with a medical<br />

transfusion apparatus. Some 7.5 L of percolate was collected<br />

every 3 days with a 10-L pail that contained 10 mL of 2 M<br />

H 2 SO 4 .<br />

The runoff samples were collected in the rice season.<br />

The rain sample was collected with a rain gauge. All water<br />

samples were stored in the dark at 4 °C until analyzed.<br />

Plant samples were collected for straw and grain nutrient<br />

analysis when the crop was harvested.<br />

The ammonia volatilization rate was measured using a<br />

continuous airflow enclosure method (Kissel et al 1977). The<br />

rate of airflow, generated by a pump, was adjusted using valves<br />

to 15–20 times the chamber volume per minute (Liao 1983).<br />

Measurement continued every day (except for a heavy rain<br />

day) until t<strong>here</strong> were no significant differences between the<br />

NH 3 volatilization rates from the N treatments and the control.<br />

NH 4+ , NO 3– , and total N in water samples were measured<br />

colorimetrically by the indophenol (NH 4+ ), ultraviolet spectrophotometry<br />

(NO 3– ), and K 2 S 2 O 8 oxidation ultraviolet spectrophotometry<br />

(total N) methods.<br />

Results and discussion<br />

Ammonia volatilization potential<br />

The cumulative NH 3 losses from U treatments were significantly<br />

higher than from the control. The average cumulative<br />

NH 3 losses in three rice seasons were 39.43 and 100.41 kg N<br />

ha –1 from the U275 and U550 treatments, which corresponded<br />

to 24.06% and 32.34% of the applied N, respectively (Table<br />

1).<br />

The cumulative NH 3 losses in the wheat season in 2002-<br />

03 were 20.99 and 40.10 kg N ha –1 from the U275 and U550<br />

treatments, which corresponded to 11.94% and 13.61% of the<br />

applied N, respectively (data not shown).<br />

The ratio of ammonia volatilization to nitrogen applied<br />

increased, along with the increase in application rate in urea<br />

Session 12: Conservation of soil, water, and environment in rice cultures 367


Table 1. The amount and ratio of N loss by NH 3 volatilization potential and runoff in the rice season.<br />

Treatments<br />

N loss (kg N ha –1 ) Loss ratio of N applied (%)<br />

2001 2002 2003 2001 2002 2003 Av<br />

NH 3 volatilization<br />

Control 0 ± 0 C a 6.92 ± 0.36 c 3.10 ± 0.85 c<br />

U275 24.11 ± 6.25 b 48.91 ± 4.40 b 45.27 ± 7.49 b 16.08 b 28.00 28.11 24.06<br />

U550 77.98 ± 11.20 a 110.67 ± 7.34 a 112.68 ± 13.34 a 25.99 34.50 36.53 32.34<br />

Runoff<br />

Control 4.1 ± 0.4 c 2.2 ± 0.4 c 4.4 ± 1.8 c<br />

U275 20.4 ± 4.5 b 12.3 ± 3.5 b 25.4 ± 2.0 b 10.9 6.7 14.0 10.53<br />

U550 44.7 ± 7.1 a 18.8 ± 3.7 a 42.7 ± 1.6 a 13.5 5.5 12.8 10.60<br />

a Average values in the same row without a common letter differ significantly at P = 0.01. b Loss ratio of N applied is N loss through NH 3 emissions<br />

minus the control value divided by N rate.<br />

treatments. But, the ratio of NH 3 loss to N applied in the wheat<br />

season was much lower than that in the rice season.<br />

Runoff loss<br />

Surface runoff occurred 5, 7, and 2 times for the 2001, 2002,<br />

and 2003 rice seasons, respectively. Nitrogen loss by runoff<br />

varied significantly with different treatments at different stages.<br />

Significant variance in both runoff total N (TN) concentrations<br />

and TN losses by runoff between different years occurred.<br />

Nitrogen loss by runoff was 20.4 and 44.7, 12.3 and 18.8,<br />

and 25.4 and 42.7 kg N ha –1 for U275 and U550 in 2001, 2002,<br />

and 2003, respectively. The ratios of nitrogen loss by runoff to<br />

N applied were 5.5–14.0% for U treatments. T<strong>here</strong> was a significant<br />

positive correlation between nitrogen runoff losses and<br />

applied N amount in urea treatments; the ratio of runoff N loss<br />

to N applied was similar (insignificant difference at P 150 kg N ha –1 and < 300 kg N ha –1 for<br />

common urea under the rice-wheat rotation in this region.<br />

Conclusions<br />

The following conclusions can be drawn:<br />

1. Urea treatments for ammonia volatilization were remarkable<br />

in this region in both the rice and wheat<br />

seasons.<br />

368 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 2. Field nitrogen balance under two rice-wheat<br />

rotations in 2001-03 (kg N ha –1 ).<br />

Treatments Control U275 U550<br />

Total income 55.3 606.1 1,156.3<br />

Rainfall 51.6 51.6 51.6<br />

Irrigation 3.7 4.5 4.7<br />

Fertilization 0.0 550.0 1,100.0<br />

Bio-uptake 190.0 448.8 630.1<br />

Total measured loss 23.2 176.7 483.6<br />

NH 3 volatilization 6.1 112.7 334.8<br />

NO 2 emissions 0.0 0.1 0.6<br />

Runoff and drainage 12.0 58.3 139.8<br />

Percolation 5.1 5.6 8.4<br />

Balance –157.9 –19.4 42.7<br />

2. The interval between rainfall and urea fertilization was<br />

the key factor in nitrogen runoff losses. The likelihood<br />

of N loss by runoff is not great if heavy rain<br />

hasn’t occurred within 5 days after fertilizer application.<br />

The N loss by runoff will also decrease markedly<br />

if the runoff outlet is heightened properly.<br />

3. TN loss by percolation has not been rising in parallel<br />

with the increasing N fertilizer application rate, and<br />

NO 3 – -N in groundwater is not directly related to N<br />

percolation from N applied to the paddy field.<br />

4. The N input by rainfall should be considered in research<br />

on nitrogen balance in the agroecosystem and<br />

eutrophication.<br />

5. A suitable urea application rate should be > 150 kg N<br />

ha –1 and < 300 kg N ha –1 under the rice-wheat rotation<br />

in this region.<br />

References<br />

Kissel DE, Brewer HL, Arkin GF. 1977. Design and test of a field<br />

sampler for ammonia volatilization. Soil Sci. Soc. Am. J.<br />

41:1133-1138.<br />

Liao XL. 1983. Method of nitrogen gas loss research. Prog. Soil<br />

Sci. 15(5):49-55. (In Chinese.)<br />

Nelson DW. 1982. Nitrogen in agricultural soils. Madison, Wis.<br />

(USA): Soil Science Society of America. p 327-363.<br />

Vlek PLG, Byrens BH. 1986. The efficacy and loss of fertilizer N in<br />

lowland rice. Fert. Res. 9:131-147.<br />

WHO (World Health Organization).1984. Guidelines for drinking<br />

water quality. Vol 1. Recommendations. Geneva (Switzerland):<br />

WHO.<br />

Zhu JG, Liu G, Han Y, Zhang YL, Xing GX. 2003. Nitrate distribution<br />

and denitrification in the saturated zone of paddy field<br />

under rice/wheat rotation. Chemosp<strong>here</strong> 50:725-732.<br />

Notes<br />

Authors’addresses: Jian-guo Zhu, Xiaozhi Wang, Zu-cong Cai, and<br />

Ren Gao, <strong>Institute</strong> of Soil Science, Chinese Academy of Sciences,<br />

Nanjing, Jiangsu 210008, China; Xiaozi Wang, Environment<br />

Science and Engineering College, Yangzhou University,<br />

Yangzhou, Jiangsu 225009, China; Ren Gao, Fujian Normal<br />

University, Fuzhou, Fujian 350007, China; Yasukazu<br />

Hosen, Japan <strong>International</strong> <strong>Research</strong> Center for Agricultural<br />

Sciences, 1-2 Ohwashi, Tsukuba, Ibaraki 305-8686, Japan, e-<br />

mail: jgzhu@issas.ac.cn.<br />

Urea deep placement increases yield and saves nitrogen<br />

fertilizer in farmers’ fields in Bangladesh<br />

W.T. Bowen, R.B. Diamond, U. Singh, and T.P. Thompson<br />

An innovative yet simple technology that increases nitrogenuse<br />

efficiency, and which is being widely disseminated for<br />

managing urea in flooded rice systems in Bangladesh, involves<br />

the deep placement of urea supergranules or briquettes into<br />

puddled soil shortly after transplanting rice. The briquettes are<br />

made by compressing prilled or granular urea in small machines<br />

with indented pocket rollers that, depending on the size<br />

of the pocket, produce individual briquettes varying in weight<br />

from 0.9 to 2.7 g. Within a week after transplanting rice, the<br />

briquettes are inserted into the puddled soil by hand, being<br />

placed to a depth of 7–10 cm in the middle of alternating<br />

squares of four hills of rice. Often referred to as urea deep<br />

placement (UDP), this technology improves N-use efficiency<br />

by keeping most of the urea N in the soil close to plant roots<br />

and out of the floodwater, w<strong>here</strong> it is more susceptible to loss<br />

as gaseous compounds or runoff (Mohanty et al 1999, Savant<br />

and Stangel 1990).<br />

The UDP technology as applied to flooded rice in<br />

Bangladesh offers a compelling example of an effective approach<br />

to managing urea fertilizer that results in not only improved<br />

efficiency but also greater yield with less urea fertilizer.<br />

Farmer awareness of the technology has been increased<br />

through training and promotional activities, including on-farm<br />

comparisons of UDP and broadcast urea in trials managed by<br />

farmers. For this report, data from on-farm trials are used to<br />

examine changes in grain yield, urea fertilizer use, and N-use<br />

efficiency attributed to the use of UDP technology.<br />

Session 12: Conservation of soil, water, and environment in rice cultures 369


Methods<br />

UDP grain yield (t ha –1 )<br />

<strong>Rice</strong> is grown throughout the year in Bangladesh, with two<br />

principal cropping seasons: boro (irrigated dry season) and<br />

aman (wet season). The boro crop is transplanted in January-<br />

February and harvested in May-June, while the aman crop is<br />

transplanted in July-August and harvested in November-December.<br />

Yields are usually greater during the boro season because<br />

of more favorable temperatures and solar radiation for<br />

crop growth.<br />

9<br />

8<br />

7<br />

6<br />

5<br />

Boro<br />

Aman<br />

On-farm trials<br />

During the 2000-04 boro and aman seasons, farmers in seven<br />

districts (Bogra, Chandpur, Jessore, Kishoreganj, Mymensingh,<br />

Pabna, and Tangail) conducted 531 on-farm trials to measure<br />

rice yields obtained in side-by-side comparisons of UDP versus<br />

the current farmers’ practice (FP) of applying split applications<br />

of broadcast urea. Both treatments (UDP and FP) were<br />

managed equally except for urea, and all farmers used semidwarf<br />

high-yielding varieties. At harvest, grain weights and<br />

moisture content were determined by taking yield cuts from<br />

two subplots of 11.2 m 2 in each of the UDP and FP main plots.<br />

Grain yields are reported as paddy (unmilled rice) at a standard<br />

moisture content of 14%.<br />

Fertilizer inputs were recorded in 304 of the comparison<br />

trials (222 during the boro and 82 during the aman). The<br />

amount of N applied in the FP treatment was chosen by each<br />

farmer according to his own usual practice or local recommendations.<br />

For the FP boro, the average was 149 kg N ha –1<br />

(range from 71 to 239 kg N ha –1 ), and for the FP aman it was<br />

95 kg N ha –1 (range from 35 to 253 kg N ha –1 ). The amount of<br />

N applied by deep-point placement of urea briquettes (UDP<br />

treatment) was substantially less; the UDP boro received an<br />

average of 79 kg N ha –1 (range from 69 to 91 kg N ha –1 ), while<br />

the UDP aman received an average of 59 kg N ha –1 (range<br />

from 53 to 64 kg N ha –1 ). Phosphorus and K were applied<br />

according to local recommendations, with an average application<br />

of 21 kg P ha –1 and 47 kg K ha –1 .<br />

Parameters evaluated<br />

The effectiveness of UDP technology was assessed through<br />

the following parameters: changes in grain yield (∆Grain yield;<br />

kg ha –1 ), changes in fertilizer N applied (∆N applied; kg N<br />

ha –1 ), and changes in the efficiency of fertilizer N use as measured<br />

by the partial factor productivity of N (∆PFP-N; kg grain<br />

yield per kg N applied). These parameters were calculated for<br />

each individual on-farm comparison of UDP and FP as follows:<br />

∆Grain yield = UDP grain yield – FP grain yield<br />

∆Applied N = UDP applied N – FP applied N<br />

∆PFP-N = PFP-N for UDP – PFP-N for FP<br />

4<br />

3<br />

2<br />

1:1 line<br />

1<br />

1 2 3 4 5 6 7 8 9<br />

Farmers’ practice grain yield (t ha –1 )<br />

Fig. 1. <strong>Rice</strong> yields (paddy) obtained in Bangladesh using deeppoint<br />

placement of urea briquettes (UDP) plotted against yields<br />

obtained using broadcast urea (farmers’ practice) in side-by-side<br />

comparisons in farmers’ fields during 2000-04.<br />

Results<br />

Figure 1 shows the relationship between UDP and FP grain<br />

yields. The 1:1 line in the figure provides a reference by which<br />

the performance of UDP can be compared directly with that of<br />

the current practice of broadcast urea (FP); hence, points to<br />

the left of the line indicate UDP dominance, w<strong>here</strong>as points to<br />

the right indicate FP dominance. Clearly, in side-by-side comparisons<br />

of UDP versus FP, grain yields were consistently<br />

greater with deep-point placement of urea briquettes.<br />

Two aspects of the comparison shown in Figure 1 are<br />

revealing. First, the yield increase with UDP was achieved using<br />

much less urea fertilizer than with FP. On average, the amount<br />

of N applied to the UDP boro crop was only 53% of that applied<br />

to FP boro. Likewise, the UDP aman crop received only<br />

62% of the N applied to FP aman. The second aspect of interest<br />

is the consistency of the UDP yield benefit across a wide<br />

range of yield environments. The regression of UDP yields on<br />

FP yields provided a highly significant linear relationship defined<br />

by the following equation: UDP = 1.02 + 1.00 FP (r =<br />

0.92, SE of regression coefficient = 0.019). The slope equal to<br />

one indicates that the average yield benefit of 1.02 t ha –1 (SE<br />

= 0.08) was the same for all farmers regardless of whether<br />

they were at the low end or the high end of the yield gradient.<br />

Figure 2 shows the comparative distributions for changes<br />

in grain yield (∆Grain yield), N fertilizer use (∆Applied N),<br />

and the partial factor productivity of applied N (∆PFP-N) for<br />

boro and aman crops. Invariably, UDP was superior to FP for<br />

all parameters, providing greater yield with less applied N,<br />

which meant that the PFP of applied N increased as well. For<br />

the boro season, the UDP yield benefit was greater than 700<br />

370 <strong>Rice</strong> is life: scientific perspectives for the 21st century


kg grain ha –1<br />

2,000<br />

1,500<br />

1,000<br />

500<br />

0<br />

–500<br />

Boro Aman Boro Aman Boro Aman<br />

kg grain per kg N applied<br />

100<br />

50<br />

0<br />

–50<br />

–100<br />

DGrain yield DApplied N DPFP-N<br />

–150<br />

Fig. 2. Comparative distributions showing the changes in grain yield (∆Grain yield), N<br />

fertilizer use (∆Applied N), and partial factor productivity of applied N (∆PFP-N) attributed<br />

to UDP technology versus the farmers’ practice (FP) for the boro and aman rice<br />

crops. The box plots display the 10th, 25th, 50th, 75th, and 90th percentile observations<br />

along with the mean (solid marker).<br />

kg grain ha –1 in 75% of the on-farm comparisons, increasing<br />

to more than 1,400 kg grain ha –1 in as many as 25% of the<br />

comparisons. At the same time, 75% of the farmers realized a<br />

reduction in applied N of more than 45 kg N ha –1 , while as<br />

many as 25% of the farmers achieved a savings that exceeded<br />

90 kg N ha –1 . Furthermore, in 75% of the comparisons, the<br />

increased yield and savings in applied N translated into increases<br />

in the PFP-N of more than 30 kg of grain per kg of<br />

applied N. Similar distributions, but with somewhat smaller<br />

values, were obtained for all three parameters during the aman<br />

season. Except for a few cases w<strong>here</strong> the use of applied N was<br />

greater for UDP aman than for FP aman (i.e., ∆Applied N was<br />

positive), all distributions showed that UDP provided greater<br />

benefits in both seasons, and t<strong>here</strong> was essentially no risk of<br />

obtaining a less favorable outcome using UDP versus FP.<br />

The average UDP yield benefit over the current practice<br />

was 1,120 kg grain ha –1 (SE = 32.4) during the boro season<br />

and 890 kg grain ha –1 (SE = 32.5) during the aman. Importantly,<br />

the savings in applied N amounted to 70 kg N ha –1 (SE<br />

= 2.4) during the boro season and 35 kg N ha –1 (SE = 9.1)<br />

during the aman. As impressive as these numbers appear, they<br />

are certainly realistic and within the range of values cited by<br />

others for both on-farm and on-station experiments (Daftardar<br />

et al 1997, Mohanty et al 1999, Pasandaran et al 1999, Savant<br />

and Stangel 1990).<br />

Discussion and conclusions<br />

The current practice of broadcasting urea represents a tremendous<br />

waste because much of the applied N is lost before it can<br />

be effectively used by the plant. Greater adoption of UDP by<br />

rice farmers could improve the use efficiency of applied N<br />

and successfully reduce losses to the environment. If the numbers<br />

obtained from the on-farm studies are taken to be representative<br />

for all of Bangladesh, then the 7 million hectares of<br />

rice (4 million boro, 3 million aman) grown annually in the<br />

country could potentially produce about 7 million t more rice,<br />

and do so with about 0.4 million t less applied N using UDP<br />

technology.<br />

The efforts to improve N-use efficiency using UDP technology<br />

in Bangladesh and other Asian countries have also<br />

helped to identify situations w<strong>here</strong> the effectiveness of UDP<br />

may be less than expected and w<strong>here</strong> adoption may also be<br />

limited (Mohanty et al 1999). For example, UDP would not be<br />

as effective on soils with high internal drainage. Additionally,<br />

it is important to recognize that UDP will be most effective<br />

when using high-yielding varieties and good management practices.<br />

For flooded rice systems, few practical improvements<br />

in fertilizer management or products prove to be as cost-effective<br />

as UDP in increasing fertilizer-use efficiency and addressing<br />

food production and environmental concerns. As UDP technology<br />

continues to be improved and adopted in Bangladesh,<br />

it promises to significantly reduce N losses to the environment<br />

while also increasing grain yield and improving farmer income.<br />

References<br />

Daftardar S, Wagle S, Savant N. 1997. Agronomic performance of<br />

urea briquettes containing diammonium phosphate in rainfed<br />

transplanted rice on farmers’ fields. J. Agric. Sci. Cambridge<br />

128:291-297.<br />

Mohanty SK, Singh U, Balasubramanian V, Jha KP. 1999. Nitrogen<br />

deep-placement technologies for productivity, profitability, and<br />

environmental quality of rainfed lowland rice systems. Nutr.<br />

Cycl. Agroecosyst. 53:43-57.<br />

Pasandaran E, Gultom B, Sri Adiningsih J, Apsari H, Rochayati S.<br />

1999. Government policy support for technology promotion<br />

and adoption: a case study of urea tablet technology in Indonesia.<br />

Nutr. Cycl. Agroecosyst. 53:113-119.<br />

Session 12: Conservation of soil, water, and environment in rice cultures 371


Savant N, Stangel P. 1990. Deep placement of urea supergranules in<br />

transplanted rice: principles and practices. Fert. Res. 25:1-<br />

83.<br />

Notes<br />

Authors’ addresses: W.T. Bowen, resident representative, <strong>International</strong><br />

Fertilizer Development Center-Asia Division, Road<br />

54A-House #2-Apt. #6, Gulshan 2, Dhaka 1212, Bangladesh;<br />

R.B. Diamond, senior scientist-retired, IFDC; U. Singh, senior<br />

scientist, Resource Development Division; T.P. Thompson,<br />

senior scientist, Market Development Division, IFDC,<br />

P.O. Box 2040, Muscle Shoals, Alabama 35662, USA.<br />

Acknowledgments: We wish to acknowledge the significant contributions<br />

made by M.M. Islam, S.A.M. Hossain, and K.M. Elahi<br />

in carrying out the work that has been presented. Funding for<br />

the on-farm studies was provided by the <strong>International</strong> Fund<br />

for Agricultural Development.<br />

New fertilizer management to maximize yield<br />

and minimize environmental effects in rice culture<br />

Masahiko Saigusa<br />

In paddy fields, leaching and denitrification of applied fertilizer<br />

nitrogen result in a low fertilizer-use efficiency. The average<br />

recovery rate of basally applied rapidly available fertilizer<br />

(RAF) nitrogen has been clarified to be about 30% in the<br />

tillage transplanting system using 15 N-labeled fertilizer. These<br />

losses of fertilizer nitrogen lead to increased nitrous oxide in<br />

the troposp<strong>here</strong>, and contribute to both global warming and<br />

destruction of the stratospheric ozone layer. Compared with<br />

basally applied nitrogen, topdressed N showed a fairly high<br />

recovery rate (50–60%). T<strong>here</strong>fore, multiple split application<br />

of N fertilizer reduces N losses, but increases operating costs.<br />

On the other hand, the invention of controlled-availability fertilizer<br />

(CAF) whose nutrient release rate meets plant nutrient<br />

demand allowed contact application of fertilizer with plant<br />

seeds or roots (co-situs application). Consequently, CAF contributes<br />

to the improvement of fertilizer-use efficiency to a great<br />

extent, mitigation of environmental loading from fertilizer, and<br />

the development of innovative fertilizer application methods<br />

such as a single basal application of total fertilizer, a single<br />

basal nursery application of nutrients, the application of an<br />

aimed form of nutrients directly to plant roots, etc., and the<br />

establishment of innovative farming systems such as no-tillage<br />

transplanting rice culture, no-tillage direct-seeding rice<br />

culture, etc. (Shoji and Gandeza 1992).<br />

The objectives of this paper are to show the concept of<br />

co-situs application of CAF and to summarize the innovative<br />

field work that has been done by our research group in the last<br />

two decades using this technique.<br />

The concept of co-situs application<br />

Rapidly available fertilizers such as ammonium sulfate, urea,<br />

etc., applied at the same site as seeds or in the intensive rooting<br />

zone often cause salt and/or ammonia injuries to plants<br />

because of their high solubility. T<strong>here</strong>fore, farmers generally<br />

have to adjust the soil intervening between fertilizer and seeds<br />

or roots, or to apply only small amounts of RAF as a contactplacement<br />

to avoid these injuries. Phenomena such as nitrification,<br />

denitrification, immobilization, and fixation of nutri-<br />

ents in the soil are caused by the intervention of soil between<br />

nutrients and plant roots as shown in Figure 1. However, the<br />

invention of controlled-availability fertilizer has made possible<br />

the contact application (co-situs application) of fertilizer with<br />

seeds or roots. The term co-situs, which means the existence<br />

of both fertilizer and seeds or roots at the same site (situs),<br />

was proposed by Shoji and Gandeza (1992) to distinguish the<br />

seed-placement or contact-placement of small amounts of RAF.<br />

T<strong>here</strong>fore, co-situs application of CAF can directly supply<br />

fertilizer components to plant roots, and thus increase fertilizer-use<br />

efficiency to a great extent by minimizing the reaction<br />

and interaction of fertilizer components with the soil (Fig.<br />

1). Consequently, it is also highly possible to mitigate the environmental<br />

loading of N 2 O and NO 3<br />

–<br />

caused by fertilizer N<br />

applied.<br />

No-tillage direct-seeding culture of rice with CAF<br />

In Japan, rice cropping has been facing serious problems, including<br />

overproduction, trade liberalization, the advanced average<br />

age of farmers, and a small number of successors, and<br />

thus a reduction in labor and production costs in rice cultivation<br />

is required. The most desirable rice farming system is direct<br />

seeding by no-tillage and a single basal fertilization using<br />

CAF, which can also reduce the growth process of rice seedlings.<br />

Single basal co-situs application of total fertilizer nitrogen<br />

with CAF, polyolefin-coated urea of the 100-day type<br />

(POCU-100), in no-tillage direct-seeding culture was conducted<br />

in comparison with a conventional culture using ammonium-sulfate<br />

(AS) for both basal and topdressing. Nitrogen<br />

recoveries of basal POCU-100, basal-AS, and topdressed AS<br />

fertilizer were 63.2%, 8.5%, and 41.5%, respectively. Reflecting<br />

the N-use efficiency, the brown rice yields of the POCU-<br />

100 plot were 33–55% superior to those in the conventional<br />

AS plot (Sato et al 1993).<br />

This no-tillage direct-seeding system is being used basically<br />

in well-drained paddy soil. However, in Tohoku (northeastern)<br />

District, the main rice-producing zone in Japan, more<br />

372 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Conventional application<br />

Co-situs application<br />

N 2<br />

O N 2<br />

Denitrification<br />

(paddy soil)<br />

Rapidly available<br />

fertilizer (RAF) Plant root<br />

Controlled<br />

availability<br />

fertilizer<br />

Plant root<br />

N 2<br />

H<br />

+<br />

4<br />

(CAF)<br />

Paddy<br />

NO 3<br />

–<br />

NH 4<br />

+<br />

Soil<br />

NO 3<br />

–<br />

Upland<br />

Soil<br />

NH 4<br />

+<br />

Soil<br />

NH 4 + , (NH 2<br />

) CO<br />

Nitrification<br />

NO 3<br />

–<br />

NO 3<br />

–<br />

Leaching<br />

(upland soil)<br />

Direct<br />

absorption<br />

Fig. 1. Dynamics of applied fertilizer in soil.<br />

than half of the paddy fields are occupied by poorly drained<br />

soil. T<strong>here</strong>fore, the development of no-tillage direct seeding<br />

of rice on Y-shaped furrows without covering soil using CAF<br />

was studied in a heavy-textured Hachirogata soil and resulted<br />

in the same level of brown rice yield as with the conventional<br />

transplanting system (Tashiro et al 2000).<br />

Single co-situs application of CAF to a nursery box<br />

In the last two decades, about one-third of the total area under<br />

rice cultivation in Japan was converted to other crops such as<br />

soybean, wheat, and forage crops by political control of rice<br />

cultivation. T<strong>here</strong>fore, for farmers, the quality of rice is becoming<br />

a greater issue than the quantity because of its much<br />

higher price. At the same time, farmers are forced to reduce<br />

labor and production costs in rice cultivation. The development<br />

of a sigmoid type of CAF, which shows a delayed N release<br />

for a specified number of days, signified a single cositus<br />

application of CAF to nursery boxes (Sato and Shibuya<br />

1991). The controlled release of nitrogen from sigmoid<br />

POCUs-100 held by rice roots, which takes place after transplanting,<br />

remarkably improved the N-use efficiency of fertilizer<br />

(Saigusa et al 1996, 2004).<br />

No-tillage transplanting cultivation<br />

with co-situs application of CAF to a nursery box<br />

No-tillage transplanting rice cultivation is expected to maintain<br />

the grain quality of rice while saving both labor and production<br />

costs by eliminating plowing and puddling. However,<br />

in this system, farmers had to apply RAF on the surface of the<br />

soil as basal and topdressing, and thus fertilizer-use efficiency<br />

was extremely low (< 10%). T<strong>here</strong>fore, the technique of growing<br />

seedlings by the single co-situs application of CAF to a<br />

nursery box was introduced in this system and both the recovery<br />

of nitrogen and brown rice yield were examined in three<br />

different types of paddy soils in comparison with those in the<br />

conventional transplanting system (Saigusa et al 1996, 2004).<br />

The recoveries of POCUs-100 in the no-tillage system, basal-<br />

AS, and the 1st and 2nd topdressed AS in the conventional<br />

tillage system were 61.4–82.7%, 31.1–43.1%, 40.0–76%, and<br />

43–82.7%, respectively. The recoveries of fertilizer in each<br />

treatment seemed to be in the following order: light clay alluvial<br />

soil > clay loam Andisol > sandy loam alluvial soil, and<br />

also basal POCUs-100 > 2nd topdressed AS > 1st topdressed<br />

AS > basal AS. These results indicate that the co-situs application<br />

of sigmoid CAF in a nursery box for the no-tillage transplanting<br />

system increases the N-use efficiency of fertilizer compared<br />

with AS in the conventional transplanting system, and<br />

thus could increase both the growth and yield of rice plants in<br />

each soil and reduce environmental degradation caused by fertilizer<br />

N (Saigusa et al 2004).<br />

Supply of the aimed form of nitrogen<br />

using co-situs application of CAF<br />

In paddy soil, nitrogen applied as nitrate is much more unstable<br />

than ammonium because of denitrification caused by its<br />

reductive condition (Fig. 1). T<strong>here</strong>fore, it is almost impossible<br />

to supply the nitrate form of nitrogen for rice plants using RAF.<br />

On the other hand, the single co-situs application of CAF may<br />

directly supply the fertilizer component to plant roots (Fig. 1).<br />

T<strong>here</strong>fore, the supply of the nitrate form of nitrogen to rice<br />

plants was examined by the co-situs application of polyolefincoated<br />

calcium nitrate (POC-CN) (Saigusa et al 2001).<br />

As Figure 2 shows, the recoveries of calcium nitrate (CN)<br />

at the harvesting stage were only about 2% in both clay loam<br />

Andisol and light clay alluvial soil because of denitrification,<br />

w<strong>here</strong>as those of POC-CN were 21–26%, which were almost<br />

the same as those of AS (22–24%). These results may show<br />

that rice roots can absorb nitrate-N from POC-CN particles<br />

because they can come into contact with the CAF without any<br />

Session 12: Conservation of soil, water, and environment in rice cultures 373


Recovery (%)<br />

80<br />

Clay loam Andisol<br />

60<br />

40<br />

20<br />

80<br />

60<br />

40<br />

20<br />

Light clay alluvial soil<br />

0<br />

0<br />

CN AS POC-CN POCU<br />

CN AS POC-CN POCU<br />

Fig. 2. Recoveries of different forms of nitrogen fertilizer by the rice plant. CN = calcium nitrate,<br />

AS = ammonium sulfate, POC-CN = polyolefin-coated calcium nitrate, POCU = polyolefin-coated<br />

urea.<br />

burning. The highest recoveries were obtained in POCU (49–<br />

50%). Reflecting the recovery of each fertilizer, the grain yields<br />

of rice were in the following order: POCU > AS = POC-CN ><br />

CN. These results imply that the supply of the aimed form of<br />

nutrient directly from fertilizer to plant roots is highly feasible<br />

through the co-situs application of CAF. Similar results were<br />

obtained in supplying NH 4 + -N in upland soil, Fe 2+ in alkaline<br />

paddy soil, Cu 2+ in high-humus Andisol, and P in Andisol by<br />

the co-situs application of CAF containing these components.<br />

From the foregoing, I conclude that co-situs application of CAF<br />

with seeds or plant roots is a unique technology and is highly<br />

feasible in developing an innovative farming system.<br />

References<br />

Saigusa M, Hossain Md Z, Shibuya K. 2004. No-tillage transplanting<br />

system of rice with controlled availability fertilizer in a<br />

nursery box. J. Integ. Field Sci. 1:67-73.<br />

Saigusa M, Hossain Md Z, Tashiro T, Shibuya K. 1996. Maximizing<br />

rice yield with controlled availability fertilizer and no-tillage<br />

culture in controlling environmental degradation. Proceedings<br />

of the symposium on “Maximizing sustainable rice yields<br />

through improved soil and environmental management,” Khon<br />

Kaen, Thailand. p 799-804.<br />

Saigusa M, Ombodi A, Owashi T, Watanabe H. 2001. Supply of<br />

aimed form of nitrogen using controlled availability fertilizer.<br />

Fertilization in the Third Millennium: Fertilizer, Food Security<br />

and Environmental Protection, 12th World Fertilizer Congress<br />

of CIEC. p 315-321.<br />

Sato T, Shibuya K. 1991. One-time application of total nitrogen fertilizer<br />

at nursery stage in rice culture. Rep. Tohoku Br. Crop<br />

Sci. Soc. Jpn. 34:15-16.<br />

Sato T, Shibuya K, Saigusa M, Abe T. 1993. Single basal application<br />

of total nitrogen fertilizer with controlled-release coated<br />

urea on non-tilled rice culture. Jpn. J. Crop Sci. 62:408-413.<br />

Shoji S, Gandeza AT. 1992. New concept of controlled release fertilization.<br />

In: Shoji S, Gandeza AT, editors. Controlled release<br />

fertilizer with polyolefin resin coating. Sendai (Japan): Konno<br />

Printing Co. p 1-7.<br />

Tashiro T, Sugawara O, Naganoma H, Chiba K, Saigusa M. 2000.<br />

Direct seeding of rice on Y-shaped furrow without tillage and<br />

covering soil in poorly drained paddy soil. Jpn. J. Crop Sci.<br />

69:547-553.<br />

Notes<br />

Author’s address: Field Science Center, Graduate School of Agricultural<br />

Science, Tohoku University, 232-3, Yomogida,<br />

Oguchi, Naruko, Tamatukuri, Miyagi 989-6711, Japan, e-mail:<br />

masa@bios.tohoku.ac.jp.<br />

Does anaerobic decomposition of crop residues impair soil<br />

nitrogen cycling and yield trends in lowland rice<br />

D.C. Olk, K.G. Cassman, M.M. Anders, K. Schmidt-Rohr, and J.-D. Mao<br />

Soil organic matter (SOM) plays a central role in the storage<br />

and release of essential soil nutrients into plant-available forms.<br />

Its behavior in nutrient cycling is thought to be affected by its<br />

chemical nature, although evidence is sparse. Recent work in<br />

irrigated lowland rice (Oryza sativa L.) soils in the Philippines<br />

suggests that the chemical nature of SOM depends in<br />

part on whether its main parent material, crop residues, decomposes<br />

anaerobically or aerobically, raising the question<br />

whether anaerobic decomposition contributed to a long-term<br />

yield decline. In addition, scattered reports from lowland rice<br />

in other regions and from other agrosystems in which crop<br />

residues also decompose anaerobically indicate recurring nutrient<br />

deficiencies, which can also reduce yield. The specific<br />

nutrients that become deficient are all prone to chemical binding<br />

with SOM. Hence, the question arises whether anaerobic<br />

decomposition of crop residues in<strong>here</strong>ntly alters the formation<br />

of new SOM and its chemical composition, which results<br />

in greater binding of new SOM with nutrients, inhibiting their<br />

release to available forms. This report will summarize existing<br />

knowledge on the occurrences of reduced nutrient avail-<br />

374 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. <strong>Rice</strong> crop uptake (kg ha –1 ) of fertilizer N and soil N at three crop growth<br />

stages for two crop rotations in Stuttgart, Arkansas, 2002. Standard errors are in<br />

parentheses.<br />

N pool Rotation Green ring 50% heading Preharvest<br />

(83 DAE) a (103 DAE) (126 DAE)<br />

Fertilizer <strong>Rice</strong>-soybean 59 (6) 52 (3) 54 (4)<br />

<strong>Rice</strong>-rice 52 (3) 42 (4) 40 (4)<br />

Difference 7 10 14<br />

Soil <strong>Rice</strong>-soybean 50 (2) 69 (11) 91 (13)<br />

<strong>Rice</strong>-rice 44 (8) 44 (8) 67 (5)<br />

Difference 6 25 24<br />

a DAE = days after emergence.<br />

ability in relation to the chemical nature of SOM in flooded<br />

soils, with emphasis on lowland rice cropping in tropical Asia<br />

and the southern U.S. rice belt.<br />

Intensive lowland rice cropping in tropical Asia<br />

A long-term decline in grain yield has been noted in some field<br />

trials under double- and triple-cropping of irrigated lowland<br />

rice (Cassman et al 1995), which involves regular anaerobic<br />

decomposition of crop residues and long-term submerged conditions.<br />

The principal cause of the yield decline appears to be<br />

decreased availability of soil organic nitrogen (N, Dobermann<br />

et al 2000), especially during late-season crop growth stages;<br />

the quantity of soil N did not decrease during the years of declining<br />

yields and crop uptake efficiency of fertilizer N changed<br />

little. Hence, research efforts have focused on changes in the<br />

chemical nature of soil organic N.<br />

An accumulation of phenolic compounds has been associated<br />

with this intensive cropping (Olk et al 1996). The phenols<br />

are found in incompletely decomposed lignin residues from<br />

the woody tissues of crop roots and stubble. Studying the young<br />

mobile humic acid (MHA) fraction that was extracted from<br />

both a triple-cropped rice soil and a nearby rice field maintained<br />

under aerobic conditions at the <strong>International</strong> <strong>Rice</strong> <strong>Research</strong><br />

<strong>Institute</strong> (<strong>IRRI</strong>), Schmidt-Rohr et al (2004) demonstrated<br />

that the triple-cropped fraction had an agronomically<br />

significant excess (55 kg N ha –1 ) of organic N bound covalently<br />

in aromatic compounds, mainly with phenolic lignin residues<br />

in an anilide molecule. This form would cycle only slowly under<br />

flooded conditions.<br />

In a double-cropped rice experiment conducted at three<br />

sites in the Philippines, phenols accumulated in the MHA fraction<br />

despite large differences among the sites in the degree of<br />

soil drying during two 2-month fallows (Olk et al 1998). Grain<br />

yields declined at the two sites with either the wettest or the<br />

driest fallows, and decomposition of crop residues was anaerobic<br />

at all three sites. Hence, the key feature of continuous rice<br />

cropping that may promote phenol accumulation and decreased<br />

availability of soil N may be anaerobic decomposition of crop<br />

residues, not the total duration of annual flooding.<br />

Soil phenol accumulation and N mineralization were<br />

measured in a 4-year study at <strong>IRRI</strong> that compared anaerobic<br />

decomposition of crop residues with aerobic decomposition<br />

for double-cropped rice. In the third wet-season crop, urea fertilizer<br />

labeled with 15 N was applied at transplanting. Two weeks<br />

later, the amount of 15 N that became immobilized in the MHA<br />

was similar for both treatments. During the rest of the season,<br />

45% of the immobilized 15 N was remineralized in the aerobic<br />

decomposition treatment, but only 8% was remineralized in<br />

the anaerobic decomposition treatment (Olk and Cassman<br />

2002). In-season mineralization of total N from the MHA was<br />

22 kg N ha –1 less with anaerobic decomposition than with aerobic<br />

decomposition. Phenols accumulated in the MHA under<br />

anaerobic decomposition, in tandem with the inhibition of N<br />

mineralization. The phenol accumulation was also associated<br />

with inhibited mineralization of soil N across crop rotations<br />

(rice-rice versus rice-maize, Zea mays L.), humic fraction, N<br />

fertilizer rate, and year. A crop response to the N inhibition<br />

could not be demonstrated because N fertilizer was applied in<br />

synchrony with crop N demand.<br />

Continuous rice rotation in Arkansas, U.S.<br />

The conventional crop rotation in eastern Arkansas is rice-soybean<br />

(Glycine max (L.) Merr.), with one crop per year. Pending<br />

market changes may promote continuous production of<br />

rice in fields near water bodies. In a 4-year field trial, however,<br />

grain yield of a continuous rice rotation was 19% (1,350<br />

kg ha –1 ) less than for rice yield following soybean (Anders et<br />

al 2004). Similar to the <strong>IRRI</strong> yield decline, agronomic symptoms<br />

attribute this yield gap to a late-season N deficiency. In a<br />

15 N-microplot study conducted in 2002, crop uptake at midto<br />

late-season crop growth stages of unlabeled N, presumably<br />

mineralized from SOM, was less for continuous rice than for<br />

rice following soybean (Table 1). The difference between crop<br />

rotations for uptake of labeled fertilizer N was less severe,<br />

suggesting an inhibition of soil N mineralization in the continuous<br />

rice rotation. In-season degradation of soil phenols also<br />

slowed under the continuous rice rotation, as their enrichment<br />

compared to rice following soybean was greater near harvest<br />

than at an early growth stage (Fig. 1). This study is ongoing.<br />

Session 12: Conservation of soil, water, and environment in rice cultures 375


Phenol content (g kg –1 organic C)<br />

18<br />

<strong>Rice</strong>-soybean<br />

Continuous rice<br />

18<br />

12<br />

Early season (55 DAE)<br />

12<br />

Preharvest (126 DAE)<br />

6<br />

6<br />

0<br />

p-Hydroxyl Cinnamyl<br />

Vanillyl Syringyl<br />

Phenol class<br />

Total<br />

0<br />

p-Hydroxyl Cinnamyl<br />

Vanillyl Syringyl<br />

Phenol class<br />

Fig. 1. Soil contents of four phenol classes for rice-soybean and continuous rice rotations at two<br />

sampling times in Stuttgart, Arkansas, 2002. Units are g phenol kg –1 soil organic carbon (C). DAE is<br />

days after emergence. Standard errors are indicated above each bar.<br />

Total<br />

<strong>Rice</strong>-wheat rotation in Japan<br />

A rice sterility problem has occurred in rice-wheat (Triticum<br />

sp.) rotations in Osato, Saitama, Japan. In a greenhouse study,<br />

Noguchi et al (1997) associated the sterility with a copper (Cu)<br />

deficiency that occurred with anaerobic decomposition of crop<br />

residues from either rice or wheat. Anaerobic soil conditions<br />

without incorporation of crop residues did not cause rice sterility.<br />

<strong>Rice</strong> uptake of manganese, and to a lesser extent of other<br />

nutrients, was also less with anaerobic decomposition than with<br />

anaerobic conditions without crop residue incorporation. Copper<br />

and manganese have a high affinity for binding with humic<br />

molecules in laboratory conditions (Schnitzer and Hansen<br />

1970). <strong>Rice</strong> crop uptake of Cu and manganese was also diminished<br />

by anaerobic decomposition of crop residues in the <strong>IRRI</strong><br />

field comparison of anaerobic decomposition with aerobic<br />

decomposition as described above (data not shown). Similarly,<br />

Cu deficiencies in organic soils are well known; the Cu is<br />

thought to be bound to SOM by oxygenated functional groups,<br />

such as phenolic hydroxyls.<br />

No-tillage in temperate regions<br />

In no-tillage systems of temperate regions, crop residues decompose<br />

to a larger extent during the springtime than under<br />

conventional tillage, which by contrast typically promotes autumn<br />

decomposition through postharvest tillage. In many temperate<br />

regions, abundant springtime precipitation saturates the<br />

soils for extended periods of time. Consequently, decomposition<br />

of crop residues is more often anaerobic, or partially anoxic,<br />

with no-tillage than with conventional tillage. In several<br />

North American studies involving 15 N-enriched fertilizer, crop<br />

uptake of unlabeled N, presumably mineralized from SOM,<br />

was significantly less with no-tillage than with conventional<br />

tillage (Doran and Smith 1987). At some locations, the decrease<br />

in soil N uptake was associated with a loss of grain<br />

yield.<br />

Discussion<br />

Evidence from multiple agrosystems is consistent with the<br />

hypothesis that anaerobic decomposition of crop residues promotes<br />

an enrichment of phenolic lignin residues in newly forming<br />

SOM, which can bind specific soil nutrients into less available<br />

forms. This hypothesis would account for the decreased<br />

in-season N mineralization that was observed in rice soils of<br />

both the Philippines and Arkansas. Phenolic compounds are<br />

also capable of binding with Cu, which also becomes deficient<br />

with anaerobic decomposition.<br />

Demonstration of strong nutrient binding, at least for N,<br />

does not itself prove that anaerobic decomposition leads to<br />

yield loss. Even strongly bound nutrient forms, most notably<br />

the anilide N found by Schmidt-Rohr et al (2004), must mineralize<br />

at some point; otherwise, total soil N would increase indefinitely<br />

with anaerobic decomposition, which is not the case.<br />

Future research will explore the hypothesis that mineralization<br />

of strongly bound nutrients is so slow as to become<br />

unsynchronized with crop nutrient demand, and as the strongly<br />

bound forms accumulate in soil, the soil nutrient supply also<br />

becomes increasingly unsynchronized, potentially diminishing<br />

the yield. Possible mitigation options include timely soil<br />

aeration, which would promote decomposition of the lignin<br />

residues and release of the bound nutrients. For example, rice<br />

fields in Japan are commonly drained during later crop growth<br />

stages to promote soil N mineralization.<br />

How relevant is chemical stabilization of soil nutrients<br />

to yield trends for Asian rice farmers Available data sets do<br />

not allow comment on whether on-farm yields or productivity<br />

(ratio of yield to inputs) have declined since lowland rice cropping<br />

was intensified 30+ years ago. A definitive database would<br />

376 <strong>Rice</strong> is life: scientific perspectives for the 21st century


include on-farm grain yields since the onset of intensive rice<br />

cropping for fields in which fertilizer rates and other management<br />

strategies have remained relatively constant. This database<br />

does not exist.<br />

Chemical binding of nutrients by phenolic lignin residues<br />

following anaerobic decomposition may most likely affect<br />

yield trends when yield is primarily limited by N, when<br />

initial yield levels are relatively high, and when N fertilizer is<br />

not applied in synchrony with crop N demand. At high yields,<br />

large amounts of crop lignin are incorporated into the soil,<br />

which may enhance N binding. In other situations w<strong>here</strong> chemical<br />

binding may not perceptibly affect yield levels, its occurrence<br />

would nevertheless cause less efficient use of soil N,<br />

requiring increased N fertilizer inputs to maintain yields.<br />

References<br />

Anders MM, Olk D, Harper T, Daniel T, Holzhauer J. 2004. The<br />

effect of rotation, tillage, and fertility on rice grain yields and<br />

nutrient flows. In: Proceedings, 26th Southern Conservation<br />

Tillage Conference for Sustainable Agriculture, 8-9 June 2004.<br />

Raleigh, N.C. (USA): North Carolina Agricultural <strong>Research</strong><br />

Service. CD format.<br />

Cassman KG, de Datta SK, Olk DC, Alcantara J, Samson M,<br />

Descalsota J, Dizon M. 1995. Yield decline and the nitrogen<br />

economy of long-term experiments on continuous, irrigated<br />

rice systems in the tropics. In: Lal R, Stewart BA, editors.<br />

Soil management: experimental basis for sustainability and<br />

environmental quality. Boca Raton, Fla. (USA): CRC/Lewis<br />

Publishers. p 181-222.<br />

Dobermann A, Dawe D, Roetter RP, Cassman KG. 2000. Reversal<br />

of rice yield decline in a long-term continuous cropping experiment.<br />

Agron. J. 92:633-643.<br />

Doran JW, Smith MS. 1987. Organic matter management and utilization<br />

of soil and fertilizer nutrients. In: Follett RF, Stewart<br />

JWB, Cole CV, editors. Soil fertility and organic matter as<br />

critical components of production systems. Madison, Wis.<br />

(USA): Soil Science Society of America. p 53-72.<br />

Noguchi A, Hasegawa I, Shinmachi F, Yazaki J. 1997. Possibility of<br />

copper deficiency and impediment in ripening in rice from<br />

application of crop residues in submerged soil. In: Ando T,<br />

Fujita K, Mae T, Matsumoto H, Mori S, Sekiya J, editors.<br />

Plant nutrition for sustainable food production and environment.<br />

Proceedings of the XIII <strong>International</strong> Plant Nutrition<br />

Colloquium. Dordrecht (Netherlands): Kluwer Academic Publishers.<br />

p 799-800.<br />

Olk DC, Cassman KG, Randall EW, Kinchesh, P, Sanger LJ, Anderson<br />

JM. 1996. Changes in chemical properties of organic<br />

matter with intensified rice cropping in tropical lowland soil.<br />

Eur. J. Soil Sci. 47:293-303.<br />

Olk DC, Cassman KG, Mahieu N, Randall EW. 1998. Conserved<br />

chemical properties of young humic acid fractions in tropical<br />

lowland soil under intensive irrigated rice cropping. Eur. J.<br />

Soil Sci. 49:337-349.<br />

Olk DC, Cassman KG. 2002. The role of organic matter quality in<br />

nitrogen cycling and yield trends in intensively cropped paddy<br />

soils. In: Proceedings, 17th World Congress of Soil Science,<br />

14-20 August 2002. Bangkok: Thailand Ministry of Agriculture<br />

and Cooperatives. p 1355(1)-1355(8).<br />

Schmidt-Rohr K, Mao J-D, Olk DC. 2004. Nitrogen-bonded aromatics<br />

in soil organic matter and their implications for a yield<br />

decline in intensive rice cropping. Proc. Nat. Acad. Sci. USA<br />

101:6351-6354.<br />

Schnitzer M, Hansen EH. 1970. Organo-metallic interactions in soils.<br />

8. An evaluation of methods for the determination of stability<br />

constants of metal-fulvic acid complexes. Soil Sci. 109:333-<br />

340.<br />

Notes<br />

Authors’ addresses: D.C. Olk, USDA-ARS, National Soil Tilth Lab,<br />

2150 Pammel Drive, Ames, Iowa 50011; K.G. Cassman, Department<br />

of Agronomy and Horticulture, University of Nebraska,<br />

Lincoln, Nebraska 68583; M.M. Anders, University<br />

of Arkansas <strong>Rice</strong> <strong>Research</strong> and Extension Center, 2900 Hwy<br />

130E, Stuttgart, Arkansas 72160; K. Schmidt-Rohr, Department<br />

of Chemistry, Iowa State University, Ames, Iowa 50011;<br />

J.-D. Mao, Dept. of Chemistry, Rocky Mountain College, 1511<br />

Poly Drive, Billings, Montana 59102, USA.<br />

Influence of the paddy-upland rotation on soil<br />

physicochemical properties and crop growth<br />

in the Honam Plain of Korea<br />

Lee Deog-Bae, Yang Chang-Hyu, Ryu Chul-Hyun, Lee Kyeong-Bo, and Kim Jae-Duk<br />

Rotation cultivation of rice and upland crops in paddies has<br />

been adopted for the multiple use of land and has affected the<br />

nutrient imbalance in the plant and soil. Multiple use of paddies<br />

has been required to adjust the balance between demand<br />

and supply of rice in some countries. Crop growth primarily<br />

depends on soil moisture content, and secondarily on nutrient<br />

content. The distribution of soil moisture and nutrients greatly<br />

depends on soil texture, groundwater level, and cropping system.<br />

Nutrient contents depend on fertilization and the application<br />

of farming materials. Rotation cultivation affects these<br />

properties. T<strong>here</strong>fore, the influence of the paddy-upland rotation<br />

on soil physicochemical properties, and crop growth and<br />

productivity, was studied in the Honam Plain area of the Republic<br />

of Korea.<br />

Session 12: Conservation of soil, water, and environment in rice cultures 377


Table 1. Change in organic matter content by cropping system (g<br />

100 g –1 ).<br />

Cropping system First Second Third Fourth Fifth<br />

year year year year year<br />

Continuous rice 2.7 2.3 2.5 2.2 2.6<br />

<strong>Rice</strong>-barley 2.8 2.5 2.5 2.6 2.3<br />

Soybean-barley 2.6 2.2 2.4 2.3 2.3<br />

Soybean-rice 2.3 2.2 2.6 2.6 2.4<br />

Soybean 2 y-rice 3.9 2.1 2.5 2.2 2.3<br />

Soybean 3 y-rice 3.0 2.3 2.1 2.0 2.2<br />

Table 2. Change in available phosphate content by cropping system<br />

(mg kg –1 ).<br />

Cropping system First Second Third Fourth Fifth<br />

year year year year year<br />

Continuous rice 188 170 148 137 139<br />

<strong>Rice</strong>-barley 105 145 161 134 131<br />

Soybean-barley 127 175 168 176 274<br />

Soybean-rice 154 153 145 144 189<br />

Soybean 2 y-rice 171 117 168 151 206<br />

Soybean 3 y-rice 157 148 159 171 192<br />

Materials and methods<br />

The experimental field was installed with a sand-gravel drainage<br />

trench with 2-m intervals, 60-cm width, and 30-cm height<br />

at 1-m soil depth in 1982. After installation of the drainage<br />

system, rice was cultivated in 1988. Treatments were continuous<br />

rice cultivation, rice-barley cropping, soybean-barley cropping,<br />

soybean-rice rotation, soybean for two years-rice for one<br />

year rotation, and soybean for three years-rice for one year<br />

cropping. Applied amounts of N-P 2 O 5 -K 2 O were 11-7-8 kg<br />

ha –1 in rice, 4-7-68 kg ha –1 in soybean, and 15-10-88 kg ha –1<br />

in barley.<br />

Results<br />

<strong>Rice</strong> yield increased after the rotation with soybean, and this<br />

effect increased gradually with two- and three-year continuous<br />

cultivation of soybean. This resulted from the increased<br />

number of panicles and number of grains per m 2 by the high<br />

content of NH 4+ -N in the soil. Meanwhile, rice yield decreased<br />

by 7% more in the barley-rice cropping system than in continuous<br />

rice cultivation.<br />

Soybean yield was higher in the annual rotation than in<br />

the biennial and three-year terms: 3.92 t ha –1 in annual, 3.56 t<br />

ha –1 in biennial, and 3.72 t ha –1 in the three-year interval. This<br />

effect resulted from the changing number of pods and grains<br />

per plant as time passed. Park et al (1993) reported that soybean<br />

yield decreased greatly in 4-year continuous cultivation<br />

in sandy loam paddy and 3-year continuous cultivation in silt<br />

loam paddy. Motomatsu (1990) also reported that soybean yield<br />

decreased by 10% in 2-year continuous cultivation and by 20%<br />

in 3-year continuous cultivation because of the reduction in<br />

soil N content and root activity and increment in disease and<br />

pest injury with continuous cropping.<br />

Barley yield increased by 4–7% in the soybean-barley<br />

cropping system vis-à-vis the rice-barley cropping system.<br />

T<strong>here</strong>fore, this was a positive effect of soybean culture on barley<br />

yield. Meanwhile, the annual yield of barley decreased<br />

gradually in both cropping systems as time passed.<br />

Upland crop cultivation increased soil porosity as time<br />

passed. The effect was higher in 2-year and 3-year cultivation<br />

of upland crops than with the annual rotation of rice. The increasing<br />

soil porosity was in the order of soybean for three<br />

years-rice rotation, soybean-barley cropping system, soybean<br />

for two years-rice rotation, and soybean-rice rotation. Iwata et<br />

al (1977) reported that soil porosity increased annually in the<br />

paddy-upland rotation with the development of aggregate.<br />

T<strong>here</strong> was little difference in organic matter content with<br />

the continuous rice cultivation, rice-barley cropping system,<br />

and rice-soybean cropping system. But organic matter content<br />

decreased drastically with soybean cultivation for two years<br />

and three years (Table 1). Kitada et al (1992) mentioned that<br />

soil organic matter decreased gradually with easy mineralization<br />

of organic matter in upland paddy conditions.<br />

Soil available phosphate content decreased gradually<br />

with continuous rice cultivation, but increased with rotation<br />

cultivation of an upland crop in the paddy (Table 2). This result<br />

was not related to fertilization amount but to phosphate<br />

dynamics. T<strong>here</strong> was little difference in the amount of phosphate<br />

fertilization among the crops. Phosphate is released in<br />

aerobic conditions and fixed in anaerobic conditions. This increment<br />

of phosphate in soybean cultivation resulted from<br />

phosphate fixation due to aerobic conditions. Kitada et al<br />

(1992) also reported that availability of phosphate decreased<br />

in upland conditions because of fixation to Fe and Al.<br />

T<strong>here</strong> was no change annually in Ca 2+ of soil with continuous<br />

rice cultivation, but the content increased after upland<br />

cultivation. Meanwhile, soybean cultivation caused an increase<br />

in Ca 2+ content in double cropping and rotation cultivation.<br />

Exchangeable K + content showed a small decrease in continuous<br />

rice cultivation, but an increase in rotation cultivation and<br />

a clearer increase in soybean-barley and soybean two yearsrice<br />

cultivation rotation. This stable content of Ca 2+ and K + in<br />

continuous rice cultivation implied that submerged rice cultivation<br />

had a positive effect on the balance of Ca 2+ and K + in<br />

the soil.<br />

The content of ammonium nitrogen was high in the order<br />

of soybean-rice, soybean two years-rice cultivation, ricebarley<br />

cropping system, soybean-barley cropping system, and<br />

continuous rice cultivation. The released amount of inorganic<br />

nitrogen in the rotational paddy was influenced by the soil texture,<br />

organic matter content, period of rotation, and cropping<br />

system (Watanabe 1985, Kogano 1987). Mineralized nitrogen<br />

was higher in upland culture than in continuous rice culture.<br />

378 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Conclusions<br />

T<strong>here</strong> are great differences in field conditions between rice<br />

and upland crops, mostly anaerobic and aerobic conditions,<br />

and irrigation of surface water and capillary migration of<br />

groundwater. These two factors could influence mass balance<br />

greatly. For a stable crop yield and soil environment in the<br />

paddy, rice cultivation can play a more positive role than upland<br />

crops. T<strong>here</strong>fore, annual rotational cultivation of rice and<br />

soybean was recommended.<br />

References<br />

Ikeda M, Harada I, Tamura K. 1958. Studies on three phases of soils.<br />

Part 4. Three phases of soil horizons and plant growth. Jpn.<br />

Soc. Sci. Soil Manure 29(2):84-86.<br />

Iwata H, Sawada M, Ookami M, Hukada K, Katou T. 1977. Redevelopment<br />

on method of paddy field land usage in lowland:<br />

change of soil physico-chemical properties in rotational paddy<br />

soil based on the ripening of upland soil. Bull. Aichi Natl.<br />

Agric. Exp. Stn. A9:125-130.<br />

Kitada K, Kamekawa K, Akiyama Y, Shimoda H, Yamagata M. 1992.<br />

Estimation of nutrient movement in rotational paddy soil based<br />

on the ripening of upland soil. Jpn. J. Soil Sci. Plant Nutr.<br />

63(3):349-351.<br />

Kogano K. 1987. Technique of stable high yield on paddy rice in<br />

rotational paddy field. Soil Field (Jpn.) 220:62-69.<br />

Motomatsu T. 1990. <strong>Research</strong> plan to increase the land utility in<br />

Japan. In: Han KH, Jo In Sang, editors. Strategic development<br />

in future and results of farmland cultivation project. Proceedings<br />

of symposium. Suwon (Korea): Rural Development<br />

Administration. p 161-183.<br />

Park CY, Kang UG, Hwang GS, Jung YT. 1993. Changes of crop<br />

yields according to cropping systems and fertilizing levels in<br />

paddy-upland rotation soils. J. Agric. Sci (S&F) 35(1):281-<br />

288.<br />

Watanabe K. 1985. Method of fertilization and soil characteristic on<br />

rotational paddy field in Hokkaido Center Region. Jpn. J. Soil<br />

Sci. Plant Nutr. 512-514.<br />

Notes<br />

Authors’ address: Honam Agricultural <strong>Research</strong> <strong>Institute</strong>, National<br />

<strong>Institute</strong> of Crop Science, Rural Development Administration,<br />

381 Songhak Dong Iksan 570-080, Republic of Korea, e-mail:<br />

leedb419@rda.go.kr.<br />

A decrease in soil fertility and crop productivity<br />

by succession of the paddy-upland rotation<br />

Hirokazu Sumida<br />

In Japan, rice production has tended to exceed domestic demand<br />

since around 1970, and the rice production adjustment<br />

by the government has already continued for more than 30 years.<br />

In 2004, the area of rice cultivation is restricted to about 60%<br />

of all paddy fields (i.e., 1.6 million ha). The government has<br />

recommended several types of alternative paddy field uses with<br />

subsidiary payments to farmers, especially alternative cropping<br />

of soybean, wheat, or fodder crops to increase self-sufficiency<br />

rates of these crops.<br />

It is known that the yields of soybean and/or wheat decrease<br />

when these crops are continuously cultivated in the upland<br />

fields that have been converted from paddy fields for many<br />

years. However, this injury from continuous cropping can be<br />

avoided by a paddy-upland (irrigated paddy rice and upland<br />

crop) rotation and the rotation leads to high yields of both rice<br />

and upland crops. T<strong>here</strong>fore, the paddy-upland rotation has<br />

been encouraged. Several previous studies on the combination<br />

of upland period and paddy period showed that more than 2–3<br />

years of paddy period is required for 2–3 years of upland period<br />

to keep crop productivity and soil nutrient dynamics suitable<br />

(Takahashi 1983, Hanai 1987, Tsukuda 1990, Kitada et al<br />

1993). Recently, it has been pointed out that soybean productivity<br />

decreased at some production sites, especially in the warm<br />

region of Japan, w<strong>here</strong> the rotation cycles are one year of upland<br />

for one to several years of paddy. Although t<strong>here</strong> is no<br />

clear evidence, this decrease in productivity could be attributed<br />

to a decrease in soil fertility. T<strong>here</strong>fore, to promote paddyupland<br />

rotation farming, sustainability of crop production in<br />

the successive paddy-upland rotation system should be investigated<br />

from a long-term view.<br />

Materials and methods<br />

The changes in soil fertility, soybean productivity, and paddy<br />

rice productivity were investigated by long-term field experiments<br />

under single cropping in a year on gray lowland soil in<br />

the cool region of Japan (National Agricultural <strong>Research</strong> Center<br />

for Tohoku Region, NARCT, Omagari, Akita).<br />

In experiment A, a field experiment in combination with<br />

different paddy/upland periods and organic matter application<br />

has been conducted since 1990. In a short-term upland rotation<br />

treatment, soybean (Glycine max (L.) Merr.) and paddy<br />

rice (Oryza sativa L.) were grown with a cycle of 1–2 years of<br />

upland and 1–3 years of paddy, respectively. A cycle of 3–4<br />

years of upland and 1–2 years of paddy was adopted in a medium-term<br />

upland rotation treatment. As a control, continuous<br />

Session 12: Conservation of soil, water, and environment in rice cultures 379


paddy rice cropping was done in a continuous paddy treatment.<br />

<strong>Rice</strong> straw was applied at 0 or 6 t ha –1 in each treatment<br />

after harvesting every autumn.<br />

In experiment B, the experimental paddy field was converted<br />

to an upland field in 1982 and soybean was cultivated<br />

during 18 years. After that, the field was returned to paddy and<br />

paddy rice was cultivated for three years. Then, in 2003, it was<br />

reconverted to an upland field for cultivating soybean. As a<br />

control, a continuous paddy treatment was prepared and paddy<br />

rice was cultivated t<strong>here</strong>. <strong>Rice</strong> straw compost was applied at 0<br />

or 20 t ha –1 to both treatments before plowing every spring.<br />

The average of total nitrogen (N) content of the applied rice<br />

straw compost was 5.5 mg g –1 (fresh-weight basis) for the 20<br />

years, and it was 3.5 mg g –1 for the last several years. The C/N<br />

ratio of the rice straw compost was about 20.<br />

For soil fertility, soil samples were collected from the<br />

plow layer in 1982 (only in experiment A), 1991, and 1999-<br />

2003. All the soil samples were air-dried and sieved (< 2 mm).<br />

Total carbon (C) and N content of the soil were determined by<br />

using the CN-Analyzer (Yanaco MT-700). The available N in<br />

the soil was measured by the soil incubation method (under<br />

submerged conditions at 30 ºC for 4 wk).<br />

Results and discussion<br />

Changes in soil fertility<br />

In the continuous paddy fields of experiments A and B, the<br />

total C, total N, and available N of soil were maintained at the<br />

initial levels without organic matter application, and were increased<br />

by organic matter application.<br />

When the successive paddy-upland rotations were continued<br />

for 10 years or more, whether the rotation was for the<br />

medium term or for the short term, a decrease in total C of the<br />

soil was observed and it wasn’t made up for by rice straw application<br />

at 6 t ha –1 . For N fertility, although the total N and<br />

available N of the soil were maintained roughly at their initial<br />

levels by rice straw application for the short-term upland rotation,<br />

the decrease in total N and available N of the soil wasn’t<br />

fully mitigated by the rice straw application in the mediumterm<br />

upland rotation (Fig. 1).<br />

Cultivating soybean for 18 years in the upland field converted<br />

from paddy field (long-term upland conversion) decreased<br />

the available N of the soil more than the paddy-upland<br />

rotation. The available N of the soil in the long-term upland<br />

conversion, even with application of rice straw compost at 20<br />

t ha –1 , was markedly lower than that in the continuous paddy<br />

field w<strong>here</strong> no organic matter was applied. By returning to a<br />

paddy field from long-term upland conversion and keeping it<br />

as a paddy field for three years, the available soil N recovered<br />

up to about 25% of the decrease caused by the 18-year longterm<br />

upland conversion.<br />

Changes in crop production related to soil fertility<br />

As Figure 2 shows, soybean yield in the successive paddyupland<br />

rotation and long-term upland conversion decreased<br />

by about 5–25% compared with that in the field w<strong>here</strong> soy-<br />

Available soil nitrogen (index)<br />

140<br />

120<br />

100<br />

80<br />

60<br />

40<br />

127<br />

Continuous P/+RS<br />

100<br />

–RS<br />

92<br />

75<br />

13 years after starting<br />

(after SB-SB-SB (or R)-SB)<br />

71<br />

Short-term U/+RS<br />

–RS<br />

Medium-term U/+RS<br />

Starting year<br />

9 years after starting<br />

(after rice-rice)<br />

Fig. 1. Changes in available soil nitrogen in the successive paddyupland<br />

rotation system. Available soil nitrogen (index): relative %<br />

of that in the continuous paddy field without rice straw application<br />

in the same year. P = paddy, U = upland, RS = rice straw, SB =<br />

soybean.<br />

bean was planted after a sufficient paddy period (the yield trial<br />

by the Soybean Breeding Lab, NARCT). In contrast, the yield<br />

of paddy rice in both cases (paddy-upland rotation and longterm<br />

upland conversion) was higher than that in the continuous<br />

paddy field.<br />

<strong>Rice</strong> straw application in the successive paddy-upland<br />

rotation produced no increase in soybean yield, w<strong>here</strong>as the<br />

rice straw compost application in long-term upland conversion<br />

increased soybean yield slightly. According to the experiment<br />

on the topdressing of N fertilizer, the N topdressing at 70<br />

kg ha –1 scarcely improved the yield of soybean planted in the<br />

upland field w<strong>here</strong> the decrease in soil N fertility occurred.<br />

These results implied that, in response to a decrease in<br />

soil N fertility, soybean yield in the successive paddy-upland<br />

rotation system decreased. In contrast, in spite of the considerable<br />

decrease in soil N fertility, the yield of paddy rice in the<br />

paddy field just returned from an upland field became higher<br />

than that in the continuous paddy field.<br />

References<br />

Hanai Y. 1987. Cropping systems in paddy field for multiple use.<br />

Res. J. Food Agric. 10(9):28-32. (In Japanese.)<br />

Kitada K, Shimoda H, Kamekawa K, Akiyama Y. 1993. Changes in<br />

soil nutrients affected by rotation of upland and paddy crop in<br />

gray lowland soil and search for the most suitable term of<br />

rotation. Jpn. J. Soil Sci. Plant Nutr. 64:154-160. (In Japanese<br />

with English summary.)<br />

72<br />

–RS<br />

380 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Yield index of soybean and paddy rice<br />

150<br />

125<br />

Short-term upland (Exp. A)<br />

Long-term upland (Exp. B)<br />

Medium-term upland (Exp. A)<br />

(gray: soybean, white: rice<br />

100<br />

75<br />

50<br />

Exp. A: av with and without rice straw application<br />

Exp. B: without rice straw compost application<br />

1990<br />

(1)<br />

[9]<br />

1992<br />

(3)<br />

[11]<br />

1991<br />

(2)<br />

[10]<br />

1993<br />

(4)<br />

[12]<br />

1994<br />

(5)<br />

[13]<br />

1996<br />

(7)<br />

[15]<br />

1995<br />

(6)<br />

[14]<br />

1997<br />

(8)<br />

[16]<br />

1998<br />

(9)<br />

[17]<br />

2000<br />

(11)<br />

[19]<br />

1999<br />

(10)<br />

[18]<br />

2001<br />

(12)<br />

[20]<br />

2002<br />

(13)<br />

[21]<br />

2003<br />

(14)<br />

[22]<br />

Year<br />

(years after starting Exp. A) [years after starting Exp. B]<br />

Fig. 2. Crop productivity in the successive paddy-upland rotation system and long-term<br />

upland conversion system. Control of soybean: soybean planted after sufficient paddy<br />

period (the yield trial by the soybean breeding lab, NARCT). Control of paddy rice: paddy<br />

rice planted in continuous paddy field (experiments A and B).<br />

Takahashi H. 1983. Land use by group farming and paddy-upland<br />

rotation system. Jpn. J. Farm Manage. 20(3):14-22. (In Japanese.)<br />

Tsukuda K. 1989. Suitable paddy-upland rotation cycle: introduction<br />

of experiments in Kanto-Tokai district. Agric. Hortic.<br />

65:385-388. (In Japanese.)<br />

Notes<br />

Author’s address: Headquarters, National Agriculture and Bio-oriented<br />

<strong>Research</strong> Organization, 3-1-1 Kannondai, Tsukuba,<br />

Ibaraki 3058517, Japan, e-mail: mizuki@affrc.go.jp.<br />

Acknowledgments: The author wishes to thank his colleagues, Dr.<br />

N. Kato and Mr. M. Nishida, for their helpful discussion.<br />

Promising technologies for reducing<br />

cadmium contamination in rice<br />

Satoru Ishikawa<br />

Cadmium (Cd) is principally dispersed in natural and agricultural<br />

environments through human activities. Japanese arable<br />

lands, especially paddy fields, are contaminated to some extent<br />

by Cd through irrigation with river water originating from<br />

mines or through emissions from metal-smelters. Recently, the<br />

joint FAO/WHO Expert Committee on Food Additives has<br />

established a Provisional Tolerable Weekly Intake (PTWI) of<br />

Cd at 7 µg kg –1 body weight per week. Based on this risk assessment<br />

of Cd, the Codex Alimentarius Commission will propose<br />

new criteria of Cd concentration in foods, especially in<br />

staple crops. The standard of Cd for rice has been discussed as<br />

being from 0.2 to 0.4 mg kg –1 the weight of polished rice.<br />

According to a survey of Cd contamination in rice by the Ministry<br />

of Agriculture, Forestry, and Fisheries (MAFF) of Japan,<br />

3.3% or 0.3% of rice cultivated in Japan exceeded a limit of<br />

0.2 mg kg –1 or 0.4 mg kg –1 , respectively. Although our diet is<br />

below the PTWI of Cd (4 µg kg –1 ), rice is the largest source of<br />

dietary intake of Cd for the Japanese people, so it is urgent to<br />

reduce the Cd concentration of rice. In this paper, current ameliorating<br />

techniques being applied in Cd-polluted paddy fields<br />

and promising techniques for reducing Cd contamination in<br />

rice are discussed.<br />

Session 12: Conservation of soil, water, and environment in rice cultures 381


Current techniques for reducing Cd contamination in rice<br />

Soil dressing<br />

In 1971, the Japanese government enforced the law that paddy<br />

fields that had produced brown rice beyond 1 mg kg –1 were<br />

subject to preventive measures against soil pollution such as<br />

soil dressing. T<strong>here</strong> are two types of soil dressing: (1) removing<br />

the Cd-polluted soil layer and replacing it with nonpolluted<br />

soils and (2) covering Cd-polluted soils with nonpolluted ones.<br />

According to a survey of rice Cd concentration after soil dressing<br />

by which the Cd-polluted soil layer with more than 25 cm<br />

was replaced, it did not exceed 0.03 mg kg –1 over more than<br />

20 years (Kuwana et al 2003). Thus, soil dressing is a permanent<br />

technique for reducing Cd contamination in rice, but an<br />

alternative approach is needed because of its enormous cost<br />

($300,000–500,000 per ha).<br />

Water management<br />

The solubility of Cd depends on the redox potential in the soil.<br />

Bioavailable Cd in the soil decreases to a great extent under<br />

submerged conditions because of the formation of less-soluble<br />

cadmium sulfide (CdS). Pot and field experiments conducted<br />

by many researchers showed that keeping a submerged condition<br />

for 3 weeks before and after heading time is a very useful<br />

method for reducing the Cd concentration of rice. Even with<br />

such conditions, however, rice grains are always exposed to<br />

the threat of Cd contamination because high levels of Cd still<br />

remain in the soil. Besides, the effect of submergence varies<br />

among years depending on weather conditions (e.g., rainfall).<br />

Application of soil amendments<br />

The application of alkaline amendments is one of the practicable<br />

methods for reducing the Cd concentration of rice. The<br />

combined use of calcium-silicate and fused magnesium phosphate<br />

for a basal dressing showed positive effects on suppressing<br />

Cd uptake by paddy rice (Takijima and Katsumi 1973).<br />

However, no effects or negative effects of alkaline amendments<br />

on Cd uptake in rice were also reported. Currently, the combination<br />

of water management and application of soil amendments<br />

for suppressing Cd contamination of rice is widely practiced<br />

in Cd-polluted paddy fields in Japan.<br />

Promising techniques for reducing Cd contamination in rice<br />

Phytoremediation<br />

Phytoremediation, which is the use of plant systems to<br />

remediate contaminated environments, has drawn attention as<br />

an environmentally friendly and cost-effective technique. The<br />

most important point for developing a successful<br />

phytoremediation (phytoextraction) technology in Cd-polluted<br />

soils is to select promising cleanup plants. Hyperaccumulator<br />

plants such as Thlaspi caerulescens (Brown et al 1994) and<br />

Brassica juncea (Salt et al 1995) have been exploited as ideal<br />

plants for phytoremediation because they possess several preferable<br />

characteristics for phytoremediation: the ability to take<br />

up and translocate an exceedingly large amount of Cd to their<br />

Table 1. Estimation of Cd removal from polluted<br />

soils using a high Cd-accumulating rice variety,<br />

Milyang 23.<br />

Item<br />

Amount<br />

Cd concentration of polluted soil 0.7 mg kg –1<br />

Average of Cd concentration 0.3 mg kg –1<br />

of nonpolluted soils<br />

Quantity of Cd to be removed per ha 400 g ha –1<br />

Cd concentration of shoots 15 mg kg –1<br />

Dry matter weight 800 kg ha –1<br />

Cd uptake by shoots 120 g ha –1<br />

Years for phytoremediation to 3–4 years<br />

be reached in nonpolluted soils<br />

shoots and hypertolerance of Cd. However, it is questionable<br />

whether hyperaccumulator plants are applicable for<br />

phytoremediation in Cd-polluted paddy fields in Japan. The<br />

primary reason is that appropriate agricultural practices such<br />

as planting, fertilization, water management, and mechanical<br />

harvesting are not well established for hyperaccumulator plants.<br />

In addition, the main targeted areas in Japan for<br />

phytoremediation have slight and moderate contamination of<br />

paddy fields, which might potentially produce paddy rice or<br />

upland crops contaminated with Cd. Under such lands, it is<br />

unknown whether hyperaccumulator plants can have an extraordinary<br />

ability for Cd uptake. Our research group found<br />

that some indica-japonica cross varieties cultivated under upland<br />

conditions accumulated a substantially high concentration<br />

of Cd in grains and shoots. When the shoot Cd concentration<br />

was compared between several rice varieties and B. juncea<br />

grown in two types of Cd-polluted soils, its concentration was<br />

2 to 4 times higher in rice varieties than in B. juncea. Moreover,<br />

Cd uptake in the shoots was approximately 6 times higher<br />

in rice varieties than in B. juncea. A remarkable decrease in<br />

Cd content in the rhizosp<strong>here</strong> was found after harvesting rice.<br />

T<strong>here</strong> are many merits for using rice as a cleanup plant, in<br />

addition to its superior ability of Cd uptake. First, the cultivation<br />

technique for rice is well established. Second, farmers<br />

can use their own machines to plant or harvest high Cd-accumulating<br />

rice varieties without any new investment. Third, they<br />

can plant a popular commercial variety immediately after ricebased<br />

phytoremediation.<br />

Based on the results of a pot experiment, estimation of<br />

Cd removal from a low-level polluted soil (0.7 mg kg –1 of 0.1<br />

M HCl extractable Cd in the soil) using Milyang 23, which is<br />

one of the high Cd-accumulating rice varieties and also a highyielding<br />

variety, is shown in Table 1. If the shoot biomass of<br />

Milyang 23 is estimated at 0.8 t ha –1 , the Cd concentration of<br />

the soil could be reached at close to 0.3 mg kg –1 , which is the<br />

average Cd concentration of nonpolluted soils, by successive<br />

planting for 3 to 4 years. A high removal efficiency of Cd by<br />

Milyang 23 was also confirmed by a field experiment, in which<br />

approximately 190 g ha –1 of Cd was removed from a paddy<br />

field polluted with 2.5 mg Cd kg –1 soil. These results suggest<br />

that high Cd-accumulating rice is an ideal plant for<br />

382 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Grain Cd concentration (mg kg –1 ) in upland conditions<br />

4.5<br />

4.0<br />

SL217<br />

3.5<br />

3.0<br />

2.5<br />

2.0<br />

1.5<br />

1.0<br />

SL218<br />

SL204<br />

SL205<br />

SL219<br />

SL225<br />

Kasalath<br />

SL238 SL212<br />

SL233<br />

SL202 SL230 SL232<br />

SL206<br />

SL239 SL235<br />

SL220 SL231SL234<br />

SL221<br />

SL214<br />

SL228<br />

SL213Koshihikari<br />

SL226 SL227<br />

SL222<br />

SL229<br />

SL203<br />

SL209<br />

SL224<br />

SL211<br />

SL236<br />

SL223<br />

SL207<br />

SL208<br />

SL215<br />

Y = 7.62x + 1.07<br />

R 2 = 0.129<br />

0.5<br />

0.0<br />

0.00 0.05 0.10 0.15 0.20<br />

Grain Cd concentration (mg kg –1 ) in paddy conditions<br />

Fig. 1. Cd concentration of grains in 39 chromosomal substitution lines carrying Kasalath (an<br />

indica rice variety) chromosomal segments in a Koshihikari (japonica) background. These<br />

lines were grown on Cd-polluted soils (1.8 mg Cd kg –1 soil) under upland and continuous<br />

paddy conditions. The concentration of Cd in grains was analyzed by inductively coupled plasmamass<br />

spectrometry after digesting with an acid mixture.<br />

phytoremediation of Cd-polluted paddy fields in Japan. For a<br />

successful decontamination by phytoremediation, it is imperative<br />

to establish postharvest technology for handling cleanup<br />

plants, which contain a large amount of Cd. One way is to<br />

incinerate the cleanup plants, turning them into ash, then recover<br />

the Cd from the ash. The other way is to use the plant<br />

biomass for a bio-energy such as bio-methanol after recovering<br />

the Cd. The National <strong>Institute</strong> for Agro-Environmental<br />

Sciences (NIAES) has organized a research consortium for a<br />

rice-based phytoremediation project.<br />

Introduction of low Cd-accumulating rice varieties<br />

Grain Cd concentration varies greatly among rice varieties<br />

(Arao and Ae 2003). This suggests the possibility of breeding<br />

varieties with less grain Cd concentration. In durum wheat,<br />

Clarke et al (1997) reported that the low grain Cd trait is highly<br />

heritable and is controlled by a single dominant gene. Recently,<br />

their work suggested that the Cd uptake locus resides on chromosome<br />

5B. A DNA marker, which was linked in repulsion<br />

with a low-Cd allele, has been developed for an efficient wheat<br />

breeding program. Although the genetic analysis of rice is much<br />

more developed than that of other crops, t<strong>here</strong> is no useful<br />

information on the low-Cd trait of rice. We tried to identify the<br />

quantitative trait loci (QTLs) controlling the Cd concentration<br />

of rice grain. Substitution lines (SLs) carrying Kasalath (an<br />

indica rice variety) chromosomal segments in a Koshihikari<br />

(japonica) background were used to identify the QTLs. A se-<br />

ries of SLs has covered the entire genome with overlapping<br />

introgressed segments of each line, and it is a powerful tool to<br />

simply detect the QTLs. The parents and 39 SLs were grown<br />

on Cd-polluted soils (1.8 mg Cd kg –1 soil) under upland or<br />

continuous paddy conditions. Figure 1 shows the Cd concentration<br />

of their grain. The average grain Cd concentration was<br />

20 times higher in upland conditions (1.67 mg kg –1 weight of<br />

brown rice) than in paddy conditions (0.08 mg kg –1 ). The grain<br />

Cd concentration in Koshihikari was significantly lower than<br />

that of Kasalath in both conditions. Although t<strong>here</strong> is no correlation<br />

between the grain Cd concentration in rice grown in<br />

paddy conditions and rice in upland conditions, several SLs<br />

(SL 207, SL 224, and SL 223) showed significantly lower grain<br />

Cd concentration than Koshihikari under both conditions.<br />

Based on graphical genotypes of SLs, the putative QTLs controlling<br />

low grain Cd were detected on chromosomes 3 and 8.<br />

As the detected SLs represent more than 90% of the Koshihikari<br />

genetic background, the development of a new Koshihikari<br />

with low grain Cd should be feasible in the near future.<br />

References<br />

Arao T, Ae N. 2003. Genotypic variations in cadmium levels of rice<br />

grain. Soil Sci. Plant Nutr. 49:473-479.<br />

Brown S, Chaney R, Angle J, Baker AJM. 1994. Phytoremediation<br />

potential of Thlaspi caerulescens and bladder campion for<br />

zinc- and cadmium-contaminated soil. J. Environ. Qual.<br />

23:1151-1157.<br />

Session 12: Conservation of soil, water, and environment in rice cultures 383


Clarke JM, Leisle D, Kopytko GL. 1997. Inheritance of cadmium<br />

concentration in five durum wheat crosses. Crop Sci. 37:1722-<br />

1726.<br />

Kuwana T, Aoyama Y, Tsudaka H, Yoshikura J, Adachi I. 2003. A<br />

survey of paddy field past to 20 years of soil dressing. Abstr.<br />

Annu. Meet. Jpn. Soc. Soil Sci. Plant Nutr. 41:288. (In Japanese.)<br />

Salt DE, Prince RC, Pickering IJ, Raskin I. 1995. Mechanisms of<br />

cadmium mobility and accumulation in Indian mustard. Plant<br />

Physiol. 109:1427-1433.<br />

Takijima Y, Katsumi F. 1973. Cadmium contamination of soils and<br />

rice plants caused by zinc mining. IV. Use of soil amendment<br />

materials for the control of Cd uptake by plants. Soil Sci. Plant<br />

Nutr. 19:235-244.<br />

Notes<br />

N uptake inhibition of the rice plant<br />

in flooded soils receiving wheat straw<br />

Fukuyo Tanaka<br />

Author’s address: National <strong>Institute</strong> for Agro-Environmental Sciences,<br />

3-1-3 Kannondai, Tsukuba, 305-8604, Japan, e-mail:<br />

isatoru@niaes.affrc.go.jp.<br />

The application of fresh plant residue, such as wheat straw,<br />

often inhibits the growth and N uptake of paddy rice (Oryza<br />

sativa L.) plants in the establishment phase. This inhibition is<br />

generally attributed to a deficiency of available N in soils with<br />

straw added because of considerable N assimilation by the soil<br />

microbes. This phenomenon is called biological N immobilization.<br />

In our previous study, however, we reported some cases<br />

in which much mineral N existed in paddy soils with added<br />

wheat straw, even though the growth of rice plants was delayed<br />

(Watanabe et al 1988). Here, N uptake activities of both<br />

rice plants and soil microbes were measured with 15 N tracing<br />

to validate that the widely accepted biological N immobilization<br />

theory was precisely the cause of rice growth inhibition<br />

by fresh wheat-straw application. Furthermore, the inhibitory<br />

substances were identified and their concentration determined<br />

in soil solutions under various conditions.<br />

Validation of the biological N immobilization theory<br />

To analyze the behavior of soil mineral N that existed at a<br />

given time, 15 N tracer experiments were conducted (Tanaka<br />

and Nishida 1996). <strong>Rice</strong> seedlings were transplanted into a<br />

pot with flooded soil, to which was applied wheat straw or no<br />

wheat straw. At 17 days after transplanting (DAT), tracer 15 N,<br />

15 NH 4 Cl solution, was added to the soil using a syringe. The<br />

soil and rice plants were sampled at 24 h after application of<br />

the tracer to avoid remineralization of the immobilized tracer<br />

15 N. The plants were divided into tops and roots. The N content<br />

and 15 N abundance were analyzed on plant and soil<br />

samples. The behavior of mineral N in the soil upon the application<br />

of the tracer can be estimated by using the ratio of distribution<br />

of 15 N in plants and soil.<br />

Figure 1A shows that the uptake of 15 N of rice in a plot<br />

receiving straw was about half of that in the control plot, even<br />

though the mineral 15 N was larger. In this experiment, the total<br />

weights of rice plants, N uptake, and N content in the straw<br />

plot were smaller than those in the control. A decrease in 15 N<br />

Distribution of tracer 15 N at 24 h after application<br />

Without straw<br />

With straw<br />

0 20 40 60 80 100<br />

Distribution (%)<br />

Nontracer N uptake of rice plants<br />

Without straw<br />

With straw<br />

Root Top Mineral N in soil<br />

0 10 20 30 40 50<br />

Nontracer N uptake (mg pot –1 )<br />

Tracer and nontracer mineral N in soil<br />

Without straw<br />

With straw<br />

Root<br />

Top<br />

0 20 40 60 80<br />

Mineral N soil (mg pot –1 )<br />

Nontracer<br />

Tracer<br />

Fig. 1. Distribution of tracer and nontracer N in the rice plant and<br />

soil. <strong>Rice</strong> plants and soils were sampled at 17 days after transplanting.<br />

Tracer N represents the behavior of mineral N at the<br />

application of tracer (A), nontracer N represents that which was<br />

derived from basal fertilizer and soil (B), tracer and nontracer mineral<br />

N in soil (C).<br />

A<br />

B<br />

C<br />

384 <strong>Rice</strong> is life: scientific perspectives for the 21st century


uptake per unit of dry matter was also found. These results<br />

indicate that the decrease in N uptake by rice plants was not<br />

associated with biological N immobilization but with the inhibition<br />

in N uptake. Furthermore, the tracer content of tops decreased<br />

by 51%, which corresponded to a decrease of only<br />

13% for roots. This suggests that the translocation of 15 N from<br />

roots to tops was also inhibited.<br />

However, nontracer mineral N (basal fertilizer and soil<br />

N) in the plot with straw applied was 83% of that in the control<br />

plot (Fig. 1C). Considering that nontracer N uptake by<br />

plants in the plot with straw application was 52% of that in the<br />

control (Fig. 1B), only a 17% decrease in mineral N in the plot<br />

with straw applied was not enough to explain the inhibition.<br />

This finding indicates that biological N immobilization was<br />

stimulated during the initial days and this might affect rice<br />

growth to some extent.<br />

Regarding the effects of 15 N tracer experiments on the<br />

behavior of N in flooded soil with wheat straw (Tanaka 2001),<br />

biological N immobilization was stimulated for the initial few<br />

DAT, although growth inhibition appeared during 10 to 20 DAT.<br />

In addition to this time mismatch between N immobilization<br />

and growth inhibition, the amount of mineral N in soil in the<br />

plot with straw applied was often larger than that in the control.<br />

Biological N immobilization in the presence of wheat<br />

straw may inhibit rice growth during the initial few DAT, but it<br />

may not be a main cause for growth inhibition. Presumably,<br />

inhibitors in the soil might cause this inhibition.<br />

<strong>Rice</strong>-growth-inhibitors formed in paddy soil<br />

It was suggested that N uptake inhibition was one of the main<br />

causes of a delay in growth of rice plants in the presence of<br />

straw in the early stage. Though various substances had been<br />

reported as growth inhibitors of rice plants, conclusive ones<br />

have not been found yet. To find growth inhibitors in flooded<br />

soils, some experiments were conducted.<br />

Soil solutions were collected from flooded soil receiving<br />

wheat straw (Tanaka et al 1990). The solutions were divided<br />

into acidic or basic fractions using diethyl ether extraction.<br />

As the acidic fraction showed an inhibitory effect on rice<br />

root elongation, the acids in the fraction were identified one<br />

by one with gas chromatograph-mass spectrometry and highperformance<br />

liquid chromatography. Aromatic acids such as<br />

benzoic acid (BA), phenylacetic acid (PA), 2-phenylpropanoic<br />

acid (2PPA), 3-phenylpropanoic acid (3PPA), 4-phenylbutyric<br />

acid (4PBA), and salicylic acid (SA) were detected (Tanaka et<br />

al 1990, Tanaka 2002). This was the first report that 2PPA and<br />

3PPA were detected from paddy field soils as a free form.<br />

The inhibitory activities of these aromatic acids on rice<br />

root elongation were assayed. Figure 2 shows that the aromatic<br />

acids have inhibitory effects on root elongation. Especially,<br />

2PPA showed the highest toxicity, which inhibited rice root<br />

elongation at a concentration of less than 0.5 µM. PA showed<br />

severe toxicity at a concentration higher than 40 µM. 3PPA<br />

Root elongation (%)<br />

120<br />

100<br />

80<br />

40<br />

2-phenylpropanoic acid<br />

20<br />

Phenylacetic acid<br />

3-phenylpropanoic acid<br />

Benzoic acid<br />

0<br />

0.1 1 10 100 1,000<br />

Concentration (mM)<br />

Fig. 2. Inhibition curve of the effect of aromatic acids on rice root<br />

elongation. Root elongation was compared with elongation of the<br />

control (100%). Twenty seedlings (root length was 5–7 mm) were<br />

used for each treatment.<br />

also inhibited root elongation at 30.7% of that in the control at<br />

40 µM.<br />

Inhibition of N uptake by the rice plant and N transport<br />

from roots to tops were also examined by hydroponics using<br />

tracer 15 N (Tanaka and Nishida 1998). The effects of BA (100,<br />

1,000 µM), 2PPA (1, 10 µM), and 3PPA (100, 1,000 µM) on<br />

N uptake activity were evaluated. Activity was defined as the<br />

ratio of 15 N uptake to plant N present before the treatments.<br />

All the treatments showed inhibition of 15 N uptake. The<br />

partitioning of 15 N to shoots, indicating the transport of 15 N<br />

from roots to shoots, was also inhibited by BA and 3PPA at<br />

1,000 µM. Though N transport inhibition by aromatic acids<br />

was reported for the first time in this paper, the toxic level was<br />

higher than that in soil solutions of paddy fields. It was rather<br />

unrealistic to consider that acids were the causative agents for<br />

the N transport inhibition caused by straw application. Further<br />

study on N transport inhibition in association with aromatic<br />

acid and other aqueous soil components is required.<br />

Behavior of aromatic acids in paddy fields<br />

The concentrations of aromatic acids in soil solution from<br />

paddy fields were determined during cropping periods. In 1989,<br />

the highest concentration was 59, 1, 11, and 12 µM for BA,<br />

PA, 2PPA, and 3PPA, respectively. 2PPA was over the critical<br />

level. Additionally, squeezes of small clusters of wheat straw<br />

sampled from paddy fields contained a high concentration of<br />

acids, for example, 122 and 194 µM for BA and 3PPA, respectively.<br />

This finding indicated that growth inhibition was<br />

not expressed uniformly over the field but was severe near the<br />

straws clusters.<br />

Further studies with field experiments showed that<br />

growth inhibition of the rice plant by the application of wheat<br />

straw was noticeable for the first 1–2 years after straw application<br />

and that it diminished gradually. The accumulation of<br />

aromatic acids also diminished over time. Some characteristics<br />

of the soil or field, such as poor water permeability, low-<br />

Session 12: Conservation of soil, water, and environment in rice cultures 385


air phase, and low temperature, were closely related to the<br />

increase in the accumulation of aromatic acids. These trends<br />

agreed with the trends in the appearance of growth inhibition<br />

of rice plants. Furthermore, it is noteworthy that the aromatic<br />

acids described <strong>here</strong> were not decomposition fragments derived<br />

from lignin of wheat straw but metabolites from soil<br />

microbes under anaerobic conditions.<br />

In conclusion, rice growth inhibition in the presence of<br />

wheat straw cannot be associated with biological N immobilization<br />

but with N uptake inhibition. Aromatic acids detected<br />

from soil solution with wheat straw inhibited rice root elongation<br />

and N uptake. Their concentration and accumulation patterns<br />

provide an important explanation for rice growth inhibition.<br />

References<br />

Tanaka F. 2001. Growth inhibition of rice (Oryza sativa L.) plants in<br />

flooded soils with added fresh wheat straw: the delicate interaction<br />

between rice plant and soil microorganisms.<br />

Nougyougijutu 56:506-510. (In Japanese.)<br />

Tanaka F. 2002. Formation of aromatic acids and growth inhibition<br />

of rice (Oryza sativa L.) plants in flooded soils with wheat<br />

straw added. Bull. Natl. Agric. Res. Cent. Kyushu Okinawa<br />

Reg. 40:33-78. (In Japanese.)<br />

Tanaka F, Nishida M. 1996. Inhibition of nitrogen uptake by rice<br />

after wheat straw application determined by tracer NH 4 + - 15 N.<br />

Soil Sci. Plant Nutr. 42:587-591.<br />

Tanaka F, Nishida M. 1998. Inhibitory effects of aromatic acids on<br />

nitrogen uptake and transport in rice (Oryza sativa L.) plants<br />

cultured on hydroponics. Soil Sci. Plant Nutr. 44:691-694.<br />

Tanaka F, Ono S, Hayasaka T. 1990. Identification and evaluation of<br />

toxicity of rice root elongation inhibitors in flooded soils with<br />

added wheat straw. Soil Sci. Plant Nutr. 36:97-103.<br />

Watanabe F, Ono S, Hayasaka T. 1988. Effect of wheat straw application<br />

on accumulation of organic acid in paddy soil and rice<br />

growth in early stage. Kyushu Agric. Res. 50:87. (In Japanese.)<br />

Notes<br />

Stable isotope ratios of hydrogen and oxygen<br />

in paddy water affected by evaporation<br />

Yohei Hamada, Shiho Yabusaki, Norio Tase, and Ichiro Taniyama<br />

Author’s address: National Agricultural <strong>Research</strong> Center, 3-1-1<br />

Kannondai, Tsukuba City, Ibaraki 305-8666, Japan, e-mail:<br />

fukuyot@affrc.go.jp.<br />

Evaporation and transpiration from a paddy field are very important<br />

for regional water balance, and t<strong>here</strong>fore irrigation<br />

management for rice cultivation, especially in monsoon Asia.<br />

Stomatal transpiration is accompanied by CO 2 uptake for photosynthesis<br />

and is essential for plant growth, w<strong>here</strong>as evaporative<br />

loss of ponded water would moderate diurnal variations<br />

of temperature and moisture around the paddy field. These<br />

two vapor fluxes into the atmosp<strong>here</strong> are often integrated and<br />

called evapotranspiration; nevertheless, they are essentially<br />

different processes. One of the reasons is the difficulty of determining<br />

these fluxes separately by micrometeorological methods<br />

such as eddy correlation, which has been widely used to<br />

directly measure evapotranspiration from various terrestrial<br />

ecosystems.<br />

As another approach, isotope hydrological techniques<br />

could divide evapotranspiration into evaporation and transpiration<br />

because only evaporation can affect the isotope composition<br />

of ponded water. For example, Simpson et al (1992)<br />

successfully calculated the proportion of evaporation occupied<br />

in total evapotranspiration using isotope analysis, at a<br />

rice paddy field located in the semiarid region of southeast<br />

Australia. In their study, the water balance of the paddy field<br />

was considerably simple: a small amount of rainfall less than<br />

10% of irrigation, no surface drainage, and a constant ponding<br />

depth. In the moist Asia region, in contrast, much rainfall oc-<br />

curs and traditional and complicated irrigation systems are<br />

widely developed. Such conditions may disturb the formation<br />

process of the isotope composition of paddy water, but few<br />

studies have been carried out to investigate the relationship<br />

between the isotope composition and evaporative loss and to<br />

confirm the possibility to separate evaporation and transpiration<br />

from a paddy field in the moist region. In this study, we<br />

investigated stable isotope ratios of paddy water samples and<br />

evaluated the effect of evaporation to examine the potential of<br />

the use of environmental isotope analysis.<br />

Methods<br />

Field observations were made in a rectangular lot of a paddy<br />

field (36°03′N, 140°01′E, 15 m above sea level; 100 m long<br />

and 54 m wide) located in Mase, Tsukuba, Japan. <strong>Rice</strong> is usually<br />

cultivated from May to August in the paddy field; the rest<br />

of year has no cultivation. We collected paddy water samples—<br />

irrigation water, drain water, and ponded water—three times<br />

during cultivation: in mid-May, early in June, and at the beginning<br />

of August in 2002. The ponded water samples were<br />

collected at six places distributed in the paddy field to detect<br />

isotopic change during surface water movement. Stable isotope<br />

ratios of hydrogen (δD) and oxygen (δ 18 O) of the paddy<br />

water samples were determined with a dual-inlet-type isotope<br />

386 <strong>Rice</strong> is life: scientific perspectives for the 21st century


atio mass spectrometer, MAT-252 (Finnigan MAT), equipped<br />

with an automatic equilibration system at the University of<br />

Tsukuba. The precisions of the isotope measurement are ±1‰<br />

and ±0.1‰ for δD and δ 18 O, respectively. Components of water<br />

balance of the paddy field—the amount of rainfall, irrigation,<br />

evapotranspiration, drainage, and infiltration, and the depth of<br />

ponded water—were also measured and recorded, as well as<br />

the parameters related to plant growth such as leaf area index<br />

(LAI).<br />

d 18 O ( )<br />

2<br />

0<br />

–2<br />

15 May<br />

7 June<br />

1-3 August<br />

Flow direction<br />

Results<br />

–4<br />

The change of δ 18 O along the flow direction of paddy water is<br />

shown in Figure 1. Ponded water samples collected at the six<br />

places are arranged consistent with the water movement in the<br />

paddy field (PW #1 to #6). As the paddy water flowed, the<br />

value of δ 18 O gradually increased. In May and June, the differences<br />

between irrigation water (IR) and drain water (DR)<br />

reached 6.1‰ and 5.3‰, respectively. In August, however,<br />

the increase in δ 18 O was little and the difference between IR<br />

and DR was only 0.6‰. The pattern of δD change along the<br />

flow direction was similar to that of δ 18 O.<br />

Figure 2 is a δ 18 O vs δD plot for the paddy water samples.<br />

A local meteoric water line (LMWL), which was determined<br />

from a long-term event-basis water collection by Yabusaki et<br />

al (2003) and indicates that the isotope composition of rainwater<br />

around the study area will be plotted along the line, is<br />

also shown. The paddy water samples were plotted almost linearly<br />

for each month. The result of linear regression analysis<br />

suggested good correlation between δ 18 O and δD (the correlation<br />

coefficients were larger than 0.98), and the slopes of the<br />

regression lines were 4.3, 4.3, and 5.8 for May, June, and August,<br />

respectively, showing smaller values than the slope of<br />

LMWL (7.4).<br />

–6<br />

–8<br />

IR<br />

PW #1<br />

PW #2<br />

PW #3<br />

Fig. 1. Change in δ 18 O of paddy water samples along the flow direction.<br />

IR = irrigation water, DR = drain water, PW = ponded<br />

water, and #n = the order of PW samples arranged along the water<br />

movement.<br />

PW #4<br />

PW #5<br />

PW #6<br />

d 18 O ( )<br />

–8 –6 –4 –2 0<br />

LMWL (dD = 7.4 d 18 O + 8.5)<br />

–20<br />

DR<br />

Discussion<br />

The results of the stable isotope analysis illustrated in Figures<br />

1 and 2 clearly indicate that the isotope composition of paddy<br />

water was intensively affected by evaporation, especially in<br />

May and June. When water vaporizes, water molecules that<br />

consist of lighter isotopes (H and 16 O) tend to become vapor<br />

more than those including heavier isotopes (D and/or 18 O).<br />

This causes isotope fractionation between liquid and vapor<br />

phases; t<strong>here</strong>fore, ponded water became more and more enriched<br />

isotopically as the water moved downstream under the<br />

influence of evaporation. In addition, the relationship between<br />

δ 18 O and δD of the water affected by evaporation is usually<br />

different from that of the water not affected. According to pioneering<br />

work by Craig (1961), most meteoric water samples<br />

collected all over the world were plotted linearly in the δ 18 O<br />

vs δD plot (the global meteoric water line, GMWL) and the<br />

slope of GMWL was 8. But the samples collected from lakes<br />

and rivers in East Africa, w<strong>here</strong> isotope compositions were<br />

strongly affected by evaporation, showed another linear relationship<br />

and the slope was about 5. This line is generally called<br />

15 May<br />

7 June<br />

1-3 August<br />

dD ( )<br />

–40<br />

–60<br />

Fig. 2. A δ 18 O vs δD plot for the paddy water samples. The local<br />

meteoric water line (LMWL) in Tsukuba after Yabusaki et al (2003)<br />

is also shown.<br />

an evaporation line (EL), and it results from the difference in<br />

isotope fractionation ratios ( 18 O/ 16 O vs D/H) between evaporation<br />

of surface water and condensation of meteoric water.<br />

The slopes of ELs obtained in the paddy field (4.3–5.8) are<br />

t<strong>here</strong>fore evidence of the influence of evaporation.<br />

Session 12: Conservation of soil, water, and environment in rice cultures 387


In August, the increase in δ 18 O was much smaller than<br />

in May and June, while the slope of EL was largest, although<br />

evapotranspiration determined by eddy correlation was relatively<br />

similar (3–5 mm day –1 for all months). Comparing the<br />

condition of plant growth in these months, the values of LAI<br />

in the paddy field were 0.05, 0.73, and 5.16 m 2 m –2 , respectively.<br />

The much larger LAI in August than in the other months<br />

implies that active transpiration and the depression of evaporative<br />

loss by the grown rice canopy would occur. Under such<br />

conditions, transpiration from the rice canopy must be predominant.<br />

By transpiration, indeed, isotope fractionation occurs<br />

between the water in a leaf and the transpired vapor, but<br />

the isotopically enriched leaf water is never brought back to<br />

the ponded water. Consequently, the isotope composition of<br />

paddy water in August changed little in contrast to May and<br />

June, when significant evaporation considerably advanced the<br />

isotopic enrichment.<br />

Conclusions and future studies<br />

As a result of this study, it was suggested that isotopic enrichment<br />

of paddy water is closely related to direct evaporation of<br />

ponded water, rather than the total evapotranspiration from<br />

the paddy field. This supports the possibility to separate evaporation<br />

and transpiration using the isotope hydrological approach,<br />

usually impossible by micrometeorological measurements.<br />

For more detailed and quantitative analysis, we conducted<br />

intensive field observations of water balance and the<br />

collection of water samples in the same paddy field during<br />

rice cultivation in 2004. Based on the data, we intend to examine<br />

the relationship among the isotope composition of paddy<br />

water, the components of water balance, and the stage of rice<br />

growth more precisely, and to construct an isotope hydrological<br />

model that can calculate the ratio of evaporation vs transpiration<br />

from a paddy field, considering the influences of rainfall<br />

and relatively complex irrigation management.<br />

References<br />

Craig H. 1961. Isotopic variations in meteoric waters. Science<br />

133:1702-1703.<br />

Simpson HJ, Herczeg AL, Meyer WS. 1992. Stable isotope ratios in<br />

irrigation water can estimate rice crop evaporation. Geophys.<br />

Res. Lett. 19:377-380.<br />

Yabusaki S, Tase N, Kihou N, Yuita K. 2003. Characteristics of oxygen<br />

isotopic ratios of soil water and groundwater at paddy,<br />

upland and grove fields in Tsukuba, Ibaraki Prefecture, Central<br />

Japan. J. Jpn. Assoc. Hydrol. Sci. 33:161-176. (In Japanese<br />

with English abstract.)<br />

Notes<br />

Erosion control by sawah in comparison<br />

to other land-use systems<br />

Fahmuddin Agus and Irawan<br />

Authors’addresses: Yohei Hamada, Terrestrial Environment <strong>Research</strong><br />

Center, University of Tsukuba, 1-1-1 Tennodai, Tsukuba, 305-<br />

8577 Japan; Shiho Yabusaki and Norio Tase, Graduate School<br />

of Life and Environmental Sciences, University of Tsukuba,<br />

1-1-1 Tennodai, Tsukuba 305-8572, Japan; Ichiro Taniyama,<br />

National <strong>Institute</strong> for Agro-Environmental Sciences, 3-1-3<br />

Kannondai, Tsukuba 305-8604, Japan, e-mail:<br />

hamada@suiri.tsukuba.ac.jp.<br />

Sawah, also known as a paddy field, has been sustainably producing<br />

rice, the staple food for most Indonesians, for hundreds<br />

or perhaps even thousands of years. Its other functions, especially<br />

in producing environmental services, are indispensable,<br />

yet have not been recognized or are ignored by most stakeholders.<br />

Sawah areas are characterized by high population density<br />

and perfectly flat plots. The sawah plot size is usually small,<br />

especially on sloping land. As such, sawah farming has low<br />

efficiency, resulting in low profitability. Low-incentive sawah<br />

farming results in accelerating conversion of sawah to nonagricultural<br />

uses.<br />

This study evaluated the environmental functions, especially<br />

soil loss and water-retaining capacity, of sawah relative<br />

to other land uses in Java in 2001. The results are important<br />

for advocating internalization of environmental services produced<br />

by sawah in national land-use-related policies, such that<br />

the existence of sawah with its multifunctionality can be maintained.<br />

Objective<br />

The objectives of this study were to assess soil loss and water<br />

retention capacity (as an indicator of flood mitigation function)<br />

of sawah relative to that of other land-use systems.<br />

Materials and methods<br />

Location<br />

Erosion from sawah was measured in Ungaran (07 o 20′S;<br />

110 o E), Central Java Province. The soil subgroup in the sawah<br />

area was classified as Typic Tropaquepts. A water retention<br />

study was conducted in the Upper Citarum Watershed<br />

(6 o 40′30″–7 o 15′00″S; 107 o 30′00″–107 o 55′00″E), West Java<br />

388 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Province. The dominant soil groups in the watershed are<br />

Eutrudepts, Dystrudepts, and Hapludalfs in uplands and<br />

Endoaquepts and Dystrudepts in lowlands (sawah).<br />

Erosion and sedimentation<br />

For sawah, soil loss was measured in two rice seasons from 18<br />

plots of terraced sawahs, ranging in area from 12 to 360 m 2 ,<br />

with a total area of 2,515 m 2 . The macro slope of these terraces<br />

is 22%. The average elevation difference between plots<br />

was 73 cm.<br />

V-notch weirs were installed at the outlets of selected<br />

plots to determine water level and discharge from the irrigation<br />

canal to the upper sawah plot, from one sawah to consecutive<br />

lower ones, and from the lowest sawah to the stream. Sediment<br />

concentrations were determined from water samples by<br />

the gravimetric technique.<br />

For the upland farming systems, sediment yield data were<br />

obtained from the literature.<br />

Water retention capacity<br />

Water retention capacity (WRC) is watershed capacity to absorb<br />

and hold (rain) water temporarily such that the portion of<br />

water does not flow as direct runoff (Nishio 1999). This includes<br />

water intercepted by plants’ canopy, ponded on soil surface,<br />

absorbed by soil pores, and additional water that could<br />

be stored by paddy fields and dams.<br />

Paddy fields surrounded by dikes temporarily store water<br />

at times of heavy rain, and discharge it gradually into downstream<br />

rivers and surrounding areas. In this way, they function<br />

as mini dams and thus hold water in the plots which would<br />

otherwise flow directly downstream, which might in turn contribute<br />

to flooding.<br />

Upland fields, on the other hand, store rainwater temporarily<br />

in the porous soil layer as well as intercept rainwater in<br />

the plant canopy. Some temporary ponding of water occurs on<br />

the soil surface because of its roughness.<br />

To understand the contribution of each land use, the WRC<br />

of each land use was assessed separately. For sawah, WRC<br />

was estimated by the difference between dike height (which is<br />

normally 12–15 cm) and normal water level (usually 0.05 m).<br />

For the upland systems, WRC was assessed by summing the<br />

canopy interception, soil surface ponding capacity, and soil pore<br />

absorption capacity, using the equation<br />

WRC = (TPS – FC)*AZ + PC + IC<br />

w<strong>here</strong> TPS is the percentage of total soil pore space, FC is the<br />

percentage of soil water content at field capacity, AZ is the<br />

depth of absorption zone or rooting zone, PC is surface ponding<br />

capacity, and IC is plant canopy interception capacity.<br />

Results<br />

Erosion and sedimentation<br />

Table 1 summarizes the measurement of sediment transport.<br />

The two-season data show that t<strong>here</strong> was a net sediment gain in<br />

Table 1. Amount of sediment entering and leaving 18 plots of terraced<br />

sawah.<br />

Variable<br />

First a<br />

<strong>Rice</strong> season<br />

Second b<br />

Total sediment entering sawah from 3.4 6.2<br />

irrigation canal (t ha –1 )<br />

Sediment yield from sawah (t ha –1 ) 1.4 0.8<br />

Sediment yield from sawah during 0.7 0.6<br />

tillage (t ha –1 )<br />

Net sediment deposition (t ha –1 ) 2.0 5.4<br />

a 31 Oct. 2001 to 31 Jan. 2002. b 16 Mar. 2002 to 1 July 2002.<br />

paddy fields as high as 2.0 t ha –1 in the first season and 5.4 t<br />

ha –1 in the second season. Sediment output from the plots is<br />

relatively high during the plowing and puddling periods but<br />

the sediment transported from one plot is mostly deposited in<br />

the next few lower plots and thus the net output of sediment at<br />

the end of the terraces is very low (about 2.2 t ha –1 y –1 during<br />

the two seasons). In comparison, sediment output was 10–20 t<br />

ha –1 y –1 from a 1.1-ha catchment planted to annual upland crops<br />

at a nearby location (Agus et al 2003). Similar research results<br />

in Indonesia (van Dijk 2002) suggested that sediment transported<br />

from rainforest and logged pine plantation forest is very<br />

low (3–7 t ha –1 y –1 ) compared to upland agricultural land uses,<br />

such as multistrata agriculture (10–12 t ha –1 y –1 ), annual cropbased<br />

agriculture on bench terraces (19–25 t ha –1 y –1 ), and<br />

vegetables on steep slopes with terraces (42–75 t ha –1 y –1 ).<br />

T<strong>here</strong>fore, it can be stated that the function of sawah in reducing<br />

soil erosion and sedimentation is more effective than, or at<br />

least is as effective as, forest.<br />

Water retention capacity<br />

The water retention capacity of different land uses at Citarum<br />

Watershed, West Java, is presented in Figure 1. The data show<br />

that forest and mixed cropping (tree-based multistrata system)<br />

in this study area had a WRC of about 0.15 and 0.09 m, respectively.<br />

Meanwhile, the WRC of paddy field, annual upland,<br />

and housing and industrial areas was 0.08, 0.06, and 0.02<br />

m, respectively. This means that during and shortly after heavy<br />

rain 1 ha of forest and sawah can store, respectively, about<br />

1,500 and 800 m 3 of water before runoff takes place. The capacity<br />

of sawah to retain water is much higher than that of<br />

annual upland and housing and industrial areas of 600 and 200<br />

m 3 ha –1 . T<strong>here</strong>fore, it can be stated that, if more sawah and<br />

upland agricultural lands are converted to housing and industrial<br />

development, the same amount of rainfall will cause greater<br />

runoff, and will finally cause a higher chance of flood.<br />

Similar research in Japan showed that the average WRC<br />

for forest, sawah, orchard, grassland, and dry cropland was<br />

0.18, 0.15, 0.11, 0.02, and 0.04 m, respectively (Nishio 1999).<br />

Session 12: Conservation of soil, water, and environment in rice cultures 389


WRC (m)<br />

0.16<br />

0.14<br />

0.12<br />

0.10<br />

0.08<br />

0.06<br />

0.04<br />

0.02<br />

0.00<br />

Fig. 1. Water retention capacity (WRC) of sawah and other landuse<br />

systems.<br />

Conclusions<br />

Forest Sawah Mixed<br />

cropping<br />

Annual<br />

upland<br />

Interception capacity<br />

Ponding capacity<br />

Pore absorption<br />

Housing<br />

Industry<br />

Sawah is superior in controlling erosion to other land uses.<br />

Erosion mainly happens in sawah during and shortly after tillage<br />

operations.<br />

The capacity of sawah to retain water during and shortly<br />

after rainfall is comparable with that of the tree-based mixed<br />

cropping system and significantly higher than that of annual<br />

crop-based and housing and industrial areas. Policy measures<br />

should be implemented to maintain the existence of sawah considering<br />

the significant environmental services it can offer, in<br />

addition to its tangible role as a rice producer.<br />

References<br />

Agus F, Vadari T, Watung RL, Sukristiyonubowo, Valentin C. 2003.<br />

Effects of land use and management systems on water and<br />

sediment yield: evaluation from several micro catchments in<br />

Southeast Asia. In: Maglinao AR, Valentin C, Penning de Vries<br />

F, editors. Proceedings of IWMI-ADB Project Annual Meeting<br />

and 7th MSEC Assembly, Vientiane, Lao PDR, 2-7 Dec.<br />

2002. Bangkok (Thailand): <strong>International</strong> Water Management<br />

<strong>Institute</strong>, Southeast Asia Regional Office. p 135-149.<br />

Nishio M. 1999. Multifunction character of paddy farming. Paper<br />

presented at the Second Group Meeting on the Interchange of<br />

Agricultural Technology Information between ASEAN Member<br />

Countries and Japan, Jakarta, Indonesia, 16-18 February<br />

1999.<br />

van Dijk AJM. 2002. Water and sediment dynamics in bench-terraced<br />

agricultural steeplands in West Java, Indonesia. PhD<br />

dissertation. Vrij University, Netherlands. 363 p.<br />

Notes<br />

Authors’ address: Soil <strong>Research</strong> <strong>Institute</strong>, Jln. Juanda 98, Bogor<br />

16123, Indonesia, e-mail: f.agus@cgiar.org.<br />

Wrap-up of Session 12<br />

Although it is recognized that the cultivation of paddy rice sustains<br />

soil fertility, t<strong>here</strong> is a large area whose fertility of soil is still<br />

low. T<strong>here</strong>fore, it is necessary to increase both the sustainability<br />

and productivity of these soils urgently. One of the main themes<br />

of the conference is “the development of sustainable rice cultivation<br />

based on environment and food security.” In this session,<br />

this theme was discussed from the viewpoint of soil and water<br />

conservation.<br />

Participants entered into “the world of paddy soils” with<br />

the presentation of Prof. K. Kyuma (Japan). His keynote lecture<br />

was “Paddy soils around the world.” Based on his more than 40<br />

years’ experience in the field of paddy soil science, he emphasized<br />

the importance of diversity of paddy soil and its environment.<br />

Diversity and sustainability of paddy soils were discussed<br />

by N. Ngoc Hung (Vietnam), K. Naklang (Thailand), and T.<br />

Wakatsuki (Japan). N. Ngoc Hung reported on the current status<br />

of soil fertility in the Mekong Delta of Vietnam. He pointed out<br />

some problems in fertility such as nitrogen (N) loss through ammonium<br />

volatilization. In contrast to the relatively fertile Mekong<br />

Delta, the paddy soils in northeastern Thailand are very infertile.<br />

K. Naklang introduced her long-term field trials, and discussed<br />

the effect of organic matter application on the improvement of<br />

soil fertility. T. Wakatsuki reported that the area with lowland rice<br />

farming has increased in West Africa. He predicted that a Green<br />

Revolution with paddy rice farming would take place in this area<br />

with the proper integration of forestry, upland farming, and lowland<br />

rice farming.<br />

To optimize fertilizer management in such diverse paddy<br />

soils, C. Witt (Singapore) proposed an effective and site-specific<br />

management of nutrients on the basis of his field trials with fertilizer<br />

application.<br />

Recently in China, rice yield has increased dramatically with<br />

the increase in fertilizer application. However, the amount of application<br />

for rice exceeds the requirement. As a result of this<br />

imbalance, N pollution is becoming a serious environmental problem.<br />

J. Zhu (China) evaluated the environmental impact of N loss<br />

under the wheat-rice system in the region around Taihu Lake. To<br />

solve this problem, it is necessary to increase the recovery of N<br />

from fertilizer urgently. M. Saigusa (Japan) reported that the application<br />

of polyolefin-coated urea, which was used as a controlled-availability<br />

fertilizer (CAF), improved N recovery. The invention<br />

of CAF now enables a co-situs application (contact application<br />

of fertilizer with plant roots) and that is improving the efficiency<br />

of fertilizer, environmental loading from fertilizer, and so<br />

on. W. Bowen (Bangladesh) also reported a good recovery of N<br />

from fertilizer with the deep placement of supergranule urea for<br />

lowland rice in Bangladesh.<br />

D. Olk (USA) indicated that the yield decline caused by<br />

intensive rice cropping under continuously flooded conditions was<br />

390 <strong>Rice</strong> is life: scientific perspectives for the 21st century


associated partly with the decrease in soil N availability. He suggested<br />

that phenolic compounds from lignin residues in soil absorbed<br />

soil organic N, and that this binding was related to the<br />

decrease in mineralization of soil N late in the season. He emphasized<br />

that this anilide structure was recalcitrant and might<br />

release N to the rice plant only very slowly or upon field drainage<br />

and soil aeration. H. Sumida (Japan) and D.B. Lee (Korea) reported<br />

that N fertility of the soil was often exhausted when paddy<br />

soils were converted into upland crops in their countries. They<br />

reported a decrease in soil N availability under continuous upland<br />

conditions. The appropriate application of organic matter or<br />

re-conversion of rotated paddy fields into flooded rice was necessary<br />

to maintain fertility in flooded rice–upland crop rotation<br />

systems.<br />

<strong>Rice</strong> is one of the greatest sources of dietary intake of<br />

cadmium (Cd) in some Asian countries. The amounts of Cd in<br />

rice grain sometimes exceeded the critical level that was proposed<br />

by Codex. T<strong>here</strong>fore, it is urgently required to develop technologies<br />

for reducing Cd levels in rice grain. S. Ishikawa (Japan)<br />

showed current advances in ameliorating technologies to reduce<br />

Cd content in polluted fields and promising technologies for<br />

remediating Cd-polluted soils.<br />

The general discussion covered the diversity of paddy soils,<br />

maintenance of soil fertility, and conservation of environments.<br />

Based on the diverse paddy rice farming in Asia, West Africa, and<br />

other regions, it was important to recognize that ecological engineering<br />

improved the artificial environment of paddy soil as a<br />

whole. D. Olk focused on soil aeration in terms of the decrease<br />

in available N under continuous flooded conditions. To avoid<br />

changing available N into recalcitrant forms, how much soil aeration<br />

is necessary Rotation with upland crops is one method for<br />

aeration, and its frequency may be mainly a matter of economics;<br />

t<strong>here</strong>fore, the relative profits for rice versus an upland crop<br />

should be calculated. Also, the presence of another decline in<br />

soil fertility by the paddy-upland rotation should be taken into<br />

account. Future research should examine the effects of soil aeration<br />

on the quality of organic matter as well as N availability.<br />

However, many other potential effects of timely soil aeration also<br />

deserve study.<br />

In conclusion, this session provided an excellent opportunity<br />

to facilitate the science of paddy soil among participants,<br />

and it shall contribute to improving our future.<br />

Session 12: Conservation of soil, water, and environment in rice cultures 391


SESSION 13<br />

Farmers’ participatory approaches<br />

to facilitate adoption of improved technology<br />

CONVENER: T. Paris (<strong>IRRI</strong>)<br />

CO-CONVENER: J.S. Caldwell (JIRCAS)


How does a farmer accept a new technology<br />

Fujihiko Tozawa<br />

Ogata village, located in Akita Prefecture in northern Japan,<br />

was built on the reclamation of Hachirogata Lake, formerly<br />

the second-largest lake in Japan, during 1957-77. This was the<br />

biggest agricultural land reclamation in Japanese history. The<br />

new reclaimed land had an area of about 15,600 ha, with residual<br />

canals and lakes of about 5,000 ha. When the project<br />

was completed in 1977, Ogata was expected to be a “model of<br />

modern agriculture,” based on large-scale and productive farming<br />

systems. Some 589 farmers were settled in Ogata from all<br />

over the country. Each of them had a farm of 15 ha, regarded<br />

as large-scale in Japan, w<strong>here</strong> the average farm size is about 1<br />

ha.<br />

Like other farmers of Ogata village, I am a full-time and<br />

large-scale rice farmer. In 1998, I established a company with<br />

some friends to sell our rice. As full-time farmers, we are always<br />

interested in technological innovations in farming and<br />

farm management because we always want to reduce costs and<br />

sell our rice under better conditions. Unlike other Japanese<br />

farmers, the majority of farmers of Ogata do not sell their rice<br />

to agricultural cooperatives, but we have multiple marketing<br />

channels. For instance, we can sell rice by individual direct<br />

marketing, or group direct marketing, or to rice wholesalers. It<br />

is common <strong>here</strong> that a single farmer has different sales channels<br />

and grows rice in different ways on his farm to respond to<br />

his different consumers. Farmers of Ogata are all independent<br />

farm owners who must decide what kind of rice they will grow,<br />

to whom they will sell, and how much. T<strong>here</strong>fore, it takes us a<br />

long time to consider whether we should accept a new technology<br />

because we should examine whether the new technology<br />

is compatible with other factors of our farm management.<br />

As for environmental problems, we have been suffering<br />

from a specific one: worsening of the water quality of the residual<br />

lake of the commonly called Hachiroko Lake, whose<br />

water quality (measured by COD) was listed as one of the worst<br />

five lakes in the country in 2001. Ogata farmers are respon-<br />

sible for the water quality deterioration of Hachiroko Lake<br />

because we use its water for agricultural irrigation and drainage.<br />

During the 40-year history of Ogata, we have been struggling<br />

to improve the water quality of Hachiroko Lake by stopping<br />

the sale of synthetic detergents in a store of the agricultural<br />

cooperative, banning pesticide spraying by airplanes, stopping<br />

the project of a golf resort planned within the village,<br />

developing various kinds of sustainable agricultural technologies<br />

from organic to no-till, etc. These efforts were partial and<br />

fragmentary at first, but they were expanded to the whole community<br />

and became systematic in the 1990s, when researchers<br />

of Akita Prefectural University and the Akita Agricultural Experimental<br />

Station started joining farmers to help them develop<br />

new technologies and social systems for sustainable farming<br />

on the reclaimed land. A series of collaborating programs between<br />

farmers and researchers began at that time, including<br />

Ogata Low-Input Sustainable Agriculture (O-LISA 1991), the<br />

<strong>Research</strong> Project for Sustainable Agriculture in Ogata (RPSAO<br />

1998), and the Declaration of Environmentally Creative Agriculture<br />

in Ogata (ECA 2001). In 2001, we established a voluntary<br />

organization to promote ECA, and I have been president<br />

of this organization.<br />

The above research has revealed that Ogata is the largest<br />

single area of sustainable rice production in Japan. Table 1<br />

shows examples of sustainable farming practices in Ogata.<br />

From the top, we see that the area of “Less chemical farming”<br />

is 5,110 ha and accounts for 74.1% of the total farmland of the<br />

village. “No chemical farming” (not the same as “organic”) is<br />

520.8 ha and the percentage of the total farmland is 7.5%.<br />

These lower input practices already cover 80% of the total<br />

farmland of the village, w<strong>here</strong>as conventional farming covers<br />

20%. As you can imagine, these figures are extraordinarily<br />

high in Japan in terms of total area, area per capita, and percentage<br />

of total farmland. We are also active in accepting “more<br />

friendly practices with Hachiroko,” namely, the “use of con-<br />

Table 1. Various sustainable farming practices in Ogata (1998).<br />

Area Number of Area per % of area in<br />

Farming practice (ha, a) farmers (b) capita the total farmland<br />

(ha, a/b) of Ogata<br />

Less chemical farming 5,110.0 – – 74.1<br />

No chemical farming 520.8 110 4.7 7.5<br />

Use of controlled-availability fertilizer 1,214.7 112 10.8 17.6<br />

Local fertilization 1,052.3 84 12.5 15.3<br />

No-puddling 132.7 14 9.5 1.9<br />

No-till 36.8 10 3.7 0.5<br />

Direct seeding 7.2 2 3.6 0.1<br />

Weeding with ducks 71.5 12 5.9 1.0<br />

Source: Taniguchi and Sato (2001).<br />

394 <strong>Rice</strong> is life: scientific perspectives for the 21st century


trolled-availability fertilizer,” “local fertilization,” “no-puddling,”<br />

“no-till,” “direct seeding,” and “weeding with ducks.”<br />

Now I return to the theme of this paper: how a farmer of<br />

Ogata accepts a new sustainable technology. To answer this<br />

question, I would like to compare organic farming and no-till<br />

farming. These two practices are useful when we investigate<br />

what makes a farmer accept a new technology. It is said that<br />

the first farmer who challenged organic farming in Ogata was<br />

Mr. Tsuneo Gotsu in 1982. As organic farming technologies<br />

were not developed at that time, he had to employ women living<br />

in neighboring communities to weed rice paddies by hand.<br />

His neighbors thought that he had become crazy because it<br />

was unthinkable not to use herbicide in such large-scale paddies<br />

as Ogata’s. These efforts were basically “ethical,” that is,<br />

based on goodwill for a better environment. But, in the 1990s,<br />

sustainable farming practices spread rapidly to the whole community,<br />

mainly because consumers’ increasing concern about<br />

food safety caused a sharp expansion of “safe food markets”<br />

all over the country. A lot of offers came from wholesalers and<br />

retailers. Many farmers of Ogata began growing rice in an organic<br />

or less chemical manner, not based on ethical intentions<br />

but on commercial interests. T<strong>here</strong> were many technical difficulties<br />

with organic farming: providing organic fertilizer; seedling,<br />

weeding, disease, and insect control; and others. But farmers<br />

tried to solve these problems in various ways. Establishing<br />

a study group and experimenting with new technologies with<br />

other farmers are the most common ways of solving problems.<br />

Sometimes we invite diverse researchers to study new technologies<br />

or new materials, and we try them within our own<br />

paddy fields. It takes time to decide whether we accept a new<br />

technology or material because we need to see whether it actually<br />

works in the particular conditions of our own fields. With<br />

efforts for years, the major difficulties of organic farming were<br />

solved, but weeding is still very difficult. What has moved<br />

farmers forward in technological innovation in organic farming<br />

is, in my view, the economic incentive. How much farmers<br />

receive for growing rice organically varies. This depends on<br />

what kinds of customers they have. If they find wealthy consumers,<br />

they could receive double the standard price of rice,<br />

or more. So, information about customers is the “top secret”<br />

for farmers of Ogata. It sometimes happens that one Ogata<br />

farmer tries to take a customer from another farmer.<br />

On the other hand, no-till is not popular in our village<br />

mostly because we have to use chemical fertilizer and herbicide<br />

for no-till farming, so that we cannot expect a higher price<br />

in the current rice market, w<strong>here</strong> the use of organic fertilizer<br />

and nonuse of chemicals are highly valued. Though we know<br />

that no-till is very effective in making water cleaner, only ten<br />

farmers among more than 500 are now practicing no-till. The<br />

great popularity of organic farming in Ogata, in contrast, has<br />

caused concern from researchers about water pollution caused<br />

by overusing organic fertilizer. Many organic farmers are aware<br />

of this problem but probably they would not change their farming<br />

style until a time when someone shows them an alternative<br />

that could provide profitability and sustainability compatible<br />

on a higher level.<br />

Reference<br />

Taniguchi Y, Sato S. 2001. An attempt of farmer-university collaboration<br />

in research on sustainable farming practices. Nogyo<br />

Oyobi Engei (Agric. and Hort.) 76-3:338. (In Japanese.)<br />

Notes<br />

Author’s address: Hanasaka Farm, 010-0442, Higashi 4-47-1, Ogata,<br />

Akita, Japan, e-mail: fugihiko@ogata.or.jp.<br />

Farmer participatory evaluation of nitrogen<br />

management technology: the case<br />

of the leaf color chart in West Bengal, India<br />

B. Bagchi, M.Z. Abedin, and S.K.T. Nasar<br />

West Bengal, the largest rice-growing state in India, has made<br />

respectable progress in rice production over the last two decades.<br />

<strong>Rice</strong> production increased from 11.2 million tons in<br />

1980-81 to 20.9 million t in 2001-02, mostly because of technological<br />

progress that raised yield from 2.16 to 3.39 t ha –1 .<br />

But the price of rice has increased at a much slower rate than<br />

the unit cost of cultivation, showing the strains of diminishing<br />

returns to farmers. One way to increase the profitability of rice<br />

cultivation is to reduce the unit cost by adopting efficient crop<br />

management technologies that can save modern inputs.<br />

Since the introduction of high-yielding varieties, farmers<br />

have been applying more fertilizer than the recommended<br />

dose. This reduces the agronomic and economic efficiency of<br />

N fertilizer and has negative consequences for the environment.<br />

The <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong> (<strong>IRRI</strong>), through<br />

experiments on soil-plant development analysis, developed a<br />

simple decision-making tool called the leaf color chart (LCC)<br />

for the timely application of N fertilizer to the rice crop. The<br />

color shades of the LCC card are designed to match leaf colors<br />

of the rice plant from signs of nitrogen “hunger” to overfeeding<br />

of the plant. By matching the color on the LCC with<br />

Session 13: Farmers’ participatory approaches to facilitate adoption of improved technology 395


that of the rice plants, farmers can decide on the proper time<br />

and amount of N application. LCC validation experiments in<br />

Vietnam and other countries have shown that farmers could<br />

save a substantial amount of nitrogen without any reduction in<br />

yield (Balasubramanian et al 2000, Bijay Singh et al 2002).<br />

To validate the technology with farmers, social scientists<br />

emphasized conducting farmer participatory research that<br />

would help farmers assess not only the suitability of the technology<br />

to the farmers’ biophysical and agronomic environment,<br />

but also its acceptability to farmers given their socioeconomic<br />

environment and cultural background. Once the farming community<br />

sees the benefit of the technology through its own experimentation,<br />

demand is expected to grow and the process of<br />

adoption would become faster. Community participatory,<br />

farmer-managed trials were t<strong>here</strong>fore conducted by farmers in<br />

West Bengal, India, during 2002-04 to validate the efficiency<br />

of the LCC in managing nitrogen in rice cultivation.<br />

The overall objectives were (1) to enable farmers to<br />

evaluate the effectiveness of the LCC in N management and<br />

(2) to assess the economic and other benefits associated with<br />

the use of the LCC. Specific objectives were to observe the<br />

effectiveness of a community participatory approach in technology<br />

assessment and its adoption. This paper reports the results<br />

of experiments in the dry season of 2002-03 and transplanted<br />

rice premonsoon and monsoon seasons in 2003 in West<br />

Bengal, India, by Bidhan Chandra Krishi Viswavidyalaya,<br />

<strong>IRRI</strong>, and a local NGO.<br />

Materials and methods<br />

Out of six agroclimatic zones of West Bengal, two zones, the<br />

new alluvial and old alluvial, were chosen for the dry season.<br />

Initially, six villages from six districts of the two zones were<br />

randomly selected for the study. As it was thought to be difficult<br />

to monitor intensively and interact closely with the farmers,<br />

a cluster of four neighboring villages in the premonsoon<br />

season and five villages in the monsoon season was identified<br />

purposively, during the subsequent seasons, based on representativeness<br />

of the flood-prone rice environment and the target<br />

group, and ease of monitoring and supervision. To do the<br />

work smoothly, partnership with a local NGO, the Nadia Zilla<br />

Farmers’ Development Organization, was established. Participating<br />

farmers were selected using a community participatory<br />

approach. Meetings were organized in each village to discuss<br />

the LCC and its role in the judicious use of nitrogen in rice<br />

cultivation. Farmers from each village selected 10 representatives<br />

from the willing farmers in the dry season. Farmers were<br />

informed of technical details for using the LCC. Since validation<br />

should be under farmers’ management conditions, they<br />

were informed that no material and financial inputs would be<br />

given to the participants so that their decision-making would<br />

not be affected or distorted. To establish an ongoing monitoring<br />

system at the community level, small groups of farmers<br />

were formed to share each LCC. Measurements were taken<br />

using the LCC matching the color of 10 uppermost fully expanded<br />

leaves from randomly selected plants per plot from<br />

the 14th day after transplanting (DAT) at 7-day intervals until<br />

flowering. For the pre-wet-season and wet-season crop, the<br />

critical value was 3.5, and for the dry-season crop it was 4.<br />

Yield was estimated through the crop-cutting method.<br />

Field days were organized before harvesting, enabling farmers<br />

to evaluate the technology. During field days, the farmers<br />

discussed among themselves and evaluated the performance<br />

by ranking the efficacy of the LCC using their own criteria.<br />

Results and discussion<br />

Farmers’ general perceptions were that the greener were the<br />

leaves, the higher yield would be. However, after testing, the<br />

participating farmers were of the opinion that, by using the<br />

LCC, the amount of nitrogenous fertilizer applied was reduced<br />

without affecting production. This saved farmers money and<br />

helped increase net returns. Nitrogen use decreased by 20.2,<br />

30.2, and 36.0 kg ha –1 over the farmers’ traditional practice in<br />

the pre-wet-, wet-, and dry-season rice crops, respectively.<br />

Participating farmers thus saved a substantial amount as fertilizer<br />

cost is an important part of direct costs.<br />

Farmers found out from their observations and from trials<br />

designed and conducted by some of them that using the<br />

LCC could significantly reduce the use of pesticides, too. They<br />

were of the opinion that higher doses of N fertilizer were responsible<br />

for increased pest and disease infestation.<br />

The real-time use of nitrogen affected the cost of cultivation<br />

and net returns of rice in different seasons. Farmers<br />

earned more profit per hectare in the LCC plots than in the<br />

farmers’ own plots. These amounts were more in LCC plots<br />

than in farmers’ plots by US$13.10 in pre-wet rice, $20.40 in<br />

wet rice, and $19.40 in dry rice (Table 1).<br />

During the field days, participating and nonparticipating<br />

farmers evaluated the performance of LCC technology.<br />

They found out that, in the LCC plots, the number of unfilled<br />

grains was lower than in farmer-managed plots and plants of<br />

LCC plots did not lodge despite strong winds, w<strong>here</strong>as plants<br />

in the farmers’ plots lodged. Some of the varieties also matured<br />

earlier by about 5 to 7 days when N was managed by the<br />

LCC than in farmers’ plots.<br />

These positive effects have significantly changed the perception<br />

of farmers that very dark green leaves are associated<br />

with higher grain yield. They now understand that N should be<br />

applied when the plant starts feeling “hungry” for nitrogen.<br />

The farmers’ rankings showed that the reduction in N<br />

use was most important and reduction in lodging was the least.<br />

The rankings were more or less uniform across communities,<br />

suggesting that farmers were equally concerned about the overuse<br />

of N. Influenced by the success of the LCC experiments,<br />

the number of participating farmers tripled by the third season.<br />

The rate of adoption has increased each season and t<strong>here</strong><br />

have been no reports of discontinuation of LCC use.<br />

The LCC technology was found to be eco-friendly. The<br />

reduction in N use has potential to reduce NO 3 pollution and<br />

minimize the use of pesticides, which would have a beneficial<br />

effect on human health, biodiversity, and soil and water qual-<br />

396 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. Cost of cultivation and profit of rice cultivation in the leaf color chart (LCC) plot and farmers’ practice<br />

(FP) in different seasons of West Bengal.<br />

Cost a ha –1 Difference in Gross return ha –1 Profit ha –1 Difference<br />

Season cost ha –1 in<br />

LCC FP LCC FP LCC FP profit ha –1<br />

Early wet season 254.90 263.80 8.90 332.60 328.40 77.70 64.60 13.10<br />

Wet season 328.20 343.10 14.90 413.40 407.80 85.20 64.80 20.40<br />

Dry season 421.50 445.30 23.80 591.40 595.80 169.90 150.50 19.40<br />

a Values are in US$.<br />

ity. The participating farmers believed that this simple tool<br />

empowers them to make decisions on the time and amount of<br />

N to be applied.<br />

It was thought that the community participatory approach<br />

used strengthened the partnership among key stakeholders,<br />

which facilitated community action and technology adoption.<br />

The farmers believed that more and more frequent interaction<br />

with the scientists and stakeholders would help enhance their<br />

knowledge of improved farming practices. It appeared that an<br />

action group has been formed in this locality. The farmers of<br />

this group were very close to each other. Evidence from the<br />

participatory approach used showed that farmer-to-farmer<br />

transfer of technology was taking place, and the technology is<br />

likely to be adopted by the large group of farmers. This experiment<br />

also had an impact on the scientific community. The<br />

scientists who visited the experimental plots appreciated the<br />

capabilities of farmers in testing new technologies under their<br />

own management.<br />

Conclusions<br />

Real-time management of nitrogen with the LCC helped farmers<br />

minimize N use, reduce the cost of cultivation, decrease<br />

pest and disease incidence, minimize chaffy grains, and protect<br />

the crop from lodging. Farmers’ perceptions that the use<br />

of more nitrogenous fertilizer brings more yield changed.<br />

Community action in technology testing facilitated better<br />

and faster decision-making for N management. Small groups<br />

established to share each LCC facilitated such evaluation. Frequent<br />

interaction with the scientists and within the farming<br />

community improved the knowledge base of the farmers. This<br />

helped to strengthen the social capital. However, the trial confirmed<br />

that a varietal interaction does exist and the communities<br />

should be encouraged to evaluate this in partnership with<br />

researchers.<br />

References<br />

Balasubramaniam V, Morales AC, Cruz RT, Thingarajan TM,<br />

Nagarajan R, Babu M, Abulrachman S, Hai LH. 2000. Adoption<br />

of the chlorophyll meter (SPAD) technology for real-time<br />

nitrogen management in rice: a review. Int. <strong>Rice</strong> Res. Notes<br />

25(1):4-8.<br />

Bijay Singh et al. 2002. Chlorophyll meter- and leaf color chartbased<br />

nitrogen management for rice and wheat in northwestern<br />

India. Agron. J. 94.<br />

Notes<br />

Authors’ addresses: B. Bagchi and S.K.T. Nasar, Directorate of <strong>Research</strong>,<br />

Bidhan Chandra Krishi Viswavidyalaya, Nadia, West<br />

Bengal, India; M.Z. Abedin, <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>,<br />

Los Baños, Philippines, e-mail: drbbagchi@vsnl.net.<br />

A farmer participatory approach in the adaptation<br />

and adoption of controlled irrigation for saving water:<br />

a case study in Canarem, Victoria, Tarlac, Philippines<br />

F.G. Palis, M. Hossain, B.A.M. Bouman, P.A.A. Cenas, R.M. Lampayan, A.T. Lactaoen, T.M. Norte, V.R. Vicmudo, and G.T. Castillo<br />

Water plays a major role in rice cultivation. On average, some<br />

4,000 L of water are required to produce 1 kg of rice (Tuong<br />

and Bouman 2003). Thus, an inadequate supply of water from<br />

crop establishment to the reproductive stage of the crop generally<br />

leads to a significant yield reduction (Wopereis et al<br />

1996, Bouman and Tuong 2001).<br />

The water supply is increasingly becoming scarce, however,<br />

because of the world’s increasing population that brings<br />

along multiple competing demands, such as for agriculture,<br />

industry, and domestic use, and climatic changes such as El<br />

Niño phenomenon (<strong>IRRI</strong> 1995, Bouman and Tuong, 2001).<br />

The increasing water scarcity threatens not only general food<br />

security in Asia but also the livelihood of most Asian farmers<br />

Session 13: Farmers’ participatory approaches to facilitate adoption of improved technology 397


ecause of the increasing irrigation costs borne by them. To<br />

meet the food demand of Asian consumers and producers, efficient<br />

water management practices are needed that maintain<br />

rice yields and production at a high level.<br />

To solve the problem of water scarcity, researchers have<br />

been developing water-saving irrigation technologies. In the<br />

Philippines and in 2001, <strong>IRRI</strong> began the project “Technology<br />

Transfer for Water Savings” (TTWS) in collaboration with the<br />

National Irrigation Administration (NIA) and Philippine <strong>Rice</strong><br />

<strong>Research</strong> <strong>Institute</strong> (Phil<strong>Rice</strong>) to facilitate farmers’ adaptation<br />

and adoption of controlled irrigation (CI) (Bouman et al 2002,<br />

Lampayan et al 2003). CI entails an irrigation schedule in<br />

which, contrary to the normal practice of continuous flooding,<br />

water is applied to the field a number of days after the disappearance<br />

of ponded water and yet high yields are maintained<br />

(Tabbal et al 2002, Belder et al 2004). The CI technology was<br />

piloted among farmers using irrigation water drawn from deepwell<br />

systems in Tarlac Province, w<strong>here</strong> these deep wells are<br />

maintained and operated by farmers’ irrigation service cooperatives<br />

(ISC).<br />

The successful adoption of a new technology such as CI<br />

depends on not only its suitability and profitability but also on<br />

social and cultural factors such as farmers’ perceptions. Furthermore,<br />

w<strong>here</strong> irrigation water use is organized in a communal<br />

way, the organizational structure and functioning play a<br />

key role as well. The objectives of this paper are (1) to determine<br />

farmers’ perceptions of CI as an effective water-saving<br />

technology in rice production and (2) to explore success factors<br />

for collective action in an organized irrigation management<br />

system that would facilitate and ensure eventual farmers’<br />

adoption.<br />

Materials and methods<br />

We focus our study on the case of the deep well P-38 of the<br />

TTWS project, a reactivated system in Canarem, Victoria,<br />

Tarlac, about 70 km north of Manila. Eleven and 12 farmer<br />

volunteers in the 2002 and 2003 dry season (DS), respectively,<br />

participated in the CI experiment. Each farmer participant contributed<br />

two (neighboring) plots with a size of 500–1,000 m 2<br />

each, one representing the current farmers’ practice (FP) and<br />

one the CI technology. The water management of the CI plots<br />

was a joint affair among all project members and aimed at<br />

site-specific optimization of the technology (in terms of irrigation<br />

rotation, depth of application, number of days without<br />

ponded water, etc.). All activities and farm inputs and output<br />

were closely monitored in both seasons. An input-output survey<br />

of rice production for all 63 farmers was done in the 2003<br />

DS using a semistructured questionnaire. Focus-group discussions<br />

(FGDs) and key informant interviews were conducted<br />

among different stakeholders such as ISC officers and members,<br />

NIA staff, and <strong>IRRI</strong> water scientists. Field observations<br />

were likewise made and records of ISC meetings were documented<br />

throughout the dry-season rice cropping.<br />

Table 1. Farmers’ perceptions about controlled irrigation (CI) as a<br />

water-saving technology.<br />

Perceptions about CI (n = 15) Frequency Percentage<br />

1. Less time, less expensive, and saves labor 15 100<br />

2. It saves a lot of water 15 100<br />

3. No yield difference vis-à-vis farmers’<br />

practice (FP) 14 93<br />

4. I learned a lot of new techniques in modern<br />

rice production such as fertilizer application,<br />

selection of pure seeds, when to spray, how<br />

to save water during irrigation, etc. 11 73<br />

5. If CI would be adopted by all members in<br />

P-38 ISC, the water rotation interval would<br />

be improved in timeliness, reliability, and<br />

equity of water distribution from one field<br />

to another. 11 73<br />

6. Grains in CI plots are rounded and heavier 5 33<br />

7. FP plots could not produce more tillers<br />

because of continuous flooding 3 20<br />

8. I observed that, in modern rice<br />

production techniques, straight planting<br />

requires more people 2 13<br />

9. Others 3 20<br />

Others: Crop stand in both FP and CI are the same, CI plots have no diseases.<br />

Farmers’ perceptions of CI<br />

The majority of the farmer-cooperators gave positive feedback<br />

about the effectiveness of CI as a water-saving technology, as<br />

shown below and in Table 1.<br />

No yield difference compared with farmers’ practice<br />

(FP). Most farmers perceived that yield in the FP plots was<br />

similar to that in the CI plots, regardless of less water being<br />

used in the CI plots. This perception agrees with the yields<br />

obtained from crop-cut samples of 2 × 2.5-m 2 areas as indicated<br />

in Table 2. In both 2002 and 2003, t<strong>here</strong> was no significant<br />

yield difference under FP and CI.<br />

Saves water. Farmers recognized that CI saves water.<br />

Aside from alternate wetting and drying of the paddy field, CI<br />

maintains only a 2-cm depth of standing water in contrast to<br />

the usual farmers’ practice of maintaining a 5–8-cm water depth.<br />

On average, the amount of water saved in CI versus FP was<br />

16% in 2002 and 24% in 2003 (Fig. 1). The largest water savings<br />

were 24% in 2002 and 33% in 2003. The higher savings<br />

in 2003 reflect the effects of the learning process: at that time,<br />

farmers were already confident about the performance of CI<br />

and willing to take more risk in saving more water.<br />

Saves time, labor, and expenses. All farmer-cooperators<br />

acknowledged that CI saves time, labor, and expenses. It reduced<br />

costs by using 20–25% less fuel and oil (Table 2). It<br />

reduced labor as farmers spent fewer hours in irrigation, depending<br />

on the distance. Moreover, the ISC could abolish water<br />

delivery during nighttime.<br />

Better grain quality. Farmers observed that rice grains<br />

from CI plots were heavier, bigger, and in better shape because<br />

of soil aeration, w<strong>here</strong>as, in FP plots, rice grains were<br />

lighter and more slender, and sometimes unfilled, because of<br />

398 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 2. Average yield, costs, and returns of rice grown under two water management practices<br />

for demonstration farmers in Canarem, Victoria, Tarlac, for the dry season of 2002 and<br />

2003. The last column gives mean data for 2003 of all 63 farmers. FP = farmers’ practice, CI<br />

= controlled irrigation, n = number of farmers.<br />

Item<br />

2002 dry season 2003 dry season All farmers of<br />

P-38 ISC<br />

PF CI PF CI<br />

(n = 11) (n = 12) (n = 63)<br />

Yield (kg ha –1 ) 5,400 5,400 6,230 6,080 4,550<br />

Gross returns (pesos ha –1 ) 51,300 51,300 62,348 60,785 44,226<br />

Costs (pesos ha –1 )<br />

Materials 15,701 13,329 3,370 12,085 11,856<br />

Seed 1,950 1,950 600 600 1,114<br />

Fertilizer 2,400 2,400 5,362 5,632 3,711<br />

Pesticides 650 650 252 252 389<br />

Fuel and oil 9,841 7,469 6,769 5,484 6,640<br />

Others 860 860 387 387 –<br />

Labor 8,567 8,521 15,174 14,936 17,242<br />

Land preparation 2,500 2,500 3,089 3,085 733<br />

Crop establishment 2,700 2,700 3,658 3,658 2,010<br />

Crop care 867 821 1,496 1,496 347<br />

Postharvest labor 2,500 2,500 6,696 6,696 8,662<br />

Permanent labor – – – – 5,488<br />

Total production cost 24,268 21,849 28,545 27,021 29,098<br />

Net profit (pesos ha –1 ) 27,032 29,451 33,803 33,765 15,127<br />

the absence of soil aeration. In 2002, members of the TTWS<br />

project took grain samples from CI and FP plots for some quality<br />

analysis. The results showed no significant difference between<br />

CI and FP grains in the milling indicators, that is, head<br />

and broken rice, brewers’ rice, bran, chalky and immature<br />

grains, discoloration, and damaged grains.<br />

ISC functioning and impact of CI<br />

At the start of the TTWS project, tensions about water use<br />

were rising because of the increase in membership of the ISC<br />

(from 45 in 1998 to 63 at present), and because of subsequent<br />

increases in service area (from 50 to 70 ha) and the lengthening<br />

of the interval of water delivery (from 7 d to 12–14 d). The<br />

introduction of CI added to the tension because farmers were<br />

apprehensive of looking at their rice fields with dry land, especially<br />

when they saw the cracking of the soil. Many farmers<br />

doubted that CI would give them the same yields as or higher<br />

yields than their usual practice and, thus, some farmers started<br />

stealing water by placing holes underneath their paddy dikes,<br />

hidden from other farmers’ eyes. Conflicts were resolved<br />

through the intercession of village officials, particularly the<br />

village security officers.<br />

At the same time, many farmers were delinquent in paying<br />

their dues, resulting in a temporary stoppage of irrigation<br />

operations. Within 2 days, most farmers settled their bills, perhaps<br />

because water deliveries ceased when the crop was close<br />

to the flowering stage, when water is really much needed. Consequently,<br />

the ruling for having access to water was likewise<br />

changed from using NIA’s fuel and oil supply to using an individual<br />

supply. All farmers need to bring their own fuel and oil<br />

to the pump for irrigation of their fields, and this resulted in a<br />

remarkable 40% decrease in the total amount of fuel and oil<br />

used. During the time when the cooperative was using fuel<br />

provided by NIA, the farmers were quite extravagant in their<br />

use, but they were very prudent in their use when fuel was<br />

individually provided.<br />

After two years, the experiences with CI also helped ease<br />

tensions in water use. Farmers were no longer apprehensive of<br />

not having ponded water on their fields for some days as they<br />

had experienced that this did not reduce yields. Cohesive interaction<br />

among farmers also increased during the experimentation<br />

because everyone was curious about the performance of<br />

CI. And, when farmers saw the effectiveness and viability of<br />

CI, many were convinced that CI could reduce their water consumption.<br />

Since CI reduced water consumption, CI became a<br />

significant factor in solving operation problems and induced<br />

farmers to cooperate, that is, with the fuel scheme of bringing<br />

one’s own fuel and oil, and to be a continuing member of the<br />

deep-well system.<br />

Factors in success of collective action<br />

and adoption of CI<br />

Collective action is the basic foundation for facilitating adoption<br />

of CI in a deep-well irrigation system. Below are the factors<br />

identified as affecting the success of collective action.<br />

Group size. Groups should be small to minimize transaction<br />

costs, but cannot be too small or else the ISC won’t be<br />

able to cover the costs of operating and maintaining the sys-<br />

Session 13: Farmers’ participatory approaches to facilitate adoption of improved technology 399


% savings P 38, Canarem<br />

35<br />

30<br />

25<br />

20<br />

15<br />

10<br />

5<br />

0<br />

High<br />

Middle<br />

Low<br />

Average<br />

High<br />

Middle<br />

Low<br />

Average<br />

2002 dry season 2003 dry season<br />

Fig. 1. Average water savings (%) in controlled irrigation over farmers’ practice in Canarem,<br />

Victoria, Tarlac, for 2002 and 2003 dry seasons, based on data from 11–12 farmers.<br />

tem. Relatively small group sizes are generally associated with<br />

homogeneity among members; in addition, communication<br />

among members takes less time and effort. In the experience<br />

of P-38, communication and management (particularly in terms<br />

of payment) were easier with less than 50 members.<br />

Service area size. The size of the service area should be<br />

small, just large enough to maintain a water delivery schedule<br />

that would not create water stress to rice plants. At P-38, when<br />

the service area increased from 45 to 78 ha, the interval between<br />

water deliveries increased to accommodate all the fields.<br />

A long time interval is not acceptable to most members, and<br />

they prefer a 7-day interval rather than 12- to 14-day intervals.<br />

Profitability. Relative profitability of adopting CI should<br />

be high enough to make collective action profitable. Based on<br />

the experiments in 2002 and 2003, the amount of water used<br />

in CI was lower than in the usual farmers’ practice (Fig. 1),<br />

and hence irrigation costs were lower as well. Water savings<br />

averaged 16–24% and costs savings 20–25% (Table 2).<br />

Strong leadership—strict enforcement of rules to solve<br />

free-rider problem. In the first four years of operation, fuel<br />

and oil were supplied by NIA as part of a loan. Records show<br />

that ISC members used fuel excessively, probably because the<br />

payment was the same for each member and because payments<br />

were not immediate but made only after harvest. The chairman,<br />

imbibing the Filipino values of smooth interpersonal relationships<br />

and a sense of shame, was not so strict in enforcing<br />

the policies and regulations, particularly those related to paying<br />

dues to the ISC. But, with the strict enforcement of rulings<br />

on payment (that had resulted in halting the operation of P-38<br />

for two days) and access to water (bringing one’s own fuel),<br />

everyone was frugal in the amount of fuel used. These new<br />

policies and the use of CI reduced total fuel consumption by<br />

40%.<br />

Excludability. Excludability (i.e., the degree to which<br />

entitled users can keep out free riders) is an important factor<br />

in the effective operation of an ISC. Excludability is high in P-<br />

38, as witnessed by the temporary suspension of operations in<br />

2002 and by the rule of providing one’s own fuel and oil, without<br />

which one does not have access to water.<br />

Institutional linkages. Partnership with local government<br />

is necessary. It reinforces cooperation and discipline among<br />

members w<strong>here</strong> the village security officers intervened in resolving<br />

conflicts related to the stealing of water. Moreover,<br />

through close monitoring and mentoring by NIA of the ISC’s<br />

operation and maintenance of the system, farmers were able to<br />

receive guidance and technical support, which helped the P-<br />

38 ISC to be a stronger cooperative.<br />

Conclusions<br />

Controlled irrigation was tested through farmer participatory<br />

research and development, and found to be a viable technology<br />

for farmers’ use, as demonstrated by P-38 ISC members.<br />

Farmers perceived that CI saves significant amounts of water,<br />

time, labor, and cash, and reduces the costs of rice production.<br />

Furthermore, CI is perceived to give similar yield and produce<br />

more tillers, and bigger and heavier grains with good shape.<br />

Scientific evidence has corroborated the farmers’ perceptions<br />

on water savings and yield performance. Though CI is suitable<br />

for adoption by farmers based on their positive perceptions,<br />

good functioning and cooperation among members of<br />

an ISC seem to be another requirement for the adoption of CI<br />

400 <strong>Rice</strong> is life: scientific perspectives for the 21st century


in groundwater irrigation systems. The factors identified for<br />

successful collective action to facilitate CI’s implementation<br />

are group size, service area, profitability, high level of excludability,<br />

strong leadership to deal with free riders, and close<br />

linkages with local governments and the NIA.<br />

References<br />

Belder P, Bouman BAM, Cabangon R, Lu G, Quilang EJP, Li Y,<br />

Spiertz JHJ, Tuong TP. 2004. Effect of water-saving irrigation<br />

on rice yield and water use in typical lowland conditions<br />

in Asia. Agric. Water Manage. 65(3):193-210.<br />

Bouman BAM, Tuong TP. 2001. Field water management to save<br />

water and increase its productivity in irrigated lowland rice.<br />

Agric. Water Manage. 49:11-30.<br />

Bouman BAM, Tabbal DF, Lampayan RA, Cuyno RV, Quiamco MB,<br />

Vicmudo VR, Norte TM, Lactaoen AT, Quilang EJP, de Dios<br />

JL. 2002. Knowledge transfer for water-saving technologies<br />

in rice production in the Philippines. Proceedings of the 52nd<br />

Philippine Agricultural Engineering Annual National Convention,<br />

22-26 April 2002, Puerto Princesa City, Palawan, Philippines.<br />

p 14-30.<br />

<strong>IRRI</strong> (<strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>). 1995. Water: a looming<br />

crisis. Program report. Los Baños (Philippines): <strong>International</strong><br />

<strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>.<br />

Lampayan RM, Bouman BAM, de Dios JL, Lactaoen AT, Quilang<br />

EJP, Tabbal DF, Llorca LP, Norte TM, Soriano J, Corpuz AA,<br />

Espiritu AJ, Malasa RB, Vicmudo VR. 2003. Technology transfer<br />

for water savings (TTWS) in Central Luzon, Philippines:<br />

results and implications. Proceedings of the 53rd Philippine<br />

Agricultural Engineering Annual National Convention, 21-<br />

25 April 2003, Davao, Philippines. p 239-251.<br />

Tabbal DF, Bouman BAM, Bhuiyan SI, Sibayan EB, Sattar MA.<br />

2002. On-farm strategies for reducing water input in irrigated<br />

rice: case studies in the Philippines. Agric. Water Manage.<br />

56:93-112.<br />

Tuong TP, Bouman BAM. 2003. <strong>Rice</strong> production in water-scarce<br />

environments. In: Kijne JW, Barker R, Molden D, editors.<br />

Water productivity in agriculture: limits and opportunities for<br />

improvement. Wallingfond (UK): CABI Publishing. p 53-67.<br />

Wopereis MCS, Kropff MJ, Maligaya AR, Tuong TP. 1996. Droughtstress<br />

responses of two lowland rice cultivars to soil water<br />

status. Field Crops Res. 46:21-39.<br />

Notes<br />

Authors’ addresses: F.G. Palis, M. Hossain, and P.A.A. Cenas, Social<br />

Sciences Division; B.A.M. Bouman and R.M. Lampayan,<br />

Crop, Soil, and Water Sciences Division, <strong>International</strong> <strong>Rice</strong><br />

<strong>Research</strong> <strong>Institute</strong> (<strong>IRRI</strong>), DAPO Box 7777, Metro Manila,<br />

Philippines; A.T. Lactoen, T.M. Norte, and V.R. Vicmudo,<br />

National Irrigation Administration, Groundwater Irrigation<br />

System Reactivation Project, Tarlac, Philippines; G.T. Castillo,<br />

Consultant, <strong>IRRI</strong>.<br />

Companion modeling and multi-agent systems<br />

for collective learning and resource management<br />

in Asian rice ecosystems<br />

F. Bousquet and G. Trébuil<br />

It is widely admitted that poor coordination among stakeholders<br />

leads to inefficient resource use, economic and environmental<br />

damage, negative externalities, and social conflict. Diverse<br />

stakeholders use resources for different purposes, with<br />

differing perceptions of their dynamics, and adopt various strategies<br />

to cope with problems. Consequently, the number of social<br />

conflicts is increasing and they are frequently reported in<br />

the national and international media, for example, the cases of<br />

water sharing at rice transplanting among farmers and villages<br />

in Bhutan, and conflicts over land use between highlanders<br />

and lowlanders in northern Thailand uplands. To manage these<br />

problems, new legislative frameworks decentralizing the management<br />

of renewable resources are being introduced in many<br />

countries. Their success depends on the quality of the local<br />

coordination among stakeholders, who often lack tools, methods,<br />

and trained managers to achieve success.<br />

Thus, t<strong>here</strong> is a demand for innovative approaches and<br />

tools to improve coordination processes among an increasing<br />

number of stakeholders using common resources at the rice<br />

agroecosystem level. Our hypothesis is that an understanding<br />

and modeling of the diversity of stakeholders’ perceptions,<br />

associated with participatory simulation sessions, can be used<br />

to improve resource management through better coordination<br />

of people’s actions in any type of rice ecosystem.<br />

The proposed companion modeling approach<br />

Usually, models are used to assemble scientific knowledge and<br />

to propose recommendations to a given decision-maker. In our<br />

case, we propose to use models to represent the different perceptions<br />

of various stakeholders in order to facilitate the coordination<br />

of their actions on a common resource. Some experiments<br />

were conducted by using geographic information systems<br />

(GIS) (Abbot et al 1998, Gonzalez 2000), but very few<br />

of them dealt with the use of simulations (Costanza and Ruth<br />

1998). The main lesson learned is that these tools, like many<br />

Session 13: Farmers’ participatory approaches to facilitate adoption of improved technology 401


technological innovations, can both marginalize and empower<br />

people and communities.<br />

Companion modeling (ComMod) is a methodology for<br />

the collective implementation and use of simulation models,<br />

and, more precisely, multi-agent simulation systems (MAS)<br />

(Barreteau 2003). The ComMod approach proposes an iterative<br />

and evolving modeling process: participatory modeling is<br />

used to facilitate stakeholders’ interactions and to identify and<br />

scope resource management problems to be discussed and<br />

negotiated. Then, simulation models are used to collectively<br />

assess scenarios selected by stakeholders. This may lead to<br />

new questions, new discussions, changes in the model, and so<br />

on.<br />

ComMod combines the use of different tools such as<br />

agent-based modeling (ABM), GIS, participatory mapping, and<br />

role-playing games (RPG). From a methodology development<br />

point of view, the ComMod approach has been tested and used<br />

in several places, leading to concrete policy recommendations<br />

or collective actions by communities (Aquino (d’) et al 2002,<br />

2003, Etienne et al 2003). The use of ComMod implies the<br />

execution of the following set of activities in an iterative way:<br />

Framing. Preliminary diagnostic analysis at the system<br />

level. Identification and understanding of the<br />

system’s ecological and social dynamics and of key<br />

issues, concerns, and intervention points with stakeholders.<br />

Collection of relevant existing data. Identification<br />

of knowledge gaps to be filled through specific<br />

surveys.<br />

Prioritization and visioning. Participatory selection<br />

of a key concrete problem to be examined. Establishment<br />

of a common vision shared by all key stakeholders<br />

through RPG and participatory simulation<br />

workshops. Delimitation of initial areas of agreement,<br />

disagreement, uncertainty, and room for coordination<br />

and negotiation. Production of qualitative guidelines<br />

for monitoring and evaluation of the subsequent<br />

ComMod activities.<br />

Participatory field work and modeling. Implementation<br />

of an iterative, integrated, flexible, and userfriendly<br />

modeling approach combining participatory<br />

workshops and laboratory work. Joint validation of<br />

the simulation tool with all concerned stakeholders,<br />

followed by participatory identification of relevant<br />

resource management scenarios to be simulated and<br />

assessed collectively, taking into account the competing<br />

uses of resources by multiple users.<br />

Collective exploration and discussion of trade-offs<br />

displayed by the simulated scenarios. Choice and design<br />

of an action plan to be implemented to tackle<br />

the resource management problem under consideration.<br />

Assessment of local impact. Assessment of the local<br />

impact of the approach for participatory and integrated<br />

renewable resource management (IRRM).<br />

Case studies<br />

For the past three years, the ComMod approach has been used<br />

to examine various resource management problems in different<br />

Asian rice ecosystems (Bousquet et al, in press).<br />

Water sharing at rice transplanting<br />

in Lingmuteychu, Bhutan<br />

Lingmuteychu is a catchment covering 34 km 2 in west-central<br />

Bhutan, which is drained by a totally rainfed stream originating<br />

from a rock face at an altitude of 2,400 m. Five small irrigation<br />

systems formed of 12 canals irrigate about 200 ha of<br />

terraced paddies belonging to 121 households of six villages.<br />

These villages share irrigation water within a broadly respected<br />

customary regime evolved during a time when demands were<br />

lower. Under the current processes of market integration, decentralization,<br />

and resource conservation policies, and changes<br />

in villagers’ social needs, this customary water-sharing set of<br />

rules is not adapted to current farming conditions anymore and<br />

causes repetitive social conflicts, particularly at rice transplanting,<br />

as these conflicts remain unresolved. T<strong>here</strong> is a definite<br />

contrast in perceptions of users on the water resource: some<br />

consider it an infinite resource, many consider this resource as<br />

an exclusively common pool with a free-access regime, w<strong>here</strong>as<br />

the state considers it as its property. The Draft National Water<br />

Policy pronounces water as a state property while it emphasizes<br />

integrated management. Under the new national community-based<br />

NRM policy (CB-NRM), this watershed has been<br />

selected as a pilot site to improve coordination among water<br />

users. It is located near the Bajo Renewable Natural Resources<br />

<strong>Research</strong> Center (RNR-RC), which is leading the national effort<br />

in the field of CB-NRM, and the Natural Resource Training<br />

<strong>Institute</strong> (NRTI) at Lobeysa, the principal institution for<br />

higher education in agriculture and resource management in<br />

the kingdom. Participatory land-use planning and rural appraisal<br />

activities were carried out by the RNR-RC Bajo team<br />

at this site. More recently, an analysis of existing water dynamics,<br />

water-sharing arrangements, and farming practices has<br />

been implemented and a first participatory workshop was held<br />

in the two upper villages (w<strong>here</strong> the conflict over water use is<br />

acute) in May 2003 to test the proposed ComMod methodology<br />

for supporting farmers from the two villages to examine<br />

collectively the problem of water exchange at rice transplanting<br />

(Gurung, in press). Based on the successful outputs, another<br />

participatory workshop was held in December 2003 to<br />

modify water-sharing rules. Figure 1 shows the assessment of<br />

the ComMod process on the perceptions of the water-sharing<br />

issue by the local stakeholders who took part in both workshops.<br />

By using a MAS model reproducing the RPG played<br />

and validated by the farmers, simulations were carried out later<br />

to examine the relative effects of social networks, communication<br />

protocols, and climate conditions on water-use efficiency.<br />

Results indicate that communication protocols constitute<br />

the most sensitive factor.<br />

402 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Respondents (%)<br />

80<br />

70<br />

60<br />

50<br />

40<br />

30<br />

20<br />

10<br />

0<br />

May 2003<br />

Dec 2003<br />

Farm<br />

activities<br />

Valuation<br />

of water<br />

Water<br />

shortage<br />

Share<br />

water<br />

Lessons learned<br />

Income<br />

Canal<br />

management<br />

Control<br />

water<br />

use<br />

Fig. 1. Lessons learned by the stakeholders after two participatory workshops.<br />

Soil and water conservation in diversifying highlands<br />

of upper northern Thailand<br />

Mae Salaep is a highland village in Mae Fah Luang District of<br />

Chiang Rai Province, w<strong>here</strong> small-scale poor Akha farmers<br />

are being rapidly integrated into the market economy. While<br />

their former agrarian system based on swiddening is being replaced<br />

by semipermanent agriculture on steep slopes, the risk<br />

of increased land degradation through soil erosion by concentrated<br />

runoff is a major problem. The diversity of farmers (economic<br />

status, agricultural practices, etc.) is already extensive,<br />

and their economic and institutional environment is becoming<br />

more complex (Trébuil et al 2002). An increasing number of<br />

individual or collective stakeholders with differing land- and<br />

water-use strategies interact in the dynamics of diversifying<br />

sloping-land agriculture. In collaboration with Chiang Mai<br />

University, the Department of Public Welfare (a government<br />

development agency looking after highland ethnic minorities),<br />

and a local NGO, a spatially explicit multi-agent model linked<br />

to a small GIS was built to represent the key interacting ecological<br />

and agronomic dynamics (slope characteristics, rainfall,<br />

main cropping systems and succession of practices, farmer<br />

differentiation, etc.) to assess the risk of soil degradation. This<br />

MAS model was later simplified and translated into an RPG<br />

to be used with farmers to validate the understanding of the<br />

agricultural dynamics by the research team. In December 2002<br />

and May 2004, two participatory modeling workshops, focusing<br />

on land-use changes (particularly the transition from annual<br />

crops to perennial plantations) and the organization of<br />

the credit system at the village level, respectively, were held<br />

with representatives from all categories of farmers and development<br />

agencies. From the first to the second workshop, at<br />

the request of the participants, the emphasis shifted from<br />

achieving a shared representation of the IRRM problem and<br />

its causes to the use of ComMod for improving the allocation<br />

of new village funds to improve the current situation and especially<br />

the access of small farmers to plantation crops to limit<br />

erosion risk. MAS simulations were used to examine the respective<br />

influence of formal and informal credit on the welfare<br />

of different kinds of stakeholders (Barnaud 2004).<br />

Conclusions<br />

The ComMod approach seems to be well received by both<br />

scientists working in the field of IRRM and local stakeholders.<br />

It is important to distinguish between the use of this approach<br />

in two specific contexts: (1) to produce knowledge on<br />

complex rice systems and (2) to support evolving, iterative,<br />

and continuous collective decision-making processes for<br />

IRRM. W<strong>here</strong> the land policy favors a decentralized management<br />

of resources, such a MAS-based companion modeling<br />

approach has great potential to improve the collective management<br />

of rice lands. It can be used to facilitate dialogue, to<br />

mitigate conflicts, and to establish coordination mechanisms<br />

regarding multiple uses of the land by multiple stakeholders.<br />

It is also a powerful tool to integrate knowledge from different<br />

disciplines, sources, and levels of organization. ComMod facilitates<br />

the collective assessment of desirable scenarios and<br />

identification of suitable innovations to overcome current<br />

IRRM problems in rice ecosystems.<br />

References<br />

Abbot J, Chambers R, et al. 1998. Participatory GIS: opportunity or<br />

oxymoron PLA Notes 33:27-34.<br />

Aquino (d’) P, Le Page C, et al. 2002. A novel mediating participatory<br />

modelling: the ‘self-design’ process to accompany collective<br />

decision making. Int. J. Agric. Resources Governance<br />

Ecol. 2(1):59-74.<br />

Aquino (d’) P, Le Page C, et al. 2003. Using self-designed roleplaying<br />

games and a multi-agent system to empower a local<br />

decision-making process for land use management: the<br />

SelfCormas experiment in Senegal. J. Artif. Societ. Soc. Simul.<br />

6(3).<br />

Session 13: Farmers’ participatory approaches to facilitate adoption of improved technology 403


Barnaud C. 2004. Erosion des sols et systèmes agraires dens les hautes<br />

terres de la Thailandes: une approche de la complexité par<br />

une modélisation d’accompagnement. Master Thesis, Mémoire<br />

de DEA, Géographie et pratique du développement. Paris,<br />

Université de Paris X-Nanterrep.<br />

Barreteau O. 2003. Our companion modelling. J. Artif. Societ. Soc.<br />

Simul. 6(1).<br />

Bousquet F, Trébuil G, Hardy B, editors. In press. Companion modeling<br />

and multi-agent systems for integrated natural resource<br />

management in Asia. Los Baños (Philippines): <strong>International</strong><br />

<strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>.<br />

Costanza R, Ruth M. 1998. Using dynamic modeling to scope environmental<br />

problems and build consensus. Environ. Manage.<br />

22(2):183-195.<br />

Etienne M, Le Page C, et al. 2003. A step-by-step approach to building<br />

land management scenarios based on multiple viewpoints<br />

on multi-agent system simulations. J. Artif. Societ. Soc. Simul.<br />

6(2).<br />

Gonzalez R. 2000. Platforms and terraces: bridging participation and<br />

GIS in joint learning for watershed management with the<br />

Ifugaos of the Philippines. PhD thesis. ITC-Wageningen University.<br />

186 p.<br />

Gurung T. In press. Companion modeling to examine water-sharing<br />

arrangements among rice-growing villages in west-central<br />

Bhutan: preliminary results. In: Bousquet F, Trébuil G, Hardy<br />

B, editors. Companion modeling and multi-agent systems for<br />

integrated natural resource management in Asia. Los Baños<br />

(Philippines): <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>.<br />

Trébuil G, Shinawatra-Ekasingh B, Bousquet F, Thong-Ngam C.<br />

2002. Multi-agent systems companion modeling for integrated<br />

watershed management: a northern Thailand experience. In:<br />

Jianchu X, Mikesell S, editors. Landscapes of diversity.<br />

Yunnan Science and Technology Press, China. Proceedings<br />

of the 3rd <strong>International</strong> Conference on Montane Mainland<br />

Southeast Asia (MMSEA 3), Lijiang, Yunnan, China, 25-28<br />

August 2002. p 349-358. At www.cbik.ac.cn/cbik/resource/<br />

MMSEA_Index.asp, accessed 8 September 2003.<br />

Notes<br />

Authors’ addresses: F. Bousquet, <strong>IRRI</strong>-Cirad-DOA, Bangkok, Thailand,<br />

e-mail: f.bousquet@cgiar.org; G. Trébuil, <strong>IRRI</strong>-Cirad-<br />

DOA Project, Bangkok, Thailand, e-mail: guy.trebuil@cirad.fr.<br />

Participatory approaches for improving rice breeding<br />

in the Mekong Delta of Vietnam<br />

Nguyen Ngoc De and Kotaro Ohara<br />

Most conventional breeding programs have been set up and<br />

designed by breeders, neglecting the role of users: farmers and<br />

farming communities. T<strong>here</strong>fore, the dissemination process of<br />

so-called “technology transfer” was very slow and costly for<br />

both breeders and farmers.<br />

The use of participatory approaches assures the involvement<br />

of farmers at different levels in the whole process of crop<br />

improvement to overcome the shortcomings of conventional<br />

breeding approaches.<br />

Can Tho University, as the leading research institution<br />

for adapting the participatory approach in rice improvement,<br />

started on-farm breeding programs as early as 1975 by sending<br />

out its staff and students to work closely with farmers for<br />

local crop improvement (Xuan et al 1993). Later, with the inception<br />

of the Community Biodiversity Development and Conservation<br />

(CBDC) project in 1994, and the global in situ conservation<br />

of biodiversity project implemented by the <strong>International</strong><br />

Plant Genetic Resources <strong>Institute</strong> (IPGRI) in 1998, participatory<br />

plant breeding (PPB) and participatory variety selection<br />

(PVS) approaches have been introduced to develop crop<br />

varieties specific to niche environments and farmers’ preferences.<br />

This paper reviews the achievements, problems, and lessons<br />

learned from these practices using new approaches in the<br />

Mekong Delta of Vietnam.<br />

Methods used in participatory crop improvement<br />

Witcombe and Joshi (1996) defined PPB as involving farmers<br />

in selecting genotypes from genetically variable segregating<br />

materials and PVS as involving the selection by farmers of<br />

nonsegregating characterized products from plant breeding<br />

programs. In practice, the use of PVS and/or PPB depends on<br />

farmers’ varietal needs and farmers’ breeding knowledge and<br />

technical skills. The PVS approach has been used to improve<br />

local landraces (crop cultivars/varieties that adapted and have<br />

been kept for a long time in local areas) and to evaluate the<br />

finished breeding materials from research institutions. When<br />

varietal options available to farmers through PVS are limited<br />

or exhausted, PPB begins.<br />

A successful PPB program should involve farmers as<br />

much as possible in the whole process of plant breeding (De<br />

2000).<br />

Participatory plant breeding involves the following steps<br />

and activities.<br />

Needs assessment and community organization<br />

Community meetings are organized to identify farmers’ problems<br />

and needs. By discussing with farmers and local officials,<br />

cooperating farmers are divided into three groups depending<br />

on their technical knowledge and skill.<br />

404 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Farmer participation<br />

Collection<br />

<strong>IRRI</strong><br />

Thailand<br />

Genebank<br />

Collaboration<br />

*<br />

*<br />

**<br />

Characterization<br />

Evaluation<br />

Conservation<br />

Use<br />

Breeding<br />

program<br />

Can Tho University<br />

Seed request<br />

IRTP/INGER<br />

Selection<br />

coding as<br />

Coordinating<br />

Receiving<br />

Selection<br />

coding as<br />

“L” lines<br />

*<br />

Preliminary observation<br />

“IR” lines<br />

*<br />

Replicated observation<br />

CBDC and IPGRI<br />

projects<br />

***<br />

Coordinating<br />

Yield trial<br />

Naming<br />

as<br />

“MTL” lines<br />

****<br />

Adaptation field test<br />

****<br />

Seed multiplication<br />

****<br />

New variety released<br />

Fig. 1. The participatory rice varietal improvement program in the Farming Systems <strong>Research</strong><br />

and Development <strong>Institute</strong>, Can Tho University, Vietnam. MTL (Mien Tay Lua) =<br />

crossed, selected, and released by Farming Systems <strong>Institute</strong>; CBDC = community<br />

biodiversity development and conservation; IPGRI = <strong>International</strong> Plant Genetic Resources<br />

<strong>Institute</strong> with on-farm conservation project; farmer participation level = from little (*) to full<br />

(****) participation.<br />

<br />

<br />

<br />

Group 1 (2–3 farmers) will take responsibility for<br />

making crosses and selecting segregating breeding<br />

materials (PPB activities).<br />

Group 2 (5–10 farmers) will field-test stable lines and<br />

promising varieties (PVS activities).<br />

Group 3 (30–40 farmers) could be involved in seed<br />

multiplication and distribution of selected varieties<br />

for local use.<br />

Setting breeding objectives<br />

and identifying donor parents<br />

Breeders work closely with farmers to identify breeding objectives.<br />

Some examples of farmers’ breeding criteria for rice<br />

are high yield, short duration, resistance to major pests and<br />

diseases, good eating quality, and so on. Based on the breeding<br />

objectives, breeders then assist farmers in searching for<br />

suitable donor parents. These donors could be found among<br />

the available genetic materials at the local level or from research<br />

institutions.<br />

The level of farmers’ participation in the rice breeding<br />

process is described in Figure 1.<br />

Conducting field activities<br />

1. Participatory plant breeding (PPB)<br />

Making crosses. Group 1 farmers are given additional<br />

training on breeding and are assisted by<br />

Session 13: Farmers’ participatory approaches to facilitate adoption of improved technology 405


Results<br />

<br />

breeders in making desirable crosses to meet local<br />

breeding objectives.<br />

Selecting from segregating materials. Early generations<br />

will be evaluated and selected together<br />

with segregating lines provided by research institutions.<br />

This process is repeated until stable<br />

lines are obtained. Farmers with adequate training<br />

can practice mass selection and pure-line<br />

selection.<br />

2. Participatory varietal selection (PVS)<br />

Genetic improvement of local adapted varieties.<br />

Farmers can improve their local landraces<br />

or common varieties for better genetic purity,<br />

higher yield, better quality, and resistance to<br />

major pests by pureline selection or mass selection<br />

methods. Sometimes, the local varieties collected<br />

from the community or other communities<br />

are reintroduced to the community after seed<br />

loss caused by a disaster. In addition, new varieties<br />

from research institutions are provided for<br />

testing together with finished products from PPB<br />

activities.<br />

Varietal testing for local adaptation. Stable lines<br />

(20–40) selected from the segregating materials<br />

or provided by research institutions are planted<br />

in an observation test with common local varieties<br />

as local checks. The promising varieties (5–<br />

10) selected from the observation test are then<br />

tested in larger plot sizes for a yield trial. Farmer<br />

field days (activities to assemble local farmers<br />

at demonstration plots for direct observation,<br />

evaluation, and interaction) are organized just<br />

before harvesting for a joint evaluation.<br />

Seed multiplication. Desirable varieties (usually<br />

2–3) from yield trials are then selected for seed<br />

multiplication by a larger group of farmers to<br />

use in the community.<br />

3. Monitoring and evaluation<br />

Farmers closely monitor and keep records on field conditions<br />

and crop performance for later analysis to determine<br />

suitable varieties. A major data set consists of<br />

growth duration, plant height, tillering capacity, grain<br />

yield, grain quality, and tolerance ability for major insects<br />

and diseases. Field visits and farmer field days involving<br />

breeders, extension workers, and farmers are<br />

the most appropriate tools for monitoring and evaluating<br />

PPB/PVS activities.<br />

Participatory varietal selection<br />

From 1975 to 2003, hundreds of promising rice varieties were<br />

tested in farmers’ fields under farmers’ management, and many<br />

varieties were identified and released as national recognized<br />

varieties using the participatory approach. Of these, some famous<br />

rice varieties are IR36 (named as NN3A), MTL2<br />

(NN6A), MTL30 (NN7A), MTL9 (NN2B), IR42 (NN4B),<br />

MTL58 (IR13240-108-2-2-3), and MTL87 (IR50404-57-2-2-<br />

3). These varieties have made a great contribution to the improvement<br />

of rice production in the Mekong Delta. Many farmers,<br />

such as Hai Huu (Long An Province), Hai Chung, Tu Tai,<br />

and Ba Chuong (Tien Giang Province), Ba Cung and Hai Triem<br />

(An Giang Province), Muoi Tuoc and Muoi Than Nong (Vinh<br />

Long Province), and many others are known as “rice selection<br />

kings.” Farmers are not only selecting suitable finished varieties<br />

but also improving the varieties formally released for better<br />

grain quality and adaptation to specific conditions in their<br />

areas by pure-line selection. This process increases both crop<br />

productivity and local crop diversity.<br />

Depending on local resource availability and management<br />

capacity, each community has received 7–30 varieties<br />

for testing and 3–4 varieties have been selected annually for<br />

seed multiplication and use (Table 1).<br />

Participatory plant breeding<br />

In the 1996-97 dry season, Can Tho University started providing<br />

63 segregating F 2 -F 3 populations of 12 crosses for four<br />

pilot communities.<br />

In 1998-99, L246-7-3-B and L247-1-5-B, the two promising<br />

farmer selections noted as SiC-1 (Soc Trang Selection,<br />

no. 1) and SiC-2 (Soc Trang Selection, no. 2), respectively,<br />

were purified by Ke Sach community (Soc Trang Province)<br />

using the bulk selection method. Mr. Canh (a farmer group<br />

leader) led the selection activities. Similarly, L246-10-1-B, a<br />

promising line selected by farmers in My Thanh community<br />

(Ba Tri District, Ben Tre Province), is also undergoing a yield<br />

test and seed multiplication. In 2003, Mr. Thanh in Cho Moi<br />

District (An Giang Province) selected two stable lines, TH1<br />

and TH2, from segregating breeding material of Can Tho University<br />

in a similar way.<br />

Discussion<br />

With technical training and field assistance, farmers can manage<br />

their own breeding programs. The total number of rice<br />

varieties in the communities is increasing through the introduction<br />

of new varieties and locally improved cultivars. As a<br />

result, land productivity and farm income have been improving.<br />

Problems<br />

Some problems have occurred.<br />

Farmers are more willing to multiply promising varieties<br />

(PVS) than to select from segregating materials<br />

or make crosses (PPB) because of the time and resources<br />

needed and the requirement of skills and intellectual<br />

input.<br />

The low education level of farmers limits the adoption<br />

of PPB; t<strong>here</strong>fore, more training and field coaching<br />

are required.<br />

406 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. Numbers of rice varieties tested and selected for local use by farming<br />

communities since 1994.<br />

Year Varieties tested Varieties selected Seed multiplication (t)<br />

Total Each Total Each Total Each<br />

community community community<br />

1994 20 6.7 5 1.6 3.2 0.8<br />

1995 197 39.4 25 4.2 4.3 0.9<br />

1996 182 26.0 22 3.1 12.6 2.1<br />

1997 58 7.3 34 3.4 18.3 2.3<br />

1998 78 8.7 30 3.0 35.6 3.9<br />

1999 90 8.2 36 3.6 39.2 3.9<br />

2000 131 9.4 44 3.7 121.4 9.3<br />

2001 192 8.7 66 3.5 316.3 16.6<br />

2002 280 10.8 107 4.7 512.4 21.3<br />

2003 275 12.0 103 4.5 647.7 28.2<br />

Av 150.3 13.7 47.2 3.5 171.1 8.9<br />

Source: Data from field survey by authors, 2003.<br />

<br />

Morris (2003) also pointed out three challenges of<br />

participatory breeding:<br />

— T<strong>here</strong> is a need to develop varietal evaluation<br />

methods capable of generating credible data for<br />

widespread acceptability.<br />

— A level of participation that will ensure equitable<br />

compensation for participating farmers is needed.<br />

— National and international regulatory frameworks<br />

that govern the evaluation, approval, and release<br />

of new plant varieties from PPB are necessary.<br />

Lessons learned<br />

The following lessons can be drawn from these activities:<br />

Farmers conserve and improve biodiversity to meet<br />

their needs for home consumption, the market<br />

economy, and adaptation to local environments and<br />

farm resources. T<strong>here</strong>fore, farmers’ needs and perceptions<br />

should be taken into consideration to bring<br />

breeders’ objectives closer to farmers’ objectives.<br />

Support from local authorities and organizations in<br />

terms of organization, management, additional funds,<br />

and facilitation is very important to ensure a successful<br />

participatory approach.<br />

Cooperation with a group/community on PPB/PVS<br />

turns out better than that with individual farmers because<br />

group/community members can help each other.<br />

Farmer field schools and farmer field days are good<br />

ways to stimulate farmers’ participation and to train<br />

farmers with a lower education.<br />

Conclusions<br />

Participatory approaches could improve breeding for local<br />

adaptation, local genetic diversity, efficiency, and the empowerment<br />

of rural communities. The achievements in these activities<br />

have had a strong impact on national seed policies,<br />

which are under review and reform in Vietnam. However, a<br />

successful participatory approach in crop improvement requires<br />

a willingness to contribute time, land, labor, and other inputs,<br />

and to incur possible risk. It requires technical knowledge and<br />

skill from farmers, and a decentralized breeding strategy and<br />

technical assistance from breeders. It also requires favorable<br />

policies and support in organization and management.<br />

References<br />

De Nguyen Ngoc. 2000. Linking the national genebank of Vietnam<br />

and farmers. In: Friis-Hansen E, Sthapit B, editors. Participatory<br />

approaches to the conservation and use of plant genetic<br />

resources. Rome (Italy): <strong>International</strong> Plant Genetic Resources<br />

<strong>Institute</strong>. p 62-68.<br />

Morris ML, Bellon MR. 2003. Participatory plant breeding research:<br />

opportunities and challenges for the international crop improvement<br />

system. Euphytica (2003):1-15.<br />

Witcombe J, Joshi A. 1996. Farmer participatory approaches for<br />

varietal breeding and selection and linkages to the formal seed<br />

sector. In: Participatory plant breeding. Proceedings of a workshop<br />

on participatory plant breeding, 26-29 July 1995.<br />

Wageningen, Netherlands. p 57-65.<br />

Xuan Vo-Tong et al. 1993. Present status of agricultural extension in<br />

Vietnam. Paper presented at the first Southeast Asia workshop<br />

on formulation of project proposals on technology transfer<br />

for major food crop production, FAO and UAF, Ho Chi<br />

Minh City, Vietnam, 6-9 Dec. 1993.<br />

Notes<br />

Authors’ addresses: Nguyen Ngoc De, Mekong Delta Farming Systems<br />

<strong>Research</strong> and Development <strong>Institute</strong>, Can Tho University,<br />

Vietnam; Kotaro Ohara, Department of Sustainable Resource<br />

Sciences, Faculty of Bio-Resources, MIE University,<br />

Japan, e-mail: nnde@ctu.edu.vn, ohara@bio.mie-u.ac.jp.<br />

Session 13: Farmers’ participatory approaches to facilitate adoption of improved technology 407


<strong>IRRI</strong>’s approach to participatory research for development:<br />

advances and limitations<br />

Thelma R. Paris and M. Zainul Abedin<br />

Why do participatory research While the traditional linear<br />

and top-down research-extension-farmer transfer of technology<br />

(TOT) model was successful in disseminating rice technologies<br />

for favorable rice environments, this approach no<br />

longer holds for rice research in unfavorable environments. In<br />

the traditional top-down approach, technologies developed<br />

were packaged for delivery to farmers and experiments with<br />

component rice technologies were conducted on-station. Despite<br />

the many available technologies generated at the station,<br />

the traditional research approach has had limited success in<br />

unfavorable rice environments, which have high biophysical,<br />

socioeconomic, and cultural diversity, and poor access to markets<br />

and infrastructure facilities. This created a mismatch between<br />

research recommendations and farmers’ needs and expectations<br />

and thus low or no adoption of technologies. Crop<br />

and natural resource management technologies require an<br />

analysis of how farmers make decisions, develop a corrective<br />

heuristic, frame it as a hypothesis, and become motivated to<br />

participate in an experiment to test it. Similarly, germplasm<br />

improvement requires an understanding of farmers’ preferences<br />

and criteria for rice varietal selection in fragile environments.<br />

We need to understand what “enabling inputs” may be required<br />

to accelerate and widen adoption. These requirements necessitate<br />

the use of participatory research approaches through<br />

which researchers and farmers can work as active partners in<br />

developing suitable technologies suited to their livelihood and<br />

ecosystems. Such active partnership creates synergistic effects<br />

as it integrates the knowledge, experience, and skills of farmers<br />

and scientists.<br />

What is participatory research<br />

“Participation” and “participatory” have become such fashionable<br />

terms recently that any kind of activity involving a<br />

group of people is termed “participatory.” As these terms embrace<br />

a multitude of meanings, and these meanings become<br />

correspondingly dilute, a serious threat is posed to the use of<br />

the term “participatory research.” The risk is that a catch-all<br />

definition of participatory research is destined to fall out of<br />

fashion and to be discarded as fashion changes, without even<br />

receiving the serious scientific evaluation of its potential that<br />

a rigorous but less trendy use of the term would invite. The<br />

term “participatory research” is a collection of approaches that<br />

enable participants to develop their own understanding of and<br />

control over the processes and events being investigated. It is<br />

loosely used to describe various types and levels of local involvement<br />

in and control of the research process (Ashby 1997).<br />

Participatory research has diverse approaches, perspectives,<br />

practices, and methods. At <strong>IRRI</strong>, participatory research<br />

differs according to various interpretations of the mode of research<br />

partnership or “participation” in research, the goal or<br />

rationale for encouraging participation, gender and stages in<br />

the project, the level of “control” or “ownership” that local<br />

people have over the research process, the scale of participatory<br />

activities and stakeholder involvement and the levels of<br />

management involved, and the level of disaggregation and representation<br />

of different stakeholders required for the research.<br />

Clearly, t<strong>here</strong> is no formula for deciding which level of<br />

participation is the best. The level chosen will depend on the<br />

objectives of the activity. What is more important is to have<br />

well-defined research problems and well-defined technologies<br />

for a vigorous process whether with farmers or other stakeholders.<br />

It is important, however, to distinguish which of these<br />

levels of farmer or community participation we refer to when<br />

research is called “participatory.”<br />

Advances in participatory research at <strong>IRRI</strong><br />

Through the years, progress has been made in participatory<br />

research at <strong>IRRI</strong>. Biological scientists in close interaction with<br />

social scientists have tested, refined, and adapted protocols<br />

for farmer/community participatory research in natural resource<br />

management (NRM) and participatory plant breeding (PPB).<br />

Participatory research (PR) has fast-tracked the adoption of<br />

innovations and in several cases has contributed to adoption<br />

on a large scale. Working with national agricultural research<br />

and extension systems (NARES) on projects using the PR approach<br />

has changed the attitudes, mind-sets, and research orientation<br />

of scientists and research managers. The specific advances<br />

in PR at <strong>IRRI</strong> in natural resource management and rice<br />

germplasm development are described below.<br />

Natural resource management<br />

In integrated pest management (IPM) in Vietnam, farmers<br />

“learn by doing” and decision rules are modified on the basis<br />

of direct experience. A radical change in the research sequence<br />

of IPM was made by starting with the farmers’ perspective<br />

during the problem definition or initial problem diagnosis. This<br />

approach provided a mechanism for scientists to learn about<br />

farmers’ decision constraints, determine research needs, use<br />

research information, and “distill” these into testable hypotheses<br />

for farmers (Heong and Escalada 2003, Huan et al 2004).<br />

In Bangladesh and in West Bengal, India, the use of the community<br />

participatory approach to research (CPAR) to evaluate<br />

408 <strong>Rice</strong> is life: scientific perspectives for the 21st century


the leaf color chart (LCC) for nitrogen management and a plastic<br />

drum seeder for direct wed seeding of rice facilitated adoption<br />

on a large scale (Bagchi et al, this volume). The formation<br />

of small groups of participating farmers around each LCC or<br />

drum seeder facilitated continued monitoring by participating<br />

farmers, which led to better decision making and adoption<br />

(Abedin 2004).<br />

Participatory varietal selection (PVS)<br />

Farmer participation in varietal selection improved the selection<br />

of suitable varieties for complex rainfed environments<br />

because farmers were given the opportunity to screen new varieties<br />

in their specific environments. Farmer-managed trials<br />

provided important information about the performance, quality,<br />

and overall acceptability of new rainfed rice varieties (Atlin<br />

et al 2002a, Gregorio et al 2004). Moreover, farmers’ selection<br />

criteria from different socioeconomic groups, including<br />

women, are now well understood by breeders (Paris et al 2001,<br />

2002). Farmer-preferred lines through PVS are spreading fast<br />

through farmer-to-farmer exchange. Lines selected from PVS<br />

are now being considered for national/formal release in eastern<br />

India (Paris et al 2002) and in Bangladesh. More and more<br />

plant breeders now practice PVS as a normal routine of the<br />

breeding process. PVS is being institutionalized with the Lao<br />

breeding program. PVS in the Thai national program is proceeding<br />

rapidly. Key ingredients from senior Thai breeders,<br />

the availability of training and methodology documentation<br />

from <strong>IRRI</strong>, and initial support from an external donor have<br />

contributed to this initial success (Atlin et al 2002b).<br />

Capacity development and institutionalization<br />

Several training workshops were conducted to enhance the<br />

capabilities of NARES partners in various aspects of PR in<br />

NRM and PVS. <strong>IRRI</strong> has incorporated PR in the curriculum<br />

of the new rice plant breeding course held every year. In-country<br />

training on PR and socioeconomic analysis has been conducted<br />

by <strong>IRRI</strong> and CIMMYT and will continue to further<br />

enhance the skills of NARES collaborators.<br />

Limitations of participatory research<br />

<br />

<br />

<br />

Although using PR has many advantages, some limitations need<br />

to be overcome. These are discussed below.<br />

Poor understanding of PR. The process of becoming<br />

a “participatory” researcher entails a holistic change<br />

in knowledge, attitude, and practice. Participatory research<br />

is often seen as a threat to classic research<br />

paradigms and not so much as complementary research.<br />

Moreover, the core capacities required for<br />

participatory research are often seen as being incompatible<br />

with dominant research norms and practices.<br />

T<strong>here</strong> is some diversity regarding the understanding<br />

of demand-driven, client-oriented, or participatory<br />

research approaches by senior management. Its basic<br />

principles and strategic dimensions are not well understood<br />

by all. Commodity orientation, which still<br />

prevails, hinders a systems approach to understanding<br />

farmers’ circumstances under constrained environments.<br />

Traditional research sees the research findings<br />

or outputs, w<strong>here</strong>as PR views livelihood and<br />

positive environmental change as the product.<br />

Lack of support from management. Not enough senior<br />

researchers have experience in participatory research<br />

at research centers. Most researchers working<br />

with participatory approaches are young, are on “soft”<br />

money, and don’t have enough possibilities to stay.<br />

Problems with continuity and quality are the consequence.<br />

Turnover of scientists is high and this limits<br />

the building of social capital with farmers. The incentives<br />

or rewards for scientists to do farmer participatory<br />

research in the Consultative Group on <strong>International</strong><br />

Agricultural <strong>Research</strong> (CGIAR) and<br />

NARES is still very much based on the production of<br />

data and number of scientific publications instead of<br />

on impact and process results. <strong>Research</strong>ers have very<br />

little incentive to do participatory research, with the<br />

risk of becoming marginalized within the scientific<br />

community.<br />

Lack of staff with training and experience on PR. Very<br />

few researchers (scientists and NARES) are trained<br />

on farmer participatory research and facilitating skills<br />

on PVS and NRM (Linquist et al 2004, Singh et al<br />

2002).<br />

Availability of social scientists. Social scientists are<br />

still a very marginal group in CGIAR centers and are<br />

not available in the agricultural research institutions<br />

that are collaborating with <strong>IRRI</strong>. In this small group,<br />

most social scientists are economists, leaving a<br />

vacuum for other pressing social science issues. Further,<br />

the few social scientists available are located in<br />

nonagriculture-based universities and logistical arrangements<br />

for field work are a problem.<br />

Necessary conditions to sustain/institutionalize farmer<br />

participatory research<br />

<br />

<br />

At the farm/community level. Farmers themselves<br />

must be interested in the problem or issue, while scientists<br />

should have knowledge and the right attitudes<br />

and skills. T<strong>here</strong> should be NGOs or similar partners<br />

in or near the village to monitor experiments and assist<br />

farmers. T<strong>here</strong> should be clear objectives and protocols<br />

that all stakeholders agree on.<br />

<strong>Research</strong>. Participatory research requires both institutional<br />

and personal commitments on a sustainable<br />

basis. T<strong>here</strong> is a need to change the mind-sets of the<br />

scientists and research administrators engaged in onfarm<br />

trials. A strong interaction between social scientists<br />

and biological scientists with NARES is essential.<br />

Institutional arrangements need to be given due<br />

importance.<br />

Session 13: Farmers’ participatory approaches to facilitate adoption of improved technology 409


At the institutional level. The integration of PR approaches<br />

into the main research and training programs<br />

at <strong>IRRI</strong> should be supported by management. <strong>IRRI</strong>’s<br />

comparative advantage lies in the application of participatory<br />

research to strategic and pre-adaptive research<br />

such as participatory research methodologies<br />

for use by NARES, NGOs, and others and in the management<br />

of natural resources, plant breeding for<br />

rainfed environments, IPM, geographic information<br />

systems, decision support tools for soil management<br />

and land-use planning, validation of technologies for<br />

rainfed environments, etc. T<strong>here</strong> is a need to include<br />

farmer participatory research methods in <strong>IRRI</strong>’s and<br />

NARES’ training programs on conventional research.<br />

T<strong>here</strong> should also be a mechanism to strengthen linkages<br />

and partnerships with NGOs and extension institutions.<br />

Donors, which pressure for more farmer<br />

participation, should make a commitment to the issue<br />

with a long-term perspective and multiyear funding.<br />

Conclusions and issues to study<br />

Not all kinds of research can be participatory and PR is not a<br />

substitute for traditional or conventional research. Participatory<br />

research will be more effective if backed by formal research<br />

or conducted in parallel with on-station research. Farmer<br />

participatory research is increasingly necessary as one moves<br />

toward more diverse and complex environments. As one moves<br />

in this direction, recommendations cannot be broadly applied<br />

and adaptive research becomes increasingly important.<br />

Farmer participatory research can be an effective tool to<br />

motivate farmers to “experiment” with new concepts, innovations,<br />

ideas, etc. It is by far the most powerful tool for changing<br />

attitudes and beliefs, especially deeply entrenched attitudes<br />

(“more seed and fertilizer will give higher yields; all insects<br />

are bad and must be killed”).<br />

Farmer participatory research helps breeders consider<br />

farmers’ needs and preferences in setting their breeding goals<br />

for a target environment. PVS, as a complement to conventional<br />

breeding, provides farmers with opportunities to evaluate<br />

and select the genotypes they want in their own fields under<br />

their level of management before they are formally released<br />

in the national systems.<br />

The appropriate scale and level of representation of different<br />

interest groups, the methods chosen, and the extent of<br />

local participation in and control over the research process<br />

will depend on the project goals, available resources, and scope<br />

of the research as well as the rationale for using the participatory<br />

approach.<br />

Strategies and methods for involving farmers, local<br />

people, extension people, research administrators, etc., will<br />

have to be followed on a case-by-case basis and may differ for<br />

germplasm improvement and NRM. Moreover, more women<br />

farmers should be included in participatory research because<br />

410 <strong>Rice</strong> is life: scientific perspectives for the 21st century<br />

they are increasingly becoming the de facto farm managers<br />

and potential users of new technologies.<br />

While most PR activities are strong in initial diagnosis,<br />

planning, design, and testing, very few have had impact. Experience<br />

in scaling up should be documented.<br />

T<strong>here</strong> is a need to study the impact of participatory research<br />

and assess other enabling mechanisms such as matching<br />

funds to support partnerships among projects as well as<br />

resolutions, regulations (such as for the varietal release system),<br />

and official instructions given by departments and local<br />

governments.<br />

We also need to reflect on the following issues:<br />

To what extent should international research organizations<br />

and NARES be involved in scaling up to accelerate<br />

impact (Methodologies)<br />

What approaches to scaling up work and which do<br />

not (Methodologies)<br />

Do international research organizations have the<br />

“warm bodies” to do this with a reduction in nationally<br />

recruited staff and budget reductions (Institutionalization)<br />

How can we unite/complement formal traditional/conventional<br />

research and informal science (participatory<br />

research) (<strong>Research</strong>)<br />

How can international research organizations facilitate<br />

mainstreaming or institutionalizing participatory<br />

research by NARES How can the practice of PR be<br />

brought out of donor-driven project activities (Institutionalization)<br />

References<br />

Abedin Z. 2004. The emerging face of rice production in Bangladesh:<br />

direct wet seeding of rice using a plastic drum seeder to make<br />

rice production more profitable. Paper presented at the <strong>International</strong><br />

Symposium on Rainfed <strong>Rice</strong> Ecosystems: Perspectives<br />

and Potential, held at Indira Gandhi Agricultural University,<br />

Raipur, Chhattisgarh, India, 11-13 October 2004.<br />

Ashby J. 1997. What do we mean by participatory research in agriculture<br />

In: New frontiers in participatory research and gender<br />

analysis for technology development: proceedings. <strong>International</strong><br />

Seminar on Participatory <strong>Research</strong> and Gender Analysis<br />

for Technology Development, 1996. Cali (Colombia):<br />

Centro Internacional de Agricultura Tropical. p 15-22.<br />

Atlin G, Paris T, Courtois B. 2002a. Sources of variation in participatory<br />

varietal selection trials with rainfed rice: implications<br />

for the design of mother-baby trial networks. In: Bellon MR,<br />

Reeves J, editors. 2002. Quantitative analysis of data from<br />

participatory methods in plant breeding. Mexico, D.F.: Centro<br />

Internacional de Mejoramiento de Maíz y Trigo. p 36-43.<br />

Atlin G, Paris TR, Linquist B, Phengchang S, Chongyikangutor K,<br />

Singh A, Singh VN, Dwivedi JL, Pandey S, Cenas P, Laza M,<br />

Sinha PK, Mandal NP, Suwarno. 2002b. Integrating conventional<br />

and participatory crop improvement in rainfed rice. In:<br />

Whitcombe JR, Parr LB, Atlin GN, editors. Breeding rainfed<br />

rice for drought-prone environments: integrating conventional<br />

and participatory plant breeding in South and Southeast Asia.<br />

Proceedings of a DFID Plant Sciences <strong>Research</strong> Programme/<br />

<strong>IRRI</strong> Conference, 12-15 March 2002, <strong>International</strong> <strong>Rice</strong> <strong>Research</strong><br />

<strong>Institute</strong>, Los Baños, Laguna, Philippines. p 36-39.


Gregorio GB, Salam MA, Karim NH, Seraj ZI. 2004. Evaluation<br />

report of sub-project on development of high-yielding varieties<br />

for coastal wetlands of Bangladesh. Dhaka (Bangladesh):<br />

<strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>.<br />

Heong KL, Escalada M. 2003. Farmer participatory experiments in<br />

pest management. In: Pound B, Snapp S, McDougall C, Braun<br />

A, editors. Managing natural resources for sustainable livelihoods:<br />

uniting science and participation. London (UK):<br />

Earthscan Publications Ltd., and Ottawa (Canada): <strong>International</strong><br />

Development <strong>Research</strong> Centre. p 210-212.<br />

Huan NH, Thien LV, Chien HV, Heong KL. 2004. Farmers’ participatory<br />

evaluation of reducing pesticides, fertilizers and seed<br />

rates in rice farming in the Mekong Delta, Vietnam. Crop Prot.<br />

(In press.)<br />

Linquist B, Bounthanh K, Houemchitsavak S, Horne P. 2004. Upland<br />

research in Laos: experiences with participatory research<br />

approaches. In: Participatory research and development. Vol.<br />

3. CIP/UPWARD, Philippines. (In press.)<br />

Paris TR, Singh A, Luis J. 2001. Listening to male and female farmers<br />

in rice varietal selection: a case in eastern India. In: CIAT<br />

2000: an exchange of experiences from South and Southeast<br />

Asia. Proceedings of the <strong>International</strong> Symposium on Participatory<br />

Plant Breeding and Participatory Plant Genetic Resource<br />

Enhancement, Pokhara, Nepal, 1-5 May 2000. Cali<br />

(Colombia): Centro Internacional de Agricultura Tropical.<br />

Paris TR, Singh RK, Atlin GN, Sarkarung S, McLaren G, Courtois<br />

B, McAllister K, Piggin C, Pandey S, Sngh A, Singh BN,<br />

Singh ON, Singh S, Singh RK, Mandak NP, Prasad K, Sahu<br />

RK, Sahu VN, Sharma MK, Singh RKP, Thakur R, Singh<br />

NK, Chaudhary D, Ram S. 2002. Farmer participatory breeding<br />

and participatory varietal selection in eastern India: lessons<br />

learned. In: Whitcombe JR, Parr LB, Atlin GN, editors.<br />

Breeding rainfed rice for drought-prone environments: integrating<br />

conventional and participatory plant breeding in South<br />

and Southeast Asia. Proceedings of a DFID Plant Sciences<br />

<strong>Research</strong> Programme/<strong>IRRI</strong> Conference, 12-15 March 2002,<br />

<strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>, Los Baños, Laguna, Philippines.<br />

p 32-36.<br />

Singh RK, Paris T, Thakur R, Singh VP. 2002. Institutionalizing<br />

participatory plant breeding within the national research systems:<br />

issues and future challenges. Paper presented at the <strong>International</strong><br />

Symposium on Agronomy Conference in New<br />

Delhi. Organized by the Department of Extension, Indian<br />

Council of Agricultural <strong>Research</strong> (ICAR), New Delhi, India,<br />

November 2002.<br />

Notes<br />

Authors’ address: Social Sciences Division, <strong>International</strong> <strong>Rice</strong> <strong>Research</strong><br />

<strong>Institute</strong>, DAPO Box 7777, Metro Manila, Philippines,<br />

e-mail: t.paris@cgiar.org.<br />

A participatory approach for building sustainable ricefarming<br />

systems in the reclaimed farmland of Ogata, Japan<br />

Yoshimitsu Taniguchi and Satoru Sato<br />

We present <strong>here</strong> a case study using a participatory approach in<br />

the regional development of sustainable rice-farming systems<br />

in Ogata village in northeastern Japan. After Mr. Tozawa’s interesting<br />

report as a farmer, we would like to present, from a<br />

scientific point of view, several principles of participatory research<br />

derived from our experience with the development process<br />

for two contrasting technologies, organic and no-till, in<br />

Ogata. This presentation is based on the on-farm research we<br />

have carried out over the past 7 years in collaboration with<br />

farmers of Ogata. The theme of this research is rural development<br />

based on sustainable agriculture. As Mr. Tozawa said,<br />

Ogata is the largest single area of sustainable rice production<br />

in Japan, and Ogata farmers are very active in using new technologies<br />

of sustainable farming. These research experiences<br />

have taught us that participation and interactiveness are the<br />

keys to success in the development of new sustainable technologies,<br />

for three reasons.<br />

First, technologies for sustainability are much more<br />

knowledge-intensive than conventional chemical-based technologies<br />

that farmers need much more time to learn, experiment,<br />

and adapt them before they can decide when and how to<br />

use them. This can be seen in the difference between organic<br />

fertilizer and chemical fertilizer. When farmers use chemical<br />

fertilizer, they have to think only about the necessary quantity<br />

of fertilizer and just place it on the ground. The fertilizer works<br />

and dissolves soon. But, when they use organic fertilizer, they<br />

have to consider a wider variety of factors: how long will it<br />

take organic fertilizer to dissolve under the ground how much<br />

of it will accumulate and when and how will it work on plants<br />

The reason organic fertilizer requires farmers to think more is<br />

that it works on plants through much more complex interactions<br />

among soil, water, and microorganisms than chemical<br />

fertilizer. Organic fertilization is more difficult because it is<br />

more site-specific than chemical fertilization. The effect of<br />

fertilizer may differ from one site to another. Thus, organic<br />

farmers have to have much knowledge of soil science, plant<br />

nutrition, ecology, etc. No-till farming is also knowledge-intensive<br />

in a different way from organic farming. Pioneering<br />

farmers of Ogata have developed new technologies as partial<br />

technologies of no-till farming. These technologies include a<br />

special type of transplanting machine for no-till and controlledavailability<br />

fertilizer for seedlings. Thus, no-till farmers have<br />

to know much about the relationship between water permeability<br />

and the nature of soil, the most effective use of con-<br />

Session 13: Farmers’ participatory approaches to facilitate adoption of improved technology 411


trolled-availability fertilizer, and the cost-reducing effect of<br />

no-till and others.<br />

Second, since each sustainable agricultural technology<br />

is partial (not a total change of the production system), farmers<br />

need to make mutual adjustments to incorporate a new technology:<br />

sometimes modifying the technology to make it more<br />

compatible with their existing farm management, and sometimes<br />

modifying their management of other components to<br />

make them more compatible with the new technology. Farmers<br />

will use new technologies only when they reach the conclusion<br />

after experimentation that these are useful for their<br />

overall farm management. For instance, labor and agricultural<br />

machinery are important factors for mutual adjustments. One<br />

Ogata farmer doubled his farm size by purchasing extra farmland.<br />

He said he would be able to manage the farm of 30 ha<br />

with only labor of his family of four adults. Another Ogata<br />

farmer has been hesitating to begin no-till farming, mainly<br />

because he could not decide whether to make a new investment<br />

by purchasing a special transplanting machine for notill.<br />

He is afraid that he would not be able to repay the loan if<br />

the price of rice continues to decrease.<br />

Third, the innovation process of sustainable farming technologies<br />

is always accompanied by uncertainties: the effects<br />

of new technology are not well defined. Technical success does<br />

not necessarily mean economic rewards or social acceptance;<br />

short-term results may change existing long-term goals. These<br />

three types of uncertainty can be seen in the example of both<br />

organic and no-till farming. In organic farming, organic fertilizer<br />

is a cause of uncertainties. Its effects may differ according<br />

to weather conditions, for example. Especially during the period<br />

of seedlings, organic farmers are extremely sensitive as<br />

to whether organic fertilizer works properly. Even experienced<br />

farmers sometimes fail with seedlings using organic fertilizer.<br />

Then they have to rush to dispose of the failed soil and seeds,<br />

and to try again from the beginning. With no-till farming, a<br />

cause of uncertainty lies in the use of herbicide and chemical<br />

fertilizer. The present technological system of no-till farming<br />

requires the use of herbicide in early spring and after transplanting,<br />

and the use of chemical fertilizer as controlled-availability<br />

fertilizer. This means that rice grown by no-till farming<br />

is not regarded as “environmentally friendly” in the present<br />

market. So, farmers cannot expect a premium. As Mr. Tozawa<br />

said, this is the most important reason why no-till has not spread<br />

in Ogata.<br />

To avoid these uncertainties, farmers tend to take a “stepby-step”<br />

approach based on communication with other agents,<br />

within the community, in markets, and in the public sector. In<br />

the above example, as was reported by Mr. Tozawa, “establishing<br />

a study group and experimenting with new technologies<br />

with other farmers are the most common ways of solving<br />

problems.” T<strong>here</strong> are 40 or 50 groups of this kind, and a farmer<br />

often joins several study groups to learn various technologies<br />

and materials. It takes time for Ogata farmers to use a new<br />

technology, but, once they accept it, that technology spreads<br />

rapidly all over the village. The use of controlled-availability<br />

fertilizer is a good example. In 1998, it covered 1,214 ha, but<br />

the latest statistics indicate that it covered more than 3,000 ha<br />

in 2003. It is also common for other agents to be involved in<br />

this process. As Mr. Tozawa said, Ogata farmers sometimes<br />

invite researchers to learn about new technologies and materials.<br />

In some cases, retailers and consumers participate in technological<br />

innovation by encouraging farmers and inspecting<br />

soil conditions and residual pesticide with rice. A participatory<br />

approach parallels this natural process of farmers, and<br />

enables research and extension support agents in the public<br />

sector to interact with this process.<br />

Notes<br />

Authors’ addresses: Y. Taniguchi, Department of Bioresource Sciences,<br />

Akita Prefectural University; S. Sato, Department of<br />

Bioresource Sciences, Akita Prefectural University, 010-0195<br />

Nakano, Shimoshinjo, Akita City, Akita, Japan, e-mail:<br />

tani@akita-pu.ac.jp, ssatoru@akita-pu.ac.jp.<br />

<strong>Rice</strong> farmers’ participatory research has played a key role<br />

in implementing the System of <strong>Rice</strong> Intensification<br />

Dandu Jagannadha Raju<br />

West Godavari District is the rice bowl of Andhra Pradesh<br />

State and the kingpin of aquaculture in India. <strong>Rice</strong> farmers<br />

have enjoyed the fruits of the Green Revolution with the introduction<br />

of new high-yielding rice varieties starting with IR8.<br />

They reached a peak and have attained the highest rice yields<br />

in the state for more than two decades. Later hybrid rice varieties<br />

did not increase yield. The regular new high-yielding rice<br />

varieties became a ray of hope but have been disappearing<br />

because of one problem or another, and continued stagnated<br />

rice yields frustrated farmers and made them switch to horticultural<br />

crops and aquaculture. In view of the existing soil and<br />

climatic conditions, the majority were still forced to adjust to<br />

rice cultivation and its stagnated yields. The farmers’ entrepreneurial<br />

behavior motivated them to turn to a new technique<br />

such as the System of <strong>Rice</strong> Intensification (SRI). Yet, the initial<br />

field problems and laborious technological skills involved<br />

in it have slowed down its introduction. But, to the surprise of<br />

everyone concerned, including the scientists, the farmers’ ini-<br />

412 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Fig. 1. Farmers’ participatory research efforts have brought out new line markers and weeders to suit different situations for easy application<br />

of SRI technology.<br />

tiative in doing research in association with extension scientists<br />

with the new SRI technology in farmers’ own fields as<br />

well as at extension center farms helped to modify existing<br />

field situations and make them suitable for the new SRI technology.<br />

This has helped with the successful implementation of<br />

SRI in India.<br />

The SRI was first introduced in India during the 2003<br />

rainy season and it was simultaneously investigated at a university<br />

extension center such as the Krishi Vigyan Kendra<br />

(KVK), Undi, West Godavari District, and in farmers’ fields.<br />

Technologies were prescreened in association with selected<br />

farmer groups through discussion and interaction sessions. Participation<br />

of farmer groups was encouraged at different stages<br />

of crop growth. At the harvesting stage, yield profitability, the<br />

cost-benefit ratio, practicability, and likes and dislikes of farmers<br />

were assessed. Field days were conducted in farmers’ fields<br />

as well as at the extension center. Farmer conventions were<br />

organized, duly inviting resourceful farmers and those farmers<br />

who had already adopted the SRI technology. This helped<br />

with constructive interaction among the farmers and motivated<br />

others to adopt the technology on a large scale in the next season<br />

itself.<br />

Farmers as scientists have undertaken several experiments<br />

based on their own experiences. They themselves have<br />

evolved location-specific and cost-effective devices such as<br />

line markers and weeders. This has encouraged other farmers<br />

to modify accordingly. The findings reveal that real farmers’<br />

participation right from the introduction of technologies has<br />

made farmers modify technologies according to their situations,<br />

thus inventing needed implements such as markers. This<br />

has made it easy to adopt different and wider spacings in rice<br />

transplanting, and the weeders were easy to operate even in<br />

critical field situations. The collective approach of farmers<br />

made it easy to manage water properly. Though at the initial<br />

stages more laborers were needed for leveling and transplanting<br />

young seedlings, this gradually became standardized with<br />

less labor and speedy transplanting. The additional crop yield<br />

of 20–30% has encouraged farmers to adopt this system on a<br />

large scale in their fields.<br />

Farmers locally manufactured small implements such as<br />

markers and weeders to suit their field conditions. They have<br />

made several modifications and developed the best of them<br />

with their own efforts, such as ropes with beads, ropes with<br />

knots, bamboo sticks with nails, fixed line markers, adjustable<br />

markers, and, ultimately, the multipurpose liner, which is now<br />

mostly used by farmers because it easily marks lines, both vertical<br />

and horizontal, at the same time with less labor. Similarly,<br />

weeders were locally manufactured, such as cono weeders<br />

and rotary weeders with bearings, and a weeder with a mesh,<br />

etc. (Fig. 1).<br />

The farmers also struggled for effective water management<br />

practices in the delta region, which is a crucial step of<br />

SRI cultivation under delta situations. These management practices<br />

included making a small pit in one corner of the main<br />

rice plots and pumping out the water, making inner new and<br />

small bunds and deep alleyways at a 2-m interval, etc. The<br />

farmers also experimented with the SRI method using various<br />

varieties in order to find out the most suitable ones (Fig. 2).<br />

Farmer participatory research<br />

An innovative and enthusiastic farmer, Mr. B. Sudhakar Reddy<br />

of Akividu village of West Godavari District, is known for his<br />

realistic approach to rice cultivation. He successfully implemented<br />

the newly introduced SRI technique on 10 ha during<br />

the kharif and rabi 2003-04 seasons with varied combinations<br />

of different varieties and spacings, with careful water and weed<br />

management practices. He achieved higher yields with all varieties.<br />

He has proved that the SRI technology can easily be<br />

implemented in any field situation. He has obtained record<br />

yields as well as formed rice plots as rice gardens by using<br />

wider spacing at 50 × 50 cm. He has also explained the technology<br />

to hundreds of farmers and correlated it to other farmers’<br />

situations. He has convinced others to adopt it in their<br />

Session 13: Farmers’ participatory approaches to facilitate adoption of improved technology 413


Fig. 2. Location-specific water management practices and different varieties tested by farmers themselves for successful implementation<br />

of SRI technology.<br />

own fields. He has become a role model for others to emulate<br />

to adopt the SRI technique easily.<br />

He himself designed an adjustable marker and used it<br />

for marking lines. This has helped him to follow different spacings<br />

(i.e., 25 × 25, 50 × 25, 50 × 50 cm).<br />

Weeding with a specially made rotary weeder was done<br />

at 7-d intervals to check further weed growth and to incorporate<br />

weeds in the soil. He could locally manufacture a weeder<br />

in collaboration with other farmers.<br />

As t<strong>here</strong> was a drainage problem in his field, he made a<br />

small ditch at one corner of his field and drained the excess<br />

water from that field into the ditch and pumped the water outside<br />

with the help of a small oil engine. Deep alleyways and<br />

small bunds were made to drain out excess water.<br />

Small farmer Sri Tirupathi Srinivas has 1 ha of land. He<br />

belongs to Ballipadu village in Attili Mandal of West Godavari<br />

District. He has cultivated paddy under the SRI method on<br />

about 0.5 ha. KVK, Undi, provided paddy seed and technical<br />

guidance to him at regular intervals. He attended all training<br />

classes conducted on SRI technology at KVK. He followed all<br />

the water and weed management practices regularly. As rats<br />

were the major problem in that area, he installed a polythene<br />

sheet all around the field, erecting it to 1-m height. The paddy<br />

plants produced a high number of tillers and he got higher<br />

yields, with 3,000 kg ha –1 more yield with SRI technology than<br />

with the conventionally transplanted variety MTU 1071. During<br />

winter 2004, he followed the SRI technology on his entire<br />

farm of 1 ha by joining with his brothers and he motivated 8<br />

other young farmers of his village to adopt this new technology.<br />

He reaped the highest yields in the district.<br />

Young and dynamic farmer M. Ramesh from Kaikaram<br />

village of Unguturu Mandal of West Godavari District struggled<br />

with weeding practices. He modified different weeders to suit<br />

his conditions and found a way to overcome his chronic weeding<br />

problem.<br />

Large farmer Sri N.V.R.K. Raju belongs to<br />

Gummampadu village of West Godavari District. Motivated<br />

by the KVK’s SRI demonstrations during kharif 2003, he<br />

implemented SRI on 40 ha during rabi 2003-04 on what was<br />

originally a fish pond. When experiencing difficulty of paddy<br />

cultivation under an acute water shortage, he was forced to<br />

switch to SRI cultivation after learning about it. He modified<br />

several weeders and line markers to suit his field conditions<br />

apart from a channelized water management system. He<br />

pumped out the excess water in the field by using an oil engine.<br />

He was the first farmer to cultivate paddy under SRI in a<br />

larger area. He reaped a good harvest and motivated several<br />

others to follow this new technique.<br />

Many of these research efforts of a group of farmers in<br />

their own fields have motivated several other farmers of the<br />

same village and neighboring villages to join in sharing their<br />

innovative efforts. This type of farmers’ innovative research<br />

has become an eye opener even to our own researchers. This<br />

clearly shows that farmers are the real initiators of their own<br />

research efforts; hence, if farmers are made partners in doing<br />

research in agriculture, a better outcome will be possible.<br />

Notes<br />

Author’s address: Acharya N.G. Ranga Agricultural University,<br />

Andhra Pradesh, India, training organizer and head, Krishi<br />

Vigyan Kendra, Undi, West Godavari District, Andhra<br />

Pradesh, India, e-mail: Drdandu_jraju@yahoo.co.in.<br />

414 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Wrap-up of Session 13<br />

Session 13 introduced several innovations in the session organization,<br />

applying the principles of participatory research to the<br />

setting. First, presenters were selected to include diverse stakeholders<br />

in agricultural research, including the representative of a<br />

farmers’ organization working with a university, and the representative<br />

of a nongovernmental organization working with a research<br />

station. Second, participants were given the opportunity<br />

to ask questions after each presentation. Third, rather than a<br />

panel of experts, a small group discussion was used, giving all<br />

participants an opportunity to contribute to the output of the session.<br />

Summary of papers presented<br />

Three papers illustrated how multiple stakeholders with different<br />

interests and strategies can contribute to participatory research.<br />

F. Tozawa provided the perspective of farmers from the Ogata<br />

area in Akita Prefecture and Y. Taniguchi the perspective of researchers<br />

at Akita Prefectural University on collaborative research<br />

to reduce the environmental “footprint” from rice production in<br />

northwestern Japan. F. Tozawa showed examples of how farmers’<br />

input was essential to make no-till and organic technology<br />

usable by farmers. He also explained how technology needs to<br />

enable farmers to produce what consumers want, and thus why<br />

consumer participation is essential in technology development.<br />

Y. Taniguchi explained how farmers are not users of technology,<br />

but the central agents in innovation that produces technology. A<br />

participatory approach enables researchers to enter the farmers’<br />

innovation process. In an example from another part of Japan, Y.<br />

Iwabuchi explained how farmers, researchers, and wildlife preservation<br />

organizations jointly developed winter-flooded rice-field<br />

technology with monitoring of wildlife populations. Farmers themselves<br />

developed an improved method for monitoring frog diets.<br />

Two papers presented results of how farmers assessed researcherdeveloped<br />

technologies to determine if they would work successfully<br />

under their conditions. B. Bagchi explained how farmers<br />

tested the leaf color chart technology in West Bengal, India. This<br />

technology enabled farmers to save on fertilizer cost with no reduction<br />

in yield. F. Palis reported how farmers in the Philippines<br />

tested controlled irrigation, which alternates wetting and drying<br />

of paddy fields. Farmers determined that this technology saved<br />

water and cost with no reduction in yield. In both cases, the trial<br />

results provided a farmer-based verification for community-based<br />

extension to other farmers and villages.<br />

Two papers presented methods for going beyond traditional<br />

farmer participatory research in both space and time. G. Trébuil<br />

provided an introduction to companion modeling, an approach<br />

that combines participatory role-playing by multiple stakeholders<br />

with agent-based computer simulations using agroecosystems,<br />

biophysical, and socioeconomic data to collectively assess scenarios<br />

of changes. As seen in an example from the northern Thai-<br />

land highlands, this method can enable farmers and researchers<br />

to explore future change options over a longer time span and<br />

wider area. It can also facilitate intra- and intervillage communication<br />

for developing and testing options for change at the watershed<br />

level, as seen in a second example on irrigation water<br />

management from Bhutan. Nguyen De presented 10 years of<br />

results of participatory plant breeding and participatory varietal<br />

selection in Vietnam. An average of 3.5 varieties have been selected<br />

and used by 29 communities through this approach.<br />

T. Paris and Z. Abedin concluded the presentations with a<br />

review of <strong>IRRI</strong>’s participatory approaches. These have moved from<br />

contractual and consultative modes, in which researchers lead<br />

and farmers respond, to the collaborative mode, in which farmers<br />

and researchers are partners. Then, as participatory research<br />

becomes collegial, farmers have acquired the ability to begin research<br />

on their own and seek out researchers to support their<br />

own efforts. The authors concluded by pointing out difficulties in<br />

institutionalizing participatory research, and offered future directions<br />

to overcome these difficulties. These include<br />

Changing the “mind-set” of scientists and research administrators<br />

to see that participatory research complements<br />

conventional research, providing a mechanism<br />

for scientists to determine research needs and understand<br />

how farmers change technologies.<br />

Recognizing that participatory research has a higher<br />

start-up cost but shortens farmer decision time in making<br />

change, and thus is cost-effective over the technology<br />

generation process from needs identification to widespread<br />

farmer change.<br />

Including participatory research methods in training programs<br />

of both <strong>IRRI</strong> and national programs.<br />

Moving participatory research beyond donor-driven,<br />

project-based activities to become an integral part of<br />

national programs in technology generation, validation,<br />

and extension.<br />

Participant contributions: methods<br />

for improving participatory research approaches<br />

After the presentations, participants were divided into two groups,<br />

each organized around a series of questions. Each small group<br />

discussed the questions, selected key points, and summarized<br />

them in slides or transparencies. Then, the two groups came<br />

back together, each group presented its summary, and members<br />

of the other group asked questions and commented.<br />

Group A’s topic was “Working with farmers as researchers.”<br />

The group considered three questions and offered the following<br />

guidelines. In these guidelines, information in parentheses<br />

is taken directly from the groups’ report, while explanation of<br />

specific terms used in participatory research has been added in<br />

brackets for readers of this summary.<br />

Session 13: Farmers’ participatory approaches to facilitate adoption of improved technology 415


Farmers’<br />

advantages<br />

<strong>Research</strong>ers’<br />

advantages<br />

Goals<br />

l cost reduction<br />

l premium quality<br />

l environment<br />

Farmer conditions<br />

<strong>Research</strong> must be interesting<br />

(for example, use role playing)<br />

Goal and<br />

hypothesis<br />

Fusion of<br />

l quantifiable goals<br />

l farmer participation<br />

in goal setting<br />

Methods<br />

l broadening scope of ideas to test<br />

l verifiable methodologies<br />

Fig. 1. Advantages (boxes) of participatory research for farmers and researchers (ovals).<br />

1. What methods can enable farmers to contribute as researchers<br />

in the field to experimentation for technology<br />

development<br />

assessment and prioritization of needs and opportunities<br />

matching appropriate interventions [innovations to<br />

test]<br />

<br />

<br />

<br />

rapport building<br />

assessment of what farmers have done so far (giving<br />

recognition to farmers’ own efforts and building<br />

on what they are doing already)<br />

technology introduction, farmer volunteerism, and active<br />

farmer/researcher partnership (researchers may<br />

supply critical inputs but risks should be shared)<br />

2. What mechanisms and types of farmer-researcher interaction<br />

can enable farmers to contribute their own<br />

ideas for scientific evaluation, rather than simply involving<br />

farmers to provide their evaluation of ideas from<br />

scientists<br />

consensus<br />

rapport building (cultural sensitivity)<br />

encouraging feedback between partners<br />

using community communication structures<br />

undertaking direct observation (in the field) and participant<br />

observation [researchers joining with farmers<br />

in carrying out trials in the field]<br />

3. How can farmer participation help biological scientists<br />

do better and more relevant science<br />

scientists gain access to farmers’ knowledge<br />

scientists learn from farmers (who have a broader<br />

perspective of the farming system)<br />

widens scientists’ horizons<br />

enables scientists to be practically oriented (praxis),<br />

thus refining technology<br />

ensures appropriate technology development<br />

Group B’s topic was “Broadening participation socially and<br />

spatially.” Before considering broadened participation, the group<br />

first summarized its understanding of the advantages of farmers<br />

and researchers participating together in on-farm research. Farmers<br />

bring their goals and conditions, while researchers bring methods<br />

that can help farmers assess new ways to achieve those<br />

goals. The results are quantifiable goals and hypotheses developed<br />

together (Fig. 1), leading to a shared, common representation<br />

of the problem to be examined and solved through farmerresearcher<br />

collaboration.<br />

The group then considered two questions for broadening<br />

participation:<br />

1. How can nonfarmer stakeholders (wholesalers, input<br />

suppliers, local government, NGOs, etc.) contribute to<br />

technology development<br />

Figure 2 shows the advantages for each type of stakeholder.<br />

Business stakeholders can obtain concrete advantages<br />

that will improve their business, while participatory<br />

research can be a social laboratory for government<br />

to learn about the actual and potential effects of<br />

policies. Consumers can have a better chance of obtaining<br />

the type of rice (or other agricultural product) of<br />

the quality they desire.<br />

2. How can technology development go beyond a few sites<br />

of intensive farmer-researcher interaction, without losing<br />

participation<br />

Several types of processes were proposed (Fig. 3). One<br />

process is based on farmers becoming trainers to enable<br />

other farmers to undertake participatory research<br />

on their own, and participatory research spreading as a<br />

method spontaneously among communities. Two especially<br />

useful tools for this process are (1) study tours by<br />

communities new to the process to communities that<br />

already have experience and results through participatory<br />

research, and (2) farmer field schools to develop<br />

site-specific field management techniques through joint<br />

observation by farmers and researchers. The latter<br />

method is well known for its successes in integrated<br />

pest management (IPM), but its use should be broad-<br />

416 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Local<br />

government<br />

Farmers and<br />

participatory<br />

research<br />

Input<br />

suppliers<br />

l<br />

l<br />

Can know effect of a policy<br />

Useful for democracy<br />

l Learn farmers’ needs<br />

- shift business strategy<br />

l Social responsibility as member<br />

of community<br />

- feel more useful<br />

Wholesalers<br />

Large<br />

retailers<br />

Niche<br />

retailers<br />

Manufacturers<br />

See their clientele<br />

Have long food chain<br />

l gain platform of communication<br />

with distributors and consumers<br />

Consumers<br />

Determine market size for investment<br />

l<br />

Possibility of new high-quality rice<br />

Fig. 2. Types of stakeholders (ovals) and advantages (boxes) of participatory research for each.<br />

Study tour<br />

Farmers<br />

trained<br />

to be trainers<br />

Farmers field school<br />

(originally IPM)<br />

IBM (integrated<br />

biological management)<br />

Other communities<br />

Retail<br />

Input<br />

suppliers<br />

Other<br />

Pilot community<br />

Knowledge<br />

communities:<br />

workshops,<br />

information<br />

b<br />

technologies*<br />

Media<br />

l soap opera<br />

l “3 reductions,<br />

3 gains”<br />

Spontaneous interaction<br />

Message should be simple<br />

*GIS, generic model<br />

tailor each stakeholder can access<br />

Web-based e-participation and e-learning<br />

Fig. 3. Scaling-up process.<br />

Session 13: Farmers’ participatory approaches to facilitate adoption of improved technology 417


ened to integrated biological management (IBM). A second<br />

process can grow out of the first, in the formation<br />

of information communities. These can use workshops<br />

and, w<strong>here</strong> possible, information technology, to develop<br />

models that can be tailored to the needs of many types<br />

of stakeholders, both farmers and nonfarmers. These<br />

can provide a basis for e-participation and e-learning.<br />

Finally, results from participatory research can be used<br />

by extension through improved media approaches. These<br />

should use formats that farmers enjoy, such as soap<br />

operas (successful in the Philippines) and simple messages,<br />

such as “3 reductions, 3 gains” (successful in<br />

Vietnam).<br />

418 <strong>Rice</strong> is life: scientific perspectives for the 21st century


SESSION 14<br />

Potential for diversification in rice-based<br />

systems to enhance rural livelihoods<br />

CONVENER: M. Hossain (<strong>IRRI</strong>)


Agricultural diversification in Asia: opportunities<br />

and constraints<br />

Prabhu Pingali<br />

Rapid economic and income growth, urbanization, and globalization<br />

are leading to a dramatic shift of Asian diets away<br />

from staples and increasingly toward livestock and dairy products,<br />

vegetables and fruit, and fats and oils. The tendency for<br />

per capita rice consumption to decline with income growth<br />

and with urbanization has been widely documented in the literature<br />

(Ito et al 1989, Huang and David 1993). FAO projections<br />

indicate that the per capita consumption of rice will level<br />

off by 2015 and start to decline by 2030 (FAO 2003).<br />

The rice sector in Asia is facing the dual challenge of<br />

sustaining high rates of rice productivity growth while transforming<br />

itself from a subsistence-oriented monoculture system<br />

to a diversified market-oriented system. This paper examines<br />

the scope for the diversification of rice-based farming in<br />

Asia. Economic, agro-climatic, and technological constraints<br />

to the commercial transformation of subsistence rice systems<br />

are identified. Priorities for research, and the primary components<br />

of a policy agenda, are described.<br />

The diversification of rice-based farming systems<br />

A recent FAO/World Bank study on farming systems and poverty<br />

suggested that diversification is the single most important<br />

source of poverty reduction for small farmers in South and<br />

Southeast Asia (FAO and World Bank 2001). The three most<br />

important systems described in the study are all rice-based<br />

farming systems (see Table 1): the tropical lowland rice sys-<br />

tem, the rice-wheat system, and the rainfed uplands. They account<br />

for about 80% of the agricultural population and some<br />

50% of the total agricultural area in Asia. The tropical lowland<br />

and rice-wheat systems are the dominant sources of rice<br />

supply in Asia. These systems witnessed rapid productivity<br />

growth during the Green Revolution and their productivity<br />

continues to be high in the post-Green Revolution period. Yet,<br />

pressure to diversify out of rice is also the greatest in these<br />

systems, primarily because of low returns to rice relative to<br />

high-value alternatives such as vegetables (Pingali et al 1997).<br />

The feasibility and cost of substituting other crops vary<br />

across all three farming systems. The flexibility of farmers to<br />

respond to the changing relative prices and relative profitability<br />

in their crop choice decision-making can be described in<br />

terms of the level of investments (both physical and human<br />

capital) required in switching from rice to nonrice crops and<br />

vice versa. Flexibility is low during the rainy season for the<br />

tropical lowlands and the rice-wheat zone because the drainage<br />

costs for growing nonrice crops can be prohibitive (Pingali<br />

et al 1997). Upland areas, however, can oscillate between rice<br />

and nonrice crops with minimum additional investment.<br />

Access to markets and the relative prices of rice and<br />

nonrice crops, especially horticulture, are additional determinants<br />

of diversification. Although roads and market places are<br />

important, proximity to urban areas expands the range of<br />

nonrice diversification options, especially for fresh produce.<br />

Table 1. Main rice-based farming systems in Asia.<br />

Land area Agricultural<br />

Farming system Amount (% of region) population Principal livelihoods<br />

(% of region)<br />

Tropical lowland rice 11 32<br />

Agricultural population 604 Irrigated and rainfed rice, vegetables,<br />

Cultivated area 93 legumes, off-farm activities<br />

Irrigated area 42<br />

<strong>Rice</strong>-wheat 9 22<br />

Agricultural population 416 Irrigated rice; wheat, vegetables, livestock<br />

Cultivated area 93 including dairy, off-farm activities<br />

Irrigated area 158<br />

Rainfed uplands 30 26<br />

Agricultural population 636 Cereals, legumes, fodder, livestock, horticul-<br />

Cultivated area 189 ture, seasonal migration, and off-farm ac-<br />

Irrigated area 38 tivities<br />

Source: Tables 5.1 and 6.1 in FAO and World Bank (2001).<br />

Note: Population figures are in millions, area figures in million hectares.<br />

420 <strong>Rice</strong> is life: scientific perspectives for the 21st century


During the wet season, rice will continue to be the dominant<br />

source of income in all but upland environments. In the<br />

irrigated lowland rice and rice-wheat systems, dry-season rice<br />

and/or wheat will continue to be the major source of income.<br />

Areas with good market access and those near urban centers<br />

will increasingly diversify to nonrice crops and vegetable production.<br />

Dry-season cropping activities in rainfed areas are<br />

limited because of technical problems related to timely and<br />

effective crop establishment, limited moisture (or excessive<br />

moisture in some cases), and generally modest or high yield<br />

instability. Off-farm activities are often more dependable<br />

sources of income, suggesting that dry-season cropping intensities<br />

would remain low even if technical problems in crop<br />

production were solved.<br />

Diversification constraints<br />

Diversification out of rice is constrained by market availability<br />

and size, land suitability and rights, irrigation infrastructure,<br />

and labor supply. W<strong>here</strong> output demand is relatively elastic,<br />

the returns from investments in land, technology, and time<br />

spent in learning about new crops are relatively higher.<br />

Diversification and risk<br />

Diversification from a rice-monoculture system to a nonrice<br />

crop system could lead to increased variability in farm household<br />

income, which basically comes from yield or price fluctuations.<br />

Moreover, the diversification “start-up” phenomenon,<br />

of high prices for several seasons leading to oversupply and a<br />

consequent collapse of prices, is all too common. This can be<br />

countered by measures to expand the market by lowering transaction<br />

costs, improving external linkages, or providing storage<br />

and processing technologies. Effective rural financial institutions<br />

will also assist in risk spreading and in the sharing of<br />

the benefits of commercialization more widely across the community<br />

and region.<br />

Land suitability and land rights<br />

The ability to profitably convert rice lands to nonrice crops is<br />

constrained by the drainage requirements for lowlands and<br />

erosion control investments in uplands. It is important to understand<br />

that not all lands can be converted to nonrice production.<br />

Even for lands that can be converted, substantial investments<br />

in land improvement need to be made to sustain the<br />

long-term productivity and profitability of nonrice crop production.<br />

Investments in land improvement are likely to be made<br />

only w<strong>here</strong> secure rights to land exist.<br />

In upland areas, w<strong>here</strong> market access is good, the profitability<br />

of diversified field crop production on soils not highly<br />

susceptible to erosion is high. For soils susceptible to erosion,<br />

profitability of field crop production is determined by the level<br />

of erosion control investments. W<strong>here</strong> such investments are<br />

high, tree crops may be a more viable option than field crops,<br />

particularly when field crop production has allowed land degradation<br />

to occur. In upland areas with poor market access, the<br />

returns from diversification out of subsistence rice production<br />

are limited in areas with either type of soil.<br />

Farmers’ interest in erosion control measures is directly<br />

related to land values and market access and is conditional on<br />

the availability of suitable technologies. Secure rights to land<br />

create the incentives farmers need to invest in land improvements<br />

that conserve and increase the long-term productivity<br />

growth that can be induced by the start of commercialization.<br />

Irrigation infrastructure<br />

Many observers have argued that existing irrigation systems<br />

constrain diversification because of the rigid designs of infrastructure<br />

and inflexible water delivery systems (Schuh and<br />

Barghouti 1988). It is argued that this inflexibility prevents<br />

appropriate allocation of water to nonrice crops, thus limiting<br />

farmers to rice monoculture. Based on these arguments, technology-based<br />

solutions to diversification within irrigation systems<br />

are advocated, mainly capital investment in improved<br />

conveyance, diversion, and drainage systems.<br />

An alternative argument would be that the failure to diversify<br />

within irrigation systems is the result of incentive failures<br />

resulting from the centralized allocation of unpriced irrigation<br />

water. Policies that establish markets in tradable water<br />

rights could establish incentives to economize on water and<br />

choose less water-intensive crops (in the dry season), by inducing<br />

water users to consider the full opportunity cost of water<br />

(Rosegrant et al 1995). The establishment of transferable water<br />

rights can provide maximum flexibility in responding to<br />

changes in crop prices and water charges as demand patterns<br />

and comparative advantage change and diversification of cropping<br />

proceeds (Rosegrant and Binswanger 1994).<br />

Labor supply<br />

Does diversified cropping increase labor requirements Yes;<br />

relative to rice, the per hectare labor requirements for onions,<br />

vegetables, and other high-value crops are substantially higher.<br />

Given the higher labor requirements for cropping and drainage,<br />

nonrice crops on irrigated lands are grown on extremely<br />

small plots, in general about a fourth of the rice area.<br />

In addition to crop labor requirements, the supervision<br />

time required from the farmer is also significantly higher: this<br />

may be the dominant labor constraint to high-value nonrice<br />

crop production given the highly inelastic nature of management<br />

labor available in the farm household compared to hired<br />

labor augmented by seasonal migrants.<br />

Implications for research<br />

<strong>Research</strong> should focus on providing farmers with the flexibility<br />

to make crop choice decisions and to move relatively freely<br />

among crops.<br />

Both substantial crop-specific research and system-level<br />

research will be required to provide farmers with flexibility of<br />

crop choice. Crop-specific research includes increases in yield<br />

potential, shorter duration cultivars, improved quality charac-<br />

Session 14: Potential for diversification in rice-based systems to enhance rural livelihoods 421


teristics, and greater tolerance of pest stresses. System-level<br />

research includes land management and tillage systems that<br />

allow for shifts of cropping patterns in response to changing<br />

incentives and farm-level water management systems that can<br />

accommodate a variety of crops within a season. Also important<br />

at the system level is research on the carryover effect of<br />

inputs and management practices across crops, for instance,<br />

high insecticide applications or the effects of intensification in<br />

terms of prolonged water saturation, the buildup and carryover<br />

across crops of pest populations, rapid depletion in soil micronutrients,<br />

and changes in soil organic matter that could lead<br />

to reduced productivity of rice monoculture systems over the<br />

long term.<br />

Given growing populations and income-induced demand<br />

for increased cereal consumption, t<strong>here</strong> continues to be a strong<br />

need to seek higher productivity levels for the staple cereals.<br />

The need to increase the productivity of cereals is higher the<br />

greater the diversion of high-potential irrigated lands to<br />

noncereal pursuits.<br />

Agenda for a food and agricultural policy<br />

Commercialization trends require a paradigm shift in agricultural<br />

policy formulation and research priority setting. The relevant<br />

development paradigm for the 21st century is one of<br />

food self-reliance, in which countries import a part of their<br />

food requirements in exchange for diverting resources out of<br />

subsistence production. Agricultural policy should emphasize<br />

maximizing farm household income rather than generating food<br />

surpluses.<br />

Governments have a difficult task to perform. On the<br />

one hand, continued food security needs to be assured for populations<br />

that are growing in absolute terms; on the other hand,<br />

research and infrastructural investments need to be made for<br />

diversification out of the primary staples. As Timmer (1992)<br />

stated, “Ultimately, the process of rural diversification must<br />

be consistent with the longer-run patterns of structural transformation.”<br />

The process of agricultural diversification should not be<br />

expected to be frictionless. Significant equity and environmental<br />

consequences can arise in the short to medium term unless<br />

appropriate policies are followed. Long-term strategies to facilitate<br />

a smooth transition to commercialization include investment<br />

in rural markets, transportation and communication<br />

infrastructure to facilitate integration of the rural economy, crop<br />

improvement research to increase productivity, and crop management<br />

and extension to increase farmers’ flexibility and reduce<br />

possible environmental problems from high input use;<br />

and establishment of secure rights to land and water to reduce<br />

risks to farmers and provide incentives for investment in sustaining<br />

long-term productivity.<br />

References<br />

FAO. 2003. World agriculture: towards 2015/2030. London (UK):<br />

Earthscan Publications Limited.<br />

FAO and World Bank. 2001. Farming systems and poverty: improving<br />

farmers’ livelihoods in a changing world. Rome and Washington,<br />

D.C.: FAO and World Bank.<br />

Huang J, David CC. 1993. Demand for cereal grains in Asia: the<br />

effect of urbanization. Agric. Econ. 8:107-124.<br />

Ito S, Peterson W, Grant W. 1989. <strong>Rice</strong> in Asia: Is it becoming an<br />

inferior good Am. J. Agric. Econ. 71:32-42.<br />

Pingali PL, Hossain M, Gerpacio RV. 1997. Asian rice bowls: the<br />

returning crisis Wallingford (UK): CAB <strong>International</strong>.<br />

Rosegrant MW, Binswanger H. 1994. Markets in tradable water<br />

rights: potential for efficiency gains in developing country<br />

irrigation. World Dev. 22:1613-1625.<br />

Timmer CP. 1992. Agriculture and economic development revisited.<br />

Agric. Syst. 40:21-58.<br />

Notes<br />

Author’s address: Director, Agricultural and Development Economics<br />

Division, FAO, United Nations, Rome, Italy.<br />

Consequences of technologies and production<br />

diversification for the economic and environmental<br />

performance of rice-based farming systems in East<br />

and Southeast Asia<br />

Huib Hengsdijk, Marrit van den Berg, Reimund Roetter, Wang Guanghuo, Joost Wolf, Lu Changhe, and Herman van Keulen<br />

<strong>Rice</strong>-based ecosystems in East and Southeast Asia are being<br />

challenged by the simultaneous requirements for more diversified<br />

products (Hossain 1998), increased productivity, and<br />

reduced environmental impact (Dobermann et al 2004). Location-specific<br />

conditions, such as access to labor and product<br />

markets, and biophysical conditions determine the potential<br />

for and constraints to diversification, adoption of technological<br />

innovations, and a productivity increase in such systems.<br />

The interrelated issues at stake in rice-based ecosystems are<br />

complex and require multidisciplinary research methods in<br />

which knowledge and information from different disciplines<br />

are integrated and synthesized. Farm household modeling<br />

422 <strong>Rice</strong> is life: scientific perspectives for the 21st century


(Singh et al 1986) as applied within the project “Integrated<br />

Resource Management and Land-use Analysis” (IRMLA) is<br />

one of such methods.<br />

Here, a farm household model is presented to study the<br />

performance of two household types differing in off-farm employment<br />

opportunities. The aim is to identify the scope for<br />

development for both types of households, taking into account<br />

multiple economic, social, and environmental objectives (such<br />

as increasing income and minimizing environmental impacts<br />

of agricultural activities). Pujiang County in Zhejiang Province,<br />

China, is used as a case study area for development and<br />

application of the model.<br />

Description of Pujiang<br />

Pujiang County is located in the center of Zhejiang Province,<br />

about 100 km southwest of the provincial capital Hangzhou,<br />

which offers ample off-farm employment opportunities. Despite<br />

the declining rice cultivation area in Pujiang, single and<br />

double rice-cropping systems are still the predominant agricultural<br />

land-use activities. About 57% of the 18,000 ha of<br />

cultivated land consists of rice paddies, while the remainder is<br />

used for upland crops, including different types of vegetables<br />

and fruits.<br />

Methodology<br />

The methodology applied has two major model components:<br />

(1) a farm household model based on linear programming techniques<br />

(Singh et al 1986) and (2) a technical coefficient generator<br />

called TechnoGIN (Ponsioen et al 2003) for quantifying<br />

input-output relations of the various production activities.<br />

The farm household model selects land-use options from a<br />

range of alternatives generated with TechnoGIN, while maximizing<br />

farm income subject to certain boundary conditions<br />

and restrictions. In this study, we identify two types of households<br />

that differ only in off-farm employment opportunities<br />

providing extra income to the household.<br />

TechnoGIN<br />

TechnoGIN is a generic expert tool for integrating different<br />

types of information on crop production and generating inputs<br />

and outputs of cropping systems. Based on soil, crop, and technology<br />

characteristics, TechnoGIN allows the characterization<br />

of specified cropping systems in terms of their relevant inputs<br />

and outputs, such as yield, crop residues, nutrient and biocide<br />

use, and labor requirements. Quantification of input-output<br />

relationships is based on the interpretation of survey data for<br />

representative cropping systems. TechnoGIN can also be applied<br />

for producing information that is often not available from<br />

surveys, such as losses of nutrients to the environment and the<br />

environmental impact of biocides.<br />

Farm household model<br />

The model accounts for the main characteristics of farm households<br />

in Pujiang: (1) a high labor/land ratio, (2) limited availability<br />

of financial capital, and (3) increasing opportunities<br />

for off-farm employment. The model maximizes household<br />

income from crop production and off-farm income, subject to<br />

the availability of land and family labor, required self-sufficiency<br />

in rice, access to working capital and off-farm employment,<br />

available agricultural technology, and market prices.<br />

Labor and financial balances are computed per 10-day period<br />

and are key constraints in our simulations.<br />

A major constraint to the adoption of new crops and<br />

improved technologies is the limited availability of working<br />

capital. Increasing employment opportunities in the nonfarm<br />

sector can alleviate this constraint, as the resulting income can<br />

be used to purchase inputs for crop production. We illustrate<br />

this process by distinguishing two farm households in this study<br />

that differ only with respect to their access to off-farm employment.<br />

The first household (HH1) has one family member<br />

(out of three) that is employed full-time in the nonfarm sector<br />

at a wage rate double the cost of hiring an agricultural laborer,<br />

that is, 5 versus 2.5 RMB per hour. The other household (HH2)<br />

uses available labor only on its own farm. Both households<br />

have a working capital of 1,000 RMB and a farm size of 0.4<br />

ha.<br />

Using the farm household model, we analyzed the following<br />

four scenarios:<br />

1. Reference. This represents the actual situation in<br />

Pujiang in which most farmers select cultivation of<br />

double or single rice systems.<br />

2. Technological innovations in rice cultivation. In this<br />

scenario, the same rice production systems are available<br />

as in the reference scenario, but now using technologies<br />

aimed at increasing crop productivity and<br />

reducing fertilizer use, through the use of hybrid rice<br />

varieties and site-specific nutrient management<br />

(SSNM) (Guanghuo et al 2004).<br />

3. Vegetables. In addition to rice cropping systems, vegetable-based<br />

cropping systems are available in this<br />

scenario.<br />

4. Vegetable prices. Here, the price ratio between rice<br />

and vegetables is changed through a stepwise reduction<br />

in vegetable prices to a minimum of 10% of the<br />

prices used in the vegetables scenario.<br />

Results<br />

Reference<br />

Both households select double rice systems that are more profitable<br />

than single rice. The economic performance of HH1 is<br />

much better than that of HH2 because of income earned through<br />

off-farm employment (Table 1). Since off-farm employment is<br />

more remunerative than farming activities, HH1 hires a limited<br />

amount of external labor during the peak period around<br />

harvesting of early rice and transplanting of late rice. T<strong>here</strong>fore,<br />

on-farm income of HH1 is slightly lower than that of<br />

HH2.<br />

Session 14: Potential for diversification in rice-based systems to enhance rural livelihoods 423


Table 1. Results (in units per year) of the reference, technological innovation, and vegetables scenarios<br />

for farm households HH1 and HH2.<br />

Reference Technological Vegetables<br />

Item Unit innovation<br />

HH1 HH2 HH1 HH2 HH1 HH2<br />

On-farm income RMB a 2,996 3,076 3,593 3,712 17,477 10,083<br />

Off-farm income RMB 14,400 0 14,400 0 14,400 0<br />

On-farm labor Month 88 92 109 117 208 132<br />

Off-farm labor Month 360 0 360 0 360 0<br />

Hired labor Month 4 0 4 0 112 36<br />

N losses kg N ha –1 285 285 237 242 583 366<br />

Biocide index ha –1 604 604 604 604 2,115 969<br />

<strong>Rice</strong> production Mg farm –1 4.2 4.2 4.7 4.8 1.2 2.1<br />

a 8.2 RMB = US$1.<br />

Technological innovations in rice cultivation<br />

Both households predominantly select double rice systems with<br />

hybrid rice varieties and SSNM. These innovations increase<br />

on-farm income by about 20% for both households (Table 1).<br />

In addition, environmental pollution through N emissions decreases<br />

by almost 20% compared to the reference situation. At<br />

the same time, rice production of both farms increases by about<br />

10%. Off-farm employment is still the major cash earner in<br />

HH1.<br />

Vegetables<br />

Because of the introduction of vegetables, on-farm income of<br />

HH1 and HH2 increases almost five times and two and half<br />

times, respectively, compared with that in the previous scenario<br />

(Table 1). HH1 grows double rice on 25% of its land,<br />

which is just enough to meet household needs for rice. On the<br />

remainder of the land, a rotation of celery, leafy vegetables,<br />

and garden radish is grown. HH2 also selects this vegetable<br />

rotation but on less than 10% of its land. Almost 75% is cultivated<br />

to a rotation of leafy vegetables followed by single rice.<br />

The rest of HH2’s land remains fallow as the household lacks<br />

working capital to purchase inputs for other cropping activities.<br />

Environmental pollution by both households increases<br />

dramatically with the introduction of vegetables (Table 1).<br />

Vegetable prices<br />

Up to a reduction in vegetable prices of 40%, the behavior of<br />

both households is similar, with household income gradually<br />

decreasing as a consequence of the lower returns for vegetables<br />

(Fig. 1). Then, the share of rice in the cropping patterns of<br />

both households increases steadily up to a reduction in vegetable<br />

prices of 90% for HH1 and 80% for HH2, below which<br />

only rice is produced. The increase in rice in the cropping pattern<br />

of HH2 is associated with an expansion of its cultivated<br />

area from 0.34 ha to the complete landholding of 0.40 ha. At<br />

the same time, N emissions to the environment decrease for<br />

both households.<br />

Household income (RMB)<br />

35,000<br />

30,000<br />

25,000<br />

20,000<br />

15,000<br />

10,000<br />

5,000<br />

0<br />

HH1<br />

HH2<br />

<strong>Rice</strong> production (Mg farm –1 )<br />

5.0<br />

4.5<br />

4.0<br />

3.5<br />

3.0<br />

2.5<br />

2.0<br />

1.5<br />

1.0<br />

0.5<br />

0<br />

N loss (kg ha –1 )<br />

600<br />

500<br />

C<br />

400<br />

300<br />

200<br />

100<br />

0<br />

0.1 0.2 0.3 0.4 0.5 0.6 0.7 0.8 0.9 1.0<br />

Fraction of original vegetable price<br />

Fig. 1. Effect of vegetable price (1.0 is the survey-based mean<br />

vegetable price, decreasing toward the left) in Pujiang for (A) household<br />

income, (B) rice production, and (C) N losses.<br />

B<br />

A<br />

424 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Conclusions<br />

The results obtained in this study have several important implications<br />

for policymakers, farmers, and other stakeholders<br />

concerned with sustainable development in the rural-urban<br />

fringes of East and Southeast Asia:<br />

The economic performance of farm households is<br />

dominated by their access to working capital through,<br />

for example, off-farm employment.<br />

Technical innovations (SSNM) can increase on-farm<br />

income and rice production and decrease environmental<br />

pollution.<br />

The introduction of vegetables in the cropping system<br />

leads to strong increases in household income,<br />

but may increase income inequalities among farm<br />

households and is detrimental to the environment.<br />

Access to credit and improved extension services are<br />

a prerequisite for, in particular, poor farmers to shift<br />

their production to activities with higher added values<br />

(such as vegetable production) that contribute to<br />

the improvement of their livelihood.<br />

References<br />

Dobermann A, Witt C, Dawe D, editors. 2004. Increasing productivity<br />

of intensive rice systems through site-specific nutrient<br />

management. Enfield, N.H. (USA): Science Publishers, Inc.,<br />

and Los Baños (Philippines): <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong><br />

(<strong>IRRI</strong>). 410 p.<br />

Guanghuo W, Sun Q, Fu R, Huang X, Ding X, Wu J, He Y,<br />

Dobermann A, Witt C. 2004. Site-specific nutrient management<br />

in irrigated rice systems of Zhejiang Province, China.<br />

In: Dobermann A, Witt C, Dawe D, editors. Increasing productivity<br />

of intensive rice systems through site-specific nutrient<br />

management. Enfield, N.H. (USA): Science Publishers,<br />

Inc., and Los Baños (Philippines): <strong>International</strong> <strong>Rice</strong> <strong>Research</strong><br />

<strong>Institute</strong> (<strong>IRRI</strong>). p 243-263.<br />

Hossain M. 1998. Sustaining food security in Asia: economic, social,<br />

and political aspects. In: Dowling NG, Greenfield SM,<br />

Fischer KS, editors. Sustainability of rice in the global food<br />

system. Davis, Calif. (USA): Pacific Basin Study Center, and<br />

Manila (Philippines): <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>.<br />

p 19-44.<br />

Ponsioen TC, Laborte AG, Roetter RP, Hengsdijk H, Wolf J. 2003.<br />

TechnoGIN-3: a technical coefficient generator for cropping<br />

systems in East and Southeast Asia. Quantitative Approaches<br />

in Systems Analysis No. 26. Wageningen (The Netherlands).<br />

69 p.<br />

Singh I, Squire L, Strauss J. 1986. Agricultural household models:<br />

extensions, applications, and policy. Baltimore, Md. (USA):<br />

The Johns Hopkins University Press.<br />

Notes<br />

Authors’ addresses: Huib Hengsdijk, Plant <strong>Research</strong> <strong>International</strong>,<br />

Wageningen UR, P.O. Box 16, 6700 AA Wageningen, The<br />

Netherlands, E-mail: Huib.Hengsdijk@wur.nl; Marrit van den<br />

Berg, Plant Production Systems, Wageningen University, P.O.<br />

Box 430, 6700 AK Wageningen, and Development Economics,<br />

Wageningen University, P.O. Box 8130, 6700 EW<br />

Wageningen, The Netherlands; Reimund Roetter, Alterra, Soil<br />

Science Centre, Wageningen UR, P.O. Box 47, 6700 AA<br />

Wageningen, The Netherlands; Wang Guanghuo, Zhejiang<br />

University, Hangzhou, China; Joost Wolf, Alterra, Soil Science<br />

Centre, Wageningen UR, P.O. Box 47, 6700 AA<br />

Wageningen, The Netherlands; Lu Changhe, <strong>Institute</strong> of Geographic<br />

Sciences and Natural Resources <strong>Research</strong>, Chinese<br />

Academy of Sciences, Building 917, Datun Road, Beijing<br />

100101, China; Herman van Keulen, Plant <strong>Research</strong> <strong>International</strong>,<br />

Wageningen UR, P.O. Box 16, 6700 AA Wageningen,<br />

and Plant Production Systems, Wageningen University, P.O.<br />

Box 430, 6700 AK Wageningen, The Netherlands.<br />

Rural poverty and agricultural diversification in Thailand<br />

Alia Ahmad and Somporn Isvilanonda<br />

Thailand has experienced steady economic growth and structural<br />

changes in its economy in the last four decades that enabled<br />

it to gain a position among the newly industrialized nations.<br />

Although a great deal of this growth comes from industrial<br />

development, the agricultural sector has contributed significantly<br />

to the process through exports, a cheap food supply,<br />

and the release of labor for industrial development. The structural<br />

changes associated with economic growth reflect the<br />

changing role of agriculture in the economy. The share of agriculture<br />

in GDP declined from 44% in the early 1960s to 10%<br />

in recent years (Isvilanonda 1998). Its share in employment<br />

has shown a similar trend, albeit at a slower pace. The share of<br />

agriculture in total employment fell from 83% in 1957 to 57%<br />

in 1999. In more recent years, it has hovered around 50%<br />

(Mundlak et al 2002).<br />

Although Thailand has been very successful in reducing<br />

poverty because of rapid and steady economic growth, rural<br />

poverty, especially in certain regions, is a serious problem.<br />

Rural-urban disparities also increased after the financial crisis<br />

because of the inability of the urban sector to absorb rural labor<br />

at a rapid rate, and the declining importance of agriculture<br />

in the total value-added. We underscore in this paper that Thai<br />

agriculture still has a major role to play, and the major challenge<br />

is to switch to high value-added products, in other words,<br />

agricultural diversification.<br />

Session 14: Potential for diversification in rice-based systems to enhance rural livelihoods 425


Background and aims of the study<br />

Agricultural diversification in Thailand means primarily<br />

deintensification of rice production. Thailand became a major<br />

rice-exporting nation in the second half of the 19th century<br />

because of its abundant suitable land. The favorable land/person<br />

ratio is one of the reasons behind Thailand’s late adoption<br />

of land-saving modern rice technology. However, the nation<br />

started losing its monopoly position in the international market<br />

in the late 1960s. Traditionally, squeezing rice farmers<br />

through an export tax, a rice premium, and government control<br />

of rice sales was the main feature of Thai policies<br />

(Siamwala 1975). Discrimination against rice farmers has<br />

weakened since the 1970s partly because of competition in<br />

the international market. The government supported the adoption<br />

of new technology through investment in irrigation/infrastructure,<br />

although this constitutes a small proportion of total<br />

rice area (Isvilanonda 1998). In spite of this, rice is facing the<br />

problem of low profitability, mainly because of the declining<br />

demand in both the international and domestic markets. Ideally,<br />

the declining profitability of rice should induce farmers<br />

to switch to other crops. But this has not happened uniformly—<br />

the pattern of deintensification of rice and diversification into<br />

other crops and nonfarm activities differs from region to region.<br />

The overall aim of this paper is to analyze the pattern of<br />

diversification at the farm level, its effects on farm income,<br />

and the constraints faced by farmers in different regions and<br />

under different production environments.<br />

This paper addresses the following questions:<br />

Is diversification out of rice more difficult in poorer<br />

regions than in prosperous regions<br />

Is diversification into other agricultural activities<br />

easier in irrigated areas growing modern rice than in<br />

rainfed areas growing traditional rice<br />

What factors affect the ability of farmers to switch to<br />

high-value crops<br />

How is diversification related to income inequality<br />

in rural areas and across regions<br />

Concepts and measures used in the study<br />

Three types of diversification have been considered:<br />

1. Crop diversification—diversification out of rice intensification<br />

measured in terms of both land and value<br />

of production.<br />

2. Diversification of agricultural production measured<br />

in terms of value of production.<br />

3. Intersectoral diversification into nonagricultural activities<br />

measured in terms of household income.<br />

The study areas and data<br />

The study is based on household-level data from two regions,<br />

Suphan Buri (SB) in the Central Plain and Khon Kaen (KK) in<br />

the Northeastern Province, the commercial and traditional ricegrowing<br />

areas in Thailand, respectively. Three production environments<br />

are selected in each province. These two regions<br />

were investigated in surveys at different times—1995, 1998,<br />

and 2001-02. The number of households investigated was 234<br />

in 1995, 240 in 1998, and 280 in 2001-02.<br />

Results<br />

Land use and cropping patterns<br />

According to our household-level survey data (2001), total<br />

sown area is much smaller (only 2.19 ha) in KK than in SB<br />

(11.7 ha), with a decline since 1995 in KK but an increase in<br />

SB. The larger farm size coupled with the increase in cropping<br />

intensity because of irrigation facilities has resulted in a rise in<br />

average sown area in SB.<br />

<strong>Rice</strong> intensification<br />

In spite of greater cropping intensity, the percentage of sown<br />

area under rice in 2001 in SB is lower (86.67) than in KK<br />

(90.67). In SB, rice intensification has declined since 1995 in<br />

contrast to KK, w<strong>here</strong> it has increased. Differences are considerable<br />

among the villages in SB, w<strong>here</strong> rice intensification<br />

is lower in irrigated areas. <strong>Rice</strong> intensification in the floodprone<br />

areas is extremely high and has influenced the region’s<br />

average. In KK, on the other hand, rice intensification is higher<br />

in irrigated areas than in rainfed or drought-prone areas. Looking<br />

at the diversification pattern, it appears that, in SB, it is<br />

cash crops and water chestnuts, rather than fruits, that led to<br />

diversification out of rice. In KK, the importance of upland<br />

crops has declined with a corresponding increase in fruit trees.<br />

Although all households grow rice in both regions, the<br />

proportion of households growing only rice is lower in SB<br />

than in KK. In KK, it is increasing, w<strong>here</strong>as in SB it is decreasing.<br />

Differences are considerable between SB and KK in<br />

rice productivity: 3.44 versus 2.47 t ha –1 , the annual average<br />

for each region as a whole. In SB, rice productivity differs in<br />

different production environments. It is very high in irrigated<br />

and flood-prone areas (4.5–5 t ha –l ) compared with rainfed<br />

areas with less than 1 t ha –l .<br />

In contrast to SB, t<strong>here</strong> are no significant differences in<br />

productivity in different production environments in KK since<br />

farmers prefer to grow local varieties in these villages, even in<br />

irrigated villages.<br />

Diversification in terms of gross value<br />

of agricultural production<br />

In both Suphan Buri and Khon Kaen, the shares of rice in terms<br />

of sown area are much greater than the shares in terms of gross<br />

value of crops. But the trend is moving in the opposite direction.<br />

<strong>Rice</strong> is gaining importance in terms of both value and<br />

sown area in KK, and is declining in importance in SB. T<strong>here</strong><br />

are significant differences within each region depending on<br />

the production environments.<br />

In Suphan Buri, diversification has increased except in<br />

flood-prone areas. Both rice and water chestnuts are a top crop,<br />

426 <strong>Rice</strong> is life: scientific perspectives for the 21st century


and the crop diversification index indicates a high level of diversification.<br />

In Khon Kaen, on the other hand, because of the increasing<br />

importance of rice, the crop diversification index in irrigated<br />

and drought-prone villages shows a declining trend, but<br />

a rising trend is observed in the rainfed village. On average, it<br />

has declined since 1995, with a slight increase in 1998.<br />

Constraints to diversification within agriculture<br />

T<strong>here</strong> appear to be three categories of problems: basic inputs<br />

(soil, labor, water), institutional factors (access to land, credit,<br />

knowledge), and price/marketing factors. Households in SB<br />

face more constraints with respect to basic facilities and marketing<br />

risks, w<strong>here</strong>as those in KK experience more institutional<br />

problems. A high person-land ratio and a smaller farm size<br />

may be important factors. The differences between the two<br />

regions are mainly due to the commercial versus subsistence<br />

nature of production. In KK, very few households, 8 out of<br />

142, mentioned marketing problems, and no household considered<br />

price fluctuation as a constraint.<br />

Household income from different sources<br />

While KK is more dependent on rice as a source of income<br />

within agriculture, its dependence on rice in total income is<br />

significantly less because of its dependence on nonfarm activities.<br />

In 2001, the percentage of nonfarm income in KK was<br />

63% versus 26% in SB.<br />

Poverty/inequality<br />

First, we look at inequality between regions, followed by inequality<br />

within each region. Inequality is expressed in two<br />

ways: first in terms of the ratio of average per capita income in<br />

the two regions (SB/KK), and second in terms of the ratio of<br />

the income of the poorest 20% and the richest 20%. In 1995,<br />

average per capita income in SB was 2.8 times the income in<br />

KK. T<strong>here</strong> has been a decline in inequality between 1995 and<br />

2001. In 1995, the poorest 20% of the population in SB earned<br />

1.3 times more than its counterpart in KK and inequality among<br />

the poor between the two regions increased in 2001. Sources<br />

of inequality between the regions are size of landholding, irrigation<br />

facilities, size of households, and nearness to metropolitan<br />

areas.<br />

Although the level of inequality in SB is higher than in<br />

KK, inequality is declining in SB at a faster rate. The lower<br />

level of inequality in KK than in SB is due to more equal distribution<br />

of the access to production factors. In SB, on the<br />

other hand, inequality in education may have played a role.<br />

However, the poor in SB have managed well both in absolute<br />

terms and in a dynamic sense because of the higher level of<br />

access to resources and opportunities.<br />

Determinants of diversification-regression analyses<br />

An OLS regression was run to find out the determinants of<br />

crop diversification (Table 1). We have used the crop diversi-<br />

Table 1. Regression results in different crop years<br />

for Suphan Buri and Khon Kaen.<br />

Variable Coefficient t-statistic<br />

Crop year 1995<br />

Age –0.002344 –1.365289<br />

Farmsize 0.007129 1.016620<br />

Personland –0.008233 –1.296398<br />

No.debt 0.028868 0.765422<br />

Rentratio –0.078738 –1.568819<br />

<strong>Rice</strong>price 0.001471 0.068920<br />

Irrigation 0.372536 4.212958<br />

Rainfed 0.257906 3.108211<br />

C 1.099079 6.067455<br />

R-square 0.113992<br />

Adjusted R-square 0.083308<br />

Crop year 1998<br />

Age –0.006359 –3.917268<br />

Debt 1.61E–07 0.452216<br />

Farmsize –0.005485 –0.725704<br />

Personland –0.011813 –1.482655<br />

No.debt 0.010956 0.239136<br />

Rentratio –0.081504 –0.954818<br />

<strong>Rice</strong>price –0.054093 –1.417187<br />

Irrigation 0.464375 5.070744<br />

Rainfed 0.115971 1.268601<br />

C 1.658754 8.398210<br />

Adjusted R-square 0.257375 0.000000<br />

R-square 0.286060<br />

Crop year 2001<br />

Age 0.000607 0.327060<br />

Debt 5.73E–07 1.580791<br />

Farmsize 0.006290 0.995595<br />

Personland –0.018344 –2.923910<br />

No.debt –0.033540 –0.989760<br />

Rentratio 0.160279 2.274592<br />

<strong>Rice</strong>price –0.027360 –0.675996<br />

Irrigation 0.572512 6.849020<br />

Rainfed 0.462669 4.854177<br />

C 0.896186 4.138147<br />

R-square 0.188981 6.990510<br />

Adjusted R-square 0.161947 0.000000<br />

Variable explanation<br />

Age<br />

Age of household head (years)<br />

Debt<br />

Amount of loan (baht)<br />

Farmsize<br />

Total landholding of household<br />

Personland Ratio of population/total land<br />

No.debt<br />

No. source of loan<br />

Rentratio<br />

Ratio of rent land/total land<br />

<strong>Rice</strong>price<br />

Paddy price at farm gate<br />

Irrigation Dummy variable (irrigation = 1,<br />

other = 0)<br />

Rainfed Dummy variable (rainfed = 1,<br />

other = 0)<br />

Note: Using flood-prone is base for production environment’s<br />

dummy variable (irrigation, rainfed, flood-prone).<br />

Session 14: Potential for diversification in rice-based systems to enhance rural livelihoods 427


fication index for each household as the dependent variable<br />

explained by access to land (+), price of rice (–), irrigation,<br />

infrastructure and water control (+), agricultural credit (+),<br />

proximity to urban areas (+), age of the household head (–),<br />

demographic pressure (–), and the proportion of rental land in<br />

total land (–).<br />

In 1995, the above factors explained 25% of the variation<br />

in diversification among the sample households. Irrigation<br />

and the age of the household head have turned out to be<br />

significant at the 1% level with positive effects and negative<br />

effects, respectively. The model worked poorly for 1998. It<br />

explained only 8% of the variation in the dependent variable,<br />

and irrigation was the only significant factor at the 1% level.<br />

The model using 2001 data explained 16% of the variation,<br />

and several factors were found to be significant—irrigation<br />

and the person/land ratio were significant at the 1% level,<br />

w<strong>here</strong>as the rental ratio was significant at the 5% level. The<br />

person/land ratio had a negative effect as expected.<br />

Conclusions and policy implications<br />

Diversification primarily refers to deintensification of rice production<br />

and a switch to other cash crops, fruits, livestock, and<br />

aquaculture. It has been found that rice intensification is higher<br />

and increasing in the northeast compared with the Central Plain.<br />

Also, diversification in terms of land-use pattern and gross<br />

value of agricultural production is lower in the former region<br />

than in the latter.<br />

The factors that constrain diversification in these two<br />

regions are quite different because of differences in the nature<br />

of farming (commercial versus subsistence). The main constraints<br />

perceived by KK farmers are the lack of access to production<br />

factors, w<strong>here</strong>as in SB farmers face marketing problems.<br />

The differences in the ability to diversify in the two regions<br />

are reflected in the growing inequality between regions,<br />

w<strong>here</strong>as inequality has declined in the more prosperous regions.<br />

It should be noted that these two regions are at different<br />

stages of agricultural transformation (Timmer 1988) and the<br />

policy implications for agricultural development and diversification<br />

are t<strong>here</strong>fore different. In the Central Plain, policies<br />

should be directed to removing contraints in the production<br />

and marketing of high-value crops. On the other hand, in the<br />

Northeastern Province, the main problem is to increase the<br />

productivity of rice cultivation as well as cultivation of other<br />

crops. Policies should be directed to securing property rights,<br />

irrigation, infrastructure, and credit facilities.<br />

References<br />

Isvilanonda S. 1998. <strong>Rice</strong> production and consumption in Thailand:<br />

the recent trend and future outlook. Thailand J. Agric. Econ.<br />

55.<br />

Mundlak, Larson, Butzer. 2002. Determinants of agricultural productivity<br />

in Thailand, Indonesia and the Philippines. World<br />

Bank Web site.<br />

Siamwalla A. 1975. A history of rice price policies in Thailand. In:<br />

Puey Ungphakorn et al, editors. Finance, trade and economic<br />

development in Thailand. Essays in honour of Kunying Suparb<br />

Yossundara.<br />

Timmer PC. 1988. The agricultural transformation. In: Chenery H,<br />

Srinivasan TN, editors. Handbook of development economics.<br />

Amsterdam (Netherlands): Elsevier Science Publishers<br />

B.V.<br />

Notes<br />

Sustaining higher efficiency in rice production<br />

Amelia S. delos Reyes, Arelene Julia B. Malabayabas, and Mercedita A. Sombilla<br />

Authors’ addresses: Alia Ahmad, Department of Economics, Lund<br />

University, Sweden; Sompom Isvilanonda, Department of<br />

Agricultural and Resource Economics, Kasetsart University,<br />

Bangkok, Thailand.<br />

Poor farmers are less able to cope with shortfalls in crop production<br />

and as a consequence diversify their activities as a<br />

precaution. This occurs more frequently in rainfed areas w<strong>here</strong><br />

uncertainties are higher because of unpredictable environmental<br />

elements (<strong>IRRI</strong> 1995). In Asia, close to 30% of the total productive<br />

area is categorized as rainfed; the majority of this is<br />

rice-based, with animal raising as a key component (Thornton<br />

et al 2002).<br />

This paper presents part of the results of the socioeconomic<br />

study on crop-animal interactions under the project Sustainable<br />

Food-Feed Systems and Improved Livelihoods of the<br />

Poor in Rainfed Lowland Areas, which is funded by the<br />

Systemwide Livestock Program. It seeks to explain the crucial<br />

role of animal production in promoting greater efficiency in<br />

rice production, and provides recommendations for development<br />

strategies to progressively improve the crop-animal production<br />

system. It is hypothesized that animal raising helps<br />

increase rice income and improves production efficiency.<br />

Integrated crop-animal systems on small rainfed rice farms<br />

Crop-animal integration on rainfed farms comes in two broad<br />

categories: systems combining crops (mainly rice),<br />

nonruminants, ponds, and fish; and systems combining crops<br />

(also mainly rice) and ruminants (Devendra 1995). The most<br />

common is the interaction between ruminants, particularly<br />

cattle/buffalo and rice. Cattle/buffalo provide animal traction<br />

during land preparation and manure (directly or indirectly) to<br />

428 <strong>Rice</strong> is life: scientific perspectives for the 21st century


enhance the soil. <strong>Rice</strong> straw, other rice by-products, and residues<br />

from other crops are fed to the animals in return. The<br />

degree of such interaction varies across countries and across<br />

areas within countries. In Khon Kaen, Thailand, for example,<br />

the use of cattle as draft power has been replaced by tractors<br />

and power tillers because of the combined effect of various<br />

factors such as the changing demand for crops and other products,<br />

the growing scarcity of the rural labor market, the decline<br />

in livestock population, etc. The degree of crop-animal<br />

interaction in Long An Province in Vietnam, which is close to<br />

Ho Chi Minh City, is less than that in An Giang, which lies<br />

close to the border of Cambodia. How does this trend affect<br />

rice production efficiency, especially among small rainfed farm<br />

areas<br />

Methodology<br />

The study employs the stochastic production frontier model<br />

popularized by Aigner et al (1977) to compare productive efficiency<br />

of different rice farm groups. The empirical form is a<br />

yield function expressed as<br />

n<br />

λn Y j = λn a + Σ b i λnX ij + e j<br />

i=1<br />

w<strong>here</strong> j = 1 … n total number of samples; Y j represents the<br />

yield of the jth farm; X i = 1 × k vector of input quantities of the<br />

jth farm;a, b i = parameters to be estimated; e j = error term<br />

such that e j = ν j + µ j , w<strong>here</strong> ν j = random error that is beyond<br />

the control of the production unit.<br />

Costs and returns in rice production<br />

Table 1 shows the average costs and returns in rice production<br />

of sample respondents at the different project sites. At most of<br />

the project sites, net income (above all costs) is shown to be<br />

highest among those belonging to Group 1. This is especially<br />

the case among the respondents in Cambodia and in Vietnam,<br />

in An Giang in particular. When the noncash costs are excluded,<br />

the net income of Group 1 in all countries (except in Indonesia<br />

and Thailand) is highest. Noncash costs account for up to a<br />

46% share of the total cost in Thailand, mostly the imputed<br />

cost of family labor. The imputed cost of the use of own animals<br />

for power or for manure accounts for from 2% to 18% of<br />

the total cost. It is in Indonesia w<strong>here</strong> a large amount of animal<br />

manure is used in rice cultivation.<br />

Stochastic frontier production results<br />

Table 2 shows the results of the stochastic frontier production<br />

analysis. The yield function is expressed as a Cobb-Douglas<br />

function; hence, the coefficients are actually elasticities. A<br />

majority of the explanatory variables in the yield function have<br />

the right signs. Important to note are the coefficients of the<br />

dummy variables representing pest infestation, partial irrigation,<br />

and the use of high-yielding varieties, which indicate a<br />

substantial impact on rice yield. The negative sign for the area<br />

coefficient has been shown in other studies (Husain et al 2001).<br />

It indicates that farmers strive hard to increase yield to enhance<br />

production from a small piece of land. The only coefficient<br />

that is significant, but with the wrong sign, is that for the<br />

price of seed. The value <strong>here</strong> is imputed by farmers, who may<br />

have based it on the price of rough rice. The coefficient of<br />

animal days is negative but this is insignificant. The sign implies<br />

that farmers tend to be using more animal days than are<br />

required, which could be the case for farm households in Group<br />

1. Sample respondents reported having employed from 10 animal<br />

days (in Thailand, w<strong>here</strong> tractors are used more extensively)<br />

to 56 animal days (in Cambodia) per hectare per year<br />

in rice cultivation. These numbers seem high compared to the<br />

normal use of animals that averages about 20 days per hectare<br />

per season or up to 40 days per hectare per year of two seasons<br />

(personal communication with V. Balasubramanian, <strong>IRRI</strong>,<br />

2004). The coefficients of the dummy variables for Groups 2<br />

and 3, respectively, are negative but insignificant. Nevertheless,<br />

they seem to confirm the beneficial effect of animal use<br />

in rice fields, especially in small marginal areas, in terms of<br />

both productivity and sustainability.<br />

Among the variables influencing technical efficiency,<br />

total income, the dummy for education, and the dummy for<br />

farming experience stand out. The estimated coefficients of<br />

these variables are significant and the negative sign indicates<br />

their tendency to reduce inefficiency. The negative sign of the<br />

coefficient for the small animal ownership dummy, although<br />

not significant, is related to these animals’ role as a quick source<br />

of cash/capital for the purchase of inputs. The negative coefficient<br />

of the Group 2 dummy, although not significant, further<br />

confirms its lesser tendency to bring about an efficiency improvement.<br />

The coefficient of the variable representing ownership<br />

of large animals is significant, but with a positive sign. This<br />

supports the conclusion derived from the yield regression portion<br />

regarding the seemingly extensive use of animals beyond<br />

the level that would further improve production efficiency. The<br />

training variable is estimated with a positive but insignificant<br />

coefficient. Only about 33% of the sample respondents at the<br />

project sites indicated having undergone training on crop production<br />

practices and technologies, be it on rice or other crops,<br />

and only 16% on animal production management techniques.<br />

The highest participation rate is reported in Vietnam. Deficiency<br />

in extension and training services is typical in remote<br />

and marginal areas because of a limited budget from the public<br />

sector. Private companies still do not have enough incentives<br />

to provide such investments. The coefficient of the credit<br />

variable in the technical inefficiency portion is significant, but<br />

with a positive sign. Capital for credit is often scarce in developing<br />

countries, much more so for small farmers because of<br />

the risk and cost involved. Farmers have often relied on moneylenders<br />

or private traders that advance funds until the crop<br />

is sold. This system of credit has not always been advantageous<br />

for improving productivity. It has rather led farmers into<br />

a vicious circle of debt, especially in unfortunate cases when a<br />

Session 14: Potential for diversification in rice-based systems to enhance rural livelihoods 429


Table 1. Costs and returns in rice production across project sites (in US$ per ha).<br />

Indonesia Vietnam Philippines<br />

Item Cambodia Thailand<br />

East Java West Java All An Giang Long An All N. Ecija Samar All<br />

Group 1 a<br />

Yield 3.84 4.25 4.25 4.32 3.48 4.22 3.82 2.05 2.74 1.83<br />

Total returns 1,485.56 663.2 663.2 858.97 511.21 818.53 1031.3 571.91 751.29 233.76<br />

Total costs 487.53 615.47 615.47 589.23 415.43 569.02 516.03 321.15 397.25 344.28<br />

Imputed 203.88 370.71 370.71 223.05 181.51 218.22 68.85 106.73 91.93 229.63<br />

Cash 283.65 244.76 244.76 366.18 233.92 350.8 447.18 214.42 305.32 114.64<br />

Net returns above cash cost 1,201.91 418.44 418.44 492.79 277.28 467.73 584.12 357.49 445.97 119.12<br />

Net returns above total cost 998.03 47.73 47.73 269.74 95.77 249.51 515.27 250.76 354.04 –110.51<br />

Group 2 a<br />

Yield 3.76 4.36 5.15 4.25 3.21 3.93 3.78 3.88 2.05 3.66 2.64<br />

Total returns 1,453.57 626.79 1,080.29 675.82 671.9 566.11 588.15 967.56 359.83 893.89 340.53<br />

Total costs 746.34 498.94 501.05 499.17 601.81 332.5 388.6 445 174.54 412.21 307.71<br />

Imputed 109.35 207.53 102.19 196.14 210.22 91.85 116.51 37.3 30.07 36.42 145.97<br />

Cash 636.99 291.41 398.86 303.02 391.59 240.64 272.09 407.7 144.47 375.79 161.74<br />

Net returns above cash cost 816.58 335.38 681.43 372.79 280.31 325.46 316.06 559.86 215.36 518.1 178.79<br />

Net returns above total cost 707.23 127.85 579.24 176.65 70.09 233.61 199.54 522.56 185.29 481.69 32.82<br />

Group 3 a<br />

Yield 2.70 4.84 4.39 4.25 3.08 3.08 2.96 1.91 2.35 2.76<br />

Total returns 976.82 872.53 941.45 938.70 644.23 644.23 616.62 555.38 580.9 316.92<br />

Total costs 493.85 494.42 648.80 642.63 637.32 637.32 389.29 302.23 338.51 302.77<br />

Imputed 129.11 91.06 228.13 222.65 284.02 284.02 35.39 57.43 48.25 128.01<br />

Cash 364.74 403.36 420.67 419.98 353.30 353.30 353.90 244.80 290.26 174.76<br />

Net returns above cash cost 612.08 469.17 520.78 518.72 290.93 290.93 262.72 310.58 290.64 142.16<br />

Net returns above total cost 482.97 378.10 292.65 296.07 6.91 6.91 227.33 253.15 242.39 14.15<br />

Average all<br />

Yield 3.73 4.36 4.46 4.25 4.18 3.84 4.06 3.78 2.04 2.91 2.65<br />

Total returns 1,437.32 641.81 955.34 795.69 835.00 554.67 735.32 979.01 559.05 769.03 319.32<br />

Total costs 508.46 518.43 634.03 575.16 591.23 349.78 505.38 480.12 311.56 395.84 307.33<br />

Imputed 189.73 230.84 215.54 223.33 222.28 110.53 182.55 54.42 98.04 76.23 141.21<br />

Cash 318.73 287.59 418.49 351.83 368.95 239.24 322.83 425.7 213.52 319.61 166.12<br />

Net returns above cash cost 1,118.59 354.23 536.85 443.86 466.05 315.43 412.49 553.31 345.53 449.42 153.20<br />

Net returns above total cost 928.86 123.38 321.31 220.53 243.77 204.89 229.95 498.89 247.49 373.19 11.99<br />

a Group 1 includes farm households that own cattle or buffalo and use those animals in their rice cultivation. Group 2 includes farm households that own cattle and/or buffalo but that are not used in rice cultivation.<br />

Group 3 includes farm households that do not own any cattle or buffalo.<br />

430 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 2. Results of the stochastic production frontier regression, <strong>IRRI</strong>-ILRI<br />

Project, 2004.<br />

Variables Coefficient t-value<br />

Yield regression component<br />

Constant 8.26769 146.81<br />

Farm area (ha) –0.17048 –9.83<br />

Seed use (kg ha –1 ) 0.00066 1.67<br />

Family labor (no. of days) 0.00004 0.17<br />

Hired labor (no. of days) 0.00015 1.45<br />

Animal power (no. of days) –0.00007 –1.39<br />

Machine use/rental (no. of days) 0.00011 2.88<br />

Fertilizer use (kg ha –1 ) 0.00029 7.55<br />

Dummy for pest infestation –0.10163 –2.56<br />

Dummy for partial irrigation 0.22159 6.94<br />

Dummy for use of high-yielding varieties 0.11421 2.28<br />

Dummy for dry season –0.01945 –0.64<br />

Dummy for Group 2 –0.05569 –0.97<br />

Dummy for Group 3 –0.06383 –0.98<br />

Technical inefficiency component<br />

Constant –15.55516 –3.23<br />

Total income ($ per household) –0.00822 –4.29<br />

Dummy for small animal ownership –0.25559 –1.08<br />

Dummy for large animal ownership 3.77959 3.16<br />

No. of male laborers to household size 0.00072 1.71<br />

Dummy for schooling beyond 6 years –2.63059 –3.32<br />

Dummy for farming experience beyond 20 years –1.49879 –3.41<br />

Dummy for participation in training 0.16356 0.63<br />

Dummy for credit availment 0.65659 2.69<br />

Dummy for Group 2 –0.23664 –0.76<br />

Dummy for Group 3 5.87091 3.14<br />

Mean efficiency, all groups 0.69<br />

Group 1 mean efficiency level 0.72<br />

Group 2 mean efficiency level 0.69<br />

Group 3 mean efficiency level 0.64<br />

Source: Food-Feed Systems Survey, 2002-03.<br />

crop fails. Larger farmers have better access to credit, often<br />

for reasons of provision of collateral and lower administrative<br />

costs of servicing larger loans. But their yields are often not<br />

higher than those of small farms.<br />

Also shown in Table 2 are the estimated technical efficiency<br />

coefficients across the three groups of rice farm households.<br />

The overall technical efficiency estimate for all the respondents<br />

is 0.69. It is highest among rice farm households<br />

belonging to Group 1 and lowest among farm households in<br />

Group 3. The differences, however, are not very large.<br />

Conclusions<br />

Crop-animal integration is beneficial from the standpoint of<br />

the savings on input expenditures, particularly on energy use<br />

in rice cultivation. The advantage of closer integration in terms<br />

of promoting production efficiency, however, was not so strong.<br />

The results seem to indicate the need to stress to farmers the<br />

proper techniques for the use of animals in land preparation to<br />

enhance their contribution to promoting production efficiency.<br />

Additional results gat<strong>here</strong>d from the stochastic production frontier<br />

analysis also indicate that t<strong>here</strong> is still some room for improving<br />

yield and efficiency in rainfed rice production. The<br />

recommendations indicated are nothing new: the provision of<br />

water and the development of high-yielding and pest-resistant<br />

varieties should continue to be on the priority list of the research<br />

and development agenda for these production environments,<br />

and public budgets for training and extension should<br />

be enhanced to reach remote and marginal areas.<br />

References<br />

Aigner DJ, Lovell K, Schmidt P. 1977. Formulation and estimation<br />

of stochastic frontier production models. J. Econometrics<br />

6(1):21-37.<br />

Devendra C. 1995. Environmental characterization of crop-animal<br />

systems in rainfed areas. In: Devendra C, Sevilla C, editors.<br />

Crop-animal interactions. <strong>IRRI</strong> Discussion Paper Series No.<br />

6. Manila (Philippines): <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>.<br />

p 43-64.<br />

Session 14: Potential for diversification in rice-based systems to enhance rural livelihoods 431


Husain AMM, Hossain M, Janaiah A. 2001. Hybrid rice adoption in<br />

Bangladesh: a socio-economic assessment of farmers’ experience.<br />

<strong>Research</strong> Monograph Series No. 18. Bangladesh Rural<br />

Advancement Committee, Bangladesh.<br />

<strong>IRRI</strong> (<strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>). 1995. Fragile lives in<br />

fragile ecosystems. Proceedings of the <strong>International</strong> <strong>Rice</strong> <strong>Research</strong><br />

Conference, 13-17 Feb. 1995. Manila (Philippines):<br />

<strong>IRRI</strong>. 976 p.<br />

Thornton PK, Kruska RL, Henninger N, Kristjanson PM, Reit RS,<br />

Atieno F, Odero AN, Ndegwa T. 2002. Mapping poverty and<br />

livestock in the developing world. Nairobi (Kenya): <strong>International</strong><br />

Livestock <strong>Research</strong> <strong>Institute</strong>.<br />

Notes<br />

Authors’ address: A.S. delos Reyes, assistant scientist II; A.J.B.<br />

Malabayabas, contractual researcher; M.A. Sombilla, consultant,<br />

<strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>, Los Baños, Philippines.<br />

Determinants of agricultural diversification in Vietnam:<br />

changes at the farm level in the Mekong<br />

and Red River deltas<br />

Magnus Jirström and Franz-Michael Rundquist<br />

A central part of current economic development in Vietnam<br />

concerns the transformation of the agricultural sector and development<br />

of the rural economy. For a rice economy, like<br />

Vietnam’s, this process includes the challenge to diversify out<br />

of rice (cf. Jirström and Rundquist 1999, Taylor 1994). This<br />

paper focuses on the farm-level processes of agricultural diversification<br />

in Vietnam’s two rice-bowl areas: the Mekong<br />

River Delta (MRD) and the Red River Delta (RRD).<br />

Data, methodology, and organization of this paper<br />

This paper presents results from a research project 1 within<br />

which household panel survey data were collected on three<br />

occasions in the MRD—1996, 1999, and 2002—and on two<br />

occasions in the RRD—1999 and 2002. The selection of study<br />

areas and households was carried out through a multistage<br />

stratified random sampling method. In the MRD, data gat<strong>here</strong>d<br />

from 180 households cover the time-span 1996-2002. In<br />

the Red River Delta, 189 farm households were surveyed in<br />

1999 and re-surveyed in 2002. Our analysis in this paper will<br />

be limited to what we call rice diversification changes measured<br />

as changes in the dependence on income from rice in the<br />

total household economy and agricultural production system.<br />

Land use and diversification characteristics<br />

of Vietnam’s delta regions<br />

Table 1 displays the significant difference in the size of landholdings<br />

in the two regions, with the RRD farmers operating<br />

farms only a third of the size of the farms of the Mekong farmers.<br />

In both regions, however, land use is dominated by rice,<br />

which is grown intensively, with a cropping index of 172% in<br />

the north and 219% in the south. In the Mekong, a rice intensification<br />

process raised the cropping index from 168 in 1996 to<br />

219 six years later. The Mekong farmers form part of a more<br />

general development of the 1990s in which farmers in several<br />

Mekong provinces have switched from double to triple rice<br />

cropping as a result of improved irrigation and drainage infrastructure<br />

(Choeng-Hoy Chung 1997).<br />

In the Red River Delta, a higher proportion of cropped<br />

land is allocated to upland, or dry, crops, a fact that is explained<br />

by the climatic conditions in the north not allowing<br />

rice cultivation in the winter season. In terms of crop diversification,<br />

Mekong farmers have made efforts to grow new crops<br />

to increase income. During the 1990s, many diversified into<br />

fruit production, but a combination of fluctuating and low product<br />

prices as well as pest- and water management-related problems<br />

seems to have discouraged farmers to the extent that the<br />

share of land allocated to fruit plantations dropped to half by<br />

2002.<br />

1 “Structural Transformation of Southeast Asia’s Agricultural Systems: Agricultural Diversification in Vietnam,” funded by the Swedish <strong>Research</strong> Council<br />

(Vetenskapsrådet). The project is carried out in cooperation with the Cuu Long Delta <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong> (CLRRI) in Can Tho and the <strong>Institute</strong> for Environment<br />

and Sustainable Development, Hanoi.<br />

432 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. Agricultural and income characteristics in the Mekong River Delta (MRD) and<br />

Red River Delta (RRD). a MRD RRD<br />

Variables<br />

1996 2002 1999 2002<br />

Total area (ha) 172.8 183.5 54.9 54.1<br />

Cropped area (ha) 332.2 440.7 112.5 108.0<br />

<strong>Rice</strong> sown area (ha) 289.4 402.4 95.0 93.3<br />

<strong>Rice</strong> sown area (%) 87.1 91.3 84.4 86.4<br />

Upland crop sown area (ha) 18.4 23.6 15.7 12.4<br />

Upland crop sown area (%) 5.5 5.4 14.0 11.5<br />

Fruit crop area (ha) 24.4 14.8 1.8 2.3<br />

Fruit crop area (%) 7.4 3.4 2.0 2.0<br />

Average land operator per household (ha) 0.96 1.02 0.29 0.29<br />

Average total household income 14,378 16,925 17,126 21,174<br />

Average rice production income 7,733 7,749 4,505 3,360<br />

Average nonrice crop income 1,629 958 1,793 1,613<br />

Average noncrop agricultural income 221 1,703 4,479 4,669<br />

Average total off-farm income 4,965 6,515 6,419 12,414<br />

Average off-farm nonfarm income n.a. 4,045 6,097 11,072<br />

a All income values are expressed as 000 VND (Vietnamese dong) in constant 2002 values; US$1 =<br />

15,279 VND (2002). n.a. = not available. T-tests for paired samples show that the difference between the<br />

two periods for the MRD is significant at the 1% level for cropped area, rice sown area, and fruit crop area.<br />

Also, for the MRD, significant differences at the 5% level are found for total household income, noncrop<br />

agricultural income, and total off-farm income. In the case of the RRD, significant differences at the 5%<br />

level, or higher, are found for all income variables. For land use only, the changes in the upland crop sown<br />

area are significant, but this time at the 1% level.<br />

Source: Information is based on sample surveys comprising 180 farm households in the MRD and 189<br />

households in the RRD from a larger research project by the authors titled “Structural Transformation of<br />

Southeast Asia’s Agricultural System: Agricultural Diversification in Vietnam.”<br />

Turning our attention to household income and its composition,<br />

the aggregate numbers in Table 1 show that Mekong<br />

farmers, in spite of access to much larger landholdings, on<br />

average have approximately 20% lower income than farmers<br />

in the north. This finding is in line with the more general observation<br />

that rural inhabitants in the Mekong region become<br />

relatively poorer than in other parts of the country (Government<br />

of Vietnam 2000). The mentioned increasing intensity of<br />

land use in the MRD has not been able to reduce the increasing<br />

income gap between the two regions. In terms of dependence<br />

on rice income for total income, the regional difference<br />

is significant. In 2002, 46% of an average Mekong farm<br />

household’s income was derived from rice production, while<br />

an average Red River Delta household depended only to some<br />

16% on rice. The share of rice in the total income was nevertheless<br />

decreasing in both survey areas (54% in the MRD in<br />

1996 and 26% in the RRD in 1999).<br />

In spite of the rather dramatic area intensification of rice<br />

production in the Mekong, farmers earned approximately the<br />

same income from rice in 2002 as in 1996. The lower profitability<br />

of rice production in the MRD is also typical for the<br />

RRD, w<strong>here</strong> income from rice cultivation from the same size<br />

of cropped land fell by some 25% from 1999 to 2002.<br />

Because of the mentioned difficulties in diversifying into<br />

fruit production, nonrice crop income has decreased by 4% in<br />

the MRD. On the other hand, noncrop agriculture (animal husbandry<br />

and aquaculture) has grown in the Mekong and now<br />

represents some 10% of total income. In the RRD, its share<br />

has fallen somewhat but remained relatively higher at about<br />

22% in 2002.<br />

The process of intersectoral diversification explains most<br />

of the growth in income in both regions. Off-farm income has<br />

grown in the MRD at a rate high enough for it to retain its<br />

relative importance—38% of total income. In the RRD, offfarm<br />

income has almost doubled, and farm households t<strong>here</strong><br />

now depend more on off-farm income—about 52% of total<br />

income—than on on-farm income. While the proximity to urban<br />

areas and income sources are more important in the RRD,<br />

farm families in the Mekong are more dependent on agriculture-related<br />

off-farm income—38% of total off-farm income<br />

in the MRD vis-à-vis 11% in the RRD.<br />

Behind the averages<br />

The farming and income characteristics discussed so far are<br />

based on mean sample values. The studied agricultural diversification<br />

process is not, however, a smooth process including<br />

all farm households in an equitable manner. In this second section<br />

of the paper, we try to capture some of the dynamics of<br />

the diversification process by analyzing and discussing four<br />

categories of rice farm households.<br />

Session 14: Potential for diversification in rice-based systems to enhance rural livelihoods 433


Methodologically, changes are described by looking at<br />

specific categories of farm households and their “movement”<br />

in rice dependence between the two points in time. <strong>Rice</strong> dependence<br />

has been defined as the proportion of income from<br />

rice in the household total income. These proportions have<br />

been categorized into four quartiles (0–25%, 25–50%, etc.).<br />

In the second stage, changes in category affiliation were examined,<br />

and several new categories were defined. First, those<br />

who stayed in the first quartile at both times were classified as<br />

Stable high diversifiers (households displaying a high level of<br />

diversification, i.e., low dependence [d”25%] on rice income<br />

in their total income). The opposite group (those who showed<br />

a high dependence [>75%] on rice income in their total income)<br />

was classified as Stable low diversifiers. Second, those<br />

who changed by two or three quartiles were classified as Significant<br />

ascenders and Significant descenders, respectively,<br />

depending on the direction of their changes. Finally, those who<br />

changed only one quartile between the two points in time were<br />

classified as “Moderate changers.” In the presentation (Table<br />

2) and discussion below, we focus on only four of these categories—Stable<br />

high diversifiers, Stable low diversifiers, Significant<br />

ascenders, and Significant descenders representing<br />

the more “spectacular” groups of the “stayers” and “movers.”<br />

Our data confirm a picture of significantly more diversified<br />

farm households in the RRD. In 2002, only 10 out of 189<br />

households depended on rice production for more than 50%<br />

of their total income. In the MRD, the situation is more dynamic,<br />

with approximately a fifth of the sample being involved<br />

in rapid diversification out of rice.<br />

Among the four categories, the Stable high diversifiers<br />

at both times and in both regions show the highest household<br />

income. However, the group Significant ascenders is rapidly<br />

catching up, with a doubling—MRD 104%, RRD 115%—of<br />

total household income. Significant descenders, on the other<br />

hand, are characterized by falling total income. Finally, in the<br />

Mekong, it is possible to discern a group of households—Stable<br />

low diversifiers—characterized by above average and increasing<br />

size of landholdings following a rice specialization path.<br />

This group, which depends almost completely on rice cultivation,<br />

has greatly increased its total income to a level well above<br />

the sample average.<br />

Determinants and patterns of diversification<br />

Searching for determinants of the observed differences in diversification,<br />

several variables were selected—access to family<br />

labor, education, farm size, and sown area. The composition<br />

of income may in itself not only be an effect of the diversification<br />

process, but also may determine its direction and<br />

speed for individual households. This section focuses on the<br />

MRD region, w<strong>here</strong> the share of farm households experiencing<br />

significant changes in the composition of income is relatively<br />

greater than in the already more diversified RRD region.<br />

Furthermore, only in the RRD is t<strong>here</strong> a group of farmers<br />

following a nondiversification path. Starting with the households<br />

experiencing the most dramatic changes in terms of the<br />

level of income diversification, the following observations can<br />

be made for the four categories.<br />

Significant ascenders as a group started out in 1996 at<br />

an income level well below the average total sample (cf. Table<br />

1) but were operating slightly above average landholdings. During<br />

the period, they were able to allocate more of their total<br />

harvested area to nonrice crops and were successful in raising<br />

their income from this source. Also, the increasing noncrop<br />

agricultural income contributed to their overall success, which<br />

primarily was explained by a dramatic increase in off-farm<br />

income.<br />

Significant descenders were, in terms of total income,<br />

starting from a relatively higher level than the previous group.<br />

However, their access to land was only two-thirds of that of<br />

the ascenders and, as their off-farm income dropped, they were,<br />

in spite of some increase in land, and a significant increase in<br />

cropping index from 166 to 255, not able to compensate for<br />

the negative change. The area used for nonrice crops did not<br />

change, but their net income from this source turned negative.<br />

This was due to the problems of pest attacks and water management<br />

related to fruit production.<br />

Stable high diversifiers enjoy high income from all income<br />

sources but rice. During the period, these households<br />

allocated somewhat less land to nonrice crops (from 0.54 to<br />

0.40 ha) but were instead able to increase their noncrop agricultural<br />

income. Over the six-year period during which the<br />

majority of households in the total sample intensified their<br />

cultivation by growing a third (summer-spring) rice crop, the<br />

Stable high diversifiers group only marginally increased the<br />

cropping index of its land. This then seems well in line with a<br />

strategy of diversifying both agricultural and nonagricultural<br />

income.<br />

Stable low diversifiers seem to follow a rice specialization<br />

strategy. They have significantly increased their landholdings,<br />

and, with a cropping index of 266, they are the most intensive<br />

land users. An important question is whether such a<br />

strategy is sustainable over time. The possibility to further increase<br />

the intensity of land use is very limited, and only a rising<br />

price of rice will keep this group on a par with an economy<br />

experiencing overall economic growth.<br />

Data in Table 2 do not reveal any strong links between<br />

the variables education and household labor, on the one hand,<br />

and the diversification changes, on the other. Apart from the<br />

striking difference in the level of education between heads of<br />

household in the RRD and MRD regions, this variable does<br />

not differ significantly between the diversification categories.<br />

Conclusions<br />

A household’s diversification process is complex. Our data<br />

tally with other data sources (e.g., Government of Vietnam<br />

1994, 2000) pointing at an ongoing agricultural diversification<br />

process in Vietnam. The change in the RRD especially<br />

seems more unidirectional. In the Mekong, w<strong>here</strong> rice dominates<br />

to a greater extent, different strategies—whether adopted<br />

by preference or not remains to be analyzed—seem to co-ex-<br />

434 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 2. Diversification changes in the Mekong River Delta (MRD) and Red River Delta (RRD) for rice diversification changes. a<br />

Stable high diversifiers Significant ascenders Significant descenders Stable low diversifiers<br />

Item MRD RRD MRD RRD MRD RRD MRD RRD<br />

1996 2002 1999 2002 1996 2002 1999 2002 1996 2002 1999 2002 1996 2002 1999 2002<br />

Number of households 16 16 70 70 34 34 12 12 7 7 3 3 20 20 0 0<br />

Total household income 21,353 24,164 23,332 27882 10,298 20,986 9,713 20,883 14,101 10,040 11,804 4,647 11,928 20,093 – –<br />

<strong>Rice</strong> production income 2,431 2,520 3,664 2,655 9,188 5,416 5,737 2,910 3,814 8,939 1,508 3,000 12,040 18,702 – –<br />

Nonrice crop income 6,496 3,894 2,311 1,594 124 1,133 1,255 1,736 1,551 -699 836 366 404 –176 – –<br />

Noncrop agricultural 3,117 4,862 6,513 7,674 –730 1,766 1,928 3,719 510 664 1,701 265 –1,208 461 – –<br />

income<br />

Off-farm income 9,309 12,888 10,844 15,959 1,716 12,671 793 12,518 8,226 1,136 7,759 1,016 692 1,106 – –<br />

Education (no. of y) 6.1 5.0 10.1 10.1 4.2 4.9 9.3 9.3 4.1 5.2 8.0 8.0 6.2 5.3 – –<br />

Labor, family 15–65 y 2.9 3.7 3.5 3.4 3.0 4.4 4.3 4.0 2.6 4.0 3.0 2.7 3.2 4.2 – –<br />

Total sown area (ha) 1.08 1.38 0.49 0.47 1.86 1.92 0.69 0.60 1.11 1.89 0.46 0.62 2.66 4.79 – –<br />

<strong>Rice</strong> sown area (ha) 0.56 0.98 0.42 0.41 1.77 1.76 0.60 0.52 0.79 1.59 0.41 0.58 2.51 4.72 – –<br />

Land operated (ha) 0.72 0.85 0.26 0.24 1.05 0.86 0.33 0.30 0.67 0.74 0.28 0.31 1.38 1.80 – –<br />

a All income values are expressed as 000 VND (Vietnamese dong) in constant 2002 values; US$1 = 15,279 VND (2002). T-tests for paired samples show that the difference between the two periods for the MRD is significant at<br />

the 1% level for rice area for Stable high diversifiers. Similarly, significant differences at the 1% level are found for Significant ascenders in the MRD for total household income, rice production income, noncrop agricultural income,<br />

and labor. Finally, for the MRD, a 1% level of significance is found for Stable low diversifiers for rice production income, noncrop agricultural income, total sown area, and rice sown area. Significant differences at the 5% level for<br />

the MRD are found for education (Stable high diversifiers); education (Significant descenders); total household income and labor (Stable low diversifiers). Significant differences at the 10% level in the MRD are found for labor and<br />

total sown area (Stable high diversifiers); nonrice crop income (Significant ascenders); rice production income, nonrice crop income, and rice sown area (Significant descenders); and land (Stable low diversifiers). In the RRD,<br />

significant differences at the 1% level are found for total household income, rice production income, and off-farm income for Significant ascenders. Also, significant differences at the 5% level for the RRD are found for off-farm<br />

income (Stable high diversifiers) and for total sown area and rice sown area (Significant descenders). Finally, significant differences at the 10% level are found for the RRD for total household income, total sown area, and rice sown<br />

area (Stable high diversifiers); rice area (Significant ascenders); and noncrop agricultural income (Significant descenders).<br />

Source: Information is based on sample surveys comprising 180 farm households in the MRD and 189 households in the RRD from a larger research project by the authors titled “Structural Transformation of Southeast Asia’s<br />

Agricultural Systems: Agricultural Diversification in Vietnam.”<br />

Session 14: Potential for diversification in rice-based systems to enhance rural livelihoods 435


ist. The next step in the search for determinants of diversification<br />

in this project will be to break down the material further<br />

in order to analyze whether differences in “geographical capital”<br />

reveal any spatial diversification patterns at the district<br />

and village levels (Sen 2003). Differences in physical access<br />

to product and labor markets as well as varying agroecological<br />

conditions at the village level will be research issues in this<br />

next step.<br />

References<br />

Choeng-Hoy Chung. 1997. Agricultural growth within a strategy for<br />

sustainable rural development in Vietnam. Vietnam’s Soc.<br />

Econ. Dev.: Soc. Sci. Rev. 11:10-29.<br />

Government of Vietnam. 1994. Vietnam Living Standard Survey<br />

(VLSS) 1992/1993. Hanoi (Vietnam): General Statistical Office.<br />

Government of Vietnam. 2000. Vietnam Living Standard Survey<br />

(VLSS) 1997/1998. Hanoi (Vietnam): General Statistical Office.<br />

Jirström M, Rundquist F-M. 1999. Diversify or perish! Structural<br />

transformation of agricultural systems: intensification and<br />

diversification in Vietnam. In: Cederlund K, Friberg T, Wikhall<br />

M, editors. Geografi I Lund, Essäer tillägnade Gunnar<br />

Törnqvist, Institutionen för kulturgeografi och ekonomisk<br />

geografi, Lunds Universitet. p 74-87.<br />

Sen B. 2003. Drivers of escape and descent: changing household<br />

fortunes in rural Bangladesh. World Dev. 31(3):513-534.<br />

Taylor DC. 1994. Agricultural diversification: an overview and challenges<br />

in ASEAN in the 1990s. ASEAN Econ. Bull. 10(3):264-<br />

279.<br />

Notes<br />

Authors’ address: Department of Social and Economic Geography,<br />

Lund University, Sölvegatan 12, S-223 62 Lund, Sweden.<br />

Growth of the rural nonfarm economy in Bangladesh:<br />

determinants and impact on poverty reduction<br />

Mahabub Hossain<br />

The role of nonfarm activities in promoting growth of the rural<br />

economy and reducing poverty is well documented (Hymer<br />

and Resnic 1969, Shand 1986, Ranis and Stewart 1993,<br />

Rosegrant and Hazell 2000). Termed the rural nonfarm<br />

economy (RNFE), this sector accounts for a large proportion<br />

of rural employment and income, and grows faster than agriculture<br />

with the development of the overall economy. As<br />

Rosegrant and Hazell (2000; p 81) observe, “From relatively<br />

a minor sector, often largely part-time and subsistence-oriented<br />

at the early stages of development, the rural nonfarm economy<br />

develops to become a major motor of economic growth in its<br />

own right, not only for the countryside but for the economy as<br />

a whole. Its growth also has important implications for the<br />

welfare of women and poor households, sometimes helping to<br />

offset inequities that can arise within the agricultural sector.”<br />

Generating productive employment for the growing labor<br />

force remains a formidable challenge for the Bangladesh<br />

economy. The capacity to absorb the incremental rural labor<br />

force in agriculture is extremely limited because of (1) no scope<br />

for expansion of the land frontier, (2) the intensity of cropping<br />

has almost reached the limit, and (3) the growth of crop production<br />

now depends almost entirely on technological progress,<br />

resulting in low employment elasticity of output. Recent censuses<br />

and labor-force surveys show a dramatic structural change<br />

in the composition of the rural labor force in favor of nonfarm<br />

activities (Hossain et al 2002). Questions arise, however, about<br />

whether the expansion is due to “push” or “pull” factors that<br />

determine whether it is a positive development for poverty<br />

reduction (Islam 1984, Hossain et al 1994).<br />

This paper uses primary data available from a recent<br />

survey of a nationally representative sample of rural households<br />

to (1) study the nature of the RNFE in Bangladesh, (2)<br />

analyze the determinants of participation in the RNFE, and (3)<br />

assess the impact of participation on a reduction in rural poverty.<br />

Data and methodology<br />

The data for the study are drawn from a repeat survey of a<br />

nationally representative sample. The benchmark survey was<br />

implemented in 1987-88 by the Bangladesh <strong>Institute</strong> of Development<br />

Studies (BIDS) on 1,245 rural households from 62<br />

villages in 57 districts, drawn by using a multistage random<br />

sampling method. In the first stage, 64 unions were randomly<br />

selected from the list of all unions in the country. In the second<br />

stage, one village was selected from each of the unions that<br />

best represented the union with regard to landholding size and<br />

literacy rate. A census of all households in the selected villages<br />

was conducted to stratify the households with regard to<br />

the size of landownership and land tenure. A random sample<br />

of 20 households was drawn from each village. The <strong>International</strong><br />

<strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong> (<strong>IRRI</strong>) studied the same villages<br />

in 2000-01. A sample of 30 households from each village was<br />

taken using the stratified random sampling method. The stratification<br />

was based on the wealth ranking technique of the par-<br />

436 <strong>Rice</strong> is life: scientific perspectives for the 21st century


ticipatory rural appraisal (PRA) method. The 2000-01 sample<br />

included households and their descendents covered in the 1987-<br />

88 survey. The author supervised the implementation of both<br />

surveys.<br />

This paper uses a narrow definition of the RNFE that<br />

includes only nonagricultural activities. We distinguish three<br />

types of such activities:<br />

Manual labor-based activities, such as self-employment<br />

in cottage industries, mechanics, wage employment<br />

in rural business enterprises, transport operations,<br />

and construction labor (nonfarm labor);<br />

Human capital-based occupations, such as salaried<br />

service in public- and private-sector institutions,<br />

teachers, religious leaders, lawyers, village doctors,<br />

and various types of personal services (services); and<br />

<br />

Physical and human capital-based activities, such as<br />

agro-processing, shopkeeping, peddling, petty trading,<br />

medium- and large-scale trading, and contractor<br />

services (business enterprises).<br />

We analyzed the factors influencing the participation of<br />

rural households in the RNFE to examine whether the expansion<br />

is caused by push or pull factors. The proportion of household<br />

income derived from the RNFE was used as a measure of<br />

the intensity of participation, which was related to several explanatory<br />

variables using multivariate regression. Since the<br />

value of the dependent variable is truncated at both ends (from<br />

0 to 100), the TOBIT model was used for estimating the values<br />

of the parameters. The model was estimated separately for<br />

the three groups of RNFE activities mentioned above.<br />

An income determination function was estimated with<br />

household-level data to assess the contribution of different<br />

factors to the growth of rural nonfarm income. The incomeearning<br />

capacity of the household would obviously depend on<br />

the size of land owned and operated, the number of earning<br />

members in the family, and the amount of nonland fixed assets<br />

used in productive activities. The productivity of family workers<br />

and the choice of economic activities would depend on the<br />

quality of labor embodied through investment in human resources,<br />

particularly education and training. The location of<br />

the village with regard to infrastructure such as roads and electricity<br />

connections would be an important determinant of the<br />

productivity of assets and profitability of enterprises, as the<br />

development of infrastructure opens up opportunities for nonfarm<br />

employment and processing, storage, and marketing of<br />

agricultural products (Ahmed and Hossain 1990). The explanatory<br />

variables of the model were selected in view of the above<br />

considerations.<br />

The impact of the growth of the RNFE on poverty was<br />

assessed by measuring a class of poverty indices (Foster et al<br />

1984)—the head count index, the poverty gap index, and the<br />

squared poverty gap index—and comparing them for households<br />

classified by involvement in the RNFE.<br />

Results and discussion<br />

Characterization of the rural nonfarm economy<br />

In 2000, 52% of the earning members of the households reported<br />

nonagricultural activities as the primary occupation and<br />

another 10% as the secondary occupation. The corresponding<br />

numbers estimated from the 1987 survey were 34% and 15%,<br />

respectively. In 2000, 30% of the workers reported these activities<br />

as a secondary occupation, substantially lower than the<br />

41% reported in 1987. In 2000, the major nonfarm activities<br />

were Services, accounting for 22% of all rural employment,<br />

followed by Nonfarm labor comprising 16%. Business enterprises<br />

accounted for 14% of employment but 23% of income<br />

because of higher productivity.<br />

The level of labor productivity is a good indicator of the<br />

strength of the RNFE. If labor productivity were lower than<br />

the agricultural wage rate, it would support the hypothesis of<br />

the operation of push factors behind the expansion of the RNFE.<br />

Higher labor productivity, on the other hand, is evidence of<br />

the existence of pull factors. The estimates of labor productivity<br />

obtained from the resurvey show that compared to agricultural<br />

wage rate the productivity is 10% to 40% higher for nonfarm<br />

labor and two to 3.5 times higher for Services and Business<br />

enterprises. The average productivity in the RNFE increased<br />

from US$1.43 per day in 1987 to $2.28 in 2000, an<br />

increase of 3.6% per year. The evidence thus supports the<br />

proposition of the existence of pull factors, that higher productivity<br />

and wage earnings in most nonfarm activities are luring<br />

labor from relatively low-productive, risky, and backbreaking<br />

farm activities.<br />

Factors affecting participation in the RNFE<br />

The parameters of the TOBIT model estimated to identify factors<br />

affecting participation in nonfarm activities are reported<br />

in Table 1. The following points can be noted from the findings.<br />

Participation in manual labor-based activities appears<br />

to be poverty-driven. The intensity of participation in nonfarm<br />

labor is negatively associated with the size of ownership of<br />

land and nonland fixed assets, and the level of education of<br />

the workers. The negative coefficient of the technology variable<br />

indicates that adoption of high-yielding rice varieties reduces<br />

the pressure on participation in the nonagricultural labor<br />

market. The negative association with age indicates the<br />

preference of the younger generation for nonfarm jobs over<br />

arduous agricultural wage labor. The coefficient of the dependency<br />

ratio shows a positive association of participation with<br />

subsistence pressure.<br />

Education is the most important factor affecting participation<br />

in Services. The larger size of landownership, access to<br />

land in the tenancy market, and the intensity of the adoption of<br />

modern varieties seem to reduce pressure on participation in<br />

Services (presumably for those at the lower end of the productivity<br />

scale), as indicated by the statistically significant negative<br />

coefficients for these variables. The negative coefficients<br />

of the variable representing number of workers and subsis-<br />

Session 14: Potential for diversification in rice-based systems to enhance rural livelihoods 437


Table 1. Factors affecting participation in rural nonfarm activities: estimates of a TOBIT<br />

model. a<br />

Factors Business Services Nonfarm<br />

enterprises labor<br />

Size of land owned (ha) –2.668 –10.697* –50.464*<br />

(–1.44) (–4.39) (–7.19)<br />

Area under tenancy (% of holding) –0.095 –0.226* 0.050<br />

(–1.86) (–3.80) (0.73)<br />

Age of the household head (y) –0.516* 0.504* –0.966*<br />

(–3.59) (3.38) (–4.81)<br />

Household workers (no.) 9.935* –3.002 23.642*<br />

(5.07) (–1.39) (7.49)<br />

Dependency ratio (consumers/workers) 4.328* –3.659* 1.833<br />

(3.67) (–2.82) (1.09)<br />

Average education of worker (y of schooling) 0.678 5.011* –3.925*<br />

(1.57) (10.63) (–5.86)<br />

Value of nonland fixed assets (thousand Taka) 0.071* 0.009 –0.833*<br />

(7.31) (0.86) (–5.24)<br />

Coverage of modern rice varieties 0.033 –0.102* –0.173*<br />

(% of cultivated area) (1.29) (–3.48) (–4.28)<br />

Status of infrastructure development 11.966* 3.159 7.670<br />

(villages with developed infrastructure (3.47) (0.83) (1.63)<br />

= 1)<br />

Constant term –44.417* –50.154* –10.345<br />

(–4.90) (–5.02) (–0.85)<br />

Sigma 61.288* 63.887* 72.213*<br />

(30.57) (27.85) (25.91)<br />

Log likelihood function –4,158 –3,548 –3,000<br />

a<br />

The dependent variable is measured as the share (%) of the nonfarm activity in total household income.<br />

Numbers within parentheses are asymptotic “t” values. * denotes statistical significance at the 1% probability<br />

of error.<br />

Source: Estimated from household-level data from the BIDS-<strong>IRRI</strong> surveys.<br />

tence pressure indicate a smaller family size in households<br />

engaged in service-sector activities.<br />

Major determinants for participation in Business enterprises<br />

are the accumulation of nonland assets, a larger number<br />

of workers in the household, and access to developed infrastructure.<br />

Participation is higher in younger households. It is<br />

interesting to note that the intensity of the adoption of highyielding<br />

rice varieties and the level of education of the worker<br />

do not exert a significant influence on participation in trade<br />

and business activities. Even the less-educated involve themselves<br />

in business provided they have access to capital.<br />

Contribution of the RNFE to income<br />

and reduction of poverty<br />

The average household income is estimated from the survey at<br />

$1,232 for 2000, a growth of 2.2% per year over 1987-2000.<br />

The growth in rural income was almost entirely on account of<br />

nonagricultural activities. The fastest-growing economic activities<br />

were business and services, followed by nonrice farm<br />

labor. The income from rice production and agricultural wage<br />

labor declined in absolute terms. The share of nonagriculture<br />

in total household income grew from 42% in 1987 to 54% in<br />

2000.<br />

The following regression equation best represents the<br />

variation in income earned from nonagricultural activities<br />

across the sample households:<br />

INCM = 3.56 + 399 WRKR + 0.22 CPTL + 26 EDCN (1)<br />

(0.90) (20.64) (35.11) (6.30)<br />

+ 403 INFR + 319 MIGRN<br />

(7.14) (6.57)<br />

+ 0.29 MIGRN*CPTL R-square = 0.66, F<br />

(16.84)<br />

= 607, N of cases = 1,887<br />

w<strong>here</strong> INCM is the amount of income from nonfarm sources<br />

(US dollars), WRKR is the number of family workers engaged<br />

in nonfarm activities, CPTL is the value (US$) of nonland fixed<br />

assets, EDCN is the years of schooling for the worker, INFR is<br />

a dummy variable for villages with access to paved roads and<br />

electricity, MIGRN is a dummy variable for households with a<br />

migrant member, and MIGRN*CPTL is an interaction term<br />

with migration and nonland fixed assets. The numbers within<br />

parentheses are the estimated t-values for the regression coefficient.<br />

The value of R-square indicates that about 66% of the<br />

variation in nonagricultural income across households is explained<br />

by the variables included in the model.<br />

Since the equation is estimated in linear form, the value<br />

of the regression coefficient shows the marginal returns from<br />

the factor. Thus, a worker employed in nonagriculture earns<br />

on the margin $399 per year, and the marginal rate of return on<br />

investment in nonagricultural capital is 22%. A worker earns<br />

an additional income of $26 for each year of schooling. House-<br />

438 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 2. Estimates of poverty: by primary occupation of the household head and size of land owned, 2000.<br />

Land owned (ha) Head count index a Poverty gap index a Squared poverty gap index a<br />

Agriculture. Nonagriculture Agriculture. Nonagriculture Agriculture. Nonagriculture<br />

With up to 0.2 ha 70.1 46.0 32.2 13.0 18.5 5.5<br />

0.2 to 1.0 ha 40.5 11.2 14.4 2.9 7.3 1.1<br />

Over 1.0 ha 11.1 0.0 3.1 0.0 1.2 0.0<br />

All households 48.3 30.9 20.3 8.7 11.2 3.6<br />

a For methodology of estimating poverty, see Foster et al (1984).<br />

Source: Own estimates based on household-level data from <strong>IRRI</strong> sample survey.<br />

holds with migrant members earn an additional $319. If the<br />

village had electricity connections and access to paved roads,<br />

the household earns an additional $403. The statistically significant<br />

regression coefficient of the interaction variable of<br />

migration with capital indicates that remittances help the accumulation<br />

of nonagricultural capital, and that the capital is<br />

invested in activities that give higher returns (29%).<br />

The contribution of different factors to income is estimated<br />

by dividing marginal returns by the average returns for<br />

specific factors (elasticity). It is found that 51% of the nonagricultural<br />

income is on account of nonagricultural labor, 19%<br />

on account of capital, 15% on account of education, and 8%<br />

on account of infrastructure. T<strong>here</strong> was a strong association of<br />

nonagricultural employment with education and infrastructure.<br />

Thus, investment for education and infrastructure development<br />

contributes significantly to the growth of nonfarm income. Does<br />

engagement in the RNFE help reduce poverty To answer this<br />

question, we estimated various measures of poverty and compared<br />

them for households in which at least one member is<br />

employed in nonagricultural activities with those that depend<br />

entirely on agriculture for livelihoods. Since land is a dominant<br />

asset in the rural economy, we also made similar comparisons<br />

for different landownership groups, to dissociate the<br />

effect of differential endowment of land. Table 2 reports the<br />

findings. For the entire sample, the households with income<br />

below the poverty line were estimated as 43% (head count<br />

index). The poverty ratio was 31% for households engaged in<br />

nonagricultural activities vis-à-vis 48% for households engaged<br />

exclusively in agriculture. The difference is more pronounced<br />

for measures representing intensity and severity of poverty.<br />

Thus, diversification into nonagriculture contributes to a substantial<br />

reduction in poverty. The conclusion holds when the<br />

effect of the differential endowment of land is controlled.<br />

Conclusions<br />

The capacity of agriculture to generate productive employment<br />

and to provide a decent standard of living is becoming<br />

increasingly limited in Bangladesh. Rural households recognize<br />

this constraint and have been addressing it by using the<br />

agricultural surplus for investment in education and accumulation<br />

of nonagricultural capital to facilitate occupational mo-<br />

bility from farm to nonfarm activities. As a result, the rural<br />

nonfarm sector has been expanding and has already become a<br />

major component of the rural economy. The findings in this<br />

paper demonstrate that the RNFE in Bangladesh is a vibrant<br />

subsector contributing to productivity growth and reduction<br />

of poverty. Greater public-sector investment in education and<br />

expansion of the physical infrastructure will accelerate the process<br />

of expansion of the nonfarm sector, and contribute to the<br />

sharing of benefits with resource-poor households.<br />

References<br />

Ahmed R, Hossain M. 1990. Development impact of rural infrastructure<br />

in Bangladesh. IFPRI <strong>Research</strong> Report No. 83. Washington,<br />

D.C. (USA): <strong>International</strong> Food Policy <strong>Research</strong> <strong>Institute</strong>.<br />

Foster JE, Greer E, Thorbeck E. 1984. A class of decomposable poverty<br />

measures. Econometrica 52(3):761-766.<br />

Hossain M, Rahman M, Bayes A. 1994. Rural non-farm economy in<br />

Bangladesh: a dynamic sector or a sponge of absorbing surplus<br />

labor SAAT Working Paper, <strong>International</strong> Labor Organization,<br />

New Delhi.<br />

Hossain M, Bose ML, Chowdhury A. 2002. Changes in agrarian<br />

relations and livelihoods in rural Bangladesh: insights from<br />

repeat village studies. In: Ramachandran VK, Swaminathan<br />

M, editors. Agrarian studies. New Delhi (India): Tulika Books.<br />

p 369-391.<br />

Hymer S, Resnick S. 1969. A model of an agrarian economy with<br />

non-agricultural activities. Am. Econ. Rev. 59(4):493-506.<br />

Islam R. 1984. Non-farm employment in rural Asia: dynamic growth<br />

or proletarization J. Contemp. Asia 14:306-324.<br />

Ranis G, Stewart F. 1993. Rural non-agricultural activities in development:<br />

theory and application. J. Dev. Econ. 40:175-201.<br />

Rosegrant MW, Hazell PBR. 2000. Transforming the rural Asian<br />

economy: the unfinished revolution. Hong Kong: Oxford<br />

University Press.<br />

Shand R. 1986. Off-farm employment in the development of rural<br />

Asia. Australian National University, Canberra.<br />

Notes<br />

Author’s address: Economist and head, Social Sciences Division,<br />

<strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>, DAPO Box 7777, Metro<br />

Manila, Philippines, e-mail: m.hossain@cgiar.org.<br />

Session 14: Potential for diversification in rice-based systems to enhance rural livelihoods 439


SESSION 15<br />

Challenges to expanding rice production<br />

in unfavorable environments<br />

CONVENER: S. Tobita (JIRCAS)<br />

CO-CONVENER: R. Lafitte (<strong>IRRI</strong>)


In vitro selection of somaclonal and gametoclonal variants<br />

for salt tolerance in rice<br />

Nguyen Thi Lang, Dang Minh Tam, Hiromi Kobayashi, and Bui Chi Buu<br />

Tissue-cultured cell lines can be selected in vitro for resistance<br />

to various stresses. Selection is done by placing a stresscausing<br />

agent in tissue cultures containing dividing cells. Tissue<br />

culture techniques have been widely used for breeding<br />

purposes, especially in selection for stress tolerance. Tissue<br />

culture is a source of genetic variability that gives rise through<br />

genetic modifications during the process of in vitro culture to<br />

a phenomenon called somaclonal variation. The possible causes<br />

of somaclonal variation include chromosome aberrations, DNA<br />

amplification, and the occurrence of transposable elements.<br />

Salt tolerance is an important plant character in areas w<strong>here</strong><br />

seedling growth is a problem. This paper reports on the current<br />

status of tissue culture technology at the Cuu Long Delta<br />

<strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong> (CLRRI). Our primary objective is to<br />

demonstrate that useful germplasm can be obtained from tissue<br />

culture and another way found to produce salt-tolerant lines<br />

using anther culture techniques in which anthers of F 1 hydrids<br />

having one or both parents with salt tolerance are cultured. A<br />

significant feature of this work is to determine what in vitro<br />

treatment, including concentration of the stressing agent and<br />

the period of time in culture, will produce the greatest probability<br />

of field-tolerant plants for a specific environment. This<br />

study aimed to create genetic variability in rice cell culture to<br />

obtain salt-tolerant plants through in vitro selection.<br />

Materials and methods<br />

Twelve rice cultivars were used to conduct in vitro selection<br />

for salt stress. The work on salt stress tolerance was done at<br />

concentrations of 0.5%, 1.0%, and 1.5% NaCl.<br />

Mature seeds were dehusked and surface-sterilized with<br />

70% ethyl alcohol for 30 sec and then for 30 min with 5%<br />

sodium hypochlorite (commercial bleach is mainly hypochlorite).<br />

Surface-sterilized seeds were rinsed several times with<br />

sterile distilled water before inoculation on callus induction<br />

medium, consisting of MS basal organic and inorganic components<br />

(Murashige and Skoog 1962) supplemented with 3.0%<br />

sucrose, 2,4-D at 1.0–2.0 mg L –1 , and kinetin at 0.0–0.5 mg<br />

L –1 (Nguyen Thi Lang 2002).<br />

The cultures were incubated under both dark and light<br />

conditions (16 h day/8 h night). The temperature was maintained<br />

at 22–25 ºC. The MS culture medium was supplemented<br />

with 3.0% sucrose, 0.8% agar, and various concentrations of<br />

growth regulators. The medium pH was adjusted to 5.8 prior<br />

to autoclaving at 15 psi for 20 min.<br />

The basal medium for rice tissue culture used is similar<br />

to that developed by Murashige and Skoog (1962). Unlike<br />

many other crops, rice requires a unique growth regulator combination,<br />

sucrose concentration, and light regime for each cultivar.<br />

Culture vessels are either glass screw vials or jars. The<br />

vials contain 10 mL of medium and are used for callus initiation.<br />

The jars containing 20 mL of medium are used after embryogenic<br />

callus, which is isolated and ready for plant regeneration.<br />

For callus induction, mature seeds are surface-sterilized<br />

and placed on the appropriate medium for a cultivar. At the<br />

end of 28 days—referred to as a “passage”—the original explant<br />

and all of its associated calli are transferred to a fresh<br />

medium. After the second passage, embryogenic calli are isolated<br />

and transferred again to a fresh medium. Embryogenic<br />

calli are usually yellow or cream-colored and dense in appearance.<br />

For long-term maintenance, embryo calli must be carefully<br />

selected and all nonembryogenic and dead calli removed<br />

at each transfer.<br />

Three crosses were tested for callus induction and plant<br />

regeneration. The F 1 seeds were grown in pots in the<br />

screenhouse, and panicles were collected at the stage when<br />

the auricle distance of the flag leaf to that of the subtending<br />

leaf was 5–10 cm. The anthers were plated in various callusinduction<br />

media when the pollen grains were at the mid-uninucleate<br />

to early binucleate stage of development. The plated<br />

anthers were kept in cold at 10 °C for 8 d and were then transferred<br />

under dim light at 25 °C until calli formed.<br />

Calli of about 1 mm in diameter were plated in N 6 + 2<br />

mg L –1 2,4-D + 1 mg L –1 NAA medium and incubated under<br />

1,000 lux at 25 °C for 4 wk. The calli were then transferred to<br />

MS + 1 mg L –1 kinetin + 0.5 mg L –1 NAA + 2 mg L –1 BA<br />

medium, until the plantlets were ready for transfer to normal<br />

growth conditions.<br />

The plantlets were grown in nutrient solution for 2 wk.<br />

The plantlets from each callus were individualized, with each<br />

one considered as a line. These were then transferred to pots<br />

and grown in the phytotron until maturity.<br />

Seeds were then surface-sterilized with 0.1% HgCl 2 for<br />

2–3 min and rinsed thoroughly with distilled water. The sterilized<br />

seeds were soaked in water for 24 h and incubated for 48<br />

h at 30 ºC. The pregerminated seeds were sown, two seeds per<br />

hole and 10 holes per variety, on a styrofoam sheet with 100<br />

holes with a nylon net bottom. The sheet was floated in distilled<br />

water for 4 d in nutrient solution in a plastic tray and<br />

salinized to EC = 6 dS m –1 by NaCl. After 4 d, the seedlings<br />

were salinized to EC = 12 dS m –1 by adding NaCl to the nutrient<br />

solution. The culture solution was renewed weekly and its<br />

pH was maintained daily at 5.0 by adding either 1 N NaOH or<br />

442 <strong>Rice</strong> is life: scientific perspectives for the 21st century


HCl. After 2 wk of salinization with EC = 12 dS m –1 , salinity<br />

symptoms were scored using a modified standard evaluation<br />

system (SES).<br />

Results<br />

Table 1. Plant regeneration of rice calli under NaCl stress.<br />

Variety<br />

% callus regeneration<br />

0.5% NaCl 1% NaCl 1.5% NaCl<br />

Pokkali 100.0 100.0 51.3<br />

AS996 100.0 55.6 68.8<br />

Nep Ao Gia 100.0 100.0 60.0<br />

Trang Diep 92.9 74.2 55.6<br />

Trang Thai Lan 100.0 100.0 73.1<br />

Mong Chim Roi 100.0 100.0 63.6<br />

KDM 105 75.0 92.9 44.1<br />

Doc Phung 100.0 100.0 64.0<br />

Doc Do 100.0 100.0 75.0<br />

Soc Nau 100.0 100.0 91.8<br />

IR29 (check) 100.0 78.6 47.6<br />

Somatic mutation<br />

Since the first successful plant regeneration by tissue culture,<br />

many variant plants have been obtained through somaclonal<br />

variation.<br />

Time for callus initiation was from 5 to 10 days after<br />

placing seeds on agar medium. The ability to form calli of<br />

cultivars on various media showed different results:<br />

1 Very good I MS + 2,4-D (2 mg L –1 )<br />

2 Good II MS + 2,4-D (1 mg L –1 )<br />

3 Medium III N 6 + 2,4-D (2 mg L –1 )<br />

4 Average IV N 6 + 2,4-D (1 mg L –1 )<br />

5 Dead<br />

In the effect of media on embryo callus formation, the<br />

medium MS + 2,4-D (2 mg L –1 ) was not significantly different<br />

from other media. For cultivar effect, Doc Do was considered<br />

as the best variety, followed by Pokkali, Soc Nau, Nep Ao<br />

Gia, Mong Chim Roi, and KDM 105, which were also viewed<br />

as more suitable genotypes for embryogenic callus formation<br />

ability than others.<br />

In the effect of media and cultivar interaction, the treatments<br />

Doc Do × MS + 2,4-D (2 mg L –1 ) and Pokkali × MS +<br />

2,4-D (2 mg L –1 ) obtained very good results. Trang Thai Lan<br />

× MS + 2,4-D (2 mg L –1 ) and KDM 105 × MS + 2,4-D (2 mg<br />

L –1 ) obtained good results on embryogenic callus formation<br />

ability.<br />

The effect of various concentrations of 2,4-D medium<br />

on callus induction showed that callus initiation was observed<br />

after 3 d of culture in all cultivars, irrespective of the light or<br />

dark period.<br />

The result showed that medium MS + 2,4-D (2 mg L –1 )<br />

was more suitable to embryogenic callus formation than the<br />

others.<br />

The effect of cultivars on embryogenic callus formation<br />

percentage indicated that Doc Do, Soc Nau, Nep Ao Gia, and<br />

AS996 were genotypes that exhibited more suitability to develop<br />

in cultural medium than others.<br />

For interactions on embryogenic callus formation percentage,<br />

treatments Doc Do × MS + 2,4-D (1 mg L –1 ) and Nep<br />

Ao Gia × MS + 2,4-D (2 mg L –1 ) obtained a percentage of<br />

embryogenic callus formation of 86.7% and 80%, which were<br />

significantly different at the 0.01 probability level, respectively.<br />

In conclusion, Doc Do, Nep Ao Gia, and other genotypes<br />

such as Pokkali and Soc Nau were also suitable for embryogenic<br />

callus formation. The optimum medium for embryogenic<br />

callus formation was MS + 2,4-D (2 mg L –1 ).<br />

Nonembryogenic (NE) calli were not regenerable when<br />

transferred to the regeneration MS medium supplemented with<br />

1.0 mg L –1 benzylaminopurine (BAP) and 0.5 mg L –1 of naphthalene<br />

acetic acid (NAA). On the other hand, when embryogenic<br />

(E) calli were transferred to the regeneration medium,<br />

root initiation and callus differentiation were observed within<br />

1 wk of incubation. Visible shoot formation was noted 4 wk<br />

later on cultivar Trang Thai Lan (82 shoots per E callus from<br />

0.5 to 1.0 cm, the average percentage of E calli from shoots<br />

was 18%) and Trang Diep (3 shoots per E callus, the average<br />

percentage of E calli from shoots was 18%). The other cultivars<br />

will continue to be observed.<br />

For salt-treatment studies, attempts to produce embryogenic<br />

calli were conducted in saline medium as 0.5%, 1.0%,<br />

and 1.5% NaCl added to the callusing medium specific for<br />

each genotype, as per results obtained in the initial experiment<br />

(Table 1). Induced calli were excised 2 wk after inoculation of<br />

explants, transferred to fresh medium for proliferation for 21<br />

d, and then transferred to the regeneration medium.<br />

NaCl (1.5%) added to the regeneration medium increased<br />

the percentage of calli showing regeneration by 90.8% and<br />

75.0% in Soc Nau and Doc Do. In Trang Thai Lan, AS996,<br />

and Pokkali, 73.1%, 68.8%, and 51.3% reduction in the number<br />

of regenerating calli was recognized. Salt-stress-sensitive<br />

genotype IR29 did not clearly respond.<br />

Anther culture of F 1<br />

crosses<br />

Haploid plants are useful for practical and genetic studies.<br />

Anther and pollen culture are simple methods for obtaining<br />

haploid plants. Selection efficiency also increases because<br />

anther culture is based on gametic instead of sporophytic selection.<br />

The probability of obtaining a desired genotype in<br />

haploid (1/2 n) is much higher than in diploid (1/4 n) w<strong>here</strong> n<br />

= number of genes controlling a particular character. The<br />

crosses from Teqing/Doc Phung, Tequing/Pokkali, and<br />

Tequing/Soc Nau have been made. Variation in culturability<br />

in terms of callus induction and plant regeneration among these<br />

crosses was observed (Table 2). The results indicate that<br />

Teqing/Doc Phung and Tequing/Pokkali were induced on calliproducing<br />

green plants (3.1, 18.2, and 0.9 reciprocity) (Table<br />

2) with the medium N 6 + 2 mg L –1 2,4-D + 1 mg L –1 NAA and<br />

plant regeneration of Teqing/Doc Phung, Tequing/Pokkali, and<br />

Session 15: Challenges to expanding rice production in unfavorable environments 443


Table 2. Percentage of embryogenic calli formation (%) from F 1 .<br />

Anthers Callus Calli- Green Albino Anther<br />

Cross on plates production Calli producing plant plant culture<br />

(no.) (%) plated green plants production production plants<br />

(%) (%) (%) (%)<br />

Tequing/Doc Phung 480 92.0 64 3.1 17.8 48.4 9.1<br />

Tequing/Pokkali 678 186.7 192 18.2 14.4 75.0 39.1<br />

Tequing/Soc Nau 491 47.5 113 0.9 0.9 53.6 0<br />

Tequing/Soc Nau obtained from the medium MS + 1 mg L –1<br />

kinetin + 0.5 mg L –1 NAA + 2 mg L –1 BA. In screening of<br />

anther culture-derived lines in a salt-screening nursery, a total<br />

of 23 lines were evaluated for salt tolerance. Among 23 lines<br />

tested, 3 promising lines from Tequing/Doc Phung were identified<br />

to be better than the resistant check.<br />

Estimation of salt tolerance in saline soil<br />

A total of 104 A4 lines, the original variety having been used<br />

as a control, were tested in normal and saline fields. Some 23<br />

lines exhibited salt tolerance. Variations were considerable<br />

among the lines. Nine lines were selected for further observation.<br />

Grain filling per panicle, 1,000-grain weight, spikelets<br />

m –2 , and yield were statistically different at the 5% level of<br />

probability from the original variety.<br />

Conclusions and suggestions<br />

MS + 2,4-D (2 mg L –1 ) is considered as a medium suitable for<br />

cultivating target cultivars. The genotypes Doc Do and Nep<br />

Ao Gia and others such as Pokkali, Soc Nau, Mong Chim Roi,<br />

and KDM 105 are also suitable for embryogenic callus formation.<br />

The regeneration MS medium supplemented with 0.5<br />

mg L –1 BAP and 1.0 mg L –1 NAA affected Trang Thai Lan (82<br />

shoots per E callus from 0.5 to 1.0 cm, obtained 18% E calli<br />

from shoots) and Trang Diep (3 shoots per E callus, obtained<br />

18% E calli from shoots). The other cultivars have been continuously<br />

observed.<br />

In NaCl 0.5% medium, E calli of all cultivars developed<br />

normally. Both treated and nontreated calli that survived in<br />

1.0% and 1.5% NaCl were of considerable benefit for further<br />

studies.<br />

Variation in culturability in terms of callus induction and<br />

plant regeneration among these crosses was observed. The results<br />

indicated that Teqing/Doc Phung and Tequing/Pokkali<br />

were induced on calli-producing green plants (3.1, 18.2, and<br />

0.9 reciprocity). Among 23 lines tested, three promising lines<br />

from Tequing/Doc Phung were identified to be better than the<br />

resistant check.<br />

The performance test of the 23 selected lines in the field<br />

was within 10 dS m –1 . The resulting three lines developed from<br />

this study have a potential for salt tolerance since their agronomic<br />

characters are much better than those of the original<br />

cultivar.<br />

References<br />

Chu CC, Wang CC, Sun CS, Yin KC, Chu CY, Bi FY. 1975. Establishment<br />

of an efficient medium for anther culture of rice<br />

through comparative experiments on nitrogen sources. Sci.<br />

Sin. 18:659-668.<br />

Murashige T, Skoog F. 1962. A revised medium for rapid growth<br />

and bioassay with tobacco tissue cultures. Physiol. Plant.<br />

15:473-497.<br />

Nguyen Thi Lang. 2002. Protocol for basics of biotechnology. Ho<br />

Chi Minh City (Vietnam): Agricultural Publishing House.<br />

Notes<br />

Authors’ addresses: Nguyen Thi Lang, Dang Minh Tam, and Bui<br />

Chi Buu, Cuu Long Delta <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>, Omon, Can<br />

Tho, Vietnam; Hiromi Kobayashi, National Agrobiological<br />

<strong>Research</strong> <strong>Institute</strong>, Tsukuba, Ibaraki, Japan, e-mail:<br />

ntlang@hcm.vnn.vn.<br />

444 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Submergence damage in rice and challenges in expanding<br />

the crop’s adaptability to submerged conditions in West<br />

and Central Africa<br />

Koichi Futakuchi<br />

In West and Central Africa (WCA), deepwater area accounts<br />

for 6% of the whole rice-growing area, mainly in the floodplains<br />

of large rivers such as the Niger River; and rainfed lowland<br />

and mangrove swamp account for 20% and 7%, respectively<br />

(Jones 1999). About one-third of all rice cultivation area<br />

faces danger from waterlogging. In addition, submergence<br />

could occur even in irrigated lowland at the seedling stage<br />

because of poor water management.<br />

In the floodplains, sudden flood can submerge the crop<br />

and waterlogging could continue during the growth of rice. To<br />

avoid submergence damage, farmers sometimes dibble rice<br />

seeds on ridges (Singh et al 1997). In some locations such as<br />

Mopti in Mali and the Sokoto Rima River floodplains in Nigeria,<br />

Oryza glaberrima, which is the other cultivated rice species<br />

besides O. sativa, and domesticated in WAC more than<br />

3,500 years ago (Jones et al 1997), is still cultivated in spite of<br />

its unfavorable traits in yield formation, that is, lodging and<br />

grain shattering, perhaps because of its high adaptability to<br />

waterlogging. Traditional O. sativa cultivars are preferably<br />

cultivated by farmers, too. One example is Gambiaka, which<br />

is considered to be adaptable to medium-deepwater conditions<br />

(50 to 100 cm deep). This cultivar has more vigorous seedling<br />

growth than improved cultivars; Gambiaka’s height and dry<br />

weight of 21-day-old seedlings were 42.3 cm and 123 mg, while<br />

those of WITA 4, WARDA’s improved cultivar released in<br />

Nigeria for the rainfed lowland ecology, were 28.9 cm and 75<br />

mg, respectively. Gambiaka t<strong>here</strong>fore has a higher possibility<br />

to escape from submergence than WITA 4.<br />

In savannah and forest zones in WCA, inland valleys<br />

prevail and rice in valley bottoms experiences waterlogging<br />

for several days after excessive rainfall. Farmers transplant<br />

large older-aged seedlings in fields to keep them away from<br />

possible submergence. However, transplanting of such seedlings<br />

is associated with lower yield than appropriate-aged seedlings<br />

because larger seedlings receive more damage at transplanting<br />

and have a shorter remaining growth duration after<br />

transplanting, which cannot compensate for the damage.<br />

Waterlogging and rice plants<br />

Damage to rice plants under waterlogging<br />

<strong>Rice</strong> is an aquatic plant and is able to grow well under flooded<br />

conditions. In deepwater conditions, rice plants promote the<br />

elongation of the coleoptile, leaf, or stem, which can reduce<br />

the danger from submergence. However, rice receives severe,<br />

sometimes fatal, injury when it is under complete overhead<br />

submergence conditions for several days, especially for juvenile<br />

plants.<br />

Water has slower rates of gas exchange, less capacity to<br />

hold gases inside, and a higher extinction coefficient for light<br />

than the air. Floodwater is usually turbid so that severe shading<br />

occurs in the water. Under complete submergence, t<strong>here</strong>fore,<br />

photosynthesis and respiration of rice plants are depressed.<br />

Low rates of gas diffusion cause the accumulation of physiologically<br />

active gases such as ethylene produced in situ in the<br />

plant (Jackson and Ram 2003). Visible symptoms of rice plants<br />

under submergence are faster elongation of a few leaves, yellowing<br />

of old leaves, slow or negative dry-matter growth, and<br />

shoot decay. After a reduction in water levels, most leaves or<br />

the whole shoot may collapse. Some can die and the survivors<br />

also suffer from poor rates of new leaf emergence and lodging<br />

(Jackson and Ram 2003). When rice plants under submergence<br />

succeed in re-contacting with the air because of elongation and<br />

survive, they are highly likely to lodge after the water level<br />

recedes.<br />

Varietal development for tolerance<br />

of complete submergence<br />

Physiological mechanisms of submergence tolerance are well<br />

elucidated in rice compared with other abiotic constraints such<br />

as drought. Jackson and Ram (2003) have widely reviewed<br />

mechanisms of injury by and tolerance of complete submergence<br />

in rice referring to both current and pioneer studies. The<br />

best source of submergence tolerance in rice was already identified,<br />

which is Indian cultivar FR13A selected from a local<br />

landrace. Mackill et al (1993) introduced the tolerance into an<br />

agronomically useful cultivar by conventional breeding. Although<br />

the tolerance was considered to be a quantitative trait<br />

controlled by several genes, studies with molecular markers<br />

revealed that a single locus, Sub 1, controlled most of the tolerance<br />

(Xu and Mackill 1996). This locus was mapped on rice<br />

chromosome 9, and a fine-scale map around Sub 1 was also<br />

developed (Xu et al 2000). The markers mapped close to Sub<br />

1 can reduce the need for time-consuming and high-cost field<br />

screening.<br />

Plant types adaptable to waterlogging in WCA<br />

In the floodplains of large rivers, waterlogging could continue<br />

for a long time. Since existing cultivars with tolerance of complete<br />

submergence can survive or receive less damage than<br />

normal cultivars under submergence of several days, their type<br />

is not suitable. An elongation type that can escape from sub-<br />

Session 15: Challenges to expanding rice production in unfavorable environments 445


Relative elongation rate to the initial height at day 0 (%)<br />

80<br />

TOG 5810 TOG 6283<br />

60<br />

40<br />

20<br />

0<br />

80<br />

CG 14 CG 20<br />

60<br />

40<br />

20<br />

0<br />

80<br />

60<br />

Norin 30<br />

IR36<br />

40<br />

20<br />

0 0 5 10 15 20 25 0 5 10 15 20 25<br />

Days of submergence<br />

Fig. 1. Changes in the rate of increased height to the initial height with the time of the<br />

submergence treatment (cited from Futakuchi et al 2001). Vertical bars indicate standard<br />

deviation of three replications. Closed circles = submergence; open circles =<br />

nonsubmergence (control).<br />

mergence is desirable. To tolerate complete submergence<br />

caused by sudden flooding until plants re-contact with the atmosp<strong>here</strong><br />

by elongation, it will also be desirable for them to<br />

have submergence tolerance to a certain extent. Vigorous initial<br />

growth will be important, too, to reduce the danger from<br />

submergence. Resistance to lodging or recovering ability from<br />

lodging after a water level reduction will be required for practical<br />

cultivars acceptable to farmers.<br />

In inland valley bottoms, submergence-tolerant types will<br />

be useful. In existing cultivars such as FR13A, however, the<br />

tolerance does not mean unharmed by submergence (Jackson<br />

and Ram 2003). Although such cultivars relatively tolerate submergence,<br />

they also have some damage and collapse more or<br />

less after submergence for several days. <strong>Rice</strong> has well-developed<br />

aerenchyma and it receives much less damage when keep-<br />

ing in contact with the air by leaves or other organs. Since<br />

sudden flooding could occur in the bottoms, the same type as<br />

with the floodplains mentioned above will be highly suitable.<br />

Setter and Laureles (1996) have reported that t<strong>here</strong> is a<br />

trade-off between stimulated elongation and tolerance in completely<br />

submerged conditions, suggesting difficulty in developing<br />

cultivars with both elongation ability and tolerance.<br />

Futakuchi et al (2001b) have tested Oryza glaberrima in relation<br />

to elongation ability and tolerance under submergence.<br />

Four O. glaberrima lines, out of which two were identified as<br />

submergence-adaptable types (TOG 5810 and TOG 6283) and<br />

the others were identified as upland-adaptable types (CG 14<br />

and CG 20), were cultivated in pots and submerged at the end<br />

of the stem elongation stage with two O. sativa checks (Norin<br />

30 and IR36). Figure 1 depicts changes in relative elongation<br />

446 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Photosynthetic rate (nmol cm –2 h –1 )<br />

1,800<br />

1,600<br />

1,400<br />

1,200<br />

1,000<br />

800<br />

600<br />

400<br />

200 TOG 5810<br />

0<br />

TOG 6283<br />

1,800<br />

1,600<br />

1,400<br />

1,200<br />

1,000<br />

800<br />

600<br />

400<br />

200<br />

0<br />

CG 14<br />

CG 20<br />

1,800<br />

1,600<br />

1,400<br />

1,200<br />

1,000<br />

800<br />

600<br />

400<br />

200 Norin 30<br />

IR36<br />

0<br />

0 5 10 15 20 25 0 5 10 15 20 25<br />

Days of submergence<br />

Fig. 2. Changes in the rate of photosynthetic oxygen evolution in a leaf slice with the time of<br />

the submergence treatment (cited from Futakuchi et al 2001). Vertical bars indicate standard<br />

deviation of three replications.<br />

rate—the percentage ratio of increased height to the initial<br />

height—after the beginning of the submergence treatment.<br />

Submergence promoted elongation for all lines/varieties tested<br />

but the extent of elongation was much larger in O. glaberrima<br />

than in O. sativa. Judging from the elongation ability, O.<br />

glaberrima should have much less tolerance of submergence<br />

than the O. sativa checks. However, O. glaberrima maintained<br />

high photosynthetic rates, which were determined by oxygen<br />

electrode, compared with Norin 30, and rates similar to those<br />

of IR36 (Fig. 2). The same result was obtained with chlorophyll<br />

content. O. glaberrima had better tolerance than expected<br />

from elongation ability under submergence.<br />

Out of the O. glaberrima lines tested, CG 14 showed the<br />

fastest elongation soon after submergence (Fig. 1) though the<br />

line had been identified as an upland type. Thirty interspecific<br />

progenies from the cross of CG 14 and an O. sativa cultivar<br />

(WAB56-104) were tested in terms of elongation ability in<br />

medium-deepwater: 50 cm deep (Futakuchi et al 2001a). This<br />

treatment started at maximum tillering and continued for 4<br />

weeks. CG 14 showed the best elongation at 2 wk after the<br />

treatment and a few interspecific progenies rivaled CG 14<br />

though elongation was promoted for all interspecifics during<br />

the treatment. One week after the end of the treatment, however,<br />

the actual plant height of the interspecifics in the control<br />

(always in shallow-water conditions) caught up with that of<br />

the interspecifics grown in the treatment. Yield and tiller numbers<br />

were much depressed by the medium-deepwater treatment.<br />

However, lodging was observed only with CG 14.<br />

The growth of O. glaberrima at the seedling stage is<br />

vigorous. For example, plant height and dry weight of CG 14<br />

at 21 days after seeding were 46.4 cm and 54.3 mg, while those<br />

of Bouake 189, a leading O. sativa variety for lowlands in<br />

Côte d’Ivoire, were 30.4 cm and 38.0 mg, respectively.<br />

Session 15: Challenges to expanding rice production in unfavorable environments 447


Oryza glaberrima could be a source to develop plant<br />

types adaptable to waterlogging in WCA, providing ability to<br />

escape from and moderately tolerate submergence. Since the<br />

two O. glaberrima lines, TOG 5810 and TOG 6283, that had<br />

been identified as submergence-adaptable types prior to the<br />

trial did not have better tolerance than IR36 (Fig. 2), it might<br />

be difficult to identify lines with strong tolerance of submergence<br />

in O. glaberrima. The problem of O. glaberrima is susceptibility<br />

to lodging. This could be overcome by crossing with<br />

O. sativa varieties having strong columns.<br />

References<br />

Futakuchi K, Audebert A, Jones MP. 2001a. Stem elongation of interspecific<br />

O. sativa × O. glaberrima progenies in deep water<br />

conditions. Jpn. J. Crop Sci. 70(extra issue 2):279-280.<br />

Futakuchi K, Jones MP, Ishii R. 2001b. Physiological and morphological<br />

mechanism of submergence resistance in African rice<br />

(Oryza glaberrima Steud.). Jpn. J. Trop. Agric. 45:8-14.<br />

Jackson M, Ram PC. 2003. Physiological and molecular basis of<br />

susceptibility and tolerance of rice plants to complete submergence.<br />

Ann. Bot. 91:227-241.<br />

Jones MP, Dingkuhn M, Aluko GK, Mande S. 1997. Interspecific<br />

Oryza sativa L. × O. glaberrima Steud. progenies in upland<br />

rice improvement. Euphytica 92:237-246.<br />

Jones MP. 1999. Food security and major technological challenges:<br />

the case of rice in sub-Saharan Africa. In: Horie T, Geng S,<br />

Amano T, Inamura T, Shiraiwa T, editors. World food security<br />

and crop production technologies for tomorrow. Proceedings<br />

of the <strong>International</strong> Symposium, October 1998. Kyoto (Japan):<br />

Kyoto University. p 57-64.<br />

Mackill DJ, Amante MM, Vergara BS, Sarkarung S. 1993. Improved<br />

semi-dwarf rice lines with tolerance to submergence of seedlings.<br />

Crop Sci. 33:749-753.<br />

Setter T, Laureles E. 1996. The beneficial effect of reduced elongation<br />

growth on submergence tolerance in rice. J. Exp. Bot.<br />

47:1551-1559.<br />

Singh BN, Fagade S, Ukwungwu MN, Williams C, Jagtap SS,<br />

Oladimeji O, Efisue A, Okhidievbie O. 1997. <strong>Rice</strong> growing<br />

environments and biophysical constraints in different<br />

agroecological zones of Nigeria. Met. J. 2:35-44.<br />

Xu K, Mackill DJ. 1996. A major locus for submergence tolerance<br />

mapped on rice chromosome 9. Mol. Breed. 2:219-224.<br />

Xu K, Xu X, Ronald PC, Mackill DJ. 2000. A high-resolution linkage<br />

map of the vicinity of the rice submergence tolerance locus<br />

Sub 1. Mol. Gen. Genet. 263:681-689.<br />

Notes<br />

Author’s address: The Africa <strong>Rice</strong> Center (WARDA), 01 BP 2031<br />

Cotonou, Benin, e-mail: k.futakuchi@cgiar.org.<br />

Ecological, morphological, and physiological<br />

aspects of drought adaptation of rice in upland<br />

and rainfed lowland systems<br />

Shu Fukai and Akihiko Kamoshita<br />

Many rice-growing areas in the world do not enjoy the availability<br />

of full irrigation water, and a rice crop often experiences<br />

drought at some time during its growth. Responses of<br />

different genotypes to water stress have been studied for a long<br />

time, and several physiological and morphological characters<br />

have been suggested to be responsible for drought tolerance in<br />

rice. Grain yield of some genotypes is affected less than others<br />

by drought, but genotypic adaptation to drought is not consistent<br />

across different drought conditions. The single factor determining<br />

genotypic variation in yield under drought conditions<br />

is crop phenology, particularly flowering time. However,<br />

within the same phenology group, no particular physiological<br />

or morphological characters have been found to be consistently<br />

responsible for genotypic variation in yield. This lack of universally<br />

useful traits has resulted in rather slow progress in<br />

developing drought-tolerant cultivars in rice (Fukai et al 1999).<br />

Some of the inconsistency in genotypic yield performance<br />

is caused by different types of drought that the rice crop<br />

may encounter. Ecological factors such as the presence of flood<br />

water before drought develops, as is often the case in rainfed<br />

lowland rice, are now recognized to affect genotypic adapta-<br />

tion to drought. For example, deep-root characters that are<br />

useful to minimize the adverse effects of drought in some upland<br />

conditions may not be expressed fully under rainfed lowland<br />

conditions w<strong>here</strong> anaerobic soil conditions prevent the<br />

development of deep root systems. Timing of drought is another<br />

ecological factor; if drought develops during the vegetative<br />

stage, the genotype’s ability to recover from drought is<br />

important, w<strong>here</strong>as, if drought develops around flowering time,<br />

the plant’s ability to tolerate drought becomes a key factor in<br />

producing higher yield than with other genotypes. This paper<br />

describes physiological and morphological characters that are<br />

useful under different types of drought (Table 1), and how that<br />

understanding can assist in the selection of drought-tolerant<br />

rice cultivars.<br />

Terminal drought<br />

Among genotypes of a similar maturity type, genotypes that<br />

can maintain high leaf water potential are often advantageous<br />

in producing higher yield under terminal drought conditions<br />

(Jongdee et al 2002, Pantuwan et al 2002). Higher water po-<br />

448 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. Physiological and morphological characters of<br />

drought tolerance under each drought type.<br />

Type of drought<br />

Terminal drought<br />

Intermittent drought<br />

Vegetative-stage drought<br />

Primary/secondary characters<br />

Early flowering<br />

Short delay in flowering<br />

High leaf water potential<br />

Low leaf death score<br />

Deep-root system<br />

Late flowering<br />

Longer delay in flowering<br />

Large green leaf area<br />

Tillering after drought period<br />

tential and associated turgor maintenance and carbohydrate<br />

supply to spikelets would assist with fertilization and hence<br />

reduce spikelet sterility.<br />

Positive turgor is required for stem extension and exsertion<br />

of panicles. Delay in flowering will be small with maintenance<br />

of turgor, and this is related to higher yield under terminal<br />

drought (Pantuwan et al 2002).<br />

Under terminal drought, the maintenance of favorable<br />

water conditions for reproductive organ growth and securing<br />

adequate grain sink size are a primary drought-tolerance mechanism,<br />

and a conservation strategy of water use may be considered<br />

to be effective. Since water runs out by maturity in terminal<br />

drought, prolonging water availability to the plants is required<br />

for higher yield. To achieve this, water may be extracted<br />

rather slowly by a smaller root system or smaller shoot system<br />

with reduced water demand (Pantuwan et al 2002).<br />

Intermittent drought<br />

In contrast to terminal drought, intermittent drought is broken<br />

by a rainfall event, and hence t<strong>here</strong> is no strong need for conservation<br />

of water as such. A deep root system with higher<br />

root density is likely to be useful under these conditions. Association<br />

between high root length density and the amount of<br />

water extracted has been well demonstrated (Lilley and Fukai<br />

1994), and, under upland conditions particularly, these root<br />

characters contribute to high yield. With intermittent drought,<br />

rainfall can replenish soil water, and hence cycles of water<br />

extraction-replenishment would take place. Under these conditions,<br />

well-developed root systems can take advantage of<br />

extracting water to a greater extent. This may not apply to terminal<br />

water conditions because the rate of water extraction<br />

would be faster and the duration of water extraction shorter<br />

(Lilley and Fukai 1994), resulting in early exhaustion of a limited<br />

amount of stored water.<br />

On the other hand, expression of deep-root characters is<br />

not always good under rainfed lowland conditions. Conditions<br />

of anaerobic soil that are likely to develop at some time in the<br />

growth cycle limit deep-root development (Pantuwan et al<br />

1997). Partitioning to deep roots is smaller under flooded conditions<br />

(ca. 0.3–1.2%) than under droughted conditions (ca.<br />

3–17%) in pots (Azhiri-Sigari et al 2000). Genotypic variation<br />

in deep-root development has been reported under anaerobic<br />

conditions, with their ranking generally similar between<br />

anaerobic and aerobic conditions, although in some cases interactions<br />

were recognized.<br />

Vegetative-stage drought<br />

Drought often develops during the early wet season, particularly<br />

in bimodal rainfall areas. This causes a major problem of<br />

failure in nursery establishment and transplanting. Seedling<br />

vigor is often related to quicker development of the deep-root<br />

system before drought development, which accelerates water<br />

extraction and maintains growth during intermittent drought.<br />

Genotype by initial soil moisture interactions were found for<br />

deep-root development.<br />

Genotypes may differ in their recovery growth after vegetative-stage<br />

drought. This may be related to the amount of<br />

leaf that remains after drought (Mitchell et al 1998) or ability<br />

to tiller after drought (Lilley and Fukai 1994).<br />

In our recent experiments in Cambodia, a short delay in<br />

flowering was associated with lower yield under early-season<br />

drought conditions, in contrast to the case of terminal drought,<br />

in which a short delay was advantageous. In the former case,<br />

early-flowering varieties flowered before full recovery and<br />

hence yield decreased, w<strong>here</strong>as late-flowering varieties had<br />

more time to recover before flowering took place.<br />

QTLs for drought-tolerance traits<br />

QTL links among primary, secondary, and integrated traits were<br />

examined from the reviews of previous studies. Five mapping<br />

populations have been extensively examined for QTL identification<br />

(CO39/Moroberekan, IR64/Azucena, Bala/Azucena,<br />

CT9993/IR62266, and IR58821/IR52561). Phenotyping environments<br />

were mostly under upland conditions. The emphasis<br />

was given to CT9993/IR62266, which has been phenotyped<br />

under lowland conditions (Kamoshita et al 2002, Lanceras et<br />

al 2004).<br />

The mapped traits were (1) primary traits (root traits,<br />

osmotic adjustment, cell membrane stability, carbon isotope<br />

discrimination), (2) secondary traits (e.g., leaf rolling, canopy<br />

temperature, leaf water potential), and (3) integrated traits (e.g.,<br />

grain and biological yields, percent spikelet sterility, delay in<br />

flowering). Phenology and plant types (e.g., plant height) were<br />

also mapped. QTL results are more available for root traits<br />

observed in pots and for easily scored drought-avoidance traits<br />

(e.g., leaf rolling).<br />

Thirty-four chromosome regions with multiple QTLs of<br />

different traits (QTL clusters) were identified. Twenty QTL<br />

clusters contained both primary and integrated traits (Table<br />

2). In RG939-RG214 (chromosome 4), QTLs for deep and<br />

thick root parameters, root penetration ability, and root-pulling<br />

force were identified, as well as a QTL for grain yield,<br />

with their positive effects coming from the deeper-root parent,<br />

Session 15: Challenges to expanding rice production in unfavorable environments 449


Table 2. Analysis of chromosome regions (QTL clusters) that have QTLs for any combination of two or<br />

more trait groups (primary, secondary, and integrated traits). Number of QTL clusters with the two<br />

identical trait groups is shown, together with one or two typical examples of QTL clusters for those<br />

trait group combinations.<br />

Trait group Trait Marker interval r 2 Allele for positive effect<br />

Integrated trait—primary trait (20) a<br />

Cluster 13<br />

RG939-RG214 (14.3 cM) b (chr. 4) c<br />

Integrated Grain yield (s) RG939-RG476 15.8 CT9993<br />

Deep root/tiller RG476-RG214 4.7 CT9993<br />

Root thickness RG476-RG214 29.9 CT9993<br />

Root thickness RG939-RG476 11.0 CT9993<br />

Primary Penetrated root thickness RG939-RG476 31.3 CT9993<br />

Penetrated root weight RG939-RG476 11.5 CT9993<br />

Root penetration index RG939-RG476 11.0 CT9993<br />

Root-pulling force RG214-RG620 19.9 CT9993<br />

Cluster 9<br />

RZ313-C63 (16.6 cM) b (chr. 3) a<br />

Integrated Biological yield (s) d RZ313-EM17_1 15.5 IR62266<br />

Primary Osmotic adjustment (s) EM17_1-C63 9.9 IR62266<br />

Primary trait—secondary trait–integrated trait–plant type–phenology (2) a<br />

Clusters 1, 2 e<br />

CDO345-RG345 (54.8 cM) b (chr. 1) c<br />

Root weight RG109-EM11_11 9.3 CT9993<br />

Root thickness CDO345-ME10_14 8.8 CT9993<br />

Primary Penetrated root thickness RG957-RG345 9.2 CT9993<br />

Deep root weight RM212-R2417 9.4 IR62266<br />

Deep root ratio C813-RG957 8.1 IR62266<br />

Deep root/tiller RM212-R2417 9.8 IR62266<br />

Rooting depth RM212-R2417 7.1 IR62266<br />

Leaf rolling (s) ME10_14-RG109 15.2 CT9993<br />

Leaf rolling (s) RM212-RG957 – –<br />

Leaf drying (s) ME10_14-RG109 20.8 CT9993<br />

Secondary Drought score (s) RM315-RG109 – –<br />

Drought score (s) RM212-RG957 – –<br />

Canopy temperature (s) RM315-RG109 – –<br />

Canopy temperature (s) RG109-EM11_11 17 –<br />

Relative water content (s) C813-RM212 12.1 CT9993<br />

Leaf water potential (s) C813-R2417 – –<br />

Integrated Grain yield RM212-R2417 13 –<br />

Grain yield RG957-RG345 9 –<br />

Grain yield (s) (ME2_16-RG811 f ) 7.8 IR62266<br />

Harvest index (s) RZ909-CDO345 18.6 CT9993<br />

Spikelet number RG109-EM11_11 15.2 CT9993<br />

Plant type Plant height (s) ME10_14-RG109 27.8, 46.8 CT9993<br />

Plant height (s) CDO345-RM102 36.2, 32.6, 23.1 CT9993<br />

Plant height ME10_14-EM11_11 45.8, 46.5 CT9993<br />

Plant height RZ909-RM102 46.1, 41.1 CT9993<br />

Panicle number (s) CDO345-RG109 18.6, 20.5, 20.8 IR62266<br />

Panicle number CDO345-RG109 21.7, 20.7, 8 IR62266<br />

Percent light interception C813-R2417 – –<br />

Phenology Heading/flowering day CDO345-ME10_14 17, 13 –<br />

Heading day (s) EM11_11-ME4_18 15 –<br />

a Numbers in parentheses are total number of QTL clusters for the corresponding two trait groups. b Length of marker intervals<br />

in centi-Morgans. c Chromosome numbers of the corresponding locations of QTL clusters. d The letter “s” in parentheses after<br />

trait names indicates that the corresponding traits were recorded under severe water stress environments. e Clusters 1 and 2<br />

are close, at 4.0 cM distance away. f With 24.2 cM apart from RG345 in cluster 2.<br />

450 <strong>Rice</strong> is life: scientific perspectives for the 21st century


CT9993 (Babu et al 2003). In this marker interval, QTLs for<br />

deep and thick root traits were found in CO39/Moroberekan<br />

and IR58821/IR52581.<br />

While many QTLs for integrated traits are linked with<br />

those for root traits, QTLs for osmotic adjustment and for biomass<br />

yield under mild stress in upland are located in RZ313-<br />

C63 on chromosome 3, with their positive effects from IR62266<br />

(Table 2). A QTL for osmotic adjustment is located on chromosome<br />

8 (G187-R1394A), which is homologous with the<br />

segment on chromosome 7 in wheat with the osmoregulation<br />

gene, together with other QTLs for drought-avoidance traits.<br />

In C813-R2417 in clusters 1 and 2 (chromosome 1), QTLs for<br />

relative water content, leaf water potential, leaf rolling, and<br />

drought scores were found together with a QTL for percent of<br />

radiation interception, indicating the effects of canopy size on<br />

plant water status (Table 2). QTLs for plant height with large<br />

genetic effects and the sd-1 gene are located in these clusters,<br />

together with a number of QTLs for primary, secondary, and<br />

integrated traits.<br />

In C813-RG811 (chromosome 2), QTLs for primary<br />

traits (penetrated root thickness through hardpan, deep-root<br />

traits) and secondary traits (relative water content, canopy temperature<br />

under drought, leaf drying) were found in more than<br />

one mapping population, as well as three QTLs for grain yield<br />

in three environments with different water regimes. The positive<br />

effects for the allele contribution came from CT9993 for<br />

both the primary and secondary traits, but grain yield was always<br />

higher for the shallower-rooting parent, IR62266, with<br />

the positive effect of the QTL for stress yield from IR62266,<br />

suggesting the highly integrated manner of yield determination.<br />

The putative QTLs for these primary and secondary<br />

drought-tolerance traits were incorporated to elite lines using<br />

the advanced backcross strategy, and the effects of markerassisted<br />

selection were evaluated. The putative candidate genes<br />

for drought tolerance are being clarified by saturation mapping<br />

(Nguyen et al 2004).<br />

Conclusions<br />

Drought-tolerance characters appear to differ under different<br />

types of drought. Understanding of prevailing drought types<br />

and associated characters is required for efficient use of these<br />

characters to increase drought tolerance in rainfed rice. These<br />

characters will then need to be incorporated into high-yielding<br />

genotypes with flowering time appropriate to the region of<br />

concern.<br />

Several QTL clusters were mapped that contained primary/secondary<br />

drought-tolerance traits and/or integrated traits,<br />

together with QTLs for phenology or plant type with large genetic<br />

effects. Some of them can be used for the advanced backcross<br />

strategy for developing more drought-tolerant cultivars.<br />

References<br />

Azhiri-Sigari T, Yamauchi A, Kamoshita A, Wade LJ. 2000. Genotypic<br />

variation in response of rainfed lowland rice to drought<br />

and rewatering. II. Root growth. Plant Prod. Sci. 3:180-188.<br />

Babu RC, Nguyen BD, Chamarerk V, Shanmugasundaram P,<br />

Chezhian P, Jeyaprakash P, Ganesh SK, Palchamy A,<br />

Sadasivam S, Sarkarung S, Wade LJ, Nguyen HT. 2003. Genetic<br />

analysis of drought resistance in rice by molecular markers:<br />

association between secondary traits and field performance.<br />

Crop Sci. 43:1457-1469.<br />

Fukai S, Pantuwan G, Jongdee B, Cooper M. 1999. Screening for<br />

drought resistance in rainfed lowland rice. Field Crops Res.<br />

64:61-74<br />

Jongdee B, Fukai S, Cooper M. 2002. Leaf water potential and osmotic<br />

adjustment as physiological traits to improve drought<br />

tolerance in rice. Field Crops Res. 76:153-163.<br />

Kamoshita A, Zhang J, Siopongco J, Sarkarung S, Nguyen HT, Wade<br />

LJ. 2002. Effects of phenotyping environment on identification<br />

of QTL for rice root morphology under anaerobic conditions.<br />

Crop Sci. 42:255-265.<br />

Lanceras JC, Pantuwan G, Jongdee B, Toojinda T. 2004. Quantitative<br />

trait loci associated with drought tolerance at reproductive<br />

stage in rice. Plant Physiol. 135:384-399.<br />

Lilley JM, Fukai S. 1994. Effect of timing and severity of water<br />

deficit on four diverse rice cultivars. I. Rooting pattern and<br />

soil water extraction. Field Crops Res. 37:205-213.<br />

Mitchell JH, Siamhan D, Wamala MH, Risimeri JB, Chinyamakobvu<br />

E, Henderson SA, Fukai S. 1998. The use of seedling leaf<br />

death score for evaluation of drought resistance of rice. Field<br />

Crops Res. 55(1-2):129-139.<br />

Nguyen TTT, Klueva N, Chamareck V, Aarti A, Magpantay G, Millena<br />

ACM, Pathan MS, Nguyen HT. 2004. Saturation mapping of<br />

QTL regions and identification of putative candidate genes<br />

for drought tolerance in rice. Mol. Genet. Genomics 272:35-<br />

46.<br />

Pantuwan G, Fukai S, Cooper M, O’Toole JC, Sarkarung S. 1997.<br />

Root traits to increase drought resistance in rainfed lowland<br />

rice. Proceedings of an <strong>International</strong> Workshop, Ubon<br />

Ratchathani, Thailand, 1996, Australian Centre for <strong>International</strong><br />

Agricultural <strong>Research</strong>, Canberra, ACT. p 170-179.<br />

Pantuwan G, Fukai S, Cooper M, Rajatasereekul S, O’Toole JC. 2002.<br />

Yield response of rice (Oryza sativa L.) genotypes to drought<br />

under rainfed lowland. 3. Plant factors contributing to drought<br />

resistance. Field Crops Res. 73:181-200.<br />

Notes<br />

Authors’ addresses: S. Fukai, The University of Queensland,<br />

Brisbane, Australia, e-mail: s.fukai@mailbox.uq.edu.au; A.<br />

Kamoshita, The University of Tokyo, Nishi-Tokyo, Japan, e-<br />

mail: akamoshita@fm.a.u-tokyo.ac.jp.<br />

Session 15: Challenges to expanding rice production in unfavorable environments 451


Managing iron toxicity in lowland rice: the role<br />

of tolerant genotypes and plant nutrients<br />

Kanwar L. Sahrawat<br />

Iron toxicity is a widespread nutrient disorder affecting the<br />

growing of wetland rice in the humid tropical regions of Asia,<br />

Africa, and South America. Large areas of wetlands ideally<br />

suited for rice production remain underused, especially in West<br />

and Central Africa, because of iron toxicity as a constraint.<br />

Iron toxicity has been reported to reduce rice yields by 12–<br />

100% depending on the intensity of the stress and tolerance of<br />

the rice cultivars (Sahrawat et al 1996, Sahrawat 2004). Iron<br />

toxicity of wetland rice is associated with a high concentration<br />

of ferrous iron in soil solution (Ponnamperuma et al 1955).<br />

The stress occurs in reduced soils when a toxic amount of ferrous<br />

iron is mobilized in soil solution in situ or when inflow<br />

brings in soluble iron from upper slopes (van Breemen and<br />

Moormann 1978).<br />

Iron toxicity occurs in soils (mostly Ultisols, Oxisols,<br />

and acid sulfate soils) high in active iron and potential acidity,<br />

irrespective of organic matter and texture. But texture, cation<br />

exchange capacity, and organic matter content influence the<br />

concentration of ferrous iron in soil solution, in which iron<br />

toxicity occurs (van Breemen and Moormann 1978). Plantand<br />

growing-medium-related factors such as plant age, accumulation<br />

of hydrogen sulfide, organic acids, and other reduction<br />

products also influence iron toxicity occurrence in rice<br />

(Sahrawat 2004).<br />

Iron toxicity symptoms vary with rice cultivars. They<br />

are characterized by a reddish brown, yellow, or purple-bronzing<br />

or orange discoloration of the lower leaves of the rice plants.<br />

Typically, iron toxicity symptoms are manifested as tiny brown<br />

spots starting from the upper tips and spreading toward the<br />

bases of the lower leaves. With progress in iron toxicity, the<br />

brown spots coalesce on the interveins of the leaves. With increased<br />

iron toxicity stress, the entire affected leaves look purplish<br />

brown, followed by drying of the leaves, which gives the<br />

rice plant a scorched appearance. Equally important, the roots<br />

of rice plants affected by iron toxicity become scanty, coarse,<br />

short and blunted, and dark brown in color; with the alleviation<br />

of the stress, the roots may slowly recover to the usual<br />

white color. Iron toxicity symptoms on rice leaves and changes<br />

in root color and morphology are useful for diagnosis of the<br />

stress. Toxicity symptoms commonly develop at the maximum<br />

tillering and heading growth stage, but may be observed at any<br />

growth stage of the rice crop.<br />

Since the first report of its occurrence (Ponnamperuma<br />

et al 1955), iron toxicity in rice has been reported in several<br />

countries in Asia, South America, and West and Central Africa<br />

(van Breemen and Moormann 1978, Yoshida 1981, De Datta<br />

et al 1994, Sahrawat 2004).<br />

Iron toxicity is a complex nutrient disorder and the deficiencies<br />

of other nutrients, especially phosphorus (P), potassium<br />

(K), calcium (Ca), magnesium (Mg), and zinc (Zn), are<br />

considered in the occurrence of iron toxicity in rice (Ottow et<br />

al 1983). Other nutrients may play an important role not only<br />

in reducing the effect of iron toxicity but also in the expression<br />

of iron tolerance by various rice cultivars (Sahrawat et al<br />

1996, Sahrawat 2004). Deficiencies of P, K, Ca, Mg, and manganese<br />

(Mn) decrease the iron-excluding power of rice roots<br />

and can thus affect the rice plant’s tolerance of iron toxicity<br />

(e.g., see Yoshida 1981, Sahrawat 2004). Deficiencies of Ca,<br />

Mg, and Mn are not commonly observed in lowland rice, except<br />

probably on acid sulfate soils; deficiencies of P, K, and<br />

Zn t<strong>here</strong>fore deserve special attention (Yoshida 1981).<br />

This paper critically reviews recent research on the role<br />

of tolerant genotypes and plant nutrients in reducing iron toxicity.<br />

The ultimate goal is to provide information that can be<br />

used for increasing rice production and productivity on irontoxic<br />

wetlands on a sustainable basis.<br />

Tolerant genotypes for reducing iron toxicity<br />

<strong>Rice</strong> cultivars differ in their tolerance for iron toxicity and the<br />

selection of rice cultivars with superior iron tolerance is an<br />

important component of research for reducing iron toxicity.<br />

Genetic differences in adaptation to and tolerance for irontoxic<br />

soil conditions have indeed been exploited for developing<br />

rice cultivars with tolerance for iron toxicity (Gunawardena<br />

et al 1982, DeDatta et al 1994). Breeding and screening efforts<br />

at the <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong> in the Philippines<br />

and at WARDA (West Africa <strong>Rice</strong> Development Association)<br />

in Côte d’Ivoire have identified a number of rice cultivars<br />

for growing in iron-toxic soils (De Datta et al 1994,<br />

Sahrawat 2004).<br />

Sahrawat et al (1996) evaluated 20 lowland rice cultivars<br />

for tolerance of iron toxicity at an iron-toxic site in<br />

Korhogo, Côte d’Ivoire, under irrigated conditions. The cultivars<br />

differed in tolerance of iron toxicity. Grain yields varied<br />

from 0.10 to 5.04 t ha –1 and iron toxicity scores, based on the<br />

extent of bronzing symptoms on foliage, ranged from 2 to 9 (1<br />

indicates normal growth and 9 indicates that most plants are<br />

dead or dying). Further evaluation of rice cultivars during 1992-<br />

97 showed that, among three promising iron-tolerant cultivars,<br />

CK 4 was the top yielder (mean grain yield 5.33 t ha –1 ), followed<br />

by WITA 1 (4.96 t ha –1 ) and WITA 3 (4.46 t ha –1 ), and<br />

tolerant check Suakoko 8 (3.80 t ha –1 ) (Table 1). These and<br />

other results suggest that high rice yields and iron toxicity tol-<br />

452 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. Grain yields (t ha –1 ) of WITA 1 and WITA 3 rice cultivars during<br />

1992-97 relative to the performance of iron-tolerant (Suakoko 8 and CK<br />

4) and iron-susceptible (Bouake 189) check cultivars under irrigated conditions<br />

in the wet season at an iron-toxic site in Korhogo, Côte d’Ivoire. a<br />

Year CK4 WITA1 WITA 3 Bouake 189 Suakoko 8 LSD (0.05)<br />

1992 – 4.33 5.04 2.87 4.85 1.080<br />

1993 5.87 5.53 5.17 4.08 5.07 0.630<br />

1994 6.05 6.66 4.30 4.69 3.73 1.100<br />

1996 3.76 3.24 3.21 2.81 2.57 0.760<br />

1997 5.63 5.02 4.59 4.99 2.79 1.345<br />

Mean 5.33 4.96 4.46 3.88 3.80<br />

a<br />

Each season, all cultivars received a uniform application of 100 kg N ha –1 , 50 kg P ha –1 ,<br />

and 10 kg Zn ha –1 .<br />

Source: Sahrawat et al (2000).<br />

erance are physiologically compatible (Sahrawat et al 2000,<br />

Audebert and Sahrawat 2000).<br />

Work done at WARDA in West Africa showed that some<br />

Oryza glaberrima cultivars, adapted to lowland rice-growing<br />

conditions, possess a higher tolerance for iron toxicity than<br />

their O. sativa counterparts. Sahrawat and Sika (2002) conducted<br />

experiments at an iron-toxic site (Korhogo, Côte<br />

d’Ivoire) during the 2000 wet and dry seasons to evaluate the<br />

performance of promising O. sativa (CK 4, tolerant check;<br />

Bouake 189, susceptible check) and O. glaberrima (CG 14)<br />

cultivars. While CK 4 and Bouake 189 showed typical iron<br />

toxicity symptoms in varying degrees, CG 14 plants did not<br />

show any iron toxicity symptoms at all as measured by iron<br />

toxicity scores. Although CG 14 did not give high grain yields<br />

because of its lower harvest index, lodging of the crop, especially<br />

under the application of nutrients, and shattering of seeds<br />

at maturity, it showed remarkable tolerance for iron toxicity.<br />

<strong>Research</strong> shows that CG 14 has a high tolerance for iron toxicity<br />

and remains an obvious choice as a donor for iron tolerance<br />

in breeding programs (Sahrawat and Sika 2002, Sahrawat<br />

2004).<br />

Role of other nutrients in reducing iron toxicity<br />

Table 2. Effects of field applications of nutrients on grain yield of<br />

iron-tolerant (CK 4) and susceptible (Bouake 189 and TOX 3069-<br />

66-2-1-6) rice cultivars on an iron-toxic soil at Korhogo, Côte d’Ivoire<br />

(1995-98). a Grain yield (t ha –1 )<br />

Treatment<br />

CK 4 Bouake 189 TOX 3069-66-2-1-6<br />

No fertilizer 4.3 (3) b 3.4 (5) 2.9 (7)<br />

N 4.4 (3) 4.1 (5) 3.3 (7)<br />

N + P 5.3 (2) 4.3 (4) 4.2 (5)<br />

N + K 4.8 (2) 4.4 (4) 3.8 (5)<br />

N + Zn 4.8 (2) 4.6 (4) 4.6 (5)<br />

N + P + Zn 5.0 (2) 4.4 (4) 4.2 (4)<br />

N + K + Zn 5.2 (2) 4.6 (3) 4.6 (4)<br />

N + P + K 5.4 (2) 4.5 (3) 4.5 (3)<br />

N + P + K + Zn 5.7 (2) 4.7 (3) 4.7 (3)<br />

LSD (0.05) 1.01 1.02 1.15<br />

a<br />

The data are an average of four years (1995-98). All cultivars received a uniform<br />

application of N (100 kg ha –1 ), P (50 kg ha –1 ), K (80 kg ha –1 ), and Zn (10 kg ha –1 ).<br />

b<br />

Iron toxicity scores are given in parentheses on a scale of 1 to 9, w<strong>here</strong> 1 = normal<br />

growth and 9 = most plants are dead or drying.<br />

Source: Sahrawat et al (2001).<br />

A high concentration of iron in soil solution can cause nutrient<br />

imbalance through antagonistic effects on the uptake of nutrients,<br />

including K and Zn. The deficiency or lack of availability<br />

of other nutrients can also affect the rice plant’s ability to<br />

decrease uptake of iron in the tops through physiological functions<br />

carried out by roots such as iron oxidation, iron exclusion,<br />

and iron retention (Yoshida 1981, Audebet and Sahrawat<br />

2000, Sahrawat 2004). Thus, it is not entirely surprising that<br />

the application of other nutrients reduces iron toxicity and<br />

improves yield of rice on iron-toxic soils. Several reports show<br />

that applications of nutrients such as P, K, and Zn reduce iron<br />

toxicity, improve growth, and increase rice yield (Sahrawat et<br />

al 2001, Nayak et al 2004, Sahrawat 2004). Sahrawat et al<br />

(2001) showed that applications of N, P, K, and Zn in various<br />

combinations reduced iron toxicity and increased yields of irontolerant<br />

and -susceptible rice cultivars. The increase in grain<br />

yields of iron-susceptible cultivars was more than that of irontolerant<br />

cultivars (Table 2).<br />

Conclusions<br />

Iron toxicity can be reduced by using iron-tolerant cultivars<br />

and by applying other nutrients whose availability is negatively<br />

affected by a high concentration of iron in soil solution. The<br />

intensified use of iron-toxic wetlands in the future is inevitable<br />

for meeting the food needs of the ever-growing population<br />

in tropical regions, w<strong>here</strong> iron-toxic soils are an important<br />

natural resource for food production. An integrated use of<br />

tolerant genotypes and improved soil and nutrient management<br />

is more practical for sustainable increases in rice productivity.<br />

Session 15: Challenges to expanding rice production in unfavorable environments 453


References<br />

Audebert A, Sahrawat KL. 2000. Mechanisms for iron toxicity tolerance<br />

in lowland rice. J. Plant Nutr. 23:1877-1885.<br />

De Datta SK, Neue HU, Senadhira D, Quijano C. 1994. Success in<br />

rice improvement for poor soils. In: Proceedings of the Workshop<br />

on Adaptation of Plants to Soil Stresses, 1-4 August 1993,<br />

University of Nebraska, Lincoln, Nebraska. INTSORMIL<br />

Publication No. 94-2. Lincoln, Nebraska (USA): University<br />

of Nebraska. p 248-268.<br />

Gunawardena I, Virmani SS, Sumo FJ. 1982. Breeding rice for tolerance<br />

to iron toxicity. Oryza 19:5-12.<br />

Nayak SC, Sahu SK, Mishra GC, Sandha B. 2004. Comparison of<br />

different amendments for alleviating iron toxicity in rice. Int.<br />

<strong>Rice</strong> Res. Notes 29:51-53.<br />

Ottow JCG, Benckiser G, Watanabe I, Santiago S. 1983. Multiple<br />

nutritional soil stress as the prerequisite for iron toxicity of<br />

wetland rice (Oryza sativa L.). Trop. Agric. (Trinidad) 60:102-<br />

106.<br />

Ponnamperuma FN, Bradfield R, Peech M. 1955. Physiological disease<br />

of rice attributable to iron toxicity. Nature 175:265.<br />

Sahrawat KL. 2004. Iron toxicity in wetland rice and the role of<br />

other nutrients. J. Plant Nutr. 27:1471-1504.<br />

Sahrawat KL, Diatta S, Singh BN. 2000. Reducing iron toxicity in<br />

lowland rice through an integrated use of tolerant genotypes<br />

and plant nutrient management. Oryza 37:44-47.<br />

Sahrawat KL, Mulbah CK, Diatta S, DeLaune, RD, Patrick WH Jr,<br />

Singh BN, Jones MP. 1996. The role of tolerant genotypes<br />

and plant nutrients in the management of iron toxicity in lowland<br />

rice. J. Agric. Sci. Cambridge 126:143-146.<br />

Sahrawat KL, Sika M. 2002. Comparative tolerance of Oryza sativa<br />

and O. glaberrima rice cultivars for iron toxicity in West Africa.<br />

Int. <strong>Rice</strong> Res. Notes 27:30-31.<br />

van Breemen N, Moormann FR. 1978. Iron-toxic soils. In: Soils and<br />

rice. Manila (Philippines): <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>.<br />

p 781-800.<br />

Yoshida S. 1981. Fundamentals of rice crop science. Manila (Philippines):<br />

<strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>. 269 p.<br />

Notes<br />

Author’s address: <strong>International</strong> Crops <strong>Research</strong> <strong>Institute</strong> for the Semi-<br />

Arid Tropics, Patancheru 502324, Andhra Pradesh, India, e-<br />

mail: k.sahrawat@cgiar.org.<br />

Soil acidity and related problems in upland rice in the tropics<br />

Kensuke Okada and Matthias Wissuwa<br />

Upland rice is grown on a total of 19.1 million ha in Asia (60%),<br />

Latin America (30%), and Africa (10%). The humid to<br />

subhumid climatic conditions prevailing in upland rice areas<br />

have typically led to various degrees of soil acidity because of<br />

deep weathering and leaching of cations. In fact, the major<br />

soils for upland rice are Ultisols and Alfisols in Asia and West<br />

Africa, and Oxisols and Ultisols in Latin America. Oxisols and<br />

Ultisols are especially typical acid soils.<br />

Soil constraints are less critical for irrigated rice because<br />

flooded conditions increase the availability of nutrients and<br />

stabilize soil pH closer to neutral, even in acid soils. On upland<br />

soils, however, soil acidity can cause yield losses of up to<br />

50% (Sarkarung 1986). It is t<strong>here</strong>fore necessary to manage<br />

soil acidity and related soil constraints to increase the productivity<br />

of upland rice.<br />

Growth-limiting factors for upland rice in acid soils<br />

The problems of acid soils are complex and are often regarded<br />

as an “acid-soil syndrome.” The major growth-limiting factor<br />

for upland rice differs depending on the degree of soil acidity.<br />

Roughly speaking, w<strong>here</strong> soil pH (in water) is lower than<br />

4.3, the Al concentration in the soil solution can be higher than<br />

100 µM. This is potentially toxic, with negative effects on the<br />

elongation of rice roots under solution culture conditions. In<br />

upland rice fields, such soil conditions are not the norm but<br />

can be induced by inappropriate management practices. For<br />

example, in Oxisols in the subhumid savannas of Colombia,<br />

this degree of acidity occurred only in the surface soil layer in<br />

the middle stage of rice development. This enhanced acidity<br />

was created by the sequential split application of urea, which<br />

reduced soil pH because of nitrification and by potassium fertilizers<br />

that exchange Al at the exchange site of clay minerals<br />

and increase Al concentration in soil solution in the moderately<br />

intensive upland rice cultivation system (Okada and<br />

Fischer 2001).<br />

<strong>Rice</strong> plants are moderately tolerant of acid soils in general,<br />

but showed wide genotypic variation in tolerance of this<br />

severe soil acidity. Semidwarf indicas were susceptible but<br />

tropical/temperate japonicas were usually tolerant. The causal<br />

factor inducing genotypic differences was investigated under<br />

these conditions and it was found to be low Ca availability<br />

rather than high Al (Okada and Fischer 2001). The relative<br />

growth of susceptible varieties was more correlated to exchangeable<br />

Ca than to exchangeable Al and Al saturation (Fig.<br />

1). The tolerant genotype had a higher Ca absorbing capacity<br />

of the roots, probably owing to higher preferential adsorption<br />

of Ca over Al at the surface of the root cell wall (Okada et al<br />

2003).<br />

When soil pH is higher than 4.3, the concentration of Al<br />

in soil solution is not toxic to the elongation of rice roots. This<br />

is the case for the commonly found acidic soils in West Africa<br />

(Ultisols and some Alfisols), w<strong>here</strong> the major chemical soil<br />

constraint is low P content/availability rather than soil acidity<br />

itself.<br />

454 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Relative yield (%)<br />

110<br />

A B C D<br />

r = –0.51 (ns) r = 0.51 (ns) r = 0.58* r = 0.43 (ns)<br />

100<br />

90<br />

80<br />

70<br />

4.4 4.6 4.8 1.5 2.0 2.5 3.0 0.2 0.3 0.4 75 80 85<br />

pH Exch-Al (cmol kg –1 ) Exch-Ca (cmol kg –1 ) Al sat. (%)<br />

Fig. 1. The response of susceptible varieties of upland rice ( Oryzica 1; Oryzica Llanos 5) to soil pH<br />

(A), exchangeable Al (B), exchangeable Ca (C), and Al saturation (D) in the topsoil of savanna (0 to 20<br />

cm). Results of 1993 to 1996 at two sites in savannas of Colombia.<br />

Genetic improvement of upland rice<br />

for tolerance of soil acidity<br />

Strongly acid soils are most predominant in South America.<br />

Besides the Amazonian rainforest, subhumid tropical savannas<br />

cover 240 million ha (Cerrados in Brazil and Llanos in<br />

Colombia and Venezuela). Dominant soils are the highly weat<strong>here</strong>d<br />

Oxisols and Ultisols. A typical example of the chemical<br />

characteristics are pH 4.8 (1:1 water), organic matter content<br />

4.2%, available P (Bray-2) 2.5 ppm, and exchangeable cations<br />

at Ca 0.18, Mg 0.13, K 0.09, and Al 2.1 cmol kg –1 soil.<br />

The aluminum saturation of the soil is 84%. Thus, these soils<br />

are characterized by low pH and low effective CEC (sum of<br />

exchangeable cations), with most of the CEC occupied by exchangeable<br />

Al.<br />

To develop rice varieties with high yield potential and<br />

acid-soil tolerance for the purpose of introducing upland rice<br />

in the rice-pasture cropping system of the savanna region was<br />

one objective at CIAT/Colombia. More than 1,360 cultivars<br />

of diverse genetic background were evaluated for acid-soil tolerance<br />

in the typical Oxisols (with 84–86%Al saturation) of<br />

the Colombian savannas (Sarkarung 1986). The acid-tolerant<br />

accessions were crossed with blast-resistant lines, further evaluated,<br />

and finally a commercial cultivar, Oryzica Sabana 6, was<br />

released in Colombia in 1991. This variety frequently achieved<br />

outstanding yield (3,500–4,000 kg ha –1 ) under upland acid<br />

savanna conditions, and has desired characteristics such as long<br />

grain and high amylose content. In 1996, a succeeding variety,<br />

Oryzica Sabana 10, was developed.<br />

Marker-assisted breeding for low-P tolerant varieties<br />

As mentioned above, phosphorus (P) deficiency is a major<br />

abiotic stress that limits rice productivity, particularly under<br />

upland conditions in acid soils such as Ultisols and Alfisols<br />

(Kirk et al 1998). In addition to areas of low absolute soil-P<br />

content, P deficiency can also arise in soils w<strong>here</strong> P is strongly<br />

bound to soil particles. Dobermann et al (1998) estimated that<br />

more than 90% of added fertilizer P may be rapidly transformed<br />

to P forms that are not easily available to plants. The development<br />

of rice cultivars capable of using a higher portion of the<br />

fixed P already present in soils may be an attractive and costeffective<br />

approach to increasing rice yields w<strong>here</strong> P deficiency<br />

is the major constraint.<br />

One promising step toward developing more P-efficient<br />

cultivars was the identification of the Pup1 locus in a QTL<br />

mapping population that was derived from rice cultivars<br />

Nipponbare (low P uptake) and Kasalath (high P uptake) and<br />

that had been evaluated on a highly P-fixing volcanic ash soil<br />

(Wissuwa et al 2002). This locus was transferred from the donor<br />

variety Kasalath into a Nipponbare genetic background.<br />

The resulting near-isogenic line, NIL-Pup1, was genetically<br />

92% identical to Nipponbare, but, when grown on the highly<br />

P-fixing soil, NIL-Pup1 had a threefold higher biomass than<br />

Nipponbare (Fig. 2). This improvement in growth was due to<br />

the ability of the NIL to acquire more P from the soil. Higher<br />

root growth rates and more efficient P uptake per unit root size<br />

(uptake efficiency) were the main differences between NIL-<br />

Pup1 and Nipponbare (Fig. 2). These effects were detected<br />

only under P deficiency but not when additional P (50 kg ha –1 )<br />

was supplied to the deficient soil. This suggested that Pup1<br />

did not affect root growth potential per se but that it helped<br />

maintain root growth when P was limiting. Model simulations<br />

have shown that an increase in P uptake efficiency in the range<br />

observed for NIL-Pup1 would be sufficient to explain subsequent<br />

increases in P uptake and plant growth, including root<br />

growth (Wissuwa 2003). Higher P-uptake efficiency is t<strong>here</strong>fore<br />

the most likely mechanism affected by the Pup1 locus.<br />

Currently, efforts at <strong>IRRI</strong> are directed toward identifying<br />

the gene(s) at the Pup1 locus.<br />

Further fine-mapping of Pup1 has advanced considerably<br />

and Pup1 has now been mapped to a 240-kb interval containing<br />

31 putative genes (Wissuwa, unpublished data). Most<br />

of these are hypothetical genes without similarity to known<br />

genes and those few that were functionally annotated were not<br />

associated with P metabolism, root growth, or P-uptake mechanisms<br />

(based on the Nipponbare sequence data). This suggests<br />

that the Pup1 locus either represents a novel gene or that the<br />

gene is simply absent or highly distorted in Nipponbare. It<br />

could also indicate, however, that the Pup1 locus performs a<br />

Session 15: Challenges to expanding rice production in unfavorable environments 455


Nipponbare NIL-Pup1 t-test<br />

–P<br />

P uptake (mg) (–P) 1.89 4.38 **<br />

P uptake (mg) (+P) 12.44 13.68 ns<br />

Root weight (g) (–P) 0.85 1.46 **<br />

Root weight (g) (+P) 3.25 3.51 ns<br />

P-uptake efficiency a (–P) 2.20 3.02 **<br />

+ Pup1 – Pup1<br />

P-uptake efficiency a (+P) 3.82 3.89 ns<br />

Fig. 2. (Left) Effect of the Pup1 locus on plant growth on a highly P-deficient, highly P-fixing soil<br />

(Andosol). NIL-Pup1 (+Pup1) has about three times as much P uptake, root dry weight, and total<br />

biomass as Nipponbare (–Pup1). (Right) Effect of the Pup1 locus on P uptake, root weight, and<br />

P-uptake efficiency. P-uptake efficiency is estimated as mg P taken up per g of root weight.<br />

regulatory function, only indirectly affecting the uptake mechanism.<br />

References<br />

Dobermann A, Cassman KG, Mamaril CP, Sheehy JE. 1998. Management<br />

of phosphorus, potassium, and sulfur in intensive,<br />

irrigated lowland rice. Field Crops Res. 56:113-138.<br />

Kirk GJD, George T, Courtois B, Senadhira D. 1998. Opportunities<br />

to improve phosphorus efficiency and soil fertility in rainfed<br />

lowland and upland rice ecosystems. Field Crops Res. 56:73-<br />

92.<br />

Okada K, Fischer AJ. 2001. Adaptation mechanisms of upland rice<br />

genotypes to highly weat<strong>here</strong>d acid soils of South American<br />

savannas. In: Ae N et al, editors. Plant nutrient acquisition:<br />

new perspectives. Tokyo (Japan): Springer-Verlag Tokyo.<br />

p 185-200.<br />

Okada K, Fischer AJ, Perez-Salasar FA, Cañon-Romero Y. 2003.<br />

Difference in the retention of Ca and Al as possible mechanisms<br />

of Al resistance in upland rice. Soil Sci. Plant Nutr.<br />

49:889-895.<br />

Sarkarung S. 1986. Screening upland rice for aluminum tolerance<br />

and blast resistance. In: Progress in upland rice research. Proceedings<br />

of the Second <strong>International</strong> Upland <strong>Rice</strong> Conference,<br />

4-8 March 1985. Manila (Philippines): <strong>International</strong> <strong>Rice</strong><br />

<strong>Research</strong> <strong>Institute</strong>. p 271-281.<br />

Wissuwa M. 2003. How do plants achieve tolerance to phosphorus<br />

deficiency: small causes with big effects. Plant Physiol.<br />

133:1947-1958.<br />

Wissuwa M, Wegner J, Ae N, Yano M. 2002. Substitution mapping<br />

of Pup1: a major QTL increasing phosphorus uptake of rice<br />

from a phosphorus-deficient soil. Theor. Appl. Genet. 105:890-<br />

897.<br />

Notes<br />

The physiological foundation of crop breeding<br />

for stress environments<br />

A. Blum<br />

Authors’ addresses: K. Okada, National Agricultural <strong>Research</strong> Center,<br />

3-1-1 Kannondai, Tsukuba, Ibaraki 305-8666, Japan; M.<br />

Wissuwa, <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>, Los Baños,<br />

Philippines.<br />

Plant sciences that address the different physiological, genetic,<br />

and environmental aspects of crop yield are becoming more<br />

divergent as time progresses. This is a result of the explosion<br />

of knowledge in each discipline on the one hand and the human<br />

limitation in coping with such an amount of knowledge.<br />

As expertise becomes more specific, the chances for interaction<br />

between scientific disciplines are diminishing. This is accentuated<br />

by funding agencies that do not consistently encour-<br />

age integrated research in plant sciences. Henceforth, while<br />

the problem of crop production under environmental stress is<br />

a problem of the whole organism and the whole cropping systems<br />

in relation to their environment, science is becoming less<br />

capable of dealing with this whole while it becomes proficient<br />

in dealing with increasingly smaller components of the whole.<br />

This is reflected in the young upcoming scientists just out of<br />

universities who enter the field of abiotic stress resistance with<br />

456 <strong>Rice</strong> is life: scientific perspectives for the 21st century


the ambition of making a contribution. As they were not always<br />

trained to understand the whole, they try to define and<br />

address abiotic stress resistance through the constrained view<br />

that they have on this trait as seen from the peephole of their<br />

own narrow discipline. This definition is naturally constrained<br />

and very often misleading.<br />

The definition of stress resistance is not just a question<br />

of scientific formality. It is a major key to understanding what<br />

stress resistance entails and how plant physiology can make a<br />

contribution to the genetic improvement of crop-plant stress<br />

resistance by way of conventional breeding, molecular biology,<br />

and genomics. This paper will attempt to explain this issue.<br />

T<strong>here</strong> is no unified abiotic stress resistance at the level<br />

of the gene or the whole plant. It is very hard to accept the<br />

often suggested conclusions of functional genomics studies in<br />

that a certain gene ascribes plant resistance to cold, heat,<br />

drought, salinity, and probably also to a certain disease. However,<br />

a unified definition of abiotic stress resistance was put<br />

forward more than 30 years ago by Levitt (1972) and discussed<br />

by Blum (1988) in relation to plant breeding. This definition<br />

provides the basis for applying stress physiology to crop improvement.<br />

T<strong>here</strong> is no unified protocol for assessing stress<br />

resistance. However, a unified concept and definition of stress<br />

resistance can help us move forward in understanding a specific<br />

stress resistance, its correct measurement, and its manipulation<br />

in breeding.<br />

Abiotic stress resistance is controlled by stress avoidance<br />

and/or stress tolerance. Stress avoidance enables the plant<br />

to avoid exposure of the plant system(s) to the stressor by excluding<br />

the stressor or the strain it produces from the system(s).<br />

Stress tolerance is the capability to sustain plant function in<br />

the presence of the stressor or the strain in the plant.<br />

Stress avoidance<br />

Avoidance mechanisms are diverse and depend on the type of<br />

stress. Avoidance can take place in the whole plant, the organ,<br />

or the cellular levels.<br />

Some examples are warranted. For drought, despite the<br />

receding supply of water, a plant can maintain hydration by<br />

either efficient moisture capture from soil or by reduced water<br />

use at a minimal cost to assimilation. The plant can maintain<br />

cellular hydration through osmotic adjustment, despite a reduction<br />

in whole-plant water potential. For salinity stress, plants<br />

such as halophytes can avoid salinization by excluding sodium<br />

at the root. Plants can also activate specific vacuolar Na+/H+<br />

antiports, which enable vacuolar accumulation and<br />

compartmentation of toxic sodium, avoiding its presence in<br />

the cell main sites of life processes.<br />

Similarly, t<strong>here</strong> are mechanisms of avoidance for various<br />

mineral toxicity stresses, mineral deficiency stress, and<br />

even heat stress. Even for freezing stress, the supercooling of<br />

internal tissue water enables avoiding of cell dehydration, which<br />

is caused by extracellular ice formation. For heat stress, various<br />

whole-plant features such as transpiration and reflective<br />

leaf surfaces allow decreasing the heat load on the plant and<br />

thus avoiding excessive heating.<br />

Stress tolerance<br />

As a general rule, plants can tolerate the presence of the stressor<br />

and its strain mainly by reverting to a quiescent state, such<br />

as dormancy. The most notable agronomic case is freezing tolerance<br />

as seen in winter cereals and hardy trees. Plants generally<br />

do not grow at freezing temperatures but they can survive<br />

this temperature in a dormant state and recover when temperature<br />

returns to normal. Similarly, dehydration tolerance can<br />

take place in dormant embryos in the dry seed or in a resurrection<br />

plant that can survive desiccation. Both will return to<br />

growth when re-hydrated.<br />

The following not quite hypothetical example will serve<br />

to accentuate the importance of the physiological dissection<br />

of abiotic stress resistance phenomena in terms of their definitions.<br />

A certain research found that two cultivars differed in<br />

their photosystem activity under drought stress. Both cultivars<br />

had an activity of 3 empirical units under nonstress conditions.<br />

Under drought stress, cultivar A had an activity of 1 unit while<br />

cultivar B had an activity of 2 units. Hence, cultivar B was<br />

taken as stress tolerant in terms of photosystem activity and<br />

researchers stated that they will now embark on research to<br />

investigate what biochemical or structural factors allow the<br />

resistant B to sustain photosystem activity under drought and<br />

perhaps this could open a new avenue into breeding droughttolerant<br />

crops. However, if the investigators would have tested<br />

their plants for water status (e.g., relative water content, RWC),<br />

they would have found that cultivar A had 60% RWC while B<br />

had 85% RWC under stress. This would have indicated that<br />

photosystem activity was higher in B because B was dehydration-avoidant.<br />

Its advantage over A in photosystem activity had<br />

nothing to do with photosystem biochemistry under stress.<br />

Cultivar B simply was not exposed to dehydration as was cultivar<br />

A.<br />

Without citing the hundreds of papers dealing with the<br />

agronomic and physiological aspects of drought stress resistance<br />

(e.g., www.plantstress.com), it can be concluded that the<br />

most common and effective factor of drought resistance in crop<br />

plants as well as native vegetation (e.g., Chaves et al 2002) is<br />

dehydration avoidance rather than dehydration tolerance. Dehydration<br />

tolerance as conditioned by a dormant state is by<br />

and large less prevalent in the agronomic domain w<strong>here</strong> growth<br />

and production under stress are prime requirements. Indeed,<br />

t<strong>here</strong> are limited cases w<strong>here</strong> drought tolerance is required,<br />

such as cereal seedling survival under post-germination drought<br />

in the Mediterranean region. It is important, however, to understand<br />

the difference between survival as a component of<br />

tolerance and sustained productivity as enabled by avoidance.<br />

On the other hand, freezing and heat resistance are exceptions<br />

in that tolerance constitutes a major mechanism.<br />

This brings the discussion to another example, involving<br />

ABA. Molecular biology research recognized that one path-<br />

Session 15: Challenges to expanding rice production in unfavorable environments 457


way of stress signal transduction involves ABA production and<br />

ABA-responsive genes. The immediate conclusion turned into<br />

an axiom was that ABA was a “stress hormone” responsible<br />

for plant resistance to stress. This axiomatic conclusion ignores<br />

past plant physiology research indicating that ABA causes<br />

reproductive failure and growth retardation, which oppose productivity.<br />

On the other hand, ABA induces dormancy. Hence,<br />

one can generalize that ABA may be a positive factor in stress<br />

tolerance and survival and a negative factor in stress avoidance<br />

and productivity under stress. It would t<strong>here</strong>fore be unlikely<br />

for crop breeders seeking to sustain yield under stress to<br />

consider ABA as a stress resistance factor in crop plants. Moreover,<br />

recent research even indicated (e.g., Landi et al 2001)<br />

that maize lines selected for low leaf ABA content were more<br />

drought-resistant in terms of yield than high-ABA lines.<br />

Finally, t<strong>here</strong> is serious concern among leading stress<br />

physiologists about the quality of testing for stress resistance<br />

in the domain of molecular biology. Too many studies that attempt<br />

to prove the effect of a certain gene or a mutation on the<br />

stress tolerance of experimental transgenic plants are unacceptable<br />

and unreasonable in terms of stress physiology. Testing<br />

may be faulty, measurements physiologically unacceptable,<br />

and the conclusions drawn can be erroneous. By not adhering<br />

to strict and legitimate stress physiology, such tests defeat their<br />

own purpose of identifying suitable genes for use in stress<br />

breeding. What is needed, rather, is a legitimate physiological<br />

dissection of gene function under stress in terms acceptable to<br />

physiologists and breeders.<br />

Conclusions<br />

This paper underlines the importance of being able to integrate<br />

the relevant knowledge produced over time in various<br />

plant science and agronomic disciplines toward breeding for<br />

stress resistance. It highlights the requirement for dissecting<br />

apparent abiotic resistance phenomena and resistance gene<br />

actions in the correct physiological terms of the immediate<br />

products and whole-plant responses. As plant and environmental<br />

sciences are becoming more fragmented and divergent, it<br />

will become very difficult to sustain applied research in plant<br />

stress resistance without the appropriate integration of plant<br />

sciences in education. Plant stress perspectives in molecular<br />

biology, physiology, genetics, breeding, agronomy, and environmental<br />

sciences should be merged into a new educational<br />

discipline of plant abiotic stress in institutes of higher education.<br />

References<br />

Blum A. 1988. Plant breeding for stress environments. Boca Raton,<br />

Fla. (USA): CRC Press. 208 p.<br />

Chaves MM, Pereira JS, Maroco J, Rodrigues ML, Ricardo CPP,<br />

Oserio ML, Carvalho I, Faria T, Pinheiro C. 2002. How do<br />

plants cope with water stress in the field Photosynthesis and<br />

growth. Ann. Bot. 89:907-916.<br />

Landi P, Sanguineti MC, Conti S, Tuberosa R. 2001. Direct and correlated<br />

responses to divergent selection for leaf abscisic acid<br />

concentration in two maize populations. Crop Sci. 41:335-<br />

344.<br />

Levitt J. 1972. Responses of plants to environmental stresses. New<br />

York, NY (USA): Academic Press. 695 p.<br />

Notes<br />

Author’s address: www.plantstress.com, PO Box 16246, Tel Aviv,<br />

Israel, e-mail:ablum@plantstress.com.<br />

Expression of a serine protease<br />

during microsporogenesis in rice<br />

Kentaro Kawaguchi, Naoshi Dohmae, Shuichi Matsuba, Hideyuki Funatsuki, Yutaka Sato, and Masao Ishimoto<br />

Pollen formation is one of the most important processes in<br />

plant reproduction and is widely known to be very sensitive to<br />

various forms of environmental stress, including low temperature.<br />

The most sensitive stage of pollen was shown to be the<br />

young microspore stage that was demonstrated using pot-grown<br />

rice under phytotron conditions (Satake and Nishiyama 1970).<br />

Male sterility induced by chilling temperature (12 to 18 °C) at<br />

the booting stage causes a serious loss of grain yield in rice<br />

and this chilling injury has been one of the most serious problems<br />

for agriculture in the temperate region (Yoshida 1981).<br />

To solve this problem, it is important to understand the physiological<br />

nature of anther development under normal and chill-<br />

ing temperature. Although the microscopic size of the rice anther<br />

has been a factor limiting progress in its biochemical and<br />

physiological analyses, recent advances in analyses of the rice<br />

genome have allowed us to use new approaches to solve the<br />

problem, such as small material size. For example, changes in<br />

the expression of transcripts in rice anthers caused by low temperature<br />

could be monitored using cDNA microarray analysis<br />

satisfactorily (Yamaguchi et al 2004). Our research objective<br />

is to discover the genes that have a key role in chilling injury<br />

by proteome analysis. In this study, we screened proteins separated<br />

from normal and chilled anthers, and the selected glycoprotein,<br />

which was specifically down-regulated by chilling, for<br />

458 <strong>Rice</strong> is life: scientific perspectives for the 21st century


their identification. We will discuss the possible function of<br />

the proteins in pollen development and susceptibility to low<br />

temperature.<br />

Proteome analysis for development of rice anthers<br />

Screening anther proteins<br />

Proteins, which would have important roles in microsporogenesis,<br />

were expected to accumulate in a stage-specific manner<br />

in developing anthers. First, we examined anther proteins<br />

from rice plants grown under normal conditions (25 °C day/<br />

19 °C night). Anther proteins prepared from the two distinct<br />

stages (microspore and heading) were separated by SDS-PAGE<br />

and visualized with Ponceau S dye or a glycoprotein detection<br />

kit. However, neither staining method showed remarkable<br />

changes in patterns of the protein bands between the two stages.<br />

On the other hand, the combination of SDS-PAGE and concanavalin<br />

A (Con A) lectin blotting analysis showed that several<br />

glycoproteins accumulated stage specifically. The 85-,<br />

82-, and 55-kDa bands gradually increased, and 64- and 63-<br />

kDa bands appeared transiently at specific stages. The stagespecific<br />

accumulation suggested that these glycoproteins function<br />

in the temporal events that occurred during anther development.<br />

Next, the effects of low temperature on the accumulation<br />

of glycoproteins were examined. <strong>Rice</strong> plants were kept at<br />

12 °C for 4 days at the booting stage for low-temperature treatment.<br />

Chilling stress modified the accumulation of a particular<br />

glycoprotein, and the 85-kDa glycoprotein was down-regulated<br />

in chilled anthers. In contrast, the other glycoproteins<br />

showed little change by the chilling treatment. So, we selected<br />

the 85-kDa glycoprotein for further analysis as a candidate<br />

that could be involved in the mechanisms of chilling injury in<br />

rice.<br />

Primary structure of the glycoprotein<br />

Two-dimensional gel electrophoresis (2DE) showed that the<br />

85-kDa glycoprotein was apparently separated as multiple spots<br />

at pI 5–6. We obtained the internal peptides and analyzed the<br />

amino acid residues by a protein sequencer and MALDI-TOF<br />

MS. Comparison of the sequence information with SWISS-<br />

PROT and EMBL using the BLAST program showed higher<br />

homology with the subtilisin-like serine proteases expressed<br />

in developing anthers in rice (Yoshida and Kuboyama 2001),<br />

lily (Kobayashi et al 1994), and tomato (Riggs et al 2001).<br />

Western analysis using the antisera raised against the lily protease<br />

showed a cross reaction to the glycoprotein from rice<br />

anthers that confirmed the result of the structural analysis.<br />

The primary structure reveals that the glycoprotein possesses<br />

all the characteristics of the subtilisin-like serine protease<br />

family. The amino acids that are forming the catalytic<br />

triad—aspartate (D), histidine (H), and serine (S)—and the<br />

substrate binding site, asparagine (N), at the active site are<br />

conserved. The N-terminal region is hydrophobic, suggesting<br />

that it acts as a signal peptide, and is transported via a secretory<br />

pathway.<br />

Possible function of serine protease<br />

in the development of rice anther<br />

Subtilisin-like serine proteases are a family of endoproteases<br />

present in diverse tissues in microorganisms, plants, and animals,<br />

and they are believed to be present in the extracellular<br />

spaces, on the plasma membrane, and on the Golgi apparatus.<br />

The essential functions in proteolysis for cell development were<br />

reported. The yeast (Saccharomyces cerevisiae) kex2 gene<br />

encoding a membrane-bound subtilisin-like serine protease was<br />

required for processing of precursors of α-factor and killer<br />

toxin (Mizuno et al 1988), and so on. In contrast, limited information<br />

on biological functions is available in plants, such<br />

as kex2p-like protease activity in tobacco suspension culture<br />

cells (Jiang and Rogers 1999).<br />

Developmentally regulated fluctuation of the protease<br />

during microsporogenesis suggests that it has important roles<br />

in the development of pollen in rice anthers. Subtilisin-like<br />

serine proteases have been studied in detail in unicellular organisms,<br />

such as Bacillus spp. and yeast, etc. This case is especially<br />

interesting because the unicellular organisms seem to<br />

be analogous to microspores. It has been thought that the protease<br />

is transported via a secretory pathway to the extracellular<br />

spaces w<strong>here</strong> the protease converts exogenous organic<br />

sources (proteins or peptides) to amino acids for obtaining<br />

nutrients. <strong>Rice</strong> microspores may be supplied with amino acids<br />

by action of the protease during their development. It is also<br />

possible that the protease is involved in the processing of precursors<br />

of important enzymes to enhance pollen development.<br />

However, these hypotheses are not yet demonstrated experimentally.<br />

The disappearance of glycoproteins under chilling<br />

stress might be one cause of the pollen abortion. If the protease<br />

has an important role in pollen development as discussed<br />

above, its down-regulation under chilling might cause irreversible<br />

injury to the microspore. To improve the chilling-susceptible<br />

nature of rice anthers, it is t<strong>here</strong>fore necessary to understand<br />

the physiological role of serine protease during anther<br />

development.<br />

Future prospects<br />

In this paper, we described a subtilisin-like serine protease that<br />

accumulates specifically in developing rice anthers. Although<br />

structural analysis showed that a glycoprotein was identified<br />

as a subtilisin-like serine protease, the proteolytic activity has<br />

not yet been practically examined. To clarify the relationships<br />

between this glycoprotein and male sterility under low temperature<br />

in rice, it is important to know whether the glycoprotein<br />

actually functions in microsporogenesis. What is the natural<br />

substrate of the protease in anthers W<strong>here</strong> does the protease<br />

function The answers to these questions will result in<br />

important keys to understanding the physiological mechanisms<br />

of chilling injury in rice anthers.<br />

Session 15: Challenges to expanding rice production in unfavorable environments 459


References<br />

Jiang L, Rogers JC. 1999. Functional analysis of a golgi-localized<br />

kex2p-like protease in tobacco suspension culture cells. Plant<br />

J. 18:23-32.<br />

Kobayashi T, Kobayashi E, Sato S, Hotta Y, Miyajima N, Tanaka A,<br />

Tabata S. 1994. Characterization of cDNAs induced in meiotic<br />

prophase in lily microspores. DNA Res. 1:15-26.<br />

Mizuno K, Nakamura T, Ohshima T, Tanaka S, Matsuo H. 1988.<br />

Yeast kex2 gene encodes an endopeptidase homologous to<br />

subtilisin-like serine proteases. Biochem. Biophys. Res.<br />

Comm. 156:254-256.<br />

Riggs CD, Zeman K, De Guzman R, Rzepczyk A, Taylor AA. 2001.<br />

Antisense inhibition of a tomato meiotic proteinase suggests<br />

functional redundancy of proteinases during microsporogenesis.<br />

Genome 44:644-650.<br />

Satake T, Nishiyama I. 1970. Male sterility caused by cooling treatment<br />

at the young microspore stage in rice plants. V. Estimation<br />

of pollen developmental stage and the most sensitive stage<br />

to coolness. Proc. Crop Sci. Soc. Jpn. 39:468-473.<br />

Yamaguchi T, Nakayama K, Hayashi T, Yazaki J, Kishimoto N,<br />

Kikuchi S, Koike S. 2004. cDNA microarray analysis of rice<br />

anther genes under chilling stress at the microsporogenesis<br />

stage revealed two genes with DNA transposon castaway in<br />

the 5′-flanking region. Biosci. Biotechnol. Biochem. 68:1315-<br />

1323.<br />

Yoshida S. 1981. Fundamentals of rice crop science. Los Baños (Philippines):<br />

<strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>. 269 p.<br />

Yoshida KT, Kuboyama Y. 2001. A subtilisin-like serine protease<br />

specifically expressed in reproductive organs in rice. Sex. Plant<br />

Reprod. 13:139-199.<br />

Notes<br />

Authors’ addresses: Kentaro Kawaguchi, Shuichi Matsuba, Hideyuki<br />

Funatsuki, Yutaka Sato, and Masao Ishimoto, National Agricultural<br />

<strong>Research</strong> Center for Hokkaido Region (NARCH),<br />

Hitsujigaoka, Toyohira, Sapporo, Hokkaido 062-8555, Japan,<br />

e-mail: kentaro@affrc.go.jp; Naoshi Dohmae, The <strong>Institute</strong><br />

of Physical and Chemical <strong>Research</strong> (RIKEN), Hirosawa,<br />

Wako, Saitama 351-0198, Japan.<br />

Acknowledgment: We thank Professor K. Hiratsuka (Yokohama<br />

National University) for his kind gift of the antiserum.<br />

Responses to chilling temperature at the early stage<br />

of development in rice: geographical clines<br />

and genetic bases as revealed by QTL analysis<br />

Kazumitsu Onishi, Noriko Ishigoh-Oka, Mieko Adachi, and Yoshio Sano<br />

Common wild rice as well as indica-type rice are distributed<br />

in tropical and subtropical areas, while japonica type rice is<br />

grown from tropical to temperate areas. Tolerances of chilling<br />

or low temperature are considered to play a role in the wide<br />

distribution of cultivated rice toward the northern region. The<br />

response to chilling temperature (nonfreezing temperature) is<br />

a complex phenomenon that includes primary and secondary<br />

injury by exposure to low temperature, depending on the stage<br />

of development (Kratsch and Wise 2000, Allen and Ort 2001).<br />

The genetic variation in responses to low temperature has been<br />

reported in cultivated rice to be associated with its taxonomic<br />

groups as well as geographic distribution (Oka 1958, Kotaka,<br />

and Abe 1988, Nagamine and Nakagahra 1990). Among various<br />

responses to low temperature, acclimation has not yet been<br />

evaluated substantially in rice. Acclimation, which is a response<br />

to cold temperature by switching to a more cold-tolerant physiological<br />

state, is known to play a role in freezing tolerance in<br />

various plant species, including wheat and barley (Thomashow<br />

1990). The objectives of this study are to investigate genetic<br />

complexities in response to low temperature among wild and<br />

cultivated strains and to evaluate their genetic bases by QTL<br />

analysis.<br />

Materials and methods<br />

We examined responses to chilling temperature at the three<br />

stages of early development (germination, plumule, and seedling<br />

stages), using 40 cultivated and 21 wild strains. These<br />

were selected from diverse origins distributed from tropical<br />

areas to Hokkaido (43 o N), Japan. Hokkaido is one of the northernmost<br />

areas of rice cultivation. Chilling tolerance was evaluated<br />

as follows:<br />

1. Germinability under chilling temperature was tested<br />

with hulled seeds placed on moistened filter papers<br />

in petri dishes which were incubated in the dark at 13<br />

°C. The number of germinated seeds was counted<br />

daily until 20 d after sowing. The germination coefficient<br />

(percentage of germinated seeds/mean days to<br />

germination) was used for comparison.<br />

2. Chilling tolerance at the plumule stage was tested by<br />

incubating germinated seeds with plumule length of<br />

460 <strong>Rice</strong> is life: scientific perspectives for the 21st century


1.5 cm, at 0–1 o C for 2 d. After they grew at 26 o C for<br />

6 d, the degree of injury was compared.<br />

3. Chilling tolerance at the seedling stage was tested using<br />

12-d-old seedlings. The seedlings were grown at<br />

5 °C for 4 d, and the degree of recovery was observed<br />

5 d after growing at 26 o C.<br />

4. Acclimation was evaluated using 12-d-old seedlings.<br />

All the examined strains appeared to die after incubation<br />

at 5 °C for 8 d; however, some were found to<br />

be tolerant after acclimation. For acclimation, the<br />

seedlings were incubated at 12 °C for 3 d before treatment<br />

at 5 °C for 8 d. The degree of recovery was<br />

observed 5 d after growing at 26 o C, giving an index<br />

of acclimation.<br />

All the degrees of tolerance were scored as an index value<br />

ranging from 0 (susceptible type) to 4 (tolerant type), making<br />

two replicates of five seedlings per line. The seedlings were<br />

grown under 14-h photoperiod.<br />

To elucidate the genetic bases of chilling tolerance, the<br />

recombinant inbred lines (RILs) from the cross between A58,<br />

a japonica type from Hokkaido (43 o N), Japan, and W107, a<br />

wild strain from Orissa (20 o N), India, were analyzed. After<br />

crossing A58 with W107, 79 RILs were established from the<br />

F 5 plants by means of the single-seed-descent method. In total,<br />

263 markers, including the reported PCR-based markers<br />

(SSR, STS, and CAPS markers) as well as MITE markers<br />

(Takagi et al 2003), were used for map construction. The F 5<br />

and F 6 plants of each RIL were used for QTL analysis of chilling<br />

tolerance. QTL analysis was conducted by simple interval<br />

mapping and MQM mapping methods using MapQTL version<br />

4.0 (Van Ooijen et al 2002).<br />

Results and discussion<br />

Genetic variation in chilling tolerance<br />

and its geographic distribution<br />

A wide range of variation was observed in all four index values;<br />

however, the pattern of genetic variation was different<br />

between taxa and varietal groups (Table 1). Among the tolerances<br />

examined, only germinability under chilling temperature<br />

was distinctly differentiated between cultivated and wild<br />

forms. No tendency was found that cultivars from Hokkaido<br />

showed a higher germinability under chilling temperature, suggesting<br />

that germinability under chilling temperature might<br />

have been selected for during domestication. At the plumule<br />

stage, japonica (including javanica) type rice was distinctly<br />

more tolerant than indica and wild strains. This tolerance is<br />

considered to reflect changes in the indica-japonica differentiation<br />

since it is diagnostic between the two types, as reported<br />

by Oka (1958). The same tendency was also found in the ability<br />

of acclimation, suggesting that the variation might be related<br />

to an intrinsic difference between the two types. However,<br />

another explanation is that the variation might have resulted<br />

from adaptation to environments within a taxonomic<br />

group.<br />

Table 1. Comparisons of the means of index values for chilling<br />

tolerance among japonica, indica, and wild rice strains.<br />

Trait Type a No. of Mean b (range)<br />

strains<br />

Germinability Jp 27 2.9 a (2.1–4.0)<br />

In 13 2.6 a (1.7–3.1)<br />

W 21 0.8 b (0–2.4)<br />

Plumule Jp 27 2.2 a (0.2–4.0)<br />

In 13 1.0 b (0–4.0)<br />

W 21 0.9 b (0–2.5)<br />

Seedling Jp 27 3.5 a (1.3–4.0)<br />

In 13 2.3 a (0–4.0)<br />

W 21 2.7 a (0–4.0)<br />

Acclimation Jp 27 3.8 a (2.0–4.0)<br />

In 13 1.9 b (0–4.0)<br />

W 21 1.6 b (0–4.0)<br />

a Jp, In, and W indicate japonica (and javanica), indica, and wild strains, respectively.<br />

b Values followed by different letters are significantly different at the<br />

1% level (Scheffe’s test).<br />

To examine micro-evolutionary forces, the relation between<br />

the index values and latitudes of their origins was investigated.<br />

Comparisons were made separately in wild and<br />

cultivated strains. Regarding tolerance in the seedling stage, a<br />

latitudinal cline was reported in cultivated strains (Nagamine<br />

and Nakagahra 1990). Our study revealed that tolerance of the<br />

12-d-old seedling was weakly correlated with latitude in cultivated<br />

strains but not in wild strains. On the other hand, a significant<br />

correlation was detected in both plumule tolerance and<br />

acclimation ability within either wild or cultivated strains (Fig.<br />

1). The distribution of the indica type is usually restricted to<br />

the tropics, while that of the japonica type (including javanica)<br />

is from tropical to temperate areas, which makes it difficult to<br />

distinguish contemporary and historical processes as mentioned.<br />

In contrast, the wild progenitor may reflect the ongoing<br />

processes responding to environments. In wild rice strains,<br />

higher correlations were detected in plumule tolerance and<br />

acclimation ability. It should be noted that acclimation has not<br />

been recognized as an adaptive factor in rice. The highest correlation<br />

in acclimation suggests that acclimation plays a significant<br />

role in chilling tolerance under natural conditions.<br />

The genetic architecture in chilling tolerance<br />

All the four tolerances examined were intercorrelated with each<br />

other among 61 rice strains. Among the responses to chilling<br />

temperature, acclimation was strongly correlated with the other<br />

tolerances (r = 0.60 to 0.71), showing a complex phenomenon<br />

of adaptation to chilling temperature. The genetic bases were<br />

investigated by QTL analysis using 79 RILs derived from A58<br />

× W107. A58 (a japonica type from Hokkaido, Japan) and<br />

W107 (annual type of Oryza rufipogon from Orissa, India)<br />

were tolerant and susceptible for the responses to chilling temperature<br />

examined, respectively. The map of 1,302 cM in total<br />

length was constructed with 263 molecular markers. Among<br />

RILs, no significant correlation was observed between the tol-<br />

Session 15: Challenges to expanding rice production in unfavorable environments 461


Latitude (°N)<br />

40<br />

30<br />

40<br />

30<br />

Japonica (and javanica)<br />

Indica<br />

Wild<br />

20<br />

20<br />

10<br />

0<br />

10<br />

r = 0.44** r = 0.50**<br />

0<br />

–10<br />

0 1 2 3 4<br />

–10<br />

0 1 2 3 4<br />

40<br />

40<br />

30<br />

30<br />

20<br />

20<br />

10<br />

10<br />

0<br />

r = 0.45**<br />

0<br />

r = 0.70**<br />

–10<br />

0 1 2 3 4<br />

Tolerance<br />

–10<br />

0 1 2 3 4<br />

Tolerance<br />

Fig. 1. The relations between latitudinal locations and chilling tolerance at the plumule stage (A) or the<br />

ability of acclimation (B) among 40 cultivated and 21 wild rice strains. ** indicates significance at the 1%<br />

level.<br />

erances except between the tolerances of seedlings with and<br />

without acclimation, suggesting that their genetic bases are<br />

largely independent. Based on QTL analysis, the three significant<br />

QTLs for plumule tolerance were detected on chromosome<br />

1 (LOD = 3.9, near the centromere), chromosome 11<br />

(LOD = 6.0, long arm), and chromosome 12 (LOD = 6.8, short<br />

arm). For the other three tolerances, however, only lower LODpeaks<br />

(suggestive QTLs) were observed on chromosomes 5,<br />

11, and 12.<br />

Furthermore, the three chilling tolerances, excluding germinability,<br />

were significantly correlated with genomic similarity<br />

index (GSI). GSI was computed as a mean value of 109<br />

codominant PCR-based markers by assigning the genotypes<br />

as 1 (A58), –1 (W107), and 0 (heterozygote), expressing the<br />

genomic likeness of an RIL to the parental strains. The results<br />

showed that chilling tolerance might be controlled by multiple<br />

QTLs distributed across the genome as supposed from the QTL<br />

analysis. In the northernmost areas of cultivation, it is considered<br />

that rice plants have been improved by adaptive changes<br />

in response to low temperature. However, our study revealed<br />

that no major QTLs are involved in the tolerances examined.<br />

These results demonstrate that the responses to chilling temperature<br />

are rather complex traits and that the combination of<br />

various genes acting on different stages of development or<br />

under different temperature regimes might be responsible for<br />

their local adaptation.<br />

References<br />

Allen DJ, Ort DR. 2001. Impacts of chilling temperatures on photosynthesis<br />

in warm-climate plants. Trends Plant Sci. 6:36-42.<br />

Kratsch HA, Wise RR. 2000. The ultrastructure of chilling stress.<br />

Plant Cell Environ. 23:337-350.<br />

462 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Kotaka S, Abe N. 1988. The varietal difference of germinability at<br />

low-temperature in rice varieties and the testing method for<br />

the percentage establishment of seedlings. J. Agric. Sci. Tokyo<br />

43:165-168. (In Japanese.)<br />

Nagamine T, Nakagahra M. 1990. Genetic variation of chilling injury<br />

at seedling stage in rice, Oryza sativa L. Jpn. J. Breed.<br />

40:449-455.<br />

Oka HI. 1958. Intervarietal variation and classification of cultivated<br />

rice. Ind. J. Genet. Plant Breed. 18:79-89.<br />

Takagi K, Nagano H, Kishima Y, Sano Y. 2003. MITE-transposon<br />

display efficiently detects polymorphisms among the Oryza<br />

AA-genome species. Breed. Sci. 53:125-132.<br />

Thomashow MF. 1990. Molecular genetics of cold acclimation in<br />

higher plants. Adv. Genet. 28:99-131.<br />

Van Ooijen JW, Boer MP, Jansen C, Maliepaard C. 2002. MapQTL<br />

4.0: software for the calculation of QTL position on genetic<br />

maps. Wageningen (Netherlands): Plant <strong>Research</strong> <strong>International</strong>.<br />

Notes<br />

Authors’ address: Graduate School of Agriculture, Hokkaido University,<br />

Sapporo 060-8589, Japan, e-mail:<br />

onishi@abs.agr.hokudai.ac.jp.<br />

QTL analysis on plasticity in lateral root development<br />

in response to water stress in the rice plant<br />

Hong Wang, Yoshiaki Inukai, Akihiko Kamoshita, Len Wade, Joel Siopongco, Henry Nguyen, and Akira Yamauchi<br />

Lateral roots constitute a great proportion of the root system<br />

of plants in quantity. Two distinct types of lateral roots have<br />

been identified in rice: the L type, which is generally long and<br />

thick, and capable of branching into higher-order laterals; and<br />

the S type, which is short and nonbranching but normally numerous<br />

(Yamauchi et al 1996). These two lateral roots differ<br />

in vascular structure in such a way that the vascular system of<br />

the S type is much less developed (Kono et al 1972). The ability<br />

of a genotype to alter its phenotypic expression in response<br />

to the environment is termed “phenotypic plasticity” (Bradshaw<br />

1965). Yamauchi et al (1996) and Bañoc et al (2000) suggested<br />

that plastic development of lateral roots under water-deficit<br />

conditions may be one of the key traits of some genotypes for<br />

the adaptation to such stress. This study aimed to identify QTLs<br />

for the plasticity of lateral root development in rice plants in<br />

response to water stress using a population of doubled-haploid<br />

lines (DHLs). We also attempted to test a hypothesis that<br />

developmental plasticity in response to water stress may differ<br />

among different types of lateral roots.<br />

Materials and methods<br />

Ninety-six DHLs were derived from a cross between CT9993-<br />

5-10-1-M (japonica, upland adapted) and IR62266-42-6-2 (indica,<br />

lowland adapted) (henceforth abbreviated as CT9993 and<br />

IR62266, respectively) (Kamoshita et al 2000).<br />

Plants were grown hydroponically using a modified<br />

growth pouch method in an environmentally controlled growth<br />

chamber for 2 weeks, w<strong>here</strong> the day/night temperature was set<br />

at 30/25 ºC, relative humidity at 70%, and photoperiod at 16<br />

hours. A plastic container (25 cm in length, 19 cm in width, 27<br />

cm in depth) was filled with water of different PEG concentrations<br />

as described below. Filter papers (18.0 cm in width and<br />

26.0 cm in height) were hung from plastic pipes (0.8 cm in<br />

diam) fixed on the side wall of the container at 1-cm intervals,<br />

and germinated seeds of each of the DHLs were sown between<br />

the two neighboring sheets of filter paper so that the grown<br />

roots would be sandwiched between them. When harvesting,<br />

it was easy to remove the root samples from the filter papers<br />

without any loss or damage. Water stress was induced by using<br />

PEG-6000. Preliminary observation showed that, in the<br />

range of 0 to 120 g L –1 , the concentration of 80 g L –1 resulted<br />

in the most contrasted root response versus 0 g L –1 (control),<br />

and thus the concentration was set at 0 and 80 g L –1 , representing<br />

well-watered and water-stress conditions, respectively.<br />

In the harvested root systems, seminal, nodal, and lateral<br />

roots were identified. Lateral roots were classified further<br />

into three types: L-type laterals, those that were long and thick,<br />

and branched into a higher order; M types, those that were<br />

long and thick but without a branch yet; and S types, those that<br />

were short, slender, and nonbranching. The length of seminal,<br />

nodal, and L- and M-type lateral roots, number of nodal roots<br />

per plant, and number of the three types of lateral roots per<br />

unit length of seminal root axis were measured. Plasticity of a<br />

given trait was evaluated as the difference between mean values<br />

of the trait in stressed and control plants for each DHL.<br />

The marker map with 315 markers, including 145 restriction<br />

fragment length polymorphism, 153 amplified fragment<br />

length polymorphism, and 17 microsatellite markers, has<br />

been constructed at Texas Tech University, Lubbock, Texas<br />

(Zhang et al 2001). Total map distance is 1,788 cM. Putative<br />

QTLs (main-effect QTLs assuming no epistasis) for the traits<br />

were identified based on QTL Mapper (version 1.0) (Wang et<br />

al 1999a,b). Main-effect QTLs were declared significant at<br />

the threshold of 0.005 and with the log of odds (LOD) value<br />

set higher than 2.0.<br />

Session 15: Challenges to expanding rice production in unfavorable environments 463


Table 1. Mean values and range of root parameters per plant of the two parents and DHL population under wellwatered<br />

conditions and water (PEG) stress.<br />

IR62266 CT9993 DHLs<br />

Root traits Well- PEG Well- PEG<br />

watered watered Well- watered PEG<br />

Mean Mean Mean Mean Mean Range Mean Range<br />

Shoot height (cm) 10.6 10.2 8.6 6.8 12.0 6.0–21.0 9.0 3.0–15.8<br />

Seminal root length (cm) 20.2 8.6 23.8 24.7 26.1 6.7–53.0 19.6 5.7–40.5<br />

Nodal root number 6.0 7.3 4.0 4.8 6.4 2.0–11.0 5.2 1.0–10.0<br />

Nodal root length (cm) 23.3 48.2 40.8 40.9 62.7 13.6–167.1 40.8 3.0–94.8<br />

L-type lateral root number a 2.0 1.8 0.1 0.6 0.7 0–2.7 0.7 0–3.2<br />

M-type lateral root number a 1.2 0.6 0 0.6 0.5 0–2.2 0.6 0–2.7<br />

S-type lateral root number a 10.2 8.7 9.9 9.1 9.4 2.8–19.6 9.6 1.6–23.0<br />

L-type lateral root length b 39.3 17.0 2.7 3.0 17.0 0–79.4 16.5 0–74.6<br />

M-type lateral root length b 21.3 1.7 0 2.0 7.3 0–40.7 5.5 0–39.3<br />

a On the basis of cm –1 seminal root axis. b On the basis of 0–10-cm seminal root axis base from shoot.<br />

Results<br />

The mean values and range of root parameters per plant of the<br />

two parents and DHL population under well-watered and water-stress<br />

(PEG) conditions are shown in Table 1. The parameters<br />

showed normal distributions, and transgressive segregations<br />

were observed among the DHL population.<br />

T<strong>here</strong> was a significant difference in the response of the<br />

three types of lateral root development to water stress between<br />

the two parents. CT9993 had a shorter shoot and longer seminal<br />

root, but fewer lateral roots than IR62266. The shoot height<br />

of CT9993 was suppressed by water stress, while that of<br />

IR62266 was not affected. The seminal root length in IR62266<br />

decreased significantly under water stress, while that of CT9993<br />

showed little change. The parents and the DHLs showed different<br />

degrees of plasticity in lateral root development and<br />

nodal root growth in response to water stress.<br />

Table 2 presents the results of putative QTLs for the plasticity<br />

of four lateral root parameters. Two QTLs near ME97-<br />

K706 and K706-ME24 for the plasticity of L-type lateral root<br />

number per cm seminal root axis were found on chromosome<br />

2. Three QTLs near ME216-RG811 and RG811-ME83 on<br />

chromosome 1, and near G188-CDO202 on chromosome 5,<br />

respectively, were identified for the plasticity of S-type lateral<br />

root number per cm seminal root axis in response to water<br />

stress. The QTL for the plasticity of the longest L-type lateral<br />

root was detected on chromosome 7 between EM173 and<br />

ME215. Two QTLs contributing to the plasticity of the longest<br />

M-type lateral root were identified on chromosome 8 between<br />

ME54-ME55 and ME104-ME54, respectively.<br />

Table 2. Chromosome (Chr.) and marker intervals likely containing<br />

QTLs (P


Bradshaw AD. 1965. Evolutionary significance of phenotypic plasticity<br />

in plants. Adv. Genet. 13:115-155.<br />

Kamoshita A, Wade LJ, Yamauchi, A. 2000. Genotypic variation in<br />

response of rainfed lowland rice to drought and rewatering.<br />

III. Water extraction during the drought period. Plant Prod.<br />

Sci. 3(2):189-196.<br />

Kono Y, Igata M, Yamada N. 1972. Studies on the developmental<br />

physiology of the lateral roots in the rice seminal roots. Proc.<br />

Crop Sci. Soc. Jpn. 41:192-204.<br />

Wang DL, Zhu J, Li ZK, Paterson AH. 1999a. Mapping QTLs with<br />

epistatic effects and QTL by environment interactions by mixed<br />

linear model approaches. Theor. Appl. Genet. 99:1255-1264.<br />

Wang DL, Zhu J, Li, ZK, Paterson AH. 1999b. User manual for<br />

QTL Mapper version 1.0. Texas A&M Univ., College Station,<br />

TX.<br />

Yamauchi A, Pardales JR Jr, Kono Y. 1996. Root system structure<br />

and its relation to stress tolerance. In: Ito O, Johansen C, Adu-<br />

Gyamfi JJ, Katayama K, Kumar Rao JVDK, Rego TJ, editors.<br />

Dynamics of roots and nitrogen in cropping systems of the<br />

semi-arid tropics. Tsukuba (Japan): Japan <strong>International</strong> <strong>Research</strong><br />

Center for Agricultural Sciences. p 211-233.<br />

Zhang J, Zheng HG, Aarti A, Pantuwan G, Nguyen TT, Tripathy JN,<br />

Sarial AK, Robin S, Babu RC, Nguyen BD, Sarkarung S, Blum<br />

A, Nguyen HT. 2001. Locating genomic regions associated<br />

with components of drought resistance in rice: comparative<br />

mapping within and across species. Theor. Appl. Genet.<br />

103:19-29.<br />

Notes<br />

Authors’ addresses: Hong Wang, Soil and Fertilizer <strong>Institute</strong>, Chinese<br />

Academy of Agricultural Sciences; Hong Wang, Yoshiaki<br />

Inukai, and Akira Yamauchi, Graduate School of<br />

Bioagricultural Sciences, Nagoya University; Akihiko<br />

Kamoshita, Field Production Science Center, University of<br />

Tokyo; Len Wade, School of Plant Biology, University of<br />

Western Australia; Joel Siopongco, <strong>International</strong> <strong>Rice</strong> <strong>Research</strong><br />

<strong>Institute</strong>; Henry Nguyen, Department of Agronomy,<br />

Plant Sciences Unit, University of Missouri, e-<br />

mail:ayama@agr.nagoya-u.ac.jp.<br />

Acknowledgment: This research was partially supported by the Japan<br />

Society of the Promotion of Science with a Grant in Aid<br />

for Scientific <strong>Research</strong> (No. 16380015).<br />

Wrap-up of Session 15<br />

The session on abiotic stresses, formally titled “Challenges to<br />

expanding rice production in unfavorable environments,” was<br />

convened by S. Tobita (JIRCAS) and R. Lafitte (<strong>IRRI</strong>). The conveners<br />

recognized that the session should deal with the linkages<br />

across different disciplines and across different levels of institutions<br />

and organizations for the challenge, as well as understanding<br />

the kinds of abiotic stresses in rice ecologies. So, we invited<br />

five speakers with a background in rice physiology or soil science,<br />

with each having specialized experience in salinity, drought,<br />

submergence, iron toxicity, and soil acidity, respectively. The<br />

molecular biology of stress responses in the rice crop were to be<br />

reviewed, taking into account some of the recent progress in this<br />

area. It was also good to have a lecture on the principles of<br />

stress physiology; <strong>here</strong>in the uniqueness of the rice crop would<br />

automatically stand out. Because the Crop Science Society of<br />

Japan concurrently organized a session on cold/heat tolerance in<br />

rice, we did not examine temperature stress in the session, but<br />

called for poster presentations on this subject.<br />

Our session began with more than 100 participants. Because<br />

R. Lafitte could not attend the symposium, the session<br />

was chaired by G.V. Subbarao (JIRCAS) and me. I briefly explained<br />

the aims and outlined the structure of the session, followed by<br />

the first speaker, Nguyen Thi Lang from the Cuu Long Delta <strong>Rice</strong><br />

<strong>Research</strong> <strong>Institute</strong> (Vietnam). She discussed tissue culture and<br />

in vitro approaches for selecting salt-tolerant somaclones in rice,<br />

for which successful examples were reported. The second lecturer<br />

was Prof. S. Fukai of the University of Queensland, Australia<br />

(whose paper is co-authored by A. Kamoshita, the University of<br />

Tokyo), who talked about experiences with drought studies at<br />

several field sites in Southeast Asia, mostly in the rainfed low-<br />

land ecology. He emphasized the importance of interactions between<br />

genotype and environment in crop performance under<br />

drought stress. Characterization of the type of drought at a proper<br />

site is sometimes not regarded as important but it does affect<br />

the selection criteria for better drought tolerance, he explained.<br />

K. Futakuchi, a Japanese scientist currently working for the Africa<br />

<strong>Rice</strong> Center, discussed his research on submergence tolerance<br />

in rice, including African rice (Oryza glaberrima) and Nericas<br />

(interspecific hybrids of Asian and African rice). His achievements<br />

covered the physiological elucidation of responses to submergence<br />

stress and genotypic variation in submergence tolerance.<br />

The audience understood that O. glaberrima rice would be a good<br />

genetic resource for achieving rice with higher tolerance of submergence<br />

stress in this region through wide hybridization.<br />

K.L. Sahrawat, working for the <strong>International</strong> Crops <strong>Research</strong><br />

<strong>Institute</strong> for the Semi-Arid Tropics (ICRISAT) in India, discussed<br />

another problem also prevalent in West Africa, iron toxicity, especially<br />

in the irrigated and rainfed lowland ecologies. With his background<br />

in soil chemistry, he explained a detailed process of chemical<br />

development of toxic iron ions in the soil. He also showed us<br />

the importance of nutrient management and the use of varieties<br />

tolerant of iron toxicity.<br />

K. Okada (National Agriculture <strong>Research</strong> Organization, Japan),<br />

in a paper co-authored by M. Wissuwa (<strong>IRRI</strong>), spoke about<br />

soil acidity problems in tropical upland areas. An investigation of<br />

typical Oxisols in South America suggested that the real cause of<br />

the genotypic difference did not result from tolerance of toxic Al<br />

but from higher Ca absorbing capacity of the roots, probably because<br />

of the higher preferential adsorption of Ca over Al at the<br />

cell wall. He also mentioned recent progress in future applica-<br />

Session 15: Challenges to expanding rice production in unfavorable environments 465


tions of the marker-assisted breeding approach to improve adaptation<br />

to soil acidity and related nutrient deficiencies in upland<br />

rice. The next speaker, J. Bennett from <strong>IRRI</strong>, the only molecular<br />

biologist in this session, reviewed old and new techniques for the<br />

study of molecular mechanisms of tolerance for many kinds of<br />

abiotic stresses, with an example involving drought tolerance.<br />

The session had a general discussion after the six presentations.<br />

The chairman emphasized the linkages across various<br />

disciplines for expanding rice production in unfavorable environments.<br />

What and how should the linkages be among agronomy,<br />

physiology, soil science, genetics, breeding, molecular biology,<br />

and so on The speakers especially discussed drought and soil<br />

acidity. We recognize that a multidisciplinary characterization of<br />

the targeted stresses could be the best strategy for our goals. A.<br />

Blum, founder of plantstress.com from Israel, synthesized the<br />

discussion based on his long and distinguished career and handson<br />

experience in stress physiology. He emphasized the physiological<br />

foundation of crop breeding for abiotic stress tolerance,<br />

with a good example of drought avoidance and tolerance. Many<br />

in the audience were convinced that, without a physiological understanding<br />

of crop stress, research could go the wrong way and<br />

selection and breeding programs could be useless.<br />

466 <strong>Rice</strong> is life: scientific perspectives for the 21st century


SESSION 16<br />

Pest management with minimal<br />

environmental stress<br />

CONVENER: C. Vera Cruz (<strong>IRRI</strong>)<br />

CO-CONVENER: Y. Suzuki (NARO)


Integrated biodiversity management (IBM) in rice fields<br />

Keizi Kiritani<br />

Kiritani (1975) stated that the central issue for agriculture in<br />

the future would be how to manage and optimize biodiversity,<br />

stability, and productivity within agroecosystems. The paddy<br />

ecosystem is an integrated, water-dependent system, which can<br />

contain many kinds of living organisms: birds, fish, reptiles,<br />

amphibia, arthropods, and plants. Paddy fields were originally<br />

wetlands that are artificially constructed devices for rice production.<br />

Nowadays, very few natural wetlands remain, and<br />

many aquatic organisms now depend partly or fully on paddy<br />

fields.<br />

To raise both land and labor productivity, the Japanese<br />

government has promoted the conversion of poorly drained<br />

wet paddy fields into well-drained ones in association with a<br />

policy to consolidate fragmented farmlands. U-shaped concrete<br />

ditches have replaced traditional earth ditches and irrigation-supply<br />

canals have been separated from drainage canals,<br />

which effectively reduced the variety of habitats for<br />

aquatic organisms.<br />

Biodiversity of arthropod fauna in paddy fields<br />

Infestations by rice borers, Chilo suppressalis and Scirpophaga<br />

incertulas, and the intermittent and sudden occurrences of outbreaks<br />

of Nilaparvata lugens were the major causes of losses<br />

in rice yield in temperate Asia. These were the major pests<br />

until around 1965. T<strong>here</strong>after, leaf- and planthoppers and the<br />

viral diseases RSLV and RDV transmitted by them were predominant<br />

for about 30 years. Meanwhile, the rice water weevil,<br />

Lissorhoptrus oryzophilus, invaded Japan in 1976 from<br />

the United States, inflicting serious damage to rice in the late<br />

1980s. Since 1995, the damage caused by various kinds of<br />

stink bugs and mirids has become the most serious problem.<br />

Many species of arthropods with diverse types of life<br />

cycles occupy different habitats within the paddy<br />

agroecosystem. Sympetrum dragonflies emerge from paddy<br />

fields and stay in coppiced woodlots to mature sexually before<br />

returning to paddy fields to oviposit. The eggs hatch in<br />

the following spring when irrigation water becomes available.<br />

Newly emerged adults of the water scorpion, Ranatra chinensis,<br />

move from paddy fields to irrigation ponds for overwintering.<br />

Oviposition takes place in paddy fields in the next spring. The<br />

migratory planthopper pests, N. lugens and Sogatella furcifera,<br />

are annually replenished by a long-range immigration from<br />

tropical endemic habitats.<br />

The biodiversity of the paddy agroecosystem t<strong>here</strong>fore<br />

depends not only on the paddy fields themselves but also on<br />

water channels, irrigation ponds, levees, surrounding fallow<br />

fields, neighboring farmlands, secondary forests, wetlands, rivers,<br />

and remote hibernating areas (Kiritani 2000).<br />

IPM perspective in relation to biodiversity<br />

In the past, most studies on paddy ecosystems have focused<br />

on productivity and its stability in terms of rice yields.<br />

Arthropods in paddy ecosystems can be classified into three<br />

main groups according to their ecological requirements: (1)<br />

resident species adapted to the continuous cropping of rice in<br />

the same field, (2) migratory species adapted to exploit rice as<br />

an annual crop, and (3) aquatic species originating from stillwater<br />

habitats in wetlands. Concerning groups 1 and 2, integrated<br />

pest management (IPM) programs, which have a primary<br />

objective of maximizing economic profit on the farm,<br />

have been implemented with various degrees of success. Although<br />

IPM is becoming widespread, those insects (Tada-nomushi<br />

= species of unknown or uncertain function that routinely<br />

occur in the habitat) that have no direct economic impact<br />

on rice production have been mostly ignored as an important<br />

element in the rice ecosystem. Consequently, some aquatic<br />

insects are in danger of extinction, thus requiring conservation<br />

(Kiritani 1979, 2000, Kiritani and Naba 1994).<br />

The green rice leafhopper, Nephotettix cincticeps, is 80%<br />

of the diet of a lycosid spider, Pardosa pseudoannulata, in<br />

paddy fields. No lycosid spiders, however, developed to adults<br />

when fed only N. cincticeps. When lycosid females were allowed<br />

to prey upon mixed species of prey, their fecundity<br />

greatly increased (Suzuki and Kiritani 1974). Those species<br />

such as chironomids and collembola, for example, that are<br />

neither pests nor natural enemies, and yet are useful as alternative<br />

food of generalist predators, can be referred to as minor,<br />

yet important, components of the community (Kiritani<br />

2000).<br />

Immigration of spiders to paddy fields occurs after the<br />

appearance of chironomids. Early insecticide applications to<br />

control rice stem borers often result in the resurgence of<br />

planthoppers and leafhoppers 1 month later because insecticide<br />

treatments simultaneously kill spiders and chironomids<br />

(Kobayashi 1961). In the tropics, prevention of outbreaks of<br />

planthoppers and leafhoppers depends on protection of earlyacting<br />

natural enemies by avoiding early insecticide spraying<br />

(Way and Heong 1994, Settle et al 1996).<br />

Levees are likely to act as refuges for various kinds of<br />

natural enemies of arthropod pests that occur in upland crops<br />

grown close to paddy fields. A dwarf spider, Ummeliata<br />

insecticeps, common in paddy fields dispersed from levees by<br />

ballooning in late May to uplands remains t<strong>here</strong> until the end<br />

of the rainy season. It behaved like a specific predator attacking<br />

a newly hatched colony of larvae of Spodoptera litura in<br />

taro fields (Nakasuji et al 1973). Another example is the<br />

anthocorid bugs, Orius spp., that are effective natural enemies<br />

of Thrips palmi, a serious invasive alien pest of eggplant. O.<br />

468 <strong>Rice</strong> is life: scientific perspectives for the 21st century


IBM<br />

Intensity of management<br />

100<br />

IPM<br />

Conservation<br />

IPM<br />

Density<br />

IPM<br />

Economic injury level<br />

IBM<br />

50<br />

Conservation<br />

Conservation<br />

Extinction threshold<br />

Fig. 1. Illustration of the concepts of IPM, conservation, and IBM.<br />

nagaii and O. sauteri occur on rice and on white clover grown<br />

on levees, respectively, before invading eggplant fields in early<br />

June (Ohno and Takemoto 1997).<br />

Integrated biodiversity management (IBM)<br />

0<br />

Paddy<br />

field<br />

Levee Ditch Irrigation<br />

pond<br />

Secondary<br />

forest<br />

Fig. 2. Difference in the intensity of management in accordance<br />

with habitats. (Adapted from Kiritani 2000.)<br />

A new concept, integrated biodiversity management (IBM),<br />

has been proposed under which IPM and conservation are reconciled<br />

and made compatible with each other (Fig. 1). IPM<br />

requires that densities of each pest species be kept below their<br />

specific economic injury level. In conservation, target species<br />

have to be managed to remain above a specific extinction<br />

threshold. Since some presently rare carnivorous aquatic<br />

arthropods, such as Lethocerus deyrollei, and some large-sized<br />

dytiscid beetles have been recorded as pests of fish culture<br />

when they were abundant, these species also should be managed<br />

to keep their populations below defined economic injury<br />

levels (Kiritani 2000).<br />

The status of a pest species could be changed by IPM<br />

into a Tada-no-mushi (minor or nontarget insect), which can<br />

function as potential food for generalist predators. S. incertulas<br />

is currently almost extinct in Japan. From the viewpoint solely<br />

of an economically oriented IPM, however, this is of little consequence<br />

because S. incertulas was an important rice pest to<br />

be controlled. But, in view of IBM, such relatively rare species,<br />

such as S. incertulas and some aquatic insects, can be<br />

considered a target for conservation.<br />

The arthropods inhabiting paddies require various habitats<br />

for the completion of their life cycles. The relative importance<br />

of IPM and conservation changes along a continuum away<br />

from the paddy field through the levee, ditch, irrigation pond,<br />

and coppiced woodlots (Fig. 2). The two lines cross at a point<br />

most appropriate for a specific location as well as for the target<br />

species concerned (Kiritani 2000).<br />

The concept of IBM is not limited to the paddy ecosystem,<br />

but is also applicable to all types of agricultural systems.<br />

Crops range from those that require intense IPM intervention<br />

with little consideration of species conservation, for example,<br />

greenhouse crops, to those for which high levels of pest control<br />

and biodiversity preservation can be attained, for example,<br />

a complex home garden or backyard in the tropics.<br />

Conclusions<br />

It is necessary that a set of elemental habitats be available for<br />

completion of the life cycle of many species and that these<br />

multiple habitats be within the range of dispersal of these species.<br />

A set of habitats, including host plants (prey), shelter,<br />

hibernacula, mating places, etc., is essential to ensure the persistence<br />

of diverse species. For aquatic insects, irrigation ponds,<br />

coppiced woodlots, and poorly drained wetlands are necessary<br />

habitats in addition to paddy fields. Because cleaning an<br />

irrigation pond could result in the complete destruction of the<br />

aquatic fauna in the pond, neighboring ponds that supply the<br />

newly cleaned pond with aquatic species should exist within<br />

an appropriate distance, for example, 1 km for dragonflies<br />

(Moriyama 1997).<br />

It is recommended to adopt IPM strategies and tactics<br />

that are compatible with conservation.<br />

Preventing alien species from invading the paddy ecosystem<br />

is very important. Alien species often jeopardize the<br />

conservation of endangered species by competition and inducing<br />

additional chemical control applications.<br />

Special consideration should be given to avoid lethal<br />

effects on species that are vulnerable to pesticides, such as<br />

aquatic, univoltine, and carnivorous or monophagous species.<br />

Bioaccumulation of persistent biotoxins is far greater in aquatic<br />

systems than in terrestrial systems. Contamination of irrigation<br />

water with pesticides must t<strong>here</strong>fore be avoided as much<br />

as possible. We can keep the amount of pesticides to a minimum<br />

by applying knowledge of the behavioral ecology of the<br />

pests.<br />

Farm management techniques that make the difference<br />

as great as possible between the population levels for an EIL<br />

Session 16: Pest management with minimal environmental stress 469


(economic injury level) and an extinction threshold should be<br />

introduced in the IBM system. As an alternative to the EIL, we<br />

could use another EIL in which the “E” refers to “ecological<br />

or environmental.” This new EIL, however, has yet to be established.<br />

In general, global warming may work in favor of natural<br />

enemies (except for spiders) by increasing the number of generations<br />

more than for their host species (Kiritani 1999). Biological<br />

control is expected to become a more important control<br />

tactic in the future. Uncertainty remains, however, regarding<br />

the extent to which host-parasitoid phenology will be synchronized<br />

after an increase in the number of generations. Parasitism<br />

and predation, similar to those in paddy fields in the<br />

tropics, would be expected to increase through this numerical<br />

response and enhance the natural control. It is inevitable that<br />

implementation of IBM involves some trial and error. We need<br />

an adaptive approach toward IBM. We should not only invite<br />

active involvement of persons interested in evaluation and<br />

improvement, but should also adopt a modest attitude toward<br />

developing and improving an ongoing IBM design.<br />

References<br />

Kiritani K. 1975. Pesticides and ecosystems. J. Pesticide Sci.<br />

Commem. Issue:65-75 (In Japanese.)<br />

Kiritani K. 1979. Pest management in rice. Ann. Rev. Entomol.<br />

24:279-312.<br />

Kiritani K. 1999. Shift of IPM strategy for rice under global warming<br />

in temperate areas. In: Zhang R, Gu D, Zhang W, Zhou C,<br />

Pang Y, editors. Integrated pest management in rice-based<br />

ecosystem. Guangzhou (China): Editorial Department of Journal<br />

of Zhongshan University. p 235-244.<br />

Kiritani K. 2000. Integrated biodiversity management in paddy fields:<br />

shift of paradigm from IPM toward IBM. Integ. Pest Manage.<br />

Rev. 5:175-183.<br />

Kiritani K, Naba K. 1994. Development and implementation of rice<br />

IPM in Japan. In: Heinrichs EA, editor. Biology and management<br />

of rice insects. New Delhi (India): Wiley Eastern Limited.<br />

p 713-731.<br />

Kobayashi T. 1961. The effect of insecticidal applications to the rice<br />

stem borer on the leafhopper populations. Special report on<br />

the forecasting of agricultural pests and diseases no. 6. 126 p.<br />

(In Japanese with English abstract.)<br />

Moriyama H. 1997. What is protecting paddy fields Tokyo (Japan):<br />

Nobunkyo. 205 p. (In Japanese.)<br />

Nakasuji F, Yamanaka H, Kiritani K. 1973. The disturbing effect of<br />

micryphantid spiders on the larval aggregation of the tobacco<br />

cutworm, Spodoptera litura (Lepidoptera: Noctuidae). Kontyu<br />

41:220-227.<br />

Ohno K, Takemoto H. 1997. Species composition and seasonal occurrence<br />

of Orius spp. (Heteroptera: Anthocoridae), predacious<br />

natural enemies of Thrips palmi (Thysanoptera:<br />

Thripidae), in eggplant fields and surrounding habitats. Appl.<br />

Entomol. Zool. 32:27-35.<br />

Settle WH, Ariawan H, Astuti ET, Cahyana W, Hakim AL, Hindayana<br />

D, Lestari AS, Pajarningsih. 1996. Managing tropical rice pests<br />

through conservation of generalist natural enemies and alternative<br />

prey. Ecology 77:1975-1988.<br />

Suzuki Y, Kiritani K. 1974. Reproduction of Lycosa pseudoannulata<br />

under different feeding conditions. Jpn. J. Appl. Entomol. Zool.<br />

18:166-170. (In Japanese with English abstract.)<br />

Way MJ, Heong KL. 1994. The role of biodiversity in the dynamics<br />

and management of insect pests of tropical irrigated rice: a<br />

review. Bull. Entomol. Res. 84:567-587.<br />

Notes<br />

Author’s address: Ito City, Shizuoka, e-mail: kiritanik@ybb.ne.jp.<br />

Habitat manipulation in sustainable pest management<br />

in the rice ecosystem of the Yangtze River Delta<br />

Xiaoping Yu, Jianming Chen, Zhongxian Lu, Xusong Zheng, Hongxin Xu, and Juefeng Zhang<br />

<strong>Rice</strong> planthoppers, Nilaparvata lugens Stål and Sogatella<br />

furcifera Horvath, are major insect pests in the Yangtze River<br />

Delta rice ecosystem. About 50–100 million tons of rice were<br />

lost per year during 1973-2000 in China because of the incidence<br />

of rice planthoppers (Yu et al 1999). Usually, the injudicious<br />

use of insecticides in the rice ecosystem caused serious<br />

problems, such as resurgence and resistance of insect pests,<br />

residue, and adverse effects on the environment. Predators and<br />

parasitoids were found to be an effective bio-agent to suppress<br />

insect pests, but natural enemies per se usually could not efficiently<br />

suppress insect pests below the damage threshold because<br />

of the low parasitism and predation rate of natural en-<br />

emies caused by an unstable rice habitat (made unstable by<br />

harvesting, pesticide application, and other practices) and winter<br />

interruption (Way and Heong 1994). T<strong>here</strong>fore, neighboring<br />

habitats are very important in conserving and enhancing<br />

the population of natural enemies in rice fields (Yu et al 1998).<br />

To evaluate the role of habitat diversity in promoting natural<br />

enemies in rice habitats, the movement of spiders and Anagrus<br />

spp. between rice and neighboring habitats was monitored.<br />

Meanwhile, spraying experiments to determine the optimal<br />

dosage of chemicals were conducted on a demonstration farm<br />

with various habitat manipulations.<br />

470 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Materials and methods<br />

Test insects<br />

Adults of delphacids, N. lugens and Sacchasydne procerus in<br />

rice fields and S. procerus in neighboring Zizania caduciflora<br />

L. habitats, were collected, and were reared in culturing mylar<br />

cages separately. The egg parasitoid A. nilaparavate was collected<br />

by exposing potted rice and Zizania plants bearing hopper<br />

eggs. The spider Pirata subpiraticus was collected using a<br />

Blower-vacuum suction machine and sorted in the laboratory<br />

for further experiments (Xu et al 1987).<br />

Dispersal patterns of egg parasitoids<br />

between habitats using sticky traps<br />

Yellow sticky traps made with a wooden plate (50 cm 2 ) were<br />

used for monitoring the dispersal of Anagrus spp. on the field<br />

bunds between habitats. The yellow sticky papers were replaced<br />

every 6 hours, and Anagrus spp. trapped on sticky paper were<br />

identified and counted.<br />

Movement of the spider P. subpiraticus between rice<br />

and Zizania habitat measured by the capture<br />

and recapture test<br />

In the field capture and recapture test, all spiders marked with<br />

rubidium were released in the releasing plot of a Zizania habitat.<br />

Spiders in neighboring rice fields were sampled by a<br />

Blower-vacuum suction machine at 5, 10, 20, and 40 m from<br />

the releasing plot on the 1st, 3rd, 7th, and 15th day after releasing.<br />

All specimens were digested and analyzed for Rb content<br />

by an Atomic Absorption Spectrometer (Perkin Elmer<br />

Model 3300) at the wavelength of 780.0 nm (Berry et al 1972,<br />

Perfect et al 1985).<br />

Effects of various spraying times and dosages<br />

in rice fields with habitat diversity<br />

A field of 0.45 ha planted with hybrid rice Shanyou 63 as singleseason<br />

rice was selected for testing. The treatments of insecticide<br />

spraying in rice fields were arranged as follows: (1)<br />

monocrotophos was sprayed on 20 June for leaffolder, (2)<br />

Fipronil was sprayed on 6 July for stem borer, (3) buprofezin<br />

was used on 1 August and 15 August for brown planthopper,<br />

and (4) spraying water only was the check. All treatments were<br />

replicated three times. Habitat manipulation was done surrounding<br />

rice fields, such as planting soybean on the field bund,<br />

digging a canal in the field at 5-m intervals, and reconstructing<br />

the field bund. The arthropods in each plot were collected<br />

using Blower-vacuum suction machines and yield loss was<br />

calculated after rice harvesting.<br />

Results<br />

The results showed that many egg parasitoids (Anagrus spp.)<br />

moved into rice fields from neighboring Zizania habitats: about<br />

60 per sticky trap per day were caught during July and August.<br />

A high frequency of movement occurred from early June to<br />

early August, especially in July and August. More Anagrus<br />

Table 1. The number of marked and unmarked lycosid spiders recaptured<br />

at various distances from a releasing plot.<br />

Days after Distance from a Individuals Individuals<br />

releasing releasing site (m) captured marked<br />

1<br />

1st day 5 35 2<br />

10 19 0<br />

20 19 1<br />

40 28 0<br />

3<br />

3rd day 5 32 2<br />

10 26 1<br />

20 16 1<br />

40 18 0<br />

7<br />

7th day 5 45 0<br />

10 28 0<br />

20 15 0<br />

40 57 0<br />

15<br />

15th day 5 24 1<br />

10 25 0<br />

20 17 0<br />

40 21 1<br />

spp. moved into rice fields from neighboring Zizania habitats<br />

than from other cultivated habitats. After October, numerous<br />

Anagrus spp. moved back to Zizania habitats from rice habitats.<br />

The proper arrangement of rice fields and Zizania habitats<br />

could significantly enhance the number of egg parasitoids<br />

in rice fields.<br />

The capture and recapture test with Rb marking demonstrated<br />

that the lycosid spider could disperse up to 40 m into<br />

rice fields from a releasing plot on the 15th day after release.<br />

However, more marked spiders were captured at the 5-m site<br />

during the first to third day (Table 1). The results showed that<br />

the spider P. subpiraticus could rapidly move into rice fields<br />

after rice transplanting, suggesting that spiders in neighboring<br />

Zizania fields could efficiently promote the spider population<br />

in rice fields.<br />

With the farmers’ conventional spraying (4 times per<br />

season of rice), most spiders and Anagrus spp. were killed;<br />

however, the number of brown planthoppers was not significantly<br />

lower than that in the other treatments with 0–3<br />

sprayings. The number of leaffolders (Cnaphalocrocis<br />

medinalis) and stem borers (Chilo suppressalis) in 3- and 4-<br />

spraying treatments was significantly higher than in treatments<br />

with 0, 1, and 2 sprayings. More rice yield was lost in 0–2-<br />

spraying treatments than in treatments with 3 and 4 sprayings.<br />

T<strong>here</strong> was no difference in rice yield between 3- and 4-spraying<br />

treatments (Table 2). It is suggested that 1–2 insecticide<br />

sprayings could be saved, especially sprayings after August.<br />

Discussion<br />

The results indicated that a high number of spiders and Anagrus<br />

spp. dispersed into rice fields after rice transplanting through-<br />

Session 16: Pest management with minimal environmental stress 471


Table 2. Test on optimizing spraying of pesticides in paddy fields. a<br />

Application Spiders Anagrus spp. Brown Leaffolder Stem borer Yield loss<br />

No. of sprayings time (date) (no. per m 2 ) (no. per m 2 ) planthopper (no. per hill) (deadhead %) (%)<br />

(no. per m 2 )<br />

No spraying 22.7 a 12.2 a 18.3 a 2.9 a 0.24 a 36.01 a<br />

One spraying 6 Jul 23.4 a 10.3 a 27.6 a 4.5 a 0.06 b 14.33 b<br />

Two sprayings 6 Jul, 15 Aug 17.5 a 4.5 b 33.1 a 4.9 a 0.03 b 9.04 b<br />

Three sprayings 6 Jul, 1 Aug, 15 Aug 12.3 a 4.2 b 25.3 a 0.9 b 0 b 0.51 c<br />

Four sprayings 20 Jun, 6 Jul, 1 Aug, 15 Aug 3.4 b 1.2 c 17.2 a 1.1 b 0 b 0 c<br />

a The transplanting date was 1 June. Data were analyzed with Duncan’s multiple range test between treatments. Means followed by a different letter in the same column are<br />

significantly different at P


Evaluating augmentative releases of the mirid bug<br />

Cyrtorhinus lividipennis to suppress brown planthopper<br />

Nilaparvata lugens in open paddy fields<br />

Masaya Matsumura, Satoru Urano, and Yoshito Suzuki<br />

Augmentative releases of natural enemies are a widely used<br />

method of controlling many pests, mainly in greenhouse vegetables<br />

(Van Driesche and Bellows 1996). In open rice fields,<br />

however, few attempts have been made to manage insect pests<br />

by releasing natural enemies. The mirid bug Cyrtorhinus<br />

lividipennis Reuter is the egg predator of the brown planthopper<br />

Nilaparvata lugens (Stål) and the whitebacked planthopper<br />

Sogatella furcifera (Horváth), the two major pests of rice<br />

throughout Asia (Chiu 1979). Although the potential growth<br />

rate of C. lividipennis is very high (Suzuki and Tanaka 1996,<br />

Matsumura and Suzuki 1999), the initial population density of<br />

C. lividipennis in Japan is usually low (Teramoto et al 1996).<br />

This is because C. lividipennis is not able to overwinter successfully<br />

in Japan, and colonization occurs annually following<br />

long-distance migration from southern China. Thus, we evaluated<br />

the effectiveness of augmentative releases of C.<br />

lividipennis to suppress N. lugens in open paddy fields.<br />

Materials and methods<br />

Mass rearing of C. lividipennis<br />

As no mass-rearing technique for C. lividipennis using an artificial<br />

diet has been established, we developed a simple method<br />

for mass rearing of C. lividipennis on rice seedlings using N.<br />

lugens eggs as food. To calculate the reproductive efficiency<br />

of C. lividipennis, 25 or 50 pairs of adult C. lividipennis were<br />

introduced into plastic cages (30 × 25 × 28 cm) containing 5–<br />

6-day-old rice seedlings infested with 50 gravid females of N.<br />

lugens. After 2 weeks, new rice seedlings were introduced into<br />

the plastic cages and the old rice seedlings were removed after<br />

all the insects had moved to the new ones. T<strong>here</strong>after, the rice<br />

seedlings were renewed at 7-day intervals. After 5 weeks, the<br />

number of adult offspring was counted. The experiments were<br />

conducted in the laboratory at a temperature of 25 ± 1 °C and<br />

a photoperiod of 16L:8D.<br />

Augmentative release experiment<br />

In 1999-2001, C. lividipennis adults (1-week-old adults produced<br />

in the laboratory) were augmentatively released at<br />

predator:prey (C. lividipennis adult:N. lugens adult) ratios of<br />

0:1 (nonrelease control), 1:1, and 1:2 (only in 1999) into replicated<br />

experimental blocks (7 × 7 m) in open paddy fields.<br />

The release was done at the start of the immigrant generation<br />

of N. lugens (early July). Because the density of N. lugens<br />

immigrants was quite low in those three years, N. lugens adults<br />

were also released at a rate of 0.2 individual per hill prior to<br />

the release of C. lividipennis. In 2001, the effect of an additional<br />

release of C. lividipennis at the start of the second generation<br />

(early August) was also evaluated.<br />

A routine population census for the two planthoppers<br />

(released N. lugens and naturally-occurring S. furcifera) and<br />

C. lividipennis was conducted using a FARMCOP suction sampler<br />

(Cariño et al 1979). A plastic cylinder (30 cm in diameter<br />

and 70 cm in height) was used to cover a rice hill. All arthropods<br />

inside the cylinder were collected with the sampler, stored in<br />

70% alcohol, and counted in the laboratory under a binocular<br />

microscope. The number of rice plants sampled was 15 per<br />

experimental block per sampling date. Censuses were made at<br />

intervals of 5–10 days from late July to late September (in<br />

1999) or early October (in 2000 and 2001).<br />

Generation boundaries and mean population density of<br />

the two planthoppers and C. lividipennis for each successive<br />

generation were calculated based on Kuno’s (1968) method.<br />

All analyses were conducted using a 3-year data set of mean<br />

population densities. The effect of the natural enemy release<br />

on population dynamics of N. lugens was determined by<br />

Yamamura’s (1999) key-factor/key-stage analysis. All statistical<br />

analyses were performed with the JMP version 5 Statistical<br />

Package.<br />

Results and discussion<br />

Mass rearing of C. lividipennis<br />

Five weeks after the introduction of C. lividipennis adults into<br />

the plastic cage, 286.8 ± 15.7 and 436.4 ± 30.3 individual adult<br />

offspring were obtained from 25 and 50 C. lividipennis adults,<br />

respectively. The population growth rate of C. lividipennis was<br />

5.7 and 4.4 per generation for the 25- and 50-adult treatments,<br />

respectively.<br />

The present method of mass rearing of C. lividipennis is<br />

high enough for stock maintenance and use in release experiments.<br />

For practical and commercial uses of C. lividipennis as<br />

a biological control agent, however, t<strong>here</strong> is a need to establish<br />

a mass-rearing technique using an artificial diet.<br />

Augmentative release experiment<br />

The population density of the first-generation N. lugens (late<br />

July to early August) was significantly suppressed when C.<br />

lividipennis was released at predator:prey ratios of 1:1 (highratio<br />

release) (ANOVA, F = 8.38, P


Population density per hill log (n + 1)<br />

3.0<br />

High-ratio release<br />

Low-ratio release<br />

Nonrelease<br />

2.0<br />

1.0<br />

G1<br />

G2<br />

G3<br />

A<br />

High-ratio release<br />

Nonrelease<br />

G1<br />

G2<br />

G3<br />

B<br />

High-ratio release<br />

Low-ratio release<br />

× 2 releases<br />

Nonrelease<br />

G1<br />

G2<br />

G3 C<br />

0.0<br />

Rep. 1<br />

Rep. 1<br />

Rep. 1<br />

3.0<br />

2.0<br />

1.0<br />

0.0<br />

Rep. 2<br />

Jul Aug Sep Oct<br />

Rep. 2<br />

Jul Aug Sep Oct<br />

Month<br />

Rep. 2<br />

Jul Aug Sep Oct<br />

Fig. 1. Population trends of Nilaparvata lugens in each replicated block (replication 1 and 2) following augmentative releases of Cyrtorhinus<br />

lividipennis in open paddy fields. (A) C. lividipennis adults were released in early July at predator:prey (C. lividipennis adult:N. lugens adult)<br />

ratios of 0:1 (nonrelease), 1:1 (high-ratio release), and 1:2 (low-ratio release) in 1999, (B) at ratios of 0:1 and 1:1 in 2000, and (C) at ratios<br />

of 0:1 and 1:1, and an additional release in early August (high ratio × 2 releases) in 2001. G1, G2, and G3 indicate the first, second, and<br />

third generation, respectively.<br />

Table 1. Key-factor/key-stage table for the population density of the third generation in<br />

Nilaparvata lugens.<br />

Generation<br />

Factor df F P<br />

G1/G0 G2/G1 G3/G2 Total<br />

Natural enemy release 1 3.129 –0.199 0.798 3.728 11.0 0.002<br />

Replication 1 0.295 –0.055 –0.026 0.215 1.9 0.201<br />

Year 2 0.872 3.491 –0.407 3.957 17.6 0.001<br />

Unknown variability 7 0.445 0.339 0.229 1.014<br />

Total 11 4.742 3.576 0.595 8.913<br />

was the most significant factor suppressing the density of the<br />

third-generation N. lugens (Table 1). One-time release of C.<br />

lividipennis was insufficient to suppress the density of thirdgeneration<br />

N. lugens (Fig. 1C). However, an additional release<br />

of C. lividipennis at the second generation (early August) successfully<br />

regulated the mean population density of the thirdgeneration<br />

N. lugens to 13.6–36.1 individuals per hill (1.13–<br />

1.56 in log scale), which is lower than the density at which<br />

“hopper-burn” damage occurs (Fig. 1C).<br />

Stepwise multiregression analysis revealed that the most<br />

important factor decreasing the population growth rate from<br />

the initial to the first generation of N. lugens was the density<br />

of released C. lividipennis (P


population increase of C. lividipennis depends on S. furcifera<br />

early in the season and on N. lugens later in the season.<br />

Our field experiment suggests that the augmentative release<br />

of C. lividipennis is highly promising for regulating N.<br />

lugens density to levels low enough to prevent “hopper-burn”<br />

damage in open paddy fields. To further enhance the effect of<br />

the released natural enemy, additional techniques such as a<br />

banker plant system (Van Lenteren 1995) should be worthwhile<br />

to evaluate. For open rice fields, eggs of the delphacid<br />

planthopper Sogatella vibix (Haupt) (a nonpest species of rice<br />

plants) found on the Japanese barnyard millet Echinochloa<br />

utilis Ohwi et Yabuno could serve as a noncrop plant reservoir<br />

for food and reproduction of C. lividipennis. The evaluation<br />

of this system is now in progress (Matsumura M and Urano S,<br />

unpublished data).<br />

References<br />

Cariño FO, Kenmore PE, Dyck VA. 1979. The FARMCOP suction<br />

sampler for hoppers and predators in flooded rice fields. Int.<br />

<strong>Rice</strong> Res. Newsl. 4(5):21-22.<br />

Chiu SC. 1979. Biological control of the brown planthopper. In:<br />

Brown planthopper: threat to rice production in Asia. Los<br />

Baños (Philippines): <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>.<br />

p 335-355.<br />

Kuno E. 1968. Studies on the population dynamics of rice leafhoppers<br />

in a paddy field. Bull. Kyushu Agric. Exp. Stn. 14:131-<br />

246.<br />

Matsumura M, Suzuki Y. 1999. Effects of prey species and honeydew<br />

feeding on development and reproduction of the mirid<br />

bug, Cyrtorhinus lividipennis Reuter (Heteroptera: Miridae).<br />

Proc. Assoc. Plant Prot. Kyushu 45:63-67.<br />

Matsumura M, Suzuki Y. 2003. Direct and feeding-induced interactions<br />

between two rice planthoppers, Sogatella furcifera and<br />

Nilaparvata lugens: effects on dispersal capability and performance.<br />

Ecol. Entomol. 28:174-182.<br />

Suzuki Y, Tanaka K. 1996. Reproductive traits of Cyrtorhinus<br />

lividipennis Reuter. Proc. Assoc. Plant Prot. Kyushu 42:69-<br />

72.<br />

Teramoto T, Nakasuga T, Yokomizo K. 1996. Seasonal prevalence<br />

of occurrence of the brown planthopper, Nilaparvata lugens,<br />

and predacious mirid bug, Cyrtorhinus lividipennis, in<br />

Nagasaki, Japan. In: Hokyo N, Norton GA, editors. Pest management<br />

strategies in Asian monsoon agroecosystems.<br />

Kumamoto (Japan): Kyushu National Agricultural Experiment<br />

Station. p 55-62.<br />

Van Driesche RG, Bellows TS Jr. 1996. Biological control. New York<br />

(USA): Chapman & Hall. 539 p.<br />

Van Lenteren JC. 1995. Integrated pest management in protected<br />

crops. In: Dent D, editor. Integrated peat management. London<br />

(UK): Chapman & Hall. p 533-537.<br />

Yamamura K. 1999. Key-factor/key-stage analysis for life table data.<br />

Ecology 80:533-537.<br />

Notes<br />

Authors’ addresses: Masaya Matsumura and Satoru Urano, National<br />

Agricultural <strong>Research</strong> Center for Kyushu Okinawa Region,<br />

Nishigoshi, Kumamoto 861-1102, Japan; Yoshito Suzuki,<br />

National Agricultural <strong>Research</strong> Center, Tsukuba, Ibaraki 3005-<br />

8666, Japan.<br />

Developing a rice production system<br />

for sustainable pest management<br />

T.W. Mew<br />

The development and cultivation of shorter-duration and agronomically<br />

well-adapted varieties has fed half of the world’s<br />

total population of about six billion people, mostly in Asia.<br />

This not only allowed intensification of the rice crop in time<br />

and space, which reduced the demand for land to grow it to<br />

meet this population pressure, but it also accounts for 30% to<br />

50% of agricultural production and 50–90% of the calories<br />

consumed by these people (Hossain and Fischer 1995). While<br />

t<strong>here</strong> is a need to achieve greater rice productivity, intensification<br />

also makes the rice crop more vulnerable to attack by rice<br />

pests and diseases (Mew et al 2004).<br />

Pests and diseases are a moving target. Genetic elasticity<br />

allows them to readjust their population to adapt to new<br />

environments and on new resistant varieties bred by plant<br />

breeders. It is not uncommon that the scenario of pest and disease<br />

profiles shifts as production systems change. Accompa-<br />

nying this intensification is the use of genetically uniform varieties<br />

that reduce the buffering capacity in the rice-cropping<br />

system. This situation creates some concerns regarding modern<br />

rice production in relation to pest outbreaks. Below, we<br />

outline some of these concerns and propose that scientists<br />

working on pest management should consider sustainable rice<br />

production systems as a means to manage pests and diseases<br />

as an important option for another doubly green revolution in<br />

agriculture.<br />

The first concern is the deployment of a few high-yielding<br />

varieties over large areas, leading to a decline in cultivar<br />

diversity. The general landscape of rice production in intensive<br />

rice ecosystems is characterized as a monoculture system.<br />

A reduction in cultivar diversity is a concern of rice intensification<br />

because maintaining adequate diversity and resilience<br />

is important in the humid tropics of Asia, w<strong>here</strong> pressure<br />

Session 16: Pest management with minimal environmental stress 475


of diseases and pests is unusually high. Current disease and<br />

pest management systems rely primarily on new resistant varieties<br />

and/or the application of pesticides. Dependence on varietal<br />

resistance often results in a “boom-and-bust” cycle because<br />

of pathogen adaptation on the widely grown few resistant<br />

varieties. The continuous cultivation of these modern varieties<br />

also replaces some of the popular traditional cultivars.<br />

While this is a true concern, still, the reality is to achieve the<br />

current level of rice production. Thus, it is not feasible and<br />

practical to plant low-yielding but diverse traditional varieties.<br />

The challenge that rice scientists, especially those involved<br />

in pest management, face is how to increase the rice<br />

supply or retain the high level of productivity of modern cultivars<br />

to feed a growing population with reduced arable land<br />

area and increased scarcity of natural resources on the one<br />

hand, and maintain cultivar diversity so as to minimize losses<br />

from disease and pest outbreaks on the other. In rice production,<br />

however, host-plant resistance is a key to sustaining rice<br />

productivity in the long term. To sustain the useful life of the<br />

resistance, resistance deployment as part of gene management<br />

should be considered an important option (Wolfe 1985). Although<br />

resistance deployment has its own limitations, it is an<br />

attractive option to reduce pest outbreaks and disease epidemics<br />

frequently caused by blast, tungro, and other diseases in<br />

the tropics. Genetic diversity would provide complementary<br />

disease resistance and other positive agronomic functions, such<br />

as resistance to lodging, good grain quality, and others. It is<br />

also efficient in R-gene use and management. It would reduce<br />

the selection pressure on pathogens and slow down pathogen<br />

evolution. The deployment of modern high-yielding and traditional<br />

high-quality varieties together, that is, if the match is<br />

feasible, would increase the productivity of rice land and farmers’<br />

income, reduce pesticide use, and thus protect rice production<br />

environments. Such a system would also harmonize<br />

the production of modern and traditional varieties, and offer a<br />

means of in situ landrace conservation. This has been demonstrated<br />

in Yunnan, China, using interplanting of modern highyielding<br />

hybrids with traditional glutinous rice with high grain<br />

quality (Zhu et al 2000).<br />

The second concern is the increase in input use to match<br />

the intensification. Farmers use more fertilizer and also more<br />

pesticides. The consequence of this practice is related to environmental<br />

deterioration and an increase in production cost.<br />

This situation suggests that rice production is subject to increasing<br />

environmental constraints. Many issues are related to<br />

natural resource management leading to potential sustainable<br />

crop production practices. In tropical Asia, however, the health<br />

base of the poor-quality farmer-saved seed for planting has<br />

been neglected despite the fact that seed base technology is<br />

the key to increasing crop production. Recent surveys indicated<br />

that t<strong>here</strong> have been extensive losses of rice yield and<br />

grain quality because of the low-quality seed used for planting<br />

by farmers.<br />

Farmers in general lack the knowledge and awareness<br />

of planting high-quality seed for crop production, which could<br />

be an important means of pest management for sustainable rice<br />

production. The widely popularized integrated pest management<br />

for years has appeared to focus on the crop in fields.<br />

Now<strong>here</strong> else in the practice of farmers’ seed health management<br />

has it been taken into account. Yet, poor-quality seed for<br />

planting is responsible for at least a 10% crop loss based on<br />

the work done in Bangladesh in a project on “Seed Health<br />

Improvement” supported by DFID (Department for <strong>International</strong><br />

Development, UK) (T.W. Mew, Taher Mia, and Mahabub<br />

Hossain, unpublished results). The research suggested that<br />

farmers could gain 10% in crop yield if high-quality seed were<br />

used for planting (Mew and Cottyn 2001). We need to realize<br />

that poor-quality seed for planting also reduces the genetic<br />

potential of modern rice varieties. Planting high-quality seed<br />

is also a means of disease management because seed carries<br />

more than 80% of the rice pathogens. In any given seed lot,<br />

rice seeds carry several pathogens in various degrees of intensity.<br />

It is difficult to demonstrate the impact on crop production<br />

by managing individual pathogens carried by seed. By<br />

applying the seed health concept, that is, if healthy seed is<br />

used for planting to manage seedborne pathogens, the diseases<br />

derived from the seedborne inoculum could be greatly minimized.<br />

T<strong>here</strong>fore, this is a system of sustainable crop production<br />

and pest management. It reduces the production cost by<br />

lowering the seeding rate and cost of weed and insect pest<br />

management in the field.<br />

The third concern relates to soil health, an area that has<br />

been widely studied. In this paper, we shall not discuss issues<br />

of soil health. It is likely that, if we achieve the above, we shall<br />

achieve health of the ecosystem. A rice production system that<br />

takes into account genetic or cultivar diversity and seed health<br />

for planting, then coupled with soil health, would sustain rice<br />

production and pest management.<br />

References<br />

Hossain M, Fischer K. 1995. <strong>Rice</strong> research for food security and<br />

sustainable agricultural development in Asia: achievements<br />

and future challenges. GeoJournal 35:286-298.<br />

Mew TW, Leung H, Savary S, Vera Cruz CM, Leach JE. 2004. Looking<br />

ahead in rice disease research and management. Crit. Rev.<br />

Plant Sci. 23(2):103-127.<br />

Wolfe MS. 1985. The current status and prospects of multiline cultivars<br />

and variety mixtures for disease resistance. Annu. Rev.<br />

Phytopathol. 23:251-273.<br />

Zhu Y, Chen H, Fan J, Wang Y, Li Y, Chen J, Fan JX, Yang S, Hu L,<br />

Leung H, Mew TW, Teng PS, Wang Z, Mundt CC. 2000. Genetic<br />

diversity and disease control in rice. Nature 406:718-<br />

722.<br />

Notes<br />

Author’s address: <strong>IRRI</strong>, DAPO Box 7777, Metro Manila, Philippines,<br />

e-mail: t.mew@cgiar.org.<br />

476 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Evaluation of a leaf blast simulation model (BLASTMUL)<br />

for rice multilines in different locations and cultivars,<br />

and effective blast control using the model<br />

T. Ashizawa, M. Sasahara, A. Ohba, T. Hori, K. Ishikawa, Y. Sasaki, T. Kuroda, R. Harasawa, K.S. Zenbayashi, and S. Koizumi<br />

Blast, caused by Pyricularia grisea (Cooke) Sacc., is one of<br />

the most devastating diseases of rice in Japan. However, levels<br />

of field resistance to the disease in most Japanese rice cultivars<br />

are relatively low because the cultivars have been developed<br />

to mainly improve eating quality in compensation for<br />

loss of the resistance. For this reason, blasticides have been<br />

used frequently to control the disease, but Japanese farmers<br />

meet the demand for fewer applications of chemicals because<br />

of food safety and environmental consciousness. To solve this<br />

dilemma, multilines, which are mixtures of near-isogenic lines<br />

(NILs) with different complete resistance to blast, have been<br />

released in Japan. Sasanishiki multiline (named Sasanishiki<br />

BL, currently mixed with Pik, Pik-m, Piz, and Piz-t lines in the<br />

proportion of 1:1:4:4) has been cultivated in Miyagi Prefecture<br />

since 1995. In Toyama Prefecture, Koshihikari multiline<br />

(Koshihikari Toyama BL), consisting of Piz-t, Pib, and Pik-p<br />

lines in the proportion of 4:4:2, has been cultivated since 2002.<br />

Moreover, Niigata Prefecture is planning to cultivate another<br />

Koshihikari multiline (Koshihikari Niigata BL) on about 90,000<br />

ha in the prefecture beginning in 2005. For effective blast control<br />

with multilines, we need to estimate the extent of blast<br />

suppression using them. However, it is difficult to overcome<br />

the limitations of field trials. The simulation approach can provide<br />

an opportunity to clarify the extent of disease suppression<br />

using multilines.<br />

A simulator of plant disease foci and epidemics in cultivar<br />

or NIL mixtures, EPIMUL, was developed by Kampmeijer<br />

and Zadoks (1977). EPIMUL can simulate spatial disease<br />

progress in mixtures, and was used for forecasting rust epidemics<br />

in mixtures at early stages of disease epidemics. However,<br />

no simulation model has been developed for rice<br />

multilines. Among simulation models for rice blast epidemics,<br />

BLASTL developed by Hashimoto et al (1986) is one of the<br />

most reliable simulators. Hence, we modified BLASTL and<br />

developed a multiline simulation model called BLASTMUL.<br />

BLASTMUL was developed based on the results of field trials<br />

using rice cultivar Sasanishiki and its NILs at the National<br />

Agricultural <strong>Research</strong> Center for Tohoku Region (NARCT)<br />

from 1998 to 2001. However, its usefulness has not been validated<br />

yet in different locations and multilines.<br />

The objective of this study is to evaluate the applicability<br />

of the model in different locations and multilines for effective<br />

control of leaf blast using the multiline approach.<br />

The model<br />

BLASTMUL is developed by modifying BLASTL. In<br />

BLASTMUL, a new parameter of spore dispersion and deposition<br />

between two hills of NILs is set (Ashizawa et al 2001).<br />

Our model calculates the number of lesions per hill in a mixture<br />

of susceptible and resistant NILs in a given proportion<br />

under various weather conditions.<br />

Field trials in Miyagi Prefecture<br />

To evaluate the appropriateness of BLASTMUL in different<br />

locations, we conducted paddy field trials at the Furukawa Agricultural<br />

Experiment Station in Miyagi Prefecture from 2000<br />

to 2001. The seeds of Sasanishiki and Sasanishiki BL No. 4<br />

were mixed uniformly in the proportions of 1:0 and 1:1. The<br />

mixed seeds were sown in upland nurseries and then transplanted<br />

by machine in 10 × 10-m paddy-field plots at a distance<br />

of 30 × 15 cm on 19 May 2000 and 15 May 2001. These<br />

experiments were arranged in a randomized block design with<br />

two replications. As inoculum sources, diseased seedlings of<br />

Sasanishiki inoculated with the blast isolate Ina86-137 (Japanese<br />

race 007.0, virulent to Sasanishiki, avirulent to Sasanishiki<br />

BL No. 4) were placed in each plot on 23 June 2000 and 20<br />

June 2001. Lesions more than 5 mm in size per hill were<br />

counted at 6- to 7-day intervals from the start till the end of<br />

leaf blast epidemics. Meteorological data were recorded beside<br />

the fields using a weather sensor system.<br />

Field trials in Niigata Prefecture<br />

We also conducted paddy-field trials under natural blast epidemic<br />

conditions at Ojiya in Niigata Prefecture from 2002 to<br />

2003. Mixed seeds of rice cultivar Koshihikari and its Pita<br />

line, whose mixture proportions were 1:0, 1:1, and 1:3, were<br />

sown and then four seedlings per hill were transplanted by<br />

hand at a distance of 30 × 18 cm in 4.2 × 5.3-m paddy-field<br />

plots on 20 May 2002 and 22 May 2003. These trials were<br />

arranged in a randomized block design with three replications.<br />

Koshihikari and the Pita line are susceptible and resistant, respectively,<br />

to the predominant Japanese races distributed in<br />

the fields. The disease assessment was as described earlier.<br />

Meteorological data were recorded using a dew sensor and a<br />

weather sensor system (AMeDAS) located at Tokamachi, close<br />

to Ojiya.<br />

Session 16: Pest management with minimal environmental stress 477


Number of lesions per hill<br />

35<br />

30<br />

25<br />

20<br />

Sim. S:R (1:0) in 2000<br />

Sim. S:R (1:1) in 2000<br />

Obs. S:R (1:0) in 2000<br />

Obs. S:R (1:1) in 2000<br />

Sim. S:R (1:0) in 2001<br />

Sim. S:R (1:1) in 2001<br />

Obs. S:R (1:0) in 2001<br />

Obs. S:R (1:1) in 2001<br />

Number of lesions per hill<br />

30<br />

25<br />

20<br />

15<br />

Sim. S:R (1:0) in 2002<br />

Sim. S:R (1:1) in 2002<br />

Sim. S:R (1:3) in 2002<br />

Obs. S:R (1:0) in 2002<br />

Obs. S:R (1:1) in 2002<br />

Obs. S:R (1:3) in 2002<br />

A<br />

15<br />

10<br />

10<br />

5<br />

5<br />

0<br />

0<br />

25 30 35 40 45 50 55<br />

Days from 1 June<br />

Fig. 1. Observed (Obs.) and simulated (Sim.) development of rice<br />

leaf blast in a mixture of susceptible (S) cv. Sasanishiki and its<br />

resistant (R) near-isogenic line, Sasanishiki BL No. 4, at proportions<br />

of 1:0 and 1:1 from 2000 to 2001. The field experiments<br />

were performed at the Furukawa Agricultural Experiment Station<br />

in Miyagi Prefecture.<br />

10<br />

8<br />

6<br />

Sim. S:R (1:0) in 2003<br />

Sim. S:R (1:1) in 2003<br />

Sim. S:R (1:3) in 2003<br />

Obs. S:R (1:0) in 2003<br />

Obs. S:R (1:1) in 2003<br />

Obs. S:R (1:3) in 2003<br />

Results<br />

4<br />

In Miyagi Prefecture, leaf blast lesions were first observed on<br />

11 July 2000 and 7 July 2001. The numbers of lesions per hill<br />

on 27 July 2000 and 23 July 2001 were 0.29 and 32 in the pure<br />

stands of Sasanishiki and 0.02 and 13 in the 1:1 mixture of<br />

Sasanishiki and Sasanishiki BL No. 4, respectively. In contrast,<br />

simulated numbers of lesions with BLASTMUL on 27<br />

July 2000 and 23 July 2001 were 0.4 and 32 in the pure stands<br />

of Sasanishiki and 0.05 and 7 in the 1:1 mixture of Sasanishiki<br />

and Sasanishiki BL No. 4 (Fig. 1).<br />

In Niigata Prefecture, leaf blast lesions were first observed<br />

on 3 July 2002 and 3 July 2003. The numbers of lesions<br />

on 24 July 2002 and 24 July 2003 were 27 and 8 in the<br />

pure stands of Koshihikari, 6 and 3 in the 1:1 mixture of<br />

Koshihikari and its Pita line, and 2 and 0.6 in the 1:3 mixture,<br />

respectively. Meanwhile, the simulated numbers of lesions on<br />

24 July 2002 and 24 July 2003 were 24 and 8 in the pure stands<br />

of Koshihikari, 5 and 2 in the 1:1 mixture of Koshihikari and<br />

its Pita line, and 0.8 and 0.6 in the 1:3 mixture of them (Figs.<br />

2A and B).<br />

Discussion<br />

Visual comparisons between the observed and simulated values<br />

were made subjectively in this study. Although the numbers<br />

of observed lesions in the mixture trials in Miyagi Prefecture<br />

were slightly larger than those of the ones observed in<br />

2000, the simulated numbers of lesions were similar to the<br />

2<br />

0<br />

25 30 35 40 45 50<br />

Days from 1 June<br />

Fig. 2. Observed (Obs.) and simulated (Sim.) development of rice<br />

leaf blast in mixtures of susceptible (S) cv. Koshihikari and its<br />

resistant (R) near-isogenic line, the Pita line, at proportions of<br />

1:0, 1:1, and 1:3 from 2002 (A) to 2003 (B). The field experiments<br />

were performed at Ojiya in Niigata Prefecture.<br />

observed ones. In 2001, the simulated numbers of lesions were<br />

slightly smaller than those observed in the 1:1 mixture. However,<br />

the simulation results in the 1:0 mixture were as expected<br />

for the year. Although the simulated numbers of lesions in our<br />

trial at Niigata were slightly smaller than the data observed in<br />

the 1:0 mixture, the simulation results in the 1:1 and 1:3 mixtures<br />

agreed well with the observed ones in 2002. These results<br />

suggest that the model is appropriate for evaluating rice<br />

mixtures for blast control in different locations and cultivars.<br />

Recently, we modified the model again to simulate leaf<br />

blast lesion development in a mixture of four NILs for four<br />

blast races. The modified BLASTMUL will contribute to evaluating<br />

the efficacy of the increased number of mixtures under<br />

various conditions, including an increase in disease pressure.<br />

In addition, the weather data have been recorded at NARCT<br />

478 <strong>Rice</strong> is life: scientific perspectives for the 21st century


for four years, in Miyagi Prefecture for two years, and in Niigata<br />

Prefecture for two years. These data will also contribute to<br />

developing a more accurate model.<br />

The 11 genes with complete resistance to blast (Pik-s,<br />

Pia, Pii, Pik, Pik-m, Piz, Pita, Pita-2, Piz-t, Pik-p, and Pib)<br />

mainly exist in Japanese rice cultivars. However, most of the<br />

Japanese cultivars possess Pik-s, Pia, or Pii, which are ineffective<br />

against the predominant Japanese blast races 001.0,<br />

003.0, and 007.0. For this reason, t<strong>here</strong> are now eight complete<br />

resistance genes available for blast control.<br />

We are currently clarifying the effect of increasing the<br />

number of NILs in multilines on the efficacy of rice blast control<br />

using BLASTMUL. However, as noted earlier, available<br />

complete resistance genes are limited. Hence, we have to incorporate<br />

new resistance genes from foreign countries into the<br />

NILs for blast control using the multiline approach.<br />

References<br />

Ashizawa T, Zenbayashi K, Koizumi S. 2001. Development of a<br />

simulation model for forecasting rice leaf blast epidemics in<br />

multilines Jpn. J. Phytopathol. 67:194. (Abstr., in Japanese.)<br />

Hashimoto A, Hirano K, Matsumoto K. 1984. Studies on the forecasting<br />

of rice leaf blast development by application of the<br />

computer simulation SP. Bull. Fukushima Pref. Exp. Stn. 2:1-<br />

104. (In Japanese, English summary.)<br />

Kampmeijer P, Zadoks JC. 1977. EPIMUL, a simulator of foci and<br />

epidemics in mixtures of resistant and susceptible plants,<br />

mosaics, and multilines. Wageningen (Netherlands): Centre<br />

for Agricultural Publishing and Documentation. 50 p.<br />

Notes<br />

Authors’ addresses: T. Ashizawa, K.S. Zenbayashi, and S. Koizumi,<br />

National Agricultural <strong>Research</strong> Center for Tohoku Region, 3<br />

Yotsuya, Omagari, Akita 014-0102, Japan; M. Sasahara and<br />

A. Ohba, Miyagi Prefectural Furukawa Agricultural Experiment<br />

Station, 88 Fukoku, Osaki, Furukawa, Miyagi 989-6227,<br />

Japan; T. Hori, K. Ishikawa, Y. Sasaki, T. Kuroda, and R.<br />

Harasawa, Niigata Agricultural <strong>Research</strong> <strong>Institute</strong>, 857<br />

Nagakura, Nagaoka, Niigata 940-0826, Japan, e-mail:<br />

toketa@affrc.go.jp.<br />

Association of candidate defense genes<br />

with quantitative resistance to rice blast<br />

and in silico analysis of their characteristics<br />

G. Carrillo, J. Wu, B. Liu, N. Sugiyama, I. Oña, M. Variar, B. Courtois, J.E. Leach, P.H. Goodwin, H. Leung, and C.M. Vera Cruz<br />

Many traits of significance in agriculture exhibit quantitative<br />

inheritance. To characterize these quantitative traits, the candidate<br />

gene approach has been applied in several cereal crops<br />

such as maize, wheat, and rice because of the detection of<br />

multiple genes defining a complex trait, their partial effects on<br />

phenotypic variation, and their less precise localization on<br />

genetic maps in comparison with traits conferring qualitative<br />

inheritance (Pflieger et al 2001, Wilson et al 2004).<br />

The availability of the whole rice genome sequence from<br />

public and private sequencing efforts has provided opportunities<br />

to predict putative functions of a gene based on sequence<br />

information, thus allowing the identification of candidate genes.<br />

Candidate genes are DNA sequences similar to known genes<br />

or conserved motifs that make it possible to infer their biological<br />

functions. Through their association with disease resistance,<br />

they become candidate defense-response (DR) genes<br />

for conferring particular phenotypes. Using the candidate gene<br />

approach, we studied the associations between candidate gene<br />

markers with disease and insect resistance in a doubled-haploid<br />

rice mapping population (Ramalingam et al 2002). This<br />

frame map has been a useful reference for selecting candidate<br />

genes involved in both pathogen recognition and general plant<br />

defense for analysis of mapping populations for improving<br />

resistance to rice blast.<br />

With the sequencing of many genomes in recent years<br />

along with the genetic and bioinformatic resources for rice,<br />

our ability to comprehensively characterize multigene families<br />

has also been greatly enhanced. These resources include<br />

the physical, linkage, and expressed sequence tag (EST) maps,<br />

a collection of >130,000 ESTs, gene prediction algorithms and<br />

automatic genome annotation systems, and online resources<br />

for comparative grass genomics. Through these resources, we<br />

examined DR genes retrieved from the <strong>Rice</strong> Genome Program<br />

database using in silico analysis.<br />

Identifying candidate genes by association<br />

with blast quantitative resistance<br />

A japonica cultivar, Moroberekan from Africa, known to exhibit<br />

durable resistance to rice blast in Asia was crossed to a<br />

popular upland cultivar, Vandana, following the advanced backcross<br />

QTL approach. This approach allows QTL analysis of<br />

the mapping population while simultaneously developing elite<br />

germplasm for commercial use (Tanksley and Nelson 1996).<br />

Eighty BC 3 F 3 and BC 3 F 4 lines derived from advanced back-<br />

Session 16: Pest management with minimal environmental stress 479


cross populations of Vandana/Moroberekan were analyzed for<br />

seedling (BC 3 F 3 ) and neck blast resistance in the greenhouse<br />

and blast nursery at <strong>IRRI</strong> and screening sites in India. A collection<br />

of 25 microsatellite markers, resistance gene analog<br />

(RGA) primers, and 51 candidate resistance genes were used<br />

for genotypic analysis of the lines. Six candidate gene markers,<br />

NBS-LRR (Pic19), Rp1 (a maize rust resistance gene),<br />

NBS (7-4F), PR5 (thaumatin), RGA 1-8 (resistance gene analog,<br />

LRR), and RGA6-7 (resistance gene analog, Kinase), and<br />

one simple sequence repeat (SSR) marker (RM21) were significantly<br />

associated with quantitative blast resistance in rice<br />

(P = 0.01). When tested against a single isolate, PO6-6, four<br />

candidate genes (oxalate oxidase, 14-3-3, RGA8-4, and RGA1-<br />

10) and four SSR markers (RM21, RM168, RM215, and<br />

RM250) were associated with resistance to this single isolate.<br />

Of these markers, two were associated with resistance involved<br />

in a reduction in diseased leaf area (DLA), five with reduced<br />

lesion number, and one with reduced lesion size. These markers<br />

accounted for observed phenotypic variation ranging from<br />

9.1% to 28.7%. Seedling reactions in the blast nursery and<br />

greenhouse tests in the Philippines were highly correlated. Field<br />

tests of BC 3 F 3 and BC 3 F 4 lines in India across screening sites<br />

identified six lines showing < 5% DLA and 13 lines showing<br />

quantitative resistance; however, only two (V4M-6-1-B and<br />

V4M-5-3-B) of these quantitatively resistant lines have good<br />

agronomic acceptability with a varying level of neck blast resistance.<br />

Other than Vandana/Moroberekan mapping populations,<br />

others such as TXZ/SHZ2 (Liu et al 2004), Oryzica Llanos<br />

5/Way Rarem (M. Bustamam, pers. comm.), and<br />

Ilpumbyeo/Moroberekan (S.S. Han, pers. comm.) are used to<br />

determine the association of candidate defense genes with quantitative<br />

resistance to blast.<br />

Accumulating different mechanisms<br />

of quantitative blast resistance<br />

To accumulate different mechanisms involved in quantitative<br />

resistance to blast, 15 BC 3 F 3 or BC 3 F 4 parental lines derived<br />

from Vandana/Moroberekan showing partial resistance and<br />

carrying positive candidate alleles were selected and crossed<br />

in all pairwise combinations. Cluster analysis of DNA profiles<br />

showed that the BC 3 population was genetically similar (>85%)<br />

to the recurrent parent Vandana (Wu et al 2004). Seeds of 10<br />

F 2 families were selected based on partial resistance of the<br />

BC 3 F 3 or BC 3 F 4 parental lines to seedling blast and neck blast,<br />

association of the parental lines with positive alleles, and phenotypic<br />

similarity to Vandana. Among the 10 F 2 families, 14<br />

F 2 plants showed a good to moderate level of agronomic acceptability<br />

and high level of seedling blast resistance (0.75–<br />

3.2% DLA). Resistant lines from selected families were advanced<br />

to F 3 until F 5 . At F 4 , the top 10% of the lines (60 out of<br />

>600 lines) derived from the progenies of VM5/VM14, VM6/<br />

VM14, and VM82/VM14 had acceptable agronomic traits, and<br />

served as a basis for further selection and advancement to F 5 .<br />

The field performance of these advanced BC lines indicated<br />

that the major QTLs have been captured in the BC lines. In<br />

this study, only a small proportion of alleles were from<br />

Moroberekan. It is possible that the loci contributing to disease<br />

resistance may not be polymorphic, thus precluding their<br />

use as informative markers.<br />

To identify informative markers for analysis of F 4<br />

intermated lines of BC 3 F 5 Vandana/Moroberekan populations,<br />

sequence tagged site (STS) markers derived from rice candidate<br />

gene sequences and SSR markers located in the region of<br />

each candidate gene were identified using TIGR and Gramene<br />

databases (www.gramene.org). Thirty SSRs gave polymorphic<br />

fragments between Vandana and Moroberekan. Of 11 DR genes<br />

(oxalate oxidase, oxalate oxidase-like proteins, aspartyl protease,<br />

14-3-3, PR-1, probenazole-induced protein, peroxidases,<br />

HSP90, thaumatin-like proteins, adenosylhomocysteinase, and<br />

aldose reductase) analyzed, polymorphic markers were obtained<br />

for oxalate oxidases, PR-1, probenazole-induced protein,<br />

and HSP90. Using 30 random SSRs dispersed in the rice<br />

genome and polymorphic candidate gene-associated markers<br />

in Vandana and Moroberekan, an initial set of F 4 resistant elite<br />

lines (7) in Cavinti, Philippines, was scanned for introgression<br />

of Moroberekan regions into Vandana and co-localization of<br />

the consensus candidate defense genes (Fig. 1A and B). Interestingly,<br />

primers derived from 1,000 bp upstream of two of<br />

the four oxalate oxidases in chromosome 3, SSRs for aspartyl<br />

protease in chromosome 7, and oxalate oxidase-like proteins<br />

in chromosome 8 co-localized with particular candidate genes<br />

in target chromosomal regions (Fig. 1B). However, only two<br />

lines, IR78221-19-6-56 and IR78222-20-7-148, which co-localized<br />

with oxalate oxidases in chromosome 3 and oxalate<br />

oxidase-like proteins in chromosome 8, were resistant to seedling<br />

and neck blast in Almora, a blast hotspot in the Indian<br />

Himalaya. Based on these results, we hypothesized that (1)<br />

highly resistant lines IR78221-19-6-56 and IR78222-20-7-148<br />

may carry combinations of several effective candidate genes<br />

under high disease pressure in Almora, and (2) the contribution<br />

of individual candidate genes conferring different mechanisms<br />

of quantitative resistance to blast has been accumulated<br />

in these lines. We are currently designing PCR primers for<br />

other consensus DR genes identified from multiple mapping,<br />

linkage, and microarray experiments to determine the combination<br />

of effective candidate defense genes in 27 intermated<br />

F 5 lines resistant in Almora.<br />

In silico analysis of selected candidate defense genes<br />

Initially, we focused on consensus DR genes for in silico analysis.<br />

Sequences were retrieved from the <strong>Rice</strong> Genome Program<br />

database (www.tigr.org/tdb/e2k1/osa1/). For genes occurring<br />

in gene families such as the germin-like proteins (GLP), we<br />

derived phylogenetic trees using the retrieved sequences. We<br />

also checked for conserved promoter motifs and identified ciselements<br />

in the 1,000-bp upstream regions using MEME (http:/<br />

/meme.sdsc.edu/) and PLACE (Plant Cis-Acting Elements,<br />

www.dna.affrc.go.jp/PLACE/).<br />

Scanning the rice genome identified more than 40 GLPs,<br />

four of which are putative oxalate oxidases in chromosome 3.<br />

480 <strong>Rice</strong> is life: scientific perspectives for the 21st century


A<br />

0<br />

25<br />

50<br />

75<br />

100<br />

rm61a 9.3<br />

rm569 11.0<br />

rm545 24.7<br />

rm157a 44.1<br />

rm7 64.0<br />

Putative<br />

oxalate<br />

oxidases<br />

0<br />

Eukaryotic<br />

aspartyl<br />

25 protease<br />

rm2 36.1<br />

rm214 49.7<br />

50<br />

rm336 61.0<br />

rm10 63.5<br />

rm6011 73.2<br />

75<br />

rm1279 75.6<br />

0<br />

rm38 16.4<br />

25<br />

rm310 38.5<br />

rm6208 42.9<br />

50<br />

rm3215 49.5<br />

rm547 58.1<br />

rm137 69.0<br />

75<br />

Oxalate<br />

oxidase-like<br />

proteins<br />

125<br />

0<br />

rm473d 113.2<br />

rm426 122.3<br />

rm168 122.8<br />

rm186 127.4<br />

rm411 127.9<br />

rm148 140.7<br />

1 3 5<br />

2 4 6<br />

7<br />

8<br />

100<br />

9<br />

rm5720 115.2.6<br />

rm248 118.0<br />

1 3 5<br />

2 4 6<br />

7 9<br />

8<br />

100 rm80 103.7<br />

rm281 119.9<br />

1 3 5<br />

2 4 6<br />

7 9<br />

8<br />

Chromosome 8<br />

Chromosome 8<br />

Chromosome 8<br />

B<br />

100<br />

rm473 113.2<br />

rm426 122.3<br />

125rm168 122.8<br />

rm186 127.4<br />

rm411 127.9<br />

rm148 140.7<br />

1 2 3 4 5 6 7 8 9<br />

rm426<br />

osglp10up<br />

osglp10<br />

osglp11up<br />

osglp11<br />

osglp12<br />

osglp13up<br />

osglp13<br />

rm168<br />

1 2 3 4 5 6 7 8 9<br />

Fig. 1. (A) Genome scan of Vandana/Moroberekan intercross progenies using SSRs, 1: Moroberekan; 2: Vandana;<br />

3–7: more resistant lines; 8–9: less resistant lines. Examples of candidate genes associated with each of the<br />

critical areas marked: putative oxalate oxidases in chr. 3, putative aspartyl protease in chr. 7, and oxalate oxidaselike<br />

proteins in chr. 8. Heterozygous loci are colored green. Because of selection in BC 3 F 3 prior to intermating, our<br />

susceptible lines in fact carry some degree of quantitative resistance. T<strong>here</strong>fore, Vandana is still the susceptible<br />

control in this analysis. (B) Detailed marker analysis of chr. 3 loci identified with 4 putative oxalate oxidases on 1:<br />

Moroberekan; 2: Vandana; 3–7: more resistant lines; 8–9: less resistant lines. PCR primers used were designed<br />

from the coding region of each gene. Primers were also designed in the 1,000-bp upstream region of each gene<br />

(OsGLP10UP, OsGLP11UP, and OsGLP13UP). Heterozygous loci are colored green. Monomorphic markers are colored<br />

light blue.<br />

These oxalate oxidase gene sequences are located next to each<br />

other, with similarities ranging from 90% to 98%. For each<br />

gene, t<strong>here</strong> was variation in the copy number of cis-elements<br />

related to biotic stress responses, such as W box, WNPR1,<br />

and WRKY, indicating that these genes have potential associations<br />

with the response of rice to pathogen infection, such<br />

as the blast fungus.<br />

Phylogenetic analyses clustered chromosome 3 oxalate<br />

oxidases with barley oxalate oxidase Y14203. Several GLP<br />

sequences in chromosome 8 were similar in conserved domain<br />

structure to barley oxalate oxidase-like protein X93171. These<br />

genes are thought to play a role in defense response by degradation<br />

of oxalate produced by fungi, the production of active<br />

oxygen species for oxidative cross-linking of cell wall components,<br />

and stress signaling by increasing extracellular<br />

[Ca + ion] (Dunwell et al 2000).<br />

Another class of DR genes is the thaumatin-like proteins<br />

or PR5 proteins. At <strong>IRRI</strong>, overexpression of PR5 delays the<br />

onset of disease symptoms of sheath blight in transgenic rice.<br />

A scan of the rice genome revealed at least 20 thaumatin-like<br />

proteins dispersed in all chromosomes except chromosome 5.<br />

Of these, thaumatin-like sequences in chromosomes 6 and 7<br />

have been mapped to IR64/Azucena doubled-haploid lines<br />

(Ramalingam et al 2003). Analysis of the 1,000-bp upstream<br />

of each gene reveals that the number of copies of cis-elements<br />

such as WRKY, WBOX, and GCC core varies from one gene<br />

to the next. PR5 proteins in barley were found to bind to<br />

β-1,3-glucans from yeasts and fungi (Trudel et al 1998). In<br />

Vandana/Moroberekan, thaumatin was significantly associated<br />

with partial blast resistance (Wu et al 2004).<br />

Future prospects<br />

The availability of rice genetic and bioinformatic resources<br />

has clearly overcome the limitations for relating QTLs to candidate<br />

genes and metabolic pathways. To improve efficiency<br />

in the selection and pyramiding of desirable plant traits, markerassisted<br />

selection may now allow candidate defense genes with<br />

Session 16: Pest management with minimal environmental stress 481


quantitative effects to be combined efficiently. The level of<br />

quantitative resistance can be estimated based on the presence<br />

of markers associated with candidate defense genes or QTLs<br />

in a plant/line. To contribute to the practicality of this approach,<br />

we continue to investigate the genetic behavior of the QTLs in<br />

different genetic backgrounds and find consensus candidate<br />

genes. We also continue to develop markers derived from consensus<br />

candidate defense genes conferring partial resistance<br />

instead of just close linkage to resistance genes, and develop<br />

efficient and economical breeding procedures using molecular<br />

genotyping. Our research has t<strong>here</strong>fore focused on these<br />

areas aimed at facilitating the selection of cultivars with broadspectrum<br />

resistance against blast pathogen populations in diverse<br />

rice-growing environments.<br />

References<br />

Dunwell JM, Khuri S, Gane PJ. 2000. Microbial relatives of the<br />

seed storage proteins of higher plants: conservation of structure<br />

and diversification of function during evolution of the<br />

cupin superfamily. Microbiol. Mol. Biol. Rev. 64:153-179.<br />

Liu B, Zhang S, Zhu X, Yang Q, Wu S, Mei M, Mauleon R, Leach J,<br />

Mew T, Leung H. 2004. Candidate defense genes as predictors<br />

of quantitative blast resistance in rice. Mol. Plant-Microbe<br />

Interact. 17:1146-1152.<br />

Pflieger S, Lefebvre V, Causse M. 2001. The candidate gene approach<br />

in plant genetics: a review. Mol. Breed. 7:275-291.<br />

Ramalingam J, Vera Cruz CM, Kukrejah K, Chittoor JM, Wu J, Lee<br />

SW, Baraoidan M, George ML, Cohen MB, Hulbert S, Leach<br />

JE, Leung H. 2002. Candidate resistance genes from rice,<br />

barley, and maize and their association with qualitative and<br />

quantitative resistance in rice. Mol. Plant-Microbe Interact.<br />

16(1):14-24.<br />

Tanksley SD, Nelson RC. 1996. Advanced backcross QTL analysis:<br />

a method for the simultaneous discovery and transfer of valuable<br />

QTLs from unadapted germplasm into elite breeding lines.<br />

Theor. Appl. Genet. 92:191-203.<br />

Trudel J, Grenier J, Potvin C, Asselin A. 1998. Several thaumatinlike<br />

proteins bind to -1,3-glucans. Plant Physiol. 118:1431-<br />

1438.<br />

Wilson LM, Whitt SR, Ibañez AM, Rocheford TR, Goodman MM,<br />

Buckler ES IV. 2004. Dissection of maize kernel composition<br />

and starch production by candidate gene association. Plant<br />

Cell Preview, www.aspb.org.<br />

Wu JL, Sinha PK, Variar M, Zheng KL, Leach JE, Courtois B, Leung<br />

H. 2004. Association between molecular markers and blast<br />

resistance in an advanced backcross population of rice. Theor.<br />

Appl. Genet. 108:1024-1032.<br />

Notes<br />

Authors’ addresses: G. Carrillo, J. Wu, B. Liu, N. Sugiyama, I. Oña,<br />

H. Leung, and C.M. Vera Cruz, <strong>IRRI</strong>, DAPO Box 7777, Metro<br />

Manila, Philippines; M. Variar, Central Rainfed Upland <strong>Rice</strong><br />

<strong>Research</strong> Station, Hazaribag 825 301, Jharkand, India; B.<br />

Courtois, CIRAD-CA, Avenue Agropolis, Montpellier Cedex<br />

5, France; J.E. Leach, Colorado State University, Fort Collins,<br />

Colo. 80523-1177, USA; P.H. Goodwin, University of Guelph,<br />

Guelph N1G 2W1, Canada.<br />

Transferring resistance genes<br />

among different cereal species<br />

Bingyu Zhao, Shavannor Smith, Jan Leach, and Scot Hulbert<br />

The transfer of genes into cereal crops from related grasses<br />

has been an important tool for improving the disease and pest<br />

resistance of some cereals. The approach to date has been limited<br />

to cereals and their close relatives because conventional<br />

genetic approaches have been used. If resistance genes could<br />

be effectively transferred among distantly related grasses in<br />

different tribes (e.g., rice, maize, and wheat), this could have a<br />

large effect on resistance breeding. Of particular relevance is<br />

the observation that a given cereal species is typically resistant<br />

to most of the pathogens that cause disease in other cereal<br />

species. If the basis of some of these nonhost resistances is<br />

due to the same types of genes that cause host resistance, we<br />

may be able to identify and transfer these genes to transfer the<br />

resistance. The contribution of typical host resistance genes to<br />

nonhost resistance is not clear, but similarities between the<br />

two types of resistance (Thordal-Christensen 2003) suggest<br />

that R genes probably play a role. One limitation of effective<br />

transfer of resistance genes is the fact that many R genes do<br />

not function in the heterologous genetic backgrounds of distantly<br />

related species (Hulbert et al 2001).<br />

Transfer of a maize resistance gene to wheat and barley<br />

The first transfer of a disease resistance gene among distantly<br />

related cereals was the maize Rp1-D gene, which was transferred<br />

to wheat and barley (Ayliffe et al 2004). Rp1-D confers<br />

resistance to common rust (Puccinia sorghi) in maize, but no<br />

rust resistance was observed in wheat or barley lines expressing<br />

the gene after inoculation with rust isolates from three different<br />

rust species. Although the Rp1-D transformation con-<br />

482 <strong>Rice</strong> is life: scientific perspectives for the 21st century


struct worked well in maize, most of the transcript appeared<br />

truncated in the other cereals. It is t<strong>here</strong>fore possible that the<br />

lack of function was due to improper expression of the gene. It<br />

is also possible that the lack of phenotype was due to the absence<br />

of the corresponding Avr gene in the other Puccinia species<br />

that attack these cereals. Experiments with other Rp1 genes,<br />

however, also failed to associate phenotypes with these genes.<br />

These experiments included one variant Rp1 gene that conditioned<br />

cell death spontaneously, without pathogen inoculation<br />

(Smith and Hulbert, unpublished). Thus, it seems that the Rp1<br />

genes will not function in these other cereals, either due to<br />

improper expression or the lack of a functional signal transduction<br />

pathway.<br />

A maize gene controls resistance to a rice pathogen<br />

It is possible to assay resistance reactions to nonhost bacterial<br />

species by infiltrating leaves of nonhost species and assessing<br />

whether a hypersensitive reaction (HR) occurs. A gene controlling<br />

a hypersensitive reaction to Xanthomonas oryzae pv.<br />

oryzicola, the rice bacterial streak pathogen, was identified in<br />

this manner in maize (Zhao et al 2004a). Although infiltration<br />

of the bacterium into maize leaves does not cause disease regardless<br />

of whether they carry the Rxo1 gene, only maize lines<br />

that carry the gene show the strong HR response. A molecular<br />

genetic analysis of the pathogen verified that the HR is under<br />

control of a classic gene-for-gene interaction. All strains of X.<br />

o. pv. oryzicola tested elicited the resistance reaction in maize<br />

lines carrying Rxo1, and a single gene was isolated from the<br />

bacterium that was responsible for the HR (Zhao et al 2004b).<br />

The avrRxo1 gene was identified by transferring a cosmid library<br />

made from X. o. pv. oryzicola into a strain of X. o. pv.<br />

oryzae that did not cause the HR when infiltrated into maize.<br />

A single cosmid clone was identified that conferred the ability<br />

to induce the HR. After testing individual genes from the cosmid<br />

in X. o. pv. oryzae, the ability to induce HR in an Rxo1-dependent<br />

manner was associated with a single gene. The avrRxo1<br />

gene encodes a novel protein that shares no homology with<br />

any known protein in public databases.<br />

Different maize lines were polymorphic for the Rxo1<br />

gene, allowing the gene to be mapped to the short arm of maize<br />

chromosome 6. An anonymous R gene-like sequence was then<br />

used as a probe to identify a gene family that cosegregated<br />

with the Rxo1 gene in several large mapping populations. The<br />

family consisted of five genes in the maize line B73 (Rxo1).<br />

Three of the five sequences were predicted to code for resistance<br />

genes, while the other two appeared truncated by<br />

retroelement-like sequences. RT-PCR experiments with primers<br />

designed to amplify all of the genes indicated that one family<br />

member was the most highly transcribed because all of 20<br />

cloned amplification products corresponded to this gene. Sequence<br />

analysis of RT-PCR products amplified with primers<br />

designed to be gene-specific verified that the other two family<br />

members predicted to code for resistance gene proteins were<br />

also transcribed, presumably at lower levels.<br />

Identification of the Rxo1 gene<br />

Several approaches were used to associate the putative resistance<br />

gene family with the Rxo1 gene and determine which, if<br />

any, of the family members confers the resistance phenotype.<br />

An RNAi silencing approach was first used to silence the family<br />

and determine whether this eliminated the resistance reaction.<br />

Transgenic HiII (Rxo1) maize lines were made that express<br />

both RNA strands of a fragment of the most highly transcribed<br />

family member. Eight of 15 transgenics carrying the<br />

RNAi construct showed little or no HR after inoculation with<br />

X. o. pv. oryzicola, indicating that silencing of the gene family<br />

silenced the Rxo1 phenotype. In addition, the lack of HR<br />

cosegregated perfectly with the transgene in progeny of one of<br />

the transgenics. The results indicated that one or more of the<br />

gene family members confers the Rxo1 phenotype.<br />

A transient transformation assay was used to examine<br />

the ability of the specific family members to interact with<br />

avrRxo1 and initiate HR. In these experiments, plasmid constructs<br />

carrying each of the potentially functional family members<br />

were separately cobombarded into Mo17 (rxo1) maize<br />

leaf cells with a plasmid expressing the avrRxo1 gene. The<br />

avrRxo1 gene was engineered for expression in plant cells by<br />

placing it between the HBT35S promoter (Sheen 1993) and<br />

the NOS terminator. The maize genes were used with their<br />

native promoters and also with the HBT35s promoter. A third<br />

plasmid, which was also included in each of the bombardment<br />

experiments, expressed the GUS gene as a reporter for cell<br />

viability. Previous experiments had indicated that transient<br />

delivery of the avrRxo1 gene into B73 maize cells expressing<br />

the native Rxo1 gene caused cell death and inhibited reporter<br />

gene expression. Delivery of the Rxo1 gene and avrRxo1 gene<br />

together would also be expected to reduce reporter gene expression<br />

if they conditioned cell death before noticeable<br />

amounts of the GUS protein were made. Only one of the gene<br />

family members noticeably reduced reporter gene expression<br />

in these experiments: the gene that was previously determined<br />

to account for most of the transcript in cDNA cloning experiments.<br />

The inhibition of reporter gene expression was nearly<br />

complete when a strong (HBT35s) promoter was used to drive<br />

the gene and only partial suppression was observed when the<br />

native promoter was used. These transient assay results indicated<br />

that the most highly transcribed family member is the<br />

functional Rxo1 gene.<br />

To verify the identity of the Rxo1 gene, stably transformed<br />

maize lines were constructed expressing the putative<br />

gene. A genomic copy of the gene with its native regulatory<br />

elements was transformed into a modified version of the maize<br />

line HiII that does not carry the Rxo1 gene. T 0 and T 1 plants<br />

expressing this gene gave HRs following inoculation with<br />

X. o. pv. oryzicola.<br />

Rxo1 functions in rice to control bacterial streak<br />

A transient assay was used to test whether Rxo1 would function<br />

to interact with avrRxo1 in rice. When Rxo1 and avrRxo1<br />

Session 16: Pest management with minimal environmental stress 483


were cobombarded into rice, they reduced cell viability, as they<br />

did in maize, indicating that they interacted to induce HR.<br />

Stable rice transformants were then made in the rice cultivar<br />

Kitaake by Agrobacterium-mediated transformation. <strong>Rice</strong> cultivar<br />

Kitaake is highly susceptible to all strains of X. o. pv.<br />

oryzicola. In the T 0 generation of the transgenic rice lines, 36<br />

out of 82 lines carrying the native Rxo1 gene showed a strong<br />

HR when infiltrated with X. o. pv. oryzicola. The HR was confined<br />

to the infiltrated region, and the bacterial infection did<br />

not spread through the leaf. In untransformed control plants,<br />

the infiltrated region became water-soaked within 48 hours<br />

and the bacterial infection spread up the leaves, eventually<br />

killing the leaf. Segregating progeny were examined from two<br />

T 0 families that showed HR and the resistance response segregated<br />

as a single gene, as expected. The results t<strong>here</strong>fore demonstrated<br />

that Rxo1 functions as a nonhost resistance gene in<br />

rice and conditions resistance reactions to X. o. pv. oryzicola.<br />

Transferring the Rxo1 gene to hybrid rice would t<strong>here</strong>fore be<br />

expected to significantly improve its resistance to X. o. pv.<br />

oryzicola.<br />

Future prospects<br />

The function of the Rxo1 gene in controlling bacterial streak<br />

resistance after transfer from maize to rice provides hope that<br />

resistance gene transfer among distantly related cereal species<br />

will be a valuable method of expanding our arsenal of genes<br />

for crop improvement. The existence of roughly 10,000 species<br />

of grasses provides a nearly unlimited source of genes<br />

and cereal genomes carry large numbers of resistance gene<br />

sequences (Monosi et al 2004). The challenge in using these<br />

genes is to develop efficient methods to find the useful ones<br />

and predict whether they will function in the backgrounds of<br />

heterologous species.<br />

References<br />

Ayliffe MA, Steinau M, Park RF, Rooke L, Pacheco MG, Hulbert<br />

SH, Trick HN, Pryor AJ. 2004. Aberrant mRNA processing of<br />

the maize Rp1-D rust resistance gene in wheat and barley.<br />

Mol. Plant-Microbe Interact. 17(8):853-864.<br />

Hulbert SH, Webb CA. 2001. Resistance gene complexes: evolution<br />

and utilization. Ann. Rev. Phytopathol. 39:285-312.<br />

Monosi B, Wisser RJ, Pennill L, Hulbert SH. 2004. Full-genome<br />

analysis of resistance gene homologs in rice. Theor. Appl.<br />

Genet. (In press.)<br />

Sheen J. 1993. Protein phosphatase activity is required for lightinducible<br />

gene expression in maize. EMBO J. 12(9):3497-<br />

3505.<br />

Thordal-Christensen H. 2003. Fresh insights into processes of<br />

nonhost resistance. Curr. Opin. Plant Biol. 6:1-7.<br />

Zhao B, Ardales EY, Brasset E, Claflin LE, Leach JE, Hulbert SH.<br />

2004a. The Rxo1/Rba1 locus of maize controls resistance reactions<br />

to pathogenic and nonhost bacteria. Theor. Appl. Genet.<br />

109:71-79.<br />

Zhao B, Ardales EY, Raymundo A, Trick H, Leach JE, Hulbert SH.<br />

2004b. The avrRxo1 gene from the rice pathogen Xanthomonas<br />

oryzae pv. oryzicola confers a nonhost defense reaction on<br />

maize with resistance gene Rxo1. Mol. Plant-Microbe Interact.<br />

17:771-779.<br />

Notes<br />

Authors’ addresses: Bingyu Zhao, Shavannor Smith, and Scot<br />

Hulbert, Department of Plant Pathology, Kansas State University,<br />

Manhattan, Kansas, USA; Jan Leach, Bioagricultural<br />

Sciences and Pest Management, Colorado State University,<br />

Ft. Collins, Colorado, USA, e-mail:<br />

shulbrt@plantpath.ksu.edu.<br />

Screening of allelopathic activity from rice cultivars<br />

by bioassay and field test<br />

Yoshiharu Fujii, Hiroshi Araya, Syuntarou Hiradate, and Kaoru Ebana<br />

The objectives of this study are to discriminate allelopathy<br />

from other competition in rice by a specific bioassay (plant<br />

box method), and to check weed suppression activity in paddy<br />

fields. The final goal is weed control without herbicides, or<br />

less use of herbicides.<br />

The main target of breeding rice cultivars in Japan has<br />

been good taste and high productivity. Recently, cultivar<br />

Koshihikari, famous for its good taste, has been sweeping over<br />

all of Japanese rice cultivation except for Hokkaido, a northern<br />

district of Japan, and a need remains for still more good<br />

rice cultivars with good taste. Now, many other new candidates<br />

are being prepared for the market. On the other hand,<br />

sustainable agriculture, which aims at less impact on the envi-<br />

ronment and makes sure human beings have a sustainable existence,<br />

is needed all over the world. In paddy fields, problems<br />

of weed control, which had been tedious and laborious<br />

work for a long time, have been successfully conquered by the<br />

introduction of specific and powerful herbicides, and few problems<br />

remain except for some perennial weeds in Japan. We<br />

thus need to be able to use allelopathy to control paddy weeds<br />

without using much or any herbicide and to accomplish safe<br />

and labor-saving rice cultivation. Our group t<strong>here</strong>fore started<br />

research on allelopathy in rice. Our target is to search for potent<br />

allelopathic rice varieties and to use these strains for weed<br />

control in paddy fields without herbicides or with little use of<br />

them.<br />

484 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Weed dry weight (g/30 × 60 cm)<br />

25<br />

Others<br />

20<br />

Barnyardgrass<br />

15<br />

Konagi<br />

10<br />

5<br />

Inuhatarui<br />

0<br />

Awa-Akamai Houman jinjya<br />

Akamai<br />

Midorimai<br />

Soujya<br />

Akamai<br />

Fig. 1. Weed suppression by allelopathic rice in paddy fields.<br />

Nebarimochi<br />

Nihonbare<br />

For allelopathy of rice, little research has been done so<br />

far. Though effects of rice residues on the following crop were<br />

reported (Chou 1986), little research has been done on the effect<br />

of root exudates of rice. Our group has been engaged in<br />

work to search for allelopathic plants and to examine allelopathy<br />

and ascertain its mechanism. In this research, we have developed<br />

a new system that can prove the possibility of allelopathy,<br />

called the “plant box method” (Fujii 1999). This method<br />

is a sort of mixed planting using agar (no nutrient) as a medium.<br />

By using this method, we can visualize allelopathy by<br />

root exudates, and we can observe differences between varieties,<br />

even in the same species.<br />

Some farmers suggested from their experience that red<br />

rice of Japanese old-type rice varieties has few accompanying<br />

weeds. Some rice cultivars used before the introduction of<br />

herbicides are possibly resistant to paddy weeds. And, some<br />

rice cultivars or ancestors of rice growing in tropical countries<br />

w<strong>here</strong> weed growth in paddy fields is serious may be resistant<br />

to weeds. So, we started screening allelopathic activity of rice<br />

cultivars by the plant box method. Our work is quite preliminary,<br />

and our findings might not apply directly to actual weed<br />

control. But, we hope that these approaches to the biological<br />

control of paddy fields will awaken Asians to weed management<br />

using allelopathy from their original rice cultivars.<br />

A total of 500 rice cultivars, varieties, and related plants<br />

were tested. They were supplied from the Japanese Gene Bank<br />

(MAFF, Tsukuba), the core collection by Dr. M. Okuno<br />

(HNAES), the Malaysian Gene Bank (MARDI), the red rice<br />

collection by Dr. T. Itani (Hiroshima Prefectural University),<br />

and the wild and traditional rice collection in Bhutan by Dr. Y.<br />

Sato (Shizuoka University).<br />

The plant box method was followed according to Fujii<br />

(1999). The receiver plant was lettuce; Great Lakes 366 is<br />

highly susceptible to bioactive substances. The plant box<br />

method was used for assaying the activity of diffusible phytotoxic<br />

metabolites (potentially allelopathic compounds) in agar<br />

in the laboratory and is summarized briefly as follows. <strong>Rice</strong><br />

plants were grown in sand culture in pots for 4 to 8 weeks.<br />

Roots were washed with tap water and then with deionized<br />

water to remove sand. Roots of three rice plants were placed<br />

gently into a nylon-mesh-bounded cylinder (3.2 cm diameter<br />

by 6.6 cm tall), which was placed upright in one corner of a 70<br />

× 70-cm-wide by 100-cm-deep clear plastic box. Plant stems<br />

were taped to the corner of the box to stabilize the plants in the<br />

box. Hot liquid agar (0.75%; 250 mL per box) was cooled to<br />

40 °C and poured into the boxes, covering all root material,<br />

but not covering stems. Boxes containing agar and rice plants<br />

were cooled on ice until the agar had solidified (about 30 min).<br />

Thirty-one lettuce seeds were inserted partially into the surface<br />

of the agar in an equidistant grid pattern. Seeds were about<br />

halfway into the agar with the germ (pointed) end down using<br />

porcelain forceps. Boxes were sealed around the rice stems<br />

and over the box surface with plastic wrap to minimize water<br />

loss, and placed in a fluorescent-lighted incubator for 5 days<br />

(25 °C, 14-h days; 20 °C, 10-h nights). Lettuce seedlings were<br />

then removed and root and shoot lengths determined to the<br />

nearest mm. Regression analysis was used to estimate lettuce<br />

root length at zero distance from rice roots (y-intercept), and<br />

slope of the inhibition curve.<br />

Experiments were conducted with rice using an agar diffusion<br />

plant box method. Apparent allelopathic activity was<br />

observed in the second year of a 5-year field trial in transplanted<br />

water-seeded rice. In this study, the red Shrine rice,<br />

called Awa-Akamai, reduced total weed biomass by about 80–<br />

90% compared with the commercial Japanese cultivar<br />

Nipponbare (Fig. 1). The mechanisms responsible for weed<br />

suppression in Awa-Akamai may be valuable for improving<br />

weed suppression in commercial rice cultivars. Suppression<br />

of barnyardgrass and broadleaf paddy weeds has been shown<br />

in the field in Tsukuba with Awa-Akamai and other red rice<br />

cultivars.<br />

In plant box tests, roots of several rice lines, including<br />

Awa-Akamai, were highly inhibitory to the elongation of lettuce<br />

roots. Nipponbare (a nonsuppressive cultivar in field tests<br />

Session 16: Pest management with minimal environmental stress 485


Table 1. Evaluation of allelopathic activity of rice by the plant box method (selected data). Data are shown in<br />

inhibitory % to the control by the plant box method.<br />

Name of cultivar R a (%) Name of cultivar R a (%) Name of cultivar R a (%)<br />

Awa-Akamai R 96 Canaboug bong R 78 Mitsuyou 23 41<br />

Melor 94 Sathi R 78 Suigen 258 41<br />

Sisumuchimai 92 Kahei 78 Nankin 11-gou 39<br />

Tsushima-Akamai R 93 Kouketsu-mochi R 77 Koganemasari 38<br />

Soujya-Akamai R 91 Hokuriku 127 77 Kameno-o 37<br />

Deng Mack Tek 89 Li Zi Hong R 77 Nihonbare 36<br />

Keichou 2 gou 88 Mack Kheua R 76 IR30 32<br />

Yamasaka 85 Dam Ngo R 75 IR24 28<br />

Asominori 85 Nago-akaho R 73 Shinsyuukaneko 28<br />

Kurumi-wase 84 Taducan 72 Reihou 26<br />

Dular 84 Nepal No. 1 72 Sasanishiki 24<br />

Takane-nishiki 84 Chuuseishinsenbon 68 Zinriki 21<br />

Moroberekan 83 Khauk Yoe 64 Toyonishiki 21<br />

Tou-Boshi 83 PI312777 62 Rexmont 20<br />

Padi Keinikir Puti R 83 Shikoku-mai R 62 Si Li Gu 20<br />

Sekiyama 83 Fujisaka 5 gou 58 Todorokiwase 20<br />

Jyukkoku 83 Dourado Precoce 55 Basmati 19<br />

Mock Kheua 81 Karh R 54 Asahi 19<br />

Vista 81 Nankin-kaoriine 54 Masria 19<br />

Nepal No. 8 81 Koshihikari 54 Sari Queen 18<br />

Daw Dam 80 Taichuu 65 49 Kantou 146 13<br />

Houman-jinjyamai R 80 Huao Ba Wang 46 Kouryowai 4 13<br />

Mushashi-kogane 80 Sabarmati 45 Nourin 8 gou 10<br />

a<br />

R in this column means red rice.<br />

in Tsukuba) was usually less inhibitory to lettuce root elongation<br />

than was Awa-Akamai. In plant box experiments in which<br />

lettuce seed planting was delayed 2 or 3 days, allowing<br />

allelochemicals to diffuse greater distances, apparent allelopathic<br />

activity was greater following longer delays.<br />

The results of the effect of rice cultivars are shown in<br />

Table 1, in which % means the inhibitory percentage of lettuce<br />

radicle length in the root surface of rice by extrapolation of<br />

the radicle length of each point apart from the root zone of<br />

rice to the control. These data show the activity and quantity<br />

of root exudates. Results of screening 500 rice varieties showed<br />

a wide variation in activity. Some varieties showed no activity,<br />

some showed strong activity, and, in some cases, the top of the<br />

lettuce radicle became brown to black. The strongest activity<br />

was of Awa-Akamai, an old red rice reserved in the old shrine<br />

in Shikoku. Its inhibitory activity was equivalent to the activity<br />

of Mucuna and Avena species that showed the strongest<br />

activity we ever tested. In Table 1, the letter R shows red rice<br />

and, generally speaking, the allelopathic activity of red rice is<br />

stronger than that of other rice cultivars.<br />

Though our research aimed to search for potent allelopathic<br />

rice varieties that inhibit the growth of accompanying<br />

weeds, the work reported <strong>here</strong> is only the first step because we<br />

used lettuce as a model plant and did not yet estimate the allelopathic<br />

effect in general paddy fields. But it became clear<br />

that t<strong>here</strong> were distinct differences among rice varieties.<br />

We would like to assess allelopathic activity by using<br />

paddy weeds as the acceptors, to identify allelopathic substances<br />

and specific genes in relation to allelopathy, and to<br />

breed new varieties that have allelopathic ability to control<br />

weeds. This project may take another 10 years or more, and it<br />

might be impossible to suppress paddy weeds completely by<br />

only allelopathy, but, in combination with other biological<br />

control, allelopathic rice strains will help us to achieve sustainable<br />

and safe rice production.<br />

References<br />

Azmi M, Abdullah MZ, Fujii Y.2000. Exploratory study on allelopathic<br />

effect of selected Malaysian rice varieties and rice field<br />

weed species. J. Trop. Agric. Food Sci. 28(1):39-54.<br />

Baker P. 1992. Weed resistance hidden in rice genes. <strong>Rice</strong> J. 8-9<br />

March.<br />

Chou C-H. 1986. The role of allelopathy in subtropical<br />

agroecosystems in Taiwan. In: Putnam AR, Tang C-S, editors.<br />

The science of allelopathy. New York (USA): John Wiley<br />

& Sons. p 57-73.<br />

Fujii Y, Shibuya T, Yasuda T. 1991. Discrimination of allelopathy of<br />

upland rice, taro, and oat by substitutive experiment and its<br />

modified experiments. Jpn. J. Soil Sci. Plant Nutr. 62:357-<br />

362.<br />

Fujii Y. 1994. The allelopathic effect of some rice varieties. In: Integrated<br />

management of paddy and aquatic weeds in Asia. FFTC<br />

Book Series, No. 45. p 160-165.<br />

Fujii Y. 1999. Discrimination and proof methods for allelopathy by<br />

bioassay, greenhouse and field tests. In: Macias FA, Galindo<br />

JCG, Molinillo JMG, Cutler HG, editors. Recent advances in<br />

allelopathy. Vol. 1. p 25-28.<br />

486 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Fujii Y, Gealy DR. 2000. Screening of allelopathic activity from rice<br />

cultivars. In: Oono K, Komatsuda T, Kadowaki K, Vaughan<br />

D, editors. Integration of biodiversity and genomic technology<br />

for crop improvement. Tokyo (Japan): Ministry of Agriculture,<br />

Forestry, and Fisheries. p 135-136.<br />

Fujii Y, Shibuya T, Nakatani K, Itani T, Hiradate S, Parvez MM.<br />

2004. Assessment method for allelopathic effect from leaf litter<br />

leachates. Weed Biol. Manage. 4(1):19-23.<br />

Notes<br />

Authors’ addresses: Yoshiharu Fujii, Hiroshi Araya, and Syuntarou<br />

Hiradate, National <strong>Institute</strong> for Agro-Environmental Sciences,<br />

Tsukuba, e-mail: yfujii@affrc.go.jp; Kaoru Ebana, National<br />

<strong>Institute</strong> of Agrobiological Sciences, Tsukuba, Japan.<br />

Evaluating near-isogenic lines with QTLs<br />

for field resistance to rice blast from upland rice cultivar<br />

Sensho through marker-aided selection<br />

Norikuni Saka and Shuichi Fukuoka<br />

<strong>Rice</strong> blast caused by Pyricularia oryzae is the most serious<br />

disease of rice in the world, and cultivation of disease-resistant<br />

cultivars is highly desirable for stable rice production. In<br />

Japan, rice cultivars with a complete rice blast-resistance gene,<br />

such as Kusabue, suffered from a massive outbreak of blast<br />

disease in the 1960s. T<strong>here</strong>after, the importance of a program<br />

for breeding varieties with field resistance to rice blast was<br />

strongly recognized (Takita and Solis 2002). However, the<br />

mechanism of field resistance has not been fully analyzed because<br />

of the complicated <strong>here</strong>ditary mode and difficulty of<br />

bioassay; thus, breeding did not proceed satisfactorily. In this<br />

study, we produced recombinant inbred lines using DNA markers<br />

for high field resistance of upland rice to simplify complicated<br />

phenomena, and to develop a method of breeding resistant<br />

cultivars.<br />

History of the breeding of rice blast resistance at AARC<br />

At the Aichi Agricultural <strong>Research</strong> Center (AARC), Mountainous<br />

Region Agricultural <strong>Research</strong> <strong>Institute</strong>, we have been<br />

breeding blast-resistant lines of rice since 1933 in an area w<strong>here</strong><br />

an outbreak of rice blast occurred, by introducing the field<br />

resistance to blast of upland rice cultivar Sensho into paddy<br />

rice. Until now, scores of rice-blast-resistant cultivars have been<br />

bred. However, it has been difficult to eliminate the inferior<br />

characteristics of upland rice such as burning up and poor quality,<br />

and only paddy rice with a part of the upland rice genes<br />

introduced has been released (Saka et al, in preparation). Breeding<br />

for excellent eating quality satisfying the needs of Japanese<br />

consumers along with field resistance to rice blast has<br />

not succeeded because these traits are controlled by polygenes.<br />

T<strong>here</strong>fore, we tried to resolve the long-pending problems using<br />

genomic techniques.<br />

Mapping and breeding NILs having each QTL region<br />

Kato et al (2002) crossed upland rice cultivar Sensho with blastsusceptible<br />

japonica paddy rice variety Norin 29 and analyzed<br />

the resistance to leaf blast of the progeny by QTL analysis.<br />

They found four QTL regions, which were detected in the vicinity<br />

of RFLP markers G271 (LOD = 24.8) and G177 (5.7)<br />

of chromosome 4 (Targets 1 and 4), in the vicinity of C1172<br />

(3.6) of chromosome 11 (Target 2), and in the vicinity of S826<br />

(3.4) of chromosome 12 (Target 3).<br />

Based on this finding, we backcrossed (B 4 F 4 –B 3 F 6 )<br />

Mine-asahi, a susceptible variety with good eating quality, with<br />

Sensho to breed lines having each of the four QTL regions<br />

independently, using DNA markers for selection. We bred NIL<br />

(near-isogenic line)-1, which has the Mine-asahi genome except<br />

for the RFLP marker G271 region of Sensho (smaller than<br />

22.3 cM), the Target 1 region; NIL-2, which has the Mineasahi<br />

genome except for the SSR marker RM229–RM287 region<br />

(smaller than 16.9 cM) of chromosome 11 of Sensho, the<br />

Target 2 region; and NIL-3, which has the Sensho genome<br />

except for the SSR marker region RM313–S13752 (smaller<br />

than 14.7 cM) of chromosome 12 of Sensho and a part of chromosomes<br />

1 and 9, w<strong>here</strong> a QTL was not detected, the Target 3<br />

region. In addition, NILs that showed resistance, although the<br />

chromosome with the resistance gene was not specified, were<br />

bred (NIL-5). From the results of a race test, the complete<br />

resistance genes of these NILs were Pia and Pii, like their backcrossed<br />

parent Mine-asahi.<br />

Effect of each QTL region on blast severity<br />

The leaf and panicle blast tests gave consistent results in the<br />

two years of testing, and the difference between the criterion<br />

varieties having Pia and Pii and other cultivars was clear. Under<br />

the same test conditions, we performed a leaf blast test for<br />

each NIL. The degree of resistance varied with the NIL, and<br />

was in the order of NIL-1 > NIL-2 >NIL-5 > NIL-3 (Fig. 1).<br />

Session 16: Pest management with minimal environmental stress 487


1 2 3 4<br />

4 5 6 7 8 9<br />

Fig. 1. Leaf blast resistance in NILs of Mine-asahi backcrossed to Sensho. 1 = Chubu 105 (r), 2 =<br />

Mine-asahi (ms), 3 = Mine-hibiki (rm), 4 = Hitomebore (s), 5 = Sensho (rr), 6 = NIL-1 (Target 1: Chr. 4-<br />

1), 7 = NIL-5 (the region undecided), 8 = NIL-2 (Target 2: Chr. 11), 9 = NIL-3 (Target 3: Chr. 12), 1–5 =<br />

check varieties.<br />

This result is in agreement with the results of QTL analysis<br />

reported by Kato et al (2002). The result of the panicle blast<br />

test was similar to that of the leaf blast test, confirming that<br />

the QTL region for resistance to leaf blast also confers resistance<br />

to panicle blast.<br />

The field resistance to rice blast of the four NILs was<br />

compared with that of the criterion varieties (Saka 1996) (Fig.<br />

2). NIL-1, which had the highest resistance, developed severer<br />

symptoms of leaf blast than Sensho, but was more resistant<br />

than Chubu 105, which is the criterion variety with high resistance,<br />

and was judged to have very high resistance. The resistance<br />

to panicle blast of NIL-1 was slightly lower than that of<br />

Sensho but was higher than that of Tiyonishiki, which had<br />

slightly high resistance. Thus, resistance of NIL-1 to panicle<br />

blast was judged to be high to slightly high. These results suggest<br />

that NIL-1, having the Target 1 region, has very high resistance<br />

to rice blast. In particular, resistance to leaf blast of<br />

NIL-1 was very high compared with that of the criterion varieties,<br />

and we consider that this line could be cultivated without<br />

the use of agrochemicals for control of this disease in areas<br />

w<strong>here</strong> rice blast occurs commonly in Japan. The resistance<br />

to leaf blast of NIL-2 having the Target 2 region was<br />

similar to or slightly higher than that of Mine-hibiki, a criterion<br />

variety, and the resistance to panicle blast of NIL-2 was<br />

similar to that of Tiyonishiki, which has slightly high resistance.<br />

Mine-hibiki and Tiyonishiki are the varieties having the<br />

highest resistance to rice blast among the recommended varieties<br />

in Japan, and they show high resistance in the area w<strong>here</strong><br />

rice blast commonly occurs. T<strong>here</strong>fore, Target 2 was considered<br />

to contribute by itself to stable rice production. NIL-5, in<br />

which the region for the resistance gene was not specified,<br />

had medium resistance to leaf and panicle blast. NIL-3, having<br />

Target 3, had slightly higher resistance to leaf and panicle<br />

blast than Mine-asahi, which has slightly low resistance, and<br />

was judged to have medium to slightly low resistance.<br />

Elite NILs with a narrow Sensho region<br />

The above-described four NILs retained the inferior traits of<br />

Sensho such as poor eating quality and coarseness of stems<br />

and leaves compared with repeatedly backcrossed parent cultivar<br />

Mine-asahi. To narrow the Sensho region, we selected a<br />

line with a narrower region for the resistance from 672 individuals<br />

of Mine-asahi*3/Sensho (B 2 F 2 ) having the Target 1<br />

region, using eight PCR markers included in RFLP marker<br />

G271–G89B (14.6 cM). As a result, we succeeded in selecting<br />

a NIL that has the Mine-asahi genome except for the chromosomal<br />

segment smaller than 0.5 cM having Target 1. This region<br />

coincided with the estimated locus of rice blast-resistance<br />

gene pi21 (Fukuoka and Okuno 2001), and this NIL had field<br />

resistance similar to that of the NIL having Target 1. Thus, the<br />

NIL is considered to be a useful breeding material. In the future,<br />

we will perform linkage drag associated with introgressed<br />

Sensho DNA to eliminate undesirable characteristics by<br />

marker-aided selection, using various NILs having different<br />

sizes of Sensho region that were selected in this study.<br />

The next target<br />

The level of field resistance to blast of NILs having QTL regions<br />

from Sensho was clarified as mentioned above. Among<br />

them, the NIL with Target 1 had high resistance, which was<br />

not observed in known paddy rice varieties in Japan, and we<br />

may be able to grow varieties with this region introduced without<br />

using agrochemicals for control of rice blast. Hereafter,<br />

not only the simple use of this region but also examination of<br />

488 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Panicle blast severity<br />

(poor)<br />

9<br />

r<br />

mr<br />

s<br />

8<br />

6<br />

7<br />

3<br />

4<br />

m<br />

6<br />

2<br />

mr<br />

5<br />

1<br />

4<br />

5<br />

3<br />

2<br />

1<br />

0<br />

(excellent) 0 1 2 3 4 5 6 7 8 9 (poor)<br />

Leaf blast severity<br />

Fig. 2. Blast resistance in NILs of Mine-asahi backcrossed to Sensho. 1 = NIL-1<br />

(Target 1: Chr. 4-1), 2 = NIL-2 (Target 2: Chr. 11), 3 = NIL-3 (Target 3: Chr. 12), 4<br />

= NIL-5 (the region undecided), 5 = Sensho (rr), 6 = Mine-asahi (ms); blue dotted<br />

line: leaf blast check varieties; Chubu 105 (r), Mine-hibiki (mr), Hitomebore<br />

(s); green dotted line: panicle blast check varieties; Tiyonishiki (mr), Nipponbare<br />

(m).<br />

the cumulative effects and confirmation of the accompanying<br />

inferior characteristics may be necessary.<br />

Recently, we started a national project to introduce these<br />

QTL regions into the leading Japanese variety of rice,<br />

Koshihikari, which occupies 32% of the paddy fields in Japan.<br />

If field resistance to rice blast can be introduced into this<br />

variety while retaining its excellent eating quality, we will be<br />

able to cultivate rice stably without disturbing the environment.<br />

Along with the above project, we are now trying to clone<br />

the pi 21 gene (Fukuoka and Okuno 2001). By clarifying the<br />

function of this gene, we should be able to understand easily<br />

the mechanism of complicated field resistance to rice blast.<br />

References<br />

Fukuoka S, Okuno K. 2001. QTL analysis and mapping of pi21, a<br />

recessive gene for field resistance to rice blast in Japanese<br />

upland rice. Theor. Appl. Genet. 103:185-190.<br />

Kato T, Endo I, Yano M, Sasaki T, Inoue M, Kudo S. 2002. Mapping<br />

of quantitative trait loci for field resistance to rice blast in<br />

upland rice, Sensho. Breed. Res. 4:119-124.<br />

Saka N. 1996. Panicle blast resistance: test method using the area<br />

w<strong>here</strong> outbreak of rice blast occurred. In: Yamamoto R,<br />

Horisue N, Ikeda R, editors. <strong>Rice</strong> breeding manual. Tokyo<br />

(Japan): National Agricultural <strong>Research</strong> Center: Yokendo<br />

Printing Co., Ltd. p 15-19.<br />

Saka N, Kudo S, Sugiura K, Okuda T, Terashima T. History for 70<br />

years, present situation and the future of the breeding of rice<br />

blast resistance in the Mountainous Region Agricultural <strong>Research</strong><br />

<strong>Institute</strong>, AARC. Plant Prod. Sci. (In preparation.)<br />

Takita T, Solis O. 2002. <strong>Rice</strong> breeding at the National Agricultural<br />

<strong>Research</strong> Center for the Tohoku Region (NARCT) and rice<br />

varietal recommendation process in Japan. Bull. Natl. Agric.<br />

Res. Cent. Tohoku Reg. 100:93-117.<br />

Notes<br />

Authors’ addresses: Norikuni Saka, Aichi Agricultural <strong>Research</strong><br />

Center (AARC), Mountainous Region Agricultural <strong>Research</strong><br />

<strong>Institute</strong>. Inabu, Aichi 441-2513, Japan, e-mail:<br />

norikuni_saka@pref.aichi.lg.jp; Shuichi Fukuoka, National<br />

<strong>Institute</strong> of Agrobiological Sciences (NIAS), Tsukuba, Ibaraki<br />

305-8602, Japan, e-mail: fukusan@affrc.go.jp.<br />

Session 16: Pest management with minimal environmental stress 489


Wrap-up of Session 16<br />

Pest management relies on the use of appropriate technologies<br />

that are based on location-specific pest composition, environment,<br />

and farmers’ socioeconomic constraints. Integrated pest<br />

management (IPM) attempts to prevent pathogens, insects, and<br />

weeds from causing economic crop losses by using a variety of<br />

management techniques that are cost-effective and cause the<br />

least damage to the environment. The objective of this session<br />

was to provide participants with new ideas and a better understanding<br />

of key issues in pest management to develop environment-friendly<br />

technologies, rather than to draw any conclusions<br />

from the studies presented.<br />

The oral session consisted of two subsessions: the first<br />

dealt with insect pest management and the second with disease<br />

management. Subsession 1 featured three presentations and<br />

four presentations were delivered in subsession 2. K. Kiritani and<br />

T.W. Mew presented their philosophy and critical overview on insect<br />

pest management and disease management for sustainable<br />

rice production, respectively. K. Kiritani focused on integrated<br />

biodiversity management (IBM), a new concept on how to merge<br />

economic optimization and conservation in pest management.<br />

T.W. Mew focused on three issues and research agendas: (1) the<br />

need for increased genetic diversity, (2) the health of farmersaved<br />

seeds for increased storage and shelf-life, and (3) soil<br />

health. To ensure sustainability in rice production systems and<br />

achieve the next Green Revolution, he advocates using appropriate<br />

varieties, emphasizing seed health, and using cropping practices<br />

that ensure a healthy ecosystem. The other two presentations<br />

made by X. Yu and M. Matsumura in the first half of Session<br />

16 discussed the use of natural enemies, that is, how to<br />

make use of domestic and migratory natural enemies as the most<br />

promising control measures in IPM. The three presentations made<br />

by T. Ashizawa, C.M. Vera Cruz, and S.H. Hulbert in the second<br />

half of Session 16 were all related to the use of host-plant resistance<br />

against pathogens. The first two presentations covered blast<br />

management using simulation modeling with BLASTMUL for rice<br />

multilines, and the association of candidate defense genes with<br />

quantitative disease resistance and in silico analysis of their characteristics.<br />

According to T. Ashizawa, BLASTMUL simulations for<br />

leaf blast epidemics usually agreed with those observed in different<br />

locations and multiline series, suggesting that this is useful<br />

for forecasting leaf blast epidemics in multilines and is a powerful<br />

tool in determining effective mixture proportions of nearisogenic<br />

lines in multilines. C. Vera Cruz and colleagues employed<br />

the candidate gene approach aimed at accumulating different<br />

mechanisms of quantitative resistance to blast. This approach<br />

integrates the molecular analysis of host-pathogen interactions,<br />

gene mapping and expression, and selection for blast resistance<br />

in elite rice lines. S.H. Hulbert discussed the transfer of resistance<br />

genes between cereal species. He explained how the function<br />

of different resistance genes was evaluated after transfer<br />

between distantly related cereal species such as rice and maize.<br />

R. Wang summarized the oral session He remarked that<br />

the studies presented showed the evolution of the science of<br />

pest management in relation to understanding pest systems, that<br />

is, the scientific understanding has gone beyond the use of component<br />

technologies into the production system. The current trend<br />

makes use of converging strategies for pest management as depicted<br />

in the areas of enhancing natural control, ecosystem diversity,<br />

and genetic diversity, all contributing toward increasing<br />

resilience of the system. Modern tools for studying host-plant<br />

resistance are being employed in understanding and managing<br />

the system. The potential for protecting the environment through<br />

reductions in pesticide application has also been recognized.<br />

Applying the concepts and tools in the context of modern science,<br />

R. Wang saw a great potential for collaboration among<br />

advanced research institutions and national agricultural research<br />

and extension systems.<br />

A total of 36 posters were presented in Session 16, covering<br />

insect pest, disease, and weed management. Two of the presentations<br />

were selected to represent the diversity of topics in<br />

this session. These posters can be read in this proceedings. These<br />

are “Evaluating near-isogenic lines with QTLs for field resistance<br />

to blast from upland rice cultivar Sensho through marker-aided<br />

selection” by N. Saka and S. Fukuoka and “Screening of allelopathic<br />

activity from rice cultivars by bioassay and field test” by Y.<br />

Fujii, H. Araya, S. Hiradate, and K. Ebana.<br />

490 <strong>Rice</strong> is life: scientific perspectives for the 21st century


SESSION 17<br />

<strong>Rice</strong> supply and demand<br />

CONVENER: O. Koyama (JIRCAS)<br />

CO-CONVENER: D. Dawe (<strong>IRRI</strong>)


<strong>International</strong> trade in rice: recent developments<br />

and prospects<br />

Concepcion Calpe<br />

In the past several decades, the international rice market has<br />

undergone major changes, in particular a shift in the general<br />

policy setting, a strong expansion in the volumes of trade, and<br />

a lingering tendency for world prices to decline in real terms<br />

and relative to the other two most-traded cereals, wheat and<br />

maize. Nonetheless, the world rice market continues to be regarded<br />

as distorted, thin, segmented, and volatile. This paper<br />

discusses whether these attributes still portray the market in<br />

the light of the trade liberalization drives prevailing in the<br />

1990s.<br />

On the policy front, interventions have diminished in the<br />

wake of the market liberalization launched by several countries<br />

since the late 1980s. The WTO agreement, in 1994, also<br />

disciplined government policies and helped improve market<br />

access. Nonetheless, rice continues to be one of the most protected<br />

commodities in both developing and developed countries,<br />

subject to high tariff and nontariff barriers, export restrictions<br />

or aids, state trading, and domestic market interventions.<br />

Since the early 1960s, trade in rice has expanded at about<br />

3% per annum, not much different from the pace of growth in<br />

wheat or maize trade (Fig. 1). However, growth has been far<br />

from steady. The liberalization thrust of the 1990s coincided<br />

with a period of dynamic expansion in the volume of rice trade,<br />

which succeeded a decade of relatively lackluster growth in<br />

the 1980s. The volume of rice exchanged rose from less than 7<br />

million tons in 1961 to 24 million t in 2000 and has continued<br />

to expand further in the early 2000s, surpassing 28 million t in<br />

2001 and 2002. Nevertheless, the international rice market is<br />

still small relative to the other major cereals, with an average<br />

of 27 million t in 2000-03, about one-quarter of the volume<br />

traded in wheat and a little over one-third of the trade in maize.<br />

Rising import demand by countries in Asia and Africa<br />

was the main force underpinning trade in rice in the 1990s and<br />

early 2000s. The increases in imports were often a reflection<br />

of more open trade policies but were also prompted by several<br />

production setbacks, for instance, in 1997 in the wake of an El<br />

Niño weather anomaly. Despite the consolidation of countries<br />

in Africa and the Near East as important and stable destinations<br />

of rice trade, the demand side of the rice international<br />

market remains highly dispersed geographically, with the top<br />

ten importers accounting for only 40% of the total.<br />

Most of the trade expansion witnessed in the past two<br />

decades was met by traditional exporters. Thailand, in particular,<br />

has maintained its leadership as the top rice exporter<br />

since 1980. Major inroads were made by Vietnam, which became<br />

the second most important source of trade supplies in<br />

the 1990s, a position from which it was eclipsed in the early<br />

2000s, when India started granting export subsidies. Despite<br />

Million t<br />

160<br />

140<br />

120<br />

100<br />

80<br />

60<br />

40<br />

20<br />

0<br />

1961<br />

1964<br />

1967<br />

1970<br />

1973<br />

1976<br />

Wheat: Y = 48.147e 0.0269t<br />

1979<br />

Year<br />

Fig. 1. Trends in global cereal trade, 1961-2003.<br />

changes in the relative positions of the major exporters, the<br />

supply side of the rice international market is still highly concentrated,<br />

with the top four exporting countries (Thailand,<br />

India, Vietnam, and the United States) supplying 66% of trade<br />

and the top ten more than 90% of the total.<br />

<strong>Rice</strong> is not a homogeneous commodity and t<strong>here</strong> are now<br />

more than 50 different published international price quotations<br />

for rice. In fact, t<strong>here</strong> are distinct submarkets featured according<br />

to several criteria, the most important of which are variety,<br />

quality (defined mainly by the percentage of brokens), and the<br />

degree of processing.<br />

The expansion of trade witnessed in the 1990s was accompanied<br />

by small but significant changes in the structure of<br />

the world rice market and in the relative importance of each<br />

segment (Table 1). The bulk of global trade continues to be in<br />

the form of milled, indica, and higher-quality rice (defined as<br />

containing less than 20% of brokens). However, aromatic rice<br />

varieties, lower-quality rice, parboiled, and paddy have made<br />

large in-roads and have increased market shares. Those gains<br />

were mainly at the expense of trade in japonica, higher-quality,<br />

and milled rice.<br />

Most of the highlighted changes can be associated with<br />

shifts in the geographical pattern of trade. The increasing importance<br />

of Africa and several Asian countries as destinations<br />

of rice flows, in particular, has sustained a large increase in the<br />

trade of lower-quality rice. The growing importance of aromatic<br />

rice varieties in global trade reflects brisk imports to the<br />

European Union (mainly of Basmati rice, imported under preferential<br />

access conditions), the United States, Canada, and<br />

Australia. However, it can also be associated with large deliveries<br />

of Hom Mali rice (a fragrant variety from Thailand) to<br />

1982<br />

1985<br />

Maize: Y = 24.223e 0.0351t<br />

<strong>Rice</strong>: Y = 6.0645e 0.0321t<br />

1988<br />

1991<br />

1994<br />

1997<br />

2000<br />

2003<br />

492 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. World trade in rice.<br />

1992-94 2001-03<br />

000 t Share (%) 000 t Share (%)<br />

Variety<br />

Indica 11,663 76 20,068 75<br />

Japonica 2,132 14 3,186 12<br />

Aromatic 1,353 9 3,322 12<br />

Glutinous 115 1 242 1<br />

US$ t –1<br />

1,400<br />

1,200<br />

1,000<br />

800<br />

600<br />

400<br />

200<br />

<strong>Rice</strong> price nominal<br />

<strong>Rice</strong> price real<br />

y = 814.52e –0.031x<br />

R 2 = 0.7354<br />

Quality<br />

High 11,781 77 20,226 75<br />

Low 3,482 23 6,592 25<br />

Degree of processing (forms)<br />

Paddy 263 2 1,122 4<br />

Husked 508 3 1,077 4<br />

Milled 12,559 82 20,639 77<br />

Parboiled 1,934 13 3,980 15<br />

Total trade 15,263 100 26,818 100<br />

countries in Africa, particularly Côte d’Ivoire, Ghana, and<br />

Senegal, albeit with a high percentage of brokens. On the other<br />

hand, high degrees of protection in japonica rice markets such<br />

as Japan, the Republic of Korea, the European Union, and<br />

Turkey have constrained the opportunities to expand japonica<br />

rice trade. Tariff escalation, w<strong>here</strong>by the more processed forms<br />

of a commodity are assigned higher tariff rates, has favored a<br />

strong expansion of trade in paddy, principally to Latin America<br />

and the Caribbean.<br />

An international commodity market is considered “thin”<br />

when it represents a relatively small proportion of global production.<br />

The international rice market represented only 3% to<br />

5% of global production in the 1980s, but a strong expansion<br />

of world trade since the mid-1990s has made it “deepen,” as it<br />

has come to represent 7% of global production in recent years.<br />

Nonetheless, the international rice market remains thin compared<br />

with wheat or maize, whose trade now accounts for some<br />

18% and 13% of global production, respectively.<br />

Thin commodity markets are often subject to large swings<br />

in volumes since relatively small changes in supply or use in<br />

important producing countries may give rise to large increases<br />

or contractions in their exports or imports. In general, however,<br />

such countries have preferred to balance their domestic<br />

markets by building up or drawing supplies from stocks, with<br />

trade considered only a “residual” option.<br />

Global trade in rice has fluctuated widely over the past<br />

two decades, from a minimum of 10.6 million to 28.3 million<br />

t, and variability measured by the coefficient of variation (CV)<br />

was high at 37% compared with a 12% variability of global<br />

rice production. It was also much higher than the variability of<br />

wheat and maize trade, which had a CV of 6% and 8%, respectively.<br />

Variability of rice trade measured decade by decade<br />

pointed to a greater stability. In the 1980s, volumes exchanged<br />

on the international rice market fluctuated within a<br />

relatively small range of 11 million to 14 million t, resulting in<br />

0<br />

1960<br />

1963<br />

1966<br />

1969<br />

1972<br />

1975<br />

Fig. 2. <strong>International</strong> rice prices.<br />

1978<br />

1981<br />

1984<br />

1987<br />

1990<br />

1993<br />

Year<br />

1996<br />

1999<br />

2002<br />

a measure of variability on the order of 8%, not very different<br />

from that prevailing on the wheat and maize markets. Trade<br />

fluctuated within a much broader band of 12 million to 28<br />

million t in the 1990s, which gave rise to a much higher CV of<br />

26%. Thus, the strong tendency for international trade to grow<br />

in the 1990s was associated with much greater volatility in<br />

volumes.<br />

The international rice market has also been characterized<br />

by a long-term tendency for world rice prices (represented<br />

by the Thai 5% broken rice, f.o.b. Bangkok) to fall in real<br />

terms (deflated by the index of unit value of manufactured<br />

goods) from 1961 to 2003 (Fig. 2). The decline in constant<br />

US$ has been 3% per annum and, in 2003, rice was worth less<br />

than 40%, in real terms, of its 1961 value. <strong>Rice</strong> prices also<br />

declined relative to wheat and maize. If 1 t of rice could be<br />

exchanged for 2.5 t of wheat in 1961, it could be bartered for<br />

only 1.3 t in 2003. A similar loss in value was evidenced relative<br />

to world maize prices.<br />

Although variability in the volume of rice trade rose in<br />

the 1990s compared with the 1980s, this did not cause the variability<br />

of world prices to follow suit. On the contrary, rice prices<br />

have become more stable over time, to the point of achieving<br />

levels of volatility similar to those exhibited by wheat and maize<br />

prices. Actually, on an annual frequency basis, prices in the<br />

1990s were more stable for rice than for wheat or maize, in<br />

sharp contrast to the pattern prevailing in the 1960s and ’80s.<br />

Stabilization of world rice quotations was also evidenced on a<br />

monthly frequency basis.<br />

Thus, the rising variability of trade flows was not associated<br />

with more volatile world prices, which have instead stabilized.<br />

Several explanations can be offered to explain this<br />

paradox. First, the deepening of the international market has<br />

meant a greater dependability of supplies. The existence of<br />

large buffer stocks, the improved flows of information on markets<br />

and prices, and the introduction of disciplines (restrictions<br />

on policies because of trade agreements such as WTO)<br />

on national and international policies are also believed to have<br />

fostered price stability on the market, in spite of the wider<br />

fluctuations in the volumes of trade.<br />

Session 17: <strong>Rice</strong> supply and demand 493


In summary, it can be said that international trade in rice<br />

has become less distorted, less thin, more unstable volumewise,<br />

but more stable price-wise and more dependable. This<br />

could have important implications for policymakers by encouraging<br />

them to lower domestic protection to the rice sector and<br />

increase their countries’ reliance on trade. However, t<strong>here</strong> is<br />

still much uncertainty on whether the tendencies observed in<br />

the 1990s will linger into the rest of the 2000s and in the de-<br />

cades to come. Against this backdrop, the outcome of the ongoing<br />

multilateral trade negotiations will be of particular importance<br />

in shaping the future of the international rice market.<br />

Notes<br />

Author’s address: Food and Agriculture Organization.<br />

<strong>Rice</strong> in the world at stake<br />

Shoichi Ito<br />

<strong>Rice</strong> has been consumed as a staple food more than any other<br />

grain in the world. However, in Asia, w<strong>here</strong> 90% of global<br />

rice is consumed, per capita rice consumption (PCRC) has been<br />

declining over time. In Japan, PCRC decreased by almost half<br />

from 125 to 65 kg during the last 45 years. In Taiwan (China),<br />

it decreased by more than two-thirds from 160 to 50 kg during<br />

the same period. As a result, domestic rice production in both<br />

countries has decreased substantially. The declining trend of<br />

PCRC seems likely to continue even though the governments<br />

of these nations have tried hard to reverse the trend (Fig. 1).<br />

The same type of situation has been occurring in other<br />

Asian countries such as South Korea, China, and India. The<br />

current situation in South Korea is similar to what happened in<br />

Japan in the 1960s when the decline began. In China, the pace<br />

of the decline currently appears to be small at 0.5 kg per year,<br />

decreasing from 110 kg in 1991. However, the diet in large<br />

areas of China is quite similar to the Taiwanese diet. T<strong>here</strong>fore,<br />

it would not be surprising even if the PCRC in China<br />

were to decline as fast as what has happened in Taiwan (China).<br />

The declining trend of PCRC in the Asian countries was first<br />

reported by Ito et al (1989) but it has not hit bottom yet. It was<br />

big news in Japan in May 2004 that PCRC in Japan dropped<br />

by as much as 2.4% during the preceding 12 months (Asahi<br />

Newspaper, June 2004). The countries w<strong>here</strong> PCRC is decreasing<br />

are not only economically developed countries. This has<br />

spread all over Asia.<br />

Even in China, which is the world’s largest rice-producing/-consuming<br />

country (holding 1.3 billion people), its PCRC<br />

has been decreasing steadily during recent years. PCRC in<br />

China was increasing until the early 1990s; however, it peaked<br />

at 110 kg in 1991 and then started decreasing. It was as low as<br />

105 kg in 2004, about a 4% drop during the last decade. If the<br />

PCRC dropped by 1 kg in China, this would mean a surplus of<br />

1.3 million tons of rice generated in the nation. Population in<br />

China is estimated to peak in the 2030s; t<strong>here</strong>fore, total rice<br />

consumption in the country could decrease anytime soon if<br />

the current situation continues.<br />

A continuous decrease in PCRC in a country eventually<br />

leads to a decrease in total consumption in the country. And<br />

this can lead to a decrease in domestic production. This causes<br />

a political problem just like the one that prevailed in Japan<br />

and Taiwan (China) during the last three decades. It is still a<br />

huge problem involving governments, producers, and consumers.<br />

In Taiwan, as total consumption decreased to a third, production<br />

decreased to a third as well. The situation in Japan is<br />

the same. This type of decrease in rice production, which is<br />

the core of Asian agriculture, is a tremendous setback. The<br />

drastic plunge in PCRC in Taiwan and Japan is not unique, but<br />

any Asian country would have to face the same fate if it did<br />

not take any effective measures.<br />

Pressure on market prices<br />

<strong>Rice</strong> production is quite sensitive to changes in market prices.<br />

The rice of Thai 5% broken was as low as US$237 per metric<br />

ton (mt), on a milled basis, in 1993. It increased since then and<br />

reached $338 in 1996 and remained relatively high until 1998.<br />

Meanwhile, rice production in Asia increased continuously,<br />

breaking records every year through 1999, reaching 371 million<br />

mt. The world total production, reflecting the situation in<br />

Asia, reached a new record at slightly over 400 million mt in<br />

1999, the first time in history to reach the 400 million mt level.<br />

However, the market prices continued to plunge and dropped<br />

way below $200 at $173 per mt by 2001. The price in 2001<br />

was the lowest since 1972. Although market prices recovered<br />

some since then, they are still drifting around $250.<br />

Accounting for about 90% of world rice production,<br />

Asian rice producers are quite sensitive to changes in market<br />

prices, and changes in global production are a reflection of the<br />

changes in Asian production. Asian rice production decreased<br />

three years in a row to as little as 344 million mt in 2002, a<br />

7.3% decrease from the record level in 1999. Asian production<br />

recovered some in 2003 and 2004. However, the historically<br />

largest amount recorded in 1999 has not been achieved<br />

even after five years. During the last five decades, each historical<br />

production record has been renewed mostly every year<br />

or after three years as the longest period after the preceding<br />

record. Nowadays, however, the preceding record has not been<br />

surpassed even at the fifth year. The very low prices around<br />

2000 have affected rice growers. In real terms, taking the consumer<br />

price index (CPI) into consideration, the low prices in<br />

2001 were practically the lowest in history. The market prices<br />

494 <strong>Rice</strong> is life: scientific perspectives for the 21st century


kg<br />

200<br />

160<br />

Milled basis<br />

Japan<br />

Taiwan (China)<br />

South Korea<br />

China<br />

120<br />

80<br />

40<br />

0<br />

1961<br />

1963<br />

1965<br />

1967<br />

1969<br />

1971<br />

1973<br />

1975<br />

1977<br />

1979<br />

1981<br />

1983<br />

1985<br />

1987<br />

1989<br />

1991<br />

1993<br />

1995<br />

1997<br />

1999<br />

2001<br />

2003<br />

2005<br />

2007<br />

Year<br />

Source: S. Ito, World Food Statistics & Graphics (http://worldfood.muses.tottori-u.ac.jp).<br />

Original data sources: USDA: PS&D View, November 2004; USBC: <strong>International</strong> Data Base, July 2003.<br />

Fig. 1. Per capita consumption of rice for Japan, Taiwan (China), South Korea, and China during 1961-2004.<br />

in 2003 and 2004 recovered some; however, the rise in prices<br />

is not enough to boost production and set a new record. Since<br />

world consumption has been greater than production during<br />

the past few years, the world rice stock has been diminishing<br />

dramatically. T<strong>here</strong>fore, market prices should be rising, but<br />

they have appeared to stop rising since early 2004.<br />

Consumption-derived supply and forecasts for rice<br />

A decrease in PCRC indicates weaker demand. The demand<br />

curve for rice in Asia may be shifting leftward on a per capita<br />

basis, meaning that rice market prices may not rise enough to<br />

increase production. Instead, rice production in Asian countries<br />

may decrease in the future as revealed in Japan and Taiwan<br />

(China) as well as recently in China.<br />

Because the power of declining PCRC is so strong, even<br />

a modeling technique should change from a market-oriented<br />

equilibrium to a consumption-derived supply model. In fact,<br />

t<strong>here</strong> are strong indications that rice consumption is not influenced<br />

much by lower rice prices, although higher rice prices<br />

tend to affect rice consumption like the example in Japan reported<br />

by Asahi Newspaper. For any estimate of the rice equilibrium<br />

model for Asian nations, it is important to develop a<br />

reasonable rice consumption model.<br />

Chinese PCRC is currently at 105 kg and is declining at<br />

approximately 0.5% annually, while the declining rates for Japan<br />

and Taiwan for the last 45 years are approximately 1.8%<br />

and 3.5%, respectively. While the FAPRI (2004) estimates rice<br />

demand and supply for the next decade or so, some researchers<br />

forecast for China with three scenarios for the next five<br />

decades using declining rates of 0.33%, a current rate of 1.77%<br />

applying the Japanese rate, and 3.45% applying the Taiwanese<br />

rate. According to the results, by 2050 Chinese PCRC would<br />

become 90.0, 46.0, and 20.8 kg with the three rates, respectively.<br />

The total rice consumption of China in 2050 would be<br />

estimated at 127 million, 65 million, and 30 million mt, respectively,<br />

with the three decreasing rate scenarios vis-à-vis<br />

the current 135 million mt. Together with other nations’ declining<br />

PCRC, total rice consumption in the world in 2050<br />

would increase to only 525 million, 463 million, and 427 million<br />

mt, respectively, in comparison with the current level of<br />

412 million mt, using the population estimated by the United<br />

Nations (2003) to increase to 9 billion by 2050 (Fig. 2).<br />

Conclusions<br />

<strong>Rice</strong> in Asia is the basis for food, culture, and the economy.<br />

Declining per capita rice consumption in Asia would eventually<br />

lead to a decline in rice production. Since rice is the major<br />

crop in Asia, downsizing in rice production would mean a loss<br />

of agricultural competitiveness as well as less value of assets<br />

and resources. Asian people heavily depend on agriculture for<br />

household income. Weak agriculture would create more unemployed<br />

people and more poverty. The Asian food culture,<br />

which is based on rice, would also lose ground inside and outside<br />

Asia. All these losses would be tremendous in Asia.<br />

Session 17: <strong>Rice</strong> supply and demand 495


1,000 mt<br />

600,000<br />

500,000<br />

World (China rate –0.331%<br />

World (China rate –3.452%<br />

World (China rate –1.77%<br />

400,000<br />

300,000<br />

200,000<br />

100,000<br />

0<br />

1960<br />

1963<br />

1966<br />

1969<br />

1972<br />

1975<br />

1978<br />

1981<br />

1984<br />

1987<br />

1990<br />

1993<br />

1996<br />

1999<br />

2002<br />

2005<br />

2008<br />

2011<br />

2014<br />

2017<br />

2020<br />

2023<br />

2026<br />

2029<br />

2032<br />

2035<br />

2038<br />

2041<br />

2044<br />

2047<br />

2050<br />

Year<br />

Fig. 2. World rice total consumption, 1960-2050.<br />

While rice is the major agricultural crop and the major<br />

source of income and calories for most of the Asian people,<br />

less production of rice with weak demand would mean that<br />

Asian people would have a less competitive agriculture relative<br />

to that of other regions in the world and more serious environmental<br />

and poverty problems in Asian rural areas. This is<br />

a critical problem not only for Asian agriculture but also for<br />

any rice producer in the world.<br />

It is t<strong>here</strong>fore important for Asian nations to cooperate<br />

among themselves and cope with the declining per capita rice<br />

consumption. While more human consumption as table food<br />

should be promoted, more diversified use of rice should be<br />

explored even more.<br />

Note: All the data for rice are on the milled basis provided originally<br />

from the U.S. Department of Agriculture. The World Food Statistics<br />

& Graphics (by Ito, http://worldfood.muses.tottori-u.ac.jp) is designed<br />

using the USDA’s PS&D Online data set.<br />

References<br />

Asahi Newspaper: <strong>Rice</strong> consumption declining consecutively for 9<br />

months, 9 June 2004.<br />

FAPRI (Food and Agriculture Policy <strong>Research</strong> <strong>Institute</strong>). 2004.<br />

FAPRI world agricultural outlook 2004: world rice,<br />

www.fapri.iastate.edu/Outlook2004/PageMker/<br />

9_Wld<strong>Rice</strong>.pdf.<br />

Ito S, Wesley E, Peterson F, Grant W. 1989. <strong>Rice</strong> in Asia: is it becoming<br />

an inferior good Am. J. Agric. Econ. 71:32-42.<br />

Ito S. World food statistics and graphics, September 2004: http://<br />

worldfood.muses.tottori-u.ac.jp.<br />

United Nations. 2003. United Nations Expert Meeting on World<br />

Population in 2003, Department of Economic and Social Affairs,<br />

Population Division New York, 9 December 2003,<br />

www.un.org/esa/population/publications/longrange2/<br />

longrange2.htm.<br />

USDA (U.S. Department of Agriculture). 2004. PS&D Online, September<br />

2004: www.fas.usda.gov/psd/complete_files/<br />

default.asp.<br />

Notes<br />

Author’s address: Tottori University, Japan, e-mail:<br />

sito@muses.tottori-u.ac.jp.<br />

496 <strong>Rice</strong> is life: scientific perspectives for the 21st century


<strong>Rice</strong> consumption in China: Can China change<br />

rice consumption from quantity to quality<br />

Chien Hsiaoping<br />

<strong>Rice</strong> is the most important crop in China, with the highest level<br />

of production. China’s rice production accounts for 28% of<br />

the world’s total production. China produced 161 million tons<br />

of rice in 2003, but this figure is relatively low compared with<br />

past years. The rice grown in China consists of indica and<br />

japonica varieties. In general, indica varieties are produced<br />

mainly in the south. Landraces of japonica are produced in the<br />

north on the lower reaches of the Chang Jiang River, and improved<br />

varieties of japonica that originated from Japanese rice<br />

are cultivated mainly in the northeast. In recent years, japonica<br />

varieties have increased rapidly, accounting for 26% of the<br />

total production, w<strong>here</strong>as indica varieties account for nearly<br />

70%.<br />

In China, rice has been consumed since ancient times.<br />

The main staple food in China has been either rice or wheat,<br />

depending on the suitability of local environments for cultivation<br />

and the diversity of races and eating habits. Because of<br />

migration between the southern and northern regions, rice consumption<br />

is now seen all over the country. It is currently considered<br />

that 840 million people (65% of the total population)<br />

eat rice as a staple food. The nationwide per capita rice supply<br />

has dropped slightly since 1984, when it peaked at 99 kg, to<br />

91 kg in 2000.<br />

Trends of rice consumption<br />

Although per capita rice consumption in China is a statistical<br />

matter and precise figures have not been obtained, recent documents<br />

(based on the food balance sheet) issued by the Chinese<br />

Ministry of Agriculture indicate that polished rice consumption<br />

is in the 90-kg range. This figure is considerably higher<br />

than that in Japan (65 kg in 1999). Based on a recent food<br />

balance sheet for rice (by crop years), 85% of total demand<br />

was for food consumption (Fig. 1). In addition, yearly seed<br />

demand has remained at 1.5 to 1.6 million tons, w<strong>here</strong>as demand<br />

for rice for industrial processing has increased slightly<br />

to 1.8 million tons (2001-02). T<strong>here</strong> is a significant loss during<br />

distribution and storage, but the total loss has decreased to<br />

some extent for four years (from about 8 million to about 7<br />

million tons). Feed demand has increased for four years. Its<br />

share of total demand has increased from 4% to 6%, and consumption<br />

of rice as animal feed has reached nearly 8 million<br />

tons. Under the current situation, future rice demand will be<br />

determined by the rate of decrease in rice consumption and<br />

the trend of population increase.<br />

Direct consumption accounted for more than 90% of total<br />

rice demand at the beginning of the 1970s. Since the latter half<br />

of the 1970s, it has started to decrease because of the increase<br />

%<br />

100<br />

80<br />

60<br />

40<br />

20<br />

0<br />

1998-99<br />

1999-2000<br />

Years<br />

2000-01<br />

2000-02<br />

Export<br />

Loss<br />

Processing<br />

Feed<br />

Seed<br />

Food<br />

Fig. 1. Share of rice demand. Source: www.agri.org.cn/<br />

analysis/include/4/dmjs.htm, 2002 China agricultural<br />

development report.<br />

in choice of other dietary options and increased consumption<br />

of meat and other foods. According to statistics on rice purchases<br />

in urban areas, direct rice consumption peaked in the<br />

mid-1980s, and per capita rice consumption (not including consumption<br />

at restaurants) has decreased ever since. In 2000, it<br />

was 46 kg, a decrease of 12% from 1995 figures. In rural areas,<br />

as estimated from the total consumption of rice and wheat,<br />

direct rice consumption has decreased slightly (90 kg in 1995<br />

to 89 kg in 2000). However, the quantitative difference in consumption<br />

between urban and rural areas is still significant.<br />

Increased income and rice consumption<br />

In general, changes in rice consumption are influenced by consumer<br />

income and price. However, price data on rice are insufficient,<br />

and rice prices have been under the control of the<br />

government for a long time because of the importance of rice<br />

as a staple. In this section, we analyze the relationship between<br />

income and consumption of rice and other foods.<br />

We obtained details of income elasticities in the 1980s<br />

and 1990s from data published by the State Statistics Bureau.<br />

Income elasticity of rice in urban areas has had negative values<br />

since the 1980s, indicating that rice is now seen as an inferior<br />

commodity in these areas (Table 1). On the other hand, in<br />

the 1980s, the income elasticity of rice in rural areas was 0.15<br />

(meaning that when income increases by 10%, rice consumption<br />

rises by 1.5%), demonstrating that rice was still a valued<br />

Session 17: <strong>Rice</strong> supply and demand 497


Table 1. Income elasticity in staple foods. a<br />

Food<br />

Urban area<br />

Rural area<br />

1981-91 1992-2000 1981-91 1992-2000<br />

<strong>Rice</strong> –0.27 –0.35 0.15 –0.16<br />

Vegetable oil 0.42 0.33 0.97 0.59<br />

Pork 0.17 –0.18 0.44 0.55<br />

Beef/mutton 1.39 (0.03) 0.43 1.23<br />

Poultry 1.43 0.40 0.97 1.59<br />

Eggs 0.53 0.58 1.07 1.36<br />

Marine products (0.06) 0.51 0.79 1.14<br />

a Numbers in parentheses indicate poor statistical fit.<br />

commodity. However, in the 1990s, income elasticity of rice<br />

in rural areas developed negative values, and rice consumption,<br />

as in urban areas, showed a downward tendency despite<br />

increased income.<br />

Food diversification was a factor in this decrease in rice<br />

consumption, and increased consumption of livestock products<br />

is considered to be an influencing factor. For the income<br />

elasticities of all stock farm products and vegetable oil (except<br />

pork in the 1990s), positive values were observed and<br />

t<strong>here</strong> was an upward tendency with increasing income, although<br />

the extent of each fluctuation was different. In urban areas, the<br />

income elasticities of livestock products were high in the 1980s.<br />

However, the elasticities declined in the 1990s, and pork in<br />

particular showed negative values, indicating decreasing consumption.<br />

We consider that these trends reflect the recent emergence<br />

of health-conscious attitudes toward lifestyle in urban<br />

China. In contrast, unlike the trend in urban areas, elasticities<br />

in rural areas showed positive values. A comparison of values<br />

in the 1980s and 1990s revealed that the elasticities of livestock<br />

products (except vegetable oil) in the 1990s were higher<br />

than those in the 1980s. Values for beef and mutton, poultry,<br />

eggs, and marine products were greater than 1, indicating that<br />

these products were regarded as superior goods. Income elasticity<br />

of pork in rural areas also increased, and a further increase<br />

in consumption because of rising income is expected.<br />

From our analysis of the fluctuations in income elasticities in<br />

urban and rural areas between the two periods, we strongly<br />

expect that consumption of livestock products will increase in<br />

the future owing to rises in the income of the rural population<br />

of 800 million.<br />

Analysis of the patterns of consumption of staple foods<br />

by income group revealed that, in urban areas, rice was mainly<br />

consumed as a staple food. The higher the income was, the<br />

lower the consumption of rice became. Compared with rice,<br />

wheat was more likely to be consumed as a processed food.<br />

We focused on unfilled buns and bread, which were the processed<br />

wheat products consumed most often. Consumption of<br />

processed foods such as buns and bread increased as income<br />

rose, w<strong>here</strong>as consumption of strong and plain flour decreased<br />

as income rose. We tried to obtain a simple regression model<br />

that related income and consumption of various foods. Income<br />

elasticities of rice by low-, middle-, and high-income groups<br />

were –0.85, –0.60, and –0.64, respectively; rice was an inferior<br />

commodity for all groups. For bread, income elasticity<br />

values were elastic in the middle- and high-income groups (1.15<br />

and 0.87, respectively). For traditional buns, high income elasticities<br />

were demonstrated in the low-, middle-, and high-income<br />

groups (2.16, 1.26, and 0.90, respectively). Because of<br />

their lower prices compared with those of other processed<br />

foods, traditional processed foods enjoy a high demand and<br />

are thus regarded as increasingly superior as income becomes<br />

lower. In the middle- and high-income groups, increased consumption<br />

of Western-style foods such as bread was caused by<br />

a rise in income. On the basis of trends in the purchase of main<br />

foods in restaurants and office dining rooms, we obtained significant<br />

elastic values for processed foods in the middle- and<br />

high-income groups. T<strong>here</strong>fore, it was evident that preferences<br />

for processed foods that could save consumers the trouble of<br />

cooking increased as income rose.<br />

Also, consumption of livestock products increased as<br />

income increased. Breakfast for households in urban areas<br />

tended to become a meal consumed out. In addition, many<br />

two-income families were characterized by their tendency to<br />

eat out for lunch. However, with the exception of rice, t<strong>here</strong><br />

were no precise statistical data on the consumption of different<br />

styles of food eaten out. T<strong>here</strong>fore, we considered that the<br />

actual amounts consumed in urban areas might be greater than<br />

those shown in the statistical data obtained.<br />

Conclusions<br />

We have reviewed the influence of eating habits and income<br />

on rice consumption, but t<strong>here</strong> is another influencing factor:<br />

population. In China, which currently has about 1.3 billion<br />

people, increased rice consumption because of population<br />

growth is expected because the population has been increasing<br />

by nearly 10 million a year, even though the growth rate is<br />

less than 1%. In addition, t<strong>here</strong> has been a change from quantity<br />

to quality in terms of consumer demand for rice. The main<br />

factors driving this change in demand are an improvement in<br />

the quality of indica rice by establishing a market for brand<br />

rice, a shift in consumption from indica to japonica rice, and<br />

the migration of people from rural to urban areas because of<br />

urbanization. We consider that these trends will not change<br />

significantly in the future because rice is a highly self-sufficient<br />

crop in China. In recent years, t<strong>here</strong> have been trends<br />

toward decreased rice consumption because of increased diversity<br />

of eating habits, increased demand for high-quality rice,<br />

and increased sophistication of foods. We have also confirmed<br />

that demand has increased for japonica rice. The supply of<br />

rice with improved quality and the production of rice crops<br />

with a high degree of self-sufficiency are goals for rice consumption<br />

in China.<br />

498 <strong>Rice</strong> is life: scientific perspectives for the 21st century


References<br />

Chien HP. 2003. <strong>Rice</strong> consumption in China. Agric. Econ. 69:5-12.<br />

Ministry of Agriculture. 2004. 2003 China agricultural statistical<br />

material. Beijing (China): China Agriculture Press.<br />

Sawada M. 1986. The effects of prices, income and household characteristics<br />

on food demand: a demand system approach. J.<br />

Rural Econ. 57(4):229-239.<br />

Wang ML. 2004. On the economy of japonica rice in China. Issues<br />

Agric. Econ. 2004(4):35-39.<br />

Notes<br />

Author’s address: <strong>Research</strong> Information Division, Japan <strong>International</strong><br />

<strong>Research</strong> Center for Agricultural Sciences (JIRCAS), e-mail:<br />

chienp@jircas.affrc.go.jp.<br />

Surplus rice supply in Asia<br />

Vichai Sriprasert<br />

Asia has long been dominant in rice production, consumption,<br />

and trade. More than 92% of world rice production, 90% of<br />

rice consumption, and 75% of rice surplus for exports are in<br />

Asia. The abundant rice supply in Asia explains why 60% of<br />

the world’s six billion people are concentrated in Asia. Will<br />

this picture change in the future<br />

Determinants<br />

<strong>Rice</strong> supply is determined by both natural endowments and<br />

human factors. Water, fertile soil, sunlight, and suitable temperature<br />

are prerequisites for growing rice. Human factors<br />

could include particular government policies on free trade versus<br />

government control, investments in infrastructure in irrigation<br />

and transportation, and emphasis on technology, for<br />

example, genetic engineering or traditional biotechnology. Both<br />

natural and human factors can have a tremendous effect on<br />

producing rice surpluses or deficits. Population density or human-land<br />

ratios can also become an overriding determinant.<br />

Origins<br />

Even though the definitive origins of rice have yet to be established,<br />

it is quite reasonable to believe that rice originated in<br />

Asia. The shear sizes of the Asian population and rice production<br />

today are good testimonies that rice must have started<br />

somew<strong>here</strong> in Asia. Remains of rice plants from 10,000 B.C.<br />

were discovered in Spirit Cave on the Thailand-Myanmar border.<br />

<strong>Rice</strong> and farming implements dating back at least 8,000<br />

years have been found along the Yangtze River in China. <strong>Rice</strong><br />

production outside of Asia constitutes only one-ninth of that in<br />

Asia. Because of the crop’s origins in Asia, rice production,<br />

consumption, and trade are all concentrated in Asia.<br />

Trade<br />

<strong>International</strong> trade in rice, in the modern era, started to develop<br />

about 150 years ago in Southeast Asia. The West, particularly<br />

the British, extended its colonial campaign with trade<br />

and threats in the East around the mid-1800s. China lost Hong<br />

Kong to the British after a humiliating defeat in the Opium<br />

War. Hong Kong was supposedly on a long-term lease, but the<br />

British never did pay any rent to China over 155 years (from<br />

1842 to 1997). India also lost its independence in 1857 after<br />

conflicts with East India Company. The U.S. naval officer<br />

Matthew C. Perry forced Japan to trade with the West in 1854.<br />

Next, the British annexed Burma (now Myanmar) in the<br />

west, and forced Thailand to open up for trade, particularly in<br />

rice. The French controlled Vietnam and Cambodia to the east.<br />

The British invested heavily in irrigation and transportation in<br />

Burma, while the French did the same in Indochina. Thailand<br />

also invested a moderate amount in similar infrastructure. Indians<br />

poured into Burma, while the Chinese immigrated into<br />

Vietnam and Thailand. <strong>Rice</strong> production in excess of the domestic<br />

requirement was stimulated by new demand for international<br />

trade. Immigrant entrepreneurs brought in their trading<br />

and managerial skills together with their initial capital. The<br />

British and the Indians helped Burma to export rice to Europe,<br />

India, and Sri Lanka, while the Chinese helped Thailand and<br />

Vietnam to export to Hong Kong and Singapore, and the Vietnamese<br />

were expanding exports to Indonesia and the Philippines.<br />

The rice economy of Southeast Asia flourished despite<br />

fears that foreigners would exploit their countries. Prior to the<br />

Second World War, Burma managed to export more than 3<br />

million tons annually. Thailand and Vietnam took turns being<br />

the second- or third-largest exporters at around 1 million tons.<br />

Foreign exploitation did indeed turn out to be a blessing in<br />

disguise.<br />

Economic systems<br />

Nationalism and independence gained after the Second World<br />

War did not help Burma to continue producing huge rice surpluses<br />

for export as when the country was operating under a<br />

market economy during the long period of British rule.<br />

<strong>Rice</strong> exports reached 2.1 million tons as early as 1900,<br />

and peaked at 3.4 million tons in 1934. In 1948, the year of the<br />

Session 17: <strong>Rice</strong> supply and demand 499


country’s complete independence, rice exports dropped to 1.2<br />

million tons. After 1965, rice exports stayed below 1 million<br />

tons for most years until today.<br />

The ravages of the Second World War, and the adoption<br />

of socialism, that is, nationalizing everything, including the<br />

rice sector, together with a policy to keep rice prices very low,<br />

destroyed farmers’ incentives to produce surplus rice for export.<br />

Similar changes from a market economy to a centrally<br />

planned economy occurred in Vietnam after the Second World<br />

War, and the country suffered the same consequences: rice<br />

exports dissipated and the country became a large rice importer<br />

of 1 million tons instead in 1969. However, Vietnam<br />

was quick to change toward a more market economy in 1986<br />

under the Doi Moi (renovation policy). In a few years, Vietnam<br />

became the second-largest rice exporter after Thailand.<br />

Unlike Burma and Vietnam, Thailand started out with a<br />

free market economy and keeps the same system today. Thailand<br />

surpassed both Vietnam and Burma and emerged as the<br />

world’s largest rice exporter for more than two decades in a<br />

row. From 1966 to 1982, the U.S. and Thailand took turns<br />

being the largest rice exporter, but China on some occasions<br />

also occupied the top position.<br />

Pressure from population density<br />

<strong>Rice</strong> exporters are countries that are generally endowed with<br />

favorable human-land ratios; they also must have a proper<br />

economic system that provides enough incentives for rice producers.<br />

Population density per km 2 for the major rice exporters<br />

discussed <strong>here</strong> are Myanmar (62), Thailand (121), and Vietnam<br />

(246). In contrast, traditional rice importers prior to the<br />

Second World War with their respective population density<br />

were Hong Kong (6,688), Singapore (6,430), Bangladesh<br />

(926), Taiwan (627), South Korea (491), Japan (336), India<br />

(318), Sri Lanka (298), the Philippines (282), China (134),<br />

and Indonesia (121).<br />

The importers that have limited land to support a large<br />

population must overcome their scarce natural endowments<br />

with technology and management. Japan, China, and India are<br />

good examples of success stories.<br />

Japan<br />

<strong>Rice</strong> imports into Japan reached 1.4 million tons in 1919 and<br />

2.3 million tons in 1938, and then declined to 1.1 million tons<br />

in 1943 and less than 1 million tons since 1956 onward. Up<br />

until 1945, Japan promoted rice production and imported<br />

mostly from its two colonies, Korea and Taiwan. <strong>Rice</strong> consumption<br />

in Japan peaked in 1962 at 118 kg per capita, but is<br />

only 61 kg per capita now. Japan has always emphasized high<br />

technology and high rice prices to their producers and at the<br />

same time tightly controlled rice production, imports, and distribution.<br />

This self-sufficiency policy has been so successful<br />

that Japan today is in the process of deregulating the rice industry<br />

and using about US$3 billion a year to reduce rice growing<br />

and allow more market forces to determine rice prices and<br />

distribution. Nonetheless, Japan is among the pioneers in rice<br />

genomic research together with China and the U.S. Field yields<br />

and milling yields for rice are among the highest in the world.<br />

But the policy to keep high rice prices for farmers precludes<br />

Japan from becoming a major rice exporter because Japanese<br />

rice was 13 times higher in price than U.S. rice in 2000.<br />

China<br />

China has a population of 1.3 billion to feed, the largest in the<br />

world. The famous Yellow River has run dry nearly every year<br />

since 1972. Because of population pressure, the government<br />

has managed to stay at the frontier of knowledge in rice production.<br />

China had a parallel development of its own during<br />

the Green Revolution. It led the world in hybrid rice, and now<br />

keeps abreast of rice genomics and genetic engineering. Its<br />

average field yield of 6.2 t ha –1 is way above the world’s average<br />

yield of 3.9 t ha –1 .<br />

In 1923, China’s rice imports reached 1.4 million tons;<br />

by 1956, it could export 1.1 million tons. In 1973, it exported<br />

2.6 million tons, and by 2000 exported 3.1 million tons. A few<br />

times in the 1960s and 1970s, China was the largest rice exporter<br />

in the world.<br />

India<br />

India used to import a lot of rice: 2.5 million tons in 1915, 3.7<br />

million tons in 1919, a peak of 4.4 million tons in 1934, and a<br />

gradual drop to 1 million tons in 1941. India became self-sufficient<br />

in 1977. Exports increased from 0.09 million tons in<br />

1994 to 4.9 million tons in 1995 and 6.7 million tons in 2002.<br />

Technology and the market economy are the key<br />

The world was not comfortable with food security in the early<br />

1960s as rice production could not catch up with population<br />

growth. Like a miracle, <strong>IRRI</strong> introduced high-yielding varieties,<br />

which were of short maturity, and two to three crops could<br />

be planted in a year. These varieties were also responsive to<br />

fertilizer. That scientific breakthrough was called the Green<br />

Revolution. A food crisis has been averted up until today. However,<br />

the growth of rice production seems to have leveled off<br />

and again t<strong>here</strong> is concern that population may outgrow rice<br />

production in the decades ahead. In the last few years, production<br />

has been running behind consumption. This situation must<br />

be corrected because it cannot be sustained.<br />

The Green Revolution helped farmers to grow more rice<br />

and real prices t<strong>here</strong>fore came down. Roughly, from 1953 to<br />

1999, rice production increased threefold, but prices dropped<br />

to one-fourth of those of the beginning period.<br />

Under such circumstances, a few observations are worth<br />

pointing out. Asia and Oceania’s shares of rice imports decreased<br />

from 69% in 1961 to 38% in 2002. This implies that<br />

those Asian importers became more self-sufficient and needed<br />

to import less.<br />

On the other hand, Asian exporters increased their shares<br />

from 70% to 75% during the same period. However, poor<br />

500 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Burmese farmers, even with limited alternatives, did not produce<br />

any more rice for export. In contrast, its neighbor farmers<br />

in Thailand and Vietnam, under a market economy, were<br />

motivated to grow more and more.<br />

Will Asia continue to provide rice surpluses<br />

If we look at Thailand as a case study, we can come up with<br />

some interesting insights. First of all, Thailand enjoys the most<br />

favorable human-land ratio. Second, the farmers are very skillful<br />

in growing rice; they can do the best with what little they<br />

have, and survive. Third, the traders, millers, and exporters<br />

who are serving the farmers are also very skillful and competitive.<br />

They are willing to buy and sell rice even without a margin.<br />

T<strong>here</strong> are plenty of such traders around, but they do not<br />

get any recognition for such a good deed. Society seems to<br />

prefer traders that charge high fees for their services! Fourth,<br />

Thai bankers are willing to finance such a competitive rice<br />

business, which has a good track record on paying interest.<br />

The principal has seldom, if ever, been recalled.<br />

Since all the major players (farmers, millers, and exporters)<br />

are all very lean, the rice industry just grows faster and<br />

faster. <strong>Rice</strong> has been freely exported from Thailand for about<br />

150 years. It took the first 125 years to reach an annual export<br />

level of only 2 million tons. The level of 5 million tons took<br />

only 25 years. The export pace for each additional 1 million<br />

tons became shorter and shorter, from over 60 years to 5 and<br />

now moving toward about 1 year! Our annual rice exports are<br />

likely to jump from 7 to 9 million tons in just four years at the<br />

end of 2004! This is a miracle of the free market.<br />

This outstanding export performance was achieved under<br />

some very unfavorable circumstances. Thai field yields<br />

are the lowest among all our competitors. Our government is<br />

intervening in the market to raise paddy prices, while India is<br />

poised to provide a rice export subsidy again. Japan, the EU,<br />

and the U.S. continue to provide heavy domestic support to<br />

their rice farmers.<br />

If Thailand were to have the same percentage of irrigation<br />

area as China or Japan, our field yields would be twoand-a-half<br />

times more than what they are today. Thailand alone<br />

can meet global rice imports! Do we have enough water to get<br />

the job done Yes, if we can obtain some water from the<br />

Salween River, which simply flows to the sea without being<br />

used much by anyone.<br />

The Green Revolution got the world out of the food crisis of<br />

the 1960s. Biotechnology, particularly genetic engineering, may<br />

change the landscape that we can see today. It is entirely possible<br />

that genetically engineered rice seeds will thrive in Africa,<br />

w<strong>here</strong> the population and rice imports have been growing<br />

faster than in any other regions in the world. Africa’s share<br />

of the world population jumped from 9% in 1950 to 13% in<br />

2000 and is projected to reach 20% in 2050. Africa’s share of<br />

world rice imports was only 8% in 1961; it became 25% in<br />

2002.<br />

Just take Nigeria as an example. Its population is 120<br />

million. <strong>Rice</strong> consumption per capita is only 23 kg versus 58<br />

kg for the average world consumption. Annual rice imports<br />

are about the same as the domestic production of 2 million<br />

tons of milled rice. The f.o.b. per metric ton of Thai 100%<br />

parboiled is about US$265, freight to Lagos is $85, and the<br />

import duty is in excess of 100% of cost and freight. That means<br />

that any rice produced locally will have an advantage or price<br />

protection against imported rice of ($265 + $85) + $85 = $435<br />

per metric ton! Under normal circumstances as in Thailand,<br />

rice production and the rice industry in Nigeria ought to explode!<br />

Asia, and particularly Thailand, will continue to generate<br />

rice exports to Africa only because Africa does not take<br />

advantage of its potential to substitute rice imports.<br />

Myanmar can regain her prewar prominence in rice similar<br />

to what Vietnam did. It is the miracle of the free market<br />

economy that Myanmar must turn to eventually to prevail.<br />

The warming of Earth may hurt rice yields and reduce<br />

Asian rice area in the vast lowland delta areas because of higher<br />

sea levels. However, advances in biotechnology, particularly<br />

in genomics, may overcome many if not all of the constraints<br />

we are aware of today. Together with freer trade in the world,<br />

if it ever really comes to fruit, rice production and trade will<br />

also change much beyond our imagination. It is quite certain<br />

that under a recurring of the oil crisis, more crops will be grown<br />

for the production of gasohol in competition with grain grown<br />

for food.<br />

Notes<br />

Author’s address: President of <strong>Rice</strong> Exporters Association (Thailand),<br />

e-mail: <strong>Rice</strong>land@<strong>Rice</strong>sources.com.<br />

Acknowledgments: Various facts and statistics are from the following<br />

sources: U.S. Bureau of the Census, <strong>International</strong> Data<br />

Base: FAOSTAT; <strong>Rice</strong> almanac, <strong>IRRI</strong> 2002; The economy of<br />

Asia: R. Barker, R.W. Herdt and B. Rose, 1985; The rice<br />

economy of monsoon Asia: V.C. Wickizer and M.K. Bennett,<br />

1921.<br />

Any surprises<br />

Session 17: <strong>Rice</strong> supply and demand 501


Review of existing global rice market models<br />

Eric J. Wailes<br />

Numerous models of the global rice market have been developed<br />

and are used by university and governmental organizations<br />

and agencies. This paper discusses several of the key<br />

model frameworks for which documentation and projections<br />

exist. An overview of the various models in terms of type and<br />

scope is presented. Comparisons are made in terms of model<br />

structure and differences in the baseline development process,<br />

model output, and projections. Differences in country/regional<br />

coverage, product disaggregation, time period of projections,<br />

and the purpose of the various models are noted. The challenges<br />

and prospects for improving quantitative modeling of<br />

the global rice economy are discussed.<br />

The need for quantitative models<br />

Quantitative models of the world rice market are needed for<br />

three alternative analytical needs (Liu and Seeley 1987). First,<br />

we need models to use for short-term impact analysis. These<br />

short-term models must be relatively flexible to address issuespecific<br />

policy and market questions, since we never know in<br />

advance what the particular problem, policy, or market issue<br />

will be. Second, we need models that are capable of intermediate-term<br />

production, consumption, trade, and price forecasting.<br />

Ideally, these models should be multicommodity and capable<br />

of accounting for substitution effects. It is also extremely<br />

useful if t<strong>here</strong> is a spatial dimension that can account for trade<br />

flows. The third use we make of market trade models is for<br />

longer-term policy analysis. The longer-term models typically<br />

are used to generate baseline projections against which policy<br />

alternatives can be compared. Typically, the longer-term models<br />

are multicommodity and have a time horizon of ten years<br />

or longer for the projection period. They tend to be more complex<br />

and useful for generating analyses that evaluate changes<br />

in market structure and policy regimes. Most of these models<br />

are partial equilibrium that focus on a broad set of commodities<br />

and countries but take as exogenous variables income,<br />

exchange rates, interest rates, employment, and other factor<br />

markets. Computable general equilibrium (CGE) models such<br />

as the Global Trade Analysis Project (GTAP) have been used<br />

extensively by the World Bank and the WTO Secretariat for<br />

analyses of the Uruguay Round and more recently of the Millennium<br />

(Doha) Round of WTO negotiations (Hertel 1997,<br />

World Bank 2003). The macro variables and factor markets<br />

are endogenized in the CGE model framework. However, because<br />

of the large data and parameter requirements of the GTAP<br />

model and other CGE frameworks, t<strong>here</strong> is considerable sacrifice<br />

in terms of reflecting current market and policy conditions.<br />

At present, the GTAP model is based on 1997 data and<br />

will be updated to 2001 data only by spring 2005.<br />

Overview of quantitative models<br />

This paper will discuss primarily the third longer-term category<br />

of partial equilibrium quantitative models. Models of<br />

the third type, which are widely recognized, include the World<br />

Food Model (WFM) of FAO, the IMPACT model of the <strong>International</strong><br />

Food Policy <strong>Research</strong> <strong>Institute</strong> (IFPRI), the AGLINK<br />

model of the Organization for Economic Cooperation and<br />

Development (OECD), the Country-Commodity Linked System<br />

(CCLS) of the United States Department of Agriculture<br />

(USDA), and the Food and Agricultural Policy <strong>Research</strong> <strong>Institute</strong><br />

(FAPRI) model of a consortium of U.S. universities.<br />

The FAO WFM is no longer maintained. The WFM was<br />

a large multicommodity and multicountry model used to examine<br />

resource, policy, and market issues. Currently, within<br />

FAO, two global modeling efforts are in a developmental process,<br />

including the @2030 model, which is more aggregated<br />

by country/region than the previous World Food Model (FAO<br />

2003). The second modeling effort within FAO is known as<br />

COSIMO, which will be a multicommodity, multicountry model<br />

based on the OECD AGLINK framework but with much greater<br />

disaggregation by countries. The IMPACT model maintained<br />

by IFPRI is an analytical framework used to examine alternative<br />

scenarios for global food demand, supply, and trade. IM-<br />

PACT covers 16 commodities, including rice, and covers 36<br />

countries and regions, accounting for essentially all of the<br />

world’s food production and consumption. It is structured as a<br />

set of country or regional submodels that are linked through<br />

trade and world reference prices that clear international markets.<br />

Unlike the @2030 and IMPACT models, the AGLINK,<br />

CCLS, and FAPRI models are updated at least annually through<br />

a process known as a reference scenario or baseline exercise,<br />

which is then published annually by each of the respective institutions<br />

as a 10-year global agricultural outlook. In this paper,<br />

comparisons of the AGLINK, CCLS, and FAPRI rice<br />

models are made first by providing a brief description of each<br />

model with respect to model type, scope, model structure, and<br />

reference scenario development, including the use of extramodel<br />

information. This is followed by some comparisons of<br />

output and projections. Finally, challenges and prospects for<br />

improving quantitative global rice modeling frameworks will<br />

be discussed.<br />

The AGLINK model maintained by the OECD is a set<br />

of country modules of OECD member nations and selected<br />

nonmember nations. As such, the model links the country modules<br />

through trade and international reference prices. The rice<br />

component of each country model t<strong>here</strong>fore constitutes the basis<br />

for representation of the global rice model. Country models<br />

include major rice importers and exporters among the OECD<br />

502 <strong>Rice</strong> is life: scientific perspectives for the 21st century


members. Non-OECD member models for rice are maintained<br />

for other major rice importers and exporters. The international<br />

reference rice price is the Thai 100%B long-grain price. The<br />

model aggregates rice trade across quality and types and is<br />

nonspatial. Domestic rice prices are specified through price<br />

transmission equations. The model is dynamic and policy-specific<br />

with respect to domestic support and trade interventions.<br />

The model structure is based on an elasticities framework. The<br />

reference scenario (baseline) projection process is initiated<br />

annually with a questionnaire sent to member and nonmember<br />

nations to obtain updated data and policy information. This<br />

provides an empirical basis to evaluate an initial baseline developed<br />

by the Secretariat. Revisions are made and then submitted<br />

for review to the Working Party on Cereals. This baseline<br />

is next evaluated for sensitivity to key macro and policy assumptions<br />

and finally is presented as a preliminary outlook<br />

draft for consideration by the Working Party on Agricultural<br />

Policies and Markets of the Committee for Agriculture. This<br />

iterative review process implies that the final baseline projections<br />

are heavily conditioned by representatives from member<br />

and participating nonmember nations. The review process ensures<br />

that the final estimates reflect the input of the country<br />

and commodity experts; however, the Secretariat takes full<br />

responsibility for the final published baseline projections<br />

(OECD 2004).<br />

The USDA Country-Commodity Linked System (CCLS)<br />

is maintained at the Economic <strong>Research</strong> Service. This framework<br />

includes a set of 42 foreign country or regional models<br />

and the Food and Agriculture Policy Simulator (FAPSIM)<br />

model of U.S. agriculture. The country models estimate production,<br />

consumption, stocks, and prices. Country models are<br />

integrated through trade and international reference prices<br />

through the LINKER module. The country models are dynamic<br />

and reflect policies and institutional behavior such as tariffs,<br />

subsidies, and trade restrictions. A rest-of-the-world model<br />

handles any excluded country-commodity coverage.<br />

The country models are structured to account, w<strong>here</strong><br />

appropriate, for both imports and exports of a given commodity.<br />

The international reference price is the Thai 100%B longgrain<br />

price. The trade framework aggregates rice across quality<br />

and types and is nonspatial. The baseline is generated<br />

through a Delphi approach, similar to the AGLINK process.<br />

As such, the projections reflect the composite of model results<br />

and judgment-based analysis by country and commodity specialists<br />

(USDA 2004).<br />

The Arkansas Global <strong>Rice</strong> Model (AGRM) is the international<br />

rice model framework used in the FAPRI baseline<br />

and is maintained at the University of Arkansas. The AGRM is<br />

based on a multicountry econometric framework. The country<br />

models consist of a supply sector, a demand sector, and a set<br />

of trade and price linkage equations. All these equations are<br />

estimated using econometric techniques. The model is dynamic<br />

and nonspatial in trade. Individual country models are then<br />

linked through net trade—a specification that highlights the<br />

interdependence of countries in the world rice economy.<br />

Simulation is conducted for the purpose of the baseline<br />

projection and policy analysis. The Thai long-grain price is<br />

used to clear the international long-grain rice market and the<br />

California ex-mill medium-grain price is used to clear the international<br />

medium-/short-grain rice market. Projections include<br />

national levels of production (area harvested and yields),<br />

consumption, net trade, stocks, and prices.<br />

Government interventions to the extent possible are explicitly<br />

reflected in the model’s structure. These policies are<br />

incorporated in the model’s supply, demand, export (or import),<br />

stocks, and price transmission equations, and are thus<br />

implicitly reflected in the model solution. Major importing and<br />

exporting countries or regions are explicitly included in the<br />

AGRM model. All other countries are included in the rest-ofthe-world<br />

(ROW) region (FAPRI 2004).<br />

Unlike the AGLINK and CCLS frameworks, which are<br />

country models with commodity submodels, the FAPRI framework<br />

is a set of commodity models with country submodels.<br />

Country consistency and co<strong>here</strong>nce are maintained through the<br />

FAPRI baseline meetings and review. The baseline process<br />

begins with an initial “meltdown” w<strong>here</strong> macroeconomic and<br />

policy assumptions are shared across the various commodity<br />

models. The meltdown process involves an iterative process<br />

of commodity model simulations and calibrations based on<br />

sharing cross-commodity estimates of prices, production, consumption,<br />

stocks, and trade. Following the meltdown, a preliminary<br />

set of baseline projections is reviewed by commodity<br />

and country experts drawn from national and international<br />

government agencies and industry organizations. This review<br />

is then used to revise and recalibrate the models to generate a<br />

final baseline publication.<br />

In addition to the AGRM framework, the University of<br />

Arkansas maintains a spatial equilibrium model framework of<br />

the global rice economy known as RICEFLOW. Unlike the<br />

previous three frameworks, RICEFLOW is distinctively different<br />

in several important respects. First, it is a static model<br />

that solves to optimize welfare quasi-rents in international rice<br />

trade subject to transaction costs, including transportation,<br />

national policy interventions, and bilateral, regional, and multilateral<br />

trade agreements. A second important difference is<br />

that RICEFLOW generates spatial rice trade estimates. Finally,<br />

and perhaps most importantly, RICEFLOW is disaggregated<br />

by rice type, degree of processing, and quality. This framework<br />

is flexible in terms of country aggregation, with as many<br />

as 49 rice importers and 13 rice-exporting countries or regions.<br />

The baseline is generated to approximate actual trade flows<br />

for a given base year. Adjustments to calibrate the model to<br />

the base year are made primarily through modifications in the<br />

transaction cost constraints. Policy and market analysis is conducted<br />

in a comparative static (equilibrium displacement)<br />

framework in which policies and other constraints are relaxed.<br />

The strength of this model is the country and commodity space<br />

disaggregation relative to the AGLINK, CCLS, and AGRM<br />

models. It is particularly useful to examine trade policy issues<br />

such as regional trade agreements, tariff escalations, preferences,<br />

and nontrade barriers (Wailes 2004). The major limita-<br />

Session 17: <strong>Rice</strong> supply and demand 503


tion is its inability to track dynamic adjustments to policy and<br />

market changes.<br />

Table 1 provides a summary of the key differences and<br />

similarities of the four global rice models discussed.<br />

Model projection comparisons<br />

As noted above, both model structure and the process of developing<br />

a baseline for the AGLINK, USDA, and AGRM/<br />

FAPRI models are similar. All three frameworks are used to<br />

generate annual 10-year outlook projections. Table 2 presents<br />

the 2004 projections for global rice production, consumption,<br />

and the international long-grain reference price, Thai 100%B<br />

long grain.<br />

The models reflect some significant differences in their<br />

projection of global rice consumption. The USDA model<br />

projects an increase of 31 million mt over the next 10 years<br />

compared with the AGLINK, with a projected increase of 33<br />

million mt, and the AGRM model, with a projected increase<br />

of 36 million mt. Increases in production are projected in all<br />

three frameworks to exceed the consumption growth, suggesting<br />

an increase in global rice stocks. The AGLINK model<br />

projects a 39 million mt increase in production, 6 million mt<br />

greater than consumption growth. The USDA baseline production<br />

increases by 41 million mt over the next 10 years, 10<br />

million mt greater than the projected consumption increase.<br />

Table 1. Summary of model characteristics for global rice quantitative<br />

models.<br />

Model characteristics AGLINK CCLS AGRM RICEFLOW<br />

Dynamic Yes Yes Yes No<br />

Countries/regions 13 31 31 62<br />

Product disaggregation No No L/M High<br />

Extra-model info High High High Low<br />

Spatial trade flow No No No Yes<br />

The AGRM framework shows increases in production of 41<br />

million mt also, but only 5 million mt greater than the projected<br />

consumption increase.<br />

More striking differences are reflected in the price projections.<br />

The USDA model clearly projects a significantly lower<br />

price path than the AGLINK and AGRM price projections.<br />

While consistent with the relatively lower consumption and<br />

higher surplus production projections, the USDA projected<br />

price by 2013 is 27% lower than the AGRM projection and<br />

17% lower than the AGLINK estimate.<br />

Summary and conclusions<br />

Quantitative models of the global rice market are typically part<br />

of a multicommodity framework. This characteristic is critically<br />

important as the dynamics of demand and supply are reflected<br />

in a framework that includes income and relative price<br />

effects. An important challenge in quantitative modeling of<br />

the global rice economy is the need to be able to capture the<br />

heterogeneous and creative nature of government intervention<br />

in this market. It is difficult to monitor changes in policy regimes<br />

as countries are slow to notify the WTO market interventions.<br />

As policy regimes change, for example, in domestic<br />

support from coupled to decoupled payments, it is difficult to<br />

obtain statistical estimates of program effects given the unavailability<br />

of time-series data.<br />

Disaggregated commodity space and inclusion of key<br />

exporting and importing countries/regions are highly desirable.<br />

While comparative static frameworks are useful, it is also valuable<br />

to understand how markets adjust from one period to the<br />

next. Finally, it is especially desirable for models to simulate<br />

the rice economy in a general equilibrium framework, especially<br />

for countries in which the rice economy is dominant in<br />

agricultural production and food consumption. Unfortunately,<br />

all of these desirable characteristics are difficult to capture in<br />

any one model. Data constraints, costs of developing and main-<br />

Table 2. Global rice production, consumption, and price projections.<br />

Item<br />

Year<br />

2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 2013<br />

OECD<br />

Production (million mt) 393 409 417 422 425 429 434 438 441 444 448<br />

Consumption (million mt) 415 415 418 421 425 428 434 438 441 444 448<br />

Prices (Thai milled 100% B, US$) 204 232 252 264 275 286 291 299 303 310 316<br />

USDA<br />

Production (million mt) 399 410 422 425 430 434 438 442 444 447 451<br />

Consumption (million mt) 416 417 423 424 428 431 434 436 440 444 446<br />

Prices (Thai milled 100% B, US$) 200 206 211 216 221 227 233 240 247 255 262<br />

AGRM/FAPRI<br />

Production (million mt) 391 410 425 430 434 436 438 442 445 449 453<br />

Consumption (million mt) 413 415 421 426 431 435 438 441 444 448 451<br />

Prices (Thai milled 100% B, US$) 207 233 241 246 256 267 281 294 308 322 335<br />

Sources: OECD (2004), USDA (2004), and FAPRI (2004).<br />

504 <strong>Rice</strong> is life: scientific perspectives for the 21st century


taining models, and access to extra-model information ultimately<br />

lead to trade-offs in the scope and design of quantitative<br />

models. Critical to understanding model results is knowing<br />

not only what the model includes but also what the model<br />

excludes in its analytical framework. Fortunately, through the<br />

development of information technology, modelers and users<br />

have access to alternative quantitative model results. This means<br />

that decisions based on model output can be evaluated and incorporated<br />

into decision-making without unrealistic reliance<br />

upon any single model. Internal and external model validation<br />

must be an important dimension of quantitative models. Models<br />

are rarely correct in projections but achieving success in<br />

direction and magnitude of market and policy effects is the<br />

standard against which all models must be judged.<br />

References<br />

FAO. 2003. World agriculture: towards 2015/2030: an FAO perspective.<br />

Bruinsma J, editor. London (UK): Earthscan.<br />

FAPRI. 2004. FAPRI 2004 U.S. and world agricultural outlook. Staff<br />

Report 1-04. Ames, Iowa (USA): Iowa State University.<br />

Hertel TW, editor. 1997. Global trade analysis: modeling and applications.<br />

Cambridge (UK): Cambridge University Press.<br />

Liu K, Seeley R, editors. 1987. The <strong>International</strong> Agricultural <strong>Research</strong><br />

Consortium: agricultural trade modeling, the state of<br />

practice and research issues. Staff Report No. AGES861215.<br />

<strong>International</strong> Economics Division, Economic <strong>Research</strong> Service,<br />

U.S. Department of Agriculture.<br />

OECD. 2004. OECD agricultural outlook 2004-2013. Paris.<br />

USDA. 2004. USDA agricultural baseline projections to 2013. Staff<br />

Report WAOB-2004-1. Office of the Chief Economist, USDA.<br />

Prepared by the Interagency Agricultural Projections Committee.<br />

Washington, D.C.<br />

Wailes EJ. 2004. Implications of the WTO Doha Round for the rice<br />

sector. Proceedings, FAO <strong>Rice</strong> Conference, Rome, Italy.<br />

World Bank. 2003. Global economic prospects 2004. In: Realizing<br />

the development promise of the Doha Agenda. Washington,<br />

D.C. (USA): World Bank.<br />

Notes<br />

Author’s address: 217 Agriculture Building, Department of Agricultural<br />

Economics and Agribusiness, Division of Agriculture,<br />

University of Arkansas, Fayetteville, Arkansas 72701,<br />

USA, e-mail: ewailes@uark.edu.<br />

Household rice consumption in Japan: quantity and price by<br />

income while controlling for household types<br />

Kimiko Ishibashi, Yoshinobu Kono, and Yuuji Ooura<br />

As food consumption has become diversified, rice consumption<br />

has gradually declined in Japan. Individual consumption<br />

of food products varies significantly by age (Ishibashi 1997),<br />

indicating the importance of the age factor in food demand<br />

analysis.<br />

Household income is highly associated with the age of<br />

the household head under the seniority system in the Japanese<br />

labor market. Real income-consumption profiles are likely obscured<br />

by the fact that Japanese older people (old in age and<br />

generation as well) consume more rice on average than (currently)<br />

younger ones, and that older children generally eat more<br />

rice than smaller ones.<br />

Based on the analysis of the panel data of household<br />

expenditure surveys, distinct differences are detected in quantity<br />

and price paid for rice among major household types. We<br />

then tried to estimate the age factor-free income elasticities of<br />

demand for rice cross-sectionally by major household types.<br />

Data<br />

The Japanese government Bureau of Statistics (JBC) conducts<br />

the Family Income and Expenditure Survey (FIES) monthly<br />

with approximately 8,000 households across the nation on a<br />

continuous basis, with one-sixth of them renewed every month.<br />

The age composition of family members, annual income, and<br />

monthly purchases of various products and services of each<br />

household are recorded in the data. We analyzed the panel data<br />

of approximately 96,000 households each year for 8 selected<br />

years from 1987 to 2001 (Courtesy of the JBC).<br />

Methodology<br />

We first classified the panel by the age of the household head<br />

and household size, with the age of family members taken into<br />

consideration.<br />

First, the amount of rice purchased and average rice price<br />

paid were examined by each household type listed below, then<br />

household purchases were regressed against the household income<br />

as follows, using the aggregate data grouped by every<br />

0.5 million yen in household annual income.<br />

ln Q = a + b ln Y<br />

w<strong>here</strong> Q = household monthly purchases (= consumption), Y<br />

= household annual income, a = intercept, and b = coefficients<br />

for income.<br />

Session 17: <strong>Rice</strong> supply and demand 505


Amount of rice purchased (kg mo –1 )<br />

16<br />

14<br />

A couple in their 30s with two children under 10 years of age<br />

A couple in their 40s with two children aged 10–20<br />

A couple in their 50s with a child in his/her 20s<br />

A couple in their 60s without dependents<br />

12<br />

10<br />

8<br />

6<br />

4<br />

3,500 4,000 4,500 5,000 5,500 6,000<br />

Yen<br />

Fig. 1. Changes in consumption of rice with respect to quantity and price paid by selected<br />

household types.<br />

Results<br />

Major household types in Japan<br />

According to the JBC, the sample household is selected in proportion<br />

to the size of the household types in Japan. The major<br />

household types selected for our analysis were<br />

Households in which a couple are in their 30s with<br />

two children under 10 years of age, 5,663 in 1987<br />

and 3,979 in 2001 in total number, for example.<br />

Households in which a couple are in their 40s with<br />

two children age 10 to 20, 4,584 in 1987 and 2,880 in<br />

2001, respectively.<br />

Households in which a couple are in their 50s with a<br />

child in his/her 20s, 2,840 in 1987 and 3,099 in 2001,<br />

respectively.<br />

Households in which a couple are in their 60s and<br />

have no dependents, 3,761 in 1987 and 7,449 in 2001,<br />

respectively.<br />

<strong>Rice</strong> consumption by household types<br />

Figure 1 clearly shows that changes in consumption of rice<br />

with respect to quantity and price varied greatly among the<br />

selected household types from 1987 to 2001. The average price<br />

paid declined consistently from 1987 to 2001 (downward slope<br />

along the X-axis) in every household type, with the younger<br />

households showing greater declines. At the same time, a decrease<br />

in quantity purchased occurred for all household types<br />

(downward slope along the Y-axis). The households of a couple<br />

in their 40s with two children from age 10 to 20, in particular,<br />

demonstrated the largest drop from approximately 15 kg per<br />

month in 1987 to approximately 9 kg per month in 2001 (the<br />

topmost line in Fig. 1).<br />

Figure 1 also shows that the households in which a couple<br />

were in their 50s with a child in his/her 20s and those of a<br />

couple in their 60s without dependents share strikingly similar<br />

tendencies in consumption changes, with the two lines overlapping<br />

over time, despite big differences in income between<br />

the two categories, that is, the former register more than 10<br />

million yen per year for most years, w<strong>here</strong>as the latter category<br />

has 2.0 to 4.0 million yen. Regarding the average prices<br />

paid, those in their 50s paid higher prices (rightward horizontally)<br />

than those in their 60s in every year.<br />

Within the same household type, that is, when the age of<br />

family members is controlled, clear tendencies are observed<br />

that the greater the household income, the smaller the consumption<br />

and the higher the price paid. For households of a<br />

couple in their 40s with two children from 10 to 20, for example,<br />

those with an annual income of 2.0 to 4.0 million yen<br />

purchased 16.8 kg of rice per month on average at the average<br />

price of 5,257 yen per 10 kg in 1987, w<strong>here</strong>as those with income<br />

over 10 million yen purchased 12.3 kg at 5,897 yen in<br />

the same year. The corresponding numbers for 1996, for example,<br />

are 12.7 kg at 4,815 yen versus 8.9 kg at 5,099 yen,<br />

and for 2001 are 8.9 kg at 3,743 yen versus 7.5 kg at 4,430<br />

yen, respectively.<br />

Income elasticities for rice<br />

Most previous studies, using cross-sectional data, suggest that<br />

income elasticities for rice should be positive in sign (Appendix<br />

table 4 in FIES annual report, various issues). To determine<br />

the pure income effects on rice consumption, we ran a<br />

regression by household types.<br />

Table 1 shows estimates of income elasticities for consumption<br />

of rice by household type, using panel data aggregated<br />

by income groups in 0.5 million yen. Both the households<br />

in which a couple are in their 30s with two children under<br />

10 years of age and those of a couple in their 40s with two<br />

children from 10 to 20 are estimated to carry negative income<br />

elasticities, –0.1 to –0.2, with meaningful t-values for most of<br />

our survey years. When these two types are grouped together,<br />

however, we get positive income elasticities, 0.2 to 0.3, with<br />

significant t-values and much greater R 2 s. This might suggest<br />

that household purchases of rice tend to increase with the growing<br />

up of children from under age 10 to teens, w<strong>here</strong>as the<br />

household income also tends to increase in accordance with<br />

the aging of household heads from their 30s to their 40s. The<br />

506 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. Estimates of income elasticities for rice by household types, selected years from 1984 to 2001, using panel data<br />

aggregated by income groups (in 0.5 million yen). a<br />

Household types<br />

A couple in their 30s with two A couple in their 40s with two Two types aggregated<br />

children under 10 years of age children from 10 to 20<br />

b-estimated Adj. R 2 t-value b-estimated Adj. R 2 t-value b-estimated Adj. R 2 t-value<br />

–0.21 0.44 –3.89 –0.08 0.11 –1.94 0.15 0.19 2.63<br />

–0.14 0.11 –1.91 –0.21 0.46 –4.68 0.15 0.27 3.20<br />

–0.13 0.12 –1.93 –0.04 –0.03 –0.59 0.32 0.52 5.31<br />

–0.08 0.02 –1.21 –0.16 0.15 –2.28 0.24 0.32 3.60<br />

–0.17 0.06 –1.55 –0.18 0.13 –2.17 0.22 0.21 2.73<br />

0.15 0.13 2.00 –0.16 0.07 –1.58 0.29 0.32 3.57<br />

–0.11 0.02 –1.24 0.19 0.14 2.18 0.34 0.48 4.74<br />

0.02 –0.04 0.22 0.04 –0.04 0.30 0.29 0.26 3.11<br />

–0.18 0.11 –2.00 –0.18 0.07 –1.67 0.06 –0.01 0.91<br />

a<br />

Double log model used: ln Q = a + b ln Y, w<strong>here</strong> Q = household monthly purchases and Y = household annual income. Glutinous and nonglutinous rice for<br />

2001, nonglutinous rice for other years.<br />

above results may strongly suggest a need for classifying households<br />

by the age of family members if we wish to determine<br />

the pure income effects on rice consumption in Japan using<br />

cross-sectional data in particular.<br />

Conclusions<br />

Tentative conclusions from our investigations are as follows:<br />

1. The household quantities of rice purchased and prices<br />

paid differ, and the patterns of change in consumption<br />

over time also vary significantly by types of<br />

household.<br />

2. When the age of family members and the household<br />

type are controlled, the households with a larger income<br />

are found to purchase a smaller amount of rice,<br />

and to pay higher prices.<br />

3. The cross-sectional income elasticities for rice are estimated<br />

to be negative in sign and significantly different<br />

from zero in Japan, opposed to most previous<br />

Wrap-up of Session 17<br />

studies, including the government FIES annual reports.<br />

Our findings, as shown in Figure 1, suggest that age effects<br />

should overwhelm income effects in rice consumption<br />

and prices paid are found to differ significantly by age of household<br />

head and household income. This should be taken to imply<br />

the importance of incorporating the age factor into analysis<br />

to better comprehend Japanese rice consumption, including<br />

future projections.<br />

References<br />

Ishibashi K. 1997. Changes in Japanese dietary patterns by age. Is<br />

the “Japanese style” disappearing Natl. Agric. Res. Ctr. Rural<br />

Econ. Res. 36:17-31.<br />

Notes<br />

Authors’ address: National Agricultural <strong>Research</strong> Center, Kannondai<br />

3-1-1, Tsukuba, Ibaraki, Japan.<br />

This session dealt with the international rice market situation,<br />

with emphasis on Asian countries. The main objectives were to<br />

obtain common understanding on past trends and future prospects<br />

in rice supply and demand among researchers by exchanging<br />

views, as well as to identify research priorities in this field.<br />

These include the identification of emerging factors influencing<br />

supply and demand of rice and the improvement of analytical<br />

tools such as econometric models.<br />

In addition to day-to-day market fluctuations, the supply<br />

and demand situation structurally and fundamentally shifts according<br />

to economic and social environmental changes. Agricul-<br />

tural research, especially the development of technologies, should<br />

be consistent with these structural shifts, so that research results<br />

will be relevant. This session t<strong>here</strong>fore attracted a large<br />

audience consisting of both economists and natural scientists.<br />

Regarding the demand side, we are encountering epochmarking<br />

phenomena such as diversification of the rice-based dietary<br />

pattern in Asian countries, the increase in processed and<br />

nonfood use for rice, and quality differentiation in the rice market.<br />

For the supply side, skepticism on yield potential prevails, as<br />

water use and chemical inputs are no longer unlimited. The cost<br />

of production tends to increase in many countries. In addition,<br />

Session 17: <strong>Rice</strong> supply and demand 507


environmental concerns and recognition of the external economics<br />

of paddy farming lead to the introduction of new types of<br />

support policies.<br />

The market itself also confronts drastic changes. Information<br />

technology accelerates the flows of market information worldwide.<br />

New market players appeared locally and globally through<br />

both vertical market integration and global trade liberalization.<br />

Market volatility seems to have become more evident, and food<br />

security issues are often mentioned in the context of price fluctuation<br />

as well as in the lack of market access. Our session tried<br />

to elucidate these changes and future prospects for rice.<br />

The session was co-chaired by O. Koyama (JIRCAS) and D.<br />

Dawe (<strong>IRRI</strong>). Five speakers made presentations. C. Calpe (FAO)<br />

covered the recent changes in international rice trade and pointed<br />

out that the current rice market is not as thin, segregated, or<br />

protected as it used to be. The disaggregated trade statistics<br />

shown by quality and variety classes were examined. Some arguments<br />

were made whether rice was becoming a normal trade<br />

good, though the general feeling was that it still keeps its special<br />

characteristics to a lesser extent. S. Ito (Tottori University) discussed<br />

future rice consumption in Asia, showing statistical evidence<br />

from some countries. He forecast that Asian agriculture,<br />

and consequently Asian rural society, would lose ground if rice<br />

consumption declined at the pace experienced in Japan, Taiwan,<br />

and Korea. He emphasized the need of investment to generate<br />

new demand in the region. Some argued that the potential requirement<br />

for additional rice consumption by the low-income<br />

population should not be underestimated.<br />

H. Chien (JIRCAS) gave details on the dynamic shift in demand<br />

from quantity to quality observed in China, and concluded<br />

that japonica rice would be welcomed by expanded markets. It<br />

was noted that the quality differences among japonica rice would<br />

determine the future geographical distribution of japonica production<br />

in China. She also mentioned that national food security<br />

was still a major concern with respect to grain policy in China. V.<br />

Sriprasert (Thai <strong>Rice</strong> Exporters Association) stressed the massive<br />

supply potential in Asia based on the historical lessons and the<br />

current level of investment in some exporting countries in Asia.<br />

His view was that t<strong>here</strong> would be plenty of business opportunities,<br />

including in Africa, if some adverse institutional restrictions<br />

were removed.<br />

E. Wailes (University of Arkansas) overviewed various activities<br />

currently conducted in the field of quantitative models on<br />

the international rice market. He stressed that model types were<br />

subject to the purpose of the analyses; thus, the evaluation of<br />

model results should also be done accordingly. It was extremely<br />

useful for the audience to grasp the cutting edge of modeling<br />

methodologies for the rice market.<br />

In general discussion, the future demand for rice, whether<br />

it will grow or not, was again a controversial issue. The importance<br />

of nonfood uses, such as for energy, bio-materials, and<br />

feed, was suggested. Areas will be emerging for both research<br />

and business opportunities. It was also suggested that research<br />

on the supply and demand situation requires information exchange<br />

among researchers; thus, wider cooperation should be promoted<br />

across business, academics, and international organizations. The<br />

session successfully provided information and instructions for<br />

participants from a wide range of research subjects.<br />

508 <strong>Rice</strong> is life: scientific perspectives for the 21st century


SESSION 18<br />

Impact of globalization on rice farmers<br />

CONVENER: M. Umemoto (NARO)<br />

CO-CONVENER: D. Dawe (<strong>IRRI</strong>)


Impacts of distorted trade policies on rice productivity<br />

Manitra A. Rakotoarisoa<br />

Studies (e.g., Wailes, 2003) showed that, although the removal<br />

of tariff and export subsidies in the highly distorted rice market<br />

would benefit the world, developing countries that produce<br />

rice but are net rice importers (e.g., Bangladesh, Brazil,<br />

Indonesia, Madagascar, Nigeria, and the Philippines) would<br />

lose. For these countries, with mostly poor rice farmers and<br />

low productivity, the increase in the producer’s gain would be<br />

too little to overcome the consumer’s loss as the market price<br />

rises. Seemingly, liberalization yields little benefit unless productivity<br />

rises first. But, did the lack of price competitiveness,<br />

caused in part by distorted rice policies that depressed revenues<br />

and profits, prevent poor farmers from adopting available<br />

technology<br />

The objective of this paper is to determine how distorted<br />

policies in the international rice market affect productivity and<br />

competitiveness in the rice sector. Specific objectives are to<br />

(1) measure the level and growth of total factor productivity<br />

(TFP) in the main rice-producing countries, (2) explain the<br />

sources of productivity gaps among rice producers, and (3)<br />

determine the interactions among trade liberalization, productivity,<br />

and competitiveness. The focus is on 33 rice-producing<br />

countries during the period 1961-2002. This study provides a<br />

new framework for measuring and analyzing sources of the<br />

productivity gap.<br />

<strong>Rice</strong> markets and policies<br />

<strong>Rice</strong> trade is thin and represented only 6.5% of global rice<br />

consumption during 1997-2002 (Childs 2002). Wailes (2003)<br />

reviewed current policies in the rice-producing countries in<br />

the OECD (Organization for Economic Cooperation and Development),<br />

w<strong>here</strong> production and exports are highly subsidized<br />

and protected. These policies have caused distortions in<br />

prices and resource allocation for developing countries. During<br />

1961-2002, the price-adjusted inflation of rice in the world<br />

market has tended downward despite the growing global rice<br />

demand, but the price of imported farm inputs has increased<br />

sharply.<br />

Framework<br />

Measuring productivity<br />

We assume that the rice production function is Y it = F (X 1 it ,...,<br />

X k it , ev it), w<strong>here</strong> index i represents country, t is the time dimension,<br />

and superscripts 1 …k represent input type. Y represents<br />

output, X’s are inputs, and X k is labor. The exponent of the<br />

residual ν it represents the level of technology. Using Cermeño<br />

et al (2003) henceforth as CMT, the residual in a dynamic form<br />

is ν it = µ i + λ t + Φν it–1 + ε it , w<strong>here</strong> ε it˜ iid (0,σ ε 2 ), µ, and λ<br />

represent individual and time-specific effects, and µ, λ, and ε<br />

are uncorrelated to each other. CMT considered two other alternatives<br />

of the expression of ν it in replacing λ t by (1) θ i *t<br />

indicating that the growth rate of TFP (coefficient on time trend)<br />

is different for each country and (2) θ*t indicating that the<br />

TFP growth rate is the same for all countries. Taking the logarithms<br />

of the production function and taking into account these<br />

three expressions of the residual, production per worker is<br />

k–1 k–1<br />

(1a) y it = γy it–1 + Σ α j x j it + Σ β j xj it–1 + δ 0 Χk it<br />

j=1 j=1<br />

+ δ 1 Χ k it–1 + θ i *t + µ i + ε it<br />

k–1 k–1<br />

(1b) y it = γy it–1 + Σ α j x j it + Σ β j x j it–1 + δ 0 Χ k it<br />

j=1 j=1<br />

+ δ 1 Χ k it–1 + θ i *t + µ i + ε it<br />

k–1 k–1<br />

(1c) y it = γy it–1 + Σ α j x j it + Σ β j xj it–1 + δ 0Χ k it<br />

j=1 j=1<br />

+ δ 1 Χ k it–1 + λ t + µ i + ε it<br />

Variables y and x represent the log of output and input per<br />

worker, and ε’s are error terms.<br />

Competitiveness and total factor productivity<br />

We define a competitiveness index C as the ratio between value<br />

added estimated at world prices and input cost estimated at<br />

shadow prices: C = pV/(ωL+rK) w<strong>here</strong> ω and r are shadow<br />

prices of labor L and capital K. Variable K combines all<br />

nonlabor inputs such as human capital, land, fertilizer, and tractor<br />

uses. p is the world price of the value added V; V = f (K, L,<br />

A) w<strong>here</strong> A is the level of technology. As in Nishimizu and<br />

Page (1986), price p can be called “terms of trade,” reflecting<br />

differences between output price and intermediate input costs.<br />

The change in competitiveness index is<br />

dC dp dω dr dL<br />

(2) = – s L – s K – (s L – a L )<br />

C p ω r<br />

L<br />

dK<br />

– (s K – a K ) – aA .dA<br />

K<br />

510 <strong>Rice</strong> is life: scientific perspectives for the 21st century


w<strong>here</strong> s L = ω.L/(ω.L + r.K) and s K = r.K/(ω.L + r.K) are the cost<br />

shares of labor and capital at shadow prices, and a K and a L are<br />

input elasticities of substitution.<br />

The first three terms in (2) represent price competitiveness,<br />

PC, which increases with C as the world price increases.<br />

The fourth and fifth terms indicate production efficiency: as<br />

cost shares decline toward input elasticities, C grows. The last<br />

term is technological progress, affecting the growth of C.<br />

TFP gap and price competitiveness<br />

PC, the first three terms in (2), also represents the (negative)<br />

value of the world’s TFP (or TFP price) rate of change. The<br />

fourth and fifth terms vanish in the long run as input elasticities<br />

approach input cost shares to indicate price efficiency.<br />

Without trade distortions and under production efficiency, C<br />

depends only on the TFP gap between the domestic country<br />

and the rest of the world, that is,<br />

(3)<br />

From Coe et al (1997), we add control variables such as<br />

openness (OPEN), human capital (HK), and access to agricultural<br />

machinery—a function of equipment price and PC—and<br />

propose the following model:<br />

(4)<br />

w<strong>here</strong> P w and q are the prices of rice and inputs and farm<br />

equipment. Subscripts w and i designate the world’s and individual<br />

country’s variables.<br />

Data<br />

Growth of<br />

TFP gap + Disturbances =<br />

(home/world)<br />

Output<br />

price<br />

Intermediate<br />

– –<br />

good’s price<br />

Other<br />

factor<br />

costs<br />

Growth<br />

of<br />

Change in<br />

+ production<br />

efficiency<br />

TFPw<br />

log ( ) t = α 0 + α 1 log(Pw) t + α 2 log(q) t<br />

TFPi<br />

+ α 3 log (HK w / HK i ) t + α 4 log(OPEN w / OPEN i ) t + η it<br />

We divide the 33 countries into three groups. Group 1 includes<br />

OECD countries, rice producers: Australia, EU (Italy), Japan,<br />

Korea, and the United States. Group 1 has high rice yields,<br />

subsidizes heavily its rice production and exports, and has high<br />

import protection. Group 2 includes developing countries, rice<br />

exporters, with little or no subsidies and relatively high yields:<br />

Argentina, China, Colombia, Egypt, Guyana, India, Myanmar,<br />

Pakistan, Suriname, Thailand, Vietnam, and Uruguay. Group 3<br />

includes mostly low-income countries that produce and import<br />

rice from the other two groups: Bangladesh, Brazil, Cambodia,<br />

Guinea, Indonesia, Iran, Laos, Madagascar, Mali, Malaysia,<br />

Nepal, Nigeria, Peru, the Philippines, Sri Lanka, and Tanzania.<br />

Data are yearly from 1961 to 2002. Appendix A explains<br />

the data sources.<br />

Table 1. Explaining the productivity gap among rice-producing countries<br />

(1971-2002).<br />

Group 2 a (low- and Group 3 b (low-<br />

Variables middle-income income rice<br />

rice exporters) importers)<br />

Dependent variable: log (TFP1/TFPi)<br />

Independent variables in log term:<br />

Output price –0.053*** –0.050***<br />

(–4.34) c (–6.09)<br />

Farm equipment price ratio 0.112*** 0.149***<br />

(8.11) (14.63)<br />

Openness ratio 0.300* 0.258<br />

(1.86) (1.47)<br />

Human capital ratio –1.017** –0.512***<br />

(–2.22) (–3.16)<br />

Lag-dependent variable 0.145 0.409**<br />

(0.78) (2.33)<br />

Durbin Watson 2.01 2.09<br />

a Group 2 includes Argentina, China, Colombia, Egypt, Guyana, India, Myanmar, Pakistan,<br />

Suriname, Thailand, Vietnam, and Uruguay. b Group 3 includes Bangladesh,<br />

Brazil, Cambodia, Guinea, Indonesia, Iran, Laos, Madagascar, Mali, Malaysia, Nepal,<br />

Nigeria, Peru, Philippines, Sri Lanka, and Tanzania. c Numbers in parentheses and<br />

below the coefficients are t-values. The symbols *** , **, and * are levels of significance<br />

at 0.01, 0.05, and 0.1, respectively.<br />

Results<br />

Measures of TFP level and growth rate<br />

Between-groups estimation. In all three models, (1a), (1b), and<br />

(1c), µ i ’s, the group-specific effects, are statistically significant<br />

for group 1 and group 2 (group 3 is the basis for comparison).<br />

As expected, the high-income countries in group 1 have<br />

the highest level of TFP versus group 2 and group 3. Model<br />

(1b) produces the best fit and indicates, through θ, that the<br />

trend in world rice productivity grew at 0.4% on average per<br />

year during 1961-2002.<br />

Within-group estimation. For group 1, model (1b) yields<br />

the best fit. The coefficient θ is significant, indicating that TFP<br />

in group 1 grew at 1.6% per year on average. For group 2,<br />

model (1a) gives the best fit. Country-specific effects on TFP<br />

are significant in eight out of 11 countries. Model (1b) provides<br />

similar results and shows that TFP in group 2 grew at<br />

1% per year during 1961-2002.<br />

For group 3, model (1b) best represents the data. All<br />

country-specific effects of TFP are significant. Also, TFP<br />

growth is about 0.8% per year, meaning that the “catching-up”<br />

hypothesis does not hold; countries in group 3 started at lower<br />

TFP levels and their TFPs have grown slower than in group 2<br />

and group 1.<br />

Explaining productivity gaps<br />

From model (1a), we build a time series on TFP levels and<br />

growth for each group. Estimates of TFP levels are plotted in<br />

Figure 1 showing the widening TFP gap, especially between<br />

group 3 and group 1. We employ TFP measures to estimate the<br />

parameters of (4).<br />

Results are in Table 1. Coefficients have the expected<br />

signs and are significant, except for the openness variable. The<br />

Session 18: Impact of globalization on rice farmers 511


Index<br />

3.0<br />

2.5<br />

Group 1 (high-income producers)<br />

Group 2 (low-income exporters)<br />

Group 3 (low-income importers)<br />

2.0<br />

1.5<br />

1.0<br />

0.5<br />

0.0<br />

1961 1965 1969 1973 1977 1981 1985 1989 1993 1997 2001<br />

1963 1967 1971 1975 1979 1983 1987 1991 1995 1999<br />

Year<br />

Fig. 1. Estimated TFP index levels for the main rice-producing countries (1961-2002).<br />

Group 1 includes Australia, EU (Italy), Japan, Korea, and the United States. Group 2<br />

includes Argentina, China, Colombia, Egypt, Guyana, India, Myanmar, Pakistan,<br />

Suriname, Thailand, Vietnam, and Uruguay. Group 3 includes Bangladesh, Brazil,<br />

Cambodia, Guinea, Indonesia, Iran, Laos, Madagascar, Mali, Malaysia, Nepal, Nigeria,<br />

Peru, Philippines, Sri Lanka, and Tanzania.<br />

TFP gap has grown partly because of the lack of price competitiveness.<br />

A 10% decrease in the world price below its free<br />

trade level has increased the TFP gap ratios between group 1<br />

and the other two groups by 0.5%. Coefficients on q are statistically<br />

significant. Each percent increase in equipment price<br />

would widen the TFP ratios by about 0.11% and 0.15% for<br />

groups 2 and 3. The rising equipment price reduced poor farmers’<br />

access to the inputs necessary to adopt available technology.<br />

As a result, their TFP levels lag behind TFP in rich countries<br />

and the TFP gap widens.<br />

The coefficients on OPEN are positive, and are significant<br />

at the 0.1 level for group 2, but not significant for group<br />

3. This supports early criticism (Rodrik 1992) that openness<br />

does not necessarily guarantee a reduction in TFP gaps. The<br />

coefficients on HK ratios are significant, indicating that rapid<br />

growth of human capital in groups 2 and 3 could help reduce<br />

TFP gaps.<br />

Conclusions and implications<br />

This paper focused on how distorted trade policies affect productivity<br />

and competitiveness in the rice sector. We estimated<br />

TFP levels and growth rates and explained the sources of the<br />

TFP gap among rice-producing countries. We found that the<br />

TFP gap in the rice sector has widened. The catching-up hypothesis<br />

does not hold: TFP levels and growth rates have been<br />

higher in high-income countries than in developing countries.<br />

The lack of price competitiveness, partly because of heavy<br />

production and trade subsidies in the OECD, was one of the<br />

sources of this productivity gap. Limited access to equipment<br />

has increased the TFP gap. Also, trade openness has a weak<br />

positive impact on the TFP gap; this may partly reflect difficulties<br />

in choosing proxies (Edwards 1997).<br />

Results imply that removing distortions on output price<br />

and input access can boost revenue and profit for rice producers<br />

in developing countries. That will allow investments for<br />

the use of available technology and reduce the TFP gap.<br />

Appendix A: Variables and sources<br />

Inputs: X f , fertilizer use, proxyed as the total fertilizer use<br />

times the share of harvested rice fields over arable land (UN<br />

FAO); X k , amount of labor in rice production proxyed as the<br />

rural labor force, that is, active workers in rural areas (World<br />

Bank); X tr , physical capital, proxyed as the average number of<br />

tractors used per unit of agricultural land times rice-harvested<br />

area; X l , rice-harvested area (UN FAO).<br />

HK: human capital, is net secondary enrollment ratio (World<br />

Bank).<br />

OPEN: openness, is trade value over GDP (World Bank).<br />

Pw: world price of rice; proxy is the f.o.b. price of 5% broken<br />

milled rice from Bangkok, Thailand; prices are in 1982 US<br />

dollars constant (World Bank).<br />

q: price of agricultural and farm equipment; proxy is the index<br />

price of agricultural and farm inputs and equipment times the<br />

exchange rate (UN FAO, U.S. Department of Labor, World<br />

Bank).<br />

512 <strong>Rice</strong> is life: scientific perspectives for the 21st century


: rental price of capital, or lending interest rate (World Bank).<br />

Y: milled rice production in metric tons (UN FAO).<br />

References<br />

Childs N. 2002. <strong>Rice</strong> outlook. Economic <strong>Research</strong> Service, United<br />

States Department of Agriculture, Washington, D.C., USA.<br />

Cermeño R, Maddala GS, Trueblood M. 2003. Modeling technology<br />

as a dynamic error components process: the case of the<br />

inter-country agricultural production function. Econ. Rev.<br />

22:289-306.<br />

Coe D, Helpman E, Hoffmaister A. 1997. North-south R&D spillover.<br />

Econ. J. 107(440):134-149.<br />

Edwards S. 1997. Openness, productivity and growth: what do we<br />

really know National Bureau of Economic <strong>Research</strong> Working<br />

Paper No. 5978.<br />

Nishimizu M, Page J. 1986. Productivity change and dynamic comparative<br />

advantage. Rev. Econ. Stat. 68:241-247.<br />

Rodrik D. 1992. Closing the technology gap: Does trade liberalization<br />

really help In: Helleiner G, editor. Trade policy, industrialization,<br />

and development: new perspectives. Oxford (UK):<br />

Clarendon Press.<br />

United Nations Food and Agriculture Organization. Various years.<br />

Agriculture database.<br />

United States Department of Labor. Bureau of Labor Statistics. Price<br />

indexes.<br />

Wailes E. 2003. Global trade and protection regime in rice trade.<br />

Draft paper. University of Arkansas.<br />

World Bank. 2003. World development indicators.<br />

Notes<br />

A new strategy for group farming in Japan<br />

Kyoichi Miyatake<br />

Authors’ address: Markets, Trade, and Institutions Division, <strong>International</strong><br />

Food Policy <strong>Research</strong> <strong>Institute</strong>, 2033 K Street N.W.,<br />

Washington, D.C. 20006, USA, e-mail:<br />

m.rakotoarisoa@cgiar.org and a.gulati@cgiar.org.<br />

Japanese rice farming was influenced by the liberalization of<br />

the domestic market and minimum access to rice trading. The<br />

price of rice decreased by 27% from 1992 to 2002. Because of<br />

this problem, the Japanese government promotes the improvement<br />

of the productivity of rice production. This policy considers<br />

large-scale individual farmers (10–20 ha) and cooperative<br />

management farms (35–50 ha) to be model farms. These<br />

are estimated to be only 45,000 of the total of 3 million Japanese<br />

farmers. So, in regions w<strong>here</strong> large-scale farms aren’t<br />

found, “community-wide group farming” based on the rural<br />

community is expected as a model of farming.<br />

In Japanese agricultural areas, traditionally, rural communities<br />

of 20 to 30 farmers have been the basic units not only<br />

of social life but also of rice-farming work, such as the management<br />

of irrigation water and joint farm work. Group farming<br />

is an activity based on the rural community, which aims to<br />

modernize and restructure rice production through joint use of<br />

farm machines, joint farm work, and community land-use arrangements.<br />

T<strong>here</strong>fore, about 10,000 farming groups were established<br />

in Japan.<br />

The Noguchi farming group of Johana town, Toyama<br />

Prefecture, is an example of community-wide group farming.<br />

The Noguchi farming group is incorporated and is now working<br />

on the organic cultivation of rice, too. This report analyzes<br />

the group’s farm management activities for over three decades<br />

and discusses its improvements.<br />

Outline of the area<br />

Traditionally, most farmers in Johana have been engaged in<br />

rice growing on their land of 1 ha or so. But, in the 1970s,<br />

factories of metals and electronics were constructed in Toyama<br />

Prefecture, and farmers obtained new jobs in nonagricultural<br />

industries. Under those conditions, most farmers in the town<br />

became part-time farmers and took part in community-wide<br />

group farming to maintain their rice production through the<br />

joint use of farm machines, joint farm work, and community<br />

land-use arrangements because their farm size was too small<br />

to modernize rice production and make enough money.<br />

As a result, 21 of the 32 rural communities in Johana<br />

now have group-farming units. The farmland managed by these<br />

units is two-thirds of the paddy field in Johana (1,367 ha). On<br />

the other hand, only 33 of the total of 649 town farmers are<br />

full-time farmers engaged in beef-cattle raising, fruit production,<br />

or vegetable cultivation in addition to rice growing.<br />

Foundation of the Noguchi farming group<br />

In Noguchi community, 16 farmers started the joint use of ricefarming<br />

machines in 1975. In 1983, when restrictions on rice<br />

growing had become serious, Noguchi community started the<br />

joint production of soybean and barley as an alternative to rice.<br />

Then, in 1985, as a project financed by Toyama Prefecture,<br />

the community introduced rice-farming machines and constructed<br />

a joint rice drying and processing plant (Table 1),<br />

t<strong>here</strong>by starting community-wide agriculture with the participation<br />

of all 23 farmers in the community. In general, community-wide<br />

farming groups adopted the joint use of machines in<br />

individual fields, and members got the harvest from individual<br />

paddy fields. But, in the group farming in Noguchi reorganized<br />

in 1985, a new system was adopted: the members worked<br />

together and the harvest was processed and sold jointly in the<br />

community. And the earnings were distributed to the member<br />

farmers as land rent and wages for farm work.<br />

Session 18: Impact of globalization on rice farmers 513


Table 1. Outline of the Noguchi farming group.<br />

Item<br />

Characteristics<br />

Members<br />

23 farm households (all households in Noguchi<br />

community): 47 participate in joint farm work<br />

(28 males, 19 females), of whom 16 are farm<br />

machine operators<br />

Farm area 29.4 ha (paddy fields; all plots enlarged to 0.3<br />

ha)<br />

Crops<br />

<strong>Rice</strong>: 21.4 ha (entirely organically cultivated);<br />

Koshihikari 60%, Gohyaku Angoku (rice for<br />

sake brewing) 40%; soybean 8.0 ha; barley<br />

4.3 ha (double cropping with soybean)<br />

Yield<br />

<strong>Rice</strong> 4.6–5.2 t ha –1 (brown rice basis); soybean<br />

1.3–2.5 t ha –1 ; barley 3.0–4.0 t ha –1<br />

Machines and facilities Two 43-hp, one 34-hp, and one 29-hp tractor;<br />

two 8-row transplanters; two 5-row combines;<br />

drying and processing building (436 m 2 ); a<br />

set of seedling culture equipment and a forklift;<br />

six 36-Koku dryers for rice (1 Koku = 180<br />

L); a soybean combine<br />

Working hours for rice 213 h ha –1 of paddy fields; of which daily management<br />

work (100 h) is entrusted to member<br />

farmers<br />

Distribution of earnings Net returns $6,646 composed of land rent<br />

$2,000 ha –1 , daily management fee $2,727<br />

ha –1 , and wage for joint work $1,918 ha –1 ;<br />

wages $16.36 h –1 for males and $14.55<br />

h –1 for females<br />

In those years, most farmers in the community experienced<br />

a generation shift from the first generation, which had<br />

established the organization for joint machine use in 1975, to<br />

their sons as the second generation. The younger farmers had<br />

served as full-time workers in nearby cities, so it became more<br />

important to increase the efficiency of group farming. This<br />

new system of profit distribution was introduced by the younger<br />

generation as its members overcame the opposition of the older<br />

generation, who wanted to continue getting the harvest from<br />

each paddy field. As a result, working time for rice decreased<br />

from 297 h ha –1 (local average) to 213 h ha –1 , although that<br />

included 100 h for daily management done by individual farmers.<br />

In addition, the farming group was incorporated in 1988,<br />

which allowed it to conclude land-lease agreements with farmers<br />

in the community and to stock earnings for future renewal<br />

of machines and facilities. Since then, the 43-hp tractor, 8-row<br />

transplanter, and 5-row combine harvester have been replaced<br />

without financial support.<br />

Securing the labor force<br />

The Noguchi farming group does, as its joint work, the main<br />

rice cultivation work, such as seedling production, preparation<br />

of paddy fields, transplanting, harvesting, and drying and<br />

processing. The farming group entrusts daily management<br />

tasks, including water management and hand weeding, to the<br />

owners of land for wages (seven retiring farmers asked their<br />

neighbors). The growing of soybean and barley, which is highly<br />

mechanized, is totally carried out by the joint efforts of the<br />

farming group. In this group, 16 members practiced the main<br />

joint work as operators, of which 11 are young farmers who<br />

work full-time in nonfarm jobs during the day, and so joint<br />

work is performed mainly on the weekends. On weekdays, five<br />

other farmers, who retired from nonagricultural work, take<br />

charge of farm work. Their agricultural know-how is useful<br />

for seedling management and drying control. On the other hand,<br />

seedling operation and transplanting require intensive work<br />

and are carried out on the weekends by all 47 inhabitants of<br />

working age, including elderly people and high school students<br />

in Noguchi community. To promote the entrustment of<br />

rice cultivation management and participation in joint farm<br />

work, the farming group has improved the distribution method<br />

of earnings by reducing the amount of land rent to farmers in<br />

the community and raising the fund for the entrustment fee<br />

and wages. The daily management fee increased from<br />

US$2,091 to $2,727 ha –1 and wages rose from $10.91 to $16.36<br />

h –1 for males and from $8.64 to $14.55 h –1 for females. Because<br />

these are very attractive rates for farmers, it was easy to<br />

secure the necessary labor force.<br />

Organic farming activities<br />

Recently, organic cultivation of high-quality rice has been encouraged<br />

in an attempt to create profitable rice farming. It is<br />

generally practiced by large, full-time farmers because organic<br />

farming requires farmers to prepare the soil by applying sufficient<br />

compost every year (20 t ha –1 in Johana), to restrict chemical<br />

application very carefully according to an agreement with<br />

buyers, and to conduct intensive nursing by continuous field<br />

observations.<br />

But farmers in Johana are mostly part-timers, and the<br />

group-farming systems play a leading role in the promotion of<br />

organic farming of rice; farmers cooperate with each other in<br />

the application of manure. Farmers also inspect paddy fields<br />

in turns to jointly make decisions about fertilizing and disease<br />

and insect control. These groups’ daily operation records were<br />

used as evidence for inspection of chemical use. On the other<br />

hand, the agricultural cooperative association in Johana did<br />

marketing promotion and made a contract of dependable selling<br />

with consumers to encourage organic farming for farming<br />

groups. By those efforts, farmers sold organic rice at a premium<br />

of $0.23 kg –1 . Now, organic farming has been introduced<br />

to 21% of the total paddy fields of the town, especially the<br />

Noguchi farming group, which has switched all of its rice production<br />

to organic cultivation.<br />

Closing remarks<br />

With this history since 1975, the Noguchi farming group has<br />

become an example of community-wide group farming in Japan.<br />

The Noguchi farming group has maintained and expanded<br />

its organization by the following four strategies (Table 2). First,<br />

the farming group was able to raise the efficiency of farm work<br />

by changing joint machine use on individual fields into joint<br />

514 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 2. Strategies of the Noguchi farming group.<br />

Strategies of the Noguchi farming group<br />

Outcomes<br />

Adoption of joint production and selling Working hours for rice<br />

of rice in the community instead of<br />

decreased to 213 h ha –1 from<br />

joint machine use in individual paddy fields. 297 h ha –1 of local average<br />

Change of distribution method of earning High wage rates:<br />

by reducing land rent and raising wage $16.36 h –1 for males,<br />

to secure necessary labor force.<br />

$14.55 h –1 for females<br />

Incorporation of group farming<br />

Renewal of tractor,<br />

allowed financing for future renewal<br />

transplanter, and combine<br />

of machines for rice cultivation.<br />

without financial support<br />

Organic rice cultivation succeeded in<br />

Farmers sold organic rice<br />

profitable farming. at a premium of $0.23 kg –1<br />

production and selling. Second, by reducing land rent payments<br />

and raising wages for farmers, farmers are encouraged<br />

to take part in joint farm work. Third, the incorporation enabled<br />

the group to have stocked earnings, which made it easier<br />

to renew farm machines. Finally, by introducing organic rice<br />

cultivation, profitable farming was obtained. With these strategies,<br />

group farming has overcome the overinvestment in machines<br />

and ineffective management, the situation that Japanese<br />

part-time farmers usually experienced, and has obtained<br />

productivity as high as that of large, full-time rice growers.<br />

That is the reason the Japanese government considers community-wide<br />

group farming to be an exemplary model of rice<br />

farming and promotes that instead of further globalization.<br />

Notes<br />

Author’s address: NARO, e-mail: kyoichi@affrc.go.jp.<br />

The role of the rice economy after the implementation<br />

of agricultural policy reform and trade liberalization<br />

from the perspective of farmers: the case of rice farmers<br />

in Java, Indonesia<br />

Roosiana<br />

<strong>Rice</strong> has traditionally been the main source of livelihood among<br />

Indonesian farmers. <strong>Rice</strong> has also remained a unique and strategic<br />

commodity, closely related to food security and economic,<br />

social, and political concerns. <strong>Rice</strong> has been the staple food<br />

for the majority of Indonesian people and still holds the highest<br />

share among consumption commodities. The rice sector<br />

employs more than 18 million farming households, or about<br />

70.8% of the total farming households in 2003, of which the<br />

farming household itself constitutes more than 48% of the total<br />

households.<br />

Because rice has an important role in the Indonesian<br />

economy, the government needs to protect both rice farmers<br />

and consumers, and assure enough rice supply to meet demand.<br />

Under the New Order administration (1969-98), the primary<br />

effort in agricultural development was devoted to increasing<br />

rice production to the point of achieving self-sufficiency.<br />

Through intensification programs, the so-called BIMAS (literally<br />

meaning mass guidance) and INMAS (literally meaning<br />

mass intensification) programs, Indonesia managed to boost<br />

rice production and achieve rice self-sufficiency in 1985. Dur-<br />

ing those periods, rice farmers mostly enjoyed subsidies, irrigation<br />

establishment, and market protection from the government.<br />

Because of the economic crisis, beginning in 1998, Indonesia<br />

introduced changes in its rice policies to include rice<br />

trade liberalization. The government opened the rice economy<br />

more to the global market. Prior New Order strategies for the<br />

rice economy were abolished gradually, including some subsidies.<br />

The rice sector has lost some protection since rice trade<br />

was liberalized in 1998, and local farmers now have to face<br />

global competition, w<strong>here</strong>as the government strategy has<br />

shifted to food security rather than self-sufficiency.<br />

This development has necessitated more research to examine<br />

the performance of the rice economy as affected by food<br />

security strategies, mostly from a macroeconomic point of view.<br />

T<strong>here</strong> are only a few studies on farmers whose lives revolve<br />

mainly around rice as their main livelihood. Using the case<br />

study approach, this paper attempts to investigate the role of<br />

the rice economy given some rice policy reforms made, from<br />

the perspective of Indonesian rice farmers in Java that histori-<br />

Session 18: Impact of globalization on rice farmers 515


cally were the country’s main rice producers. Likewise, the<br />

study tries to determine some factors that influence the performance<br />

of the rice economy at the farm level, such as equity<br />

aspects.<br />

The study area and sample and data collection<br />

With growing attention to data quality and cost-effectiveness,<br />

small-sample surveys were designed to obtain comparative data<br />

for relatively developed areas of rice farming. These villages<br />

were in Central Java and Yogyakarta provinces, which were<br />

purposely selected to represent current and common conditions<br />

of rice farmers in Java. The selected villages, Gelaran I<br />

hamlet of Bejiharjo and Karangtengah hamlet of Karangtengah<br />

village in Gunungkidul Regency, Sedayu hamlet of Awonggo<br />

village in Magelang Regency, and Ceporan and Towangsan in<br />

Klaten Regency, represented relatively developed rice-farming<br />

areas in Java.<br />

Respondents were selected purposely from a number of<br />

rice farmers who were available during the surveys. All respondents<br />

were farmers working in their own fields. Of the<br />

total of 101 respondents, 21 were from Bejiharjo village, 25<br />

from Karangtengah village, 25 from Awonggo village, and 30<br />

from Ceporan and Towangsan villages. A coded questionnaire<br />

containing two major parts was formulated. The first part had<br />

questions dealing with general information on the farming<br />

household, its activities, and general social and economic conditions.<br />

Questions in the second part asked farmers to recall<br />

their conditions before 1998 in comparison with recent conditions.<br />

Role of the rice economy for farmers<br />

As has been implied in prior sections, the main role of rice for<br />

paddy farmers has been closely related to the household’s income.<br />

In the past, farmers could have a larger rice field than<br />

now; t<strong>here</strong>fore, farmers could rely on rice as the main source<br />

of livelihood. As generations have passed and land has been<br />

shared with more people, especially by inheritance, farmers<br />

who hold land have increased in number. However, the size of<br />

landholding for each individual farmer has decreased over<br />

generations.<br />

Field surveys indicated that 84 out of 101 respondents<br />

(83.17%) were farmers with a landholding of less than 0.5 ha.<br />

The rest of the respondents had less than 1 ha of rice field.<br />

Most respondents were rice farmers who always spent their<br />

lives in the field everyday, and who have been rice farmers for<br />

more than 20 years. Only 16 farmers of the 101 respondents<br />

had other nonrice agricultural activities besides rice cultivation<br />

as their main source of income.<br />

The surveys tried to find out what farmers thought about<br />

the role of the rice economy in their livelihood, particularly<br />

after the policy reform, and most of them still considered rice<br />

as their main source of livelihood. However, since their fields<br />

were small, they used some portions from the harvest for their<br />

own consumption and for social and community purposes.<br />

Farmers must have other assets such as livestock for extra expenses.<br />

As a matter of fact, those farmers still keep growing<br />

rice more as a tradition than to make a profit.<br />

<strong>Rice</strong> performance and equity<br />

Economic development today gives more attention to the relation<br />

between equity and efficiency (Baldassarri and Piga 1996).<br />

While development in the rice economy achieved efficiency<br />

goals with increased rice production, equity objectives seemed<br />

to be left behind, particularly for rice farmers. Studies on equity<br />

in the Indonesian rice economy are still few. Prior studies<br />

suggested that factors affecting equity in the Indonesian rice<br />

economy mostly came from technological changes and rice<br />

strategies. Jatileksono (1987) in his study about equity achievement<br />

concluded that technology changes worsened income<br />

distribution between favorable and unfavorable areas unless<br />

modern varieties along with irrigation expanded to the unfavorable<br />

areas. Another study by Naylor (1991) stated that primarily<br />

rice producers, a high-income group, benefited from<br />

the transfer effects of government strategies in rice prices and<br />

irrigation investment. In contrast to national-level studies, our<br />

study focuses on the performance of the rice economy regarding<br />

equity at the farm level. Based on survey findings, our<br />

study presents three factors affecting equity of the rice economy<br />

after the policy reform of 1998. These factors were landholding,<br />

the rice selling price and prices of consumption goods,<br />

and an assessment of modern technologies and new information.<br />

Landholding. Landholding has become crucial for traditional<br />

rice farmers. T<strong>here</strong> were no changes in the<br />

size of land ownership after the reform. Even though<br />

productivity was quite high, on average 4–5 t ha –1 of<br />

unhusked dry rice, with a small piece of land, it was<br />

difficult for farmers to improve their level of welfare.<br />

The rice selling price and prices of consumption<br />

goods. Except for farmers of Ceporan and Towangsan<br />

villages, farmers had a rice selling price that was<br />

slightly higher than the floor price. However, the<br />

prices of consumption goods have moved higher than<br />

the profit gained from rice cultivation. As a result,<br />

income from rice was not sufficient to pay for public<br />

services such as education for children and health<br />

services. <strong>Rice</strong> policy reform thus did not bring significant<br />

changes to intervening prices for better farmers’<br />

welfare.<br />

Technology changes and new information. Based on<br />

survey results, it was found that rice production after<br />

the reform did not change much. Some farmers increased<br />

their rice production per ha, but most of them<br />

did not. The cropping pattern during the year also<br />

remained the same, and was not affected by the reform,<br />

which eliminated subsidies and incentives given<br />

to farmers. However, with the higher cost of inputs,<br />

when production was low and the rice selling price<br />

was not high, farmers had almost no ability to make<br />

516 <strong>Rice</strong> is life: scientific perspectives for the 21st century


savings to improve their economy. When the opportunity<br />

to expand their fields was small, rice farmers<br />

could optimize field cultivation by applying technology<br />

changes and new information in rice farming and<br />

income generation. However, limited assessment was<br />

made of this.<br />

Concluding remarks<br />

Agricultural policy reform and trade liberalization since 1998<br />

have brought about some changes in rice strategies that led to<br />

less protection and fewer incentives for rice farmers. Results<br />

of the field surveys in five villages in Central Java and<br />

Yogyakarta provinces showed that rice farmers still considered<br />

rice as their main source of income despite insufficiency<br />

in income generation from rice cultivation. The present situation<br />

of rice at the farm level suggested three factors that affected<br />

equity achievement: landholding, the rice selling price<br />

and prices of consumption goods, and technology changes and<br />

new information. An assessment of rice farmers regarding these<br />

three factors is indeed necessary, particularly to improve their<br />

level of welfare.<br />

References<br />

Baldassarri M, Piga G. 1996. Distributive equity and economic efficiency:<br />

trade-off and synergy. In: Baldassarri M, Paganetto L,<br />

Phelps ES, editors. Equity, efficiency and growth: the future<br />

of the welfare state. Hampshire and London (UK): MacMillan<br />

Press Ltd. p 257-275.<br />

Jatileksono T. 1987. Equity achievement in the Indonesian rice<br />

economy. Yogyakarta (Indonesia): Gadjah Mada University<br />

Press. 120 p.<br />

Naylor R. 1991. Equity effects of rice strategies. In: Pearson S, Falcon<br />

W, Heytens P, Monke E, Naylor R, editors. <strong>Rice</strong> policy in<br />

Indonesia. Ithaca, N.Y. (USA): Cornell University Press.<br />

p 138-161.<br />

Notes<br />

Author’s address: Graduate School of <strong>International</strong> Development,<br />

Nagoya University Furo-cho, Chikusa-ku, Nagoya 464-8601,<br />

Japan, e-mail: m020109d@mbox.nagoya-u.ac.jp.<br />

El Niño sensitivity, resource endowment, and socioeconomic<br />

characteristics: the case of wetland rice in Java, Indonesia<br />

Shigeki Yokoyama and Bambang Irawan<br />

Objectives and method<br />

Regional factors influencing climatic vulnerability were analyzed<br />

at the subdistrict (kecamatan) level on Java island of<br />

Indonesia in the case of the 1997-98 El Niño. Out of 1,454<br />

subdistricts w<strong>here</strong> wetland rice grows, area loss was observed<br />

in 58%, with an average rate of –6.9% per subdistrict. Most of<br />

them were located in the highland regions of the southern parts<br />

of West and Central Java provinces.<br />

The principal component analysis was applied to clarify<br />

the local characteristics that determine El Niño vulnerability.<br />

The analysis incorporated 16 variables of four categories: (1)<br />

natural conditions, (2) level of infrastructure, (3) household<br />

characteristics, and (4) farming performance. The data were<br />

obtained from the Central Bureau of Statistics and came from<br />

four publication series: (1) Land use in Java, (2) Agricultural<br />

census 1993, (3) Potency of villages, and (4) Annual reports<br />

from the agricultural offices of Kabupaten in Java. The description<br />

of variables is as follows.<br />

Natural conditions<br />

X1: Percentage of villages with altitude


Table 1. Coefficient of principal factors and their correlations with variables. a<br />

Item<br />

Principal factor<br />

F1 F2 F3 F4 F5 F6 F7<br />

Factor coefficient 4.353 2.441 1.713 1.020 0.912 0.851 0.818<br />

Factor contribution (%) 27.2 15.3 10.7 6.4 5.7 5.3 4.6<br />

Cumulative contribution (%) 27.2 42.5 53.2 59.5 65.2 70.6 75.2<br />

Coefficient of correlation of principal factors and variables<br />

X1 –0.497 0.004 –0.126 0.033 0.004 –0.018 0.002<br />

X2 0.088 0.043 0.007 0.050 0.494 –0.034 0.022<br />

IN1 –0.549 0.010 0.185 0.006 0.037 –0.001 –0.012<br />

IN2 –0.630 –0.077 –0.035 0.001 0.001 0.014 –0.114<br />

IN3 0.575 0.013 0.087 –0.009 0.002 0.002 0.152<br />

IN4 –0.012 0.558 0.082 –0.147 0.013 0.051 0.001<br />

IN5 0.094 –0.541 –0.040 0.149 –0.004 0.059 0.016<br />

IN6 0.159 –0.070 0.146 0.159 0.073 0.004 –0.211<br />

IN7 –0.001 0.183 0.597 –0.037 –0.115 –0.081 –0.019<br />

IN8 –0.211 –0.002 0.072 0.105 –0.012 0.474 0.010<br />

HH1 –0.596 0.076 0.184 0.021 0.002 0.017 0.003<br />

HH2 –0.518 0.125 0.139 0.011 0.004 0.027 0.002<br />

HH3 0.003 –0.681 0.011 –0.039 0.024 0.015 0.001<br />

HH4 –0.174 –0.506 0.009 –0.564 0.005 0.007 0.083<br />

R1 0.095 –0.074 0.462 0.003 –0.188 –0.042 0.001<br />

R2 –0.368 –0.035 0.006 –0.059 –0.016 0.003 0.171<br />

a Boldface = high coefficient of correlation.<br />

Wetland rice performance<br />

R1: Crop intensity per year (%)<br />

R2: Yield (kg ha –1 )<br />

Results of principal component analysis and grouping<br />

Results of principal component analysis show that 75% of the<br />

total variance could be explained by seven principal factors<br />

(Table 1). The first factor, highly correlated to variables X1,<br />

IN1, IN2, IN3, HH1, and HH2, represents production conditions,<br />

contributing 27% to the total variance. The second factor,<br />

related to IN4, IN5, HH3, and HH4, stands for social infrastructure.<br />

The third factor, related to IN7 and R1, indicates<br />

technological level and productivity. The fourth factor, related<br />

to HH4, could be interpreted as social structure. The fifth factor,<br />

related to X2, indicates rainfall. Those five factors, being<br />

able to explain about 65% of the total variance, are used for<br />

kecamatan grouping.<br />

Table 2 shows the grouping of kecamatans based on five<br />

principal factors. The comparison of mean values of variables<br />

between groups shows that several variables were highly correlated<br />

to one another. For instance, kecamatans with the most<br />

villages located in regions with altitude of 500 m or in upland regions<br />

(G2 and G3). Wetland rice yield in lowland kecamatans was<br />

also higher than in upland ones because the former generally<br />

had better irrigation networks. This was clarified by the higher<br />

proportion of technical irrigated land in lowland regions (IN2).<br />

G2 and G3 were both located in upland regions and had<br />

high annual rainfall, though several other variables showed<br />

differences between the two. G2 was relatively high in IN4 (%<br />

of villages with paved main road) but relatively low in IN5<br />

(number of households to number of cars), IN7, IN8, HH3,<br />

and R1. This means that G2 and G3 had a different level of<br />

infrastructure, household landholding, and crop intensity for<br />

wetland rice, even though they had similar natural resource<br />

endowments.<br />

A similarity of natural resource endowments is also observed<br />

for G1 and G4. Both groups were located in lowland<br />

regions and had relatively low annual rainfall. However, G1<br />

had a better transportation infrastructure (IN4) and larger average<br />

farm size (HH1 and HH2) than G4. In contrast, G4 had<br />

a higher crop intensity for wetland rice than G1.<br />

Rainfall decrease, area decrease, and vulnerability<br />

The rainfall decrease caused by El Niño varies by locality because<br />

of the difference in natural resource endowments. However,<br />

at a homogeneous level of rainfall decrease, production<br />

loss might differ, depending on farmers’ capability to cope with<br />

the effects of a rainfall decrease on their agricultural production.<br />

The farmers’ ability to adjust to a rainfall decrease is a<br />

function of the characteristics of farmers’ households, infra-<br />

518 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 2. Rainfall decrease, area decrease, and vulnerability index by group of kecamatans.<br />

Group of kecamatans<br />

Variable Description of variable Lowland area Upland area<br />

G1 G4 G2 G3<br />

Characteristics of kecamatans<br />

IN4 Percentage of villages with paved main road (%) High Low High Low<br />

IN5 Ratio of number of households to number of cars Low Low Low High<br />

IN6 Ratio of wetland area to number of water pumps Low Low Moderate High<br />

IN7 Ratio of wetland area to number of agicultural input kiosks High High Low High<br />

IN8 Percentage of villages accessible to mass transportation High High Low High<br />

HH1 Ratio of wetland area to farmland High Moderate Low Low<br />

HH2 Mean wetland size (ha per farm household) High Moderate Low Low<br />

HH3 Percentage of farm households with wetland size<br />


Comparison between groups G1 and G4, both lowland<br />

regions, shows similar results. The higher vulnerability index<br />

of group G4 than group G1 was accompanied by a lower transportation<br />

infrastructure (IN4) and farm size (HH1 and HH2)<br />

and higher crop intensity (R1).<br />

Summary and conclusions<br />

The subdistricts of Java island, Indonesia, were grouped into<br />

four based on the combination of location and crop intensity:<br />

G1 (low altitude [well irrigated], low crop intensity), G2 (high<br />

altitude [less irrigated], low crop intensity), G3 (high altitude<br />

[less irrigated], high crop intensity), and G4 (low altitude [well<br />

irrigated], high crop intensity). Because of the higher rainfall<br />

decrease and poor irrigation, the impact of the area decrease is<br />

higher on highlands (G2, G3). While El Niño sensitivity, defined<br />

as A/R (A: percentage of area loss, R: percentage of rainfall<br />

reduction), is higher in G3 and G4, w<strong>here</strong> more rice is<br />

cultivated in the dry season compared to G1 and G2. This finding<br />

is consistent with the fact that El Niño-induced drought<br />

was more prominent in the dry season of 1997. Other characteristics<br />

of an area highly sensitive to El Niño are (1) remoteness<br />

or poor transportation infrastructure, (2) lower availability<br />

of water pumps, (3) lower availability of input kiosks, and<br />

(4) high proportion of small farms (less than 0.5 ha). As expected,<br />

areas with good infrastructure are less vulnerable to<br />

climatic shocks, while smaller farms are more vulnerable.<br />

Notes<br />

Authors’ addresses: Shigeki Yokoyama, National Agriculture & Biooriented<br />

<strong>Research</strong> Organization, Japan, Kannondai 3-1-1,<br />

Tsukuba, Ibaraki, Japan; Bambang Irawan, Indonesian Center<br />

for Agro Socio-Economic <strong>Research</strong> and Development, Jalan<br />

A. Yani No. 70, Bogor, Indonesia, e-mail:<br />

syokoyam@affrc.go.jp.<br />

Global competitiveness of medium-quality Indian rice:<br />

a PAM analysis<br />

B.V. Chinnappa Reddy, M.S. Raghavendra, and Lalith Achoth<br />

During the last five decades, rice area in India has increased<br />

from 20 million to about 45 million hectares and rice production<br />

from 22 million to 90 million tons. Productivity increased<br />

from 700 to 2,000 kg ha –1 . <strong>Rice</strong> is a major cereal for more<br />

than 70% of the world’s poor in Asia, w<strong>here</strong> more than 90% of<br />

rice production and consumption take place. Despite the rapid<br />

expansion of rice trade globally, as argued by Gulati and<br />

Narayanan (2003), the world rice market is characterized by<br />

thinness, volatility, and segmentation. <strong>Rice</strong> markets are affected<br />

by distortions caused by a plethora of controls imposed by<br />

both developed and developing countries because of various<br />

political, economic, and food security compulsions. In the long<br />

run, trade liberalization is likely to benefit both consumers and<br />

producers in developing countries, in addition to the availability<br />

of cheaper grain in the importing countries (Gulati and<br />

Naranayan 2003).<br />

India is a traditional exporter of high-quality basmati<br />

rice. But the export of nonbasmati rice was rather small in<br />

earlier years, as it was not export-competitive (Chand 2002).<br />

However, the devaluation of the Indian rupee drastically altered<br />

the export scenario of the country. This was followed by<br />

a gradual relaxation of restrictions on the export of rice, which<br />

resulted in a gradual increase in exports of medium-quality<br />

rice. To assess the export potential and consequent welfare<br />

gain from rice, it is mandatory to assess the export competitiveness<br />

of medium-quality rice. As Karnataka symbolizes<br />

medium-quality rice production in the country, we have chosen<br />

this state for assessing the export competitiveness and concomitant<br />

welfare gain due to the export trade of rice.<br />

Methodology<br />

Policy matrix analysis<br />

The trade competitiveness of Indian medium-quality rice was<br />

analyzed using the framework of the policy analysis matrix<br />

(PAM) as proposed by Monke and Pearson and presented by<br />

Yao (1997). To construct the PAM, world prices (free on board,<br />

FOB, for exports, and cost, insurance, and freight, CIF, for<br />

imports) were used. For domestic factors, which are not traded<br />

internationally, social costs (Pxi) were calculated using the<br />

value of marginal product approach that uses factor shares (Si)<br />

of various inputs (Xi) together with the mean value of inputs<br />

and outputs (Y) and price (Py). Social cost was obtained as<br />

Pxi = { (Si/Xi) × Y} × Py. The nontradable inputs considered<br />

were labor (human and bullock), farmyard manure, and rental<br />

value of land. The tradable inputs were seed, fertilizers, and<br />

pesticides.<br />

Nominal protection coefficients (NPCs), effective protection<br />

coefficients (EPCs), and domestic resource cost (DRC)<br />

were computed to reveal trade competitiveness. Trade competitiveness<br />

was estimated using the above three measures for<br />

rice in India using the data from Karnataka on the importable<br />

hypothesis for the two periods, preliberalization (1985-86 to<br />

1991-92) and postliberalization (1996-97 to 2000-01).<br />

NPC was calculated as a ratio between the domestic price<br />

and the international price of a comparable grade of rice, adjusted<br />

for all the transfer costs such as freight, insurance, handling<br />

costs, margins, losses, etc.<br />

520 <strong>Rice</strong> is life: scientific perspectives for the 21st century


EPC for rice was defined as EPCi = (VA i<br />

d<br />

/VA i b ) w<strong>here</strong><br />

VA i<br />

d<br />

is the value added of output i at domestic prices and VA i<br />

b<br />

is the value added of output i at border prices.<br />

DRC was obtained as DRC = a ij v j /(P i<br />

b<br />

– a ij P i b ) w<strong>here</strong> a ij<br />

(j = K + 1 to n) is the technical coefficient (input use per unit<br />

of output) for domestic resource (nontraded intermediary input),<br />

j is the production of output i, and v j is the shadow price<br />

of such an input.<br />

The cost of cultivation data needed for computing the<br />

PAM were collected from the Directorate of Agriculture, Government<br />

of Karnataka, Bangalore. The international reference<br />

price of the crop was collected from various issues of the FAO<br />

production yearbook and from the FAO Web site.<br />

Partial equilibrium analysis<br />

The extent of price distortions created by the policies in the<br />

face of free trade was computed and likely gain or loss to producers<br />

and consumers was also estimated. A partial equilibrium<br />

approach proposed by Lutz and Scandizzo (1980) was<br />

used to evaluate the impact of the price changes on demand,<br />

supply, and welfare based on the following measures:<br />

1. Net social loss in production (NSLp)<br />

NSLp = ½ (Qw – Q) (Pw – Pp)<br />

2. Net social loss in consumption (NSLc)<br />

NSLc = ½ (Cw – C) (Pw – Pc)<br />

3. Total net social loss (NSL)<br />

NSL = NSLp + NSLc<br />

4. Welfare gain of producers (Gp)<br />

Gp = Q (Pp – Pw) – NSLp<br />

5. Welfare gain of consumers (Gc)<br />

Gc = Q (Pw – Pc) – NSLc<br />

6. Net effect of liberalization on welfare in the state<br />

Q (Pp – Pw) – Q (Pw – Pc)<br />

7. Change in government revenue<br />

dG = (NSLp + NSLc) – Gp – Gc<br />

w<strong>here</strong> Qw = production at world prices, Q = production at<br />

domestic prices, Pw = border prices, Pp = price faced by domestic<br />

producers, Pc = price faced by domestic consumers,<br />

Cw = consumption at world prices, and C = consumption at<br />

domestic prices.<br />

The basic parameters of supply and demand elasiticies<br />

needed for this evaluation were drawn from a study by Reddy<br />

(1997). To compute production values, the wholesale price of<br />

rice was used. For consumption values, the retail price was<br />

used. The world reference prices were derived from the international<br />

price and adjusted for transportation, marketing, and<br />

trading margins.<br />

Results and discussion<br />

Trade competitiveness of Indian rice<br />

Trade competitiveness of a commodity reveals whether a country<br />

has an opportunity to engage in export trade. It is interesting<br />

to observe that rice, which is the major crop in Karnataka<br />

State, had been largely competitive on an importable basis with<br />

its NPC values being below unity during the reference period.<br />

Table 1. Results of a policy analysis matrix (PAM) of rice.<br />

Year NPC a EPC DRC SRP<br />

1985-86 0.81 1.19 0.95 0.62<br />

1986-87 0.89 1.20 0.99 0.52<br />

1987-88 0.81 1.12 0.91 0.42<br />

1988-89 0.68 0.91 0.76 0.25<br />

1989-90 0.63 0.76 0.63 0.10<br />

1990-91 0.65 0.82 0.70 0.17<br />

1991-92 0.66 0.79 0.68 0.11<br />

Average b 0.74 1.00 0.82 0.35<br />

1992-93 0.77 0.97 0.82 0.35<br />

1993-94 0.65 0.88 0.73 0.20<br />

1994-95 0.69 1.00 0.79 0.32<br />

1995-96 0.64 1.00 0.78 0.27<br />

1996-97 0.67 0.93 0.77 0.27<br />

1997-98 0.55 0.68 0.53 0.04<br />

1998-99 0.52 0.61 0.49 –0.05<br />

1999-2000 0.53 0.59 0.49 –0.07<br />

2000-01 0.64 0.84 0.59 0.15<br />

Average c 0.58 0.73 0.58 0.07<br />

a<br />

NPC = nominal protection coefficients, EPC = effective protection coefficients,<br />

DRC = domestice resource cost, SRP = subsidy ratio to producer<br />

coefficient. b Average of 1985-86 to 1991-92. c Average of 1992-<br />

93 to 2000-01.<br />

EPC estimates showed that, in only five years during the 17-<br />

year reference period, it was more than 1, indicating that the<br />

state had protected the crop only in those years. However, for<br />

the reference period, the average EPC revealed that Karnataka<br />

is an efficient producer of rice (Table 1). Over the years, EPC<br />

had been declining, which implies an increasing rate of competitiveness<br />

of rice. This could be due to the emergence of<br />

efficient production technology and the impact of economic<br />

reforms in the country.<br />

The estimates of DRC revealed that the state had a comparative<br />

advantage in rice production (DRC was below 1). The<br />

level of DRC shows that the value of domestic resources used<br />

in producing 1 ha of rice in Karnataka was less than the cost of<br />

its import. DRC level decreased in the postliberalization period,<br />

which reveals an improvement in the comparative advantage<br />

of rice production in recent years. The subsidy ratio<br />

to producer coefficient (SRP), which was computed to analyze<br />

the degree of state protection for the rice crop, was 0.07<br />

for the state for the period 1996-97 to 2000-01. This implies<br />

moderate state protection for rice production. However, the<br />

levels of incentives provided to farmers are very meager compared<br />

to the magnitude of protection in developed countries.<br />

Welfare gains and welfare losses because<br />

of liberalization<br />

The results of an analysis of the impact of trade liberalization<br />

are presented in Table 2. These are estimated based on derived<br />

elasticities and on the estimated NPCs. The supply elasticity<br />

used for the analysis was 0.10 for rice. The loss to society<br />

because of liberalization of rice trade was estimated at<br />

around Rs. 5,800. The loss to society because of inefficiency<br />

in production resulting from a rise in the price was Rs. 4,200.<br />

Session 18: Impact of globalization on rice farmers 521


Table 2. Welfare impact of rice trade liberalization. a<br />

Net monetary effects of price distortions on rice in Karnataka<br />

NSLp NSLc NSL Estimated welfare gain Estimated welfare loss Net effect of<br />

(Rs.) (Rs. 000) (Rs. 000) of producers, WGp of consumers, WGc Liberalization on<br />

(Rs. million) (Rs. million) welfare in the state<br />

4,200 1,600 5,800 7,718.55 2,864.35 4,854.20<br />

Gains and losses because of projected changes in prices resulting from<br />

Value of production Percentage of WGp Value of consumption Percentage of WGc to value<br />

at Pp (v) (Rs. million) to value of production at Pc (w) (Rs. million) of consumption<br />

36,219.80 21.31 41,074.00 6.97<br />

Production and consumption effects of price changes of selected commodities in Karnataka<br />

Production Consumption Estimated change Estimated change<br />

(million t) (million t) in production (million t) in consumption<br />

4.19 2.94 0.453 0.799<br />

a US$1 = Rs. 46.00.<br />

The effects of price distortion on production and consumption<br />

are additive with respect to trade effects. For Karnataka, the<br />

liberalization of agriculture would result in a change in production<br />

because of the change in prices. <strong>International</strong> prices<br />

adjusted for transportation costs were higher by 21% than domestic<br />

prices during the postliberalization period (2001-02).<br />

These higher world prices would result in increased domestic<br />

production of the crop to the extent of 0.453 million t of rice.<br />

But, higher international prices would result in a decrease in<br />

rice consumption of 0.799 million t.<br />

Welfare gains were much larger than the respective welfare<br />

losses. Results revealed that welfare gains to producers<br />

were 21.31% (Rs. 7,718.55 million) of the total value of production.<br />

Conversely, consumers in the state and region incurred<br />

substantial welfare loss because of the rise in rice prices (Rs.<br />

2,864.35 million) in 2001-02.<br />

Conclusions<br />

The study shows that liberalization will benefit the rice sector<br />

in terms of giving farmers a better deal. Consumers may have<br />

to pay a higher price because of the limited domestic supply<br />

and increase in prices. The positive impact on the farming community<br />

may lead to more efficient rice production and in the<br />

process increase the export prospects of rice.<br />

References<br />

Chand R. 2002. Trade liberalisation, WTO and Indian agriculture.<br />

New Delhi (India): Mittal Publications.<br />

Gulati A, Narayanan S. 2003. <strong>Rice</strong> trade liberalization and poverty.<br />

In: Mew TW, Brar DS, Peng S, Dawe D, Hardy B, editors.<br />

<strong>Rice</strong> science: innovations and impact for livelihood. Manila<br />

(Philliphines): <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>. p 939-<br />

956.<br />

Lutz E, Scandizzo P. 1980. Price distortions in developing countries:<br />

a bias against agriculture. Eur. Rev. Agric. Econ. 7:5-<br />

27.<br />

Reddy BDR. 1997. Dynamics of cropping pattern in dry zones of<br />

Karnataka and implications of global trade liberalisation. PhD<br />

thesis. University of Agricultural Sciences, Bangalore, India.<br />

Yao S. 1997. Comparative advantages and crop diversification: a<br />

policy analysis matrix for Thai agriculture. J. Agric. Econ.<br />

48:211-222.<br />

Notes<br />

Authors’ address: Department of Agricultural Economics, University<br />

of Agricultural Sciences, GKVK, Bangalore 560 065,<br />

India, e-mail: batlahalli@yahoo.com.<br />

522 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Behavior and strategies of Japanese rice producers<br />

under globalization<br />

Masaki Umemoto<br />

In 2002, the domestic supply of Japanese rice consisted of<br />

8.876 million tons of production and 0.77 million t of minimum<br />

access import. <strong>Rice</strong> was cultivated on 1.688 million ha.<br />

To maintain the crop’s taste, farmers have not been pursuing<br />

high yield, but, thanks to good weather, the average rice yield<br />

was 5.27 t ha –1 and almost constant since 1994. On the other<br />

hand, domestic demand for rice decreased from 10.26 million<br />

t (1992) to 8.95 million t (2002). Japanese per capita rice consumption<br />

decreased drastically from 1960 to 1980, and this<br />

considerable decrease in rice consumption still continues. It is<br />

also important to notice that, in that period, the producers’ price<br />

of rice fell, corresponding to the decrease in demand (Fig. 1).<br />

This shows that the consumption of rice itself is diminishing.<br />

The decreasing demand together with the high average<br />

yield necessitate a reinforcement of rice supply adjustment. In<br />

2002, the set-aside area of rice production reached 39% of<br />

paddy fields. T<strong>here</strong>fore, to convert crops from rice, a lot of<br />

subsidy was paid to farmers. The government expended<br />

US$2.467 billion for this rice supply adjustment program in<br />

2002, and it occupied one-half of financial expenditures related<br />

to rice policy. Consequently, a decrease in these expenditures<br />

became an urgent issue.<br />

On the other hand, in 1992, the government designed a<br />

structural change in arable farming, targeting 80,000 farms cultivating<br />

20 ha each, with a target of sharing 60% of paddy<br />

fields by 2020. Nevertheless, in 2000, the share of the rice<br />

crop area cultivated by large-scale farms (more than 5 ha of<br />

rice crop area) was only 14%. This means that the accumulation<br />

of farmland for core farmers is stagnant and structural<br />

adjustment has not progressed as the government expected.<br />

These facts show that nowadays t<strong>here</strong> are three main issues<br />

in Japanese rice production. First, market-oriented rice<br />

production is required. It is especially essential to grasp market<br />

needs and seek out new demand for rice. Second, the conversion<br />

from rice to other crops in paddy fields should be reinforced<br />

to achieve a rice supply adjustment. It is also important<br />

to increase the rate of food self-sufficiency. Third, the government<br />

needs to tackle reform of the production structure by encouraging<br />

large-scale farmers.<br />

Japanese rice policy reform and objectives of this paper<br />

To solve these problems, the government launched a <strong>Rice</strong><br />

Policy Reform in April 2004. By implementing the policy, the<br />

government expected to cope with market globalization through<br />

a remarkable change from the existing rice supply adjustment<br />

program. The government abolished the set-aside program to<br />

achieve efficient land resource allocation for rice production<br />

<strong>Rice</strong> crop area (000 ha)<br />

Producers’ rice price (US$ t –1 )<br />

3,000<br />

2,750<br />

2,500<br />

2,250<br />

2.000<br />

1,750<br />

<strong>Rice</strong> crop area<br />

<strong>Rice</strong> yield<br />

Set-aside area (000 ha)<br />

Demand for rice (10,000 t)<br />

<strong>Rice</strong> yield (kg ha –1 )<br />

1,100<br />

Set-aside area<br />

Demand<br />

<strong>Rice</strong> price<br />

1,000<br />

900<br />

800<br />

700<br />

600<br />

1,500<br />

500<br />

1994 1996 1998 2000 2002<br />

1995 1997 1999 2001<br />

Year<br />

Fig. 1. Trend of Japanese rice supply, demand, and price. Source:<br />

References for rice production Production Bureau, Ministry of Agriculture,<br />

Forestry, and Fisheries.<br />

under market mechanisms by 2010. The government also aims<br />

to encourage large-scale farms. T<strong>here</strong>fore, the government is<br />

now considering a conversion from a price-support policy to<br />

direct payment for targeted farmers.<br />

This paper discusses the reactions and strategies of Japanese<br />

rice producers responding to various economic and political<br />

changes. Whether the structure of Japanese rice farming<br />

will change as the government hopes depends highly on farmers’<br />

responses. T<strong>here</strong>fore, it is essential to understand farmers’<br />

strategies in their specific socioeconomic context. Reactions<br />

to policy and market conditions differ according to farming<br />

types. T<strong>here</strong>fore, first I describe the major farming types of<br />

rice producers. Next, I discuss their socioeconomic characteristics<br />

and behavior. Finally, I conclude with the future perspectives<br />

of Japanese rice production and the necessary conditions<br />

for changes in agricultural structure.<br />

Major farming types of rice producers and their behavior<br />

Japan has various types of rice producers such as the part-time<br />

family farm, large-scale family farm, agricultural corporate<br />

firm, group-farming organization based on the rural community,<br />

farm contractor, rural agricultural public corporation, and<br />

agricultural cooperative. However, the following four types<br />

Session 18: Impact of globalization on rice farmers 523


are the major rice producers: part-time family farm, groupfarming<br />

organization based on the rural community, large-scale<br />

family farm, and agricultural corporate firm.<br />

The part-time family farm is still a major rice producer<br />

in Japan, and its number was 2.76 million in 2000. It works on<br />

rice production during days off and earns its main income from<br />

nonagricultural jobs. The part-time family farm has a priority<br />

to maintain paddy fields as the family estate inherited from<br />

predecessors and not to consider profits from rice production.<br />

T<strong>here</strong>fore, this farm might increase rice crop areas to correspond<br />

to the abolishment of the set-aside program, and, even<br />

if the rice price falls, some of them will continue rice production.<br />

But, the number of part-time family farms is gradually<br />

decreasing according to the aging of farmers. The young generation<br />

especially hesitates to do work with the rice crop.<br />

Group-farming organizations based on the rural community<br />

mainly consist of part-time family farms, but their activities<br />

can be regarded as an improvement of productivity and<br />

reconstruction of regional farming. The common features of<br />

group farming are the collective ownership of machinery and<br />

facilities, joint work on rice cultivation, and regional adjustment<br />

of land use. The purposes of this group farming are to<br />

reduce production costs and maintain paddy fields. The number<br />

of group-farming organizations was only 9,961 in 2000.<br />

Recently, however, the leading actors of rural areas such as<br />

the personnel of agricultural cooperatives or agricultural extension<br />

services are actively encouraging farmers to organize<br />

group farming. Meanwhile, the government is promoting groupfarming<br />

organizations to formalize as a corporate body because<br />

the government assumes that the corporate body is a<br />

more suitable economic entity than the group-farming organization.<br />

It is expected that the number of group-farming organizations<br />

will increase, resulting in a rationalization of rice<br />

production, while the conversion of group-farming organizations<br />

to corporate bodies that pursue profit seems difficult.<br />

Large-scale family farms and agricultural corporate firms<br />

are keenly interested in increasing farm size and diversifying<br />

their business vertically and/or horizontally. Both types are<br />

expected to be leading rice producers. The large-scale family<br />

farm is mainly managed and worked by family labor. Meanwhile,<br />

agricultural corporate firms employ nonfamily members<br />

and assign them some management work. The farm sizes<br />

of large-scale family farms are 10 to 20 ha, and two or three<br />

family members usually cultivate rice, wheat, soybean, and<br />

feed crops. On the other hand, agricultural corporate firms are<br />

50 to 100 ha, and their investment in machinery and facilities<br />

is three to five times as much as that of the family farm.<br />

The large-scale family farm mainly aims at expanding<br />

rice, wheat, and soybean crop area to reduce production costs<br />

and increase farm income. Meanwhile, agricultural corporate<br />

firms are pursuing both diversified agribusiness and expansion<br />

of farm size. Through these strategies, they manage to<br />

keep enough working time for full-time employees.<br />

These two types have several different characteristics,<br />

but both equally reinforce marketing. First, they usually sell<br />

polished rice to consumers or retail stores directly. Second,<br />

some of them address the production of organic rice and/or<br />

chemicals used in rice. Japanese consumers have recently paid<br />

attention to food safety and to labeling (production areas, varieties),<br />

taste, and price level. So, to meet these consumers’<br />

needs, producers are trying to supply branded products. Third,<br />

they are introducing a traceability system for their products<br />

because many Japanese consumers require information on the<br />

quality of rice and its cultivation methods. Finally, they invite<br />

their customers (consumers, retailers) to their farms for interpersonal<br />

contact to keep clients in good standing. These Japanese<br />

rice producers’ strategies are effective for advantageous<br />

marketing, resulting in higher profitability of rice production.<br />

The future of Japanese rice production<br />

From the review of major rice producers’ strategies, we summarize<br />

our conclusions. To resolve the first three issues, such<br />

as the decrease in rice demand, conversion from rice crops in<br />

paddy fields, and structural change, it is important to encourage<br />

the large-scale family farms and agricultural corporate firms<br />

by supporting their strategies. T<strong>here</strong>fore, whether Japanese rice<br />

farming copes with globalization and the changes in farming<br />

circumstances depends on how much and how fast those viable<br />

producers dominate production.<br />

But the <strong>Rice</strong> Policy Reform, which abolished the compulsory<br />

set-aside program, might lead to an increase in supply,<br />

resulting in a drop in price. Core farmers are most susceptible<br />

to a drop in price. Figure 2 shows the effects of a price drop<br />

for large-scale farms. The <strong>Rice</strong> Policy Reform prepared a compensation<br />

program for rice income in the case of a price drop,<br />

but the amount that farmers receive from that policy is limited,<br />

within about 10% of existing rice income. T<strong>here</strong>fore, even for<br />

a 20-ha farm, if the rice price declines to under $2.70 per kg<br />

(the price level in September 2004), it will be difficult to gain<br />

comparable income with nonagricultural work. Especially in<br />

the case of smaller farms (15 ha, 10 ha), at each price they<br />

couldn’t get enough income. Additionally, if the government<br />

abolishes the financial support for farmers who participate in<br />

the set-aside program, farm income will decline according to<br />

the price decline (Fig. 2).<br />

T<strong>here</strong>fore, it is important to accelerate the accumulation<br />

of farmland for farmers who pursue expanded farm size, and,<br />

to avoid a decline in farm income corresponding to a drop in<br />

price, the government needs to prepare an effective direct income<br />

compensation policy for core farmers immediately.<br />

Notes<br />

Author’s address: National Agricultural <strong>Research</strong> Center, Kannondai<br />

3-1-1, Tsukuba, Ibaraki, Japan, e-mail: umemoto@affrc.go.jp.<br />

524 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Income of full-time labor (US$ thousand year –1 )<br />

72.7<br />

Farm land size (20 ha)<br />

63.6<br />

Income of nonagricultural worker<br />

per year ($54,500)<br />

54.5<br />

45.5<br />

36.4<br />

Farm land size (15 ha)<br />

27.3<br />

18.2<br />

Farm land size (10 ha)<br />

9.1<br />

Farm land size (30 ha but no subsidy)<br />

2.7 2.6 2.4 2.3 2.1 2.0 1.8 1.7 1.5<br />

<strong>Rice</strong> price (US$ kg –1 )<br />

Fig. 2. Effects of a decline in price. Note: the numbers in this figure were calculated by using linear<br />

programming methods. The farm model is as follows: two family laborers. Crops are rice, wheat, and<br />

soybean. The farmer receives a subsidy from the government for the wheat or soybean crop in the<br />

paddy field (US$4,545 ha –1 ) and rice income compensation within 10% of existing income, but the<br />

nonsubsidized farmer receives nothing.<br />

The future perspective of upland rice farmers in Indonesia<br />

in the era of globalization<br />

Yusman Syaukat and Sushil Pandey<br />

<strong>Rice</strong> is the dominant staple food for about 220 million people<br />

in Indonesia. Indonesia achieved self-sufficiency in rice in 1984<br />

following the intensive effort of the government through various<br />

public assistance programs for increasing rice production.<br />

Unfortunately, rice self-sufficiency could not be maintained<br />

for long and the import volume slowly crept up over time. In<br />

2003, rice imports reached 2 million metric tons, which made<br />

Indonesia the biggest rice-importing country in the region<br />

(Sidik 2004).<br />

Land is the basic resource for agricultural activities. The<br />

upland and rainfed lowland play an important role in the agricultural<br />

sector of Indonesia, since a vast area of cultivated land<br />

(about 65.8%) is under rainfed conditions (BPS 2003). The<br />

existence of upland is dominant on all the main islands of Indonesia<br />

(Table 1). In Java, the proportion of upland area is<br />

about 33.5%. However, the high incidence of rural poverty,<br />

instability of production, and fragility of the environment are<br />

among the important characteristics of rainfed upland areas<br />

(Partohardjono 1993).<br />

Upland rice is one important product of upland agriculture.<br />

In 2002, the total production of upland rice reached 2.6<br />

million tons, w<strong>here</strong>as lowland rice produced 45.2 million t.<br />

Sumatra and Java islands account for the major share of upland<br />

rice area and production in Indonesia. Total upland rice<br />

area of Indonesia is 1 million ha and upland rice accounts for<br />

less than 10% of the total rice area of Indonesia. Government<br />

efforts to achieve self-sufficiency in rice during the 1980s focused<br />

on lowland irrigated rice. Upland rice has remained<br />

somewhat neglected in the public-sector assistance programs<br />

of Indonesia.<br />

In upland areas, w<strong>here</strong> the opportunity costs of land and<br />

labor are relatively low, Indonesia may still have a comparative<br />

advantage in upland rice production. The objectives of<br />

this paper are (1) to evaluate the importance of upland rice<br />

and its relation with poverty level and (2) to discuss the likely<br />

impact of trade liberalization on upland rice production and<br />

the livelihoods of upland farmers.<br />

Characteristics of upland rice production<br />

Upland rice production is characterized by tiny percentages of<br />

marketed output, low yields, and relatively low levels of use<br />

of modern inputs. Upland rice production activities involve a<br />

large number of Indonesians. Although the contribution of<br />

upland rice to the total national rice production is relatively<br />

low, it has an important role in supporting farmers’ livelihoods.<br />

Most upland farmers cultivate upland rice mainly to meet their<br />

family needs. Because of the small area of land ownership,<br />

low yield, and lack of government support, most upland rice<br />

farmers are poorer than their wetland counterparts.<br />

Session 18: Impact of globalization on rice farmers 525


Table 1. Total area of agricultural land in Indonesia by islands, 2003 (excluding Maluku<br />

and Papua).<br />

Island<br />

Total area (ha)<br />

Irrigated land Rainfed land Upland Total<br />

Sumatera 1,691,544 710,997 7,097,329 9,499,870<br />

17.81% 7.48% 74.71% 100.00%<br />

Java 4,663,175 879,417 2,792,861 8,335,453<br />

55.94% 10.55% 33.51% 100.00%<br />

Bali and Nusa Tenggara 708,886 89,283 1,471,482 2,269,651<br />

31.23% 3.93% 64.83% 100.00%<br />

Kalimantan 321,534 413,829 6,687,296 7,422,659<br />

4.33% 5.58% 90.09% 100.00%<br />

Sulawesi 1,116,706 327,196 2,953,964 4,397,866<br />

25.39% 7.44% 67.17% 100.00%<br />

Indonesia 8,501,845 2,420,722 21,002,932 31,925,499<br />

26.63% 7.58% 65.79% 100.00%<br />

Source: BPS (2003).<br />

Following trade liberalization agreements under the Uruguay<br />

Round (signed in 1994), the government of Indonesia<br />

deregulated trade in food crops, including rice. In line with<br />

these agreements, Indonesia has abolished input subsidies,<br />

output price protection, and reduced tariffs for rice. The resulting<br />

price disparity between the international and domestic<br />

retail price has increased the imports of cheap rice into Indonesia<br />

(Sidik 2004). Although imports of cheap rice are expected<br />

to have a positive effect on the poverty of poor consumers,<br />

commercial rice farmers will have to adjust production to the<br />

prevailing price regime.<br />

Upland rice, farmer livelihoods, and poverty<br />

Upland rice is still an important food in the hilly region w<strong>here</strong><br />

farmers have limited access to lowlands, irrigation facilities<br />

are limited, and market access is poorly developed. Under these<br />

conditions, the opportunity costs of land and labor become<br />

relatively low. Subsistence production of upland rice is observed<br />

under such conditions. Though upland is considered to<br />

be “marginal land,” it plays an important role since farmers<br />

use it to cultivate rice and secondary crops.<br />

Upland farmers tend to have a different perspective in<br />

growing rice than wetland farmers. For wetland farmers, rice<br />

is a commercial commodity. Wetland farmers grow rice to<br />

obtain profits by selling their products to the market. In contrast,<br />

upland farmers mostly grow rice to make sure that they<br />

obtain enough production to meet their food requirements. They<br />

sell rice only if t<strong>here</strong> is a surplus of production over consumption.<br />

Poverty is a significant and persistent problem in the<br />

agricultural sector of Indonesia. About 23.7 out of 37.1 million<br />

poor people of Indonesia (63.9%) are those who work in<br />

agriculture (BPS 2002). The relationship between the percentage<br />

of upland rice area (UpArea, i.e., ratio between total area<br />

of upland rice and the total area of both upland and wetland<br />

Percent<br />

70<br />

Upland rice<br />

60 Wetland rice<br />

50<br />

40<br />

30<br />

20<br />

10<br />

0<br />

Kept as seeds Consumed Paid as land rent Sold<br />

Fig. 1. Comparision of upland and wetland rice disposal.<br />

rice) and the incidence of poverty (Poor) using district-level<br />

data is estimated as<br />

Poor = 17.5336 + 0.0456 UpArea<br />

(30.721) (1.895) R 2 = 0.102<br />

The results indicate that t<strong>here</strong> is a positive and significant (at<br />

the 5% level) relationship between the percentage of poverty<br />

and percentage of upland area in each district, meaning that<br />

every 1% increase in the area of upland rice is associated with<br />

an increase in poverty incidence of 0.05%.<br />

A survey of upland rice farmers in West Java was conducted<br />

in 2003 to generate household-level data regarding<br />

upland rice systems. The main reasons given by farmers for<br />

growing upland rice were (1) to meet their household needs<br />

(80%) and (2) because of “custom”—they just know (upland)<br />

rice activities (9%). Allocation of upland rice production is<br />

mainly to meet household needs (66%) (Fig. 1). This indicates<br />

the importance of upland rice in farmers’ livelihoods. They<br />

grow upland rice to make full use of the available family labor<br />

and land. Even if lowland rice is available in the market, its<br />

526 <strong>Rice</strong> is life: scientific perspectives for the 21st century


purchase is limited because of the lack of income and the subsistence-oriented<br />

livelihood strategy.<br />

Future prospects for upland rice<br />

As upland rice is a subsistence crop, its production is unlikely<br />

to be affected directly by the availability of cheap imported<br />

rice following trade liberalization. Survey results indicate that<br />

farmers who don’t have sufficient purchasing power will continue<br />

to grow upland rice even when cheap rice is available in<br />

the market at a low price. In years when the production of<br />

upland rice is low, farmers simply substitute other crops such<br />

as cassava and maize for upland rice instead of purchasing<br />

rice in the market, mainly because of a lack of income. So, the<br />

effect of trade liberalization on upland rice is likely to depend<br />

more on how it will affect overall farm income. As trade in<br />

agricultural commodities is liberalized, other commercial crops<br />

such as rubber, coconut, and cloves that substitute for upland<br />

rice may become more profitable. A shift toward these crops<br />

may gradually lead to less reliance on upland rice as farmers’<br />

income and purchasing capacity improve.<br />

Only the poorest of the poor who are dependent on upland<br />

rice for their livelihoods and those who lack other means<br />

of enhancing their income are likely to continue to grow upland<br />

rice. Hence, although t<strong>here</strong> is likely to be some shrinkage<br />

in upland rice area in the wake of trade liberalization, the reduction<br />

in upland rice area is likely to be proportionately less<br />

than that for lowland rice area. However, in the long run, as<br />

adjustments in the prices of crops that are substitutes for upland<br />

rice occur in response to trade liberalization, upland rice<br />

may lose its comparative advantage altogether.<br />

References<br />

BPS (Central Statistics Agency of Indonesia). 2002. Data dan<br />

informasi kemiskinan tahun 2002: buku 2 - kabupaten. Jakarta,<br />

Indonesia.<br />

BPS. 2003. Land area by utilization in Indonesia: agricultural survey.<br />

Jakarta, Indonesia.<br />

Partohardjono S. 1993. Upland agriculture in Indonesia: recent trends<br />

and issues. In: Bottema JWT, Stoltz DR, editors. Upland agriculture<br />

in Asia. Proceedings of a workshop held in Bogor,<br />

Indonesia, 6-8 April 1993.<br />

Sidik M. 2004. Indonesia rice policy in view of trade liberalization.<br />

A paper presented at the FAO <strong>Rice</strong> Conference held in Rome,<br />

Italy, 12-13 February 2004.<br />

Notes<br />

Authors’ addresses: Yusman Syaukat, Department of Agricultural<br />

Socio-Economics, Bogor Agricultural University, Bogor, Indonesia,<br />

e-mail: ysyaukat@indo.net.id; Sushil Pandey, <strong>International</strong><br />

<strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>, Philippines, e-mail:<br />

sushil.pandey@cgiar.org.<br />

Impact of globalization on rice farmers in Thailand<br />

Rangsan Pitipunya<br />

Globalization makes the world smaller and affects people’s<br />

lives in many aspects. With the fast development of information<br />

technology (IT), our way of life has changed drastically.<br />

IT has markedly changed our way of life, economics, society,<br />

and policy worldwide. Every country has to prepare itself to<br />

cope with this change. Besides IT development, the World<br />

Trade Organization (WTO), which aims to create efficient and<br />

fair international trade, has been established. To promote agricultural<br />

trade, three measures, market access and tariff reduction,<br />

domestic support reduction, and export subsidy reduction,<br />

have been implemented since 1995. In general, it is believed<br />

that the WTO and IT will boost the volume of agricultural<br />

trade, which will create benefits for many people, especially<br />

farmers. However, in Thailand, this belief is questioned;<br />

t<strong>here</strong>fore, it is crucial to discuss the impact of the WTO and IT<br />

on farmers. Because the number of rice farmers in Thailand is<br />

the most compared to other farmers in the country, this paper<br />

will focus only on the impact of the WTO and IT on rice farmers.<br />

Thailand, the WTO, and IT<br />

Thailand and the WTO<br />

As a member of the WTO, Thailand committed to the following:<br />

1. Reduce average tariffs on 740 tariff lines by 24% in<br />

10 years (1995-2004), with a minimum reduction of<br />

10% on all tariff lines. The average tariff rate will<br />

decrease from 49% in 1995 to 27–40% (37% on average)<br />

in 2004 (DTN 2004).<br />

Thailand opened its domestic rice market in two<br />

ways. The first one was to set import tariff rate quotas<br />

at 30%. The quota amounts were set at 237,863<br />

and 249,757 tons in 1995 and 2004, respectively. The<br />

second was to reduce tariffs for imported rice (more<br />

than quota) from 58% in 1995 to 52% in 2004. For<br />

processed rice products, t<strong>here</strong> is no tariff quota, but<br />

t<strong>here</strong> will be a tariff reduction and commitment to an<br />

import tariff rate.<br />

Session 18: Impact of globalization on rice farmers 527


2. Reduce domestic support by 13% in 10 years. In 1999,<br />

rice production support was US$333.03, dropping<br />

from $354.53 in 1995 (DTN 2004).<br />

Development of information technology<br />

Thailand has been using IT for about 20 years. However, this<br />

technology was not widely used until 1995, when the Thai government<br />

established its IT 2000 policy framework for IT development<br />

from 1995 to 2000, with three fundamental prerequisites<br />

that must necessarily be in place and function together:<br />

(1) a national information infrastructure, (2) a well-educated<br />

populace and adequate IT labor, and (3) good governance with<br />

a dare to dream and a resolve to act. The termination of IT<br />

2000 was followed by a second, called IT 2010, which was<br />

approved by the cabinet in March 2002. The IT 2010 policy<br />

framework, implemented from 2001 to 2010, set a higher goal<br />

of transforming the Thai economy into a knowledge-based<br />

economy (Krutkaew 2004). The Ministry of Information Technology<br />

and Communication has been established to take these<br />

responsibilities. An IT master plan has also been set up to promote<br />

widespread IT use. Consequently, IT has been used widely<br />

in the last 2–3 years.<br />

The impact of the WTO and IT on Thai rice farmers<br />

It was expected that Thailand should have been able to increase<br />

its amount of rice exports because its climate is suitable<br />

for rice cultivation. Many millions of tons of rice are left over<br />

that can be exported to the world market every year. According<br />

to the WTO agreement, its members have to reduce domestic<br />

rice production support, export subsidies, and other trade<br />

barriers. This is a good chance for Thailand to increase its<br />

amount of rice exports. Consequently, the domestic rice market<br />

had to adapt itself to new conditions that certainly affect<br />

Thai rice farmers. In addition, at present, IT has been widely<br />

used and is also another factor affecting farmers’ life.<br />

For rice exports, it was found that the amount of exported<br />

rice decreased in 1996. It dropped from 6,198 million<br />

tons in 1995 to 5,460 million tons in 1996. After that, the<br />

amount of rice exports has obviously increased. Even though<br />

it fell in some years, it climbed to over 7 million tons since<br />

2001 and in 2003 the amount of exported rice was 7.343 million<br />

tons. It can be seen that income from rice exports has<br />

expanded since 1995. Income was $1,948.19 million, which<br />

rose from $1,555.05 million in 1994. Then, it gradually declined<br />

to about $1,600 million and again climbed to $1,846.84<br />

million in 2003 (Table 1).<br />

The variation in export income depended not only on<br />

the export amount but also on the export price, which had a<br />

close relationship with the farm price and profit. Table 1 showed<br />

that farmers could obtain profit from rice production almost<br />

every year. In 1995, the average profit from rice was $17.10<br />

per ton. After that, profit rose to more than $40 per ton in 1996<br />

and remained at a high level until 1999. Since then, profit declined<br />

to $6.20 per ton in 2000. Because the product price<br />

dropped drastically, farmers lost $4.72 per ton in 2001. After<br />

Table 1. Important information on rice production in Thailand. a Year<br />

Items<br />

1994 1995 1996 1997 1998 1999 2000 2001 2002 2003<br />

Milled rice export<br />

Amount (million t) 4.86 6.20 5.46 5.57 6.54 6.84 6.14 7.69 7.33 7.35<br />

Value (million US$) 1,555.05 1,948.19 1,998.22 2,074.85 2,098.29 1,950.59 1,631.38 1,577.46 1,629.41 1,846.84<br />

Price ($ t –1 ) 320.06 314.33 365.96 372.68 320.83 285.22 265.64 205.10 222.16 251.41<br />

Farm price ($ t –1 ) 149.62 161.74 197.05 166.32 159.63 143.33 114.99 97.40 108.98 117.68<br />

Net profit ($ t –1 ) 15.54 17.10 46.59 40.87 61.12 27.16 6.20 -4.27 5.88 6.65<br />

Total product of paddy (t)<br />

Wet season 16.48 18.16 17.73 17.78 18.79 18.66 19.02 19.79 20.90 19.63<br />

Dry season 1.97 2.95 4.29 4.55 4.79 4.34 5.16 6.06 5.62 6.43<br />

Average product of paddy (t ha –1 )<br />

Wet season 1.83 2.01 1.93 1.94 2.06 2.07 2.10 2.14 2.26 2.16<br />

Dry season 3.96 4.28 4.51 4.42 4.14 4.20 4.10 4.34 4.17 4.21<br />

Cultivated area (million ha)<br />

Wet season 8.98 9.02 9.19 9.17 9.11 9.00 9.05 9.24 9.25 9.11<br />

Dry season 0.50 0.69 0.95 1.03 1.16 1.03 1.26 1.39 1.35 1.53<br />

Sources: Office of Agricultural Economics, own calculations.<br />

528 <strong>Rice</strong> is life: scientific perspectives for the 21st century


that, farmers gained profit from rice production again, but it is<br />

rather low.<br />

Because of earning profit, Thai rice farmers expanded<br />

their production by improving productivity and expanding<br />

planting area. For productivity, Table 1 showed that since 1994<br />

productivity has not been increasing steadily. In the rainy season,<br />

yield fluctuated from 1.83 to 2.26 t ha –1 , w<strong>here</strong>as, in the<br />

dry season, it was 3.96 to 4.50 t ha –1 . The main factor affecting<br />

rice productivity was overall environmental conditions,<br />

particularly rainfall. Production technique, particularly planting<br />

method, compared between before and after being a WTO<br />

member, is similar. However, because of the health hazard resulting<br />

from chemical substances, a few farmers have begun<br />

nonchemical practices in rice cultivation lately.<br />

Even though the expansion of rice production by increasing<br />

productivity was not distinct but in the case of increasing<br />

planting area was obvious, particularly in the dry season, planting<br />

area increased about 0.093 million ha per year. It increased<br />

from 0.50 million ha in 1994 to 1.53 million ha in 2003. As a<br />

result, rice production in the dry season in the same period<br />

rose from 1.97 million to 6.426 million t. Because of land limitations,<br />

the planting area in the rainy season increased slightly<br />

from 8.98 million ha in 1994 to 9.11 million ha in 2003. T<strong>here</strong>fore,<br />

the total product also increased a bit from 18.161 million<br />

t to 19.631 million t.<br />

As mentioned above, it seems that being a WTO member<br />

provides a good opportunity for Thai rice exports and enables<br />

farmers to expand their production. However, t<strong>here</strong> is a<br />

question whether the increase in rice exports since 1995 resulted<br />

from being a WTO member or not. Poapongsakorn and<br />

Corman (2004) indicated that the increasing rate of rice exports<br />

in 1995-2000 (after being a WTO member) was 3.88%<br />

per year lower than that during 1985-1994, when exports increased<br />

4.15% per year. Furthermore, it was noted that the<br />

market share of Thai rice in developed countries after 1995<br />

seemed to decrease, particularly in Japan and the European<br />

Union. In addition, statistical analysis cannot confirm the significant<br />

impact of agreements under the WTO framework on<br />

the expansion of Thai rice exports. Besides, some additional<br />

observations found that the expansion of Thai rice exports may<br />

be due to the depreciation of the Thai currency (baht) because<br />

of the economic crisis. Pouthipong (2003) indicated that the<br />

foreign exchange rate was a significant factor affecting demand<br />

for Thai rice exports.<br />

Regarding IT, it has been found that the technology affected<br />

people living in big cities who have a high education<br />

and young age. But its impact on rice farmers who are poor,<br />

have a low education, and are old was not clear. However, in<br />

the near future, when IT infrastructure has been completely<br />

set up throughout the country, it is believed that the technology<br />

will become an important tool of Thai rice-farming development.<br />

Conclusions<br />

It still cannot be concluded that the WTO is a factor affecting<br />

the expansion of the Thai rice market. However, after being a<br />

member of this organization, the trend of Thai rice exports has<br />

been increasing. Some research results revealed that Thai competitiveness<br />

in the world rice market has increased (Tawhon<br />

2003). Moreover, the WTO is a forum for its members to negotiate<br />

and reach agreement. T<strong>here</strong>fore, Thailand should cooperate<br />

with this organization closely. Creating subgroup members<br />

having the same or relevant problems should be carried<br />

out continuously to strengthen bargaining power.<br />

Though the impact of IT on Thai rice farmers has not<br />

been seen clearly, in the near future it is expected to be an<br />

important tool in the development of rice farmers and the agricultural<br />

sector. T<strong>here</strong>fore, Thai rice farmers should prepare<br />

themselves to cope with this kind of technology.<br />

References<br />

DTN (Department of Trade Negotiations). 2004. Negotiation on<br />

agricultural product under WTO and FTA. Bangkok (Thailand):<br />

DTN. 205 p.<br />

Krutkaew C. 2004. Strategy and direction of information and communication<br />

technology development in Thailand. Exec. J.<br />

24:26-30.<br />

Poapongsakorn N, Corman S. 2004. Multilateral negotiation on<br />

agricultural product: unbalance, failure, and future of Doha<br />

Round. In: Thai economy and multilateral negotiation. Proceedings<br />

of Symposium 27, 17 August 2004. Bangkok (Thailand):<br />

Faculty of Economics, Thammasart University. p 5-1–<br />

5-100.<br />

Pouthipong P. 2003. A study of export demand for Thai rice before<br />

and after devaluation. Bangkok (Thailand): Kasetsart University.<br />

68 p.<br />

Tawhon K. 2003. A composition of factors affecting rice export<br />

growth of Thailand. Bangkok (Thailand): Kasetsart University.<br />

174 p.<br />

Notes<br />

Author’s address: Kasetsart University, Bangkok, Thailand, e-mail:<br />

fecorsp@ku.ac.th.<br />

Session 18: Impact of globalization on rice farmers 529


The rice economy and rice policy in China<br />

Li Ninghui<br />

China is the largest country that produces rice in the world and<br />

also the largest country that consumes rice. China’s rice production<br />

plays a very important role not only in China’s grain<br />

economy but also in the world rice economy.<br />

Table 1 shows that China produces more than 30% of<br />

the rice with around 20% of the world’s paddy area. This implies<br />

that the yield of rice in China is higher than the average<br />

in the world. However, these shares have been going down.<br />

This downward trend mainly results from the Chinese<br />

government’s policy of structural adjustment of rice production<br />

to enhance the production of high-quality rice while reducing<br />

low-quality rice in response to the change in consumers’<br />

behavior in rice consumption. Chinese demand for rice<br />

consumption is shifting from quantity to quality as economic<br />

development occurs. Owing to the progress of science and technology<br />

for agricultural production, China’s grain supply versus<br />

demand has changed from chronic shortage to surplus in a<br />

good harvest year, keeping a balance in a normal year and a<br />

temporary shortage in a bad harvest year, since the end of the<br />

1990s. Thanks to the good rice harvest in the second half of<br />

the 1990s, the surplus grain supply gave the Chinese government<br />

a good chance to smoothly implement policies of adjusting<br />

the agricultural production structure, including the rice<br />

production structure, to meet consumers’ diversified demand.<br />

Figure 1 tells us that we can categorize rice production<br />

and consumption into three stages. The first stage was the period<br />

before the mid-1980s, when production and consumption<br />

rose rapidly and in the same phase. During that period, production<br />

and consumption were almost balanced. The second<br />

stage was the period from the mid-1980s to the end of the<br />

1990s, when production rose with a large fluctuation and consumption<br />

went up smoothly. During that period, the rice surplus<br />

and deficit switched several times, with a large surplus in<br />

the end. The third stage was the period starting at the beginning<br />

of the 2000s, when both production and consumption went<br />

down, but production at a faster speed. Fortunately, the trend<br />

Table 1. China’s share of the rice economy.<br />

China’s share of rice 1970 1980 1990 1999 2000 2001<br />

In the domestic grain economy (%)<br />

Cultivated area 27.1 28.9 29.1 27.6 27.6 27.2<br />

Output 45.8 43.6 42.4 39.0 40.7 39.2<br />

In the world rice economy (%)<br />

Cultivated area 24 23 23 20 19.4 19.0<br />

Output 36 38 38 34 31.3 30.0<br />

Data source: National Bureau of Statistics of China.<br />

(000 t)<br />

150,000<br />

140,000<br />

Production<br />

Consumption<br />

130,000<br />

120,000<br />

110,000<br />

100,000<br />

90,000<br />

1980<br />

1982<br />

1984<br />

1986<br />

1988<br />

1990<br />

1992<br />

1994<br />

1996<br />

1998<br />

2000<br />

2002<br />

Year<br />

Fig. 1. Milled rice production and consumption from 1980 to 2002.<br />

530 <strong>Rice</strong> is life: scientific perspectives for the 21st century


of a sharp decrease in rice production in recent years has been<br />

halted and recovered, according to a report from the National<br />

Bureau of Statistics.<br />

The Chinese government’s rice policy targeted high output<br />

for a long time in order to feed China’s huge population,<br />

with limited arable land. In the 1960s, a new variety of rice,<br />

called semi-short-stem rice, was cultivated and extended in<br />

China, whose output relies heavily on fertilizer use, while the<br />

Green Revolution was being experienced in other countries<br />

during the same period. In the early 1980s, the cultivated area<br />

of upgraded varieties of rice, which were mainly conventional<br />

high-yielding varieties and hybrid varieties, accounted for more<br />

than 98% of the total cultivated area of rice. In the late 1970s<br />

and 1980s, varieties with disease resistance were cultivated<br />

and extended in China.<br />

However, rice production aimed at high yield has faced<br />

a growing challenge since the early 1990s. After the opening<br />

of the domestic rice market to consumers starting in 1993, the<br />

cultivated area of hybrid rice gradually stopped going up, and<br />

even shrank because the quality of hybrid rice was relatively<br />

low. The demand for high-quality rice significantly affected<br />

regional and varietal distribution (i.e., indica and japonica) of<br />

rice production, which resulted in the rapid expansion of cultivated<br />

area in northern China, especially northeast China,<br />

w<strong>here</strong> japonica rice is produced. The share of rice area in northern<br />

China increased from less than 6% in the early 1980s to<br />

Table 2. Structural change in rice production of China in 1980-2000. a<br />

Cultivated area share Cultivated area share Share of<br />

Year by variety (%) by region (%) hybrid rice<br />

area (%)<br />

Indica Japonica South North<br />

1980 89 11 94 6 14<br />

1985 88 12 93 7 26<br />

1990 84 16 90 10 49<br />

1995 79 21 89 11 52<br />

2000 73 27 86 14 50<br />

a Cultivation of hybrid rice reached a peak in 1991-92. Cultivated area of hybrid rice<br />

accounted for 40% of the total cultivated area of rice.<br />

10% in 1990 and 14% in 2000. In some provinces along the<br />

middle reaches and downstream of the Yangtze River, such as<br />

Jiangsu, Zhejiang, Shanghai, and Anhui, w<strong>here</strong> indica rice is<br />

the traditional product, farmers produce more and more<br />

japonica, even surpassing indica. This resulted in the share of<br />

japonica area increasing from 11% in 1980 to 16% in 1990<br />

and 27% in 2000.<br />

By varieties, we see that in the 1960-70s, a group of<br />

precocious early rice and cold-resistant late rice was cultivated<br />

in China, which resulted in the extension of double-cropped<br />

rice and increased total output greatly.<br />

Double-cropped rice yielded 7.04 t ha –1 in 1975, 56%<br />

higher than the yield of single-cropped rice (4.43 t ha –1 ). This<br />

difference was 63% in 1990-94, when the yield of singlecropped<br />

rice increased to 6.63 t ha –1 and the yield of doublecropped<br />

rice increased to 10.63 t ha –1 . This big difference was<br />

the main reason that the cultivated area of double-cropped rice<br />

expanded under the guidance of the policy for output.<br />

The output growth of double-cropped rice, however, was<br />

obtained at the cost of two times more labor input and fertilizer<br />

input per unit of paddy field than those in single-cropped<br />

rice.<br />

The rapid development of the rural economy and growth<br />

of rural household income enhanced the opportunity cost of<br />

rural labor. In response to the change in production environments<br />

and conditions, the Chinese government adjusted the<br />

policy that encouraged multiple-cropped rice. As a result, the<br />

cultivated area of double-cropped rice decreased from 66% of<br />

the total area in 1980 to 58–60% in 1990.<br />

<strong>Rice</strong> policy in China<br />

At present, the new policies that have been implemented for<br />

rice production are mainly the following:<br />

Protection of necessary paddy fields. With this policy,<br />

if a field is determined to be necessary as a paddy<br />

field, it will be forbidden to be used in nonagricultural<br />

activities, but it is allowed to be changed to plant<br />

another crop so that it can be reused as a paddy field<br />

in case it is needed in the future.<br />

Table 3. Cultivated area and yield of early rice, late rice, and single-harvest rice.<br />

Cultivated area distribution (%) Yield (t ha –1 )<br />

Double-cropped Single-cropped Double-cropped Single-cropped<br />

Year rice rice rice rice<br />

Early Late Middle rice and Early Late Middle rice and<br />

rice rice one-season late rice rice rice one-season late rice<br />

1975 36 35 29 3.80 3.24 4.43<br />

1980 33 33 34 4.43 3.29 4.64<br />

1985 30 30 40 5.10 4.65 5.96<br />

1990 28 30 42 5.49 5.13 6.50<br />

1994 27 33 40 5.11 5.53 6.55<br />

Data source: China <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>, 1993. Agricultural Yearbook of China, 1990-1995.<br />

Session 18: Impact of globalization on rice farmers 531


Construction of a rice production base. The unit of a<br />

base is a county. T<strong>here</strong> are about 200 bases so far.<br />

The central government provides 2 billion yuan of<br />

favorable loans to support rice production in these<br />

bases.<br />

Support of natural rice production. The standard of<br />

natural rice production has been established, and natural<br />

rice production bases have been determined and<br />

are being constructed in Heilongjiang, Jilin, Zhejiang,<br />

and Jiangsu. The trend is that these bases will be expanded<br />

soon.<br />

Support of research and extension of rice production<br />

science and technology. The Chinese government<br />

strengthened its financial input into research on “super<br />

rice” and rice genes.<br />

The new policies that have been implemented<br />

for rice procurement are mainly the following:<br />

Cancellation of the policy that procured early indica<br />

rice at a protected price in 2000. In the early 1990s,<br />

the cultivated area of early indica rice accounted for<br />

Wrap-up of Session 18<br />

Notes<br />

<br />

25% of the total cultivated area of rice, and this output<br />

accounted for 10% of the total output of rice.<br />

However, on the demand side, most consumers didn’t<br />

like early indica rice because its taste was not so good.<br />

T<strong>here</strong>fore, the government cancelled the protected<br />

price for procuring this product in order to get farmers<br />

to reduce its production.<br />

High quality and high price. The Chinese government<br />

increased the procurement price of high-quality<br />

rice to encourage its production. To carry out this<br />

policy and enforce the management of rice quality,<br />

the Chinese government implemented a new standard<br />

of rice quality in 2000 to replace the old one implemented<br />

in 1986.<br />

Author’s address: <strong>Institute</strong> of Agricultural Economics, Chinese Academy<br />

of Agricultural Sciences, Beijing, China, e-mail:<br />

linh@mail.cass.net.cn.<br />

The theme of session 18 was the “Impact of globalization on rice<br />

farmers.” We focused on farmers’ response to the progression of<br />

globalization. Globalization is usually treated as a matter of WTO<br />

agricultural negotiations on agricultural economics. Globalization<br />

is the liberalization and deregulation of the market system, but it<br />

also fosters the interactions among policy, the economy, information,<br />

and culture of each country. Especially, the information<br />

technology (IT) revolution will strongly affect agricultural production.<br />

T<strong>here</strong>fore, it is important to consider globalization from a<br />

wider perspective.<br />

The session focused on three major topics:<br />

1. What are the major farming types of rice farmers (rice<br />

producers) and what are their socioeconomic characteristics<br />

in each country<br />

2. How do rice farmers face changes in economic conditions<br />

brought about by globalization, and how do they<br />

react to those changes<br />

3. What are the future perspectives of rice farmers in each<br />

country<br />

From these viewpoints, we explored the conditions of rice<br />

farmers among Asian countries.<br />

With this concept, we held two symposia. Symposium 1<br />

had four presentations: a comparative analysis for total factor<br />

productivity in 33 rice-producing countries from 1961 to 2002<br />

(“Impacts of trade liberalization on competitiveness and productivity<br />

in the rice sector,” M. Rakotoarisoa, USA), an empirical<br />

study on Japanese group faming (“New strategy of group farming<br />

in Japan,” K. Miyatake, Japan), research on Indonesian rice farmers<br />

under globalization (“The role of the rice economy after the<br />

implementation of agricultural policy reform and trade liberaliza-<br />

tion from the perspective of farmers,” Roosiana, Indonesia), and<br />

the classification of areas against climatic shocks (“El Niño sensitivity,<br />

resource endowment, and socioeconomic characteristics:<br />

the case of wetland rice in Java, Indonesia,” S. Yokoyama, Japan).<br />

These analyses indicated that current problems in rice production<br />

and the impacts of globalization on rice farmers really<br />

differed among countries and areas. They also indicated that farmers<br />

were undertaking regionally specific behavior regarding their<br />

socioeconomic circumstances. Questions and discussion for these<br />

presentations mainly concentrated on how researchers grasped<br />

that diversity. A statistical approach and field research were applied<br />

but a detailed farming survey will be indispensable for an<br />

empirical study on rice production and rice producers’ behavior.<br />

Symposium 2 had four presentations by speakers from Japan,<br />

Indonesia, Thailand, and China. They reported their countries’<br />

main issues on rice production and rice farmers.<br />

M. Umemoto (“Behaviors and strategies of Japanese rice<br />

producers under globalization”) showed the main types of Japanese<br />

rice producers and their behaviors. Next, he analyzed the<br />

impact of the rice price decline on large-scale family farms and<br />

agricultural cooperative firms. Finally, he pointed out the need<br />

for an effective income compensation policy in Japan.<br />

Y. Syaukat (“Future perspectives of upland rice farmers in<br />

Indonesia in the globalization era”) analyzed the impact of globalization<br />

on Indonesian upland rice farmers. He explained that<br />

upland rice is an important product of upland agriculture, but it<br />

has remained somewhat neglected in public-sector assistance<br />

programs. Then, he concluded that only the poorest of the poor<br />

who are dependent on upland rice for their livelihoods are likely<br />

532 <strong>Rice</strong> is life: scientific perspectives for the 21st century


to continue to grow upland rice. In the long run, with adjustments<br />

in crop prices in response to trade liberalization, upland<br />

rice could lose its comparative advantage.<br />

R. Pitipunya (“Impact of globalization on rice farmers in<br />

Thailand”) discussed the impacts of trade liberalization on Thai<br />

rice farmers. He paid special attention to the impacts of the IT<br />

revolution. His statistical analysis had shown that the significant<br />

impact of the WTO on rice exports was not confirmed, and the<br />

expansion of Thai rice exports might have resulted from the depreciation<br />

of the Thai currency. He then mentioned that IT was<br />

expected to be an important tool in agricultural development in<br />

the near future; t<strong>here</strong>fore, farmers have to prepare to cope with<br />

this technology.<br />

Li Ninghui (“<strong>Rice</strong> economy and rice policy in China”) analyzed<br />

the trend of Chinese rice supply and demand. He stated<br />

that, in China, rice production and consumption have decreased.<br />

Especially, the amount of rice production had dropped drastically.<br />

He also pointed out that, after the opening of the domestic<br />

rice market in 1993, the cultivated area of hybrid rice gradually<br />

declined because its quality was relatively low. The demand for<br />

high-quality rice significantly affects the regional layout and variety<br />

layout of rice production. He then introduced the new rice<br />

policy in China: protection of necessary paddy fields, construction<br />

of a rice production base, support of natural rice production,<br />

and cancellation of the policy that procured early indica-type rice.<br />

All of this would encourage the production of high-quality rice.<br />

These reports discussed the various problems related to<br />

rice production and rice farmers in each country, especially referring<br />

to socioeconomic conditions. With these presentations, questions<br />

mainly focused on three issues. First was the evaluation of<br />

government policy regarding globalization. Next were the prospects<br />

for the trend of international rice supply and demand. It<br />

was recognized that whether China, with its huge population,<br />

would continue to be self-sufficient in rice or not could become a<br />

serious problem for the international rice market. Finally were<br />

the prospects for rice export competitiveness. Because R.<br />

Pitipunya reported low productivity of Thai rice, the possibilities<br />

for it were discussed.<br />

It was concluded that it was difficult to summarize briefly<br />

the theme of this session, the impact of globalization on rice<br />

farmers, because rice production possesses specific and varied<br />

socioeconomic characteristics in each country. The theme of this<br />

symposium overrides other important issues in each country’s<br />

agriculture; t<strong>here</strong>fore, it should be treated as a long-term subject.<br />

To clarify those specific problems, it is important to tackle<br />

with comparative analyses various countries’ rice production aspects.<br />

T<strong>here</strong>fore, cooperative and continuous research would be<br />

effective.<br />

Session 18: Impact of globalization on rice farmers 533


SESSION 19<br />

Climate change and rice production<br />

CONVENER: T. Imagawa (NIAES)<br />

CO-CONVENERS: T. Hasegawa (NIAES), Y. Hayashi (NIAES),<br />

and J. Sheehy (<strong>IRRI</strong>)


Effects of elevated atmospheric CO 2 concentration<br />

and increased temperature on rice: implications<br />

for Asian rice production<br />

T. Horie, H. Yoshida, S. Kawatsu, K. Katsura, K. Homma, and T. Shiraiwa<br />

It is predicted that the carbon dioxide concentration (CO 2 ) in<br />

the atmosp<strong>here</strong> will double within this century the concentration<br />

at the beginning of the last century and that the increases<br />

in [CO 2 ] and other greenhouse gases will cause global warming<br />

of 1.5 to 5.8 °C at the end of this century (IPCC 2001).<br />

Such global environmental change is considered to have an<br />

enormous impact on Asian rice production, so that prediction<br />

of its impact by region is important not only for future food<br />

security but also for the sustainable development of rice-farming<br />

societies in Asia. Many experimental studies (Baker 2004,<br />

Horie et al 2000) and simulation studies (Matthews et al 1995,<br />

Horie et al 1995) have been made to clarify elevated [CO 2 ]<br />

and increased temperature effects on rice. On the basis of these<br />

previous studies and a multilocational field experiment (Horie<br />

et al 2003) covering wide-ranging rice genotypes and environments<br />

in Asia, we developed a new rice model for simulating<br />

growth and yield of different genotypes under variously<br />

different environments (Yoshida et al 2004, Yoshida and Horie<br />

2005, Horie 2005).<br />

This paper briefly reviews important findings from the<br />

previous studies on [CO 2 ] and temperature effects on rice, then<br />

explains the structure of our rice model and results of model<br />

simulation on rice yield at different locations in Asia under<br />

increased [CO 2 ] and temperature conditions, and discusses the<br />

implications of the simulation results for future Asian rice production.<br />

<strong>Rice</strong> responses to [CO 2<br />

] and temperature: a review<br />

To understand rice responses to [CO 2 ] and temperature, extensive<br />

research has been done using experimental facilities<br />

of closed chambers (Allen et al 1995), open-top chambers<br />

(Ziska et al 1997), and temperature gradient chambers (Horie<br />

et al 2000) since 1980. Since results of these studies have been<br />

fully reviewed in Horie et al (2000), only important findings<br />

from these studies for model synthesis are summarized <strong>here</strong>.<br />

Those previous studies showed that elevated [CO 2 ] accelerated<br />

rice development; nearly doubled [CO 2 ] increased leaf<br />

photosynthesis by 30–70%, canopy photosynthesis by 30–40%,<br />

and crop biomass yield by 15–30%, depending on genotype<br />

and environment; and that elevated [CO 2 ] had a minor effect<br />

on rice nitrogen (N) uptake, which appeared to be associated<br />

with the relatively insensitive response of leaf area growth to<br />

[CO 2 ]. Those rice responses to [CO 2 ] resulted in a substantial<br />

grain yield increase under elevated [CO 2 ] and nearly optimum<br />

temperature conditions. Analysis of reported data on rice yield<br />

response (R) to [CO 2 ] under optimum temperatures revealed<br />

that the relative response with yield at 353 µmol mol –1 with<br />

unity can be well approximated by the following equation:<br />

R = a (Ca – Co)/{K + (Ca – Co)} (1)<br />

w<strong>here</strong> Ca is ambient [CO 2 ], Co is [CO 2 ] at which R becomes<br />

zero, and a and K are empirical constants. Indica rice genotypes<br />

showed a higher yield response to [CO 2 ] than japonica<br />

genotypes (Fig. 1). The values of a, K (µmol mol –1 ), and Co<br />

(µmol mol –1 ) for indica genotypes were 1.89, 288, and 30.6,<br />

respectively, and those for japonicas were 1.39, 124, and 30.6,<br />

respectively. Thus, relative yield increases at 700 µmol mol –1<br />

are estimated to be 32% for indicas and 17% for japonicas.<br />

With the increase in daily maximum temperature averaged<br />

over flowering period above about 36 ºC, rice yield generally<br />

declined because of spikelet sterility induced by high<br />

temperatures. Importantly, elevated [CO 2 ] increased spikelet<br />

susceptibility to high-temperature damage (Kim et al 1996).<br />

Nearly doubled [CO 2 ] decreased the threshold temperature for<br />

high-temperature damage of spikelets by 1–2 ºC more than<br />

the ambient [CO 2 ].<br />

Simulation of rice growth and yield under elevated [CO 2<br />

]<br />

and increased temperatures<br />

The model used for the simulation<br />

Many attempts have been made to predict global climate change<br />

effects on rice by rice growth simulation models (Matthews et<br />

al 1995, Horie et al 1995). However, the models employed for<br />

prediction did not consider the important interacting effect of<br />

[CO 2 ] and temperature on high-temperature-induced spikelet<br />

sterility, nor genotypic differences in the responses to [CO 2 ]<br />

and temperature that are described above. Considering these<br />

insufficiencies of existing rice models, we synthesized a physiologically<br />

based rice growth and yield simulation model named<br />

GEMRICE (Genotype by Environment simulation Model for<br />

RICE). Since important components of this model have been<br />

reported in Yoshida et al (2004 and 2005) and Horie et al<br />

(1995), we describe only briefly the structure of GEMRICE.<br />

GEMRICE consists of six model components for simulating<br />

processes of phenological development, photosynthesis,<br />

respiration, biomass growth, spikelet number determination,<br />

and grain filling. The phenological development process<br />

component is the same as the previous model SIMRIW (Horie<br />

et al 1995). The photosynthesis component simulates leaf pho-<br />

536 <strong>Rice</strong> is life: scientific perspectives for the 21st century


R (relative yield)<br />

2.0<br />

1.5<br />

Ueda et al (2000)<br />

Kim et al (1996)<br />

Kim et al (2003)<br />

Huang et al (2002)<br />

Allen et al (1995)<br />

Baker (2004)<br />

Ziska et al (1997)<br />

Ueda et al (2000)<br />

Indica<br />

R 2 = 0.85<br />

1.0<br />

Japonica<br />

R 2 = 0.77<br />

0.5<br />

Ca<br />

0<br />

0 200 400 600 800 1,000<br />

Ca=CO 2 concentration (mmol mol –1 )<br />

Fig. 1. [CO 2 ]-yield response curves of indica (open symbols) and japonica (closed symbols)<br />

rice genotypes grown under nearly optimum temperatures. The figure was drawn with experimental<br />

data from various reports shown in the figure.<br />

tosynthetic rate as a function of radiation flux density, temperature,<br />

and [CO 2 ], in which stomatal conductance and leaf<br />

N content are given as genotype-dependent plant parameters.<br />

Canopy photosynthetic rate is given by integrating leaf photosynthetic<br />

rate with respect to leaf area index (LAI), taking into<br />

account solar radiation flux density in the canopy as a function<br />

of LAI. Respiration consists of growth and maintenance<br />

respirations, both of whose rates are given as functions of plant<br />

N content. The maintenance respiration rate is also a function<br />

of temperature. The photosynthetic and respiration rates are<br />

both calculated on an hourly basis by inputting hourly temperature<br />

and solar radiation, which were estimated from their<br />

daily values.<br />

Crop biomass growth rate (CGR) is calculated on a daily<br />

basis by subtracting daily respiration from daily photosynthesis.<br />

The number of spikelets per unit area is calculated as the<br />

difference between the spikelet number differentiated and that<br />

degenerated. The differentiated spikelet number is determined<br />

by multiplying plant N content at 2 wk before full heading by<br />

a genotype-dependent coefficient, and the degenerated spikelet<br />

number by a function of CGR during the 2-wk period before<br />

full heading. Spikelet sterilities caused by both cool temperature<br />

at the meiosis stage and high temperature during flowering<br />

are simulated by the respective functions of temperature.<br />

The [CO 2 ] effect on high-temperature-induced spikelet<br />

sterility is also considered. Grain-filling rate is calculated as a<br />

function of sink and source size and temperature. Sink size is<br />

given by a logistic function of the current grain yield and the<br />

maximum sink size, which in turn is a function of effective<br />

spikelet number per unit area (= spikelet number produced –<br />

spikelet number sterilized). Source size is the sum of the current<br />

daily photosynthesis and amount of nonstructural carbohydrates<br />

stored in the plant.<br />

In the current version of GEMRICE, LAI and plant N<br />

content are given as external parameters by assuming that effects<br />

of [CO 2 ] and temperature on those parameters are relatively<br />

small.<br />

Estimation of parameter values and model validation<br />

The model GEMRICE contains 49 plant parameters to describe<br />

rice growth and yield formations, of which 37 are genotypeindependent<br />

and 12 genotype-dependent. To estimate values<br />

of these parameters and validate the model, a cross-locational<br />

field experiment named the Asian <strong>Rice</strong> Network Experiment<br />

(ARICENET, Horie et al 2003) was conducted on growth and<br />

yield of nine common genotypes. The experimental sites were<br />

eight locations: Iwate, Nagano, Kyoto, and Shimane in Japan;<br />

Nanjing and Yunnan in China; and Chiang Mai and Ubon<br />

Ratchathani in Thailand, covering 39N (Kitakami, Iwate) to<br />

15N (Ubon Ratchathani). The nine genotypes used included<br />

representative cultivars from indica, temperate and tropical<br />

japonicas, and a glaberrima-sativa hybrid (NERICA). The<br />

experiment was conducted in 2001 and 2002 at the respective<br />

sites.<br />

Approximately half of the ARICENET data were used<br />

for parameter estimation and the remainder for model validation.<br />

GEMRICE with parameter values thus estimated could<br />

simulate spikelet number per unit area, biomass, and grain yield<br />

of ARICENET data with R 2 values of 0.86, 0.80, and 0.87,<br />

respectively (Yoshida et al 2003).<br />

Session 19: Climate change and rice production 537


Yield change from current [CO 2 ] and temperature (%)<br />

40<br />

20<br />

0<br />

60<br />

40<br />

20<br />

–40<br />

60<br />

40<br />

20<br />

0<br />

0<br />

–20<br />

–20<br />

–40<br />

–60<br />

–80<br />

[CO 2 ] 700 ppm + 0 °C<br />

[CO 2 ] 700 ppm + 2 °C<br />

[CO 2 ] 700 ppm + 4 °C<br />

IR72<br />

Nipponbare<br />

Iwate Kyoto Nanjing Yunnan Ubon<br />

Fig. 2. Percentage yield change from the current under 700 µmol<br />

mol –1 [CO 2 ] with 0, 2, and 4 ºC temperature rises, simulated for<br />

cultivars IR72 and Nipponbare at Iwate and Kyoto in Japan, Nanjing<br />

and Yunnan in China, and Ubon Ratchathani in Thailand. Climate<br />

data in 2001 and 2002 at each location were used as base climate.<br />

Simulated effects of elevated [CO 2<br />

]<br />

and increased temperature on rice yield<br />

Growth and yield simulations were made for different rice<br />

genotypes grown under 700 µmol mol –1 [CO 2 ] and different<br />

degrees of temperature rise at the respective ARICENET sites.<br />

The [CO 2 ] of 360 µmol mol –1 and weather conditions in 2001<br />

and 2002 at the respective sites were used as base [CO 2 ] and<br />

climate conditions for the simulation. Figure 2 represents the<br />

simulation results on cultivars of IR72 (indica) and Nipponbare<br />

(japonica) at Iwate and Kyoto in Japan, Nanjing and Yunnan<br />

in China, and Ubon in Thailand as percentage yield change<br />

from the base conditions at each site. Simulation results on<br />

IR72 at Iwate and Nipponbare at Ubon are not shown in Figure<br />

2 because these cultivars showed very poor adaptability to<br />

the climates of those sites.<br />

The model predicted higher yield responses to elevated<br />

[CO 2 ] in IR72 (indica) than in Nipponbare (japonica) simulated<br />

for all the locations under the current temperature condi-<br />

tions, which agrees well with the observation shown in Figure<br />

1. Since the model assumed the same leaf photosynthetic response<br />

to [CO 2 ] for both genotypes, the higher yield response<br />

of IR72 to [CO 2 ] was due to its larger sink formation ability<br />

and, hence, more source limitation under ambient [CO 2 ] than<br />

Nipponbare. The model predicted that doubled [CO 2 ] alone<br />

will increase yield of the two genotypes by about 20–30% at<br />

most locations simulated. This effect of [CO 2 ] was drastically<br />

reduced by a 2 ºC temperature increase at all locations except<br />

Iwate in northern Japan. At Kyoto, w<strong>here</strong> summer temperature<br />

is high, doubled [CO 2 ] with a 2 ºC temperature rise will<br />

significantly reduce the yield of Nipponbare, reflecting the<br />

increased spikelet susceptibility to high temperature damage<br />

by elevated [CO 2 ]. It was predicted that doubled [CO 2 ] with a<br />

4 ºC temperature rise would have severe negative effects on<br />

rice yield at most Asian locations except for northern areas<br />

such as Iwate. The negative effects were more pronounced in<br />

warm-temperature regions such as Kyoto and Nanjing than in<br />

tropical areas such as Ubon. However, the results at Ubon in<br />

Figure 2 were on wet-season rice, and severe negative effects<br />

on dry-season rice yield were predicted t<strong>here</strong> under conditions<br />

of doubled [CO 2 ] with a temperature rise of more than 2 ºC.<br />

The review of the previous studies and the model simulation<br />

indicated that the anticipated global climate change associated<br />

with increased greenhouse gases will have large and<br />

different effects on rice production in Asia, depending on locations<br />

and genotypes. The model predicts that, while doubling<br />

[CO 2 ] with a temperature rise of more than 2 ºC will<br />

significantly increase rice yield in cool temperate areas, it will<br />

drastically reduce the yield in warm temperate areas and for<br />

dry-season rice in the tropics. This is an important subject for<br />

further studies to identify adaptive technologies for mitigating<br />

the negative effects of global warming on rice production in<br />

each region in Asia.<br />

References<br />

Allen LH Jr, Baker JT, Albrecht SL, Boote KJ, Pan D, Vu JCV. 1995.<br />

Carbon dioxide and temperature effect on rice. In: Peng S,<br />

Ingram KT, Neue H-U, Ziska LH, editors. Climate change<br />

and rice. Berlin (Germany): Springer-Verlag. p 258-277.<br />

Baker JT. 2004. Yield responses of southern US rice cultivars to<br />

CO 2 and temperature. Agric. Forest Meteor. 122:129-137.<br />

Horie T, Nakagawa H, Ohnishi M, Nakano J. 1995. <strong>Rice</strong> production<br />

in Japan under current and future climates. In: Matthews PB,<br />

Kropff MJ, Bachelet D, van Laar HH, editors. Modeling the<br />

impact of climate change on rice production in Asia.<br />

Wallingford (UK): CAB <strong>International</strong>. p 143-164.<br />

Horie T, Baker JT, Nakagawa H, Matsui T, Kim H-Y. 2000. Crop<br />

ecosystem responses to climatic change: rice. In: Reddy KR,<br />

Hodges HF, editors. Climate change and global crop productivity.<br />

Wallingford (UK): CAB <strong>International</strong>. p 81-106.<br />

Horie T, Yoshida H, Shiraiwa T, Nakagawa H, Kuroda E, Sasaki T,<br />

Hagiwara H, Kobata T, Ohsumi M, Kobayashi K. 2003. Analysis<br />

of genotype by environment interaction in yield formation<br />

processes of rice grown under a wide environmental range in<br />

Asia. 1. Asian <strong>Rice</strong> Network (ARICENET) research and preliminary<br />

results. Jpn. J. Crop Sci. 72(extra issue 2):88-89.<br />

538 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Horie T. 2005. Determination of the yield potential and associated<br />

traits in rice. Gamma Field Symposia 43. <strong>Institute</strong> of Radiation<br />

Breeding, NIAS. (In press.)<br />

Huang J, Yang H, Dong G, Wang Y, Zhu J, Yang L, Shan Y. 2002.<br />

Effects of free-air CO 2 enrichment (FACE) on yield formation<br />

in rice (Oryza sativa). Chinese J. Appl. Ecol. 13:1210-<br />

1214.<br />

IPCC (Inter-Governmental Panel on Climate Change). 2001. Climate<br />

change 2001: the scientific basis. Contribution of working<br />

group I to the third assessment report of IPCC. London<br />

(UK): Cambridge University Press.<br />

Kim H-Y, Horie T, Nakagawa H, Wada K. 1996. Effects of elevated<br />

CO 2 concentration and high temperature on growth and yield<br />

of rice: the effect on yield and its components on Akihikari<br />

rice. Jpn. J. Crop Sci. 65:644-651.<br />

Kim H-Y, Lieffering M, Kobayashi K, Okada M, Matthew WM,<br />

Gumpertz M. 2003. Effects of free-air CO 2 enrichment and<br />

nitrogen supply on the yield of temperate paddy rice crops.<br />

Field Crops Res. 83:261-270.<br />

Matthews RB, Horie T, Kropff MJ, Bachelet D, Centeno HG, Shin<br />

JC, Mohandas S, Singh S, Defeng Z, Lee MH. 1995. A regional<br />

evaluation of the effect of future climate change on<br />

rice production in Asia. In: Matthews RB, Kropff MJ, Bachelet<br />

D, van Laar HH, editors. Modeling the impact of climate<br />

change on rice production in Asia. Wallingford (UK): CAB<br />

<strong>International</strong>, p 95-139.<br />

Ueda T, Nakagawa H, Okada K, Horie T. 2000. Varietal differences<br />

in yield and spikelet fertility of rice in response to elevated<br />

CO 2 concentration and high temperature. Jpn. J. Crop Sci.<br />

69(extra issue 1):112-113.<br />

Yoshida H, Horie T, Ohnishi M, Katsura K. 2003. Analysis of genotype<br />

by environment interaction in yield formation processes<br />

of rice grown under a wide environmental range in Asia. 2. A<br />

model explaining genotypic and environmental variation in<br />

spikelet number per unit area. Jpn. J. Crop Sci. 72(extra issue<br />

2):90-91.<br />

Yoshida H, Horie T. 2005. Analysis of genotype by environment<br />

interaction in yield formation processes of rice grown under a<br />

wide environmental range in Asia. 5. Jpn. J. Crop Sci. 73(extra<br />

issue 2). (In preparation.)<br />

Ziska LH, Namuco O, Moya T, Quilang J. 1997. Growth and yield<br />

response of field-grown tropical rice to increasing carbon dioxide<br />

and air temperature. Agron. J. 89:45-53.<br />

Notes<br />

Authors’ address: Graduate School of Agriculture, Kyoto University,<br />

Sakyo-ku, Kyoto 606-8502, Japan, e-mail:<br />

horiet@adm.kais.kyoto-u.ac.jp.<br />

Monitoring rice growth and development using<br />

a crop model: the case of northern Japan<br />

Masaharu Yajima<br />

<strong>Rice</strong> yield has increased dramatically with the development of<br />

improved nursery techniques, new varieties resistant to lodging<br />

and diseases, and new yield-enhancing agrochemicals.<br />

Although rice farmers commonly attain high yield, yield fluctuations<br />

sometimes occur because of unfavorable weather conditions<br />

during the rice-cropping season in particular areas. A<br />

recent study shows that summer weather in northern Japan since<br />

1982 appears to exhibit a distinct five-year cycle, with a pressure<br />

difference between Wakkanai in Hokkaido and Sendai in<br />

Tohoku. The temperature also follows similar five-year cycles<br />

and the second year of each cycle is typical of the Yamase, a<br />

cold northeasterly wind, and is consistent with the cool summer<br />

in northern Japan (Kanno 2004). For instance, severe spikelet<br />

sterility because of cool weather that occurred during meiosis<br />

of the pollen mother cell to the flowering stage of the rice<br />

crop in some areas of Tohoku Region in 1980, 1988, 1993,<br />

and 2003 greatly reduced yield.<br />

This paper intends to describe the research approach and<br />

initial results of wide-area monitoring of crop growth and development<br />

in 1993 and 2003 using a rice crop model (Yajima<br />

1996) to construct the initial version of a climatic early warning<br />

system against cool summer damage of rice under changing<br />

climate.<br />

Monitoring crop growth and development<br />

using a rice crop model<br />

The approach involved using the development stage and spikelet<br />

sterility and yield models, and crop and geo-climatic data<br />

sets to develop a prediction system.<br />

Based on the development stage (DVS) model designed<br />

by Horie (1987), values of 0, 1, and 2 are assigned to emergence<br />

(seed germination), heading, and physiological maturity,<br />

respectively. The value of DVS at any point of crop development<br />

is calculated by integrating the developmental rate<br />

(DVR), expressed as a function of daylength and daily mean<br />

temperature, with time.<br />

Generally, dry matter accumulation at any point in rice<br />

growth is proportional to the accumulated solar radiation intercepted<br />

by the canopy, except at the final stage of rice growth,<br />

when DVS is close to 2. The model used to estimate daily dry<br />

matter increase was adopted from Monteith (1977).<br />

The spikelet sterility model on the relationship between<br />

spikelet sterility and cool-temperature sensitivity of the rice<br />

plant at the panicle development stage was proposed by Yajima<br />

et al (1989), with the following equation:<br />

Session 19: Climate change and rice production 539


G = Σ (To – Ti) W(DVS)<br />

for Ti < 18.9 and 1.20 > DVS > 0.72 (1)<br />

w<strong>here</strong> W(DVS) is the panicle sensitivity factor for cool temperature<br />

as a function of DVS. <strong>Rice</strong> shows two sensitivity peaks<br />

to cool temperature. The first is observed at DVS = 0.88, which<br />

corresponds to meiosis of the pollen mother cell, and the second<br />

is at DVS = 1.07, which corresponds to the mid-flowering<br />

stage.<br />

Grain yield is proportional to dry matter accumulation<br />

at physiological maturity (W m ) and is expressed as follows:<br />

Y = HI × (1 – UF/100) × W m (2)<br />

w<strong>here</strong> Y is the grain yield (brown rice) and HI is the harvest<br />

index, with a value of 0.4.<br />

Crop data such as variety planted, transplanting date,<br />

heading date, and actual paddy yield were provided by the<br />

Department of Statistics, Ministry of Agriculture, Forestry, and<br />

Fisheries (MAFF). The Automated Meteorological Data Acquisition<br />

System (AMeDAS) provided the real-time weather<br />

information all over Japan. Digital national land information<br />

in Japan is also provided by the Ministry of Land, Infrastructure,<br />

and Transport for the information on land elevation, land<br />

use, and other geographical data on each rectangular grid-point<br />

1 km × 1 km in dimension. The mesh climatic data system<br />

provided an opportunity to estimate the daily mean temperature<br />

and solar radiation at each grid-point so that real-time<br />

weather information would be available at every mesh (1 km 2 )<br />

all over Japan (Seino 1993).<br />

The investigation focused on Tohoku Region involving<br />

the monitoring of Aomori, Iwate, Miyagi, Akita, Yamagata,<br />

and Fukushima prefectures in 1993 and 2003. Each prefecture<br />

was divided into three to five subdivisions based on geographic<br />

and climatic conditions. Using the two abovementioned models,<br />

crop development and percentage of sterility were estimated<br />

for Tohoku Region in 1993 and 2003. The real-time<br />

mesh data on daily air temperature and solar radiation at 1 km<br />

× 1 km grid-points were estimated by using Seino’s method<br />

with daily AMeDAS data. Crop data were provided by MAFF.<br />

Results from simulation<br />

Spikelet sterility and yield index<br />

The percentage of sterility caused by cool temperature was<br />

estimated for Tohoku Region in 1993 and 2003. Spikelet sterility<br />

estimates of 50–100% were obtained in the Pacific<br />

Ocean–side prefectures, particularly in areas with large negative<br />

temperature deviations (3–5 o C) from climatic normals.<br />

Spikelet sterility estimates for the prefectures on the Japan Sea–<br />

side, which ranged from 10% to 30%, may be due to the negative<br />

deviation of air temperature from climatic normals by 1–<br />

3 o C, particularly during meiosis of mother pollen cells until<br />

heading in these areas.<br />

When the estimated spikelet sterility in Tohoku Region<br />

was plotted against that observed by the Department of Statistics<br />

of MAFF, a highly significant linear relationship (R =<br />

–0.932***) was obtained in 2003. This suggests that the spikelet<br />

sterility model is suitable for prediction purposes.<br />

<strong>Rice</strong> growth and yield<br />

As described in the methodology, the combined use of DVS,<br />

crop growth, and spikelet sterility models leads to the estimation<br />

of yield. In this case, daily mean temperature and solar<br />

radiation from the mesh data and the crop growth data were<br />

used. Yields were estimated using the rice crop model for<br />

Tohoku Region in 1993 and 2003. Estimated yields based on<br />

the actual daily mean temperature and solar radiation were<br />

generally high (4–5 t ha –1 ) on the Japan Sea–side, particularly<br />

in some parts of Aomori, and most parts of Akita and Yamagata<br />

prefectures. Low yield estimates were obtained on the Pacific<br />

Ocean–side of Aomori and Iwate prefectures. On the inland<br />

and southern portions of Iwate, and about 40% of Fukushima,<br />

yield ranged from 2 to 4 t ha –1 .<br />

With the climatic normal as the basis of the yield estimate,<br />

it is apparent that the estimated yield in the Japan Sea–<br />

side prefectures surpassed 5.5 t ha –1 . These areas consistently<br />

yielded high even when the yield estimates were based on actual<br />

temperature and solar radiation. Estimated potential yields<br />

in Aomori (Pacific Ocean–side) could be as high as 4.5 t ha –1<br />

under the climatic normal, but yield estimates were below 1 t<br />

ha –1 under the adversely cool temperature in 1993. Similarly,<br />

the estimated potential yield in Iwate and Miyagi prefectures<br />

decreased by 1–3.5 t ha –1 under the adverse cool weather.<br />

As a check for the reliability of the yield estimates, actual<br />

yields under climatic normals and cool weather conditions<br />

were plotted against estimated yields under two climatic<br />

conditions. The good fitness of the actual and estimated yields<br />

in the unity slope proved the reliability of the rice crop model<br />

in the monitoring and prediction of yield (Fig. 1).<br />

Importance of shifting heading date<br />

by changing transplanting days<br />

It is known that cool damage, which is sometimes called the<br />

accident element, differs greatly according to heading date.<br />

Using the crop model, the effects of shifting transplanting date<br />

on sterility and yield were examined under weather conditions<br />

in 2003. It was proved that sterility decreased considerably<br />

only by delaying transplanting slightly in week 1 on the Pacific<br />

Ocean–side in Aomari, Iwate, and Miyagi prefectures. It<br />

seems reasonable to expect a reduction in cool summer damage<br />

by shifting the transplanting date or by changing rice varieties<br />

to minimize the risk from unfavorable weather under<br />

changing climate (Table 1).<br />

Conclusions<br />

A crop model was used to develop a monitoring and forecasting<br />

system for rice development, spikelet sterility, and yield in<br />

Tohoku Region, Japan, in 1993 and 2003. With the use of meshweather<br />

data, rice models were developed and varietal characteristics<br />

of rice planted in the monitored area, spatial distribu-<br />

540 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Estimated yield (t ha –1 )<br />

7<br />

6<br />

Normal year<br />

2003<br />

5<br />

4<br />

3<br />

(1:1)<br />

2<br />

r = 0.944<br />

1<br />

0 1 2 3 4 5 6 7<br />

0 1 2 3 4 5 6<br />

Observed yield (t ha –1 )<br />

Fig. 1. Spatial distribution of estimated yield (left) and its comparison with observed yield in<br />

2003 (right), Tohoku Region.<br />

Table 1. Estimated sterility and yield resulting from shifting transplanting date in 2003.<br />

Prefecture<br />

Sterility (%) Yield (t ha –1 )<br />

Agroecological<br />

zone 2003 1 wk 2 wk 2003 1 wk 2 wk<br />

later later later later<br />

Aomori Aomori 27.2 6.5 7.3 3.77 4.88 4.47<br />

Tsugaru 14.3 3.8 6.3 4.87 5.42 4.79<br />

Nanbu 47.4 6.6 9.5 2.26 4.05 3.56<br />

Shimokita 46.5 11.9 11.2 2.23 3.76 3.63<br />

Iwate Upper Kitakami 23.2 11.4 14.4 3.55 3.83 3.17<br />

Lower Kitakami 13.5 5.2 6.9 4.06 4.32 3.96<br />

Southeast 25.4 7.9 8.5 3.31 4.10 3.80<br />

Shimohei 57.1 23.4 14.2 1.66 2.92 2.87<br />

North 58.0 26.9 16.9 1.70 2.83 2.78<br />

Miyagi South 15.4 4.9 5.4 3.74 4.15 3.95<br />

Central 14.6 3.3 3.9 3.71 4.19 3.97<br />

North 12.5 3.7 4.9 3.90 4.22 3.97<br />

East 15.0 3.2 3.1 3.70 4.31 4.15<br />

tion of mean air temperature, and its deviation from climatic<br />

normals, as well as spikelet sterility caused by cool temperature,<br />

were determined. A significant linear correlation was<br />

obtained between the estimated spikelet sterility and yield. The<br />

results suggest the importance of using a crop model to monitor<br />

and forecast rice development stages and spikelet sterility<br />

at the regional level or in areas affected by cool temperature<br />

damage. With this method, extension staff could easily provide<br />

information on the possible occurrence of spikelet sterility<br />

in particular areas, which could enable rice growers to take<br />

necessary countermeasures to minimize the yield reduction<br />

from cool temperature.<br />

References<br />

Horie T. 1987. A model for evaluating climatic productivity and water<br />

balance of irrigated rice and its application to Southwest Asia.<br />

Southwest Asian Studies, Kyoto Univ. 25:62-71.<br />

Kanno H. 2004. Five-year cycle of north-south pressure difference<br />

as an index of summer weather in northern Japan from 1982<br />

onwards. J. Meteorol. Soc. Jpn. 82:711-724.<br />

Seino S. 1993. An estimation of distribution of meteorological elements<br />

using GIS and AMeDAS data. Jpn. J. Agric. Meteorol.<br />

48:379-383.<br />

Yajima M, Nitto A, Seino H. 1989. Estimation of percent sterility of<br />

rice spikelets with DVS model. Abstract for 1989 Annual<br />

Meeting of the Agricultural Meteorological Society, Japan.<br />

p 58-59.<br />

Yajima M. 1966. Monitoring regional rice development and coolsummer<br />

damage. JARQ 30:139-143.<br />

Session 19: Climate change and rice production 541


Yajima M. 1996. Monitoring and forecasting of rice growth and development<br />

using crop-weather model. Proceedings of the 2nd<br />

Asia Crop Science Conference, Crop Science Society of Japan.<br />

p 280-285.<br />

Yajima M. 2003. Early warning system against cool summer damage:<br />

case of Northern Japan. In: Coping against El Niño for<br />

stabilizing rainfed agriculture: lessons from Asia and the Pacific.<br />

CGPR Center Monograph 43. p 57-70.<br />

Notes<br />

Author’s address: Department of Biology and Environmental Sciences,<br />

National Agricultural <strong>Research</strong> Center for Tohoku Region,<br />

National Agricultural <strong>Research</strong> Organization, Morioka,<br />

Iwate 020-0198, Japan, e-mail: yajima@affrc.go.jp.<br />

Coping with climate variability and change in rice<br />

production systems in the Philippines<br />

Felino P. Lansigan<br />

Climate variability is a major source of risk in rice production<br />

since it greatly affects yield variation and often leads to yield<br />

losses (Pantastico and Cardenas 1980, Lansigan et al 2000).<br />

Climate change is also expected to affect crop growth and development,<br />

resulting in yield reduction (Peng et al 1995,<br />

Matthews et al 1996). The stability of rice production systems<br />

in tropical agroenvironments depends on adaptation strategies<br />

and mitigation measures applied to cope with these events.<br />

This paper analyzes the effects of climate variability and<br />

change on rice production in the Philippines. Climatic events<br />

that are important to rice growth and production are analyzed.<br />

The paper distinguishes the effects associated with risks from<br />

long-term weather aberrations and short-term weather fluctuations.<br />

Coping strategies to adapt to or mitigate the effects of<br />

climate variability and change are discussed.<br />

Climate variability and change<br />

The Philippines has a tropical climate that is conducive to rice<br />

production year-round. The Philippine climate is generally characterized<br />

by four climatic types in terms of the relative duration<br />

and intensity of the wet and dry periods in different parts<br />

of the country. Type 1 climate has a pronounced wet period<br />

from May to November, and a dry period from December to<br />

April. Type 2 climate is characterized by no clear dry season,<br />

and maximum rainfall is experienced from November to January.<br />

Type 3 climate is characterized by no distinct wet and dry<br />

seasons but is relatively dry from November to April. Type 4<br />

climate has rainfall more or less evenly distributed throughout<br />

the year.<br />

Extreme climate variability conditions such as during the<br />

occurrence of El Niño and La Niña events have greatly affected<br />

the spatial and temporal distribution of rainfall in tropical<br />

rice-growing areas such as the Philippines. Figure 1 shows<br />

the percentile of the 12-month total rainfall in the Philippines<br />

for the period April to March during El Niño years in the last<br />

four decades. Significant changes in rainfall patterns occurred<br />

during different periods within the year. These extreme events,<br />

with a return period of 7–10 years, have tended to occur more<br />

frequently in recent years. Historically, El Niño events are often<br />

accompanied by the occurrence of temperature extremes<br />

(i.e., high temperatures during unusually prolonged periods<br />

that induce changes in potential evapotranspiration and soil<br />

moisture availability), resulting in severe droughts that cause<br />

reduced crop yields. Different areas across the archipelago experience<br />

varying degrees of drought.<br />

The Philippines is often visited by an average of 20 typhoons<br />

a year, which mostly occur in the eastern and northern<br />

portions of the archipelago. Typhoons, which are often accompanied<br />

by intense rainfall and strong winds, usually occur from<br />

June to October. These cause significant yield losses during<br />

the wet season, the growing period for most crops.<br />

Current climate change studies (IPCC 2001) anticipate<br />

that future climate will experience an appreciable increase in<br />

temperature, changes in the spatio-temporal distribution of precipitation,<br />

and increased frequency and intensity of extreme<br />

weather events. The frequencies of occurrence of successive<br />

wet and dry periods such as El Niño and La Niña and tropical<br />

cyclones and typhoons with strong winds are expected to increase.<br />

In recent years, typhoons have begun to be experienced<br />

during periods when they were less expected (e.g., November<br />

or December). Unfortunately, these events coincide with the<br />

period when rice and other crops are about to be harvested, or<br />

when the second crop has been planted.<br />

Effects of climate variability and change<br />

on rice growth and productivity<br />

Climate variability affects rice growth and the various crop<br />

processes and activities in rice production. It determines planting<br />

date, duration of crop growth, crop yield, and also management<br />

practices in rice production. The occurrence of extreme<br />

climate variability such as El Niño or La Niña events<br />

characterized by a prolonged dry period or heavy rainfall spell<br />

coinciding with the critical stages of crop growth and development<br />

may lead to significantly reduced crop yields and extensive<br />

crop losses. Statistics on rice production and productivity<br />

in the Philippines (Phil<strong>Rice</strong>-BAS 2000) show that the<br />

542 <strong>Rice</strong> is life: scientific perspectives for the 21st century


1951-52 1953-54 1957-58 1968-69 1972-73 1976-77<br />

1997-98<br />

1982-83 1986-87 1991-92 1992-93 1993-94 1994-95<br />

Percentile*<br />

≤10 Severe drought effects 41–60 Near normal to above normal >90 Severe flood damage<br />

11–20 Drought effects 61–80 Way above normal conditions *Percentile is a way to present<br />

variability with respect to time<br />

21–40 Moderate drought effects 81–90 Potential flood damage<br />

Fig. 1. Spatial and temporal variability of 12-month (April-March) rainfall during El Niño years in the Philippines. (Source: PAGASA 2000.)<br />

observed declines in production and yield coincide with the<br />

occurrence of El Niño events. <strong>Rice</strong> production has declined<br />

during these extremely dry periods since crop productivity or<br />

yield level has decreased, and the area planted to rice has been<br />

reduced to adapt to the anticipated drought period. The risk<br />

associated with climate variability of rice production in general<br />

depends mainly on the growth stage of the rice crop when<br />

the weather aberration occurs.<br />

Several studies using temperature gradient tunnels, crop<br />

simulation models, and field experiments have been conducted<br />

to evaluate the effects of climate change on rice crop growth<br />

and development, particularly temperature increase and increased<br />

or double CO 2 concentration (e.g., Horie 1993, Horie<br />

et al 1996, Matthews et al 1996). In general, simulation analyses<br />

and field experiments have shown a reduction in rice yields<br />

because of the sterility of spikelets, which are very sensitive to<br />

a temperature increase. The same studies have also shown that<br />

rice varieties respond nonlinearly with increased CO 2 concentration<br />

(Peng et al 1995).<br />

Coping strategies for climate variability and change<br />

Crop management to cope with climate variability<br />

Inasmuch as climate variability and change are inevitable, rice<br />

production systems should be able to adapt to weather fluctuations<br />

and climatic aberrations to minimize their negative<br />

effects. Coping with or managing climate variability and change<br />

in rice production systems requires a combination of adapta-<br />

tion and mitigation measures that involve the choice of rice<br />

crop variety, adaptation of cultural management practices, and<br />

understanding of climate science. Crop management measures<br />

include a range of possible strategies such as the following<br />

(Lansigan 2003): (1) adjusting the cropping calendar to synchronize<br />

crop planting and the growing period with soil moisture<br />

availability, (2) changing the rice variety to plant (i.e.,<br />

planting a drought-tolerant or early-maturing variety), (3) varying<br />

planting density, and (4) optimizing water-use efficiency<br />

by improving irrigation facilities and introducing water-saving<br />

techniques.<br />

Crop improvement strategies<br />

Biological measures being pursued to cope with climate variability<br />

and change include the breeding of drought-tolerant<br />

varieties and lodging-resistant cultivars in national and international<br />

rice breeding programs. Drought-tolerant rice varieties<br />

can be planted that are more adapted to warmer or drier<br />

conditions. This involves the screening and testing of rice<br />

germplasm collections that are sources of tolerance of water<br />

stress or that require less water for crop growth. Lodging-resistant<br />

cultivars will be useful in areas generally experiencing<br />

more frequent and intense typhoons with strong winds and more<br />

precipitation.<br />

Crop insurance for and risk from climate variability<br />

Risks associated with reduced rice production and yield losses<br />

caused by climate variability can be partly alleviated by pro-<br />

Session 19: Climate change and rice production 543


Estimating<br />

crop area<br />

Downscaling<br />

climate forecasts<br />

Cropping strategy<br />

Simulating<br />

seasonal crop<br />

yields<br />

Fig. 2. Schematic of a knowledge-based crop forecasting system using seasonal climate prediction, estimation of crop area, and simulation<br />

of rice yields.<br />

viding appropriate crop insurance coverage to rice farmers.<br />

Current crop insurance practices in the Philippines cover only<br />

the cost of land preparation and rice crop establishment. The<br />

crop insurance policy at the moment often does not consider<br />

the varying extent of vulnerability of rice-growing areas in<br />

different locations with different climatic types as well as the<br />

differences in risk from climate variability, which are site-specific<br />

and time-dependent. Although crop insurance has been<br />

recognized as an effective coping strategy, it is less popular<br />

among rice farmers because of the usually unaffordable insurance<br />

premium. Promotion of crop insurance to rice farmers<br />

requires not only the provision of a more reasonable insurance<br />

premium but also attractive crop insurance coverage schemes<br />

or options such as insuring not only the cost of crop establishment<br />

but also (1) the expected crop yield or (2) the expected<br />

revenue based on harvestable crop.<br />

Seasonal climate prediction and rice production<br />

In recent years, advances and developments in climate science,<br />

meteorology, and global data observation and monitoring<br />

networks have enabled the reasonably accurate prediction<br />

or real-time forecast of seasonal climate up to a 3-month lead<br />

time. Reliable forecasts of seasonal climate serve as important<br />

and crucial information to an early warning system to support<br />

crop production to recommend appropriate management actions<br />

or measures to take considering the anticipated climatic<br />

conditions during the cropping period. More specifically,<br />

knowledge-based crop forecasting that uses these seasonal climate<br />

forecasts will be useful in guiding rice farmers and concerned<br />

government agencies and other stakeholders to act accordingly<br />

to minimize the negative or detrimental consequences<br />

of climate variability. Such a crop forecasting system currently<br />

being piloted in the Philippines (Fig. 2) involves using seasonal<br />

climate forecasts and a validated process-based rice crop<br />

simulation model to predict rice crop performance under the<br />

predicted seasonal climate outlook during the growing period.<br />

Seasonal climate forecasts are often made at a regional<br />

level, and have to be downscaled to a specific location (e.g.,<br />

province of a country) to produce forecasts of rice yield performance<br />

in a given area. Crop forecasts provide useful information<br />

to stakeholders (e.g., farmers, extension workers, traders,<br />

and planners) in rice production systems at different levels.<br />

The crop forecasting system also includes efficient and<br />

effective tools and mechanisms to deliver the forecast information<br />

to the intended users in the area.<br />

Conclusions<br />

The vulnerability of rice production systems to climate variability<br />

in tropical regions depends on its time of occurrence<br />

relative to the growth stage of the crop. Advances in crop science,<br />

meteorology, and other sciences offer potential for knowl-<br />

544 <strong>Rice</strong> is life: scientific perspectives for the 21st century


edge-based approaches and strategies to manage, adapt to, and<br />

cope with climate variability and change. Effective and efficient<br />

adaptation and mitigation measures should be promoted<br />

to prepare stakeholders in rice production systems to enhance<br />

their resilience and flexibility when facing inevitable climatic<br />

events.<br />

References<br />

Horie T. 1993. Predicting the effects of climatic variation and effect<br />

of CO 2 on rice yield in Japan. J. Agric. Meteorol. 48:567-<br />

574.<br />

Horie T, Nakagawa H, Ohnishi M, Nakano J. 1996. <strong>Rice</strong> production<br />

in Japan under current and future climate. In: Matthews RB,<br />

Kropff M, Bachelet D, editors. Modeling the impacts of climate<br />

change on rice production in Asia. Wallingford (UK):<br />

CAB <strong>International</strong>. p 143-164.<br />

IPCC (Intergovernmental Panel on Climate Change). 2001. Climate<br />

change 2001: impacts, adaptation, and vulnerability. Contribution<br />

of Working Group II to the Third Assessment Report<br />

of the IPCC. Washington D.C., USA.<br />

Lansigan FP, delos Santos WL, Coladilla JLO. 2000. Agronomic<br />

impacts of climate variability on rice production in the Philippines.<br />

Agric. Ecosyst. Environ. 82:129-137.<br />

Lansigan FP. 2003. Assessing the impacts of climate variability on<br />

crop production, and developing coping strategies in rainfed<br />

agriculture. UN CGPRT Monograph No. 43, Bogor, Indonesia.<br />

p 21-36.<br />

Matthews RB, Kropff M, Bachelet D, editors. 1996. Modeling the<br />

impacts of climate change on rice production in Asia.<br />

Wallingford (UK): CAB <strong>International</strong> and <strong>IRRI</strong>.<br />

PAGASA (Philippine Atmospheric, Geophysical, and Astronomical<br />

Services Administration). 2000. El Niño years in the Philippines.<br />

Quezon City.<br />

Pantastico EB, Cardenas AC. 1980. Climatic constraints to rice production<br />

in the Philippines. In: Agrometeorology of the rice<br />

crop. Los Baños (Philippines): <strong>International</strong> <strong>Rice</strong> <strong>Research</strong><br />

<strong>Institute</strong>. p 3-8.<br />

Peng S, Ingram KT, Neue H-U, Ziska LH, editors. 1995. Climate<br />

change and rice. Berlin (Germany) and Los Baños (Philippines):<br />

Springer-Verlag and <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>.<br />

374 p.<br />

Phil<strong>Rice</strong>-BAS (Philippine <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong> and Bureau of<br />

Agricultural Statistics). 2000. <strong>Rice</strong> statistics handbook (1970-<br />

1997). Muñoz (Philippines): Phil<strong>Rice</strong>-BAS.<br />

Notes<br />

Author’s address: <strong>Institute</strong> of Statistics (INSTAT), University of the<br />

Philippines Los Baños, College, Laguna, 4031 Philippines,<br />

e-mail: fpl@instat.uplb.edu.ph.<br />

Effect of elevated CO 2 on nutrient uptake<br />

and nutritional conditions of rice<br />

Jianguo Zhu<br />

The China rice/wheat FACE (free-air carbon-dioxide enrichment)<br />

has been running since 2001. It is the first FACE approach<br />

to determine the effects of elevated CO 2 on intensive<br />

agroecosystems with a rice/wheat rotation under field conditions.<br />

The FACE system followed the Japanese design with<br />

three FACE rings, 12.5 m in diameter, and three ambient rings.<br />

The experimental setup was a split-plot design with CO 2 treatments<br />

(two CO 2 concentrations) as the main plots and N fertilization<br />

as subplot treatments (two N levels). Different from<br />

others, the China FACE system is run continuously year-round,<br />

24 h a day. The target CO 2 concentration ([CO 2 ]) at the ring<br />

center was 200 µmol mol –1 above ambient.<br />

Results showed that elevated CO 2 affects nutrient uptake<br />

and nutritional conditions of rice. Nitrogen content (%)<br />

in the rice plants sampled at different growth stages decreased<br />

significantly under FACE treatment, but N accumulation increased<br />

slightly because of the significant enhancement in dry<br />

matter production. Ear N concentration increased at the heading<br />

stage but decreased at the ripening stage. No significant<br />

effect was found on root N concentration at tillering, but root<br />

N concentration at jointing, heading, and ripening decreased.<br />

The FACE treatment resulted in a significant increase in N-<br />

use efficiency for biomass production (NUEp), which was<br />

measured at the 28th day after transplanting, at heading, and<br />

at maturity. A significant increase in N-use efficiency for grain<br />

output (NUEg) and nitrogen harvest index (NHI) under the<br />

FACE treatment was also observed. Nitrogen content (%) and<br />

N accumulation in rice plants increased significantly under<br />

high-N treatment, but N-use efficiency in rice plants decreased.<br />

Elevated CO 2 significantly increased P and K uptake in<br />

aboveground tissues. P fertilization had no significant effect<br />

on various tissue dry biomass. Leaf P concentration at jointing,<br />

heading, and ripening increased, but no significant effect<br />

was found on P concentration in the stem, ear, and root. P and<br />

K concentration in rice was not influenced in the same way as<br />

N concentration by elevated CO 2 . The dilution effect is always<br />

used to explain the decrease in N content led by elevated<br />

CO 2 ; however, it could not be used to explain the increase in P<br />

content. The average soil exchangeable K in the FACE ring<br />

increased more under the NN treatment than under the LN<br />

treatment in the rice season. The possible increase in soil or-<br />

Session 19: Climate change and rice production 545


ganic acid or HCO 3<br />

–<br />

because of elevated CO 2 may increase<br />

the release of soil mineral K.<br />

C content in various tissues changed unremarkably and<br />

the ratio of C over N (C/N) increased. Elevated CO 2 increased<br />

the C/N ratio in the leaf, stem, ear, and root by 1.8%, 11.1%,<br />

10.1%, and 18.7%, respectively, under LN, and by 7.6%,<br />

54.7%, 12.0%, and 33.9% under NN at the rice ripening stage.<br />

CO 2 enrichment led to a striking increase, particularly<br />

in the jointing and heading stages, in the concentrations of<br />

Fe 2+ , Mn 2+ , Ca 2+ , and Mg 2+ in the soil solution, w<strong>here</strong>as K +<br />

and Zn 2+ contents decreased. In addition, elevated CO 2 increased<br />

the concentrations of Si, P, Cl – , and HCO 3 – , but decreased<br />

S and SO 4<br />

2–<br />

in the soil solution. No N-supply effects<br />

were found on soil solution chemistry. Dissolved organic C,<br />

soil redox processes, and other biological processes played a<br />

key role in the dynamics of soil solution. During the rice-growing<br />

season, elevated CO 2 decreased soil redox potential. However,<br />

no CO 2 enrichment effects were found on soil-solution<br />

pH and soil exchangeable cations.<br />

Elevated CO 2 tended to increase the bioavailability of<br />

Fe, Mn, Cu, and Zn extracted with DTPA solutions. After the<br />

2002 and 2003 rice harvests, the concentration of DTPA extractable<br />

Fe increased by 15% (P ≤0.008) and 13% (P ≤0.001)<br />

in the soil layer at 0–5 cm, respectively. Enriched CO 2 led to a<br />

reduction in Cu concentration in all kinds of rice organs, as Fe<br />

did in roots. However, CO 2 enrichment increased Fe concentration<br />

in stems, senescent leaves, and ears. Except for roots,<br />

Zn and Mn followed the general pattern of nutrient reductions<br />

in rice shoots, but most of them were not statistically significant.<br />

Based on the increase in biomass under elevated CO 2 ,<br />

total content per hill of Fe, Mn, and Zn in rice roots and shoots<br />

was enhanced by CO 2 enrichment at four growing stages. No<br />

nitrogen treatment effect was found on plant-available micronutrients.<br />

Our results demonstrate that CO 2 -driven changes in soil<br />

microbial and redox processes in a paddy field could enhance<br />

soil CO 2 , CH 4 , and cation concentrations in the soil solution.<br />

Our findings also indicate that elevated CO 2 may stimulate<br />

soil chemical weathering because of higher P CO2 in the soil<br />

and more organic acids secreted by plant roots. This stimulation<br />

may increase soil nutrient mineralization and supply more<br />

available nutrients with growing plants. In the short term, we<br />

suggest that increased micronutrient demand in rice plants<br />

could be met by stimulating the availability of nutrients in the<br />

soil. However, it must be kept in mind that we may<br />

overgeneralize these results with only three years’ work. We<br />

cannot obviate the possibility that belowground responses to<br />

elevated atmospheric CO 2 are specific to particular soil types,<br />

cultivation systems, plant species, communities, and ecosystems.<br />

T<strong>here</strong>fore, more attention should be paid to the longterm<br />

effects of increasing atmospheric CO 2 on belowground<br />

processes in different intact ecosystems in the coming decade.<br />

The China <strong>Rice</strong>/Wheat FACE project is one research<br />

program within the China-Japan Science and Technology Cooperation<br />

Agreement. The main instruments and apparatus of<br />

the FACE system were supplied by the Japanese <strong>Rice</strong> FACE<br />

project. The project was supported by the Chinese Academy<br />

of Sciences, National Natural Science Foundation, and the<br />

Ministry of Science and Technology of China. The project also<br />

had financial support from the National <strong>Institute</strong> for Agro-Environmental<br />

Science of Japan.<br />

Notes<br />

Author’s address: State Key Laboratory of Soil and Sustainable Agriculture,<br />

<strong>Institute</strong> of Soil Science, Chinese Academy of Sciences,<br />

Nanjing 210008, China.<br />

Effect of soil properties, substrate addition, microbial<br />

inoculation, and sonication on methane production<br />

from three rice topsoils and subsoils in the Philippines<br />

Sudip Mitra and Deepanjan Majumdar<br />

Production and emission of CH 4 from rice fields, a gas about<br />

23 times more radiatively active than CO 2 , are an important<br />

feature of the global carbon cycle (Ramanathan et al 1985).<br />

<strong>Rice</strong> fields were identified as a major source of CH 4 and the<br />

intensity of CH 4 release to the atmosp<strong>here</strong> depends on several<br />

factors, including soil parameters (Denier van der Gon et al<br />

1992, Yao et al 1999, Mitra et al 1999). According to Yagi and<br />

Minami (1990), emission rates (flux) of CH 4 vary according<br />

to soil type and the organic matter applied; Bachelet and Neue<br />

(1993) illustrated the potential importance of differentiating<br />

soil types when estimating CH 4 emissions from rice fields.<br />

This study contains a series of experiments to characterize<br />

CH 4 production in three different rice topsoil and subsoil<br />

samples and their blends in different ratios created to produce<br />

gradients in soil properties for assessing CH 4 production potentials<br />

influenced by these properties. Blending was done with<br />

the assumption that, during long-term farming, topsoil and subsoil<br />

get mixed with each other, creating a similar situation. To<br />

estimate production potential, a laboratory incubation study<br />

was conducted estimating both entrapped and emitted CH 4 .<br />

Production potential was tested under special circumstances<br />

such as sterilization followed by inoculation, straw incorpora-<br />

546 <strong>Rice</strong> is life: scientific perspectives for the 21st century


tion and sonication to understand the influence of microbial<br />

addition, substrate addition, and the impact of the possible release<br />

of organo-minerals from the soil matrix on methane production.<br />

Materials and methods<br />

Soil collection and preparation<br />

Three rice soils (e.g., Luisiana, Maahas, and Pila) with a wide<br />

range of soil properties (Table 1) were collected from Central<br />

Luzon, Philippines, by a core sampler of 8 cm in diameter from<br />

0–20-cm (topsoil) and 30–50-cm (subsoil) layers. Soil from<br />

20–30-cm depth was not taken to avoid the possible mixing of<br />

the topsoil and subsoil. The entire volume of soil layer was<br />

mixed thoroughly and one subsample was taken for physicochemical<br />

analysis. After air-drying, soil samples were ground<br />

and passed through an 80-mesh sieve. Subsamples of air-dried<br />

topsoil and subsoil were blended in a 1:1, 3:1, and 1:3 ratio<br />

and mixed thoroughly, air-dried again, and stored in darkness<br />

at 25 °C temperature until the incubation experiment.<br />

Incubation study to estimate CH 4<br />

production<br />

The experiment was conducted by taking 20 g of soil and 40<br />

mL of de-ionized water in a 100-mL spoutless glass beaker<br />

with three replicates, which were then incubated. Gas samples<br />

were collected and analyzed periodically at 7-day intervals up<br />

to 91 days of incubation (DOI). The incubation procedure, gas<br />

sampling, and analysis have been described in detail elsew<strong>here</strong><br />

by Mitra et al (2002).<br />

Sterilization. In this set of soils, the beakers containing<br />

the soil suspensions and rubber corks were heat-sterilized separately<br />

at 121 °C for 40 min before incubation. After sterilization,<br />

the beakers were sealed with rubber corks immediately<br />

under a laminar flow and were then kept in the incubator at 30<br />

°C for 86 days. Nonsterilized natural soil was also incubated<br />

as a control.<br />

Sonication. In a separate set of soils, the beakers containing<br />

the soil suspension were treated in a sonicator-ultrasonic<br />

processor at 100 W output for 5 min. The beakers were<br />

kept in a water bath during sonication to reduce heating of the<br />

samples.<br />

Addition of rice straw. <strong>Rice</strong> straw was air-dried, pulverized,<br />

and passed through a 40-mesh sieve. Subsamples of 0.4<br />

g of rice straw powder were added to the soil suspension in the<br />

beakers.<br />

Statistical analysis<br />

Duncan’s multiple range test (DMRT) was done by MSTAT<br />

(version 1.41), developed by the Crop and Soil Science Division,<br />

Michigan State University, USA. All other analyses were<br />

done by MS Excel software developed by Microsoft Corporation,<br />

USA.<br />

Results and discussion<br />

Methane production and emission<br />

from topsoil, subsoil, and their blends<br />

The physicochemical properties of topsoils, subsoils, and<br />

blends in different topsoil/subsoil ratios are given in Table 1<br />

jointly with total CH 4 production. Some soil properties, such<br />

as pH and active Fe content, remained fairly stable in both<br />

layers and also in the different blends. In contrast, nitrogen<br />

and carbon content showed a steep decrease with decreasing<br />

topsoil share; only the nitrogen for Pila soil represented an<br />

exception from this trend for unknown reasons. In all other<br />

cases, the five other soil parameters correspond to a gradient<br />

N and C content of the soil, while other parameters are fluctuating<br />

without a consistent trend.<br />

Methane production began relatively early during the<br />

incubation; the peak appeared within 3 weeks after flooding<br />

of soil and then came down sharply. This pattern was typical<br />

for most rice soils in the absence of external substrates (Mitra<br />

et al 2002). As soon as the in<strong>here</strong>nt C was exhausted by the<br />

methanogens, the CH 4 production rate dropped sharply. Maahas<br />

topsoil had a much lower CH 4 production than the other two<br />

topsoils (Table 1). Production rates were consistently lower<br />

than 9 µg g –1 soil d –1 . In Pila topsoil, CH 4 production was very<br />

intense within the first week, resulting in an early maximum,<br />

and it decreased gradually over the remaining incubation period.<br />

For all three soils, total CH 4 production showed a decreasing<br />

trend in the order topsoil > 3:1 blend > 1:1 blend<br />

>1:3 blend > subsoil. However, while the 1:1 blend yielded<br />

very low production rates for Luisiana and Maahas (corresponding<br />

to 1.7% and 0.3% of the production by the respective<br />

topsoil; see Table 1), this blend resulted in an intermediate<br />

value for Pila (26% of the production by topsoil).<br />

For all three topsoils, soil Eh dropped to low values (data<br />

not shown). However, Eh levels varied in a relatively broad<br />

range during the later stages. Soil pH stabilized near neutral<br />

after flooding in all the soils and did not have wide fluctuations.<br />

Effect of different soil treatments on CH 4<br />

production<br />

Sterilization. After sterilization, no CH 4 production was observed<br />

in the first phase of incubation and a rapid increase was<br />

seen in production rates after inoculating the topsoils. All three<br />

topsoils showed maximum production rates at the sampling<br />

date directly after inoculation, followed by a sudden drop (Fig.<br />

1). Methane production peaks were much higher in the sterilized<br />

topsoils than in the control topsoils. When the topsoils<br />

were re-inoculated, apparently a large amount of unused organic<br />

C became readily available to the newly introduced<br />

methanogens. In the subsoils, production levels were generally<br />

low even after inoculation. Only Pila subsoil showed some<br />

discernible CH 4 production, but production rates increased with<br />

a considerable delay compared to the control.<br />

Different CH 4 production patterns were previously attributed<br />

to different abundance of viable methanogenic bacte-<br />

Session 19: Climate change and rice production 547


Table 1. Physicochemical properties of topsoil, subsoil, and blends of different topsoil/subsoil ratios and their total methane production.<br />

pH Active Fe Active Mn Available P Total N Total C Clay Silt Sand CH 4 production a (mean ± SD)(mg kg –1 soil)<br />

Soils (1:1 H 2 O) (%) (%) (mg kg –1 ) (g kg –1 ) (g kg –1 ) (%) (%) (%)<br />

Control Sonication Straw app. Sterilization<br />

Topsoil<br />

Luisiana 4.3 4.33 0.09 4.1 1.84 18.13 29 66 5 433.9 ± 52.9 g 813.2 ± 101.1 c 2,534.7 ± 638.4 e 609.7 ± 28.5 c<br />

Maahas 6.4 2.05 0.07 15.0 1.55 16.40 55 36 9 169.3 ± 26.9 d 252.4 ± 51.4 b 2,297.5 ± 286.7 d 44.4 ± 10.1 b<br />

Pila 7.5 0.50 0.10 62.0 3.64 45.50 21 58 21 837.1 ± 43.7 i 1,070.9 ± 94.9 d 3,067.8 ± 604.5 f 836.2 ± 90.3 d<br />

3:1 (topsoil + subsoil) blend<br />

Luisiana 5.4 4.21 0.14 4.3 1.40 11.90 67 30 3 253.3 ± 33.2 f – – –<br />

Maahas 6.9 2.86 0.19 15 0.90 9.80 58 39 3 39.7 ± 9.1 b – – –<br />

Pila 8.1 0.98 0.12 97 3.70 31.60 33 54 13 551.3 ± 53.2 h – – –<br />

1:1 (topsoil + subsoil) blend<br />

Luisiana 5.9 4.11 0.18 5.1 0.90 9.01 68 30 2 7.3 ± 0.9 a – – –<br />

Maahas 7.2 2.97 0.22 13 0.70 7.52 52 44 4 0.5 ± 0.04 a – – –<br />

Pila 7.9 0.94 0.09 67 3 26 35 54 11 216.6 ± 15.4 e – – –<br />

1:3 (topsoil + subsoil) blend<br />

Luisiana 6.2 4.07 0.23 4.3 0.80 7.02 68 30 2 1.3 ± 0.4 a – – –<br />

Maahas 7.0 3.19 0.24 11 0.60 5.59 50 47 3 1.2 ± 0.2 a – – –<br />

Pila 8.0 0.69 0.05 44 0.24 21.10 41 49 10 112.7 ± 11.4 c – – –<br />

Subsoil<br />

Luisiana 5.3 4.31 0.29 3.1 0.58 0.57 51 43 6 0.1 ± 0.1 a 0.2 ± 0.07 a 1,996.7 ± 282.8 c 0.3 ± 0.1 a<br />

Maahas 6.8 3.13 0.29 3.5 0.28 2.60 43 54 3 0.3 ± 0.1 a 0.1 ± 0.06 a 1,363.3 ± 291.9 b 0.9 ± 0.7 a<br />

Pila 7.1 0.50 0.10 19 1.85 1.94 44 47 9 0.9 ± 0.2 a 0.4 ± 0.3 a 734.5 ± 58.2 a 4.0 ± 0.6 a<br />

a Values followed by the same letters are not significantly different from each other at the 5% level of significance according to Duncan’s multiple range test (DMRT). DMRT was performed separately for CH4 methane production in<br />

different treatments.<br />

548 <strong>Rice</strong> is life: scientific perspectives for the 21st century


CH 4 (mg g –1 soil d –1 )<br />

25<br />

20<br />

15<br />

Control<br />

A<br />

0.06<br />

0.04<br />

Control<br />

E<br />

10<br />

5<br />

0<br />

0 20 40 0 80<br />

0.02<br />

0.00<br />

0<br />

20 40 60 80<br />

Straw incorporation<br />

120<br />

B<br />

100<br />

80<br />

60<br />

40<br />

20<br />

0<br />

0 20 40 6 0 80<br />

Straw incorporation<br />

100<br />

F<br />

80<br />

60<br />

40<br />

20<br />

0<br />

0 20 40 6 0 80<br />

6<br />

Sonication<br />

50<br />

C<br />

40<br />

30<br />

20<br />

10<br />

0<br />

0 20 40 0 80<br />

Sonication<br />

0.16<br />

G<br />

0.12<br />

0.08<br />

0.04<br />

0.00<br />

0 20 40 6 0 80<br />

80<br />

60<br />

40<br />

20<br />

PI<br />

LU<br />

MA<br />

Inoculated<br />

Sterilization<br />

D<br />

0.16<br />

0.12<br />

0.08<br />

0.04<br />

Inoculated<br />

Sterilization<br />

H<br />

0<br />

0 20 40 6 0 80<br />

DOI<br />

0.00<br />

0 20 40 6 0 80<br />

Fig. 1. Methane production in topsoils (A,B,C,D) and subsoils (E,F,G,H) as influenced by<br />

sterilization and subsequent inoculation, sonication, and straw incorporation. DOI = days<br />

of incubation; PI = Pila, LU = Luisiana, and MA = Maahas. Please note different scaling on<br />

Y axis.<br />

Session 19: Climate change and rice production 549


ia in the soil samples, which became active when water and<br />

substrates were provided (Roy et al 1997). However, the results<br />

of our study with sterilized and inoculated soil samples<br />

did not give any evidence of an effect by the abundance of<br />

methanogenic bacteria.<br />

Methane production is a very complicated biochemical<br />

process driven by the microbial degradation of organic matter<br />

under anoxic conditions by methanogenic bacteria and is the<br />

final step in a series of sequential reduction processes that are<br />

initiated when soil is flooded (Patrick and Reddy 1978,<br />

Ponnamperuma 1981). In topsoils, sterilization followed by<br />

inoculation resulted in an increase in CH 4 production immediately<br />

following inoculation. Sterilization has not only interrupted<br />

the decay of in<strong>here</strong>nt soil organic carbon, it has also<br />

prompted CH 4 production by supplying readily degradable biomass<br />

C stemming from the destroyed microbial community.<br />

Apparently, the entire suite of bacteria involved in substrate<br />

supply and CH 4 production was going through very rapid<br />

growth after sterilization. This pulse triggered by inoculation<br />

had resulted in a much higher total CH 4 production than the<br />

control. Enhancement of CH 4 production on exogenous carbonaceous<br />

substrate addition has been previously observed (Lu<br />

et al 2000), but the effect of sterilization and subsequent inoculation<br />

on methane emissions is rarely studied. Ironically<br />

enough, this treatment did not enhance CH 4 production in<br />

Maahas and Pila subsoils versus their respective controls, which<br />

might be due to less dead microbial biomass after sterilization<br />

or poor microbial community establishment after inoculation.<br />

Straw incorporation. The stimulating effect of rice straw<br />

on CH 4 production was observed for topsoils and subsoils. All<br />

topsoils had shown high CH 4 peaks within the initial 3 weeks<br />

of incubation, resulting in similar increments triggered by straw<br />

application, that is, approximately 2,150 mg CH 4 kg –1 soil more<br />

production than the control (Fig. 1). Subsoils were also very<br />

responsive to straw amendment; CH 4 production from the<br />

amended subsoils exceeded that from the untreated topsoils.<br />

However, while the straw-borne increment in Luisiana subsoil<br />

was high, CH 4 production was apparently impeded in Maahas<br />

and Pila subsoils. But, in all the subsoils, the percent increase<br />

in CH 4 production compared with the control was much higher<br />

than what was found in topsoils.<br />

Effect of sonication of CH 4 production. Sonication is<br />

often used to separate organo-minerals from the soil matrix,<br />

namely, organic matter associated with clay (Watson 1971).<br />

Sonication of soil resulted in diverging effects on CH 4 production<br />

in topsoils (Fig. 1). Luisiana topsoil showed higher<br />

production rates after sonication and total production increased<br />

by approximately 30% vis-à-vis the control. Pila topsoil showed<br />

an earlier and higher peak, but overall production was almost<br />

at an identical level. In contrast, production rates generally<br />

decreased in Maahas topsoil, resulting in a 70% reduction in<br />

overall production. For the subsoils, CH 4 production increased<br />

upon sonication but only Pila showed an appreciable (78%)<br />

stimulation through sonication.<br />

In Luisiana topsoil, this process seems to have supplied<br />

substrate that was not degradable without sonication enhancing<br />

CH 4 production. In Pila topsoil, sonication provided substrate<br />

that would have been otherwise degraded at a later stage,<br />

so that t<strong>here</strong> was no change in total production. In Maahas<br />

soil, however, sonication has reduced CH 4 production. Although<br />

we have no clue on the mechanisms of this effect, we<br />

assume an effect of the high clay content (55%) of Maahas<br />

topsoil.<br />

Conclusions<br />

The enhanced rate of CH 4 production after inoculation in sterilized<br />

soils demonstrated the importance of dead microbial<br />

biomass as substrate and the external inoculation of<br />

methanogens, which created a perfect methanogenic condition.<br />

The establishment of microbial communities was found to be<br />

a critical factor for regulating CH 4 production after inoculation<br />

in sterilized soils. Intrinsically, although subsoils had a<br />

very low CH 4 production potential, the addition of rice straw<br />

significantly increased their potential. Sonication of soils was<br />

done to see the effect of the physical disturbance on CH 4 production<br />

potential. Sonication apparently has certain effects on<br />

the soil matrix and thus on the association of organic matter<br />

and clay, which might have regulated CH 4 production in different<br />

soils. However, further studies are needed to find a<br />

clearer answer to this observation.<br />

References<br />

Bachelet D, Neue HU. 1993. Methane emissions from wetland rice<br />

areas of Asia. Chemosp<strong>here</strong> 26:219-237.<br />

Denier van der Gon H, Neue HU, Lantin RS, Wassmann R, Alberto<br />

MCR, Aduna JB, Tan MJ. 1992. Controlling factors of methane<br />

emission from rice fields. In: Batjes NH, Bridges EM,<br />

editors. World inventory of soil emission potentials. WISE<br />

Rep 2, ISRIC. Wageningen, Netherlands. p 81-92.<br />

Lu Y, Wassmann R, Neue HU, Huang C, Bueno CS. 2000.<br />

Methanogenic responses to exogenous substrates in anaerobic<br />

rice soils. Soil Biol. Biochem. 32(11-12):1683-1690.<br />

Mitra S, Jain MC, Kumar S, Bandyopadhyay SK, Kalra N. 1999.<br />

Effect of rice cultivars on methane emission. Agric. Ecosyst.<br />

Environ. 73:177-183.<br />

Mitra S, Wassmann R, Jain MC, Pathak H. 2002. Properties of rice<br />

soils affecting methane production potentials. 1. Temporal<br />

patterns and diagnostic procedures. Nutr. Cycl. Agroecosyst.<br />

64(1-2):169-182.<br />

Patrick WH Jr, Reddy CN. 1978. Chemical changes in rice soils. In:<br />

Soils and rice. Manila (Philippines): <strong>International</strong> <strong>Rice</strong> <strong>Research</strong><br />

<strong>Institute</strong>. p 361-379.<br />

Ponnamperuma FN. 1981. Some aspects of the physical chemistry<br />

of paddy soil. In: Proceedings of the symposium on paddy<br />

soils, Beijing, <strong>Institute</strong> of Soil Science. Beijing (China):<br />

Academia Sinica, Science Press. p 59-94.<br />

Ramanathan V, Cicerone RJ, Singh HB, Kiehl JT. 1985. Trace gas<br />

trends and their potential role in climate change. J. Geophys.<br />

Res. 90:5547-5566.<br />

Roy R, Klüber HD, Conrad RF. 1997. Early initiation of methane<br />

production in anoxic soil despite the presence of oxidants.<br />

FEMS Microbiol. Ecol. 12:311-320.<br />

550 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Watson JR. 1971. Ultrasonic vibration as a method of soil dispersion.<br />

Soils Fert. 37:127-134.<br />

Yagi K, Minami K. 1990. Effects of organic matter application on<br />

methane emission from some Japanese paddy fields. Soil Sci.<br />

Plant Nutr. 36:599-610.<br />

Yao H, Conrad R, Wassmann R, Neue HU. 1999. Effect of soil characteristics<br />

on sequential reduction and methane production in<br />

sixteen rice paddy soils from China, the Philippines and Italy.<br />

Biogeochemistry 47:269-295.<br />

Notes<br />

Modeling the effects of farming management<br />

alternatives on greenhouse gas emissions:<br />

a case study for rice agriculture in China<br />

Authors’ addresses: Sudip Mitra, Center for Global Environment<br />

<strong>Research</strong>, The Energy and Resources <strong>Institute</strong> (TERI), Darbari<br />

Seth Block, Habitat Place, Lodhi Road, New Delhi 110003,<br />

India, e-mail: sudip@teri.res.in, sudipmitra@yahoo.com, previously<br />

with Crop, Soil, and Water Sciences Division, <strong>International</strong><br />

<strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>, Los Baños, Philippines;<br />

Deepanjan Majumdar, Department of Environmental Sciences,<br />

<strong>Institute</strong> of Science and Technology for Advanced Studies and<br />

<strong>Research</strong> (ISTAR), Vallabh Vidyanagar 388120 Gujarat, India.<br />

Acknowledgments: Support provided by the <strong>International</strong> <strong>Rice</strong> <strong>Research</strong><br />

<strong>Institute</strong> (<strong>IRRI</strong>), Philippines, and The Energy and Resources<br />

<strong>Institute</strong> (TERI), India, is kindly acknowledged.<br />

Changsheng Li, Steve Frolking, Xiangming Xiao, Berrien Moore III, Steve Boles, Yu Zhang, Jianjun Qiu, Yao Huang, William Salas, and Ronald Sass<br />

Since the early 1980s, water management of rice paddies in<br />

China has changed substantially, with midseason drainage<br />

gradually replacing continuous flooding (Shen 1998). This has<br />

provided an opportunity to estimate how management alternatives<br />

affect greenhouse gas emissions at a large regional scale.<br />

Both methane (CH 4 ) and nitrous oxide (N 2 O) fluxes from<br />

agroecosystems are highly variable in space and time, affected<br />

by ecological drivers (e.g., climate, vegetation, and anthropogenic<br />

activity), soil environmental factors (e.g., temperature,<br />

moisture, pH, redox potential, and substrate concentration gradients),<br />

and biochemical or geochemical reactions (Li 2000,<br />

Li et al, 2004). Process-based models are used to quantify trace<br />

gas fluxes driven by the local climate, soil, vegetation, and<br />

management conditions at the site scale. Geographic information<br />

systems (GIS) databases provide spatially differentiated<br />

information on climate, soil, vegetation, and management to<br />

drive the model runs across the region. To quantify the effects<br />

of water management change on carbon (C) sequestration and<br />

CH 4 and N 2 O emissions from approximately 30 million hectares<br />

of rice paddies in China, we integrated a process-based<br />

model, DNDC, with a GIS database of paddy area, soil properties,<br />

paddy management (fertilizer use, water management,<br />

crop residue management, planting and harvest dates), and daily<br />

weather data.<br />

DNDC was originally developed for predicting C sequestration<br />

and trace gas emissions for nonflooded agricultural<br />

lands, simulating the fundamental processes controlling<br />

the interactions among ecological drivers, soil environmental<br />

factors, and relevant biochemical or geochemical reactions,<br />

which collectively determine the rates of trace gas production<br />

and consumption in agricultural ecosystems (Li et al 1992,<br />

1994). Details of management (e.g., crop rotation, tillage, fer-<br />

tilization, manure amendment, irrigation, weeding, and grazing)<br />

have been parameterized and linked to the various biogeochemical<br />

processes (e.g., crop growth, litter production,<br />

soil water infiltration, decomposition, nitrification, denitrification,<br />

etc.) embedded in DNDC (Fig. 1). To enable DNDC to<br />

simulate C and N biogeochemical cycling in paddy rice ecosystems,<br />

we modified the model by adding a series of anaerobic<br />

processes. The paddy-rice version of DNDC has been described<br />

and tested in recent manuscripts (Cai et al 2003, Li et<br />

al 2004), and is summarized briefly <strong>here</strong>.<br />

The Nernst equation, a basic thermodynamic formula<br />

defining soil redox potential (i.e., Eh) based on concentrations<br />

of the oxidants and reductants existing in the soil liquid phase<br />

(Stumm and Morgan 1981), and the Michaelis-Menten equation,<br />

a widely applied formula describing the kinetics of microbial<br />

growth with dual nutrients (Paul and Clark 1989), were<br />

linked to each other in DNDC to simulate variation of soil Eh<br />

and its impact on rates of the redox reactions, which produce<br />

or consume CH 4 or N 2 O during the frequent changes between<br />

saturated and unsaturated conditions driven by water management.<br />

CH 4 or N 2 O is produced or consumed under certain Eh<br />

conditions (–300 to –150 mV for CH 4 , and 200 to 500 mV for<br />

N 2 O production), so the two gases are produced during different<br />

stages of the varying soil redox potential. The major substrates<br />

controlling production of CH 4 or N 2 O are dissolved<br />

organic carbon (DOC), ammonium, and nitrate. DNDC allocates<br />

the substrates to drive nitrification, denitrification, and<br />

fermentation based on a simple kinetic scheme, the so-called<br />

“anaerobic balloon.” An anaerobic balloon is defined as the<br />

effective anaerobic volumetric fraction of a soil, which is quantified<br />

by the Eh value as calculated with the Nernst equation.<br />

When the substrates are allocated within the balloon, they will<br />

Session 19: Climate change and rice production 551


Ecological<br />

drivers<br />

Climate Soil Vegetation Human activity<br />

Annual<br />

average<br />

temp.<br />

Potential<br />

evapotrans.<br />

Water demand<br />

Water uptake<br />

N demand<br />

Daily growth<br />

C0 2<br />

Litter<br />

Very labile Labile Resistant<br />

LAI-regulated<br />

albedo<br />

Soil temp.<br />

profile<br />

Soil moist.<br />

profile<br />

Soil climate<br />

Evap.<br />

0 2<br />

diffusion<br />

Trans.<br />

Soil Eh<br />

profile<br />

Vertical<br />

water<br />

flow<br />

0 2<br />

use<br />

Water stress<br />

N uptake<br />

Grain<br />

Stems<br />

Root respiration<br />

Roots<br />

Plant growth<br />

Effect of temperature and moisture on decomposition<br />

NH 4<br />

+<br />

DOC<br />

Decomposition<br />

Microbes<br />

Labile Resistant<br />

Humads<br />

Labile Resistant<br />

Passive humus<br />

Soil<br />

environmental<br />

factors<br />

Temperature Moisture pH Eh Substrates: NH 4 + , NO 3 – , DOC<br />

NO –<br />

2<br />

NO<br />

N 2 O<br />

N 2<br />

Denitrification<br />

Nitrate<br />

denitrifier<br />

Nitrate<br />

denitrifier<br />

N 2 O<br />

denitrifier<br />

DOC<br />

NO 3<br />

–<br />

DOC<br />

NO –<br />

3<br />

N 2 O<br />

Nitrification<br />

Nitrifiers<br />

NO<br />

NH 4<br />

+<br />

NH 3<br />

NH 3<br />

Clay-<br />

NH 4<br />

+<br />

Soil Eh<br />

Aerenchyma<br />

DOC<br />

Fermentation<br />

CH 4 production<br />

CH 4 oxidation<br />

CH 4 transport<br />

CH 4<br />

Fig. 1. Structure of the DNDC model.<br />

participate in the reductive reactions (e.g., denitrification,<br />

methanogenesis); when the substrates are allocated outside of<br />

the balloon, they will be involved in oxidative reactions (e.g.,<br />

nitrification, methanotrophy). When a soil is flooded, oxygen<br />

diffusion into the soil is severely restricted, which reduces the<br />

soil Eh and causes swelling of the anaerobic balloon. The enlarged<br />

balloon will hold more DOC or nitrate to stimulate<br />

methanogenesis or denitrification. This mechanism has been<br />

embedded in DNDC to link the soil water regime to trace gas<br />

emissions for rice paddy ecosystems. The modified DNDC<br />

model has been tested against several methane flux data sets<br />

from wetland rice sites in the United States, Italy, China, Thailand,<br />

and Japan (Li et al 2002, Cai et al 2003). The test results<br />

indicate that DNDC is capable of estimating the seasonal patterns<br />

and magnitudes of CH 4 and N 2 O fluxes from the sites<br />

although discrepancies exist for some of the tested cases.<br />

A GIS database was constructed to hold the 30 million<br />

ha of rice paddies with different rotation systems at the county<br />

scale in China. The area occupied by each rotation in each<br />

county was quantified by combining a county-scale statistical<br />

database of crop-sown areas with a Landsat TM-derived landcover<br />

map for all of mainland China (Frolking et al 2002).<br />

The database also includes soil texture, pH, bulk density, and<br />

organic carbon content, and daily weather data for 1990 from<br />

610 weather stations across China. General data on fertilizer<br />

use, tillage, planting and harvest dates, crop residue management,<br />

and crop varieties were taken from various sources. Two<br />

water management scenarios, continuous flooding (CF) and<br />

midseason draining (MSD), were used in the model simulations.<br />

The modeled results indicated that the ranges in total<br />

CH 4 emissions with CF and MSD management were 6,400–<br />

12,000 and 1,700–7,800 Gg CH 4 -C y –1 , respectively. Taking<br />

the mean values, changing water management from continuous<br />

flooding to midseason draining caused a reduction in aggregate<br />

methane emissions from rice paddies of about 40%, or<br />

6 Tg CH 4 y -1 . This is 5–10% of total global rice paddy methane<br />

emissions (Prather et al 2001). The mitigating effect of<br />

midseason draining on CH 4 flux was highly uneven across the<br />

country. The highest flux reductions (>200 kg CH 4 -C ha –1 y –1 )<br />

552 <strong>Rice</strong> is life: scientific perspectives for the 21st century


were in Hainan, Sichuan, Hubei, and Guangdong provinces,<br />

with warmer weather and multiple-cropping rice systems. The<br />

smallest flux reductions (8.0 kg N ha –1 ) in<br />

Jilin, Liaoning, Heilongjiang, and Xinjiang provinces, w<strong>here</strong><br />

the paddy soils contained relatively high organic matter. The<br />

change in water management had very different effects on net<br />

greenhouse gas mitigation when implemented across climatic<br />

zones, soil types, or cropping systems. Maximum CH 4 reductions<br />

and minimum N 2 O increases were obtained when the<br />

midseason draining was applied to rice paddies with warm<br />

weather, high soil clay content, and low soil organic matter<br />

content, for example, Sichuan, Hubei, Hunan, Guangdong,<br />

Guangxi, Anhui, and Jiangsu provinces, which have 60% of<br />

China’s rice paddies and produce 65% of China’s rice harvest<br />

(see details in Table 1).<br />

References<br />

Cai Z, Sawamoto S, Li C, Kang G, Boonjawat J, Mosier A, Wassmann<br />

R. 2003. Field validation of the DNDC model for greenhouse<br />

gas emissions in East Asian cropping systems. Global<br />

Biogeochem. Cycles 17(4):doi:10.1029/2003GB002046.<br />

Frolking S, Qiu J, Boles S, Xiao X, Liu J, Zhuang Y, Li C, Qin X.<br />

2002. Combining remote sensing and ground census data to<br />

develop new maps of the distribution of rice agriculture in<br />

China. Global Biogeochem. Cycles 16(4):doi:10.1029/<br />

2001GB001425.<br />

Li C, Frolking S, Harriss RC. 1994. Modeling carbon biogeochemistry<br />

in agricultural soils. Global Biogeochem. Cycles 8:237-<br />

254.<br />

Li C, Frolking S, Frolking TA. 1992. A model of nitrous oxide evolution<br />

from soil driven by rainfall events. 1. Model structure<br />

and sensitivity. J. Geophys. Res. 97:9759-9776.<br />

Li C. 2000. Modeling trace gas emissions from agricultural ecosystems.<br />

Nutr. Cycl. Agroecosyst. 58:259-276.<br />

Li C, Mosier A, Wassmann R, Cai Z, Zheng X, Huang Y, Tsuruta J,<br />

Boonjawat J, Lantin R. 2004. Modeling greenhouse gas emissions<br />

from rice-based production systems: sensitivity and<br />

upscaling. Global Biogeochem. Cycles 18(1):doi:10.1029/<br />

2003GB002045.<br />

Paul EA, Clark FE. 1989. Soil microbiology and biochemistry. Second<br />

Edition. San Diego, Calif. (USA): Academic Press. 273<br />

p.<br />

Prather M, Ehhalt D, Dentener F, Derwent R, Dlugokencky E, Holland<br />

E, Isaksen I, Katima J, Kirchhoff V, Matson P, Midgley<br />

P, Wang M. 2001. Atmospheric chemistry and greenhouse<br />

gases. In: Houghton JT, Ding Y, Griggs DJ, Noguer M, van<br />

der Linden PJ, Dai X, Maskell K, Johnson CA, editors. Climate<br />

change 2001: the scientific basis. Contribution of Working<br />

Group I to the Third Assessment Report of the Intergovernmental<br />

Panel on Climate Change. Cambridge (UK): Cambridge<br />

University Press. p 239-287.<br />

Shen S. 1998. Soil fertility in China. Beijing (China): Chinese Agricultural<br />

Press. (In Chinese.)<br />

Stumm W, Morgan JJ. 1981. Aquatic chemistry: an introduction<br />

emphasizing chemical equilibria in natural waters. 2nd Edition.<br />

New York, N.Y. (USA): John Wiley & Sons. 780 p.<br />

Notes<br />

Authors’ addresses: Changsheng Li, Steve Frolking, Xiangming<br />

Xiao, Berrien Moore III, Steve Boles, Yu Zhang, <strong>Institute</strong> for<br />

the Study of Earth, Oceans, and Space, University of New<br />

Hampshire, Durham, NH, 03824, USA; Jianjun Qiu, <strong>Institute</strong><br />

of Agricultural Resources and Regional Planning, Chinese<br />

Academy of Agricultural Science, Beijing, China; Yao Huang,<br />

College of Resource and Environmental Sciences, Nanjing<br />

Agricultural University, Nanjing, China; William Salas, Applied<br />

Geosolutions, LLC, Durham NH 03824 USA; Ronald<br />

Sass, Department of Ecology and Evolutionary Biology, <strong>Rice</strong><br />

University, Houston TX 77005, USA, e-mail:<br />

changsheng.li@unh.edu.<br />

Acknowledgments: This research has been supported by NASA’s<br />

Terrestrial Ecology Program (NAG5-12838 and NAG5-7631),<br />

the NASA EOS-IDS program (NAG5-10135), and the Asian-<br />

Pacific Global Change Network (Land Use/Management<br />

Change and Trace Gas Emissions in East Asia—APN 2001-<br />

16). Development of the anaerobic biogeochemistry in DNDC<br />

was supported by the USDA Forest Service’s Southern Global<br />

Change Program.<br />

Session 19: Climate change and rice production 553


Table 1. Provincial paddy area and simulated CO 2 , CH 4 , and N 2 O maximum and minimum fluxes for continuous flooding (CF) and midseason draining (MSD) water<br />

management. CO 2 flux equals negative change in soil organic carbon storage. Sign convention for all fluxes is positive flux equals net emission from soil. All areas<br />

and all flux values greater than 10 Gg were rounded to two significant figures.<br />

Production b CO 2 Gg C y –1 CH 4 Gg C y –1 N 2 O Gg N y –1<br />

Province a (Gg C y –1 )<br />

CF min CF max MSD min MSD max CF min CF max MSD min MSD max CF min CF max MSD min MSD max<br />

Sichuan c 11,000 1,500 240 1,600 –380 1,800 1,300 1,300 200 49 34 72 47<br />

Hunan 12,000 370 –1,700 280 –2,000 1,100 550 580 110 38 32 54 41<br />

Jiangsu 9,000 1,800 1,400 1,900 1,300 1,200 770 1000 480 25 18 36 25<br />

Jiangxi 7,600 74 –1,000 –3 –1,200 1,100 560 710 72 33 22 54 31<br />

Anhui 6,300 600 –710 780 –920 1,100 460 870 77 29 14 38 19<br />

Hubei 8,300 510 –1,200 490 –1,300 1,100 410 650 46 24 13 33 16<br />

Guangdong 7,600 310 –700 57 –870 860 470 400 150 26 22 40 29<br />

Guangxi 6,200 1,800 15 1,700 –13 670 260 260 13 38 26 56 33<br />

Yunnan 2,600 180 –290 130 –320 160 81 18 3 12 12 17 14<br />

Guizhou 2,200 450 –560 530 –550 200 96 74 9 14 10 21 13<br />

Fujian 3,600 –1 –180 –39 –250 260 170 140 29 14 10 21 13<br />

Henan 1,600 340 88 300 26 340 140 230 27 6 3 9 4<br />

Liaoning 1,800 490 390 660 450 1,800 140 230 61 10 8 19 17<br />

Jilin 1,700 650 370 680 500 150 100 120 30 12 8 22 24<br />

Shaanxi 450 130 180 120 160 110 64 77 7 4 3 7 4<br />

Shanghai 800 160 140 160 120 150 95 120 56 2 2 3 2<br />

Inner Mongolia n.a. d 120 160 120 180 34 21 27 5 3 2 4 3<br />

Shandong 520 –47 20 –44 27 61 50 50 34 1 1 2 2<br />

Hebei 450 –22 22 –5 37 28 26 34 27 1 1 1 1<br />

Zhejiang 6,100 340 –390 340 –480 730 390 550 140 23 17 34 23<br />

Heilongjiang 3,200 1,800 1,400 1,800 1,600 270 180 230 78 36 26 44 44<br />

Tianjin 190 –14 11 7 27 17 16 32 26 0.7 0.6 1 1<br />

Ningxia 270 –47 –38 –29 –36 2 3 10 2 0.7 0.5 1 1<br />

Gansu n.a. d 7 11 7 12 2 2 2 0.6 0.1 0.1 0.2 0.2<br />

Hainan 790 610 210 610 200 200 100 73 19 8 4 12 5<br />

Beijing n.a. d –1 7 3 7 5 4 6 2 0.1 0.1 0.2 0.1<br />

Shanxi n.a. d 4 7 6 8 3 3 3 2 0.1 0.1 0.2 0.2<br />

Xinjiang n.a. d 51 56 57 63 51 27 42 7 2 1 2<br />

China 94,000 12,000 –2,000 12,000 –3,500 12,000 6,400 7,800 1,700 410 290 610 420<br />

a Provinces sorted by paddy area. Tibet and Qinghai provinces excluded because of small paddy areas.<br />

b Mean annual rough rice production for 1991-2000 (<strong>IRRI</strong> 2004); carbon fraction of dry weight<br />

assumed to be 50%. c Includes Chongqing Province, which was established from land in Sichuan Province in 1997. d Production data (see note 2 above) not reported individually for some provinces; total<br />

production for all nonreported provinces = 370 Gg C y –1 ; China total equals sum of all reported and nonreported provinces.<br />

554 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Impact of rising atmospheric CO 2 on CH 4 emissions<br />

from rice paddies<br />

Weiguo Cheng, Kazuyuki Yagi, Kazuyuki Inubushi, Kazuhiko Kobayashi, Hidemitsu Sakai, Han-Yong Kim, and Masumi Okada<br />

Recent anthropogenic emissions of key atmospheric trace gases<br />

(e.g., CO 2 , CH 4 , N 2 O, and CFC) that absorb infrared radiation<br />

may lead to an increase in global mean surface temperature,<br />

and thus have the potential to bring about changes in climate<br />

(IPCC 2001). Depending on population growth and energyuse<br />

scenarios, atmospheric CO 2 concentration is expected to<br />

rise from 370 ppm currently to about 485 to 1,000 ppm by<br />

2100 (IPCC 2001). CO 2 and CH 4 are two important greenhouse<br />

gases and they are responsible for approximately 55%<br />

and 20%, respectively, of the anthropogenic global warming<br />

effect. Most atmospheric CH 4 is produced by microbial activities<br />

in extremely anaerobic ecosystems, such as natural and<br />

cultivated wetlands, sediments, sewage, landfills, and the rumens<br />

of herbivorous animals. The methane from rice paddies<br />

accounts for about 17% of the anthropogenic sources. Also,<br />

plant-mediated transport is a very important pathway for CH 4<br />

emissions from cultivated rice soils. Many studies have demonstrated<br />

a positive effect of elevated CO 2 on rice biomass<br />

(above- and belowground) production and grain yield. The<br />

direct effect of elevated CO 2 on rice root biomass and tiller<br />

number would be expected to indirectly affect CH 4 production<br />

and emissions from rice fields, although such an effect<br />

has not been identified previously. T<strong>here</strong>fore, we carried out a<br />

controlled-environment chamber experiment at Tsukuba and a<br />

free-air CO 2 enrichment (FACE) experiment at Shizukuishi,<br />

Iwate, Japan, for a series of rice growth seasons, in order to<br />

understand the influence of elevated CO 2 on CH 4 emissions<br />

from rice paddies.<br />

Materials and methods<br />

Controlled-environment chamber experiment<br />

This research was conducted at the National <strong>Institute</strong> for Agro-<br />

Environmental Sciences (NIAES), Tsukuba, Japan. Six controlled-environment<br />

chambers (Climatron, Shimadzu, Kyoto)<br />

were used. The size of the chambers was 4 × 3 × 2 m (L × W ×<br />

H). CO 2 concentration was maintained at 350 µmol mol –1 in<br />

three chambers (ambient CO 2 ) or at 650 µmol mol –1 in three<br />

other chambers (elevated CO 2 ). During the day, the CO 2 concentration<br />

was maintained by a computer-controlled system<br />

by injecting pure CO 2 to compensate for CO 2 uptake by the<br />

rice plants (Oryza sativa, cultivar Nipponbare). During the<br />

night, CO 2 levels increased because of plant respiration, but<br />

were not allowed to increase to >100 µmol mol –1 higher than<br />

the daytime levels by means of a computer-controlled air ventilation<br />

system, which introduced ambient air when necessary<br />

to reduce the CO 2 concentration. In this experiment, air temperature<br />

inside all controlled-environment chambers was con-<br />

trolled to follow ambient air temperature. In the 1998 and 1999<br />

rice growth seasons, rice straw was applied to the soil at 300<br />

and 150 g m –2 , respectively. The CH 4 emitted from the chambers<br />

was determined by an automated monitoring system during<br />

all rice growth seasons.<br />

To understand how elevated CO 2 affects CH 4 emissions<br />

by plant-mediated transport or ebullition diffusion through<br />

flooding water, and how drainage affects CH 4 emissions in<br />

elevated CO 2 conditions, a pot experiment in the Climatron<br />

was carried out in the 2002 season. No rice straw was applied.<br />

The flooding water was maintained at a 5-cm depth until 2<br />

September (3 weeks before harvest); then, all pots were drained,<br />

and the water level was maintained at 5 cm below the soil<br />

surface. A cylinder and a doughnut chamber were used to measure<br />

CH 4 flux with and without plants.<br />

FACE experiment<br />

The FACE experiments with rice plants were conducted at<br />

Shizukuishi, Iwate, Japan. The soil was an Andosol paddy soil.<br />

A randomized complete block design with two levels of target<br />

atmospheric CO 2 concentration (ambient CO 2 and FACE =<br />

ambient + 200 µmol mol –1 ) and four replicate blocks was used.<br />

The rice (Oryza sativa) test cultivar was Akita Komachi. CH 4<br />

flux was determined with a cylindrical, transparent, acrylic,<br />

closed-top chamber. The samples were collected and measured<br />

once every 2 weeks. The total seasonal emissions from each<br />

plot for both the 1999 and 2000 seasons were calculated and<br />

analyzed statistically.<br />

Results and discussion<br />

In rice soils, acetate and H 2 -CO 2 are the major substrates for<br />

CH 4 production. The carbon sources for CH 4 production in<br />

rice soils are from soil carbon, applying organic material, rice<br />

root exudates, and root autolysis products. The seasonal CH 4<br />

emission rates increased by elevated CO 2 (+300 µmol mol –1 )<br />

in the controlled-environment chambers were 23% in 1998 and<br />

145% in the 1999 season with different rice straw application<br />

rates at 300 and 150 g m –2 , respectively, indicating that the<br />

effect of elevated CO 2 on CH 4 emissions was influenced by<br />

rice straw application. A large amount of rice straw applied<br />

before rice transplanting led to large CH 4 emissions during<br />

the early rice growth period, w<strong>here</strong>as t<strong>here</strong> was no difference<br />

between ambient and elevated CO 2 treatments. Elevated CO 2<br />

increased CH 4 emissions in rice paddies during middle-later<br />

rice growth periods because root exudates and root autolysis<br />

products under elevated CO 2 conditions increased the carbon<br />

source for CH 4 production in anaerobic soil. T<strong>here</strong>fore, the<br />

Session 19: Climate change and rice production 555


Tiller number<br />

and stem size<br />

+<br />

CH 4<br />

transport<br />

(by micropores)<br />

+<br />

+<br />

+<br />

O 2<br />

diffused to<br />

CO rhizosp<strong>here</strong><br />

2<br />

+ CH<br />

(by aerenchyma)<br />

4<br />

oxidation<br />

–<br />

CH 4<br />

emissions<br />

+<br />

+<br />

+<br />

Root biomass<br />

+<br />

Root<br />

exudation<br />

+<br />

CH 4<br />

production<br />

+ positive effect, –<br />

negative effect.<br />

The size of the arrows in the last steps indicated potential changes during all the rice growth period.<br />

Fig. 1. A conceptual model depicting how elevated CO 2 affected CH 4 emissions from rice<br />

paddies.<br />

effect of elevated CO 2 on increasing total CH 4 emissions in<br />

the 1999 rice growth season was much greater than that in<br />

1998 because of lesser amounts of rice straw applied in 1999<br />

(Yagi et al 2000).<br />

The results from a pot experiment under controlled-environment<br />

chambers during the 2002 rice growth season<br />

showed that the increase in CH 4 emissions caused by elevated<br />

CO 2 was significant after the grain-filling stage of rice; the<br />

total emissions were enhanced 58% by elevated CO 2 . The CH 4<br />

emitted by ebullition-diffusion accounted for 11.3% and 11.9%<br />

of total emissions under ambient and elevated CO 2 conditions,<br />

respectively. In contrast, no CH 4 was emitted from plant-free<br />

pots, suggesting that the CH 4 emitted from rice-plant pots was<br />

most contributed by the rice plant through root exudates and<br />

root autolysis products. The CH 4 flux decreased when the<br />

flooding water was drained under both ambient- and elevated-<br />

CO 2 treatments, implying that drainage management will have<br />

an important role in mitigating future CH 4 emissions from<br />

paddy fields, when more CH 4 will likely be emitted from<br />

flooded rice paddy soils under increasing atmospheric CO 2<br />

concentration (Cheng et al 2003).<br />

When free-air CO 2 was enriched to 550 µmol mol –1 , the<br />

CH 4 emissions from the rice paddy field increased significantly,<br />

by 38% in 1999 and 51% in the 2000 season. Net CH 4 emissions<br />

are determined by the balance between methane production<br />

and methane oxidation in the rice plant and paddy soil<br />

ecosystems. The CH 4 production potential in the FACE was<br />

significantly larger than that in the ambient-CO 2 treatments at<br />

the flowering stage in the middle rice growth period because<br />

elevated CO 2 increased CH 4 production by root exudates and<br />

root autolysis products. However, elevated CO 2 had no net<br />

effect on CH 4 oxidation activity during the same period. Also,<br />

the elevated CO 2 increased rice tiller numbers and CH 4 transport<br />

through the rice plant in FACE treatments (Inubushi et al<br />

2003).<br />

In conclusion, elevated CO 2 affects CH 4 emissions from<br />

rice paddies both by increasing the net balance between CH 4<br />

production and oxidation and by increasing the pass-way<br />

through the rice plant (Fig. 1). Several studies were made on<br />

the effect of elevated atmospheric CO 2 concentration on CH 4<br />

emissions from wetland and paddy soils (Table 1). CH 4 from<br />

rice paddies and natural wetlands accounts for 32.7% of the<br />

total global sources to the atmosp<strong>here</strong>. If we consider that CH 4<br />

emissions from natural wetlands and rice paddies would be<br />

enhanced by elevated CO 2 , the global warming potential of<br />

CH 4 could become more important as atmospheric CO 2 increases,<br />

as was recently predicted (Lelieveld et al 1998).<br />

References<br />

Cheng W, Yagi K, Sakai H, Kobayashi K. 2003. Effects of elevated<br />

CO 2 on CH 4 and N 2 O emissions from submerged rice soil: a<br />

pot experiment. 2003 ASA-CSSA-SSSA Annual Meetings, 2-<br />

6 November 2003, Denver, Colorado, USA. CD-ROM.<br />

Dacey JWH, Drake BG, Klug MJ. 1994. Stimulation of methane<br />

emission by carbon dioxide enrichment of marsh vegetation.<br />

Nature 370:47-49.<br />

Hutchin PR, Press MC, Lee JA, Ashenden TW. 1995. Elevated concentrations<br />

of CO 2 may double methane emissions from mires.<br />

Global Change Biol. 1:125-128.<br />

Inubushi K, Cheng W, Aonuma S, Hoque M, Kobayashi K, Miura S,<br />

Kim H, Okada M. 2003 Effects of free-air CO 2 enrichment<br />

(FACE) on CH 4 emissions from a rice paddy field. Global<br />

Change Biol. 9:1456-1464.<br />

IPCC. 2001. Climate change 2001: the scientific basis. Cambridge<br />

(UK): Cambridge University Press.<br />

Lelieveld J, Crutzen PJ, Dentener FJ. 1998. Changing concentration,<br />

lifetime and climate forcing of atmospheric methane.<br />

Tellus 50B:128-150.<br />

556 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. A review of the effects of elevated CO 2 on CH 4 emissions from wetland paddy soils.<br />

Study description CH 4 emissions Reference<br />

increasing (%)<br />

Wetlands<br />

Tidal marsh, open-top chambers 80 Dacey et al (1994)<br />

(690 ppm)<br />

Ombrotrophic mire, open-top chambers 145 Hutchin et al (1995)<br />

(550 ppm)<br />

O. aquaticum grew in wetland, glasshouse 136 Megonigal and Schlesinger (1997)<br />

(700 ppm)<br />

Paddy soils<br />

<strong>Rice</strong> (IR72), <strong>IRRI</strong> open-top chambers 49–60 Ziska et al (1998)<br />

(650 ppm)<br />

<strong>Rice</strong> (Nipponbare), Climatron (650 ppm) 23–145 This research (Yagi et al 2000)<br />

<strong>Rice</strong> (Akitakomachi), FACE (550 ppm) 38–51 This research (Inubushi et al 2003)<br />

<strong>Rice</strong> (Nipponbare), pot in Climatron 58 This research (Cheng et al 2003)<br />

(650 ppm)<br />

Megonigal JP, Schlesinger WH. 1997. Enhanced CH 4 emissions from<br />

a wetland soil exposed elevated CO 2 . Biogeochemistry 37:77-<br />

88.<br />

Yagi K, Li Z, Sakai H, Kobayashi K. 2000. Effect of elevated CO 2<br />

on methane emission from a Japanese rice paddy. FACE 2000<br />

Conference, 27-30 June 2000, Tsukuba, Japan. p 40.<br />

Ziska LH, Moya TB, Wassmann R, et al. 1998. Long-term growth at<br />

elevated carbon dioxide stimulates methane emission in tropical<br />

paddy rice. Global Change Biol. 4:657-665.<br />

Notes<br />

Authors’ addresses: Weiguo Cheng, Kazuyuki Yagi, and Hidemitsu<br />

Sakai, National <strong>Institute</strong> for Agro-Environmental Sciences,<br />

Tsukuba 305-8604, Japan; Kazuyuki Inubushi, Faculty of<br />

Horticulture, Chiba University, Matsudo, Chiba 271-8510,<br />

Japan; Kazuhiko Kobayashi, Graduate School of Agricultural<br />

and Life Sciences, the University of Tokyo, Tokyo 113-8657,<br />

Japan; Han-Yong Kim, Department of Agronomy, Chonnam<br />

National University, Gwangju 500-757, Korea; Masumi<br />

Okada, National Agricultural <strong>Research</strong> Center for Tohoku<br />

Region, Morioka 020-0198, Japan, e-mail:<br />

cheng@niaes.affrc.go.jp.<br />

The detrimental effect of tropospheric O 3<br />

on lowland rice is ameliorated by elevated CO 2<br />

T. Ishioh, K. Kobori, and K. Imai<br />

The atmospheric carbon dioxide (CO 2 ) concentration is increasing<br />

year by year because of human activities such as fossil<br />

fuel combustion and deforestation. The elevated levels of<br />

CO 2 promote photosynthesis of C 3 plants. For example, in lowland<br />

rice, photosynthesis and biomass production are promoted<br />

and plant development is accelerated by elevated CO 2 . More<br />

than a 20% yield increment of rice is often reported under<br />

doubled CO 2 conditions (Imai et al 1985, Kim et al 1996). On<br />

the other hand, atmospheric ozone (O 3 ), a major component<br />

of photochemical air pollutants, is often generated around urban<br />

areas during the sunny summer season in Japan. Ozone<br />

causes injury, with visible symptoms, growth inhibition, and<br />

yield decline in a range of field crops. From now on, under<br />

further industrialization and global warming, the frequency of<br />

occurrence of O 3 above the environmental quality standard<br />

(0.06 ppm in Japan) will increase and detrimentally affect crop<br />

plants. Thus, O 3 and CO 2 have opposite effects on production<br />

processes of crop plants. However, investigations on the interaction<br />

of these two gases in lowland rice are limited (Ishioh<br />

and Imai 2003, 2004, Kobori and Imai 2003, Olszyk and Wise<br />

1997).<br />

In our study, we exposed a japonica lowland rice cultivar<br />

to O 3 and CO 2 at the vegetative growth stage and at the<br />

heading to early-maturity stage and examined plant responses<br />

over short (3 h) and long (2 wk) terms to clarify the interaction<br />

of these two gases.<br />

Materials and methods<br />

A lowland rice cultivar (Oryza sativa L. cv. Koshihikari) was<br />

grown outdoors in small plastic pots containing 2.5 kg of soil<br />

and 4 g of compound chemical fertilizer (NPK=15:15:15, %)<br />

Session 19: Climate change and rice production 557


Experiment 1 (vegetative growth stage)<br />

In short-term<br />

1-0<br />

(3 h) (4 h)<br />

Experiment 1 (flowering to early-maturing stage)<br />

Flowering<br />

In long-term<br />

1-1<br />

1-2<br />

1-3<br />

1-4<br />

(1 wk) (1 wk) (1 wk)<br />

Outdoors<br />

Flowering to early maturing<br />

Early maturing<br />

(1 wk) (1 wk)<br />

Outdoors<br />

Fig. 1. Duration of treatments.<br />

: Gas exposure : O 3 -free air (CO 2 : 400 ppm)<br />

(experiment 1), or in large plastic pots containing 10 kg of soil<br />

and 8 g of chemical fertilizer (experiment 2).<br />

In experiment 1, at the vegetative growth stage (shortterm<br />

exposure, a half of the 7th leaf on main stem appeared;<br />

long-term exposure, a half of the 9th leaf on main stem appeared),<br />

nine plants (one plant per pot) were transferred into<br />

four naturally-lit phytotrons and were exposed to combinations<br />

of two levels of O 3 (0 ppm vs 0.1 ppm, 0630 to 1830)<br />

and two levels of CO 2 (400 ppm vs 800 ppm, 0000 to 2400)<br />

atmosp<strong>here</strong> (control plot, 0 ppm O 3 + 400 ppm CO 2 ; 0.1 ppm<br />

O 3 + 400 ppm CO 2 plot; 0.1 ppm O 3 + 800 ppm CO 2 plot; and<br />

0 ppm O 3 + 800 ppm CO 2 plot) for up to 3 h (short-term exposure)<br />

or 2 wk (long-term exposure) under 28/23 °C (day/night)<br />

and 60% relative humidity conditions (Fig. 1). The concentrations<br />

of O 3 and CO 2 , respectively, were assumed to be clean<br />

air or polluted air with O 3 and air of current or future doubled<br />

CO 2 . Gas exchange rates of fully expanded 6th leaves (shortterm<br />

exposure) or 8th leaves (long-term exposure) were examined<br />

for each of six plants with a portable measurement<br />

system (LI-6400, LI-COR, Inc.) at 0, 1, 2, 3, 4, 5, and 6 h<br />

(short-term exposure) and 0, 4, 11, 14, 18, and 21 d (longterm<br />

exposure) of treatment. Environmental conditions were<br />

CO 2 corresponding to treatment, 1,500 µmol m –2 s –1 PPFD,<br />

28 °C leaf temperature, and 1.5 kPa saturation deficit. After<br />

the treatments, plants were measured for their leaf areas and<br />

separated into leaf blade, leaf sheath + stem, and root fractions<br />

and oven-dried at 80 °C for 48 h and weighed. Based on<br />

the leaf area and dry weight values, growth parameters such as<br />

relative growth rate (RGR), net assimilation rate (NAR), leaf<br />

area ratio (LAR), leaf weight ratio (LWR), and specific leaf<br />

area (SLA) were calculated.<br />

In experiment 2, from flowering to early-maturity stage,<br />

plants were exposed to combinations of two levels of O 3 and<br />

two levels of CO 2 concentrations as described in experiment 1<br />

(Fig. 1). Gas exchange rates were measured at 0, 7, and 14 d<br />

of treatment. After the treatments, plants were transferred outdoors<br />

and cultivated ordinarily until full maturity. At maturity,<br />

plants were harvested and the dry weight of each organ, yield,<br />

and yield components were determined.<br />

Results<br />

At the vegetative growth stage (experiment 1), visible injury<br />

on the leaf surface appeared rapidly after the O 3 treatment<br />

(within 1–2 d) and leaf function such as gas exchange declined<br />

severely. In both the short- and long-term exposures, rapid<br />

declines in net photosynthetic rate and stomatal conductance<br />

occurred just after the O 3 treatment and these were not recovered<br />

when the plants were transferred into O 3 -free air (Fig. 2;<br />

experiment 1). T<strong>here</strong>fore, plant growth rate was suppressed<br />

and both leaf area and dry-matter production decreased in the<br />

0.1 ppm O 3 + 400 ppm CO 2 plot. Accordingly, the RGR decreased<br />

after the O 3 treatment because of decreased NAR. The<br />

LWR in the 0.1 ppm O 3 + 400 ppm CO 2 plot was higher than<br />

in the other plots in short- and long-term exposures and this<br />

indicated a decline in dry-matter partitioning to the root fraction.<br />

On the other hand, in a plot with 0.1 ppm O 3 + 800 ppm<br />

CO 2 , stomatal conductance decreased under doubling CO 2 and<br />

this could avoid injury to leaf function. Both net photosynthetic<br />

rate and growth rate were maintained as high as those of<br />

the control plot (0 ppm O 3 + 400 ppm CO 2 ).<br />

From flowering to early-maturity stage (experiment 2),<br />

the net photosynthetic rate was affected differently by the duration<br />

of treatments. A single exposure to O 3 decreased the net<br />

photosynthetic rate but the overall effect did not reflect on the<br />

whole-plant dry matter at maturity. The relevant factors might<br />

be the aging of the plant and/or meteorological conditions after<br />

the treatment, but a clear explanation was not obtained.<br />

However, once suffering O 3 fumigation, plants showed a tendency<br />

to have sterile and less fertile caryopses at the lower<br />

positions of the rachis branch of the panicle. This suggested<br />

that O 3 also suppressed the translocation of photoassimilate.<br />

Conclusions<br />

A high level of O 3 (0.1 ppm) inhibited photosynthesis, drymatter<br />

production, and yield of lowland rice. However, under<br />

elevated CO 2 (800 ppm), such effects of O 3 (0.1 ppm) were<br />

ameliorated. Especially in the exposure experiments at the<br />

558 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Net photosynthetic rate (mmol m –2 s –1 )<br />

40<br />

Exposure to O 3<br />

and/or CO 2<br />

O 3<br />

-free air<br />

35<br />

30<br />

25<br />

20<br />

15<br />

10<br />

5<br />

0<br />

Stomatal conductance (mmol m –2 s –1 )<br />

0.8<br />

0.7<br />

0.6<br />

0.5<br />

0.4<br />

0.3<br />

0.2<br />

0.1<br />

0<br />

0 4 7 11 14 18 21<br />

Days of treatment<br />

Fig. 2. Effects of O 3 and CO 2 concentrations on net photosynthetic rate and stomatal conductance<br />

at vegetative growth stage (experiment 1, long-term; 1-4).<br />

= 0 ppm O 3 + 400 ppm CO 2 plot, = 0.1 ppm O 3 + 400 ppm CO 2 plot,<br />

= 0.1 ppm O 3 + 800 ppm CO 2 plot, = 0 ppm O 3 + 800 ppm CO 2 plot.<br />

vegetative growth stage, the main reason could be a decline in<br />

stomatal conductance (in other words, stomatal closure) induced<br />

by elevated CO 2 , which suppressed the invasion of O 3<br />

inside the leaf cavity as a physical barrier. The O 3 effect on<br />

yield could be attributed to an increase in infertile caryopses<br />

at lower positions of the rachis branch of the panicle because<br />

of a decline in photoassimilate accumulation. Further investigations<br />

should be done for the light environment, plant age,<br />

and biochemical reactions in treatments to understand the interaction<br />

of O 3 and CO 2 in lowland rice.<br />

References<br />

Imai K, Coleman DF, Yanagisawa T. 1985. Increase in atmospheric<br />

partial pressure of carbon dioxide and growth and yield of<br />

rice (Oryza sativa L.). Jpn. J. Crop Sci. 54:413-418.<br />

Ishioh T, Imai K. 2003. Effects of atmospheric ozone and carbon<br />

dioxide concentrations on growth and yield of lowland rice.<br />

Jpn. J. Crop Sci. 72(Suppl. 2):286-287. (In Japanese.)<br />

Ishioh T, Imai K. 2004. Interaction between ozone and carbon dioxide<br />

on gas exchanges in leaves of lowland rice. Jpn. J. Crop<br />

Sci. 73(Suppl. 2):240-241. (In Japanese.)<br />

Session 19: Climate change and rice production 559


Kim HY, Horie T, Nakagawa H, Wada K. 1996. Effects of elevated<br />

CO 2 concentration and high temperature on growth and yield<br />

of rice. 2. The effect on yield and its components of Akihikari<br />

rice. Jpn. J. Crop Sci. 65:644-651. (In Japanese.)<br />

Kobori K, Imai K. 2003. Effects of atmospheric ozone and carbon<br />

dioxide concentrations on photosynthesis of lowland rice. Jpn.<br />

J. Crop Sci. 72(Suppl. 2):284-285. (In Japanese.)<br />

Olszyk DM, Wise K. 1997. Interactive effects of elevated CO 2 and<br />

O 3 on rice and flacca tomato. Agric. Ecosyst. Environ. 66:1-<br />

10.<br />

Notes<br />

Authors’ address: School of Agriculture, Meiji University, Kawasaki,<br />

Kanagawa 214-8571, Japan, e-mail: imai@isc.meiji.ac.jp.<br />

Effects of topdressing on grain shape and grain damage<br />

under high temperature during ripening of rice<br />

Satoshi Morita, Osamu Kusuda, Jun-ichi Yonemaru, Akira Fukushima, and Hiroshi Nakano<br />

High temperatures during the rice-ripening period significantly<br />

diminish grain dry weight and increase grain damage (Nagato<br />

and Ebata 1960, Yoshida and Hara 1977, Tashiro and Wardlaw<br />

1991, Morita et al 2004). It is thought that unusually high temperatures<br />

in recent years have caused a reduction in first-grade<br />

quality rice in Japan (Terashima et al 2001). The major factors<br />

in grade reduction were an increase in immature grains with a<br />

white portion, deep ditch on the grain surface, and thin shape.<br />

Recently, it has been suggested that these adverse effects of<br />

high temperature on rice ripening have been accelerated by<br />

the reduced topdressing during the panicle formation stage<br />

designed to improve edibility (Terashima et al 2001).<br />

The objective of this study was to demonstrate the effect<br />

of topdressing at the panicle-formation stage on grain dry<br />

weight and the occurrence of immature grains with a white<br />

portion, deep ditch, and thin shape under high temperature.<br />

Recently, immature grains with a white portion have been identified<br />

by grain quality inspectors during the inspection system.<br />

However, immature grains with a deep ditch and thin shape<br />

were not detected by machines. To enable a numerical comparison,<br />

we developed a new method of determining grain shape<br />

using digitized images.<br />

Materials and methods<br />

Experiments were performed in fields of the National Agricultural<br />

<strong>Research</strong> Center for Kyushu Okinawa Region at Chikugo<br />

(33°12′N, 130°30′E), Japan. The seedlings of rice (Oryza<br />

sativa L. cv. Hinohikari) growing 4 weeks after sowing were<br />

transplanted to paddy fields (gray lowland soil) on 18 June<br />

2003. Planting density was 20.8 hills m –2 (30 cm × 16 cm),<br />

with 3 seedlings per hill. An experiment was established in a<br />

randomized block design with three replications (11 m 2 per<br />

replication). A basal dressing of 6 g N m –2 (commercial NPK<br />

(16:16:16) fertilizer) was applied in all plots. Topdressing at<br />

18 and 8 d before heading (DBH) with ammonium sulfate was<br />

in six patterns: 3–3 (g N m –2 ), 3–1.5, 3–0, 1.5–1.5, 1.5–0, and<br />

0–0. The average temperature during the 20 d after heading<br />

was 27.7 ºC, which was 5–6 ºC higher than the optimum temperature.<br />

To determine yield, yield components, and grain quality,<br />

48 hills (2.3-m 2 area) from each replication were harvested<br />

at maturity (2 October). Yield and 1,000-grain weight were<br />

recorded as filled grain (with a thickness of 1.7 mm or more)<br />

weights of brown rice adjusted to 15% grain water content.<br />

Grain-filling percentages were calculated as 100 × filled grain/<br />

total spikelet number. Filled grains were graded by the inspection<br />

system, and grain quality was measured by a grain quality<br />

inspector (RGQI 10A, Satake, Japan). Nitrogen contents of<br />

filled grains were measured by the Japan Grain Inspection<br />

Association (Tokyo, Japan).<br />

For grain shape analysis, eight grains (3rd, 4th, 5th, and<br />

6th grains from the top on the 3rd and 4th rachis-branch in<br />

each panicle) of one panicle per plot were sampled. The<br />

samples were dehulled with a forceps and cut in half along the<br />

cross section. The grain images, viewing from the grain top or<br />

bottom, were digitized through a digital microscope at 50 magnifications.<br />

After transforming the digitized 24-bit full color<br />

images into binary ones, an image analysis was performed to<br />

measure grain contour with rθ polar barycentric coordinates (r<br />

indicates the distance, %, from the center point, half of X and<br />

Y radius, respectively, in the grain image, and θ denotes the<br />

angles of direction toward the vascular bundle). θ angles were<br />

within 0–180 degrees (i.e., numbers and areas of the cells at<br />

90 degrees were the averages of those at 270 degrees and 90<br />

degrees), since the top and bottom of a grain image showed no<br />

distinction from one another.<br />

Results and discussion<br />

Yield, yield components, and grain quality<br />

Grain yields were higher at higher levels of N topdressing because<br />

of higher grain numbers per unit area and higher 1,000-<br />

ripened-grain weights (Table 1). Grades of grain quality were<br />

higher, and the percentages of the immature grain number were<br />

lower, at higher N levels of topdressing, especially at 8 DBH<br />

(Table 1). T<strong>here</strong> were no significant differences between the<br />

560 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. Effects of topdressing at panicle formation stage on yield and grain quality.<br />

Treatments a Ripened b Grain no. Ripened 1,000- Grade of Sum of Milky Basal Grain N<br />

(g N m –2 ) grain yield per m 2 grain ripened-grain quality c immature white white content e<br />

(g m –2 ) (×100) (%) weight (g) (1–3) grains (%)<br />

3–3 620 304 90.0 22.7 1.7 39.4 8.4 6.2 1.24 *<br />

3–1.5 617 ns 306 ns 90.1 ns 22.5 ns 1.8 ns 42.6 ns 9.4 ns 9.4 ns 1.18 *<br />

3–0 593 ns 300 ns 89.4 ns 22.1 * 2.0 ns 46.7 * 10.0 ns 10.0 * 1.11 *<br />

1.5–1.5 578 ns 282 ns 91.7 ns 22.3 * 1.8 ns 44.5 * 7.8 ns 11.4 * 1.13 *<br />

1.5–0 561 * f 286 ns 90.7 ns 21.6 * 2.0 ns 51.5 * 8.2 ns 14.0 * 1.07 *<br />

0–0 544 * 281 ns 90.3 ns 21.5 * 2.3 * 53.5 * 8.8 ns 13.4 * 1.06 *<br />

a Topdressing at 18 and 8 days before heading with ammonium sulfate. b Grains with a thickness of 1.7 mm or more were regarded as ripened grains. c By inspection system. 1st<br />

high = 1, 1st low = 1.5, 2nd high = 2, 2nd low = 2.5, 3rd high = 3, 3rd low = 3.5. d Measured by RGQI 10A (Satake). e Measured by the Japan Grain Inspection Association.<br />

f *Indicates a significant difference from the 3–3 treatment at the 5% level by Dunnett’s multiple range test.<br />

Ratio between the distance from the center point to the contour<br />

of grain cross section of 3-3 treatment and that of other treatments<br />

1.02<br />

1.00<br />

3-3 treatment = 1<br />

0.98<br />

0.96<br />

3-3<br />

3-0<br />

1.5-0<br />

0.0<br />

0.94<br />

0 30 60 90 120 150 180<br />

Angle of direction toward vascular bundle (º)<br />

Fig. 1. Comparison between the grain contour of 3-3 treatment and that of other<br />

treatments. Standard errors of the ratios between the distance from the center<br />

point to the grain contour of the 3-3 treatment and that of other treatments<br />

ranged from 0.007 (1.5-0 treatment) to 0.016 (3-0 treatment), on average, from<br />

0 to 180º.<br />

percentages of milky white grains of the 3–3 treatment and<br />

those of other treatments. However, the percentages of basal<br />

white grains of the 3–3 treatment were significantly lower than<br />

those of other treatments, except for the 3–1.5 treatment. These<br />

results coincide with the report that immature grains with a<br />

white portion increased at a higher grain number per unit area<br />

(Terashima et al 2001, Kobata et al 2004) and at a lower N<br />

level (Terashima et al 2001) under high temperature at ripening.<br />

In this study, it was clear that the reactions to the increase<br />

in the nitrogen application change with the type of immature<br />

grain (i.e., milky white or basal white) under high temperature.<br />

But, the reason for this has been unclear. Further research<br />

into the physiological and morphological factors of white portions<br />

in the endosperm will be required.<br />

Grain shape<br />

Image analysis of grain projection from the grain top or bottom<br />

revealed that lower N levels in the reproductive stage under<br />

high temperature caused inferior grain growth, especially<br />

at 30 to 50 degree angles from the vascular bundle direction<br />

from the center point of the cross section (Fig. 1), w<strong>here</strong> the<br />

photoassimilates were thought to be accumulated at a later stage<br />

of ripening. These areas of angles contain a deep ditch made<br />

from the joint line of the lemma and palea.<br />

Image analysis of the longitudinal projection from the<br />

grain lateral side also revealed that lower N levels caused inferior<br />

growth at ventral shoulder parts (from –120 to –150<br />

degrees) and at the dorsal bottom square parts (from 30 to 60<br />

degrees) of grains (Fig. 1). The latter parts corresponded to<br />

the parts of the white portion in the basal white grain.<br />

Akiyama et al (1997) have classified rice cultivars by<br />

image analysis of the size of white cores in the grain. However,<br />

image analysis of rice grain shape had not been previously<br />

reported. In this study, the inferior growth position in<br />

the grains, revealed by image analysis of grain shape, may indicate<br />

the time and/or position in which a lower nitrogen application<br />

under high temperature has an immediate adverse<br />

effect. This suggests that image analysis of grain shape will be<br />

Session 19: Climate change and rice production 561


of value in understanding the adverse effect of high temperature<br />

and in improving rice ripening under such an environment.<br />

References<br />

Akiyama Y, Yamada H, Takahara Y, Yamamoto K. 1997. Classification<br />

of rice cultivars for sake brewery based on white-core<br />

characters. Breed. Sci. 47:267-270.<br />

Kobata T, Uemuki N, Inamura T, Kagata H. 2004. Shortage of assimilate<br />

supply to grain increases the proportion of milky white<br />

rice kernels under high temperatures. Jpn. J. Crop Sci. 73:315-<br />

322. (In Japanese with English summary.)<br />

Morita S, Shiratsuchi H, Takanashi J, Fujita K. 2004. Effect of high<br />

temperature on ripening in rice plant: analysis of the effects<br />

of high night and high day temperatures applied to the panicle<br />

and other parts of the plant. Jpn. J. Crop Sci. 73:77-83. (In<br />

Japanese with English summary.)<br />

Nagato K, Ebata M. 1960. Effects of temperature in the ripening<br />

periods upon the development and qualities of lowland rice<br />

kernels. Proc. Crop Sci. Soc. Jpn. 28:275-278. (In Japanese<br />

with English summary.)<br />

Tashiro T, Wardlaw IF. 1991. The effect of high temperature on kernel<br />

dimensions and the type of occurrence of kernel damage<br />

in rice (Oryza sativa L.). Aust. J. Agric. Res. 42:485-496.<br />

Terashima K, Saito Y, Sakai N, Watanabe T, Ogata T, Akita S. 2001.<br />

Effects of high air temperature in summer of 1999 on ripening<br />

and grain quality of rice. Jpn. J. Crop Sci. 70:449-458. (In<br />

Japanese with English summary.)<br />

Yoshida S, Hara T. 1977. Influence of air temperature and light on<br />

grain filling of an indica and japonica rice (Oryza sativa L.)<br />

in a controlled environment. Soil Sci. Plant Nutr. 23:93-107.<br />

Notes<br />

Authors’ addresses: Satoshi Morita, Akira Fukushima, and Hiroshi<br />

Nakano, NARO, National Agricultural <strong>Research</strong> Center for<br />

Kyushu Okinawa Region, Fukuoka 833-0041, Japan; Osamu<br />

Kusuda, NARO, National <strong>Institute</strong> of Vegetable and Tea Science,<br />

Mie 514-2392, Japan; Jun-ichi Yonemaru, NARO, National<br />

Agricultural <strong>Research</strong> Center for Tohoku Region,<br />

Morioka 020-0198, Japan, e-mail: moritas@affrc.go.jp,<br />

kusuda@affrc.go.jp, yonemaru@affrc.go.jp,<br />

afuku@affrc.go.jp, nakanohr@affrc.go.jp.<br />

Wrap-up of Session 19<br />

The conclusions of the Third Assessment Report (TAR) of the<br />

Intergovernmental Panel on Climate Change (IPCC) leave no doubt<br />

that Earth’s climate is changing in a manner unprecedented in<br />

the past 400,000 years. The report forecasts that by 2100 mean<br />

planet-wide surface temperatures will rise by 1.4 to 5.8 °C, precipitation<br />

will decrease in the subtropics, and extreme events will<br />

become more frequent. However, changes in climate are already<br />

being observed—the last 60 years were the warmest in the last<br />

1,000 years and changes in precipitation patterns have brought<br />

greater incidence of floods or drought globally. The TAR also concluded<br />

that natural phenomena do not explain these observed<br />

changes—that t<strong>here</strong> is now clear evidence of human influence.<br />

Climate change is a development problem as well as an<br />

environmental problem. It is a development problem because<br />

those engaged in agriculture must learn how to adapt to the<br />

consequences of an altered atmosp<strong>here</strong>, higher temperatures,<br />

and greater variability and more extremes in weather. Coping simultaneously<br />

with the other adverse environmental consequences<br />

of anthropogenic activity, such as air quality, will be no easy matter.<br />

The combination of changes in air quality and composition,<br />

acid rain, and climate will produce a new bioclimate for food<br />

production systems. The potentially beneficial effects of increases<br />

in CO 2 may be offset by the increases in ozone at ground level<br />

(tropospheric concentrations) as well as high-temperature stress.<br />

It is arguable that most developing countries are not well informed<br />

about the probable impact of bioclimatic change and are t<strong>here</strong>fore<br />

most vulnerable to its consequences.<br />

To understand the quantitative effects of climate change<br />

on rice production, it is necessary to have rice simulation models<br />

that can predict the outcome of the new bioclimates on rice. The<br />

models have to have parameters measured in “controlled environments.”<br />

The first paper of the session by T. Horie and H. Yoshida<br />

described the development of such a model, with particular reference<br />

to high-temperature stress and its use to predict future<br />

yields in China, Thailand, and Japan.<br />

One curious consequence of climate change is that in some<br />

regions temperatures could get cooler because of changes in<br />

currents and atmospheric pressure differentials. The second paper<br />

of the session by M. Yajima focused on the effects of cool<br />

weather in northern Japan on spikelet sterility and methods of<br />

protecting rice against cold damage.<br />

Coping with the effects on rice of weather variability associated<br />

with climate change in the form of increased frequency of<br />

wet and dry periods, tropical cyclones, and typhoons in the Philippines<br />

was the topic of the third paper by F. Lansigan.<br />

Climate change will have direct effects on rice but may<br />

also alter soil nutrient availability for rice. The fourth paper by J.<br />

Zhu described how free-air CO 2 enrichments can affect plant<br />

nutrients in the soil solution.<br />

<strong>Rice</strong> ecosystems will be affected by climate change, but<br />

t<strong>here</strong> has also been great concern about the contribution of rice<br />

to climate change. Understanding the properties of rice soils in<br />

relation to methane emissions is crucial to efforts to minimize<br />

those emissions and this topic was explored by S. Mitra and D.<br />

Majumdar.<br />

Professor Li and his colleagues investigated the alternatives<br />

for farmers in managing their crops so as to reduce methane<br />

emissions. They developed a tool by integrating a processbased<br />

model with a GIS database to scale up their experimental<br />

observations from the field to a regional level. They investigated<br />

562 <strong>Rice</strong> is life: scientific perspectives for the 21st century


the effects of mid-season drainage in different cropping seasons<br />

and on different soils. Their results highlighted the benefits of<br />

their management systems in reducing emissions of methane,<br />

but revealed the associated problem of stimulating the emission<br />

of nitrous oxide.<br />

Climate change studies need to cover a range of issues at<br />

widely different time and space scales. Many uncertainties still<br />

exist in our predictions of future climates, rice production, and<br />

impacts of rice cultivation on the environment at each scale. To<br />

reduce uncertainties and to develop mitigation and adaptation<br />

strategies, three key components should work together: robust<br />

modeling, large-scale databasing, and continuous experimentation.<br />

The great challenge is to achieve a balance between rice<br />

cultivation and environmental conservation as addressed by T.<br />

Horie and K. Minami in the general discussion.<br />

Session 19: Climate change and rice production 563


SESSION 20<br />

Improving rice productivity through IT<br />

CONVENER: S. Ninomiya (NARO)<br />

CO-CONVENER: M. Bell (<strong>IRRI</strong>)


Data mining using combined yield<br />

and quality maps of paddy fields<br />

Tadashi Chosa<br />

<strong>Research</strong> on precision agriculture has been attracting attention<br />

with regard to the production of rice in Japan (Umeda<br />

1999) and other Asian countries (Sung et al 2002). It is thought<br />

that precision farming could solve the problem of variability<br />

within and between fields, leading to economic and environmental<br />

benefits, as well as stable production. The methods of<br />

precision agriculture are based on information technology. In<br />

precision farming, farmers make optimal decisions depending<br />

on site-specific information, such as on fertility, growth, and<br />

yield.<br />

In recent times, progress has been made in developing<br />

information acquisition technology (Shibata et al 2002, Chosa<br />

et al 2004); progress has also been made with respect to applications<br />

for site-specific management (Chosa et al 2003). However,<br />

it is difficult to make recommendations for management<br />

or applications based on the information acquired. Although<br />

some successful case studies have been reported (Toriyama et<br />

al 2003), no general method for producing recommendations<br />

has been determined.<br />

Theoretically, if the fertility and variations in fertility of<br />

an area can be determined, the added nitrogen required to reach<br />

a targeted nitrogen absorption level, or to decrease variability,<br />

can be calculated. Similarly, if the absorption of nitrogen is<br />

determined through yield, a revised amount of nitrogen can be<br />

calculated for application the following year. However, nitrogen<br />

absorption is not the same in each area, for each year,<br />

because of differences in soil conditions, climate, fertilizer<br />

application method, and type of cultivation. For this and other<br />

reasons, it is difficult to generalize the formulation of a recommendation.<br />

This paper presents guidelines for making recommendations<br />

for the next year’s crop using yield and grain quality<br />

maps of paddy fields. The information provided by mining the<br />

data in these maps should be more useful than the information<br />

provided by the individual maps. Combining the two types of<br />

maps for the purpose of site-specific management can reveal<br />

useful information.<br />

Yield and quality acquisition systems<br />

To acquire yield information, a hybrid yield-monitoring method<br />

(Chosa et al 2004a) was used. This method uses a sequencemonitoring<br />

sensor simultaneously with a batch-monitoring sensor.<br />

The sequence yield monitor, which is used to measure the<br />

grain flow rate, consists of an emitting unit and a receiving<br />

unit fixed to the top of the clean grain auger of the combine<br />

harvester. The output signal is an analog signal that varies according<br />

to the particle flow between the emitting and receiving<br />

units. A batch yield monitor is used to measure the mass of<br />

grain inside the combine tank. This monitor is a load cell unit<br />

that is fixed under the grain tank of the harvester and responds<br />

to particles filling the tank. The output signal of this sensor is<br />

also analog. As position information is acquired by GPS at the<br />

same time as yield information, the yield map is drawn after<br />

the harvest.<br />

A gathering unit for analysis of the quality of samples<br />

(Chosa et al 2004b) that can be attached to a combine harvester<br />

was used to acquire quality information. This system<br />

consists of a leading tube in the form of a cylinder, receiving<br />

cups that gather the grain from the leading tube, and a turning<br />

table that supplies the receiving cups. The leading tube is inserted<br />

into the combine tank at an angle and leads the grain<br />

sample from inside the combine tank to the outside. As the end<br />

of the tube inside the tank is cut obliquely, the angle of the<br />

tube controls the sampling weight and can be used to stop the<br />

sampling. When the sampling is stopped, normal operations<br />

can be conducted. Grain dropped through the leading tube is<br />

gat<strong>here</strong>d in sampling cups that are supplied by the turning table.<br />

Grain samples corresponding to random harvest positions can<br />

be collected through appropriate operation of the turning table.<br />

After the harvest, the quality parameters of the samples collected<br />

can be analyzed, such as the moisture content, protein<br />

content, and outward quality. Since position information is<br />

acquired through the GPS at the time of sampling, the quality<br />

map is drawn after the analysis.<br />

Farm work for data acquisition<br />

To examine variability in yield and quality, a field survey was<br />

conducted during combine harvesting.<br />

The combine harvester used was a modified commercial<br />

four-row operating combine harvester (head-feeding type,<br />

25.7 kW, harvesting width 1.2 m). The combine was equipped<br />

with the yield and quality acquisition systems described above.<br />

Commercial combine harvesters can easily be equipped with<br />

both systems. Although the person who runs the combine must<br />

operate the information acquisition systems, the harvesting operation<br />

is otherwise the same as is usual for this farm work.<br />

After the harvest and analysis of the yield, quality, and<br />

position information, the yield map and quality map were generated.<br />

Protein content was used as a measure of rice quality.<br />

The protein content of each sample was measured using nearinfrared<br />

light.<br />

The yield and quality variability maps were overlapped<br />

to determine a recommendation for cropping and fertilizing<br />

strategies for the next year.<br />

566 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Table 1. Field categories on the basis of yield and protein content.<br />

Category Yield Protein Analysis and prescription<br />

1 High Low Proper management was conducted.<br />

The same management<br />

is recommended for the next<br />

year.<br />

2 Low Low If the priority is yield, more nitrogen<br />

is required.<br />

3 High High If the priority is quality, less nitrogen<br />

is required.<br />

4 Low High This problem cannot be controlled<br />

by fertilizing. Other causes such<br />

as soil structure, disease, and<br />

insects should be discussed.<br />

Results and discussion<br />

Variations in yield and quality were observed. The cropping<br />

and fertilizing strategies for the next year, determined by these<br />

maps, indicate that areas with lower yields will require more<br />

nitrogen, and areas that produce rice with excessive protein<br />

content will require less nitrogen. However, the situation with<br />

nitrogen absorption is further complicated because of differences<br />

in soil conditions, climate, fertilizer application, and type<br />

of cultivation. Occasionally, contradictions arise; for example,<br />

areas that produce rice with low protein content sometimes<br />

have high yield. Basing the fertilizing strategy on calculation<br />

of the nitrogen absorption may not result in an optimal recommendation.<br />

T<strong>here</strong>fore, another data-mining method for determining<br />

fertilizing strategies that use yield and quality maps is<br />

proposed <strong>here</strong>.<br />

Initially, each area is divided into two categories, based<br />

on the yield map: the high-yield area and low-yield area. Next,<br />

each area is also divided into two categories based on the quality<br />

map of the same time period, the low-protein-content area and<br />

high-protein-content area. Finally, each part of the field is classified<br />

into four categories by combining all of the above categories:<br />

category 1 has high yield and low protein content,<br />

category 2 has low yield and low protein content, category 3<br />

has high yield and high protein content, and category 4 has<br />

low yield and high protein content (Table 1). Ideally, every<br />

area should be managed to have the qualities of category 1.<br />

Some of the categories may require the same cropping and<br />

fertilizing strategies in the subsequent year. If the priority is<br />

yield, the category 2 areas require more nitrogen. If the priority<br />

is quality, the category 3 areas require less nitrogen. It is<br />

natural to assume that other problems that cannot be controlled<br />

by fertilizing, such as soil structure, disease, and insects, occur<br />

in category 4 areas. T<strong>here</strong>fore, more surveys may be required<br />

for category 4 areas to determine an appropriate recommendation.<br />

Figure 1 shows a category map based on yield<br />

and quality maps. Maps of this type will constitute useful tools<br />

for determining recommendations for cropping and fertilizing<br />

strategies for the following year. A further refinement to the<br />

method would be to incorporate logical thresholds, and actual<br />

proof with respect to the recommendations would also be informative.<br />

(m)<br />

30<br />

20<br />

10<br />

0<br />

0 10 20 30 40 50 60 70 80 90 100<br />

(m)<br />

Conclusions<br />

This study has presented guidelines for making recommendations<br />

for site-specific crop management. Information on yield<br />

and quality can be obtained using this newly developed system.<br />

A new data-mining method for determining fertilizing strategies<br />

using yield and quality maps has been presented <strong>here</strong>.<br />

The category maps resulting from this method suggest qualitative<br />

strategies for the crop of the following year.<br />

References<br />

Chosa T, Shibata Y, Omine M, Kobayashi K, Toriyama K, Sasaki R.<br />

2003. Map-based variable control system for granule applicator.<br />

J. Jpn. Soc. Agric. Machine. 65(3):128-135.<br />

Chosa T, Shibata Y, Omine M, Toriyama K, Araki K. 2004a. A study<br />

on a yield monitoring system for head-feeding combines. J.<br />

Jpn. Soc. Agric. Machine. 66(2):137-144.<br />

Chosa T, Shibata Y, Omine M, Nozaki I, Sekiguchi M, Hosokawa H.<br />

2004b. Development of a gathering unit for quality analyzing<br />

sample to be put on a combine harvester. Proceedings of the<br />

40th Annual Meeting of JSAM Kanto branch. p 42-43.<br />

Shibata Y, Sasaki R, Toriyama K, Araki K, Asano O, Hirokawa M.<br />

2002. Development of image mapping techniques for site-specific<br />

paddy rice management. J. Jpn. Soc. Agric. Machine.<br />

64(1):127-135.<br />

Sung J, Lee C, Park W, Jung I, Kim S. 2002. The spatial variability<br />

of yield, growth status, soil properties, elevation and quality<br />

in Korean rice. ASAE paper: 023085.<br />

Toriyama K, Sasaki R, Shibata Y, Sugimoto M, Chosa T, Omine M,<br />

Saito J. 2003. Development of a site-specific nitrogen management<br />

system for paddy rice. Jpn. Agric. Res. Q. 37(4):231-<br />

218.<br />

Umeda M. 1999. Precision Agriculture Project in Kyoto University.<br />

J. Jpn. Soc. Agric. Machine. 61(4):4-11.<br />

Notes<br />

Catergory 1: high yield and low protein content<br />

Catergory 2: low yield and low protein content<br />

Catergory 3: high yield and high protein content<br />

Catergory 4: low yield and high protein content<br />

Fig. 1. Category map based on yield and quality.<br />

Author’s address: NARC, Hokuriku, 1-2-1 Inada, Joetsu, Niigata<br />

943-0193, Japan, tchosa@affrc.go.jp.<br />

Session 20: Improving rice productivity through IT 567


A wireless sensor network with Field-Monitoring Servers<br />

and MetBroker in paddy fields<br />

Masayuki Hirafuji, Tokihiro Fukatsu, Hu Haoming, Takuji Kiura, Tominari Watanabe, and Seishi Ninomiya<br />

Environmental data such as weather data and crop data such<br />

as rice growth in paddy fields are necessary for crop management<br />

and scientific studies. In addition, production history<br />

systems and traceability systems for food security are becoming<br />

indispensable. A wireless sensor network could be one of<br />

the best solutions for this need.<br />

So far, many kinds of sensor-network solutions, such as<br />

Mote (Khan et al 1999) and TINI (www.ibutton.com/TINI/),<br />

have been proposed. However, specification of the sensors is<br />

poor for monitoring crops. Wireless broadband communication,<br />

high-resolution image-monitoring technology, and various<br />

sensors are needed for monitoring rice in real-time in paddy<br />

fields. For example, a rice blast prediction system,<br />

MetBLASTAM (http://cse.naro.affrc.go.jp/ketanaka/model/<br />

applet/Blastam.html), requires information on air temperature,<br />

humidity, and leaf wetness. Specific data such as images of<br />

emerging rice blast are indispensable to revise the prediction<br />

system. To estimate the photosynthetic rate of rice, the spatial<br />

distribution of CO 2 concentration should be measured in realtime<br />

in the paddy field.<br />

We developed Field-Monitoring Servers for those requirements,<br />

and constructed a wireless sensor network in paddy<br />

fields. Their cost is extremely low and their functions are much<br />

advanced compared with conventional sensor networks or<br />

weather stations. The observed data are freely available on<br />

our Web site. Any users can use the data directory, and applications<br />

such as the rice blast prediction system, through<br />

MetBroker, which provides data in standard format for applications<br />

by linking these applications to conventional weather<br />

databases such as AMeDAS and NOAA.<br />

The Field-Monitoring Server<br />

A field server is a Web server installed in fields, and the Field-<br />

Monitoring Server (FMS) is a kind of field server for realtime<br />

monitoring. The FMS can monitor fields in real-time and<br />

use wireless local area network (LAN) hotspots around the<br />

FMS (Hirafuji 2000). The FMS consists of a field server engine<br />

(micro Web server for control and data acquisition), a<br />

wireless LAN access-point, a network camera, and sensors<br />

(Hirafuji and Fukatsu 2002, Fukatsu and Hirafuji 2003).<br />

The field server engine is a main panel that functions<br />

like a Web server, analog I/O, digital I/O, DDS (Direct Digital<br />

Synthesizer), FPAA (Field Programmable Analog Array), and<br />

analog multipliers. The DDS generates an alternative signal<br />

up to 70 MHz. The FPAA serves to construct dynamic analog<br />

circuits, such as a low-pass filter and super-heterodyne radio<br />

receiver, using its embedded 20 CAB (Configurable Analog<br />

Block) and analog multipliers. By combining these elements,<br />

the FMS can be connected to various sensors and probes directly.<br />

A typical specification of FMSs follows:<br />

1. Casing: heat-resistant, waterproof, dustproof, and suitable<br />

to the landscape.<br />

2. Sensors: air temperature, humidity, PPFD (photosynthesis<br />

photon flux density), soil temperature, soil<br />

moisture, CO 2 concentration, leaf wetness, ultraviolet<br />

light, infrared light, etc.<br />

3. Image data: 0.3–8 M pixels depending on cameras.<br />

4. Wireless communication range: 300 m–10 km depending<br />

on external antennas.<br />

5. Hotspot service: within 100 m–1.5 km depending on<br />

antennas and circumstances.<br />

6. Communication speed: 54/11 Mbps.<br />

7. Power supply: AC adapter, embedded solar cell, or<br />

external solar cells.<br />

8. Size: diameter is 20 cm and length is about 30 cm.<br />

9. Cost: less than $500 to $2,000 per unit depending on<br />

embedded devices.<br />

The full-wireless Field-Monitoring Server for paddy fields<br />

Conventional FMSs require cables for the power supply, since<br />

power from the solar cell embedded on the rooftop of the FMSs<br />

is too low (0.5 W) to drive an FMS continuously, as it requires<br />

more than 50 W for nights and the rainy season. The hardest<br />

job for the installation of FMSs was the construction of wiring.<br />

This will be much harder in paddy fields. So, the fullwireless<br />

FMS was developed, especially for paddy fields with<br />

several energy-saving technologies (Hirafuji et al 2004). Client<br />

connection FMSs can rest periodically to save power. The<br />

full-wireless FMSs connect other conventional standard FMSs<br />

as clients at hotspots provided by the standard FMSs, which<br />

are driven by an AC adapter or larger solar cells and consume<br />

more energy to maintain the backbone and the hotspot service.<br />

Fieldserver-Agents and MetBroker<br />

Field servers can be controlled by users using a Web browser,<br />

also simultaneously controlled by a Fieldserver-Agent, which<br />

is a kind of artificial intelligence (Fukatsu and Hirafuji 2004).<br />

The collected data are stored in public database servers such<br />

as a PC-cluster at NARC or a computer center. A Fieldserver-<br />

Agent controls almost all FMSs in the world and collects data<br />

automatically, such as the Google Web crawler. The agent is<br />

accessing FMSs every 1–10 min. Farmers and consumers can<br />

568 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Fig. 1. Field Monitoring Servers in the paddy field.<br />

view the data. The sorted images are shown as time-lapse<br />

movies to monitor plant growth and farms. This function can<br />

be a production history system and a farm security system.<br />

Applications can use the data by using MetBroker<br />

(Laurenson et al 2002), which has transformed conventional<br />

weather databases and data of FMSs into standardized data<br />

automatically. MetBroker is also a network service. Applications<br />

determined to be used by MetBroker can access an enormous<br />

amount of data through MetBroker. If a new FMS is<br />

installed in a field, the measured data instantly become available<br />

applications.<br />

Experiments<br />

We installed five FMSs; three FMSs are in a paddy field and<br />

one FMS is on a rooftop at NARC’s Yawara experiment station<br />

in Yawara village. The first FMS (FMS-1) on the rooftop<br />

is connected to the Internet by the Asymmetric Digital Subscriber<br />

Line (ADSL), since the Yawara station is not connected<br />

to the optical fiber network of MAFFIN (the Ministry of Agriculture,<br />

Forestry, and Fisheries Network). The second FMS<br />

(FMS-2) is connected to FMS-1 by a repeating mode of wireless<br />

AP (a kind of ad hoc network), and the third FMS (FMS-<br />

3) is also connected to the FMS-2 by repeating. The fourth<br />

FMS (FMS-4) and fifth FMS (FMS-5) are connected by an<br />

AP-Client mode as a client around FMS-2, which provides a<br />

hotspot service. FMS-4 and FMS-5 were installed in the paddy<br />

field (Fig. 1). The power for FMS-4 was supplied by a cable,<br />

which was hard to use in a such a dirty field. So, we employed<br />

a full-wireless FMS for the fifth FMS. Power for the FMS-5<br />

was supplied by an embedded small solar cell. Sensors for the<br />

FMSs are<br />

FMS-1: air temperature, humidity, intensity of solar radiation<br />

(power of solar cell), and inside temperature.<br />

FMS-2: air temperature (2 types), humidity, intensity of<br />

solar radiation, inside temperature, and CCD<br />

camera (0.3 Megapixels).<br />

FMS-3: air temperature, CO 2 concentration, leaf wetness,<br />

intensity of UV, and inside temperature.<br />

FMS-4: air temperature, PPFD (2 layers), and inside temperature.<br />

FMS-5: air temperature, humidity, recharging current (intensity<br />

of solar radiation), battery voltage, and<br />

inside temperature.<br />

In addition, we tested a 3-Megapixel high-resolution<br />

digital camera with a magnifying lens to FMS-2. We could<br />

observe the surface of a rice leaf; the resolution is up to about<br />

10 micrometers (Fig. 2). This microscope camera can be installed<br />

in the paddy field and also controlled by the Fieldserver-<br />

Agent. In total, 23 sensors and two cameras were installed in<br />

the paddy field. All of the measured data were collected by the<br />

Fieldserver-Agent automatically.<br />

We isolated the FMSs from the global IP network using<br />

VPN for security using FieldServerGateway (Kiura et al 2002).<br />

However, real-time data and collected data are always available<br />

on the Field Server Web site (http://model.job.affrc.go.jp/<br />

FieldServer/monitor/).<br />

Results and discussion<br />

We needed four visits to the Yawara station for installation of<br />

the five FMSs and ADSL router. That is troublesome for farmers<br />

and researchers, so we improved the FMSs and now we<br />

can finish such installation within a half day. The function of<br />

the hotspot and ad hoc network could be connected among the<br />

FMSs successfully, and FMSs now provide a ubiquitous network<br />

service at the station. The CO 2 concentration in the paddy<br />

field can be measured continuously and the relationship with<br />

other monitored data such as UV light is clear.<br />

Session 20: Improving rice productivity through IT 569


Fig. 2. Surface of a rice leaf: live high-resolution image recorded by the Field-<br />

Monitoring Servers with other environmental data in the paddy field.<br />

So far, the FMSs were installed in both the paddy field<br />

and at many experimental sites in several countries such as<br />

Japan, the United States, Thailand, Denmark, China, Korea,<br />

Canada, and Taiwan (China). The FMSs in paddy fields became<br />

extremely dirty after one year, and the sensors were damaged.<br />

So, we are improving the FMSs; for example, an air filter<br />

was appended to the air intake.<br />

Conclusions<br />

A wireless sensor network is constructed in paddy fields using<br />

FMSs. We can access the Internet in the area ubiquitously by a<br />

Wi-Fi wireless-LAN. The sensor network has collected data<br />

in real-time since July 2003. The collected data were used to<br />

develop new sensors such as a leaf-wetness sensor. Relationships<br />

hidden in enormous amounts of measured data and<br />

weather databases can be found by MetBroker and data mining.<br />

So far, we lack detailed data in paddy fields w<strong>here</strong> we<br />

could not install measurement equipment, and only some data<br />

and numerical estimations have been employed. At present,<br />

we can now collect an enormous amount of data automatically<br />

and monitor them in real-time by live cameras with the FMSs.<br />

Any people, such as researchers and consumers, can inspect<br />

paddy fields anytime at any place using the collected data.<br />

This can make rice production more scientific, more reliable,<br />

and safer.<br />

References<br />

Fukatsu T, Hirafuji M. 2003. Development of Field Servers for a<br />

field monitoring system. Agric. Info. Res. 12:1-12.<br />

Fukastu T, Hirafuji M. 2004. The agent system for Field Monitoring<br />

Servers to construct smart sensor-network. Fifth <strong>International</strong><br />

Workshop on Artificial Intelligence in Agriculture, 8-10 March<br />

2004.<br />

Hirafuji M. 2000. Creating comfortable, amazing, exciting and diverse<br />

lives with CYFARS (CYber FARmerS), an agricultural<br />

virtual corporation. Proceedings of the Second Asian Conference<br />

for Information Technology in Agriculture. p 424-431.<br />

Hirafuji M, Fukatsu T. 2002. Architecture of Field Monitoring Servers.<br />

Proceedings of the Third Asian Conference for Information<br />

Technology in Agriculture. p 405-409.<br />

Hirafuji M, Fukatsu T, Hu Haoming. 2004. Full-wireless Field Monitoring<br />

Server for advanced sensor network. Proceedings of<br />

AFITA/WCCA, 2004. p 686-691.<br />

Kahn JM, Katz RH, Pister KSJ. 1999. Mobile networking for smart<br />

dust. ACM/IEEE <strong>International</strong> Conference on Mobile Computing<br />

and Networking (MobiCom 99), Seattle, Wash., USA.<br />

Kiura T, Fukatsu T, Hirafuji M. 2002. Field server gateway: gateway<br />

box for Field Monitoring Servers. Proceedings of the Third<br />

Asian Conference for Information Technology in Agriculture.<br />

p 410-413.<br />

Laurenson M, Kiura T, Ninomiya S. 2002. Providing agricultural<br />

models with mediated access to heterogeneous weather databases.<br />

Appl. Engin. Agric. 18:617-625.<br />

Notes<br />

Authors’ addresses: National Agricultural <strong>Research</strong> Center, e-mail:<br />

hirafuji@affrc.go.jp, fukatsu@affrc.go.jp, hhaoming@<br />

affrc.go.jp, kiura@affrc.go.jp, tomonari.watanabe@<br />

affrc.go.jp, snino@affrc.go.jp.<br />

570 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Prediction of airborne immigration of rice insect pests<br />

Akira Otuka, Tomonari Watanabe, Yoshito Suzuki, Masaya Matsumura, Akiko Furuno, and Masamichi Chino<br />

The whitebacked planthopper Sogatella furcifera and the<br />

brown planthopper Nilaparvata lugens are major pests of rice<br />

in eastern Asia. They migrate from southern China into Japan<br />

mainly in the Bai-u rainy season in June to July every year<br />

(Seino et al 1987). Generally, the prediction of planthopper<br />

migration provides farmers and plant protection advisers with<br />

information about the migration source as well as area of migration.<br />

It is especially important to know the migration source,<br />

which helps to understand the immigrant’s characteristics such<br />

as biotype, pesticide resistance, etc. Conventional prediction<br />

methods used 6- or 12-hour two-dimensional wind data<br />

(Rosenberg and Magor 1983, Watanabe et al 1990), but their<br />

prediction quality was limited. A three-dimensional simulation<br />

method using a boundary layer model was developed<br />

(Turner et al 1999). However, a prediction system based on<br />

this model has not yet been developed.<br />

To achieve high-precision migration prediction, a realtime<br />

prediction system was developed using three-dimensional<br />

simulation models. This paper presents the simulation method<br />

and its evaluation results.<br />

Materials and methods<br />

Planthopper behavior<br />

Sogatella furcifera and N. lugens are tiny insects about 3–4<br />

mm in size and 1–3 mg in weight (Ohkubo 1973). Many field<br />

observations have shown that the planthoppers take off at either<br />

dusk or dawn (e.g., Ohkubo and Kisimoto 1971). A radar<br />

observation showed that S. furcifera and N. lugens flew to an<br />

altitude of several hundred to 1,000 m above the ground at an<br />

estimated upward speed of 0.2 m s –1 (Riley et al 1991). The<br />

species fly at about 1 m s –1 , w<strong>here</strong>as the wind speed when<br />

migration occurs is typically more than 10 m s –1 (Seino et al<br />

1987). Laboratory experiments of tet<strong>here</strong>d N. lugens adults<br />

indicated that they have the ability to fly for up to 23 hours in<br />

air of high humidity (Ohkubo 1973). N. lugens ceases flying<br />

at cooler temperatures; half of them stop beating their wings<br />

when the air temperature is below 16.5 °C (Ohkubo 1973).<br />

Their postmigration landing process is not yet fully understood.<br />

Planthopper migration simulation model<br />

Takeoff area. Because information on the planthopper’s density<br />

in source regions was not available, it was assumed that<br />

the population density in June to July was high enough for the<br />

planthopper to take off from source regions. In the simulation,<br />

several takeoff areas of 50–100 km 2 were set up in southern<br />

China and Taiwan. These takeoff areas were located in paddy<br />

fields, and covered the major source regions.<br />

Model. The migration simulation model originates from<br />

a particle dispersion model, GEARN, developed by the Japan<br />

Atomic Energy <strong>Research</strong> <strong>Institute</strong> (JAERI), which calculates<br />

atmospheric dispersion of radioactive particles in case of a<br />

nuclear accident (Ishikawa and Chino 1991). GEARN was<br />

modified to model the planthopper’s migration behavior. Figure<br />

1 shows a schematic model. This model calculates the position<br />

of many planthoppers, and doesn’t discriminate between<br />

N. lugens and S. furcifera. Nearly 2,000 planthoppers for each<br />

takeoff area took off randomly within the area at 10 or 21 UTC<br />

(Universal Time Coordinate), which locally corresponds to<br />

dusk or dawn, respectively. They then flew up at a speed of<br />

0.2 m s –1 for 1 hour. Taking off ceased 1 hour later, at 11 or 22<br />

UTC. During their flight over the sea, the planthoppers moved<br />

at the same speed as the wind because they are slow fliers.<br />

Vertical diffusion was taken into account by a random walk<br />

model, but horizontal diffusion was not because preliminary<br />

results showed too much horizontal diffusion over Japan. Since<br />

the planthoppers don’t like cooler air, a temperature ceiling of<br />

16.5 ºC was set up, and they could not go beyond that ceiling.<br />

Wind, temperature, and vertical diffusion coefficient data were<br />

given by numerical weather forecasts. Simulation duration was<br />

48 h. The model calculated the relative aerial density of<br />

planthoppers based on their position on the model grid. The<br />

horizontal resolution was 33 km. Areas of relative density larger<br />

than zero in the lowest level, which was less than 100 m above<br />

the ground, were used for prediction. These areas were called<br />

“migration clouds” (Fig. 2).<br />

Prediction system<br />

First, the latest meteorological data were supplied online to an<br />

advanced numerical weather prediction model, MM5 (Grell<br />

et al 1994). The model forecast atmospheric fields for the next<br />

72 hours at 1-hour intervals. Second, these forecast fields were<br />

supplied to the planthopper migration simulation model,<br />

GEARN, which calculated displacement of a number of modeled<br />

planthoppers and predicted relative aerial density. The<br />

data were converted to PDF files at 3-hour intervals and sent<br />

to the project’s Web site. These processes were conducted automatically.<br />

The system predicted migrations over the next two<br />

days. The maps of relative aerial density provided information<br />

on the timing and area of arrivals. The system also gave<br />

possible migration sources.<br />

Results and discussion<br />

Evaluation<br />

Figure 2 shows an example of predicted migration clouds. An<br />

evaluation was conducted using daily catch data obtained at<br />

three sites in Kyushu, western Japan, in 2003 and 2004. The<br />

sites were Saga (33.17°N, 130.33°E), Kumamoto (32.95°N,<br />

130.78°E), and Kagoshima (31.52°N, 130.50°E). The system<br />

Session 20: Improving rice productivity through IT 571


Takeoff Flight Over Japan<br />

Temp. ceiling of 16.5 ºC<br />

Wind + V-diffusion<br />

0.2 m s –1 for 1 h<br />

33 km<br />

100 m<br />

50 km<br />

Sim. grid<br />

China and Taiwan East China Sea Japan<br />

Fig. 1. Schematic of the migration simulation model. Black circles represent modeled planthoppers. As<br />

many as 1,852 planthoppers per one takeoff area were randomly generated at 10 or 21 UTC. The<br />

simulation duration was 48 h.<br />

E<br />

N<br />

40º<br />

110º 120º 130º<br />

40º<br />

tions were evaluated by a hitting ratio defined as:<br />

Hitting ratio (%) = Number of days when the migration<br />

was correctly predicted/Total number of days × 100<br />

30º<br />

30º<br />

The results in 2003 showed a hitting ratio of 79%, and with<br />

84% the result in 2004. The average hitting ratio of rainfall<br />

forecasts for the Kyushu region in June in the two years was<br />

80%. This number was comparable to that of migration prediction.<br />

20º<br />

110º 120º 130º<br />

20º<br />

Fig. 2. An example of migration clouds. This figure shows the predicted<br />

distribution of relative density of planthoppers at 6 UTC,<br />

25 June 2004, which started at 21 UTC from all the takeoff areas.<br />

predicted daily migrations by seeing whether a migration cloud<br />

would cover the evaluation site or not. To judge predictions,<br />

daily catches of S. furcifera captured at the sites in June to<br />

mid-July were used. Catches of N. lugens were too small to be<br />

used for the evaluation. Traps used were net traps and a<br />

Johnson-Taylor-type suction trap. The net trap was a 1-m tow<br />

net mounted at the top of a pole 10 m high. More than one<br />

catch was interpreted as a migration event. The daily predic-<br />

Discussion<br />

This is the first real-time prediction system to use three-dimensional<br />

wind fields given numerically by weather forecasts.<br />

The system enabled migration prediction that presented information<br />

about the timing and area of migrations. Nonetheless,<br />

several issues need to be discussed.<br />

The takeoff assumption. The strong assumption made<br />

for the prediction was that planthoppers were supposed to take<br />

off from every predefined takeoff area at every takeoff time.<br />

The regions w<strong>here</strong> planthopper density is high in June and<br />

July are located in southern China at latitudes less than 25°N<br />

(Zhou et al 1995). The takeoff areas in Fujian, Guangdong,<br />

Guangxi, and Hainan provinces qualify as such regions. In some<br />

years, however, northern regions around 30°N have been invaded<br />

by the beginning of June. T<strong>here</strong>fore, the other northern<br />

takeoff areas were included. Since the theoretically designated<br />

takeoff areas widely cover possible source regions, this assumption<br />

seems reasonable.<br />

572 <strong>Rice</strong> is life: scientific perspectives for the 21st century


The evaluation period. This was limited to June to mid-<br />

July for several reasons. The first was that the evaluation period<br />

must match the takeoff assumption. Conditions in source<br />

regions in earlier months, such as in April and May, would not<br />

match the assumption very well since planthopper density<br />

would still be low (Zhou et al 1995). T<strong>here</strong>fore, if the evaluation<br />

period included the earlier months, the evaluation would<br />

result in too many false positives, and hence an underestimation<br />

of the hitting ratio. The second reason is that most migrations<br />

from overseas are concentrated in the Bai-u rainy season,<br />

making it the period of greatest concern. Third, from an<br />

evaluation point of view, since preceding migrations in earlier<br />

months were limited in number, the contamination of local<br />

planthoppers in the trap data in June and July was expected to<br />

be low, which was an important condition in conducting an<br />

accurate evaluation. A local planthopper is defined as a<br />

planthopper captured by the trap because of taking off shortly<br />

after landing in Japan, or as a “second-generation” planthopper,<br />

born to immigrants. After mid-July, evaluation becomes rather<br />

difficult because of the contamination of locally reproduced<br />

planthoppers. T<strong>here</strong>fore, the limited evaluation period of June<br />

to mid-July was selected.<br />

Migration source. If a migration cloud from each takeoff<br />

area is traced and its timing and area are compared with<br />

actual catch data, an accurate source estimation can be made.<br />

We have already conducted hourly catch investigations in 2003<br />

and 2004, which clearly showed sharp migration peaks of several<br />

hours. Using these data, we could estimate accurate migration<br />

sources of an order of a few hundred km.<br />

<strong>International</strong> cooperation. The current version of the<br />

prediction system can predict migrations for Korea, and can<br />

be used to analyze migrations within China. Establishing a<br />

prediction system for East Asia is one of the challenging next<br />

steps.<br />

References<br />

Grell G, Dudhia J, Stauffer D. 1994. A description of the fifth-generation<br />

Penn State/NCAR Mesoscale Model (MM5). NCAR<br />

Technical Note NCAR/TN-398+STR. Boulder, Colo. (USA):<br />

NCAR. 122 p.<br />

Ishikawa H, Chino M. 1991. Development of regionally extended/<br />

worldwide version of system for prediction of environmental<br />

emergency dose information: WSPEEDI, (II) long-range transport<br />

model and its application to dispersion of Cesium-137<br />

from Chernobyl. J. Nucl. Sci. Technol. 28:642-655.<br />

Ohkubo N, Kisimoto R. 1971. Diurnal periodicity of flight behaviour<br />

of the brown planthopper, Nilaparvata lugens Stål, in the 4th<br />

and 5th emergence periods. Jpn. J. Appl. Entomol. Zool. 15:8-<br />

16. (In Japanese with English summary.)<br />

Ohkubo N. 1973. Experimental studies on the flight of planthoppers<br />

by the tet<strong>here</strong>d flight technique. Jpn. J. Appl. Entomol. Zool.<br />

17:10-18. (In Japanese with English summary.)<br />

Riley JR, Cheng X-N, Zhang, X-X, Reynolds DR, Xu G-M, Smith<br />

AD, Cheng J-Y, Bao A-D, Zhai B-P. 1991. The long-distance<br />

migration of Nilaparvata lugens (Stål) (Delphacidae) in China:<br />

radar observations of mass return flight in the autumn. Ecol.<br />

Entomol. 16:471-489.<br />

Rosenberg LJ, Magor JI.. 1983. Flight duration of the brown<br />

planthopper, Nilaparvata lugens (Homoptera: Delphacidae).<br />

Ecol. Entomol. 8:341-350.<br />

Seino H, Shiotsuki Y, Oya S, Hirai Y. 1987. Prediction of long-distance<br />

migration of rice planthoppers to northern Kyushu considering<br />

low-level jet stream. J. Agric. Meteorol. 43:203-208.<br />

Turner R, Song Y-H, Uhm K-B. 1999. Numerical model simulations<br />

of brown planthopper Nilaparvata lugens and white-backed<br />

planthopper Sogatella furcifera (Hemiptera: Delphacidae)<br />

migration. Bull. Entomol. Res. 89:557-568.<br />

Watanabe T, Seino H, Kitamura C, Hirai Y. 1990. A computer program,<br />

LLJET, utilizing an 850 mb weather chart to forecast<br />

long-distance rice planthopper migration. Bull. Kyushu Nat.<br />

Agric. Exp. Stn. 26:233-260. (In Japanese with English summary.)<br />

Zhou B-H, Wang H-K, Cheng X-N. 1995. Forecasting systems for<br />

migrant pests. I. The brown planthopper Nilaparvata lugens<br />

in China. In: Drake VA, Gatehouse AG, editors. Insect migration.<br />

Cambridge (UK): Cambridge University Press. p 353-<br />

364.<br />

Notes<br />

Authors’ addresses: Akira Otuka, Tomonari Watanabe, Yoshito<br />

Suzuki, and Masaya Matsumura, National Agriculture and Biooriented<br />

<strong>Research</strong> Organization (NARO), 3-1-1, Kannondai,<br />

Tsukuba, Japan; Akiko Furuno and Masamichi Chino, Japan<br />

Atomic Energy <strong>Research</strong> <strong>Institute</strong> (JEARI), Tokai, Ibaraki,<br />

Japan.<br />

Session 20: Improving rice productivity through IT 573


Distance education and eLearning<br />

for sustainable agriculture: lessons learned<br />

Robert T. Raab and Buenafe R. Abdon<br />

T<strong>here</strong> is no doubt that the agricultural sector, no less than any<br />

other, is facing a range of old and new challenges as a result of<br />

today’s economic and environmental pressures. Key among<br />

these are population growth, increased market complexity,<br />

continuing economic inequality, and the need to raise productivity<br />

without adversely endangering the natural resource base<br />

(McCalla 2001).<br />

A growing global population means that agriculture will<br />

need to produce enough food to feed an expected two billion<br />

additional people by 2025 and this additional production must<br />

be achieved with less natural resources. Compounding these<br />

problems is the changing economic nature of agriculture, with<br />

increased commercialization, sophistication, and globalization.<br />

T<strong>here</strong> is a growing consensus that learning will be a major<br />

factor to help agriculture and agricultural producers successfully<br />

deal with these challenges. “Knowledge—and related<br />

information, skills, technologies, and attitudes—will play a key<br />

role in the sustainable intensification of agriculture and success<br />

of rural development investments,” stated Alex et al<br />

(2002).<br />

Getting the essential knowledge to those who need it<br />

most remains difficult and expensive, but much optimism has<br />

been generated as a result of the increased growth and sophistication<br />

of new electronic information services—even in remote<br />

rural areas. Information and communication technologies<br />

(ICTs), and such specialized ICT applications as<br />

eLearning, are offering new options to deliver knowledge and<br />

information to farmers directly and indirectly through knowledge<br />

intermediaries.<br />

eLearning is one form of distance learning, a type of<br />

educational situation in which the instructor and students are<br />

separated by time, location, or both. eLearning typically involves<br />

the use of the Internet to access learning materials; interact<br />

with the content, instructor, and other learners; and obtain<br />

support during the learning process in order to acquire<br />

knowledge, construct personal meaning, and grow from the<br />

learning experience.<br />

Proponents make several convincing arguments about<br />

the power and potential of eLearning. eLearning provides learning<br />

opportunities in subjects not offered locally or w<strong>here</strong> local<br />

offerings lack quality. It is ideally suited for individuals who<br />

lack time for classroom courses. Perhaps most importantly,<br />

participating in an online class gives students the skills required<br />

for lifelong learning.<br />

Although eLearning is still in its infancy, particularly in<br />

developing countries, some experience has been gained. Below,<br />

we will look briefly at w<strong>here</strong> and how eLearning is being<br />

applied in agriculture and continue on to examine some of the<br />

lessons learned.<br />

Applications of digital technologies to agricultural learning<br />

eLearning and digital technologies are increasingly influencing<br />

and enriching all forms of agricultural education. This is<br />

most apparent in informal and formal education, but with tentative<br />

pilot applications in nonformal education as well.<br />

Traditional means of informal education and learning in<br />

agriculture, based on knowledge and skills being passed between<br />

generations and between community members, are becoming<br />

much less effective. This is a result of several factors,<br />

such as fewer experts in rural areas, agricultural innovations<br />

are increasingly coming from outside the community, fewer<br />

traditional courses are being offered, and much information is<br />

time-sensitive and/or needed quickly (Agriculture and Agri-<br />

Food Canada 2003). Comprehensive and growing repositories<br />

of online agricultural information provide a powerful means<br />

of overcoming these constraints and allow the independent<br />

learner to delve deeply into a myriad of subjects with the click<br />

of a mouse.<br />

Formal education has long been limited by geography,<br />

high cost, and lack of access by particular groups; as a result,<br />

eLearning and associated technologies are increasingly being<br />

used to overcome these obstacles. This trend is most prominent<br />

in higher education in developed countries and recent figures<br />

show that 80% of the top U.S. and European universities<br />

will offer global courses in 2004, with many of these offerings<br />

related to agriculture.<br />

While informal and formal education are certainly important<br />

for the future of agriculture, nonformal education is<br />

arguably the most critical. T<strong>here</strong> is now almost too much information<br />

available online for informal learning and taking<br />

full advantage of these resources requires special skills to locate<br />

and evaluate. Agricultural knowledge acquired through<br />

formal education is soon outdated and obsolete. Properly conceived<br />

and developed, nonformal eLearning can substantially<br />

complement formal and informal efforts and provide up-todate<br />

and relevant agricultural knowledge.<br />

Lessons<br />

Although schools and other providers of education first began<br />

experimenting with online education only just over a decade<br />

ago, much has already been learned. Below, some key lessons<br />

are listed and discussed.<br />

574 <strong>Rice</strong> is life: scientific perspectives for the 21st century


eLearning works<br />

Recent studies have shown that some 50% of North American<br />

farmers take advantage of the informal educational opportunities<br />

available through the Internet through such services as e-<br />

mail (85%), searching information on agricultural products and<br />

services (78%), and news on agriculture (77%). Although these<br />

opportunities are not yet as prevalent in developing countries,<br />

evidence is clear that developing-country farmers and agricultural<br />

professionals are equally eager to learn in this way. The<br />

success of www.agriwatch.com and the ITC company’s<br />

eChoupal project (www.digitaldividend.org/case/<br />

case_echoupal.htm) provides convincing evidence of this.<br />

The best eLearning courses are characterized by incorporating<br />

substantial interaction, are student-centered and<br />

constructivist, provide learner support, and use an integrated<br />

technology environment. Several studies have shown that learning<br />

outcomes associated with formal and nonformal eLearning<br />

are equal to the outcomes of traditional training courses given<br />

similar content and good instructional design.<br />

Experience also shows that, even in developing countries,<br />

properly designed and delivered online courses are effective<br />

and in demand. For example, over a period of three<br />

years, the agLe@rn program of the Asia Pacific Regional Technology<br />

Centre (APRTC) provided some 900 learning opportunities<br />

for agricultural professionals in 20 Asian and 17 African<br />

countries. A survey showed that alumni appreciated the<br />

knowledge they gained, were excited about their new abilities<br />

to network with peers around the world, and were better prepared<br />

to take advantage of digital learning resources. Perhaps<br />

most importantly, they were actively sharing their newly gained<br />

knowledge with students, colleagues, and farmers (Raab and<br />

Abdon 2003).<br />

Rate of application and adoption<br />

of eLearning approaches<br />

The majority of eLearning-related initiatives to date in both<br />

developed and developing countries have been in the area of<br />

online publishing of information as resources for informal learning.<br />

Almost all research and development organizations now<br />

routinely publish their findings and studies in electronic form<br />

and make these documents available through the Internet.<br />

Although aggregated data are not available on formal agriculture-related<br />

courses, it is clear that more and more universities<br />

and schools in developed countries are offering online<br />

learning opportunities. For example, the number of students<br />

taking online courses in the United States grew at more than<br />

25% from 1999 to 2002 and some sectors of higher education<br />

expect an annual growth rate exceeding 25% in online learners<br />

over the next few years (Allen and Seaman 2003). Developing<br />

countries lag seriously behind in this area as a result of high<br />

initial costs and lack of access to information, training, infrastructure,<br />

and resources (UNDP 2001).<br />

Nonformal educational opportunities for agriculturalists<br />

are virtually nonexistent in developing countries and, although<br />

some are available, they are not widely taken advantage of in<br />

developed countries. In developed countries, the main factors<br />

behind this slow adoption have been identified as a lack of<br />

opinion leaders who can provide expert, trusted advice about<br />

online learning and perceptions that<br />

eLearning has uncertain or unproven benefits<br />

Internet and computer access are not sufficient<br />

Online interactions are insecure and not confidential<br />

<br />

<br />

Advanced computer skills are required<br />

The cost is high in relation to benefits (Agriculture<br />

and Agri-Food Canada 2003)<br />

These concerns are no doubt shared by farmers and agricultural<br />

professionals in developing countries, who also have<br />

to deal with more serious cost, computer literacy, and connectivity<br />

limitations, in addition to language and literacy constraints.<br />

The most appropriate targets for eLearning<br />

in support of agriculture<br />

While no one questions that the priority target for knowledge<br />

development efforts must ultimately be agricultural producers,<br />

reaching this group remains problematic because of a range<br />

of cultural and technological constraints. It appears, however,<br />

that these constraints are much less serious among rural knowledge<br />

intermediaries, the many individuals employed by government<br />

extension systems, nongovernment organizations,<br />

academia, and the private sector, who have the responsibility<br />

to provide information and educational opportunities for farmers.<br />

It is also apparent that these individuals are effective in<br />

knowledge transfer and are at least as much in need of new<br />

knowledge and information as the clients they serve.<br />

Sustainability of eLearning efforts<br />

is a major problem<br />

Experience is showing that only a limited number of eLearningrelated<br />

initiatives are economically sustainable, with the exception<br />

of some informal learning resources. Farmers, in developed<br />

and developing countries, with sufficient financial<br />

resources are willing to pay for various kinds of market information<br />

if they feel it can be used to improve profits. Students<br />

(or their parents) will pay for online learning leading to a formal<br />

degree or certification if convinced it will result in better<br />

employment opportunities or a bigger paycheck. It is much<br />

more difficult to convince a learner to pay for a nonformal<br />

course for which the personal financial benefits are not clear<br />

or for which the major beneficiaries may well be others.<br />

Progress will depend on long-term, public-sector,<br />

and/or donor support<br />

The majority of eLearning initiatives, in both developed and<br />

developing countries, are now supported through government<br />

grants or research and development money and are generally<br />

not independently sustainable once the funding runs out. Given<br />

the current situation and the newness of this approach, it is<br />

probably not realistic to expect most initiatives to survive without<br />

continued public funding except in a very few informal<br />

learning niche markets.<br />

Session 20: Improving rice productivity through IT 575


However, the continued involvement of the public sector<br />

may well be in society’s best interest. If learning is available<br />

only to the elite few who can afford it, t<strong>here</strong> is considerable<br />

danger that the divide between the rich and poor will not<br />

only remain but grow. Winrock (2003) cautions that while, in<br />

general, reliance on the private sector is good, “information<br />

and access to it closely resemble a public good threatened with<br />

undersupply by market failures.” In cash-strapped developing<br />

countries, donor support as well will be critical.<br />

References<br />

Agriculture and Agri-Food Canada. 2003. An overview of e-Learning<br />

in Canadian agriculture and Agri-business. www.agr.gc.ca/<br />

ren/serv/elearn_e.cfm.<br />

Alex G, Zijp W, Byerlee D, et al. 2002. Rural extension and advisory<br />

services: new directions. Rural Development Strategy Background<br />

Paper #9. Washington, D.C. (USA): Agriculture and<br />

Rural Development Department, World Bank.<br />

www.worldbank.org/wbi/sdruralpoverty/ag_extension1/Materials/additional/Rural_extension.pdf.<br />

Allen IE, Seaman J. 2003. Sizing the opportunity: the quality and<br />

extent of online education in the United States, 2002 and 2003.<br />

Sloan-C, The Sloan Consortium. www.sloan-c.org/resources/<br />

sizing_opportunity.pdf.<br />

McCalla AF. 2001. Challenges to world agriculture in the 21st century.<br />

Agricultural and Resource Economics Update. University<br />

of California, Davis. www.agecon.ucdavis.edu/outreach/<br />

areupdatepdfs/UpdateV4N3/spring2001.pdf.<br />

Raab R, Abdon BR. 2003. Assessment and use of agLe@rn Knowledge<br />

and course materials. Bangkok (Thailand): APRTC.<br />

www.aprtc.org/for_alumni/multiplier.htm.<br />

UNDP (United Nations Development Programme). 2001. Human<br />

development report 2001: making new technologies work for<br />

human development. Published by Oxford University Press,<br />

Inc., New York City. Retrieved 1 October 2001 from<br />

www.undp.org/hdr2001/.<br />

Winrock. 2003. Future directions in agriculture and information and<br />

communication technologies (ICTs) at USAID. Prepared for<br />

USAID/Economic Growth, Agriculture, and Trade/Agriculture<br />

and Food Security. Retrieved 30 August 2003 from<br />

www.dot-com-alliance.org/documents/AG_ICT_USAID.pdf.<br />

Notes<br />

Authors’ address: Sustainable Development eLearning Network, e-<br />

mail: rraab@sdlearn.net.<br />

The <strong>Rice</strong> Knowledge Bank<br />

Mark Bell and David Shires<br />

The fast and effective transfer of research findings to farmers<br />

has always been one of the biggest challenges facing those in<br />

agricultural development. All too often, new knowledge is successfully<br />

developed and validated, only to fail in reaching those<br />

who need it most—the farmers. Into this gap between research<br />

and impact has stepped the <strong>International</strong> <strong>Rice</strong> <strong>Research</strong><br />

<strong>Institute</strong>’s (<strong>IRRI</strong>) <strong>Rice</strong> Knowledge Bank (RKB). Not only is it<br />

one of the world’s first digital extension services for those who<br />

provide information and support for farmers, it is also the first<br />

comprehensive, digital rice-production library containing a<br />

wealth of information for rice-related training and extension.<br />

More importantly, it provides this service using a format that<br />

sets a new standard for knowledge access within the agricultural<br />

development community. Containing the most up-to-date<br />

and validated knowledge, the RKB is providing government<br />

extension services, nongovernment organizations (NGOs), and<br />

universities with unprecedented access to training and support<br />

knowledge.<br />

First and foremost, <strong>IRRI</strong> is a rice science research institute.<br />

However, <strong>IRRI</strong>’s founders knew that, to get research findings<br />

out of the laboratory and into farmers’ fields, t<strong>here</strong> had to<br />

be an education component. Over the past 40 years, <strong>IRRI</strong> has<br />

used a variety of instructional methodologies and technologies<br />

to satisfy its education mandate. Printed materials, photo-<br />

graphic slide–audio tape modules, instructional video, early<br />

attempts at computer-aided instruction, video-conferencing,<br />

and information presented on CD-ROM have all supported<br />

face-to-face classroom instruction both at <strong>IRRI</strong> headquarters<br />

and in country training programs. Now, <strong>IRRI</strong> is developing<br />

and adding another set of tools to better serve its education<br />

mandate: those that are collectively known as information and<br />

communication technologies (ICT), which include distancelearning<br />

methodologies and use of the Internet.<br />

<strong>IRRI</strong> has moved to harness the power of ICT by carefully<br />

matching the new media’s capabilities to the needs of<br />

rice-related training to bring relevant knowledge, in the most<br />

useful form, to field officers when and w<strong>here</strong> they need that<br />

knowledge. The RKB has received critical acclaim (for example,<br />

BBC Earth Report, September 2004—the “Further readings”<br />

section provides more reviews of the RKB) as a tool to<br />

distill, store, and provide access to the vast array of <strong>IRRI</strong>’s<br />

training and support knowledge for rice science and extension.<br />

Rationale for the RKB<br />

Ask any farmers what they perceive as their major needs and<br />

you will probably be told three things: access to credit, a good<br />

576 <strong>Rice</strong> is life: scientific perspectives for the 21st century


and reliable price for their harvest, and relevant, up-to-date<br />

knowledge. The knowledge that farmers require covers all aspects<br />

of their farming, from the efficient management of farms,<br />

through improved production technologies, to the best<br />

postharvest practices. Knowledge of markets and marketing is<br />

also usually included in their list of knowledge needs. <strong>IRRI</strong>,<br />

through its extensive 40-year research agenda and associated<br />

work in social science and extension, has accumulated much<br />

of the knowledge that will meet these farmer needs.<br />

However, <strong>IRRI</strong> recognized early that an ICT solution<br />

was not going to be successful in achieving impact from its<br />

research findings and improving the livelihoods of farmers if<br />

the approach was only to collate a large amount of knowledge<br />

and make it available through the Internet. To be successful,<br />

other, more important factors had to be included in the design<br />

of an ICT-based system.<br />

The first question <strong>IRRI</strong> tackled was, “Who would make<br />

up the primary audience for the <strong>IRRI</strong> Internet presence and its<br />

array of rice-related knowledge” Clearly, to achieve the goal<br />

of obtaining impact and improving livelihoods from <strong>IRRI</strong> research,<br />

farmers had to be the ultimate beneficiaries of the<br />

project, but they were probably not going to be the primary<br />

users of the RKB. A lack of ready access to ICT infrastructure,<br />

literacy and language capability, and information skills suggested<br />

that, at least initially, a direct farmer target audience<br />

was not appropriate. How then to improve the flow of information<br />

to farmers <strong>IRRI</strong>’s work across the region suggested<br />

that increased capacity of existing farmer intermediaries to<br />

provide better, more timely knowledge in a more usable form<br />

was necessary. Thus, <strong>IRRI</strong> decided that the primary audience<br />

for the RKB would be intermediaries who work directly with<br />

farmers—intermediaries within government extension services,<br />

NGOs, and universities.<br />

The second issue <strong>IRRI</strong> examined was, “Which information<br />

should be included in the RKB” After 40 years of intensive<br />

research covering all aspects of production,<br />

postproduction, and marketing across the region, t<strong>here</strong> was no<br />

shortage of readily available knowledge presenting itself for<br />

inclusion. Investigations within the target audience suggested<br />

that a huge bank of information was not the solution but rather<br />

a careful distillation of the most relevant knowledge would be<br />

more useful.<br />

After these decisions were made, <strong>IRRI</strong> designed a Web<br />

presence, the RKB, whose primary audience is farmer intermediaries.<br />

The RKB contains content that meets the audience’s<br />

needs in improving the delivery of extension services to the<br />

farming community, and makes relevant, up-to-date knowledge<br />

available in a form appropriate to its intended use by farmers.<br />

Assembling the RKB<br />

The RKB was assembled from the knowledge base of <strong>IRRI</strong> by<br />

selecting those knowledge parts that were applicable to the<br />

intended audience, validating the selected knowledge, and assembling<br />

it into a dynamic, easy-to-use form. All the knowledge<br />

was assembled such that it was readily available to the<br />

target audience in the form it required—online, on CD-ROM,<br />

or in print. The RKB was structured as a single-source publishing<br />

resource.<br />

Thus, the RKB was based on three fundamental characteristics<br />

that have proved to be vital in making ICT effective<br />

in training and extension activity:<br />

the RKB has a definite focus: a clear audience and<br />

purpose;<br />

all of its content has the specific characteristics of<br />

being focused, credible, value-added, and demanddriven;<br />

and<br />

single-source publishing provides the form of output<br />

best suited to users.<br />

Characteristics of RKB content<br />

To ensure that the knowledge in the RKB is best suited to the<br />

audience, four characteristics were established and are applied<br />

to all content in the RKB: focused, credible, value-added, and<br />

demand-driven.<br />

1. Focused. A great temptation when using the immense<br />

power of ICT to store, search, and deliver information<br />

is to include as much information as possible—<br />

the principle that “more is better.” <strong>IRRI</strong>, of course, is<br />

well equipped to pursue this strategy because of its<br />

accumulated wealth of research and farming knowledge<br />

accumulated over 40 years of activity across the<br />

region. T<strong>here</strong>fore, much effort is needed to ensure<br />

that the RKB remains focused, containing only the<br />

knowledge that is relevant to extension and research<br />

training and support. Much other valuable knowledge<br />

is omitted and is published through other channels by<br />

<strong>IRRI</strong>. In this way, the target audience is able to quickly<br />

identify knowledge that is directly relevant to it without<br />

having to search through large amounts of what<br />

is, to it, irrelevant knowledge.<br />

2. Credible. Because most members of the target audience<br />

are not trained in many aspects of rice production<br />

and processing, it is not easy for them to judge<br />

the accuracy or relevance of knowledge. T<strong>here</strong>fore, a<br />

basic characteristic of the RKB has to be that all of<br />

the content is credible. <strong>IRRI</strong> instituted and maintains<br />

a rigorous quality-control process that ensures that<br />

all content is accurate, up-to-date, and validated. In<br />

addition, the quality-control process also ensures that<br />

all content possesses these RKB characteristics. The<br />

quality-control process involves review of and signoff<br />

on content by the relevant <strong>IRRI</strong> scientists and review<br />

by RKB staff. With these mechanisms in place,<br />

users can approach the RKB with confidence in the<br />

quality and relevance of the knowledge they locate.<br />

3. Value-added. The knowledge captured in the RKB is<br />

not merely presented in its original scientific form<br />

but is enhanced by presentation in differing forms that<br />

make the knowledge more accessible and more directly<br />

usable.<br />

Session 20: Improving rice productivity through IT 577


Reference guides contain the field-related information<br />

required by extension officers and scientists.<br />

They are concise, easy-to-read manuals, not<br />

scientific papers. They are all presented in an attractive,<br />

easy-to-use electronic book format. The<br />

information in the RKB is not stored as Word<br />

files or PDF files, but in a fully-indexed book<br />

form for users’ convenience.<br />

Fact sheets are the distilled essence of topics that,<br />

on one page, provide all of the vital points about<br />

that topic. They summarize the essence of information<br />

in the reference manuals.<br />

Decision support tools are computer programs<br />

that lead users easily through a process to solve<br />

their particular problem. By questioning users,<br />

the decision support tools lead users to the knowledge,<br />

reference manual sections, or fact sheets<br />

that cover their problem.<br />

eLearning courses have been created to capture<br />

and present some key training in a form that users<br />

can access when and w<strong>here</strong> they want and at<br />

a time of their own choosing. These courses can<br />

be supported by remote tutoring and electronic<br />

discussion groups.<br />

4. Demand-driven. The RKB ensures that its knowledge<br />

base and the access mechanisms are driven by user<br />

needs. It ensures this through <strong>IRRI</strong>’s extensive incountry<br />

networks that continually identify country<br />

needs. In addition, the RKB itself maintains extensive<br />

statistics of usage that help refine the in-country<br />

needs analyses gat<strong>here</strong>d through traditional means.<br />

One particular demand-driven innovation is the<br />

inclusion of country sites, accessible from the home<br />

page by clicking on the country’s flag. These sites<br />

contain the best, most relevant local knowledge that<br />

complements the <strong>IRRI</strong> knowledge. Much of this<br />

knowledge is in the local language and is particularly<br />

directed to local needs and conditions.<br />

Future of the RKB<br />

The RKB will continue to develop over the coming years in<br />

two areas: further content development and the RKB’s application<br />

in countries across the region. The aim of all future development<br />

will be to continue to ensure that the focus of the<br />

RKB remains strong, its content is always up-to-date and accurate,<br />

and its effective use increases in countries.<br />

Four activities are planned in the area of content development:<br />

1. Knowledge will be related to field application. More<br />

emphasis will be placed on ensuring that the content<br />

is, as much as possible, linked to field practice so<br />

that its transfer to farmers is as easy as possible.<br />

2. Up-to-date content will be maintained through links<br />

to <strong>IRRI</strong>’s research agenda and major development<br />

projects. To ensure that the content is the best and<br />

most up-to-date available, more emphasis will be<br />

placed on the use of the RKB by <strong>IRRI</strong> scientists as a<br />

tool to increase the impact of their research. Major<br />

<strong>IRRI</strong> development projects such as the Irrigated <strong>Rice</strong><br />

<strong>Research</strong> Consortium (IRRC) and the Consortium for<br />

Unfavorable <strong>Rice</strong> Environments (CURE) will be involved<br />

in both the dissemination of RKB knowledge<br />

and contributions to the RKB.<br />

3. Content of the RKB will be supplemented by in-country<br />

knowledge. To enhance the scope and relevance<br />

of the content, closer links with country partner<br />

projects will be encouraged, resulting in more goodquality<br />

local knowledge being captured in the RKB.<br />

4. An effective feedback loop to research agendas will<br />

make the RKB more relevant to the overall development<br />

of rice-related activity. Links with <strong>IRRI</strong>’s and<br />

national research agendas will be strengthened, ensuring<br />

the continued health of the knowledge base<br />

that is the RKB.<br />

To improve the scope and quality of application of the<br />

RKB in countries across the region, three areas of activity will<br />

be pursued:<br />

1. Country use through the identification, training, and<br />

support of committed partners will be expanded.<br />

2. The quality and scope of country sites, and the country<br />

information behind the country flags on the home<br />

page, will be expanded through the capture of the best<br />

of the local knowledge available.<br />

3. The expertise to develop independent knowledge<br />

banks will be transferred to national systems and they<br />

will be supported through their development process.<br />

A vision for the RKB<br />

The vision that <strong>IRRI</strong> has for the RKB is much the same now as<br />

it was when it was first conceived. The RKB has always aimed<br />

to provide needed, accurate information in the most appropriate<br />

form for the target audience. The current vision states,<br />

“<strong>IRRI</strong>’s <strong>Rice</strong> Knowledge Bank is the world’s leading repository<br />

of rice-related extension & research training and support<br />

materials, being effectively used by intermediaries and farmers<br />

to improve livelihoods. The <strong>Rice</strong> Knowledge Bank is the<br />

primary focal point for networking and sharing information<br />

between rice communities.”<br />

Further readings about the RKB<br />

Atkinson AD, Bell MA. 2003. Organized free for all. <strong>Rice</strong> Today<br />

2(1):22-25.<br />

Atkinson AD, Bell MA. 2003. The <strong>Rice</strong> Knowledge Bank: strengthening<br />

capacity. Int. <strong>Rice</strong> Res. Notes 27(2):5-10.<br />

578 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Amerasinghe N. 2003. <strong>Rice</strong> Knowledge Bank: a review. ADB <strong>Institute</strong>.<br />

www.adbi.org/articles/29.<strong>Rice</strong>.Knowledge.Bank/<br />

default.php.<br />

Bell MA, Fredenberg P, Atkinson A, Shires D. 2004. How rice farmers<br />

benefit from ICT. New Agriculturalist on-line. www.newagri.co.uk/04-4/focuson/focuson3.html.<br />

Noronha F. 2003. <strong>Rice</strong> could get a bounty crop, thanks to the Net.<br />

Express Computer, India’s No. 1 IT Business Weekly.<br />

www.expresscomputeronline.com/20030106/indcomp2.shtml.<br />

Notes<br />

Authors’ address: <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong>, DAPO Box<br />

7777, Metro Manila, Philippines, e-mail: m.bell@cgiar.org,<br />

d.shires@cgiar.org.<br />

Integrated information systems<br />

for crop research and improvement<br />

Graham McLaren, Arllet Portugal, Alexander Cosico, William Eusebio, Teri Ulat, May Ann Sallan, Victor Jun Ulat, and Richard Bruskiewich<br />

<strong>International</strong> germplasm exchange was the engine of the Green<br />

Revolution. In the past, however, much of the important information<br />

generated from this exchange was accessible only locally,<br />

in field <strong>books</strong> or researchers’ files. Although major international<br />

initiatives for germplasm collection and conservation<br />

followed the Green Revolution, much collected material<br />

is still not used because it is difficult to access. As a result, the<br />

potential impact on agriculture has not yet been realized. However,<br />

the free exchange of information, through international<br />

crop information systems, should provide the foundation for a<br />

second revolution that adds value to germplasm by seamlessly<br />

uniting its conservation, evaluation, use, and exchange.<br />

Furthermore, new technologies in molecular biology and<br />

genomics mean that traditional phenotypic information must<br />

be linked to large quantities of sequence and genetic information<br />

so that functional genomics and allele-mining activities<br />

can speed up germplasm enhancement.<br />

The <strong>International</strong> Maize and Wheat Improvement Center<br />

(CIMMYT) devised an information strategy and developed<br />

software on a main-frame computer during the 1980s to facilitate<br />

unambiguous identification of wheat germplasm, t<strong>here</strong>by<br />

establishing links among information from different sources<br />

(Fox et al 1996a). In 1995, CIMMYT and <strong>IRRI</strong> canvassed<br />

other CGIAR centers to establish a project to develop an <strong>International</strong><br />

Crop Information System applicable to a wide range<br />

of crops.<br />

The <strong>International</strong> Crop Information System (ICIS)<br />

Extensive communication among CGIAR centers highlighted<br />

the economies to be gained by collaborating on the development<br />

of an information system that could be used for many<br />

crops. At a meeting held at CIMMYT in September 1994, a<br />

prototype CD-ROM was demonstrated and Open Database<br />

Connectivity (ODBC) was chosen as a programming standard<br />

for international collaboration. This ensures that the choice of<br />

database system for a particular crop is independent of the<br />

decision to use ICIS.<br />

Several CGIAR centers, national agricultural research<br />

and extension systems, and advanced laboratories are collaborating<br />

to develop ICIS as a generic system that will accommodate<br />

all data sources for any crop. The vision of ICIS is to<br />

integrate different data types into a single information system<br />

and provide specialist views and applications that operate on<br />

a single integrated data platform. ICIS must also seamlessly<br />

integrate private local data with public central information to<br />

give local researchers access to global crop information. After<br />

all phases of development are complete, ICIS will seamlessly<br />

support a range of activities including germplasm conservation,<br />

functional genomics, allele mining, breeding, cultivar testing,<br />

and release. Data will be accessible from CD-ROM or the<br />

Internet, and users could either adopt the complete system or<br />

individual components complementary to their own systems.<br />

The driving force behind ICIS is accessing and sharing data<br />

rather than providing analytical and statistical tools. This is<br />

because the major bottleneck to intelligent data integration and<br />

use was not statistical software, but rather the drudgery of finding,<br />

extracting, preparing, and managing the data.<br />

Functionality<br />

The ICIS system is fast, user-friendly, PC-based, and distributable<br />

on CD-ROM or via the Internet. It contains<br />

A genealogy management component to capture and<br />

process historical genealogies as well as to maintain<br />

evolving pedigrees, and to provide the basis for unique<br />

identification and internationally accepted nomenclature<br />

conventions for each crop.<br />

A data management system for genetic, phenotypic,<br />

and environmental data generated by evaluation and<br />

testing, as well as for providing links to genomic maps.<br />

Links to geographic information systems that can manipulate<br />

all data associated with latitude and longitude<br />

(e.g., international, regional, and national testing<br />

programs).<br />

Session 20: Improving rice productivity through IT 579


Applications for maintaining, updating, and correcting<br />

genealogy records and tracking changes and updates.<br />

Applications for producing field <strong>books</strong> and managing<br />

sets of breeding material, and for diagnostics such<br />

as COPs (coefficients of parentage) and genetic profiles<br />

for planning crosses.<br />

Tools to add new breeding methods, new data fields,<br />

and new traits.<br />

Tools for submitting data to crop curators and for distributing<br />

data updates via CD-ROM and electronic<br />

networking.<br />

Remote users<br />

One of the innovative features of ICIS is that it permits independent<br />

users to integrate their own local data with public central<br />

data. ICIS does this by allowing read-only access to the<br />

central database for a particular crop and supporting a local<br />

copy of the central data model w<strong>here</strong> the local data are stored.<br />

Apart from providing user-friendly access to the data, so that<br />

crop scientists can make informed decisions, the system provides<br />

a local data management system for users and captures<br />

relevant data for the crop. Periodic updates to the central database<br />

by users make their data available to all other users as<br />

well as browsers of the central database.<br />

The data model<br />

The data model and database system of ICIS are designed for<br />

maximum flexibility to cater to as wide a range of crops as<br />

possible. The model must be independently adopted for a specific<br />

crop and data entered to create an independent system<br />

for that crop.<br />

The Genealogy Management System. The core of ICIS<br />

is a common genealogical data model, called the GMS, which<br />

must be sufficiently well designed and universal to accommodate<br />

a wide range of crops. The functions of the GMS are to<br />

(1) assign and maintain unique germplasm identification, (2)<br />

retain and manage information on genealogy, and (3) manage<br />

the nomenclature and chronology of germplasm development.<br />

Each germplasm entity is identified by a controlled<br />

CropID (the domain), a UserID (the authority), and a locally<br />

assigned GERMPLASM_ID (GID). The logical connection between<br />

a GID and a packet of seeds or other propagating material<br />

is that different packets that germplasm specialists would<br />

not like to mix receive different GIDs. Figure 1 shows information<br />

on method, location, date of genesis, and other attributes<br />

managed through the data model. Each germplasm record is<br />

linked to its progenitors through their GIDs. Germplasm is<br />

divided into two categories, generative and derivative. Generative<br />

germplasm is produced by generative methods, which<br />

tend to increase and combine genetic variability such as crosses<br />

or mutations. Derivative germplasm is produced by derivative<br />

methods, which tend to refine and target genetic variability,<br />

such as selection methods, or which aim to maintain genetic<br />

status through management methods such as seed increase or<br />

conservation. Germplasm produced by generative methods may<br />

have any number of progenitors. Derivative germplasm is derived<br />

from a single germplasm source.<br />

Germplasm collects a multitude of labels during the development<br />

and release process. These are all tracked as NAMES<br />

in the GMS. One name must be identified as the preferred name.<br />

NAMES may contain imbedded information, and this can be<br />

made accessible to application programs for specific name<br />

types by specifying a format for the name.<br />

Attributes are text variables used to store information<br />

about the genesis, genealogy, nomenclature, or chronology of<br />

germplasm. Attribute types are defined and described as<br />

USER_DEFINED_FIELDS. Like names, attributes may contain<br />

imbedded information in the form of subfields or variables<br />

within the attribute text.<br />

The Data Management System. The functions of the<br />

DMS are to (1) store and manage documented and structured<br />

data from a genetic resource, varietal evaluation, and crop<br />

improvement studies; (2) link data to specialized data sources<br />

such as GMS, and soil and climate databases; and (3) facilitate<br />

inquiries, searches, and data extraction across studies according<br />

to structured criteria for data selection.<br />

All types of data can be accommodated in DMS, including<br />

raw data, observed data, derived data, and summary statistics.<br />

Data may have continuous or discrete numeric values, or<br />

text or categorical character values. For example, observations<br />

on disease resistance or nutrient efficiency of a genotype can<br />

be numerical measurements, scored or calculated indices, or<br />

text data. More complex forms of data, such as pictures or<br />

documents, will also be considered. Figure 2 shows the basic<br />

data model of the DMS, and shows the linkages between the<br />

entities described below.<br />

A STUDY is the basic, reportable unit of research; it is<br />

synonymous with the notions of experiment, nursery, or survey.<br />

Since the DMS must deal with any of these, we use the<br />

term “STUDY.” A STUDY is characterized by a set of scientific<br />

objectives and testable hypotheses and results in the collection<br />

of one or more data sets. FACTORS are classifying variables<br />

in a STUDY, which take values from finite sets of discrete<br />

LEVELS. Factors are named and described in each STUDY. They<br />

have three main attributes: the PROPERTY of the experimental<br />

material or survey units being manipulated or stratified, the<br />

METHOD or procedure by which the levels are applied, and the<br />

SCALE or measurement units in which the levels are expressed.<br />

All levels of a particular factor are expressed in the same scale.<br />

The names of factors are consistent within studies and equivalent<br />

factors are linked across studies through common<br />

PROPERTYs. PROPERTY is subject to a controlled vocabulary to<br />

facilitate this linkage.<br />

Data sources such as field objects, sampling units, or<br />

data classes such as treatment are identified by combinations<br />

of levels of design or sampling factors. These are referred to<br />

as OBSERVATION UNITS, which may be grouped into subsets or<br />

EFFECTS. DATUM values are recorded for one or more VARI-<br />

ATES. Each VARIATE has the same three attributes as a FACTOR,<br />

the PROPERTY or trait being measured, the METHOD or proce-<br />

580 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Germplasm<br />

Generative germplasm<br />

Has progenitors<br />

Derivative germplasm<br />

(Recursive links)<br />

Has group<br />

Has source<br />

Developed by<br />

Methods<br />

Called<br />

Names<br />

Developed at<br />

Locations<br />

Named at<br />

Named by<br />

Developed by<br />

Users<br />

Assigned at<br />

With value of<br />

Attributes<br />

Assigned by<br />

Defined property<br />

User-defined fields<br />

Fig. 1. Data model for the ICIS Genealogy Management System.<br />

dure by which the value is observed or derived, and the SCALE<br />

or measurement units in which the value is expressed.<br />

Correcting data<br />

Corrections and changes will inevitably be made in any database.<br />

Only authorized users can make these changes, and all<br />

changes are logged so that the sequence of changes can be<br />

traced and can be “undone” if required.<br />

One common occurrence of changes is when new information<br />

about an existing germplasm record is entered into a<br />

local database. If the existing record is also in the local database,<br />

then the local user can complete the changes. But, if it is<br />

in the central database, changes cannot be completed until the<br />

central database is updated. Verifying and completing requested<br />

changes are part of the update process and sufficient information<br />

and justification need to be recorded in the changes table<br />

to allow the process to be completed.<br />

Verification and completion of changes in the central<br />

database may take some time but local users would like to see<br />

their changes reflected immediately. This is achieved by the<br />

DLL, which always checks the local CHANGES table for central<br />

changes and applies them at run time for the specific installation<br />

w<strong>here</strong> they are recorded.<br />

Stand-alone software modules<br />

Components of ICIS include a Genealogy Management System<br />

(GMS); Set Generation Module (SETGEN), including the<br />

External Pedigree Input Tool (EPIT); Field Book Module<br />

Session 20: Improving rice productivity through IT 581


Study<br />

Applied by<br />

Property management<br />

module<br />

Observed by<br />

Factor<br />

Application of<br />

Expressed in<br />

Applied by<br />

Property<br />

Measured of<br />

Expressed by<br />

Variate<br />

Scale<br />

Value of<br />

Indexed by<br />

Effect<br />

Method<br />

Measured by<br />

Vector<br />

Element<br />

of<br />

Measurement<br />

of<br />

Representation of<br />

Level<br />

Indexed by<br />

Observation<br />

unit<br />

Data<br />

Fig. 2. Data model for the ICIS Data Management System.<br />

(FLDBK); Trait Management System (TMS); Data Management<br />

System (DMS); a Work Book (WRKBK) for data input<br />

and query; and the Data Retriever for cross-study data queries<br />

(RTV). The first four modules focus on germplasm and management<br />

of genealogy and nomenclature. The next three handle<br />

the management of evaluation and characterization data, and<br />

the Retriever provides access to both raw and processed data.<br />

User-defined data<br />

Users will be able to define new relationships among<br />

germplasm by specifying new breeding methods. They can<br />

specify attributes of the germplasm to be stored, types of names,<br />

location descriptors, and traits and variates for characterization<br />

and evaluation data. Data with any form of factorial structure<br />

can be managed.<br />

Links to global bioinformatics resources<br />

Other databases of agricultural information have close links<br />

with ICIS. The System-wide Information Network for Genetic<br />

Resources (SINGER) aims to provide global access to genetic<br />

resources data across all CGIAR-mandated crops and commodities.<br />

Germplasm records in ICIS that relate to accessions<br />

in the CGIAR collections are linked with SINGER so that the<br />

ICIS can provide information on the use and deployment of<br />

those genetic resources.<br />

Each individual ICIS database manages data for a particular<br />

crop and generally does not share data with other crops.<br />

This integrating role of genetic resources information across<br />

crops is played by SINGER (Fig. 3).<br />

ICIS has also enjoyed collaboration with the USDAsponsored<br />

GrainGenes and Gramene database initiatives. Linking<br />

these implementations to ICIS will provide access to sequence<br />

information and molecular maps, which will facilitate<br />

functional genomics and allele mining and integrate information<br />

across crops at the genomic end of the spectrum.<br />

The <strong>International</strong> <strong>Rice</strong> Information System (IRIS)<br />

IRIS is the rice implementation of ICIS. The GMS of IRIS<br />

stores information on about one and a half million varieties,<br />

breeding lines, and accessions of rice. This allows pedigree<br />

analysis to trace germplasm flows and relationships between<br />

lines that can be used to improve evaluation estimates or plan<br />

improvement programs. The DMS of IRIS contains 5 million<br />

data values from over 500 studies from breeding, screening,<br />

and international testing trials. This allows integrative analysis<br />

over different environments. These data are available<br />

through a web interface and are linked to rice data sources<br />

throughout the world (Bruskiewich et al 2003).<br />

Conclusions<br />

The technical challenge for plant scientists and software developers<br />

is to implement the type of system outlined <strong>here</strong>. The<br />

challenge for administrators is perhaps more difficult—to facilitate<br />

the continued free exchange of information and to nurture<br />

a scientific culture in which users take full advantage of<br />

the data of others and, in turn, contribute to shared databases.<br />

582 <strong>Rice</strong> is life: scientific perspectives for the 21st century


SINGER<br />

Access to basic genetic resources data:<br />

accessions, cooperators, standards, characterization, transfer, collecting<br />

Data sharing across crops<br />

Central<br />

databases<br />

User<br />

databases<br />

Wheat <strong>Rice</strong> Sorghum Others<br />

Data types:<br />

l Genetic resources<br />

data management<br />

l Characterization<br />

l Evaluation<br />

l Genealogy<br />

l Nomenclature<br />

l Unique identification<br />

of germplasm<br />

ICIS<br />

data model and information system<br />

Fig. 3. Relationship between SINGER and ICIS.<br />

References<br />

Bruskiewich RM, Cosico AB, Eusebio W, Portugal AM, Ramos LM,<br />

Reyes T, Sallan MA, Ulat VJ, Wang X, McNalley K, Sackville-<br />

Hamilton R, McLaren CG. 2003. Linking genotype to phenotype:<br />

the <strong>International</strong> <strong>Rice</strong> Information System.<br />

Bioinformatics 19(Supp. 1):i63-i65.<br />

Fox PN, Lopez C, Skovmand B, Sanchez H, Herrera R, White JW,<br />

Duveiller E, van Ginkel M. 1996. <strong>International</strong> Wheat Information<br />

System (IWIS), Version 1. Mexico, D.F.: Centro<br />

Internacional de Mejoramiento de Maíz y Trigo. On compact<br />

disk.<br />

Fox PN, Skovmand B. 1996. The <strong>International</strong> Crop Information<br />

System (ICIS)—connects genebank to breeder to farmer’s<br />

field. In: Cooper M, Hammer GL, editors. Plant adaptation<br />

and crop improvement. Wallingford (UK): CAB <strong>International</strong>.<br />

Notes<br />

Authors’ address: <strong>International</strong> <strong>Rice</strong> <strong>Research</strong> <strong>Institute</strong> (<strong>IRRI</strong>),<br />

DAPO Box 7777, Metro Manila, Philippines.<br />

Using APAN for content delivery: possibilities for the CGIAR<br />

Paul O’Nolan<br />

In the mid-1990s, the Consultative Group on <strong>International</strong><br />

Agricultural <strong>Research</strong> (CGIAR) positioned itself well to take<br />

advantage of new opportunities provided by information technology,<br />

with projects such as the Integrated Voice and Data<br />

Network (IVDN) and the System-Wide Information Network<br />

for Genetic Resources (SINGER)—an application that de-<br />

pended on new levels of connectivity. The IVDN brought the<br />

first digital Internet connections to several of the countries in<br />

which the CGIAR operates. Since then, the world has changed<br />

a great deal, as evidenced by disconnections from the IVDN<br />

and connections to local Internet service providers that didn’t<br />

exist seven or eight years ago. Unfortunately, the CGIAR is no<br />

Session 20: Improving rice productivity through IT 583


longer at the forefront in bringing the fruits of new information<br />

and communication technologies to bear on scientific and<br />

development problems. To date, only a single CGIAR center<br />

is connected to second-generation Internet networks. As a system,<br />

the CGIAR has fallen years behind w<strong>here</strong> it should be.<br />

<strong>Research</strong>ers in many national agricultural research and extension<br />

systems in Asia and elsew<strong>here</strong> now enjoy better connectivity<br />

to advanced research networks than CGIAR scientists,<br />

so now is a good time for the CGIAR to do some catching up.<br />

Recently, the Information and Communication Technology<br />

and Knowledge Management (ICTKM) program of the<br />

CGIAR has, with funding from the World Bank, committed<br />

funds (approx. US$100,000) to kick-start advanced research<br />

networking (ARN) in the CGIAR. This paper presents some<br />

ways in which advanced research network connectivity will<br />

have an impact on research and education in the CGIAR.<br />

Background<br />

The CGIAR first joined the Asia Pacific Advanced Network<br />

(APAN; www.apan.net) when <strong>IRRI</strong> joined on behalf of the<br />

system in 1999 under the leadership of the then acting head of<br />

the <strong>IRRI</strong> Training Center, Dr. Robert Raab. Using a single PC<br />

with a nondedicated 128 kbps APAN connection, videoconferencing<br />

technology was used to have <strong>IRRI</strong> scientists give<br />

seminars at the Ministry of Agriculture in Bangkok and attend<br />

a seminar at <strong>IRRI</strong> on bioinformatics presented from Singapore.<br />

Under Raab’s leadership, <strong>IRRI</strong> funded APAN connectivity for<br />

the Thai national agricultural research system (NARS) for two<br />

years, after which the NARS took it over, retained the connection,<br />

and began to use a national network to disseminate adapted<br />

and translated versions of <strong>IRRI</strong>-originated training materials.<br />

In subsequent years, <strong>IRRI</strong>’s APAN connection improved,<br />

eventually becoming a dedicated 2 Mbps link; <strong>IRRI</strong> went on<br />

to create the <strong>Rice</strong> Knowledge Bank<br />

(www.knowledgebank.irri.org), an electronic, Internet-accessible<br />

digital repository of knowledge about rice; the first national<br />

“mirror” copy of the <strong>IRRI</strong> Web site was created in<br />

Beijing, hosted by the <strong>Institute</strong> of Microbiology (at<br />

www.irri.cn). More recently, in 2004, <strong>IRRI</strong> signed a memorandum<br />

with the Agriculture, Forestry, and Fisheries <strong>Research</strong><br />

Council of the Japanese Ministry of Agriculture, Forestry, and<br />

Fisheries (MAFF/AFFRC) agreeing that <strong>IRRI</strong> and MAFF/<br />

AFFRC shall jointly develop, distribute, and promote mirroring<br />

systems for improving access to and sharing of Internetbased<br />

information in Japan and in other countries in the Asian<br />

region—using the APAN network, the hub of which is in<br />

Tsukuba, Japan.<br />

A copy of the <strong>International</strong> <strong>Rice</strong> Information System<br />

(IRIS), a version of the <strong>International</strong> Crop Information System<br />

(ICIS) that <strong>IRRI</strong> is developing in cooperation with partner<br />

organizations from several countries (home page: http://<br />

iris.irri.cgiar.org), is now hosted online at MAFF’s Information<br />

Network (MAFFIN) headquarters in Tsukuba. Data are<br />

replicated between MAFFIN and <strong>IRRI</strong> using APAN and it is<br />

planned that the MAFFIN network operating center (NOC)<br />

will be the hub for future data replication to networking centers<br />

in other Asian countries connected to APAN. Mirrored data<br />

will also be available via the Internet. <strong>IRRI</strong> will provide content<br />

and MAFFIN will provide network resources, including<br />

storage and bandwidth to this end.<br />

In principle, a vehicle now exists for sharing a wide variety<br />

of different kinds of information relevant to agricultural<br />

research and development among APAN-connected organizations<br />

in the region. Sharing can be done on a bilateral basis<br />

between pairs of nodes or via the NOC hub on a one-to-many<br />

basis. Shareable content could originate in the region, or externally,<br />

and be made available via partners, such as CGIAR<br />

institutes.<br />

T<strong>here</strong> are many reasons to mirror data. In the case of the<br />

China mirror of <strong>IRRI</strong>’s Web site, the copy helps students and<br />

scientists avoid paying for international communications<br />

charges using a commercial Internet service provider. It has<br />

been <strong>IRRI</strong>’s experience in India, Thailand, and elsew<strong>here</strong> that<br />

content stored locally is more likely to be translated and<br />

adapted. When used with suitable file-sharing software, mirror<br />

sites may provide faster and more reliable access to large<br />

data sets by distributing the burden of data transfers. In addition,<br />

mirror sites, which need not be public, can help in disaster<br />

mitigation.<br />

Even with the rapid decline in the cost of bandwidth in<br />

recent years and its growing availability, it is clear that mirroring<br />

will remain a useful technology for a long time, and that<br />

much of the utility will derive from added-value features such<br />

as data annotation, search capabilities, use of standard formats,<br />

etc. Even simply sharing metadata about what data are potentially<br />

available could be very valuable. It should be possible to<br />

co-opt a peer-to-peer file-sharing tool of the kind typically used<br />

to share music (often illegally) to share metadata among communities.<br />

Today, a great deal of valuable scientific information<br />

is hidden away inside organizations and even its existence<br />

may be hard to discover.<br />

APAN and the CGIAR today<br />

Meanwhile, Internet technology has marched on. Most, but not<br />

all, of the CGIAR institutes now have local rather than international<br />

Internet connectivity as they did five years ago. One<br />

of the CGIAR’s ICTKM projects is a so-called “2nd-Level<br />

Connectivity” enhancement project, designed to improve connectivity<br />

at nonheadquarters locations, such as country offices<br />

and regional offices, with a special focus on Africa.<br />

However, <strong>IRRI</strong> is still the only center connected to an<br />

advanced research network (APAN); we hope that it will be<br />

joined in this by several sister CGIAR institutes in 2005 (the<br />

<strong>International</strong> Potato Center, CIP, in Peru; the <strong>International</strong><br />

Center for Tropical Agriculture, CIAT, in Colombia; and <strong>International</strong><br />

Maize and Wheat Improvement Center, CIMMYT, in<br />

Mexico are currently planning to connect to Internet2 in 2005,<br />

with funding from the CGIAR ICTKM advanced research networks<br />

project, led by <strong>IRRI</strong>). Today, every networked computer<br />

in <strong>IRRI</strong> has a broadband connection to APAN. The APAN link<br />

584 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Before<br />

Los Baños<br />

PHNET, Makati<br />

<strong>IRRI</strong><br />

2 Mbps<br />

(E1)<br />

1.5 Mbps<br />

APAN<br />

Commercial<br />

ISP<br />

Internet<br />

Fig. 1. <strong>IRRI</strong>’s APAN connectivity in 2003: a shared local loop from <strong>IRRI</strong> to a co-located<br />

router at the premises of the Philippine Network Foundation (www.ph.net) in Manila for<br />

a 1.5 Mpbs APAN link and a 1 Mbps commercial Internet connection (one of two in<br />

operation). ISP = Internet service provider.<br />

After<br />

Los Baños<br />

U.P.<br />

Los Baños<br />

PHNET, Makati<br />

U.P.<br />

Open<br />

University<br />

<strong>IRRI</strong><br />

2 Mbps<br />

(E1)<br />

<strong>IRRI</strong><br />

IPB<br />

<strong>IRRI</strong><br />

6 Mbps<br />

(3 × E1)<br />

2 Mbps<br />

(E1)<br />

Ai3<br />

APAN<br />

ASTI, Quezon City<br />

PREGINET<br />

Fig. 2. <strong>IRRI</strong>’s APAN connectivity in 2004: the 6 Mbps local loop to the Advanced Science<br />

and Technology <strong>Institute</strong> (ASTI) at the University of the Philippines Diliman<br />

(www.upd.edu.ph) will be operational in 2005. Here, a CGIAR institute serves as a bridge<br />

between both national and international partners.<br />

to the Philippines increased from 1.5 Mb to 6 Mbps in February<br />

2004. In the Philippines, the Department of Science and<br />

Technology has sponsored the creation of a national network,<br />

PREGINET, the Philippine <strong>Research</strong>, Education, and Government<br />

Information Network (http://preginet.asti.dost.gov.ph).<br />

This network now connects all 19 regions of the Philippines<br />

with broadband links and more than 70 institutions are connected<br />

to it. Video-conferencing between nodes and broadcasting<br />

of meetings using video-streaming technologies are routine.<br />

Recent changes in <strong>IRRI</strong>’s APAN connectivity are summarized<br />

in Figures 1 and 2.<br />

With the change in the national termination point of<br />

APAN from PHNET to ASTI, as shown in Figure 2, <strong>IRRI</strong> opted<br />

to install a faster local loop that would enable better exploitation<br />

of the extra APAN bandwidth. The original circuit was<br />

retained as a backup and made available to the local scientific<br />

community. Locally, the University of the Philippines Los<br />

Baños (UPLB), the University of the Philippines Open University<br />

(UPOU), and the <strong>Institute</strong> of Plant Breeding (IPB) were<br />

interconnected with fiber optic cable that converged in an <strong>IRRI</strong><br />

building. They were not connected to APAN, nor, more importantly,<br />

to PREGINET.<br />

Apart from local loop communication costs and infrastructure<br />

costs, advanced research network bandwidth is free<br />

to the end user. When CGIAR scientists are connected to<br />

Internet2 or to APAN or similar networks, including connected<br />

national networks in a growing number of countries, they can<br />

make use, at no marginal cost, of video-conferencing, videostreaming,<br />

and other communication-intensive technologies<br />

(e.g., for large data transfers, and for hosting and synchronizing<br />

mirror sites of genomic, climatic, and other data).<br />

Session 20: Improving rice productivity through IT 585


Fig. 3. July 2004. A planned Access Grid node begins to take shape at <strong>IRRI</strong>. The<br />

facility has been used by <strong>IRRI</strong> staff for videoconferences with scientists on PREGINET.<br />

<strong>IRRI</strong> has begun construction of an Access Grid node<br />

(www.accessgrid.org). Once additional CGIAR centers connect<br />

to advanced research networks, the CGIAR network can<br />

play a bridging role in facilitating face-to-face interactions<br />

between national partners at some locations and external partners.<br />

With the Access Grid’s suitability for informal group<br />

meetings, we hope that the technology “catches on” and is used<br />

for informal meetings by communities of interest.<br />

In 2004, four CGIAR centers acquired grid cluster computer<br />

systems for bioinformatics and genomics research. It is<br />

planned that these resources will be shareable on the CGIARwide<br />

area network and improvements in ARN connectivity to<br />

address this should have spillover benefits for bandwidth for<br />

content sharing and delivery.<br />

APAN and the CGIAR tomorrow<br />

Despite the explosive growth in the number of cell phones in<br />

the region in recent years, access to communication technology<br />

is out of reach for many Asians, in particular the rural<br />

poor. In Bangladesh, for example, it is estimated that only 5%<br />

of the population has a cell phone despite annual growth rates<br />

of 85%. 1 This will surely change dramatically in the next 5–10<br />

years as cellular and wireless Internet devices become ever<br />

cheaper, more capable, and increasingly convergent. The empowering<br />

effects of access to communication by the poor are<br />

well documented. What the world needs, and will surely have<br />

soon, is an affordable multifunctional device for voice and data<br />

communications. A new state-of-the-art device, such as an HP<br />

iPAQ 6300, costs about $500. For half as much, one eminent<br />

researcher, Raj Reddy, now claims it is possible to make and<br />

sell a device that connects the world’s poor. 2<br />

It seems likely that we are, at most, only a few generations<br />

of cellular and wireless technology away from a $100<br />

device. This is still not affordable by all individuals but should<br />

be accessible to most communities in populated areas.<br />

What will the connection be between researchers using<br />

networks like APAN and farmers and extension workers with<br />

Internet access via a prepaid subscription to a wireless Internet<br />

service The “CGIAR Knowledge Bank in your pocket” will<br />

be attainable. Whether it will feed anyone, of course, will be<br />

another challenge. Just delivering content will not be enough.<br />

Clearly, we are only at the beginning of an exciting era.<br />

Notes<br />

Author’s address: Head, Information Technology Services, <strong>IRRI</strong>,<br />

DAPO Box 7777, Metro Manila, Philippines,<br />

p.onolan@cgiar.org.<br />

1 www.asiamedia.ucla.edu/article.aspparentid=10184. Bangladesh cellphone<br />

market holds huge potential, Asia Media, 13 Apr. 2004.<br />

2 www.iht.com/articles/534041.html. At $250, a PC that aims to connect<br />

world’s poor. John Markov. <strong>International</strong> Herald Tribune, 16 Aug. 2004.<br />

586 <strong>Rice</strong> is life: scientific perspectives for the 21st century


A decision support system for site-specific nitrogen<br />

management of paddy rice<br />

Ryouji Sasaki, Kazunobu Toriyama, and Yoichi Shibata<br />

<strong>Rice</strong> yield and quality depend highly on soil nitrogen fertility<br />

(Murayama 1979). Yearly fluctuations of temperature and sunshine<br />

also affect rice growth and yield considerably. Thus, a<br />

decision support system formed by inputting those physical<br />

variables has been anticipated. A decision support system for<br />

rice was developed in Australia to calculate the amount of<br />

topdressing nitrogen fertilizer based on leaf nitrogen analysis<br />

(Angus et al 1996).<br />

Recently, the number of farmers with more than 10 ha<br />

has increased in Japan, accompanied by land consolidation, in<br />

which several small fields (0.1 to 0.3 ha) are joined to form a<br />

large field (1 ha), aiming at increasing production efficiency.<br />

However, this has often engendered variability in soil fertility<br />

within a large field, and thus uniform application of fertilizer<br />

results in the lodging of rice plants and considerable spatial<br />

variability in grain yield and quality. More information-intensive<br />

fertilization strategies, by which nitrogen fertilizers are<br />

precisely applied according to site-specific information about<br />

soil fertility, are needed to match fertilizer inputs to the seasonal<br />

pattern of rice crop nutrient demand and soil nitrogen<br />

supply. Although t<strong>here</strong> was a trial for site-specific nutrient management<br />

in several Asian countries in cooperation with <strong>IRRI</strong><br />

(Witt and Dobermann 2002), the required precision to overcome<br />

the variability in the reclaimed large field would be much<br />

higher. Thus, we have developed a computer-based decision<br />

support system based on the idea of site-specific nutrient management<br />

to solve the above problems.<br />

Simulation model and structure of the system<br />

Outline of the simulation model<br />

The simulation model employed in the system contains several<br />

simple submodels that simulate the development and<br />

growth of rice plants in daily time steps (Table 1). Most of the<br />

submodels were modified or evolved from the models by precursors.<br />

The developmental stage of rice plants is estimated<br />

by maximum and minimum air temperature, and is expressed<br />

as a continuous variable. The influence of daylength on panicle<br />

initiation is not considered in this model. The parameters of<br />

the model for soil nitrogen mineralization, such as mineralization<br />

rate constant, mineralization potential, and apparent<br />

activation energy, should be derived from the experimental<br />

data.<br />

Structure of the system<br />

This decision support system is named “<strong>Rice</strong>NiSMo” (<strong>Rice</strong><br />

Nitrogen Simulation Model). It is written in Visual Basic and<br />

runs on PCs with Windows-OS. The target rice plant of the<br />

system is transplanted Koshihikari, a leading variety in Japan<br />

with good taste. This system has roughly four functions, as<br />

follows.<br />

Registration of nitrogen fertilizer. Not only ammonium<br />

sulfate or ammonium chloride but also the compound fertilizer,<br />

high-analysis mixed fertilizer, coated urea (controlledrelease<br />

urea N) could be registered in this system. Two or three<br />

different types of nitrogen fertilizers, which are mixed for basal<br />

dressing by users, could also be registered as original N fertil-<br />

Table 1. Relationships between simulated items and factors for the simulation.<br />

Simulated items<br />

Developmental stage<br />

Plant age in leaf number<br />

Soil nitrogen mineralization<br />

Nitrogen release from coated urea<br />

Nitrogen uptake<br />

Growth<br />

Canopy development<br />

Intercepted solar radiation<br />

Elongation of culm<br />

Lodging index<br />

Grain yield<br />

Factors<br />

Temperature<br />

Temperature, developmental stage<br />

Temperature<br />

Temperature<br />

Soil N mineralization, effective soil depth, amount of<br />

N fertilizer, temperature, developmental stage<br />

Intercepted solar radiation, temperature, plant N status<br />

Nitrogen uptake, plant N status, developmental stage,<br />

temperature<br />

Global radiation, leaf area<br />

Developmental stage, canopy development at panicle<br />

initiation stage, amount of N fertilizer as topdressing<br />

Culm length<br />

Dry weight, N uptake at harvest stage<br />

Session 20: Improving rice productivity through IT 587


izers. However, the mixed N fertilizer for topdressing is not<br />

available at present. The temporal nitrogen release from the<br />

coated urea is simulated by the model reported by Hara (2000).<br />

Simplified estimation of soil fertility. To estimate soil<br />

fertility, users are requested to input each date and value in a<br />

normal year into the system as follows: (1) date of puddling,<br />

transplantation of seedlings, and harvest; (2) name of nitrogen<br />

fertilizers and the amount of basal and topdressing; and (3)<br />

grain yield as brown rice.<br />

We have collected a large number of data sets for brown<br />

rice yield and N uptake at harvest from field trials at several<br />

prefectural experiment stations in the Hokuriku region. These<br />

data sets were from 1994 to 1999. Grain yield ranged from 2.7<br />

to 7.0 t ha –1 . T<strong>here</strong> was a close relationship between grain<br />

yield and N uptake at harvest; t<strong>here</strong>fore, N uptake at harvest<br />

(Nup) could be calculated by using the yield data. The amount<br />

of N uptake from fertilizer (Nup_fertilizer) can be estimated<br />

assuming a reported recovery efficiency of fertilizer N. Thus,<br />

the N uptake from soil (Nup_soil) could be calculated by subtracting<br />

Nup_fertilizer from Nup. On the other hand, a temporary<br />

value for effective soil depth is preset to simulate the<br />

amount of mineralized soil N per unit land area. Soil N fertility<br />

depends on the amount of organic nitrogen in the soil profile.<br />

The importance of nitrogen fertility in subsoil was also<br />

suggested (Sekiya and Shiga 1977). T<strong>here</strong>fore, tuning the simulated<br />

Nup_soil with the Nup_soil calculated from the yield data<br />

would give a plausible estimate of effective soil depth. Although<br />

measurement of organic nitrogen along the soil profile<br />

by near-infrared spectroscopy (Toriyama et al 2003) is convenient,<br />

it still takes time for soil sampling and preparation for<br />

measurement. Recently, a yield-monitoring combine with a<br />

GPS has been developed in Japan (Chosa et al 2002); thus, the<br />

variability of soil fertility within a large field could be better<br />

estimated from the monitored yield data by employing the<br />

abovementioned scheme.<br />

Calculating the recommended amount of N fertilizer. The<br />

amount of N fertilizer for basal application and topdressing is<br />

calculated as follows. At first, agronomic variables, such as<br />

planned date of fertilization, puddling, transplantation of rice<br />

seedlings, and the like, and parameters reflecting soil N fertility<br />

are input into the system. Then, the growth and N uptake of<br />

rice plants is simulated by input variables with weather data of<br />

a normal year, and the application rate of basal N and<br />

topdressing N is computed to close the gap between the estimated<br />

and required N uptake at both stages.<br />

<strong>Rice</strong> variety Koshihikari tends to lodge at harvest. N<br />

uptake at panicle initiation was closely related to culm length<br />

at the ripening stage (Sasaki et al 2001), which is a good indicator<br />

for forecasting lodging at harvest. The optimum amount<br />

of N topdressing based on growth and N uptake at panicle<br />

initiation to avoid or reduce lodging could be recommended.<br />

Users of this system will be able to decide on optimum<br />

N fertilization based on the calculated values for the respective<br />

field. If the field is large and has considerable variability<br />

in soil fertility, then the procedures as above are followed likewise<br />

for each site so that variability in yield and quality among<br />

sites can be reduced.<br />

Application rate and timing of topdressing N. The input<br />

variables for cultivation and/or amount of fertilizer can be altered<br />

if necessary, and weather data for the respective year can<br />

be input daily or timely. The results of simulation for growth,<br />

canopy development, and the like could be referred to by users.<br />

The growth stage of both normal and ongoing years could<br />

be calculated. As fluctuations occur yearly in the soil N supply<br />

by temperature, the preset application rate of topdressing N<br />

can be reconsidered. It is recommended to measure the N uptake<br />

of the rice canopy at panicle initiation and revise the calculated<br />

value because the simulation model is simplified. Nitrogen<br />

uptake could be measured by a ground-based image<br />

mapping system equipped with a GPS and a CCD camera with<br />

band pass filter for near-infrared images, and a CCD camera<br />

to take images of the rice canopy vertically from zenith to the<br />

ground (Shibata et al 2002).<br />

The optimum date for harvesting could also be predicted<br />

by this simulation model based on the accumulated temperature.<br />

Thus, users can prepare harvesting work based on the<br />

prediction.<br />

Problems for future research<br />

Although the initial purpose to develop a decision support system<br />

for site-specific management of paddy rice was achieved,<br />

continuous improvement of the simulation model is necessary,<br />

especially when rice quality becomes a concern. The regulation<br />

of N content in rice grain based on the simulation model<br />

like the one above is strongly anticipated because N content is<br />

the index of rice palatability in Japan. Thus, the system will<br />

require a model with the relationship between the N status of<br />

the rice plant and N content of rice grains. The present model<br />

estimates the amount of N mineralized under specific conditions,<br />

and thus further study is needed to increase the validity<br />

of the model. Finally, variable rate applications are essential<br />

for site-specific management of rice in large-sized fields. For<br />

that purpose, a yield-monitoring combine is also important.<br />

T<strong>here</strong>fore, it is very important to communicate the information<br />

between these machines and this system on a computer.<br />

The system also needs a revision to enable the calculation of<br />

profit based on a price of grain and a cost of fertilizer N and<br />

the like.<br />

References<br />

Angus JF, Williams RL, Durkin CO. 1996. MANAGE RICE: decision<br />

support for tactical crop management. In: Ishii R, Horie<br />

T, editors. Crop research in Asia: achievements and perspectives.<br />

Proceedings of the 2nd Asian Crop Science Conference,<br />

21-23 August 1995. Fukui City (Japan): Asian Crop Science<br />

Association. p 274-279.<br />

Chosa T, Kobayashi K, Daikoku M, Shibata Y, Omine M. 2002. A<br />

study on yield monitoring system for head-feeding combines.<br />

I. Adoption of an optical sensor and a load cell as a yield<br />

monitor. J. Jpn. Soc. Agric. Mach. 64:145-153.<br />

588 <strong>Rice</strong> is life: scientific perspectives for the 21st century


Hara Y. 2000. Estimation of nitrogen release from coated urea using<br />

the Richards function and investigation of the release parameters<br />

using simulation models. Soil Sci. Plant Nutr. 46:693-<br />

701.<br />

Murayama N. 1979. The importance of nitrogen for rice production.<br />

In: Nitrogen and rice. Manila (Philippines): <strong>International</strong> <strong>Rice</strong><br />

<strong>Research</strong> <strong>Institute</strong>. p 5-23.<br />

Sasaki R, Horie T, Toriyma K, Shibata Y. 2001. Factors affecting the<br />

yearly fluctuation in culm length of rice. Jpn. J. Crop Sci.<br />

70:489-498.<br />

Sekiya S, Shiga H. 1977. A role of subsoil of paddy field in nitrogen<br />

supply to rice plants. JARQ 11:95-100.<br />

Shibata Y, Sasaki R, Toriyama K, Araki K, Asano O, Hirokawa M.<br />

2002. Development of image mapping techniques for site-specific<br />

paddy rice management. J. Jpn. Soc. Agric. Mach. 64:127-<br />

135.<br />

Toriyama K, Sasaki R, Shibata Y, Sugimoto M, Chosa T, Omine M,<br />

Saito J. 2003. Development of a site-specific nitrogen management<br />

system for paddy rice. JARQ 37:213-218.<br />

Witt C, Dobermann A. 2002. A site-specific nutrient management<br />

approach for irrigated, lowland rice in Asia. Better Crops Int.<br />

16:20-24.<br />

Notes<br />

Authors’ addresses: Ryouji Sasaki, National Agricultural <strong>Research</strong><br />

Center for Western Region, e-mail: ryouji@affrc.go.jp;<br />

Kazunobu Toriyama, Japan <strong>International</strong> <strong>Research</strong> Center for<br />

Agricultural Sciences, e-mail: toriyama@affrc.go.jp; Yoichi<br />

Shibata, Obihiro University of Agriculture and Veterinary<br />

Medicine, e-mail: yshiba@obihiro.ac.jp.<br />

Wrap-up of Session 20<br />

The importance of information technology (IT) is increasing rapidly<br />

in agricultural production and research, as demonstrated by<br />

several examples of IT-related activities with rice. IT, unlike many<br />

other technologies, is horizontally applicable in that it has applications<br />

throughout almost all aspects of agriculture. This session<br />

discussed the present status of IT-based activities and provided<br />

an opportunity to discuss the future of IT applications in rice research<br />

and production.<br />

During this session, seven oral papers and nine posters<br />

were presented. Seven of the oral papers and one poster have<br />

been recommended for inclusion as full papers in the conference<br />

proceedings. The papers cover the application of IT in precision<br />

farming, a low-cost wireless-based field-monitoring robot,<br />

an integrated database system to efficiently transfer knowledge,<br />

lessons learned in an eLearning activity, an integrated system to<br />

accelerate rice breeding, and a high-performance Internet infrastructure<br />

to harness IT applications. The following is the summary<br />

of each paper and a discussion from each presentation.<br />

T. Chosa, in “Data mining using combined yield and quality<br />

maps of paddy fields,” discussed developments in precision farming<br />

in recent years, particularly in Japan and some other Asian<br />

countries. Precision farming involves making optimal decisions<br />

based on site-specific information, such as fertility, growth, and<br />

previous crop yields. In spite of the progress in information acquisition<br />

technology and site-specific management, t<strong>here</strong> are still<br />

difficulties in providing optimal recommendations for crop management<br />

and no general method for producing recommendations<br />

has been determined. This paper suggested the need to<br />

develop a categorical map as a guideline for making recommendations<br />

for crop management in succeeding years by combining<br />

yield and quality maps of paddy fields. During discussion, the<br />

benefits of this approach to farmers were pointed out as one of<br />

the most important criteria for further development in precision<br />

farming.<br />

M. Hirafuji and others, in “A wireless sensor network with<br />

Field-Monitoring Servers and MetBroker in paddy fields,” discussed<br />

a low-cost, wireless-based field-monitoring system, Field Server.<br />

Field Server is a Web server installed in fields. When used with a<br />

Field-Monitoring Server (FMS), it allows real-time monitoring to<br />

identify wireless LAN hotspots around the FMS. The FMS consists<br />

of a Fieldserver-Engine (a micro Web server for control and<br />

data acquisition), wireless LAN access point, network camera,<br />

and sensors. By combining these elements, the FMS can be connected<br />

to various sensors and probes directly. A group of Field<br />

Servers can be linked to develop a linked sensor network. Data<br />

acquired from Field Servers by an agent program are stored in<br />

the FMS archive in an XML format and the stored data are linked<br />

to a weather database, accessible through a weather data mediator,<br />

MetBroker, to provide a consistent interface to several<br />

agricultural software applications. A group of Field Servers has<br />

been used in paddy fields for a long-term experiment without any<br />

trouble. Several questions arose during the discussion period—<br />

particularly about the availability and price of the FMS.<br />

A. Otuka and others, in “Prediction of airborne immigration<br />

of rice pest insects,” reported on a new simulation model to predict<br />

the airborne immigration of rice insect pests to Japan. The<br />

whitebacked planthopper and the brown planthopper are major<br />

pests of rice in eastern Asia, and migrate from southern China to<br />

Japan, primarily in June to July each year. Generally, the prediction<br />

of planthopper migration provides farmers and plant protection<br />

advisers with information about the source of the migration<br />

as well as w<strong>here</strong> the migration is occurring. Knowing the migration<br />

source is important as it helps to understand pest characteristics<br />

such as biotype, pesticide resistance, etc. The quality of<br />

conventional prediction methods that use 6- or 12-h two-dimensional<br />

wind data is limited. The authors adopted a three-dimensional<br />

simulation method using a boundary layer model to develop<br />

a new method to predict pest immigration. Field observations<br />

of pest immigration over two seasons showed that the new<br />

method could predict immigration of the pest 2 days before its<br />

arrival with a precision as high as 80%. Compared with the precision<br />

of the former method, this precision is fairly high, indicating<br />

Session 20: Improving rice productivity through IT 589


that the new method is useful. The new method can also be a<br />

tool to determine the take-off areas of pests.<br />

R. Raab and B. Abdon, in “Distance education and<br />

eLearning for sustainable agriculture: lessons learned,” described<br />

the experiments and lessons learned by the authors, who have<br />

been providing an eLearning service as an NGO activity in the<br />

Asian region. Specialized information and communication technology<br />

(ICT) applications such as eLearning are offering new options<br />

to deliver knowledge and information to farmers directly<br />

and indirectly through knowledge intermediaries. eLearning provides<br />

learning opportunities in subjects not offered locally or w<strong>here</strong><br />

local offerings lack quality. Agricultural knowledge acquired through<br />

formal education can soon become outdated and obsolete. Properly<br />

conceived and developed, nonformal eLearning can substantially<br />

complement formal and informal efforts and provide up-todate<br />

and relevant agricultural knowledge. Although not yet as<br />

prevalent in developing countries, t<strong>here</strong> is clear evidence that<br />

developing-country farmers and agricultural professionals are<br />

equally eager to learn in this way. The majority of eLearning-related<br />

initiatives to date in both developed and developing countries<br />

have been in the area of online publishing of information as<br />

resources for informal learning. Although aggregated data are<br />

not available on formal agriculture-related courses, more and<br />

more universities and schools in developed countries are offering<br />

online learning opportunities. The most appropriate targets for<br />

eLearning in support of agriculture are currently agricultural professionals<br />

and knowledge intermediaries.<br />

M. Bell and D. Shires, in “The <strong>Rice</strong> Knowledge Bank,” reported<br />

the concept and purpose of the <strong>International</strong> <strong>Rice</strong> <strong>Research</strong><br />

<strong>Institute</strong>’s <strong>Rice</strong> Knowledge Bank (RKB). Access to information<br />

is a major limitation to improving the livelihoods of farmers<br />

in Asia. <strong>IRRI</strong> t<strong>here</strong>fore developed RKB as the world’s leading<br />

ICT repository of rice-based extension and training knowledge.<br />

Containing the most up-to-date and validated knowledge, the<br />

RKB is providing government extension services, NGOs, and universities<br />

with unprecedented access to training and support knowledge.<br />

The RKB was assembled from the knowledge base of <strong>IRRI</strong><br />

by selecting those knowledge parts that were applicable to the<br />

intended audience, validating the selected knowledge, and assembling<br />

it into a dynamic, easy-to-use form. All RKB content is<br />

focused, credible, value-added, and demand-driven. Further, drawing<br />

on best industry practice, the RKB is developed around the<br />

concept of “single-source publishing,” which allows target audiences<br />

to access information in the format best suited to their<br />

circumstances: through the Internet, on CD-ROM, or on paper.<br />

Since its launch in September 2002, the RKB has received more<br />

than 4 million hits.<br />

G. McLaren and others, in “Integrated information systems<br />

for crop research and improvement,” reported on the <strong>International</strong><br />

<strong>Rice</strong> Information System (IRIS) of <strong>IRRI</strong>. IRIS is the rice portion<br />

of the <strong>International</strong> Crop Information System (ICIS), a database<br />

system for the management and integration of global information<br />

on genetic resources and crop improvement for any crop.<br />

Major constraints to developing knowledge-intensive crop improvement<br />

programs include ambiguous germplasm identification, difficulty<br />

in tracing pedigree information, and lack of integration<br />

among genetic resources, characterization, breeding, evaluation,<br />

and use data. ICIS is being developed to overcome these constraints.<br />

The Genealogy Management System (GMS) is the core<br />

database, which ensures unique identification of germplasm,<br />

management of nomenclature, and retention of all germplasm<br />

development information. The GMS links germplasm with characterization<br />

and evaluation data, and a trait ontology with a controlled<br />

vocabulary ensures integration of information across different<br />

studies. New components are being added to the database<br />

to handle the diversity of rice functional genomics data,<br />

including genomic sequence data, molecular genetic data, expression<br />

data, and proteomic information. Integration with international<br />

bioinformatics resources is facilitated by adopting Web<br />

services technology using both XML Schema and BioMoby standards.<br />

P. O’Nolan, in “Using APAN for content delivery: possibilities<br />

for the CGIAR,” explained that the Consultative Group on<br />

<strong>International</strong> Agricultural <strong>Research</strong> (CGIAR) first joined the Asia<br />

Pacific Advanced Network (APAN) when <strong>IRRI</strong> joined on behalf of<br />

the system in 1999. A copy of the IRIS, a version of the ICIS that<br />

<strong>IRRI</strong> is developing in cooperation with partner organizations from<br />

several countries, is now hosted online at MAFF’s Information<br />

Network (MAFFIN), headquartered in Tsukuba. Data are replicated<br />

between MAFFIN and <strong>IRRI</strong> using APAN and it is planned<br />

that the MAFFIN network operating center (NOC) will be the hub<br />

for future data replication to networking centers in other Asian<br />

countries connected to APAN. Mirrored data will also be available<br />

via the Internet. Recently, <strong>IRRI</strong>’s APAN connectivity was totally<br />

changed, and today every networked computer in <strong>IRRI</strong> has a broadband<br />

connection to APAN. <strong>IRRI</strong> has also begun construction of<br />

an Access Grid node. Once additional CGIAR centers connect to<br />

advanced research networks, the CGIAR network can play a bridging<br />

role in facilitating face-to-face interactions between national<br />

partners at some locations and external partners.<br />

R. Sasaki and others, in “A decision support system for<br />

site-specific nitrogen management of paddy rice,” discussed a<br />

decision support system for site-specific nutrient management.<br />

As the scale of paddy fields is increasing in Japan, the in-field<br />

soil fertility variability in these larger fields becomes an issue because<br />

uniform application of fertilizer results in lodging of rice<br />

plants and considerable spatial variability of grain yield and quality.<br />

Thus, more information-intensive fertilization strategies, by<br />

which nitrogen fertilizers are precisely applied based on site-specific<br />

information about soil fertility, are needed to match fertilizer<br />

inputs to the seasonal pattern of rice crop nutrient demand and<br />

soil nitrogen supply. The authors developed a computer-based<br />

decision support system to solve this problem. The simulation<br />

model employed in the system contains several simple submodels<br />

that simulate development and growth of rice plants in daily time<br />

steps. This decision support system is named “<strong>Rice</strong>NiSMo” (<strong>Rice</strong><br />

Nitrogen Simulation Model).<br />

590 <strong>Rice</strong> is life: scientific perspectives for the 21st century

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