PHILIPPINES
This country report is prepared as a contribution to the FAO publication, The
Report on the State of the World’s Forest Genetic Resources. The content and the
structure are in accordance with the recommendations and guidelines given by
FAO in the document Guidelines for Preparation of Country Reports for the State
of the World’s Forest Genetic Resources (2010). These guidelines set out
recommendations for the objective, scope and structure of the country reports.
Countries were requested to consider the current state of knowledge of forest
genetic diversity, including:
Between and within species diversity
List of priority species; their roles and values and importance
List of threatened/endangered species
Threats, opportunities and challenges for the conservation, use and
development of forest genetic resources
These reports were submitted to FAO as official government documents. The
report is presented on www. fao.org/documents as supportive and contextual
information to be used in conjunction with other documentation on world forest
genetic resources.
The content and the views expressed in this report are the responsibility of the
entity submitting the report to FAO. FAO may not be held responsible for the use
which may be made of the information contained in this report.
Publisher
Ecosystems Research and Development Bureau
Food and Agriculture Organization of the United Nations
Bibliographic
Entry and Citation
Ecosystems Research and Development Bureau. 2012.
Philippine Country Report on Forest Genetic Resources,
ERDB, College, Laguna. 162 p.
ISBN
978-971-8831-36-6
This publication is produced through the project: “Philippine Country Report on Forest
Genetic Resources” implemented by the Department of Environment and Natural
Resources - Ecosystems Research and Development Bureau and funded by FAOPhilippines thru the Country Representative’s Technical Cooperation Programme Facility.
Printed by
Lobster Printing, Pasay City, Philippines
FRONT and BACK COVER PHOTO: Seed Production Area of A. mangium in Bansud,
Oriental Mindoro, Philippines.
Country Report on
Forest Genetic Resources
Philippines
Country Report on Forest Genetic Resources
iii
Foreword
T
he world’s forest genetic resources are in a state of siege. For
too long a time, the forests of the world have been subjected
to severe exploitation to satisfy the needs of an ever growing
population. This is not surprising as indeed the forests are springs
of resources that can satisfy most basic needs of man. History tells
us that the forests have been the dominant habitats of the early
human civilization. Before the advent of sedentary agriculture,
the forest resources have largely supported the nomadic life of
human beings. In most countries of the world, the forests and
the various natural resources they contain have also provided the
foundation for progress and development. Even in these current
times, people have been turning to the forests for their sources
of livelihood, and food and fuel during periods of scarcity. It is no
wonder then that in the course of history, we have seen the steady
decline in both the quantity and quality of the forests around the
world.
Nowhere in the world could such be true as in the Philippines.
Significant stages in the economy of the country in the past could
be tied with the state of forest and forest resources use. It was in
the Philippines where systematic logging of the tropical forests in
Southeast Asia had been first demonstrated. For a time during the
early part of the last quarter of the previous century, the forestry
sector has been the top contributor to the Philippines’ gross
domestic product. Back then, the Philippines had been exporting
quality logs to countries abroad. Other than being the top dollar
earner for the country that time, the forest industries had been
providing work to several thousands of Filipinos and boosting
the economy in the local areas where timber concessions were
operating. But that was long ago. From a high of about 19 million
hectares or about 65% of the total area of the country at the start
of the last century, the forests of the country have steadily been
decimated through the years. At the end of the last century, the
forest of the country was down to a measly 17% of the total area
of the nation.
A belated recognition of the implications of such sobering
circumstance was the irreversible consequences of such to the
forest genetic resources of the country. It cannot be denied that
Philippines
iv
Country Report on Forest Genetic Resources
Foreword
with the systematic and indiscriminate cutting of the country’s
forests in the past, a huge part of these genetic resources has
been removed never to benefit the Filipinos again today and in the
years to come. That the Philippines has been declared as one of the
biodiversity hotspots of the world points to the fact that it had lost
a significant portion of such forest genetic resources, and that the
loss will continue unless drastic measures are instituted to reverse
such phenomenon. The Philippines’ forest genetic resources are
indeed not inexhaustible resources as they were once perceived
to be.
Today, there are indications of an increasing awareness on the
need to conserve and protect whatever remains of the forest
genetic resources of the country. Several big initiatives, both by
the government and the private sectors, are achieving limited
gains in so far as curbing the further depletion of the Philippines
forest genetic resources is concerned. But more needs to be done.
It should be obvious to everyone that the current efforts towards
forest genetic conservation in the country are still wanting,
with the current programs and activities largely fragmented in
nature. There is the felt need to harmonize all these initiatives
and formulate and implement seriously a national program on the
conservation of forest genetic resources in the country.
The preparation of this country report on the state of the forest
genetic resources in the Philippines as part of the program of the
Food and Agriculture Organization of the United Nations on the
“State of the World’s Forest Genetic Resources” could very well
be the means to jumpstart a meaningful national initiative. Other
than providing this impetus, this country report also hopes to
strengthen further the current awareness on the value of forest
genetic resources and the urgent need to sustainably manage
and/or conserve such.
The report can very well provide the foundation for a more
concerted effort on the sustainable management and conservation
of the Philippines forest genetic resources. This needs to be done,
and undertaken in the immediate future, before it becomes too
late.
RAMON J. P. PAJE, CESO I
Secretary
Department of Environment
and Natural Resources
Philippines
Philippines
Country Report on Forest Genetic Resources
v
Preface
T
he Country Report on the State of the Forest Genetic Resources
is the Philippines contribution to the preparation of the “The
State of the World’s Forest Genetic Resources (SoW-FGR)” by
the Food and Agriculture Organization of the United Nations. The
latter is a response of the FAO to the felt need to continually
guarantee the sustainable use and conservation of the world’s
forest biological diversity to insure that such is able to provide for
food security, poverty alleviation, environmental conservation, as
well as the economic and social advancement and the maintenance
of cultural and spiritual values in the communities that depend
on them. As envisioned by the FAO, the country reports were
to provide the foundation for the drafting of the SoW-FGR. To
provide for a common framework on the reporting process and to
insure the uniformity of the information that shall be used in the
writing of the Sow-FGR, the FAO prescribed a set of guidelines in
the preparation of the country reports. This report endeavored
to conform mostly to the framework and prescriptions in the
guidelines.
In addition to heightening the awareness on the critical need for
more sustainable use and management of the country’s forest
genetic resources, the Report also provides a platform for the
planning and implementation of activities that should lead to
the conservation of the same on a national level. In keeping
with the FAO instituted guidelines, the Philippine Country Report
has attempted to provide a comprehensive assessment of the
following: the state of forest genetic resources in the Philippines
and their roles in the forest and forestry production systems in
the country, including the associated biodiversity and the factors
driving the changes; the current contribution of forest genetic
resources to sustainable forest development, and food, and
agriculture; how the contribution of forest genetic resources to
sustainable forest development, and food and agriculture can
be enhanced, identifying opportunities and obstacles, as well as
strategies to realize the opportunities and overcome any obstacles,
and; the needs and priorities for capacity building to enable the
conservation, sustainable use and development of forest genetic
resources.
Philippines
vi
Country Report on Forest Genetic Resources
Preface
The Report contains insights on the past and current management
of the forest genetic resources in the Philippines, the different insitu and ex-situ forest genetic resources conservation programs,
a description of the few tree improvement and breeding activities
undertaken, existing infrastructures and facilities as well as laws,
rules and regulations and other policy issuances related to forest
genetic resources use and conservation, the country’s participation
in regional and international agreements and collaborative projects,
existing knowledge base and education programs, research and
development programs and projects, and the different capacity
building initiatives on the sustainable use and conservation of
forest genetic resources in the country.
The Ecosystems Research and Development Bureau of
the Department of Environment and Natural Resources took the
lead in the drafting and finalization of the country report. The
completion of this Report would not have been possible without
the help of a number of persons and institutions. Their work is
acknowledged with much appreciation. They have contributed so
much in advancing the cause of conserving and managing the
forest genetic resources of the Philippines in a sustainable manner.
MARCIAL C. AMARO, JR., CESO III
Director
Ecosystems Research and Development Bureau
Philippines
Country Report on Forest Genetic Resources
vii
Executive
Summary
T
he need to conserve forest genetic resources has long been
seriously recognized. Taking the lead in the efforts to stem the
tide of the continuous loss of and/or conserve the world’s forest
genetic resources is the Food and Agriculture Organization (FAO)
of the United Nations which has organized the Panel of Experts on
Forest Gene Resources or the Forest Gene Panel as early as 1967.
This urgent concern was further translated into action with the
FAO Commission on Genetic Resources for Food and Agriculture
agreeing on the preparation of a report on “The State of the World’s
Forest Genetic Resources.” The global report will draw from the
country reports that shall be prepared by the member countries.
This is the Country Report on the Forest Genetic Resources (FGR)
of the Philippines.
This country report was prepared in accordance with the Guidelines
for the Preparation of Country Reports for the State of the World’s
Forest Resources prepared by the FAO. The FAO designed the
Country Reports to cover genetic resources of environmental,
economic, social and cultural values. Specifically, the country
reports were expected to bring insights on current management
activities of forest genetic resources, in-situ and ex-situ genetic
conservation as well as improvement and breeding activities,
support facilities, and participation and/or involvement in regional
and international cooperation and collaboration pertaining to forest
genetic resources, and capacity building needs on both knowledge
and genetic resources management.
In keeping with the guidelines, this report is an attempt to assess
the state of the Philippine’s forest genetic resources and their roles
and values. In the assessment, “aspects of forest biodiversity, the
production systems and the environment in which these resources
are used, the range of products and services which they provide,
the consumption patterns and socio-cultural practices associated
with them, the ecosystem functions which they sustain and their
roles in achieving sustainable forest management, food security
and poverty alleviation” were likewise discussed.
Philippines
viii
Country Report on Forest Genetic Resources
Executive
Summary
The Philippines lies just above the equator between 4°30’ and
21°20’ North latitude and 116°40’ and 126°34’ East longitude and
is made up of over 7,107 islands. Of the total land area, 94%
comes from the 11 largest islands. The land area is 300,000 square
kilometres (sq km) or 30,000,000 hectares (ha). Water within the
land occupies an area of 1,830 sq km. The coastline measures
36,289 km. The prevailing climate is tropical rain monsoon from
November to April and Southwest monsoon from May to October.
There are only two seasons, wet and dry as per the monsoon rains.
The terrain is mostly mountainous with narrow coastal lowlands.
Natural hazards include 20-22 cyclonic typhoons per year,
landslides, flooding, active volcanoes, destructive earthquakes
and tsunamis. Current environmental issues include uncontrolled
deforestation especially in watershed areas, soil erosion, air and
water pollution in major urban areas, coral reef degradation,
and increasing pollution of coastal mangrove swamps that are
important as fish breeding grounds.
In situ conservation of forest genetic resources in the Philippines
largely takes place in protected areas in the Philippines. In
situ conservation in protected areas started in the Philippines
as early as 1932, through the institution of the National Parks
System. In totality, 60 national parks and 8 game refuges and
bird sanctuaries were established under this system. These parks,
refuges and sanctuaries became a core component of the National
Integrated Protected Areas System (NIPAS) which was established
in 1992 through Republic Act (RA) 7586. The objective of NIPAS
is to “integrate outstanding remarkable areas and biologically
important public lands that are habitats of rare and endangered
species of plants and animals, biogeographic zones and related
ecosystems whether terrestrial, wetland or marine, all of which
shall be designated as protected areas”. The national parks
established before 1992 became the initial components of NIPAS.
Currently, there are 302 of these in the NIPAS with a total area
of more than 5.5 million ha, including natural parks, protected
landscapes and seascapes, natural monuments or landmarks,
resource reserves, wildlife sanctuaries, natural biotic areas, and
marine parks and mangrove swamps. Only about 93 have, thus
far, been given Presidential Proclamation or Congressional actions
covering some 2.95 million ha or just 9.8% of the total land area
of the Philippines. Constraints in the in situ conservation of forest
genetic resources in the country include inadequate inventories of
their plant biodiversity or detailed information on which rare and
threatened species occur in which protected areas, the abundance
of rare, endangered, or threatened species in production forests,
the threat of alien invasive species in PAs, lack of knowledge and
skills of field personnel doing timber cruising on rare, endangered
and threatened tree species, non-delineation on the ground of the
boundaries of the PAs, encroachment of farming activities into the
PAs, and institutional and management limitations.
Philippines
Country Report on Forest Genetic Resources
Executive
Summary
ix
Ex situ conservation efforts for forest genetic resources in the
Philippines generally involve establishment of field genebanks
or plantations, botanical gardens, and seed banks. For a time
genebanks mostly of commercial fast growing exotic species in the
form of tree plantations were maintained by large integrated wood
industries (e.g. PICOP Resources, Inc.) in the country. But such
living collections were also subjected to harvesting. To date, there
may still be a few remaining collections but they are no longer
being maintained and that records pertaining to accessions in such
areas are mostly missing. There are now three rattan genebanks,
a field genebank of agroforestry tree species, two palmetum,
two mangrovetum, and three bambusetum. All are adequately
maintained. There are botanic gardens in several areas in the
country notable of which is the Makiling Botanic Gardens of the
University of the Philippines Los Baños (UPLB) in the Province of
Laguna. There are clonal multiplication gardens of dipterocarps and
tree plantation species. There are seed production areas identified
but their maintenance and documentation are inadequate.
There are a few seed orchards established by ERDB. There are
significant efforts on clonal propagation, both macro- and micropropagation. Few researches related to ex situ conservation have
been undertaken so far. Initiatives on the ex situ conservation of
forest genetic resources in the Philippines are largely fragmented
and clearly, more needs to be done along this area.
Much needs to be done also when it comes to the sustainable
use and management of forest genetic resources in the country.
The continuous destruction of the environment poses a great
threat to the availability of forest genetic resources. Destruction
is mainly caused by land conversion for settlement, agricultural
development, shifting cultivation, logging, forest fire, and to some
extent mining, energy projects, and pest and diseases. The country’s
forest genetic resources are threatened by overexploitation for
commercial purposes (e.g. collection of wild orchids for export),
land conversion (logging and shifting cultivation) and habitat
fragmentation. Furthermore, previous efforts and current activities
on the genetic improvement and/or breeding of forest species
in the Philippines are few and largely fragmented. The country
doesn’t have a national tree improvement program as yet to tie in
all the initiatives on forest genetic improvement including forest
genetic resources conservation.
There are several types of organizations that are known to be
conducting field and laboratory works on forest genetic resources
conservation. These are the Department of Environment and Natural
Resources through its Ecosystems Research and Development
Bureau and its regional field research units (Ecosystems Research
and Development Services), the academic institutions (e.g. the
UPLB, the Visayas State University in Leyte Province, and other
state colleges and universities), conservation-oriented NGOs
Philippines
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Country Report on Forest Genetic Resources
Executive
Summary
and a few private wood industries in the past. The government’s
NIPAS program is a positive force in the efforts towards in-situ
conservation of FGR. The recently launched National Greening
Program seeks to contribute to ex-situ conservation. There are
few organizations that have undertaken serious FGR conservation
initiatives with some being national in scope. The achievements
of these organizations and their programs are potential building
blocks for reinforcing FGR conservation efforts in the country in
the future.
Institutionally, the Philippines has also established the structure
to guarantee the continuity of initiatives towards the conservation
of forest genetic resources in the country. Various laws have
been enacted and local ordinances have been promulgated that
are designed to safeguard such resources. These efforts are
complemented by a continuing program on information, education,
and communication designed to promote the conservation of forest
genetic resources.
The Philippines is also a party to a number of multilateral
environmental agreements (MEAs) which aims to conserve and
sustainably use biological diversity. These include the United
Nations Environment Programme (UNEP) Convention on Biological
Diversity (CBD), the Cartagena Protocol on Biosafety, and the
Convention on International Trade of Endangered Species of
Wild Fauna and Flora (CITES). In like manner, the country is a
member of international organizations whose thrusts include the
sustainable use of FGR like the IUFRO and the APAFRI and has
been collaborating with regional initiatives whose objectives are
to seek better understanding of FGR related topics. The latter
includes the International Neem Network, the ASEAN Peatland
Forests Project, and the ASEAN Biodiversity Centre. All these
involvements have given a boost to the government’s efforts
geared towards implementing programs and projects designed to
create better appreciation of the value of and the need to conserve
and sustainably use the country’s forest genetic resources.
The formulation and implementation of a National Forest Tree
Improvement Program is an imperative to tie in all the past and
present efforts on the conservation and the sustainable use of
country’s forest genetic resources.
This report also highlights the wealth of the Philippines in terms
of its forest genetic resources. From its forests comes a multitude
of goods – food, wood, medicine and “cosmeceuticals”, non-wood
forest products, and raw materials for the handicrafts and novelty
items. Methods are now evolving towards the effective valuing of
the services that come with the sustainable management of the
forest genetic resources. With this development is the increasing
appreciation of the concept of payment for environmental services
that will work towards more vigorous efforts towards the sustainable
Philippines
Country Report on Forest Genetic Resources
xi
use of such resources. In the Philippines too, current interest on
REDD+ very well complements the thrust on the conservation of
existing forest genetic resources of the nation.
Executive
Summary
In the face of such developments are challenges that the country
will have to address to further the moves towards such conservation
efforts. These include the need for more skills and knowledge
on forest genetic resources among the country’s environmental
managers and the general public, the conduct of more scientific
studies aimed at generating additional basic knowledge on forest
genetic resources and producing better technologies to address
the regeneration of the same including more efficient utilization
schemes, the need for more surveys of the protected areas in
the country, establishment of more facilities for the ex-situ
conservation of forest genetic resources, and the implementation
of an efficient and effective monitoring system of conservation
priority protected areas.
Philippines
xii
Country Report on Forest Genetic Resources
Contents
iii
Foreword
v
Preface
vii
Executive Summary
xv
List of Tables
xvi
List of Figures
xvii
List of Appendix Tables
xviii
List of Acronyms
1
Introduction
2
Basic Geographic Description
3
Climate and Weather Conditions
4
Topographic Features
4
Population and Economy
4
The Philippine Forestry Sector
6
References
7
Chapter 1. The Current State of Philippine Forest Genetic
Resources
7
Introduction
7
Types of Forest Vegetations and their Genetic Resources
10
Forest Resources
11
Factors Influencing the State of Forest Genetic Resources
12
Current and Emerging Technologies
14
Main Value of Forest Genetic Resources
16
References
19
Chapter 2. In Situ Genetic Conservation
19
In Situ Conservation in Protected Forest Areas
20
In Situ Conservation in Production Areas
22
Priority In Situ Conservation Areas
22
Constraints to In Situ Conservation
23
Priority R & D Areas for In Situ Conservation
Philippines
Country Report on Forest Genetic Resources
xiii
24
Capacity Building Needs
24
References
27
Chapter 3. Ex Situ Genetic Conservation
27
Field Genebanks and Plantations
28
Botanical Gardens
29
Seed Banks, Clone Banks, and In Vitro Genebanks
30
Plant Rescue
30
Clonal Propagation
31
Research Gaps
33
Education and Training
33
References
35
Chapter 4. The State of Use and Sustainable Management
of Forest Genetic Resources
35
Utilization of Conserved Forest Genetic Resources and the
Major Constrains to their Use
36
The State of Forest Genetic Improvement and Breeding Program
37
Tree Improvement
38
Seed Production Areas
39
Seed Orchards
40
Species and Provenance Trials
41
Seed Collection, Processing, Storage, and Distribution
42
Research and Development Activities
44
Mass Propagation of Improved Varieties
46
References
51
Chapter 5. The State of National Programs, Research,
Education, Training and Legislation
51
The Department of Environment and Natural Resources
52
National Programs on Forest Genetic Resources Conservation
55
Research, Education and Training
62
Legislation
67
Needs for Developing Forest Genetic Resources Legislation
67
References
69
Chapter 6. The State of Regional and International
Collaboration
69
Regional and Sub-Regional Collaborations
70
International Collaborations
72
Needs and Priorities for Future International Collaboration
Philippines
xiv
Country Report on Forest Genetic Resources
75
Chapter 7. Access to Forest Genetic Resources and
Sharing of Benefits Arising from their Use
76
International Agreements
77
National Legislations and Policies
81
Chapter 8. The Contribution of Forest Genetic Resources
to Food and Health Security, Poverty
Alleviation, and Sustainable Development
81
FGR Contribution to Food and Health Security, Poverty
Alleviation, and Sustainable Development
81
Philippine Wildfood Plants
82
Contribution to Health and Security
82
Forest Based Industries/Activities Supporting Poverty alleviation
85
Initiatives towards sustainable development and people-oriented
forest development program
89
Issues and challenges
89
References
Philippines
Country Report on Forest Genetic Resources
xv
Tables
Page
Table No.
Title
2
1
Philippine forest cover as of 2010
5
2
Breakdown of Philippine forests into types
10
3
Forest ownership and area
15
4
Summary of number of threatened Philippine plants
per category
16
5
Annual quantity of seeds produced and current state
of identification of forest reproductive material of the
main forest tree and other woody species in country
17
6
Annual number of seedlings (or vegetative propagules) planted and the state of identification of the
reproductive material used for the main forest tree
and other woody species in the country
20
7
Summary of proclaimed protected areas in the
Philippines
28
8
Species found in the Mangrove Genebank at
Pagbilao, Quezon
29
9
Botanic gardens in the Philippines
30
10
Summary of Acacia mangium seeds records and
acquisition by PTFI-SMH in Mindoro oriental
31
11
Provenances and Seedlots of Acacia mangium used
in PTFI-Talacogon Plantation
32
12
Summary of dipterocarp species planted in the ERDB
hedge garden
45
13
Tree species studied using tissue culture in the
Philippines
67
14
Needs for developing forest genetic resources
legislation
73
15
Needs and priorities of the Philippines for
international collaboration on forest genetic
resources
88
16
Various forest tenurial instruments implemented, as
of 2010
Philippines
xvi
Country Report on Forest Genetic Resources
Figures
Page
Table No.
Title
2
1
The location of the Philippines in Southeast Asia
3
2
Climate types in the Philippines
5
3
Extent of forest cover in the Philippines from 1990
to 2010
5
4
Development of forest plantations in the
Philippines from 1990 to 2010
51
5
Forest genetic conservation and management
framework showing both the in situ and ex situ
strategies (Pollisco, 2009).
Philippines
Country Report on Forest Genetic Resources
xvii
Appendix Tables
Page
Appendix
Table No.
Title
11
1
Forest species in the Philippines with
economic importance and/or uses
93
2
Forest species used for plantation,
agroforestry or enrichment planting in natural
forests
96
3
Main tree and other woody forest species
providing environmental services or social
values 104
97
4
List of tree and other woody forest species
considered to be critically endangered in all or
part of their range from genetic conservation
point of view
103
5
List of forest species whose genetic variability
has been evaluated
105
6
Priority areas for plant conservation
(Important Plant Areas or Important Plant
Sites (DENR–PAWB, CI, & UP–CIDS 2002)
108
7
Potential seed production areas/seed sources
by region
112
8
Policy issuances related to forest genetic
resources conservation and sustainable use
promulgated by the Philippine government
120
9
Wildfood plants in the Philippines forest
129
10
Forest species used as raw materials for
holiday decors, wearables, gifts, and other
novelty items
Philippines
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Country Report on Forest Genetic Resources
List of Acronyms
ACB
ADB
AFFLA
AFTA
APAFRI
APFP
ASEAN
ATSAL
ATSC
BFI
BK
BMS
CADT
CALT
CBD
CBFM
CBFMP
CBFMA
CDM
CFNR
CFP
CIA
CITES
COP
CPPAP
C&I
CSC
CSIRO
CSO
DAO
DENR
DOST
EC
EO
ERDB
ERDS
EU
FAO
FGR
ASEAN Centre for Biodiversity
Asian Development Bank
Agroforestry Farm Lease Agreement
ASEAN Free Trade Area
Asia Pacific Association of Forest Research Institutions
ASEAN Peatland Forests Project
Association of Southeast Asian Nations
Agroforestry Tree Seed Association of Lantapan
Australian Tree Seed Centre
Bukidnon Forests, Inc.
Bantay Kalikasan
Biodiversity Monitoring System
Certificate of Ancestral Domain Title
Certificate of Ancestral Land Title
Convention on Biological Diversity
Community Based Forest Management
Community-Based Forest Management Program
Community Based Forest Management Agreement
Clean Development Mechanism
College of Forestry and Natural Resources
Community Forestry Program
Central Intelligence Agency
Convention on International Trade of Endangered Species
of Wild Flora and Fauna
Conference of Parties
Conservation of Priority Protected Areas Project
Criteria and Indicator
Certificate of Stewardship Contract
Commonwealth Scientific and Industrial Research Organization
Clonal Seed Orchard
DENR Administrative Order
Department of Environment and Natural Resources
Department of Science and Technology
European Commission
Executive Order
Ecosystems Research and Development Bureau
Ecosystems Research and Development Services
European Union
Food and Agriculture Organization of the United Nations
Forest Genetic Resources
Philippines
Country Report on Forest Genetic Resources
FLD
FLAgT
FLGMA
FMB
FORTIP
FPE
FRA
FPRDI
GDP
GEF
GMO
GO
ICC
ICRAF
IEC
IFMA
INBAR
IPA
IPB
IPRA
IPS
IRR
ITPLA
ITTO
IUCN
LGU
MBG
MEA
MIS
NAMRIA
NCIP
NEDA
NEP
NIPAS
NIPAP
NGOs
NGP
NIA
NPC
OGAs
PA
PACBRMA
PAMB
PAMP
PAWB
PCARRD
PCHM
xix
Forest & Landscape Denmark
Forest Land use Agreement for Tourism
Forest Land Grazing Management Agreement
Forest Management Bureau
Regional Project on Improved Productivity of Man-Made
Forests Through Application of Technological Advances in
Tree Breeding and Propagation
Foundation for Philippine Environment
Forest Resources Assessment
Forest Products Research and Development Institute
Gross Domestic Product
Global Environment Facility
Genetically Modified Organisms
Government Organization
Indigenous Cultural Communities
The World Agroforestry Centre
Information, Education, and Communication
Integrated Forest Management Agreement
International Network for Bamboo and Rattan
Important Plant Area
Institute of Plant Breeding
Indigenous Peoples’ Rights Act
Important Plant Site
Implementing Rules and Regulations
Industrial Tree Plantation License Agreement
International Tropical Timber Organization
International Union for the Conservation of Nature and Natural
Resources
Local government unit
Makiling Botanic Gardens
Multilateral Environmental Agreements
Management Information System
National Mapping and Resources Inventory Authority
National Commission on Indigenous People
National Economic Development Authority
National Ecotourism Plan
National Integrated Protected Areas System
National Integrated Protected Areas Project
Non-government Organizations
National Greening Project
National Irrigation Administration
National Power Corporation
Other government agencies
Protected Area
Protected Area Community-Based Resource Management
Agreement
Protected Area Management Board
Protected Area Management Plan
Protected Areas and Wildlife Bureau
Philippine Council for Agriculture, Forestry and Natural Resources
Research and Development
Philippine Clearing House Mechanism for Biodiversity
Philippines
xx
Country Report on Forest Genetic Resources
PCSD
PICOP
PES
PNG
PNOC
PSLP
PTFCF
PTFI
RA
RDE
REDD
RP
R&D
SBMA
SCU
SIBF
SIBP
SIFMA
SINP
SLP
SFM
SME
SoW-FGR
SPA
SSO
SUDECOR
SUSTEC
TFLA
TLAs
UNDP
UNEP
UNFCC
UP
UPLB
USD
USDA
WB
WTO
WWF
Philippine Council for Sustainable Development
Paper Industries Corporation of the Philippines
Payment for Environmental Service
Papua New Guinea
Philippine National Oil Corporation
Public Sector Linkage Program
Philippine Tropical Forest Conservation Foundation
Provident Tree Farms, Inc.
Republic Act
Research, Development, and Extension
Reducing Emissions from Deforestation and Forest Degradation
Republic of the Philippines
Research and Development
Subic Bay Metropolitan Authority
State, colleges , and universities
Samar Island Biodiversity Foundation
Samar Island Biodiversity Program
Socialized industrial Forest Management Agreement
Samar Island Natural Park
Special Land use Permit
Sustainable Forest Management
Small and Medium Enterprises
State of the World’s Forest Genetic Resources
Seed Production Area
Seedling Seed Orchard
Surigao Development Corporation
Sustainable Ecosystems International Corporation
Tree Farm Lease Agreement
Timber License Agreements
United Nations Development Programme
United Nations Environment Programme
United Nations Framework Convention on Climate Change
University of the Philippines
University of the Philippines Los Baňos
United States Dollars
United States Department of Agriculture
World Bank
World Trade Organization
World Wildlife Fund
Philippines
Country Report on Forest Genetic Resources
1
Introduction
F
orest genetic resources have long played a
key role in the history of the world. Significant
events in the past have seen how mankind has
been intricately woven with the forests of the
world and all the resources thereat. It is no
wonder then that the phenomenal increase in
the global population has been accompanied
by the continuous diminution of the forests
of the world. And with the shrinkage of the
forests is the inevitable reduction or even the
virtual loss of valuable genetic resources in
the said areas.
In this report, forest genetic resources
represent the entire “genetic variation in trees
which are of potential or present benefit to
humans” (FAO, 1989). The FAO, the Forest
& Landscape Denmark, and the International
Plant Genetic Resources Institute, now the
Bioversity International (FAO, FLD, IPGRI,
2004) define forest as denoting a stand,
population or landscape of trees, and typically
other associated woody plants. The term
genetic in the same report refers to “variation of
genetic (DNA) origin, and variation of genes at
different levels: (1) variation between species,
(2) variation between populations within
species and (3) variation between individual
trees within populations. The largest variation
is between species, and loss of whole species
is therefore also the most dramatic loss of
future options.” Finally, resources refers to the
“use of genetic variation—in the broad sense
stated above—considered to be of potential
value for humans at present or in the future.”
These concepts are adopted in this report.
The need to conserve forest genetic resources
has long been seriously recognized. Taking
the lead in the efforts to stem the tide of
the continuous loss of and/or conserve the
world’s forest genetic resources is the Food
and Agriculture Organization (FAO) of the
United Nations which has organized the Panel
of Experts on Forest Gene Resources or the
Forest Gene Panel as early as 1967. This
urgent concern was further translated into
action with the FAO Commission on Genetic
Resources for Food and Agriculture agreeing
on the preparation of a report on “The State
of the World’s Forest Genetic Resources.”
The global report will draw from the country
reports that shall be prepared by the member
countries. This is the Country Report on the
Forest Genetic Resources of the Philippines.
This country report was prepared in accordance
with the Guidelines for the Preparation of
Country Reports for the State of the World’s
Forest Resources prepared by the FAO. The
FAO designed the Country Reports to cover
genetic resources of environmental, economic,
social and cultural values. Specifically, the
country reports were expected to bring
insights on current management activities of
forest genetic resources, in-situ and ex-situ
genetic conservation as well as improvement
and breeding activities, support facilities, and
participation and/or involvement in regional
and international cooperation and collaboration
pertaining to forest genetic resources, and
capacity building needs on both knowledge
and genetic resources management.
In keeping with the guidelines, this report
is an attempt to assess the state of the
Philippine’s forest genetic resources and their
roles and values. In the assessment, “aspects
Philippines
2
Country Report on Forest Genetic Resources
of forest biodiversity, the production systems
and the environment in which these resources
are used, the range of products and services
which they provide, the consumption patterns
and socio-cultural practices associated with
them, the ecosystem functions which they
sustain and their roles in achieving sustainable
forest management, food security and poverty
alleviation” were likewise discussed.
Researchers and technical staff of the Ecosystems Research and Development Bureau
(ERDB) of the Department of Environment and
Natural Resources (DENR) spearheaded the
preparation of the report. Initially, an extensive
literature search and retrieval of documents
from research and development organizations
in the country, as well as academic institutions
engaged in activities on forest genetic
resources conservation and management
and related fields. The information
collected were then consolidated
and formed the bases in writing the
draft of the country report. This was
also referred to the DENR Regional
Research Sectors nationwide for
comments and improvement. A
National Consultative Workshop on
the State of the Philippine Forest
Genetic
Resources
(FGR)
was
then convened for the purpose of
validating and enriching further the
contents of the draft country report.
Key researchers and staff from the
ERDB and other scientists whose
expertise and experiences relate to
FGR participated during the National
Workshop. The draft country report
was presented in a plenary session.
Discussion groups were formed
and each chapter of the draft
country report was comprehensively
assessed as to the contents. The
country report was finalized with
inputs from the national workshop.
about 1,000 kilometers from the southeast
coast of the mainland of Asia. It lies between
21°20’ north and 4°30’ north latitude and
116°55’ east and 126°36’ east longitude (Fig.
1). It is bounded on the west and north by the
South China Sea, on the east by the Pacific
Ocean; and on the South by the Celebes Sea
and the coastal waters of Borneo. The country
straddles important shipping lanes both in the
China Sea and the Pacific Ocean making it
a strategic location for trading of goods and
other commercial activities . This is the reason
why the Philippines is sometimes referred to
as the “Pearl of the Orient Seas.”
With its total land area of 115,830 square miles
(300,000 square kilometers), it constitutes
two percent of the total land area of the world
and is classified as a medium sized country.
The entire archipelago of 7,107 islands is
Basic Geographic Description
Forming part of the Southeast Asian
region, the Philippines is located
Fig. 1.
The location of the Philippines in
Southeast Asia.
Philippines
Country Report on Forest Genetic Resources
divided into three major island groups, Luzon,
Visayas, and Mindanao. The largest island of
Luzon is where the capital city of Manila is
located. It is also the most populous among the
island groups. Industrial activities are mostly
concentrated in the regions surrounding Metro
Manila, as well as in the central part of the
Philippines, particularly in the Island of Cebu
in the Visayas.
Climate and Weather Conditions
Using temperature and rainfall as bases, the
climate of the country can be divided into two
major seasons: (1) the rainy season, from
June to November; and (2) the dry season,
from December to May. The dry season may
be subdivided further into (a) the cool dry
season, from December to February; and (b)
the hot dry season, from March to May. Based
on the distribution of rainfall, four climate
types are recognized. The description of each
type and the prevailing types in the different
regions of the country are described in Fig. 2).
3
Based on the average of all weather stations in
the Philippines, excluding the City of Baguio,
the mean annual temperature is 26.6°C.
The coolest month is January with a mean
temperature of 25.5°C while the warmest
month occurs in May with a mean temperature
of 28.3°C. Latitude is an insignificant factor
in the variation of temperature while altitude
shows greater contrast in temperature.
The difference between the mean annual
temperature of the southernmost station in
Zamboanga and that of the northernmost
station in Laoag City is insignificant. In other
words, there is essentially no difference in
the mean annual temperature of places in
the island groups of Luzon, the Visayas, or
Mindanao measured at or near sea level.
The Philippines has a high prevailing relative
humidity throughout the year mainly due to
high temperatures and the surrounding bodies
of water. The average monthly relative humidity varies between 71 percent in March and
85 percent in September. The combination of
warm temperature and high relative and absolute humidities give rise to
high sensible temperatures
throughout the archipelago.
It is especially uncomfortable during March to May,
when temperature and humidity attain their maximum levels.
The mean annual rainfall of
the Philippines varies from
965 to 4,064 millimeters
an-nually.
Baguio
City,
eastern Samar, and eastern Surigao receive the
greatest amount of rainfall
while the southern portion
of Cotabato receives the
least amount of rain. At
General Santos City in
Cotabato,
the
average
annual rainfall is only 978
millimeters.
Fig. 2. Climate types in the Philippines.
Philippines
4
Country Report on Forest Genetic Resources
The Philippines is often visited by tropical cyclones which exert a great influence on the
climate and weather conditions of the country.
A huge portion of the rainfall, humidity and
cloudiness are due to the influence of these
weather disturbances that generally originate
from the east in the region of the Marianas
and Caroline Islands of the Pacific Ocean which
have the same latitudinal location as Mindanao. Their movements follow a northwesterly
direction, sparing Mindanao from being directly hit by majority of the typhoons that cross
the country.
org/wiki/Geography_of_the_Philippines_30
December 2011).
The country's most extensive river systems
are the Pulangi River, which flows into the
Mindanao River (Rio Grande de Mindanao); the
Agusan, in Mindanao which flows north into
the Mindanao Sea; the Cagayan in northern
Luzon; and the Pampanga, which flows south
from east Central Luzon into Manila Bay.
Laguna de Bay, east of Manila Bay, is the largest
freshwater lake in the Philippines. Several
rivers have been harnessed for hydroelectric
power.
Topographic Features
Population and Economy
Topographically, the Philippines is broken up
by the sea, which gives it one of the longest
coastlines of any nation in the world. Most
Filipinos live on or near the coast, where
they can easily supplement their diet from
approximately 2,000 species of fish. Off the
coast of eastern Mindanao is the Philippines
Through, which descends to a depth of 10,430
meters. The Philippines is part of a western
Pacific arc system that is characterized by
active volcanoes. Among the most notable
peaks are Mount Mayon near Legazpi City,
Taal Volcano south of Manila, and Mount Apo
on Mindanao. All of the Philippine islands are
prone to earthquakes. The northern Luzon
highlands, or Cordillera Central, rise to between
2,500 and 2,750 meters, and, together with
the Sierra Madre in the northeastern portion of
Luzon and the mountains of Mindanao, boast of
rain forests that provide refuge for numerous
upland tribal groups. (http://en.wikipedia.
In the year 2008, the Philippines has a
population density of 303 people km2, and an
annual population growth rate of 1.8% (FAO,
2010). It was also estimated that of the total
population, 35% lives in the rural areas. In
the same year, per capita GDP in the country
was determined at 3, 513 USD with an annual
growth rate of 3.8%.
The Philippine Forestry Sector
The Global Forest Resources Assessment of the
FAO (2010) estimated that the Philippine forests
cover an area of 7,665,000 hectares or 26%
of the total land area of the Philippines (Table
1). Other wooded lands occupy 10,128,000
hectares or 34% of the total land mass.
From 1990 onwards, a progressive increase in
forest cover has been observed (Fig. 3) from
Table 1. Philippine forest cover as of 2010 (FAO, 2010).
Total Land Area (1000 square kilometers)
Total Forest Area (1000 ha)
Percent Forest Cover
Primary Forest Cover (1000 ha)
Primary Forest, % total forest
Other wooded land (1000 ha)
Other wooded land % total forest
Philippines
Area (1,000 has.)
29817
7665
26
861
11
10128
34
Country Report on Forest Genetic Resources
Fig. 3.
Extent of forest cover in the
Philippines from 1990 to 2010.
6,775,000 hectares to 7,665,000 hectares
(FAO, 2010).
Naturally regenerated forests occupy the
bulk (84%) of the total forest area in the
country (Table 2). The old growth forests in
the Philippines account for 11% of the total
forest area with 861,000 hectares. The rest
are established forest plantations with an area
of 352,000 hectares (5% of the total forest
area). The large bulk of the plantations (99%)
are planted with exotic species (Eucalyptus,
Acacias, Paraserianthes falcataria, Gmelina
arborea, and Swietennia macrophylla). Over
the years, the area of the planted forests has
Fig. 4.
Development of forest
plantations in the Philippines
from 1990 to 2010.
also increased (Fig. 4).
The FAO Global Forest Resource Assessment of
2010 also indicated that 76%, 8%, and 16% of
the forests of the country are primarily devoted
to production, soil and water protec-tion/
conservation, and biodiversity conserva-tion,
respectively. Furthermore, 85% of the forests
are publicly owned and the rest are of private
ownership. Of the total forest area, 24% or
1,804,000 hectares are within protected areas
and that 29% (2,250,000 hectares) are being
utilized under existing fo-rest management
plans, either by the government, or the private
sector.
Table 2. Breakdown of Philippine forests into types (FAO, 2010).
Forest Type
Area
Primary forest (1000 ha / % of forest area)
Other naturally regenerated forest
(1000 ha | % of forest area)
Planted Forest (1000 ha / % of forest area)
5
%
Total Area
861
11
6452
84
352
5
Philippines
6
Country Report on Forest Genetic Resources
References
FAO, FLD, IPGRI. 2004. Forest genetic resources
conservation and management. Vol.
1: Overview, concepts and some
systematic approaches. International
Plant Genetic Resources Institute,
Rome, Italy.
Internet
http://en.wikipedia.org/wiki/Geography_of_
the_Philippines
http://www.fao.org/forestry/fra/fra2010/en/
http://kidlat.pagasa.dost.gov.ph/cab/climate.
htm
Philippines
Country Report on Forest Genetic Resources
7
Chapter 1
The Current State of Philippine
Forest Genetic Resources
forest losses but also the degradation of forest
genetic resources (FGR).
Introduction
T
he Philippines lies just above the equator
between 21°20’ north and 4°30’ north
latitude and 116°55’ east and 126°36’ east
longitude and is made up of over 7,107 islands.
Of the total land area, 94% comes from the
11 largest islands. The land area is 300,000
square kilometres (sq km) or 30,000,000
hectares (ha). Water within the land occupies
an area of 1,830 sq km. The coastline
measures 36,289 km. The prevailing climate is
tropical rain monsoon from November to April
and Southwest monsoon from May to October.
There are only two seasons, wet and dry as
per the monsoon rains. The terrain is mostly
mountainous with narrow coastal lowlands.
Natural hazards include 20-22 cyclonic typhoons
per year, landslides, flooding, active volcanoes,
destructive earthquakes and tsunamis. Current
environmental issues include uncontrolled
deforestation especially in watershed areas,
soil erosion, air and water pollution in major
urban areas, coral reef degradation, and
increasing pollution of coastal mangrove
swamps that are important as fish breeding
grounds.
The pressures of a growing population which
has reached 101,833,938 million people
(CIA, 2011) have resulted in much of these
forests being cleared for shifting cultivation,
cash cropping, fuelwood collection, livestock
grazing, unsustainable logging and the
frequent occurrences of anthropogenic fires.
Rapid urbanization vis-a-vis land conversion
developments has further escalated not only
Types of Forest Vegetations and their
Genetic Resources
Lowland evergreen rain forest
This is the most common of the tropical rain
forests in the Philippines which includes the
Dipterocarps and the mixed Dipterocarps. It
could be found at elevations from 0 to 900 m
above sea level and is well observed in sites
with evenly distributed rainfall or those with
short dry season. This forest type is situated
along the typhoon belt. The canopy structures
are diffused and allow more light penetration
in the understory. These light conditions
promote a dense growth of rattans, lianas,
epiphytes and herbaceous plants on the forest
floor and arecoid tree palms and seedlings and
saplings as emergents.
Semi-evergreen rain forest
These forests are dominated by a single dipterocarp species, Dipterocarpus grandiflorus or
Shorea contorta. This forest type is found in
the western side of the archipelago including
the provinces of Palawan and Zambales in
Luzon which have seasonally dry climate.
Semi-deciduous forest
The species growing in this forest type
are capable of growing in water-stressed
conditions. They are often on the leeward side
Philippines
8
Country Report on Forest Genetic Resources
of the mountains or on dry coastal hills. In
western Mindoro, this forest type is dominated
by Pterocarpus indicus, Intsia bijuga, Toona
calantas, Koordersiodendron pinnatum, Pometia
pinnata, Dipterocarpus validus, Bischofia
javanica and Alstonia scholaris. Vitex parviflora
dominates this forest type in the northwestern
coastal hills of Luzon and near the East coast
of Mindoro. Associated species include
Wallaceodendron celebicum, Litchi chinensis
ssp. philippinensis, Pterocarpus indicus,
Intsia bijuga, Lagerstroemia piriformis, and
Kingiodendron alternifolium. In Palawan,
patches of this formation are still present
in the Irawan Valley, Calauag and south of
Roxas with the common emergents including
Pterocymbium
tinctorium,
Pterospermum
diversifolium, Garuga floribunda and Intsia
bijuga.
flora including among others Planchonella
sp. and the heavy metal indicators Scaevola
micrantha,
Brackenridgea
palustris
and
Exocarpus latifolius. Other tree species include
Neissosperma glomerata and species of
Gymnostoma, Surregada, Archidendron and
Pouteria. The Mt. Victoria area is the largest
region of ultramafic forest in Palawan and
is home to the endemic tree Embolanthera
spicata one of only two species in the genus
(the other being in Indo-China). The ultramafic
forests in north eastern Mindanao are taller,
reaching 15 to 20 m, and include Tristamiopsis
micrantha, Sararanga philippinensis and
Terminalia surigaoensis. In Dinagat Island
and also in the northeastern tip of Mindanao
and Leyte the ultramafic forest contains the
endemic tree Xanthostemon verdugonianus.
Beach forest
Forest over limestone
This formation occupies low, karst limestone
hills, either coastal or bordering large uplifted
river valleys, which are mainly composed of
crystalline covered by a shallow or very thin
soil. A number of leguminous trees are dominant in this formation, namely Afzelia rhomboidea, Sindora supa, Intsia bijuga, Albizia
acle, Wallaceodendron celebicum, Pterocarpus
indicus and Kingiodendron alternifolium. Other
dominant species include Pterocymbium tinctorium, Zizyphus talanai, Toona calantas, Mimusops
elengi, Maranthes corymbosa, Wrightia pubescens ssp. laniti, Lagerstroemia piriformis and
Heritiera sylvatica and such smaller trees as
Diospyros ferrea, Pterospermum diversifolium
and Mallotus floribundus. This formation is apparently similar to the so- called Molave (Vitex
parviflora) forest.
Forest over ultramafic rocks
This forest type occurs in Palawan, Eastern
Isabela and Northern Zambales in Luzon,
northeastern and Southeastern Mindanao
and in Dinagat Island. This forest type is
found on soil high in heavy metals. Some of
the ultramatic forests on Palawan are only
about 2-5 m of height and contain a unique
The principal species occurring in the Philippine
beach forests are Terminalia catappa, Erythrina
orientalis, Barringtonia asiatica, Thespesia
populneoides, Hibiscus tiliaceus, Calophyllum
inophyllum, Pongamia pinnata, Tournefortia
argentea, Casuarina equisetifolia and Scaevola
frutescens. They are usually found along the
sandy beaches of seacoasts. Terminalia catappa may occur in small patches of pure stands.
Dendrolobium umbellatum and Pandanus doratissimus also occur commonly in the beach
forest. On the accreting sand there is usually
a narrow strip of herbaceous vegetation dominated by Ipomoea pescaprae.
Mangrove forest
A total of 39 mangrove tree species has been
recorded for the Philippines. The following
are the common and abundant tree species:
Rhizopora apiculata, R. mucronata. Bruguierra
cylindrica, B. gymnorhiza, B. parviflora, B. sexangula, Ceriops decandra, C. tagal, Avicennia
marina, A. officinalis, Sonneratia alba and S.
caseolaris. The seaward side where the soil
is generally mixed with sand or coral limestone is occupied by species of Avicennia and
Sonneratia. Osbornia octodonta of Australian
affinity is the associated species, which forms
Philippines
Country Report on Forest Genetic Resources
almost pure thickets. Rhizophora stylosa also
invades sandy shores and coral terraces and
does not occur inland. On the inner edges of
the mangrove formation the following species
can be found; Bruguierra and Ceriops, as well
as Lumnitzera littorea, L. racemosa, Aegiceras
corniculatum, A. floridum, Camptostemon
philippinense, Scyphiphora hydrophyllacea,
Excoeria agallocha, Heritiera littoralis and
Cerbera manghas. The following species
may be rare to frequent and occur along the
borders: Glochidion littoralis, Dolichandrome
spathacea, Barringtonia racemosa, Xylocarpus
granatum and X. moluccensis. In cut over
areas and along the edges, the swamp fern
Acrostichum aureum and two species of the
spiny scandent Acanthus are prominent. On
the inland edge of the mangrove and the
upper tidal limit of estuaries, extensive pure
stands of Nypa fructicans occur, especially
along water courses.
Peat swamp forest
The importance of the peat swamp forests
in the Philippines has just been recently
appreciated with the participation of the
Philippines in the ASEAN Peatlands Forests
Project. (APFP) The IPAS surveys in 1991
briefly described peatland near Bunawan
in the Agusan Marsh, whilst surveys during
the consultation workshops for the APFP in
November and December 2005 yielded more
information on additional areas of peatlands
in the Agusan Marsh (Caimpugan Peat Dome)
and the Leyte Sab-a Basin peatland. However,
these have mostly been brief studies and there
has been very little or no work on the flora and
fauna of the peatlands, nor their hydrology or
pedology.
The ASEAN Peatlands Forests Project has
reported two areas in the Philippines where
substantial areas of peat have been found: the
Agusan Marsh and the Leyte Sab-a Basin. The
Sab-a Basin is a west-east elongated basin
close to the north coast of Leyte separated
from it by a metamorphic ridge. The total
area is about 3,088 ha of which 44% has
been reclaimed for agriculture. The remaining
9
unutilized peatland (1,740 ha) in the eastern
half of the basin consists of small remnant areas
of swamp forest and sedge/grass peat swamp
(ADB 2000). The two smaller peat basins in the
area Daguitan (210 ha) and Kapiwaran (430
ha) have mostly been converted to agricultural
land.
The Agusan Marsh holds the largest area of
peatland in the Philippines. Two areas of
peatland within the marsh have been confirmed – one just to the north of Bunawan,
the vegetation of which has mostly been
cleared and burned, and the other to the west
of Caimpugan, which exhibits the characteristics of a peat dome, the forest of which is
mostly intact except close to the Hibong River.
This tract of forest is estimated to have an
area of 5,300 hectares. There may be other
areas of peat within the marsh, especially in
Terminalia copelandii/Metroxylon sagu forests
in the northwest portion of the marsh. In a
recent survey led by the late Botanist Leonard
Co, four generic record of plant species have
been made in the Caimpugan Peat Forest.
These are Thoracostachyum cf. sumatranum,
Lepironia articulate, Syzygium zeylanicum,
and Tristaniopsis aff. micrantha (http://www.
aseanpeat.net/index.cfm?&menuid=38)
Freshwater swamp forest
The middle Agusan Valley and west of
Pagalungan, both areas in Mindanao, as well
as the Candaba and Liguasan Marshes, were
cited to have freshwater swamp forests.
Mineral rich fresh water from rivers and
streams regularly and occasionally inundate
this formation. The floristic composition of this
forest type is likely that of Metroxylon sagu a
dominant component. The freshwater swamp
forest is occasionally dominated by Terminalia
copelandii and Nauclea orientalis. Other codominants are Albizia saponaria and Sesbania
cannabina. Common sedges and grasses found
in the marshland include Phragmites vallatoria,
Eriochloa procera, and Scirpodendron ghaeri.
Philippines
10
Country Report on Forest Genetic Resources
Lower montane rain forest
This forest formation found at elevations
ranging from 400 to 950 m and extending
up to 1500 meter above sea level (masl)
is
dominated
by
Shorea
polysperma
together with oaks (Lithocarpus), oil fruits
(Elaeocarpus), laurels (Litsea) and makaasim
(Syzygium). The understory is composed
of epiphytic ferns, herbaceous shrubs of
Rubiaceae (e.g. Psychotria) and Acanthaceae
(e.g Strobilanthes). Sauraria and species
of Urticaceae including climbers such as
Freycinetia are common in gaps and gullies.
Pinus kesiya occurs as a fire climax tree species
in pure stands in the Cordillera Mountains
of Luzon. Pinus merkusii on the other hand,
occurs on the driest sites in Western Mindoro
and Luzon (Zambales and Abra).
Upper montane rain forest
This forest formation considered as mossy
forest occurs in elevations greater than 1,500
m. The topograpy is rough with steep ridges
and canyons. High rainfall pattern and humidity
promote growth of mosses, liverworts, ferns
and other epiphytes on the tree trunks.
Strong winds prevent tall trees; hence, most
of the trees are dwarf. Ferns and grasses
occupy open areas. Dacrydium, Dacrycarpus
and Podocarpus and broad leaf genera such
as Lithocarpus, Symplocos, Engelhardtia,
Syzygium and Myrica are the most common
tree species. Additionally, species of Ericaceae
(Rhododendron, Vaccinium and Diplycosia)
and Melastomataceae (Astronia, Medinilla and
Melastoma) are common, and so is the tree
fern genus Cyathea.
Subalpine forest
Found in very high elevations (2,470-2,587
m asl), the vegetation of subalpine forests
is generally characterized by the dominance
of small, woody dicots with microphylloussclerophyllous leaves which form a low,
dense canopy. This forest formation is found
in the Mt. Halcon-Mt. Sialdang range, in
Mindoro Island and some sites in Mt. Pulag
in Mt. Province, and Mt. Mantalingahan in the
southern portion of the Island of Palawan. The
more common woody dicots in Mt. Sialdang
subalpine rain forest are Styphelia suaveolens,
Rhododendron, Quadrasianum, Vaccinium
myrtoides, Myrica javanica, Leptospermum
flavescens, Taxus sumatrana and Eurya
coriacea. The plant community is quite similar
to those of Mt. Kinabalu (4,101 m) in Borneo
and Mt. Kerinci (3,800 m) in Sumatra).
Forest Resources
The country’s forest is considered among
the richest terrestrial ecosystems in terms of
biological diversity. Flora in the Philippines is
Table 3. Forest ownership and area
Forest ownership
Total Land Area
Alienable and Disposable Land (Private)
Forest Land (Public)
Unclassified Forest Land
Classified Forest Land
Established Timberland
Established Forest Reserves
National parks/GRBS/WA
Civil Reservations
Military Reservations
Fishponds
Area (ha)
30,000,000
14,194,675
15,805,325
755,009
15,050,316
10,056,020
3,270,146
1,340,997
126,130
165,946
91,077
Reference: Forest Management Bureau (DENR). 2009. Philippine Forestry Statistics.
Philippines
% of Area
100.00
47.32
52.68
2.52
50.17
33.52
10.90
4.47
0.42
0.55
0.30
Country Report on Forest Genetic Resources
approximately 14,000 species, which is about
5% of the world’s flora. It is estimated that
there are over 8,000 species of angiosperms,
33 species of gymnosperms,1,100 species of
pteridophytes, 1,271 species of bryophytes,
more than 3,550 species of fungi and molds,
about 1,355 species of algae and 79 species
of lichens. There are 26 genera of flowering
plants and ferns that are endemic to the
Philippines. Flowering plant endemism ranges
from 45% to 60%.
About 15,900,000 ha of the country’s land area
are classified as forest lands. However, only
7,665,000 ha of this area are actually covered
by forest as mentioned earlier. This represents
24% of the total land area or 0.1 ha of forest
per capita (FAO, 2007). This proportion is the
second lowest in the Southeast Asian Region,
higher only to Singapore which does not really
have any forest at all. The optimal forest area
for the Philippines is believed to be about
12,000,000 ha, or 40% of the land area. This
means that an additional 4,832,000 ha of land
should be reforested.
Historically, forest tenure and ownership in the
Philippines was based on the Regalian doctrine
during the colonial period in allocating and
managing its natural resources, including
forest and forest land. The present distribution
of forest ownership in the Philippines is a
result of a series of decentralization from
a highly regulatory and centrally controlled
policies to a more participatory and peopleoriented approach. Table 3 shows the present
distribution and classification of forest
ownership in the Philippines.
Factors Influencing the State of Forest
Genetic Resources
The forestry situation in the Philippines has
been shaped and continues to be shaped by a
number of forces. These drivers of change do
not work separately but often in combination
with one another. One factor creates a
situation which drives another factor to exert
its pressure on the sector.
11
The combination of forces that had tremendous
impact on the forestry sector is rapid population
growth and destructive logging. Many of the
population that had no place else to go in the
lowlands migrated into the uplands. The influx
of people in the uplands was made easier due
to the presence of logging roads and loggedover areas became faster and easier to clear
for agricultural purposes with the use of fire.
This brought destruction to the forest and
during the 1960s the rate of forest destruction
reached as high as 300,000 ha annually. The
Philippines, which has a population growth rate
of 2.35% a year, has yet to come up with an
effective population program. If the situation
is not addressed, it is estimated that the
population will double in 29 years. The intensity
of logging activities has declined because the
forest has deteriorated. The migration into the
forest, however, continues. It is estimated that
the population in the uplands is more than 20
million now.
The economy is also a driver of change. Since
the middle of the 1990s the economy of the
Philippines has been improving. This was
brought about by strides in industrialization
with foreign investors establishing factories
and manufacturing facilities in the country. The
economy has also been helped by the huge
remittances of overseas Filipino workers which
were reported to be more than US$18 billion
in 2010. With the increase in industrialization
many prime agricultural lands were converted
to industrial parks and economic zones. The
increased purchasing power of families of
overseas workers contributed to the increase
in demand for housing. Factory workers
also required housing. Thus, many of the
agricultural lands were also converted to
real estate developments including shopping
centers. However, the industries could not
create enough jobs for the rapidly increasing
population. Many of the displaced farmers and
those who could not find employment in the
urban areas migrated into the uplands.
The improved economic condition of some
families allowed them time for recreation.
They also became aware of the health benefits
Philippines
12
Country Report on Forest Genetic Resources
of forests and made demands for recreational
services. This also resulted in the establishment
by the government of mini-parks especially
in urban areas, the planting of green zones
in government and school grounds and other
open spaces.
Another driver of change that has great
impact on the forestry sector is the energy
situation. The escalating price of fossil
fuel has made the Philippine Government
focus its attention on the development of
alternative sources of fuel. Thus, it passed
the Biofuels Act of 2006 which mandates
the replacement of a certain percentage of
gasoline and diesel with biofuels. To supply
the biofuels the government has started a
program on the development of plantation of
jatropha (Jathropa curcas) as a source of raw
material for biodiesel. The government has
targeted about 2 million hectares of jatropha
plantations in forestlands. In response to this,
the Department of Environment and Natural
Resources (DENR) has allocated 375,000 ha
of open forestlands for this purpose. Since this
area is within forestlands, this certainly will
change the vegetative structure.
The increase in prices of fossil fuel has also
directed the attention of people to the use of
fuelwood for cooking and for industrial uses.
This will certainly aggravate the forestry
situation as more communities will gather
fuelwood from the forest areas. It is expected
that the price of fuelwood and charcoal will
consequently increase the demands for
fuelwood and thus, there will be more fuelwood
collection from the forests. One positive note is
that the government is now contemplating the
establishment of more fuelwood plantations.
With increased prices of fuelwood and charcoal,
the private sector may be encouraged to invest
in fuelwood plantations.
It is also expected that the energy crisis will
see the resurgence of biomass-to-energy
systems that were tried in the late 1970s
and early 1980s. These were not vigorously
pursued because fossil fuel was still cheap
then and the biomass-to-energy systems were
inefficient and expensive to operate. Besides
the biomass-to-energy technologies need improvement.
The deteriorating global environment and in
particular the destruction of forest resources
around the world has generated concern among
governments. This has led to many conventions whose aims are to stop the destruction
of biodiversity and habitats. The Philippines
is partly to many of these conventions. The
nature and progress of the participation of
the country is described in greater detail in
Chapter 7 of this report.
The commitments of the Philippines to improve
the environment of the country and pursue
conservation and protection of biodiversity
and its habitat saw the enactment of a number
of laws one of which is the National Integrated
Protected Areas System (NIPAS) Act (Republic
Act No. 7586) of 1992. The implementation of
this law brought about the establishment of
protected areas. As of July 2007 there were
77 terrestrial protected areas covering 1.85
million ha. Many more areas are lined up for
proclamation as protected areas. Most if not
all of the protected areas have natural second
growth dipterocarp forests as components.
While protected areas could provide protection
and better management of the natural second
growth forest within their boundaries, the
proclamation of protected areas has certainly
reduced the area of natural second growth
forests for timber production.
Current and Emerging Technologies
Technologies are drivers of change and positive
changes in the forestry sector could well be
initiated and sustained by the application of
production and utilization technologies. This
section reviews technologies that when applied
or pursued further in the field could trigger
much awaited positive changes in the sector.
Some technologies developed outside of the
sector could also have tremendous impacts
when applied in the forestry sector.
Philippines
Country Report on Forest Genetic Resources
The success of plantation development often
lies in the right choice of the species, the
quality of seedlings or planting materials,
correct planting procedures, maintenance of
the planted trees including their protection and
the quality of the site. To ensure sustainable
supply of improved seeds, establishment
of seed orchards is necessary. To ensure
production of high quality planting materials,
and get exact replica of the plus trees, cloning
is recommended. Besides, the technology is
the most appropriate alternative propagation
method for species that have limited seed
sources or with seeds difficult to propagate.
Fertilization is a very important component in
successful plantation development. However,
the use of inorganic fertilizer aside from being
expensive could also deteriorate the soil
and pollute water systems. Bio-N has been
developed for agricultural crops particularly
rice, corn and vegetables. It increases the
growth of the root system of the plant by
increasing its ability to absorb soil nutrients
and water resulting in faster growth. Bio-N
has possibilities for use in the nursery during
seedling production and during plantation
establishment thus reducing the cost of
plantation development and faster increased in
forest cover. One kilogram of Bio-N is enough
to fertilize a hectare of rice field, otherwise
needing 4 sacks of inorganic fertilizer for the
same area.
Indigenous mycorrhizal inoculants for seedlings
have been developed for reforestation and
similar activities. The “Mykovam” and the
“Mycogroe” which are based on mycorrhiza,
a fungal association in the roots of plants
have been developed and are now being
mass produced. Their use however needs to
be further promoted in forest development
activities in the country.
Another technology that has been developed
for plantation establishment is computer
software that assists would-be plantation
developers to identify the species suitable
for various sites in the country. This serves
as a guide for plantation development in the
13
country guaranteeing the success of such and
contributing to increased forest cover.
Technologies that expand the resource base
promote sustainable forest management. The
use of species that have not been considered
commercial before has reduced pressure on the
few species that have been traditionally used.
Processing technologies have been developed
for lesser-used species as well as small
diameter logs, tree tops and branches. Nonconventional raw materials such as climbing
bamboos and forest vines have been studied
and technologies developed for their use in
the manufacture of handicrafts. A detailed
discussion on this aspect is made in Chapter
8 of this report. Similarly, the use of these
raw materials will ease pressure on the use of
rattan poles sourced from the natural stands.
In addition to expanding the raw material
base they also provide new opportunities for
livelihood for upland communities through
collection and sale of these raw materials.
In forest product utilization, technologies
have been developed to improve efficiency in
processing, consequently lessening wastages.
The use of such technologies ultimately would
lead to the expansion of the resource base.
Use of alternative species and materials for
handicrafts provides additional materials that
ease pressure on the dwindling resource of
traditional species. Processes that lengthen
the service life of construction materials have
the effect of expanding the resource base since
replacement of these materials is reduced.
Several advances in biotechnology in the forestry
sector could help the sector achieve its goal of
increased forest cover and self-sufficiency in
wood and other forest products. These are in
tissue culture, cloning and organic fertilizers.
Protocols for tissue culture of bamboo, rattan
and a number of plantation tree species have
been developed and field trials of tissue cultured
seedlings have been made. Cloning is already a
well developed technology for the production of
high quality planting materials in the forestry
sector. In fact commercial plantations have
used cloned seedlings. A company has been
Philippines
14
Country Report on Forest Genetic Resources
set up in North Central Mindanao to produce
cloned Gmelina arborea for sale to plantation
developers. The Ecosystems Research and
Development Service (ERDS) of DENR Region
10 particularly the research center in Bukidnon
is now selling cloned Swietenia macrophylla
seedlings.
The challenge in this area is the wider use of
these biotechnologies for the establishment
of forest plantations which will reduce
their development cost and increase their
productivity. This depends on information
campaign by the government on the use of
these technologies by small farmers and large
plantation developers and on the conduct of
further research in these areas.
If the government embarks on a nationwide
campaign based on the use of cloned
seedlings and biofertilizers or the use of
these technologies and appropriate plantation
management in government reforestation
projects, there will be higher survival rates
and better quality of plantations. Furthermore,
if the government provides more funds for
further research on biotechnology there will
be greater chances of improving the forest
cover of the country.
One of the reasons the Philippines had failed
in its forest protection efforts is its inability to
monitor its forest resources at the site level.
Monitoring has been limited to surveillance
of the movement of forest products through
check points and recently through a computerbased monitoring system. The use of satellite
images and/or aerial photographs to monitor
the changes in forest cover of tenure holders
especially the Timber License Agreements
(TLAs) and Integrated Forest Management
Agreements (IFMAs) as well as CommunityBased
Forest
Management
Agreements
(CBFMAs) and those of the military and civil
reservations and other forest managers like
the National Power Corporation (NPC), the
Philippine National Oil Company (PNOC) and
the National Irrigation Administration (NIA)
has not been widely and regularly undertaken.
NAMRIA regularly acquires satellite images
that can be used to monitor changes in forest
cover. The large tenure-holder such as the
TLAs and IFMAs are required to submit to
the DENR aerial photographs of their areas.
These should be used to monitor forest areas
and make the tenure-holders accountable for
whatever unauthorized operations that result
in negative impacts in their areas. The DENR
should be able to institute a corresponding
system of disincentives, sanctions, and
penalties for those who do not protect their
forest or those who abuse the use of their
tenure. Failure to do this will result in further
degradation of the country’s forest resources.
The above technologies improve success in
forest plantation development and thus, the
ability to increase forest cover. They also
increase the efficiency of the utilization of
forest products with the effect of expanding
the resource base. The overall impact is
the conservation of the forest leading to
sustainable forest management.
Main Value of Forest Genetic Resources
The main forest tree species actively managed
for productive purposes are given in Appendix
Table 1. Some of these are trees, while others
are bamboos and rattans. Some are exotics
while others are native to the Philippines.
For their utility; some are used in pulp and
paper, furniture, fuelwood, charcoal, general
construction, plywood, windbreak, erosion
control, tannin, matches, wooden shoes,
reforestation, veneer, medicines (bark and
leaves) mine props, wood carving, cabinets,
basketry, fences, spear and flutes, musical
instruments, cigar boxes, paper making,
bamboo shoots for food, building construction
and handicrafts. Appendix Table 2 shows the
list of species that are commonly used either in
plantation, agroforestry or enrichment planting
(this includes windbreak, shelterbreak, hedgerows, etc.).
The main forest tree species actively managed
or identified for environmental services are in
Appendix Table 3. They are either exotic or
native to the Philippines.
Philippines
Country Report on Forest Genetic Resources
In 2007, the DENR came out with DAO 2007-01
which established a national list of threatened
plants (Table 4). The DAO also prohibited
the collection and trade of species in this
list unless a permit is granted by the DENR
pursuant to the Wildlife Act. (http://chm.ph/
index.php?option=com_content&view=artic
le&id=68:forest-and-mountain-biodiversityoverview&catid=36:biodiversity-in-the-philipp
ines&Itemid=90_30dec2011)
Table 4. Summary of number of
threatened Philippine plants per
category (DAO 2007-01)
Category
Critically endangered
Number of Plant
Species
99
Endangered
187
Vulnerable
176
Other threatened species
Other wildlife species
64
169
Ninety nine (99) species were identified as
critically endangered. Most of these belong
to Family Dipterocarpaceae, Orchidaceae and
Palmae species. Some critically endangered
Dipterocarps are Hopea acuminata, Shorea
astylosa and Vatica pachyphylla. Genus
Paphiopedilumhas the most number of critically endangered species in the Orchidaceae
Family and Genus Hetorospathe and Pinanga
for Palmae. Under the category of endangered, many species belong to Family
Orchidaceae, Cyatheaceae, Asclepiadaceae and
Melastomataceae.
The main forest tree species considered critically endangered in the country are listed in
Appendix Table 4. These include trees, orchids,
ornamental plants and rattans. The trees are
sources of timber, lumber and construction
materials; the orchids and ornamental plants
are for environmental purposes such as for
landscaping/beautification.
A very rough estimate of the quantity of seeds
that have been collected for use by the DENR
15
in its current National Greening Program
indicates a limited number of species yet that
is being used (Table 5). Estimates of seedling
production are also reflected in Table 6.
Some species are exotic such as Acacia mangium, and Gmelina arborea. The list of forest
species for which genetic variability has been
evaluated is shown in Appendix Table 5.
Other noteworthy projects include the following as enumerated in the following sources
from the internet: (http://chm.ph/index.
php?option=com_content&view=article&id=4
00%3Aforest-and-mountain-biodiversity-proj
ects&catid=87&Itemid=90#0_30Dec2011)
• Samar Island Biodiversity Project (SIBP)
• Mt. Apo Natural Park Restoration and Development Cum Livelihood Project
• Cave Management and Conservation Program
• National Ecotourism Programme (NEP) Phase 1
• Mainstreaming Ecotourism in Communitybased Natural and Cultural Resource Management Phase 2
• Developing Ecotourism Strategies for Biodiversity Conservation and Livelihood Opportunities
• Ethnobotanical Study of Plants in Aurora
• Ecological Analysis of the Lamao Forest
Reserve as Ecotourism Site for Biodiversity
Conservation
• Ecosystem Diversity Assessment of Aurora
• Comprehensive Wetland Resource Inventory and Assessment of Vascular Plants in
Casiguran and Dilasag, Aurora
• Expanding and Diversifying National System
Of Terrestrial Protected Areas of the Philippines
(EDNSTPAP) Project
• Vulnerability Assessment of Tignoan
Watershed in Real, Quezon Province
• Visayan Warty Pig (Negros Origin) Conservation Program
• Philippine Cockatoo Conservation Program
• Philippine Tarsier Conservation Program
• Philippine Spotted Deer Conservation Program
• Palawan Wildlife Rescue and Conservation
Center
• Tamaraw Conservation Program
• Philippine Raptors Conservation Project
Philippines
16
Country Report on Forest Genetic Resources
Table 5. Annual quantity of seeds produced and current state of identification
of forest reproductive material of the main forest tree and other woody
species in the country.
Scientific name
Native (N)
or Exotic (E)
Acacia mangium
Alstonia macrophylla
Alstonia scholaris
Bauhinia malabarica
Bauhinia monandra
Cassia javanica
Diploknema ramiflora
Erythrina subumbrans
Eucalyptus urophylla var. urophylla
Eucalyptus urophylla var. wetarensis
Gymnacranthera paniculata
Kibatalia gitingensis
Lagerstreomia speciosa
Myristica elliptica
Oroxylum indicum
Pithecelobium dulce
Planchonella duclitan
Samanea saman
Sesbania grandiflora
Sterculia foetida
E
N
N
E
E
N
N
N
E
E
N
N
N
E
N
E
N
E
N
N
Total quantity
of seeds used
(Kg)
200
400
2
200
2
7
1
9
500
3
9
50
4
5
11
5
3
Quantity of
seeds from
documented
sources
(provenance/
delimited seed
zones)
22
300
500
2
200
2
7
2
370
2
10
500
5
10
50
5
6
14
5
3
Reference: ERDB Seed Laboratory Report 2011 and Seed Production Areas of A. mangium and Eucalyptus spp.
of Science 138 (1): 23-28, June 2009.
ISSN 0031 – 7683.
References
Abasolo M.A., 2007. Genetic diversity of
Parashorea
malaanonan
(Blanco)
Merr. (Dipterocarpaceae) in the Mt
Makiling Forest Reserve Philippines
using microsatellite markers derived
from Shorea species. MSc Plant Genetic
Resources Conservation and Management, Graduate School, University
of the Philippines Los Baños, College,
Laguna. 117 pp.
Abasolo M.A., E.S. Fernando, T.H. Borromeo
and D.M. Hautea. 2009. Cross-Species
Amplification of Shorea Microsatellite
DNA Markers in Parashorea malaanonan
(Dipterocarpaceae). Philippine Journal
Baja-Lapis, A.C., N.M. Calinawan, Ma. T.
Delos Reyes and M.O. Quimado. 2009.
Genetic Variation in Populations of Narra
(Pterocarpus indicus Willd.) from Five
Selected Provinces in the Philippines
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from Oct 05-08, 2009.
Baja-Lapis, A.C.; M.E. David; C.G. Reyes and
B.N. Servas-Audije. 2004. ASEAN Most
Precious Plants. ASEAN Regional Center
for Biodiversity Conservation. 221 p.
Philippines
Country Report on Forest Genetic Resources
17
Table 6. Annual number of seedlings (or vegetative propagules) planted and the
state of identification of the reproductive material used for the main forest
tree and other woody species in the country.
Scientific Name
Acacia mangium
Albizia procera
Alstonia macrophylla
Antidesma bunius
Bauhinia purpurea
Cassia fistula
Cassia spectabilis
Cynometra ramiflora
Diospyros discolor
Dracontomelon dao
Gmelina arborea
Heritierra sylvatiuca
Instia bijuga
Kibatalia gitingensis
Micromelum inodorum
Oroxylum indicum
Parashorea malaanonan
Parkia timoriana
Piliostigma malabaricum
Pittosporum pentandrum
Polyscias florosa
Polyscias nodosa
Ptrocarpus indicus
Samanea saman
Sesbania grandiflora
Swietinia macrophylla
Syzygium nitidum
Syzygium polycephaloides
Terminalia microcarpa
Vitex parviflora
Quantity of seeds Quantity of
Native (N) Total quantity from documented
vegetative
or
of seedlings
sources
reproductive
Exotic (E)
planted
(provenance/ materials used
delimited seed
zones)
E
N
N
N
N
N
N
N
N
N
E
N
N
N
N
N
N
N
N
N
N
N
N
N
N
E
N
N
N
N
4,143
4,728
2,399
4,482
4,055
2,902
13,469
120
10
227
270
304
30
20
49
772
350
1,629
1,500
190
65
12,191
330
15,749
3,314
2,901
10
2,295
1,419
312
4,143
4,728
2,399
4,482
4,055
2,902
13,469
120
10
227
100
304
170
30
20
49
772
350
1,629
1,500
50
140
65
12,191
330
15,749
3,314
2,901
1,885
1,419
312
10
410
Reference: ERDB Seed Laboratory and National Greening Program Reports 2011.
Central Intelligence Agency. 2011. The World
Factbook: Philippines. Updated August
16, 2011, Retrieved August 18, 2011,
from https://www.cia.gov/library/publications/the-world-factbook/geos/
rp.html.
De Guzman N.M. 1996. Mating system of
narra (Pterocarpus indicus Willd.) in Mt
Makiling, Philippines. MS thesis, UPLBCFNR, College, Laguna, Philippines.
De Guzman, B.D.; E.S. Fernando and J.V. Santos.
1986. Guide to Philippine Flora and
Philippines
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Fauna. Natural Resources Management
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University of the Philippines. JMC Press,
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Philippines. 256 pp.
Delos Reyes, Ma.T.A,; A.C. Baja-Lapis and
N.M.
Calinawan.
2010.
Isozyme
Analysis of Palasan (Calamus merrillii
Becc.) from the Provinces of Bukidnon,
Albay, Compostela Valley and Quezon, Philippines Using Starch Gel
Electrophoresis. Paper presented during
the Regional Rattan Conference of the
ITTO- Philippines ASEAN Rattan Project,
ITTO PD 334/05 Rev. 2(1) held at
Dusit Thani Hotel, Ayala Centre, Makati
City, Philippines on 29 August to 01
September, 2010
Delos Reyes, Ma. T. A.; A.C. Baja-Lapis,; N.M.
Calinawan and M.O. Quimado. 2010.
Isozyme Analysis of Limuran (Calamus
ornatus Blume var. philippinensis
Becc.) PALMAE: Calamoideae from
Three Seed Sources in Luzon Island,
Philippines. Paper presented during the
Scientific Forum on Climate Change and
Biotechnology on November 24, 2010
held at the Events Room NIDO Fortified
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Gamboa-Lapitan, P. and Hyun Jo. 2005. Mating
system of Parashorea malaanonan
(M. Blanco) Merr. (Bagtikan) in Mt.
Makiling, Laguna, Philippines. Philipp
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Quimado, M.O. 2002. Characterization of LargeLeaf Mahogany (Swietenia macrophylla
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Polymorphic DNA (RAPD) Markers. PhD
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Quimado, M.O.; A.C. Laurena and AC BajaLapis. 2011. Assessment of Genetic
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Markers. Paper presented during the
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Celebration of the International Year of
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_________.
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ntent&view=article&id=400%3Af
orest-and-mountain-biodiversityprojects&catid=87&Itemid=90#0
Philippines
Country Report on Forest Genetic Resources
19
Chapter 2
In Situ Genetic Conservation
I
n situ or on-site genetic conservation means
the conservation and management of the
species or its populations or individuals in
their original or natural habitats and recovery
of viable populations of species in their natural
surroundings and, in the case of domesticated
or cultivated species, in the surroundings
where they have developed their distinctive
properties.
The establishment of protected forest reserves
has been the main strategy of conserving
forest genetic resources in many parts of
the world. In situ is the preferable longterm genetic conservation solution for most
species and especially those that are rare and
endangered. This is because by dedicating
the sites containing the populations to be
conserved, one is also preserving, in effect, the
set of ecosystems in which the selected species
populations are growing. This then allows for
the continuation of genotype and environment
(GxE) interactions, adaptations, and evolution
of the conserved populations. Thus, the in situ
approach provides for a long-term dynamic
situation wherein the populations continue to
evolve in nature.
In Situ Conservation in Protected Forest
Areas
In situ conservation in protected areas started
in the Philippines as early as 1932, through
the institution of the National Parks System.
In totality, 60 national parks and 8 game
refuges and bird sanctuaries were established
under this system. These parks, refuges
and sanctuaries became a core component
of the National Integrated Protected Areas
System (NIPAS) which was established in
1992 through Republic Act (RA) 7586. The
objective of NIPAS is to “integrate outstanding
remarkable areas and biologically important
public lands that are habitats of rare and
endangered species of plants and animals,
biogeographic zones and related ecosystems
whether terrestrial, wetland or marine, all of
which shall be designated as protected areas”.
The NIPAS is the major legal instrument for
in situ conservation of plant biodiversity in
general in the country (Catibog-Sinha 1994)
and forms a significant component of the
Philippine National Biodiversity Strategy and
Action Plan (PAWB-UNEP 1997). It is worthy
to note that the Philippines has one of the
oldest national park system in South East Asia
established in the early 1900s. The 4,244 ha
Makiling Forest Reserve in Luzon Island is one
of the earliest having been established in 1910.
This and other national parks established
before 1992 became the initial components
of NIPAS. Currently, there are 239 of these
in the NIPAS with a total area of more than
5.42 million ha, including natural parks,
protected landscapes and seascapes, natural
monuments or landmarks, resource reserves,
wildlife sanctuaries, natural biotic areas, and
marine parks and mangrove swamps. Only
about 112 have, thus far, been recognized
under various Presidential Proclamations while
12 has been established through legislative
Philippines
20
Country Report on Forest Genetic Resources
acts. These cover approximately 3.54 million
ha or just 11.8% of the total land area of the
Philippines (Table 7). For the large majority of
the protected areas in the Philippines, there
are no complete inventories of their plant
biodiversity or detailed information on which
rare and threatened species occur in which
protected area. Efforts are being pursued by
country. Thus, in 2000, timber harvesting in
old growth forests, mossy forests, and in those
located in areas over 1,000 m of elevation and
with more than 50% slope was banned by
the Philippine government to conserve forest
genetic resources (FGR).
Although many protected areas in the
Philippines, especially those identified as
initial components of the NIPAS, were not
determined based solely on plant biodiversity
consideration, such, nonetheless, serve as
de facto plant genetic resource conservation
areas or genetic reserves for many commercial
timber trees and other economically important
species that continue to be exploited in the
In situ Conservation in Production Areas
Some programs for the management of the
protected areas in the Philippines
Table 7. Summary of proclaimed protected areas
include the Conservation of
in the Philippines (DENR-PAWB 2011).
Priority Protected Areas Project
(CPPAP) funded by the World Bank
Protected
Buffer Zone
and the Global Environmental
Region
No.
Area
Area
Facility (WB–GEF), the National
(ha)
(ha)
Integrated
Protected
Areas
Program (NIPAP) funded by
Total
112
3,542,967.2
223,843.5
the European Union (EU), and
the Samar Island Biodiversity
Project (SIBP) funded by the
CAR
1
77,561.0
3,465.5
United
Nations
Development
Region I
8
18,455.8
Programme (UNDP) and the
Region II
10
980,235.5
Global
Environmental
Facility
Region III
6
23,989.2
(GEF). Subsequently, other conservation projects have come into
Region IVA
8
79,185.3
reality examples of which are the
Region IVB
10
588,823.4
11,677.0
Administration and Development
Region V
10
31,108.9
of the Hinulugang Taktak ProtecRegion VI
5
154,363.3
169.0
ted Landscape, and Mt Apo
Region VII
9
70,823.8
788.0
Restoration and Development
Poject to name a few. Non-goRegion VIII
10
450,400.0
125,400.0
vernment organiztions such as
Region IX
12
293,966.3
16,593.3
the Haribon Foundation, Inc., the
Region X
9
103,122.1
51,354.7
local network of Conservation
Region XI
8
102,008.9
10,035.5
International, the Foundation for
Region XII
2
231,550.0
Philippine Environment, Philippine
Foundation for Tropical Forests
Region XIII
3
337,351.1
4,360.6
Conservation and many other
NCR
1
22.7
smaller local organizations are
actively
involved
in the restoration and protecthe Philippine Plant Conservation Committee
tion
work.
to address this issue.
Despite the expansion of the network of
protected areas in the Philippines, these remain
very limited in their coverage, especially for
many commercial timber trees of the lowland
dipterocarp forests (Fernando, 2001). A consensus has been growing that protected
areas alone will not be sufficient to effectively
Philippines
Country Report on Forest Genetic Resources
conserve biodiversity and forest tree genetic
resources in the Philippines. For example,
the great bulk of the genetic resources of
commercial timber trees (e.g. dipterocarps)
are not found in currently declared forest
reserves or protected areas. These timber
species are usually restricted to the lowland
rain forests where much of the large-scale
commercial logging in the Philippines has been
undertaken for many decades. The challenge,
therefore, has been to include biodiversity
conservation measures, even as timber is
harvested from natural forests. Many around
the world including the Philippines, have begun
to develop measures to maintain biodiversity
within the practice of forestry.
In the Philippines, the Sustainable Ecosystems
International Corporation (SUSTEC), a nongovernment organization, and the Surigao
Development Corporation (SUDECOR), a
private logging company, in cooperation with
the government’s Department of Environment
and Natural Resources (DENR), undertook a
pioneering work in biodiversity conservation in
a natural tropical rainforest. The International
Tropical Timber Organization (ITTO)-funded
project, although managed primarily for timber production, has shown through empirical
evidence, that forest production and biodiversity conservation can go together to a large
extent. A sustainable forest management plan
was formulated to further improve the biodiversity conservation capacity of the forest
area (ITTO and SUSTEC, 2002).
The sustainable forest management plan and
the guidelines that integrate biodiversity and
genetic resource conservation measures with
timber production are currently being developed, specifically by SUDECOR in its timber
concession areas. The plan includes, among
others, very specific management strategies
for the timber production zone within the
logging concession. There are proposed strict
standards in pre-logging inventory and tree
marking (of trees to be cut) and felling. Among
the specific guidelines being designed are the
following:
(a)
(b)
(c)
(d)
(e)
(f)
21
Tree marking will be governed not only
by the volume, number, class-size of the
trees, and replacement growth rates, but
also by the species and its biodiversity
and genetic resource conservation value.
For instance, tree species characterized
by small populations or restricted distribution (e.g. rare species) will be marked
as trees to be left;
Adherence to the minimum 60 cm diameter breast height requirement for
trees to be cut. The Philippines follows a
selective logging limiting the diameter of
trees to be cut to 60 cm and above;
Deviation from high grading or cutting
of the largest or best trees all the time.
This is to ensure that the phenotypically
superior trees in the site are not
completely depleted;
Exclusion from marking for cutting both
individual flowering and fruiting trees and
those in the priority list for conservation;
Directional felling to minimize damage
to saplings, especially those of timber
species with high commercial value or in
priority list for conservation; and
At least one mother tree of not less than
40 cm dbh per timber tree species per
hectare will be marked as residual.
This is to guarantee that prelogging timber
tree species will continue to exist in the area
and at the same time promoting a better
distribution of tree species across all cutting
areas. This will be on top of the tree-marking
goal estimated for the area (Umali-Garcia
et al. 1998; Fernando and Balatibat, 1998;
Fernando, 2001).
The development and implementation of a
sustainable forest management using the criteria and indicators system was another step
towards a more vigorous conservation effort
for forest genetic resources in the country.
With funding support from the International
Tropical Timber Organization (ITTO), the
DENR through the Forest Management Bureau
implemented a project that led to the development of the Philippine C & I System.
Philippines
22
Country Report on Forest Genetic Resources
In the Philippine C & I System, a set of criteria
has been formulated that should work towards
the attainment of sustainable management of
the concerned forest management unit. In each
criterion, a set of indicators has further been
identified to help identify changes in the forest
being managed. Criterion 5 in the Philippine
Criteria & Indicator System specifically deals
with the maintenance of biological diversity in
the forest management unit.
The conservation of ecosystem diversity can
best be accomplished by the establishment
and management of a system of protected
areas (combinations of IUCN Categories I
to VI) containing representative samples of
all forest types linked as far as possible by
biological corridors or ‘stepping stones’. This
can be ensured by effective land-use policies
and systems for choosing, establishing and
maintaining the integrity of protected areas in
consultation with and through the involvement
of local communities.
The indicators include the following: (1)
Protected areas containing forests; (2)
Protected areas connected by biological
corridors or stepping stones; (3) Existence
and implementation of procedures to identify
and protect endangered, rare and threatened
species of forest flora and fauna; (4) Number
of endangered, rare and threatened forest
dependant species; (5) Measures for in situ
and/or ex situ conservation of the genetic
variation within commercial, endangered, rare
and threatened species of forest flora and
fauna; (6) Existence and implementation of
procedures for protection and monitoring of
biodiversity in production forests by retaining
undisturbed areas, protecting rare, threatened
and endangered species, protecting features
of special biological interest (e.g. nesting sites,
seed trees, niches, keystone species, etc),
and assessing recent changes in (a) to (c), of
previous page through inventories, monitoring/
assessment programs, and comparison with
control areas, and; (7) Extent and percentage
of production forest which has been set aside
for biodiversity conservation.
Priority In Situ Conservation Areas
In 1988, 18 sites were identified by the Threatened Plants Unit at Kew (Cox, 1988) as centers of plant diversity in the Philippines. During the conduct of the Philippine Biodiversity
Conservation Priority Setting Programme in
2002, 43 priority areas for plant conservation
have been listed for the Philippines (Appendix
Table 6). These are usually sites that include
unique threatened habitats, exceptional botanical richness, high in species endemism, or
include rare and endangered species. These
are also referred as Important Plant Areas
(IPAs) (Plantlife International 2004). Of the 88
conservation priority sites for plants or IPAs,
only 39 sites are currently within established
protected areas.
Constraints to In Situ Conservation
Our forest genetic resources are further
threatened
by
over-exploitation
for
commercial purposes (e.g. collection of wild
orchids for export), habitat destruction mainly
caused by land conversion for settlement and
agricultural development, logging and shifting
cultivation or slash-and-burn farming, habitat
fragmentation, forest fire, chemical pollution,
and to some extent mining, energy projects,
pests and diseases (DENR PAWB, 2006).
Another constraint is the threat posed by
non-invasive or alien invasive species due to
the disturbed state of the forest ecosystems.
The 2000 IUCN Red List included 227 species
of such plants in the country. As of 2005 as
earlier mentioned, the Philippine National List
of Threatened Species of Plants prepared by
the DENR-PAWB through the Philippine Plant
Conservation Committee includes 526 species.
Of these, 99 are critically endangered, 187
are in the endangered, 176 vulnerable and 64
other threatened species
Many field personnel lack the necessary
knowledge and skills in identifying thousands
of other plants (and even lower forms of flora,
microflora animals) for conservation and in
appreciating their importance. Information
on inventory and actual state of these plants
Philippines
Country Report on Forest Genetic Resources
is likewise limited. This is critical and could
have formed part of the prescriptions during
forest inventory works as part of the Philippine
Selective Logging System. An actual ground
demarcation of conservation (protected) areas
from the production areas seldom exists.
Protected areas are frequently occupied by
people who practice continuously upland
agriculture. Their numbers are increasing in
some areas. Institutional and management
limitations restrict protection in biodiversityrich areas. Budget constraint and political will
are the common causes of insufficient and
inadequate forest protection programs. The
National Integrated Protected Area System
(NIPAS) and the Indigenous Peoples’ Rights
Act (IPRA) clash with each other in many
respects, particularly along the issues of
actual management, administration, rights of
extraction and exploitation, and protection of
conservation forests. Conflicts in claims and
interests between major stakeholders result
in stalemate in conservation programs. As the
forest genetic resources hang precariously, this
delicate balancing act of harmonizing interests,
claims, vision, policies and programs among
the major stakeholders is sorely longing for
immediate and stable resolution.
With the rapid decline of its habitats, in situ
conservation through the protected areas
system in the Philippines remains as the
best hope for conserving plant biodiversity
and genetic resources. The protected areas,
however, are still limited in their scope, often
excluding lowland dipterocarp forests that
harbor the majority of the commercial timber
trees. The recently identified Conservation
Priority Areas for Plants or Important Plant
Areas not yet covered under the NIPAS must
be integrated into the protected area system.
Sustainable forest management systems
involving integrated and careful planning of
timber harvesting operations that incorporate
plant genetic resource conservation measures
are a promising strategy. Although there is a
high diversity of plant species and habitats
in the Philippines, the financial resources
for plant biodiversity conservation are often
limited.
23
Priority R & D Areas for In Situ
Conservation
The production of planting materials for
endangered, indigenous and other forest
genetic resources and the development of in
situ conservation stands shall be a primary
priority. There is a need for a holistic strategy
for wood production which also prevents the
eminent danger of the irreversible loss of forest
genetic resources. The fundamental problem
to be addressed at this point is the lack of
supply of improved planting materials for
production purposes, and of planting materials
for conservation of endangered indigenous and
other forest genetic resources.
To address the abovementioned concerns,
priority R & D areas for the conservation of
FGR in situ have been identified as follows:
•
•
•
•
•
•
•
Extinction of species and their respective
genetic resources. That is, critical habitats
of Mindoro pine (Pinus merkusii), Philippine
teak (Tectona philipinensis) in Lobo and San
Juan, Batangas and Occ. Mindoro where it is
endemic, narek (Hopea cagayanensis), apitong (Dipterocarpus grandiflorus) in Bohol
and Palawan, and other local endangered
tree species need to be protected;
Specific access and benefit-sharing from
forest biodiversity development; conservation biology and demography or population
studies; on threatened endemic plants,
Research on economically important species;
Periodic assessment of conservation status of all known Philippine plants periodically (e.g. inventory, taxonomy, database
of FGR on in situ conservation sites);
Ecological studies of Important Plant
Sites(IPS) and Important Plant Areas
(IPAs) (carbon sink, watershed and environmental services, ecotourism, genetic
diversity);
Policy assessment and formulation in support of FGRs (e.g. bio-prospecting, rescue
centers) ;
Development of a database for FGRs;
Philippines
24
Country Report on Forest Genetic Resources
Economic valuation studies of FGRs (for bioprospecting purposes, ecological services,
etc.);
Assessment of socio-economic and cultural
practices and their impacts to FGR conservation (e.g. ethno-botany); and
Survey, inventory and mapping of rare and
endangered species.
•
To complement these R & D areas, important
management strategies are needed as follows:
•
•
•
•
•
•
•
•
•
•
•
•
•
•
•
•
•
•
•
•
Prevention of biological pollution;
Ground demarcation of forest lands, e.g.,
production areas, protection areas, restoration areas;
Protection of residual forests and other
conservation areas which are biodiversityrich areas;
Harmonization of the NIPAS Act and the
Indigenous People’s Rights Act (IPRA);
Habitat rehabilitation and restoration;
Management of biodiversity in areas not
declared as protected areas;
Identification and designation Important
Plant Sites (IPS) or Important Plant Areas
(IPA) or in situ Plant Conservation Centers;
Development and implementation of conservation and management plan for each
of the designated IPS. Such plan must
include mechanisms that will ensure active
participation of concerned local government units and other stakeholders; and
Coordination, communication and networking among institutions, scientists and
policy makers on FGR in situ conservation.
More participation by local government
units on conservation activities
More aggressive and sustained IEC on conservation of tree genetic resources
Capacity Building Needs
The capacity-building needed to enhance FGR
conservation in situ are as follows:
•
Education & Training (e.g. skills and
knowledge on species identification and
inventory)
•
•
Public Awareness (Information, Education
and Communication, IEC)
Resource mobilization to support FGR conservation activities
Management Information System (MIS)
Inclusion of FGR conservation in academic
curriculum
Other extension programs – demonstration farms, cross site visits
Strategies on FGR conservation (in situ)
and results of R & D technology
Stakeholders’
participation
in
FGR
conservation
Advocacy of FGR conservation – policy
makers, implementers of conservation
activities, e.g. forest managers, local government units and communities, academe,
research and science community
Policy issues on FGR conservation – Bioprospecting, biosafety
References
Catibog-Sinha, C.C. 1994. Implications of the
NIPAS law for the conservation of forest
genetic resources in the Philippines. In:
Drysdale R. M., John S.E.T. and Yapa
A.C. (Eds.). Proceedings: International
Symposium on genetic conservation
and production of tropical forest tree
seed. ASEAN-Canada Forest Tree Seed
Center Project, Muak Lek, Saraburi,
Thailand. pp. 214–220.
Cox, R. 1988. The Conservation Status of
Biological Resources in the Philippines.
IUCN, Gland, Switzerland.
DENR-PAWB. 2003. Statistics on Philippine
Protected Areas and Wildlife Resources. 234p. Department of Environment
and Natural Resources, Quezon City,
Philippines.
DENR–PAWB. 2004. 2004 Statistics on
Protected Areas and Wildlife Resources.
Department of Environment & Natural
Resources – Protected Areas and
Wildlife Bureau.
Philippines
Country Report on Forest Genetic Resources
DENR–PAWB. 2006. Framework for Philippine
Plant Conservation Strategy and Action
Plan. Department of Environment &
Natural Resources – Protected Areas
and Wildlife Bureau. Quezon Avenue,
Diliman, Quezon City.
DENR–PAWB, CI, & UP–CIDS. 2002. Philippine
Biodiversity Conservation Priorities:
A Second Iteration of the National
Biodiversity Strategy and Action Plan.
113 p. Department of Environment
and Natural Resources, Conservation
International – Philippines, and U.P.
Center for Integrated Development
Studies.
DENR–UNEP. 1997. Philippine Biodiversity:
An Assessment and Action Plan. 298p.
Department of Environment and Natural
Resources and the United Nations
Environment Programme. Bookmark,
Inc., Makati, Philippines.
Fernando, E.S. 2001. Genetic resource
conservation for timber in the Philippines.
In: Thielges BA, Sastrapradja SD,
Rimbawanto A, editors. In situ and
Ex situ Conservation of Commercial
Tropical Trees. International Tropical
Timber Organization and Faculty of
Forestry, Gadjah Mada University,
Yogyakarta, pp 69–82.
25
Plantlife International. 2004. Identifying and
Protecting the World’s Most Important
Plant Areas. 7p. Plantlife International,
Salisbury, U.K.
Tolentino, E.L. Jr. 2009. Status of Philippines
forest genetic resources: their conservation and management practices. In:
Forest Genetic Resources Conservation
and Management: Status in seven South
and Southeast Asian countries. Editors
R. Jalonen, K.Y. Choo, L.T. Hong and
H.C. Sim. A publication of APFORGEN.
FRIM, Bioversity International and
APAFRI. pp. 103-135.
Umali-Garcia M, Melegrito L, dela Cruz R.E.
1998. Vegetative propagation and clonal
testing of different Gmelina arborea
provenances under nursery condition.
In: Proceedings of Joint Seminar of 7th
Annual Bio-Refor and JSPS Scientific
Seminar on “Sustainable Development
of Biotechnology in the Tropics”. Traders
Hotel, Manila. November 3–5, 1998.
Fernando, E.S. and J.B. Balatibat. 1998. Resource inventory and assessment of
biodiversity in the Subic Bay Metropolitan Authority. Annual Report. DOST–
PCARRD–SBMA, Philippines.
ITTO, SUSTEC. 2002. Final technical report
for the conservation and maintenance
of biological diversity in tropical forests
managed primarily for timber production Surigao del Sur, Philippines.
(ITTO Project PD 35/96 Rev 2 (F).
DGSP Graphics Printing, Pasig City,
Philippines. 175p.
Philippines
Country Report on Forest Genetic Resources
27
Chapter 3
Ex Situ Genetic Conservation
E
x situ conservation means the conservation
of species germplasm outside of its
natural habitat. Such conservation stands
serve to capture and maintain genetic
variation in planted gene or seed banks.
Most ex situ collections are active collections
especially those that are being used for
tree improvement wherein accessions are
immediately available for multiplication and
distribution for production, educational and
research uses. Bambusetum, mangrovetum,
palmetum and rattan genebank are examples
of base and active collections because they
serve both purposes of being conserved and
preserved for future use and at the same time
as immediate sources of planting materials for
distribution.
Ex situ conservation efforts for forest genetic
resources in the Philippines generally involve
the establishment of field genebanks or genetic
resources plantations, botanical gardens, and
seed banks.
Field Genebanks and Plantations
The then Paper Industries Corporation of
the Philippines (PICOP), a Timber License
Agreement (TLA) holder in Mindanao was one
of the first few logging concessionaires which
established large-scale forest plantations in
the Philippines to support its own pulp and
paper mill in the early 1970s. The species
in PICOP’s plantations were Swietenia
macrophylla, Pinus caribaea, Gmelina arborea,
Acacia mangium, Falcataria moluccana and
Eucalyptus deglupta. PICOP’s industrial tree
plantations in the 1980s totally covered more
than 46,000 ha of mainly of the last two species
(Reyes 1987). The forest plantations were
supported by PICOP’s own forest research and
tree improvement programs such as species
provenance trials, progeny testing and plus
tree selection for potential mother trees.
However, the company stopped operations
sometime in 2008 due to some legal problems
with the government. Since then, the status
of the plantations has not been monitored.
Undoubtedly, living collections of excellent
genotypes of the different plantation species
which were sources of seeds and materials for
vegetative propagation have already been cut.
A collaborative effort of DENR and the New
Zealand government on plantation development and management gave rise to the
Bukidnon Forest Inc. (BFI). Among its significant contributions is the domestication of
exotic acacias, eucalyptus and pines for planting in open grassland (Imperata cylindrica)
sites. An extensive study on species selection
and suitability of seed origin was conducted.
Based on the two-year results, the most promising species were Acacia aulacocarpa, A.
auriculiformis, A. crassicarpa, A. mangium,
Eucalyptus urophylla, E. camaldulensis, E.
tere-ticornis, E. pellita, E. grandis, E. deglupta, crosses E. deglupta × pellita, E. grandis ×
urophylla, and Pinus caribaea var. hondurensis
and var. bahamensis. Information gathered
from the project revealed that the BFI had
adequate genetic resources of E. urophylla, A.
Philippines
28
Country Report on Forest Genetic Resources
mangium and A. crassicarpa to establish seed
production areas and seedling seed orchards
(Cuevas, 1999; Crizaldo, 1999). In 1997,
the BFI started a trial planting of indigenous
species, such as Shorea contorta, Anisoptera
thurifera and Vitex parviflora (Cuevas 1999).
The plantings are being monitored by BFI staff
for growth and development.
A rattan genebank has been established in a
5-ha area in the ERDB Experimental Forest
in Los Baños, Laguna. It contains 444 rattan
plants composed of 47 taxa of endemic and
exotic species. A duplicate rattan genebank
has been established in Malaybalay, Bukidnon.
and being maintained in Mt. Makiling, Los
Baños, Laguna. (include the location/source of
the propagules)
As an ex situ conservation strategy, a pilot
demonstration area was established in Biñan,
Laguna using eight indigenous species and
application of mycorrhizal isolates and compost.
The species are: ipil (Instia bijuga), akleng
parang (Albizia procera), batino (Alstonia
macrophylla), dungon (Tarrietia sylvatica),
molave (Vitex parviflora), narra (Pterocarpus
indicus), bitaog (Callophyllum inophyllum),
and malapapaya (Polyscias nodosa).
Botanical Gardens
In addition, bambuseta have been established
in Los Baños (6 ha with 29 species), Baguio
City (7 ha with 70 species) and Davao (3 ha
with 32 species) to preserve indigenous and
introduced bamboo species.
Mangrove species are maintained in experimental forest reserves, one of which is in
Pagbilao, Quezon with 17 species (Table 8).
Palms are collectively stored in a palmetum
established in the Los Baños Experiment Station
Table 8. Species found
Pagbilao.
1. Nilad
2. Api-api
3. Buta-buta
4. Tangal
5. Bakauan-lalaki
6. Bakauan-babae
7. Pagatpat
8. Piapi
9. Nipa
10. Malatangal
11. Bungalon
12. Busain
13. Bakauan-bangkau
14. Pototan
15. Tinduk-tindukan
16. Tabigi
17. Pedada
The Philippines has ten botanical gardens
(Table 9) with a total of 16,000 taxa (Fernando
and Balatibat, 1998). Many of these are small
collections of plants for public display, while others
are living collections for plant genetic resource
conservation research and education. Most, if
not all, remain poorly-funded and under-staffed;
in the greater majority there are no scientific
activities and no documentation or inventory of
collections.
in the Mangrove Genebank at
Scyphiphora hydrophyllacaea
Avicennia officinalis
Excoecaria agallocha
Ceriops tagal
Rhizopora apiculata
Rhizopora mucronata
Sonneratia alba
Avicennia marina var. rumphiana
Nypa fructicans
Ceriops decandra
Avicennia marina
Bruguiera gymnorrhiza
Rhizopora stylosa
Bruguiera sexangula
Aegiceras floridum
Xylocarpus granatum
Sonneratia caseolaris
Philippines
The Makiling Botanic Gardens
(MBG) in Los Baños, Laguna
is the only fully developed botanical garden in the country.
It has approximately 5-ha of
recreational area and arboretum and about 200 ha of
natural forest. It was formally
established in 1963 through
RA 3523, “for the purpose of
supporting professional instruction and research relating
to forestry and plant sciences
generally and for serving the
needs of tourists as well as the
educational and recreational
needs of the general public”.
On the average it receives up
to 103,000 visitors each year,
more than 60% of which are
primary and secondary school
students and nearly 50%
Country Report on Forest Genetic Resources
29
Table 9. Botanic gardens in the Philippines.
Botanic Garden
Administrator
Location
Arboretum of the University of
the Philippines
University of the Philippines-Diliman
Quezon City
La Union Botanical Garden
City Government of San Fernando
La Union
Makiling Botanical Gardens
University of the PhilippinesLos Baños
Laguna
Manila Zoo and Botanical
Garden
Public Recreation Bureau, City of Manila
Manila
Pation Botanico Garden
Philippine National Museum
Manila
Philippine Bambusetum
Department of Environment and
Natural Resources
Baguio City
The Hortorium
University of the PhilippinesLos Baños
Laguna
University of Santo Tomas
Botanical Garden
University of Santo Tomas
Manila
Siit Arboretum Botanic Garden
Eric Hanquinet
Negros Oriental
Source: Catibog-Sinha and Heaney, 2006
come from the Metro Manila area. The Makiling
Botanic Gardens maintains an arboretum of
Dipterocarpaceae representing more than half
of all the species known in the Philippines. It
also has plantations of Swietenia macrophylla
representing probably the earliest seed lot of
this species first introduced in the Philippines
in June 1913 from the Royal Botanic Gardens
in Calcutta, India (Ponce, 1933). MBG’s collections of commercial timber trees also include,
among others, Vitex parviflora, Pterocarpus
indicus, Afzelia rhomboidea, Intsia bijuga,
Sindora supa, Madhuca betis, Petersianthus
quadrialatus, Agathis philippinensis, Tectona
grandis, Tectona philippinensis, Cedrela odorata, and Endospermum peltatum (Fernando,
2001).
Seed Banks, Clone Banks and In Vitro
Genebanks
In the Philippines, there are currently no known
forest tree seed banks and in vitro genebanks.
While there are facilities in the ERDB for short
term storage of tree seeds, these are mostly
used for orthodox seeds. In vitro methods and
tissue banks are not mainly used by ERDB as
conservation strategies. Tissue banks are not
viable options for the long-term conservation
of forest genetic resources. Furthermore, seed
storage problems especially for recalcitrant
species like dipterocarps and lesser known
species, including non-timber species need
further research studies. The investment
needed in the laboratory in terms of manpower, equipment and supplies, especially
power generators for ensuring the integrity
of in vitro collections, are reasons for their
non-utilization.
The Institute of Plant Breeding (IPB) of the
University of the Philippines Los Baños, through
its National Plant Genetic Resources Laboratory,
is maintaining a genebank for agroforestry
species such as Gliricidia sepium and a collection
of indigenous and endemic fruit tree species.
Philippines
30
Country Report on Forest Genetic Resources
The Institute also has facilities for storing seeds
and tissues for an indefinite length of time.
Currently it is keeping specimens of cereals,
horticultural and ornamental collections, but
none yet on timber species. Nevertheless, the
Institute, in collaboration with the MBG, is going
to implement a program on the conservation
of biodiversity of high value crops, including
indigenous palms and selected forest species
(Garcia, 1999).
Table 10. Summary of Acacia mangium
seeds records and acquisition
by PTFI-SMH in Mindoro
YEAR
1982
1983
1984
1985
1986
1987
TOTAL
Plant Rescue
Scientists at the National Museum in Manila
have started a Plant Rescue Operation which
was triggered by the recent Mt. Pinatubo
eruption. No similar activities have been
planned for other volcanic areas in the
Philippines to prepare for future natural events
(Garcia, 2000).
Clonal Propagation
Clonal propagation involves utilization of the
vegetative portion of plants in producing trueto-type plants. It is used to produce high
quality planting materials from outstanding/
recommended mother trees.
The Provident Tree Farms Inc. (PTFI) in
southern Philippines ventured into an Industrial
Tree Plantation License Agreement (ITPLA)
in 1982 (Nuevo 1997). This private company
included tree improvement in its long-term
management strategy to meet the challenges
of increasing volume and quality of logs and
fibre. The company focused on Gmelina arborea
and Acacia mangium. Table 10 presents the
Acacia mangium seedlot acquisition of PTFISMH, in Mindoro from as early as 1982 through
1987. The table shows considerable number
of various acquisitions in a span of six years.
The various provenances could provide genetic
base wide enough for a starting program
in tree improvement. Table 10. Summary
of Acacia mangium seeds records and acquisition
by PTFI-SMH in Mindoro.
The PTFI made an extensive first generation
selection of landraces of G. arborea throughout
NO. OF SEEDLOTS OR
PROVENANCE
87
15
2
66
45
8
223
Mindanao (Southern Philippines) and a high
intensity selection of A. mangium from the
best trees among the provenances introduced
from Australia and Papua New Guinea
Table 11 presents the provenances used
in plantation from 1983 to 1988. Planting
made in 1989 and onwards originated from
seeds collected from the earlier plantations in
Mindoro and finally from Talacogon.
For G. arborea, the journal only indicated the
sources of the land races as having emanated
from Nasipit, Agusan del Norte, from the local
sources in the vicinity, and from Canlubang,
Laguna. Similarly for Falcata moluccana, seeds
came from local sources, Nasipit, Mindoro and
PICOP area.
The PTFI also developed a technology for the
cloning of terminal shoot utilizing unsterilized
shoot tips and mass-growing them in unsterile rooting medium of ordinary river sand.
The company’s ramet multiplication garden
has been able to produce in total one million
stecklings, which is sufficient to fulfill its planting stock requirements with some surplus for
external demands (Nuevo, 1997).
Clonal multiplication gardens composed of
selected genotypes with desirable phenotypic
characteristics are established near field nurseries. These are ready sources of propagules
for macro and in vitro propagation, adding
Philippines
Country Report on Forest Genetic Resources
31
Table 11. Provenances and Seedlots of Acacia mangium used in PTFI-Talacogon
Plantation.
PLANTATION STAND NOS.
1983
54
1984
1, 3
Australia, Olive River
PH1H518200165
35
Australia, Olive River
PH1H518200168
9
Australia, Olive River
PH1H518500165
10, 11
Australia, Olive River
PH1H518500170
PNG, Oriomo, River
PH1H518500150
Australia, Olive River
PH1H518500002
1985
12
1986
61, 62, 64
1987
5, 66, 67, 68
1988
7, 8, 32, 45, 69, 70
72, 76
PROVENANCE
SMH REGISTRATION/
SEEDLOT NO.
YEAR
PNG, Oriomo River
Australia, Syndicate
Road
Australia, Rex Range,
Mossman
PNG, Oriomo River
efficiency in propagation. It eliminates the
need for frequent travels to very far sources
just to collect shoots for clonal propagation.
Endangered indigenous tree species are
collected as wildlings or seeds/seedlings and
placed in the vicinity of nurseries as hedge
gardens. ERDB and Regional DENR-ERDS have
established hedge gardens in their nurseries,
mostly of dipterocarps. Table 12 shows the
dipterocarp species planted at the ERDB hedge
garden. Philippine teak stockplants from Lobo,
Batangas are also added, as well as molave
from Dasol, Pangasinan. Selection is not
practiced when it comes to conservation and
not intended for tree improvement.
Research Gaps
The following R & D areas are hereby recommended for more improved ex situ conservation
efforts in the country:
• Effects of forest fragmentation on genetic
diversity, since fragmentation would affect
PH1P51830004
PH1H518200052
PH1H518600018
PH1H518600050
abundance, composition and behaviour of
many pollinating species; propagation of
beach forest species which could be on the
verge of extinction,
• Ultra-dry seed storage for orthodox species.
The ultra-dry seed storage technology is
based on the principle that desiccating seeds
to much lower moisture contents than those
generally used in standard procedures will
allow seed storage for an extended period
at room temperature, thereby avoiding the
requirement for refrigeration facilities. The
seeds are placed in hermetically sealed
containers. This is very important because
seeds are the most convenient form for
distributing germplasm to farmers and
other users.
• Storage behavior of many indigenous tree
species. The orthodox and recalcitrant seeds
we know in the past as the two kinds of seeds
are now updated to include intermediate
seeds. This kind of seed is also desiccationsensitive, but is more tolerant than recalcitrant seeds. It is less tolerant than
Philippines
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Country Report on Forest Genetic Resources
Table 12. Summary of dipterocarp species planted in the ERDB hedge garden
(Pollisco, 2000)
Species
Source
Date
Collected
Planting
Materials
Date
Established
No. of
Stock
Plants
Almon
(Shorea almon)
Bukidnon
1995
Wildlings
June 1997
188
Apitong
(Dipterocarpus
grandiflorus)
SBMA Forest
Reserve
Oct. 1995
Wildlings
June 1996
10
Bagtikan
(Parashorea
malaanonan)
Mt. Makiling
1998
Seeds
June 1997
103
Dagang
(Anisoptera aurea)
Mt. Makiling
1994
Seeds
June 1998
8
Dalingdingan (Hopea
foxworthyi)
Mindoro
Oriental
Feb. 1995
Wildlings
May 1996
141
Gisok-gisok
(Hopea philippinensis)
Bislig,Surigao
del Sur
Oct. 1994
Jan. 1995
Wildlings
April 1997
222
Hagakhak
(D. validus)
Mt. Makiling
May 1999
Wildlings
Dec. 1999
17
Palosapis
(Anisoptera thurifera)
Ipo Dam,
Angat,Bulacan
1955
Seeds
May 1996
522
Panau
(D. gracilis)
SBMA Forest
Reserve
Oct. 1995
Wildlings
June 1996
180
Red lauan
(S. negrosensis)
Peñablanca,
Cagayan
Oct. 1995
Wildlings
May 1996
210
Tangile
(S. polysperma)
SBMA Forest
Reserve
1997
Seeds
August 1998
White lauan
(S.a contorta)
SBMA Forest
Reserv
1995
Seeds
May 1996
190
Yakal-saplungan
(Hopea plagata)
Malaybalay
Feb. 1995
Wildlings
May1996
275
orthodox and do not conform to orthodox
storage behavior. Once dried, they become
particularly susceptible to injury caused by
low temperature (Ellis et al., 1990; 1991).
The storage life of intermediate seeds can
be prolonged by this further drying but it
remains impossible to achieve the longterm conservation of orthodox seeds.
76
• Data base for priority species and priority
areas including success stories;
• Evaluation of existing Botanical Gardens;
• Establishment of new Botanical Gardens
that showcase Philippine native plants;
• Role of indigenous knowledge systems;
• Provenance testing;
• Promotion of indigenous tree species;
Philippines
Country Report on Forest Genetic Resources
•
•
•
•
•
•
•
dysgenic nature of the present selective
logging system;
Employing multiple use in upland communities; mass propagation of non-timber forest
species;
Integration of production and protection
objectives in industrial tree plantations;
Harnessing biotechnology for increased
growth/development of trees and pest/disease resistance
Establishment and maintenance of ex situ
conservation centers of wild plants
Establishment of new seed stands/sources,
seed orchards and genebanks of important
FGR
Establishment of protocols for macropropagation of rare and endangered
species.
Molecular genetic techniques for priority
species.
Education and Training
The ASEAN Regional Centre for Biodiversity
(ARCBC, now ASEAN Centre for Biodiversity
or ACB) has actively conducted several
trainings to upgrade the capacities of different
organizations on biodiversity. Some of the
training courses include a National workshop
on Understanding and Managing Biodiversity at
the Provincial and Landscape Levels, a National
Trainers’ Training on Biodiversity Conservation
and Sustainable Development Education
at the Tertiary Level, and a Regional Plant
Taxonomy Training. The Protected Area and
Wildlife Bureau (PAWB) has conducted training
courses on techniques for plant identification
and vegetation assessment. However, during
the field interview related to the ITTO-funded
project on forest genetic resources, many
staff members of PAWB expressed the need
for more training considering that only a few
people were included in the previous training
courses. Other government agencies, such as
the Ecosystems Research and Development
Bureau (ERDB), have conducted short training
courses on plant collection and herbarium
techniques and macro- and micro-propagation
of selected premium and indigenous species.
The Philippine National Museum–Plants Unit
33
has training programs on plant conservation
techniques, plant collection and identification,
biodiversity assessment (flora/vegetation),
curation of herbaria, and inventory and
do-cumentation of ethnomedicinal plants,
using of Botanical Resources and Herbarium
Management System (DENR–PAWB, 2006).
Capability-building needed by institutions to
promote ex-situ conservation and enhance FGR
Conservation are as follows:
• Education and Training on plant genetic
diversity and conservation of FGR
• Public Awareness (Information Education,
Campaign) through improved libraries,
popular and technical publications, lectures,
seminars, workshops and conferences
• Resource mobilization to support FGR
Conservation activities
• Management Information System (MIS)
• Inclusion of FGR Conservation in academic
curriculum
• Other extension programmes – demo farms,
cross site visits
• Establish a system, including websites,
which will ensure a constant exchange
of information on the genetic resources
of Philippine plants between and among
cocerned institutions and organizations,
and make this information accessible to all
interested parties.
References
Catibog-Sinha, C.S. and L. R. Heaney. 2006.
Philippine
Biodiversity:
Principles
and Practice. Quezon city: Haribon
Foundation
for
the
Conservation
of
Natural
Resources,
Inc.
Crizaldo, E.N. 1999. R & D agenda for
Philippine forest tree genetic resources. Paper for the National Symposium
and Workshop on Philippine Forest Tree
Genetic Resources, 30–31 August,
1999, Makiling Center for Mountain
Ecosystems,
UPLB-CFNR,
College,
Laguna, Philippines.
Philippines
34
Country Report on Forest Genetic Resources
Cuevas E.B. 1999. Tree improvement and genetic conservation efforts of Bukidnon
Forest Inc., an industrial tree plantation at Bukidnon Province, Philippines.
Paper presented during the National
Symposium and Workshop on Philippine
Forest Tree Genetic Resources held
at TREES, CFNR, Los Baños, Laguna,
Philippines. August 30, 1999. National
Status Reports 129
Fernando E.S. and Balatibat J.B. 1998.
Resource
inventory
and
assessment of biodiversity in the Subic Bay
Metropolitan Authority. Annual Report.
DOST–PCARRD–SBMA, Philippines.
verdugonianus) outside its natural
habitat. DENR–ERDS. Terminal Report.
Los Baños, Laguna, Philippines.
Nuevo C.C. 1997. The role of clonal propagation
in compensatory forest plantations
and tropical forest rehabilitation. In:
Kikkawa J, Dart P, Doley D, Ishii K, Lamb
D, Suzuki K, editors. Proceedings of the
6th International Workshop of BIO–
REFOR, (J., eds.). Brisbane, Australia.
December 2–5, 1997, pp. 75–79
Reyes M.R. 1987. PICOP revisited. Philippine
Lumberman 33(7):16–18, 32, 34–35.
Garcia M.U. 1999. State of the art review on
conservation of forest tree species in
the Philippines. Paper presented in
the Regional Workshop on “Strategies
for Genetic Resource Conservation
of Tro-pical Timber Species, 3–7 May
1999, Kuala Lumpur and Working
Paper for the National Symposium and
Workshop on Philippine Forest Tree
Genetic Resources, 30–31 August,
1999, Makiling Center for Mountain
Ecosystems,
UPLB-CFNR
College,
Laguna, Philippines.
_______. 2000. State-of-the-Art review on
genetic conservation of forest tree species in the 130 National Status Reports
Philippines. AIFM–ITTO Project PD 31/94
Rev. (F). (Unpublished). 42 pp.
Matusalem R.M. 1993. Species trial of selected
common reforestation species on a volcanic ecosystem of Mt. Mayon. DENR–
ERDS. Terminal Report. Los Baños,
Laguna, Philippines.
Maun M.M. 1978. Eucalyptus species trials.
Sylvatrop: Philippine Forestry Research
Journal 3(3):197–200. Los Baños,
Laguna, Philippines.
Nasayao E, German E. 1993. Growth and development of mankono (Xanthostemon
Philippines
Country Report on Forest Genetic Resources
35
Chapter 4
The State of Use and Sustainable Management of
Forest Genetic Resources
F
orest genetic resources is a concept that
refers to environmental, social, economic,
cultural and scientific values of the heritable
materials contained within and among species
(Koshy et al., 2002). In sustainable forest
management, Lutfi (2009) noted that a balance
should be attained i.e. a balance between
society’s increasing demand for forest and
benefits and the preservation of forest health
and diversity. The balance is critical to the
survival of forests and to the prosperity of
forest-dependent communities.
In a paper, “Harnessing Forest Genetic
Resources for Sustainable Forest Management”,
Garcia (1995) described measures to increase
the usefulness of forest genetic resources in
the Philippines. The paper touched on the
following issues:
1.
2.
3.
4.
5.
6.
7.
8.
9.
10.
Enhanced information gathering and
exchange for floristic surveys and forest
inventory;
Role of indigenous knowledge systems;
Revitalized breeding programmes;
Provenance testing;
Promotion of indigenous tree species;
Dysgenic nature of the present selective
logging system;
Employing multiple use in upland communities;
Mass propagation of non-timber forest
products;
Mixed plantings;
Integration of production and protection
objectives in industrial tree plantations;
11.
Harnessing biotechnology for increased
growth/development of trees and pest/
disease resistance.
Utilization of Conserved Forest Genetic
Resources and the Major Constraints to
their Use
The conservation, protection and sustainable
use of natural resources are embodied in several laws of the Philippines. The following
provisions in the Philippine constitution are
related to the conservation of forest resources:
1.
Protection and achievement by the State
of the right of all Filipino people to a balanced and healthful ecology in acordance
with the rhythm and harmony of nature
(Sec.16, Art.II); framework of national
unity and development (Sec. 22, XI);
2.
State of ownership of all natural resources and inalienability, except agricultural
lands (Sec. 2, XII);
3.
Full control and supervision by the State
on exploration, development, and utilization of natural resources either by
directly undertaking such activities or by
entering into co-production, joint venture or production-sharing agreements
with Filipino citizens or Filipino owned or
controlled corporations or associations
(Sec. 2, XIII);
Philippines
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Country Report on Forest Genetic Resources
4.
Small scale utilization of natural resources (Sec. 2,XIII);
5.
Determination by Congress of the specific limits of forest lands by marking of
their boundaries on the ground (Sec.4,
XII);
6.
Protection of the rights of indigenous cultural communities (ICC) by the State to
their ancestral lands to ensure their economic, social, and cultural well-being (Sec.
5, XII).
The above constitutional provisions as
regards the use of forest genetic resources
are further clearly enunciated in Section 1
of Executive Order No. 578 issued in 2006
which says that “in accordance with law, it
is the policy of the state to protect, conserve
and sustainably use biological diversity to
ensure and secure the well-being of present
and future generations of Filipinos. This
state policy extends to all the components
of biological diversity – ecosystems, species
and genes.” The same policy mandated the
DENR and all other government agencies as
well as all local government units to “integrate
and mainstream the protection, conservation
and sustainable use of biological diversity
into their policies, rules and regulations,
programs, projects, and development planning
processes.” As a matter of procedure, the EO
tasked all government agencies and local
government units to formulate and submit
to DENR, for monitoring compliance, their
respective biological programs.
The proper conservation of plant genetic
resources will guarantee their availability for
the use of present and future generations.
Forest genetic resources can be developed
to protect the environment, rehabilitate
degraded lands and improve the welfare of
rural communities. However, the continuous
destruction of the environment poses a great
threat to the availability of forest genetic
resources. Destruction is mainly caused by
land conversion for settlement, agricultural
development, shifting cultivation, logging,
forest fire, and to some extent mining, energy
projects, and pest and diseases (DENRPAWB, 2006). Fernando (2001) reported that
the country’s forest genetic resources are
threatened by overexploitation for commercial
purposes (collection of wild orchids for
export), land conversion (logging and shifting
cultivation) and habitat fragmentation.
The State of Forest Genetic
Improvement and Breeding Program
Previous efforts and current activities on
the genetic improvement and/or breeding of
forest species in the Philippines are few and
largely fragmented. The country doesn’t have
a national tree improvement program as yet,
to tie in all the initiatives on forest genetic improvement including forest genetic resources
conservation.
Forest genetic improvement had been conducted for several species. Some of the
projects that dealt on tree breeding are the
following:
1.
Development of genetically superior trees
in the genus Eucalyptus with funding
from the now defunct PICOP. Three
species of Eucalyptus (E. deglupta, E.
urophylla, and E. pellita) were crossed.
EP3 x ED1 and EP x EU excelled in height
growth rate, over their mid-parents
132% and 140% respectively. The hybrids also exhibited more vigorous and
homogenous seedlings heights
2.
Provenance
trial
of
Pinus
kesiya
(GOP, 10 years) – Some provenances
performed better than the others in
height growth. Twelve local and three
foreign provenances were tested. In
terms of diameter and height growth,
no significant differences were noted
between local and foreign provenances.
3.
Provenance trial of Pinus caribaea (GOP,
10 years) – Differences in height and diameter growth rate was not significant;
5.25% of the experimental trees developed foxtail.
Philippines
Country Report on Forest Genetic Resources
4.
Provenance trial of Eucalyptus camaldulensis (GOP, 9 years) – Forty-nine provenances from Australia were tested.
Survival, height and diameter growth
rates were significantly variable.
5.
Tolerance on pests and diseases of P.
caribaea, P. elliottii, P. pseudostrobus
(GOP) – Significant difference among
provenances were observed.
6.
7.
Morphological evaluation of Leucaena
leucocephala hybrids type (UPLB, 1
year) – Foreign strains as tree type compared to the native as shrub type. When
crossed, the F1 hybrids are intermediate
to the parents especially in leaf characters.
Screening of Leucaena for tolerance to
acidic soils (UPLB, 6 months) – Fifty four
accessions of local and foreign origins
were screened. Accessions 68 and 19
were outstanding with 242 and 220 mg
dry weight at 5 weeks after germination
with growths of 35 and 30 mg per week,
respectively. Tolerance to acidic soil was
highly correlated with growth.
Tree Improvement
Tree improvement refers to the application of
forest genetics principles within a given silvicultural system for the purpose of improving
the genetic quality of the forest. Its goal is to
improve the genetic value of the population
while maintaining genetic diversity. Meeting
this goal means that genetic improvement
is aimed at the population level, rather than
improvement of breeds or inbred lines. It can
be attained using a short-term or a long-term
approach although the latter provides the
optimum genetic gains.
The short-term approach to tree improvement
uses natural stands or existing land race
plantations, which have already adapted to
local environment conditions, although they
have narrow genetic base. This approach is a
temporary solution for the supply of improved
37
planting materials until the genetically improved seeds and propagules shall have been
produced by the long-term improvement
output. The approach includes, but not limited
to, the establishment of seed production areas
in natural stands or plantations, establishment
of interim seed orchards and timber stand
improvement in natural forests.
The long-term approach, on the other hand,
includes more advanced activities, such as
species/provenance trials, progeny trials, clonal
tests and hybridization.
Seed Stands provide the primary source of
phenotypically superior planting materials.
They serve as the direct link in the
establishment of seed orchards, the advanced
sources of improved planting materials.
Primarily, they function as an interim source
until progeny tested seeds are obtained from
the seed orchards.
Successful selection of plus trees from
identified seed sources of priority forest tree
species throughout the country focused on
forms and resistance to pests and diseases.
Some of the traits considered during the
selection include total height, diameter at
breast height, stem straightness, forking,
circularity, branch angle, branch thickness and
branch persistence/pruning ability.
With the objective of selecting plus trees of
several species, the UNDP and FAO funded
a project called FORTIP (Regional Project on
Improved Productivity of Man-made Forests
through Application of Technological Advances
in Tree Breeding and Propagation). The project selected more than 100 plus trees of
Swietenia macrophylla in the Makiling Forest
Reserve and the Quezon National Park, over
150 plus trees of Pinus kesiya in natural
stands at Baguio City and Bokod Watershed
Reservation area, about 30 plus trees of
Pterocarpus indicus in the Makiling Forest
Reserve and about 35 plus trees of Gmelina
arborea in Magat, Nueva Vizcaya (Zabala,
1996).
Philippines
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Country Report on Forest Genetic Resources
To upgrade the quality of seed stands as
source of propagules for breeding and mass
propagation, provenance/progeny trials of
Pterocarpus indicus, Vitex parviflora, and G.
arborea were established in Quezon, Bohol
and Davao, respectively by the DENR Research
Sector in 2009 under its tree improvement
program.
To support the continuing nationwide reforestation program with the expectation of having sustainable source of improved varieties
of forest trees and genetically superior planting
materials, the DENR through the Ecosystems
Research and Development Bureau (ERDB)
and Ecosystems Research and Development
Sector (ERDS) initiated the establishment of
potential seed production areas (SPA) and
Seed Sources throughout the country (Appendix Table 7).
Bansud, Oriental Mindoro in 1996 by ERDB in
collaboration with the CSIRO Division of Forestry’s Australian Tree Seed Centre (ATSC).
The seedlots used in the establishment of the
SPA came from provenance bulk collections
of ATSC. The SPA had an initial spacing of
5.0 m x 1.5 m (or 1,333 trees/ha). Thinning/
rouging was conducted in two stages with the
first thinning at about two years after planting when the trees were around 6 m tall and
the second thinning at age 3 when the trees
averaged 9 m tall. The final stocking is 150200 trees/ha. The SPA serves as a source of
high-quality seeds and planting materials for
the two species.
FORTIP project reported the establishment of
seed production areas of Acacia mangium in
Puerto Azul, Ternate, Cavite in 1994. The Tree
Seed Center of the Commonwealth Scientific
and Industrial Research Organization of
Australia (CSIRO) in cooperation with FORTIP,
the Ecosystems Research and Development
Bureau (ERDB), the Bukidnon Forests Incorporated (BFI) and the Forest Management
Bureau (FMB) established seed production
areas (SPA) of Eucalyptus urophylla, Acacia
mangium and A. crassicarpa at Bansud,
Mindoro, Malaybalay, Bukidnon and Baslay,
Negros Oriental.
In 1995, the DENR, having finally realized the
value of establishing a good and sustained
forest genetic resources for the country’s
reforestation
efforts,
initiated
through
Administrative Order No. 9 the identification,
establishment, maintenance, and protection
of Seed Production Areas (SPAs) throughout
the Philippines. The objective was to make
the SPAs the primary sources of seeds for
forest plantations. As embodied in the order,
SPAs may be established in government tree
plantations, industrial tree plantations, private
forest tree plantations, and in natural forest
stands. These identified plantations and natural
stands should meet the following criteria: (1)
for established plantation of similar species,
the minimum area should not be less than 10
ha; (2) for contiguous natural stands of mixed
species, the area should not be less than 10
ha; and (3) all identified mother trees shall be
marked on the site, recorded in the inventory
form, and plotted on a map. All established
SPAs, except those on private lands, were to
be delineated and proclaimed as permanent
SPAs, subject to re-evaluation every 5 years.
Commercial timber harvesting within the
proclaimed SPA inside public forest was also
to be strictly prohibited. Private landowners
with at least 2 ha of forest plantation may also
apply for accreditation with the DENR as seed
production area (SPA).
The 5.6 ha SPA for Acacia mangium and
Eucalyptus urophylla has been established in
The National Forest Tree Seed Committee of the
DENR has identified potential seed production
Seed Production Areas
Potential seed production areas are identified
and delineated in natural stands or plantations
with a high frequency of phenotypically good
planting materials. The stands are upgraded
and managed entirely for seed production.
Undesirable trees are removed or rouged, retaining only 150-250 trees/ha, which are tall,
big in diameter, with straight bole and have
balanced crown.
Philippines
Country Report on Forest Genetic Resources
areas all over the country. Teams conducted a
country-wide survey and identified 27 candidate
plantations in 10 regions. The species in the
identified plantations included indigenous
species (Casuarina equisetifolia, Pterocarpus
indicus and Vitex parviflora) and exotics of
different origins (Swietenia macrophylla,
Gmelina arborea, Eucalyptus camaldulensis
E. deglupta, Paraserianthes falcataria, and
Tectona grandis). Unfortunately, the program
did not prosper due to fear of public criticism
over tree rouging.
In line with the Research and Development
Projects of the National Forestation Program, a
project called Establishment and Management
of SPAs (Seed Production Areas) was conducted. One study under the project concentrated
on the roles of seed production areas in forest
plantation (Lustica et al., 1999). During
the 5-year study, information on the seeds
and phenology of Casuarina equisetifolia, C.
rumphiana, Eucalyptus camaldulensis and Shorea macrophylla were obtained at Dumarao,
Capiz, Iloilo and Aklan. Another study under
the project was national provenance trial for
narra (Pterocarpus indicus; Favila, 1996).
The five-year study compared five different
provenances of P. indicus at two locations, the
Leon National College of Agriculture (LNCA) and
the Calinog Agricultural and Industrial College.
Acacias and eucalypts in Bansud, Or. Mindoro
SPA produced the following seed yield: 1) A.
mangium had an average of 399.45 g/tree,
the highest of which was 765 g/tree; 2) E.
urophylla, the average yield of 73.07 g/tree,
the highest of which is 102 g/tree (Dimayuga
and Pader, 2006).
As to dipterocarps, DENR has selected over 50
plus trees at the seed production area in the
Experimental Forest, Bislig, Surigao del Sur
and at the Forest Reserve in Subic, Olongapo,
Zambales (Zabala, 1996).
Seed Orchards
Seed orchards are plantations of selected clones
or progenies which are isolated or managed
39
to avoid or reduce pollination from genetically
inferior sources outside the orchard, and is
intensively managed to produce frequent,
abundant, and easily harvested crops of seeds.
Seed orchard represents a more advanced step
than SPA. The purpose of establishing a seed
orchard is not only to produce large quantities
of improved seeds but can also be regarded as
a breeding population as basis for further tree
improvement.
A clonal seed orchard of Gmelina arborea
of 1.5 ha with 29 clones and 161 ramets
planted at 8 x 8 m spacing, and hybridizing
seedling seed orchard of A. mangium and
A. auriculiformis (0.75 ha) were established
at Puerto Azul, Ternate, Cavite by the ERDB
under the FORTIP project in 1995 and 1994,
respectively. Similarly, a 1.5-ha clonal seed
orchard of Swietenia macrophylla and a 2-ha
clonal seed orchard of Pterocarpus indicus were
established at Tayabas, Quezon in 1994–1995.
In 2007, the Public Sector Linkages Program
of the Australian Government’s Overseas Aid
Program (PSLP of AusAID) in collaboration with
the Ecosystems Research and Development
Services of DENR Regions 10 and 13, funded the
activities geared towards improving the productivity and profitability of trees in farms and
community-managed plantations in Northern
and North eastern Mindanao, and the other on
the application of advanced forest tree seed
technologies to improve rural wood-based
economic opportunities in the tree plantation
provinces of Mindanao. As a re-entry activity
which was still a part of the project, a total of 6
hectares of progeny trials of Acacia mangium
and Swietenia macrophylla were established
in the Northern Mindanao Institute of Science
and Technology (now Caraga State University)
in Ampayon, Butuan City and in Mapaua Tree
Farms, an IFMA holder at Mapaua, Cagayan de
Oro City. Another objective for the implementation of the said project was to enhance the
capabilities of the local DENR personnel with
the knowledge, skills, and technologies in the
application of advanced forest seed collection,
processing, storage and distribution or sales
Philippines
40
Country Report on Forest Genetic Resources
within the target provinces of Mindanao. From
2009 up to present, additional 17-ha trials of
Acacia mangium, Paraserianthes falcataria,
Eucalyptus deglupta, and Gmelina arborea
were established in the Caraga Region.
and multiplication of phenotypically superior
industrial forest plantation species such as
Paraserianthes falcataria, Gmelina arborea,
Endospermum peltatum and Eucalyptus deglupta (Fernando, 2001).
Species and Provenance Trials
More provenance trials of P. indicus have been
conducted in a volcanic ecosystem at Mt. Mayon
in Albay (Matusalem, 1993), and at the Bicol
National Park (Lauricio, 1997). Lauricio (1997)
compared the growth of prickly P. indicus from
Bukidnon and Camarines Sur and smooth P.
indicus from Camarines Sur, Capiz and Quezon. The different provenances showed good
growth.
One of the objectives of provenance trial is to
identify those provenances whose seeds will
produce well-adapted and productive genetic
materials for plantations. Productivity itself
may not always imply rapid growth but also
good survival, resistance to adverse environmental factors and pests, improved wood
quality, and good seed production.
Through its regional research offices, DENR has
started a number of species and provenance
trials. Since as early as 1958, trial plantings
of Eucalyptus have been conducted all over
the Philippines (Lizardo, 1960). Other species
trials of Eucalyptus provenances, obtained
from the Northern Territories of Australia, Italy,
Philippines, New South Wales and Brazil, have
been reported by Maun (1978). Agpaoa (1980;
see also Agpaoa and Tangan, 1981) claimed
that E. camaldulensis planted in Ilocos Norte,
Benguet, Nueva Ecija and Nueva Vizcaya
grew and survived better than Casuarina
equisetifolia, Leucaena leucocephala, Gmelina
arborea and Albizia procera.
Species and provenance trials and establishment of seed orchards have long been
conducted by DENR for species of Acacia,
Casuarina, Eucalyptus, Gmelina, Pterocarpus,
Pinus, Swietenia, Xanthostemon and other
multipurpose species (Garcia, 1999). Many of
these projects faltered due to changes in the
leadership and institutional reorganizations as
well as lack of sustained government support
(Ordinario, 1992). Some of the provenance trial
plots later formed seed sources for the younger
plantations by DENR and private planters.
The PICOP Resources Incorporated (PICOP),
the Provident Tree Farms Incorporated (PTFI)
and the Bukidnon Forests Incorporated (BFI)
have been practicing ex situ conservation
activities through provenance introduction
Siarot and Paler (1992) did in PICOP a provenance trial of 17 seedlots of Acacia mangium from Sabah (Malaysia) and Queensland.
The study reported no significant differences
in terms of average total height, but a highly
significant difference was observed in terms
of average diameter at breast height after five
years. The study further noted that a seedlot
from Sabah was free from canker. Siarot and
Paler (1992) recommended further genetic
improvement to attain perfectly straight boles.
Lanting and de Chavez (2002) also reported a
provenance trial of Acacia mangium and species trials of A. auriculiformis, A. aulacocarpa,
A. crassicarpa, A. mangium, A. mangium ×
auriculiformis and Gmelina arborea at Ternate,
Cavite. Seeds of A. auriculiformis were sourced
from Queensland, whereas G. arborea seeds
originated from Makiling Forest Reserve, Sabah
Wood Industry and from Diadi, Nueva Vizcaya.
The other four species came from Papua New
Guinea. The study identified 150 seed trees of
the different species but further noted that the
seed yield from these trees was inadequate to
support the national reforestation project.
A provenance trial of Pinus caribaea var. hondurensis was conducted at Jalau Reforestation
project in Calinog, Iloilo by Eusebio (1983).
There
were
nine
provenances
tested.
Moreover, DENR has conducted provenance
trials of Pterocarpus indicus (Matusalem,
1993; Lauricio, 1997; Favila, 1996); Casuarina
Philippines
Country Report on Forest Genetic Resources
equisetifolia, C. junghuniana, Acacia mangium,
A. auriculiformis, A. crassicarpa, A. aulacocarpa, G. arborea, A. mangium × auriculiformis,
Pinus caribaea (Eusebio, 1983); Eucalyptus
camaldulensis (Agpaoa and Tangan, 1981) and
Xanthostemon verdugonianus (Nasayao and
German, 1993). All these species, except for
P. indicus and X. verdugonianus, are exotics.
To upgrade the quality of seed stands as
source of propagules for breeding and mass
propagation, provenance/progeny trials of
narra (Pterocarpus indicus), molave (Vitex
parviflora), and yemane (G. arborea) were
established in Quezon, Bohol and Davao,
respectively by ERDB in 2009 under its tree
improvement program.
Seed Collection, Processing, Storage and
Distribution
Seeds are the most economical sources of planting materials and the easiest to transport.
However, most of the indigenous species are
found in remote areas and produce seeds after
long intervals. Added to this is the fact that
most have recalcitrant seeds. Other species
show some degree of dormancy or require
different pre-treatments. The most recent
significant seed research that was developed
is the Malapapaya (Polyscias nodosa) seed
technology by Dayan and Reaviles (2001) and
has been used by MP Woods for their plantation
in Gumaca, Quezon. It is the raw material for the
manufacture of chopsticks, popsicle sticks, bento
boxes and veneer. Seed technology of other
species are published in DENR Recommends
series.
A report by Tolentino et al., (2006) on the
assessment of mother trees of the different
species by SPA-designated stands, seed
orchards, and other designated seed sources
and plantations of government (DENR, SCU),
corporate/private companies (timber licensees),
and smallholder tree farms (CBFMA, private
plantations) revealed the following results:
1) documentation of seed origin is seldom
practiced; 2) the number of mother trees
from where seeds are collected varies. There
41
are those whose sources have more than 100
trees, but some smallholder tree farmers have
limited number of trees (<10 trees) from which
seeds are collected. Corporate or institutional
(GO-based) plantations have access to a wide
variety of seed sources, particularly superior
ones, while resource-limited farmers do not
have access to improved seeds; 3) basic policies
(DENR Administrative Order 95-9 and its
implementing guidelines DENR Memorandum
95-20) to insure the quality of seeds were
laid out before but they have weaknesses
and shortcomings that need to be addressed.
The effectiveness of DAOs and memorandum
circulars should also be assessed in contrast to
complete tree seed legislation, i.e., a Tree Seed
Law for the Philippines.
A farmer-operated association for the production, collection, processing, development
and marketing of seeds was established in
1998 in Lantapan, Bukidnon. Since then
the Agroforestry Tree Seed Association of
Lantapan (ATSAL) has grown from the initial
15 to 60 members. The association has been
instrumental in training thousands of farmers
in collecting, handling and marketing of quality agroforestry seeds. The marked difference
of this group with other seed vendors is that
this non-formal system for seed production
and distribution enabled smallholders to
produce and market quality germplasm
based on standardized methods, as noted by
Koffa and Garrity (2001). The same authors
described the approaches in maintaining
diversity in germplasm sources in farming
systems, namely: (a) work directly with the
genetic resources which the smallholders
value and conserve; (b) create and conserve
protected areas; and (c) provide smallholders
with genetic diversity in the form of landrace
germplasm from a range of sources.
ATSAL has sold more than 5,000 kg of assorted seeds of exotic and indigenous tree species, and thousands of seedlings to buyers in
Mindanao, Visayas and even in Nairobi, Kenya.
Since its foundation, ATSAL has earned three
million Philippine Pesos (60,000 US$). The
profits were distributed among the member
Philippines
42
Country Report on Forest Genetic Resources
farmers and used to support the organization.
This example highlights the significant roles of
upland farmers in contributing towards genetic conservation of important forest resources.
Additionally, it emphasizes the fact that forest
genetic conservation is not a monopoly of
corporate or government agencies.
The Ecosystems Research and Development
Services of DENR Region 13 established
the Mindanao Tree Seed Center in 2008. Its
establishment was made possible through the
participation to the training on “advanced forest
tree seed technologies to improve wood-based
economic opportunities in the three plantation
provinces in Mindanao”, which is a part of
the Public Sector Linkage Program (PSLP) of
the Australian Government’s Overseas Aid
Program. To strengthen its implementation,
DOST-PCARRD approved the implementation
of different important activities of the center
through the project entitled “Seed Collection
and Management of Mindanao Tree Seed
Center cum Production of Quality Seedlings”
under the Action Program of the Establishment
of ITP Action Program on the Establishment of
Commercial Plantation and Efficient Utilization
of Wood Products in Caraga Region. The center
serves as the channel for facilitating the flow of
seeds from selected sources while capturing,
keeping, processing relevant information
in a Seed Information System in order to
improve productivity of the tree plantations.
The center started dispatching industrial tree
plantation (ITP) seeds in 2010 to the different
DENR projects, private tree farmers and to
a research organization. With its campaign
message of “better plantations come from
better seeds/planting materials”, more private
farmers and people’s organizations are buying
quality seeds from the center. With the
implementation of National Greening Program
in 2011, the center included in its identification
of superior mother trees and collection of the
seeds/planting materials of indigenous trees.
DENR Administrative Order No. 2010-11 issued on 05 May 2010 provides for the regulations governing forest tree seed and seedling
production, collection and disposition. Among
the objectives of this Order is to “ensure the
continuous production of adequate supply
of phenotypically and genetically-improved
planting materials to meet the requirements
for high quality seeds and seedlings by the
government and private sectors in the establishment and development of tree plantations, tree farms, forest gardens, forestation,
agroforestation projects, and rehabilitation of
watersheds and coastal areas.
Research and Development
There are several R & D projects that have
been conducted as regard ex situ efforts in the
Philippines.
In a study on field performance of rooted
cuttings, Pollisco (2000) reported about the
destructive sampling done on three year old
dipterocarp rooted cuttings and seedlings/wildlings planted at the Mt. Palay-palay National
Park, Mataas na Gulod, Ternate, Cavite, to
compare their root systems. The species used
were white lauan (P. contorta), guijo (Shorea
guiso) and palosapis (Anisoptera thurifera).
Results showed that the root system of 3-yr
old cuttings had more than one macro-root,
each of which is comparable in size to the tap
root of seedlings. Wildlings were found to have
a major advantage of having plenty of lateral
roots, presumably because of their having
established initial ectomycorrhizal infection
upon germination, an advantage over both
seedlings and rooted cuttings. Read (1991),
as cited by Becker (1983), stated that when
seeds germinate, they quickly become infected
by mycorrhizal fungi already established in association with the adult trees.
Initially, no major differences were found in
terms of height and diameter growth of the
cuttings and seedlings derived from juvenile
materials. The vegetatively-derived palosapis
grew more slowly in the early part than the
seedlings, although the sand-rooted cuttings
leveled-off with the seedlings after 11 months.
Zobel (1992) also observed that rooted cuttings of sycamore (Planatus occidentalis) grew
in the same pattern as palosapis (Anisoptera
Philippines
Country Report on Forest Genetic Resources
thurifera), while rooted cuttings of Bambasopsis quinata grew faster than seedlings.
Dipterocarps are commonly regarded as
shade tolerant during early development and
light demanders after the seedling or sapling
stage (Appanah and Weinland, 1993). Many
dipterocarp species either failed completely
or performed poorly when planted directly
on Imperata cylindrica grasslands. Poor performance of planted dipterocarps on open
grassland was also reported by Zabala (1986).
Contrary to these reports, 7-yr. old white lauan
(P. contorta) planted in the Caliraya, Laguna
field trial was found to be growing vigorously
in the open (Pollisco, 2006), with bushy crown.
Those planted under different nurse trees in
different areas were observed to be smaller
in both height and diameter increments.
Dipterocarp trees under narra (P. indicus) in
Cavite did not perform well, which may be
attri-buted to the closed canopy of the nurse
trees during most parts of the year (Pollisco,
2004). Dr. Zabala stated that it is intensive
and may have prohibited further development of Anisoptera marginata saplings. The
same is true with dipterocarps planted under
mahogany in Malaybalay, Bukidnon wherein
only occasional sunflecks penetrate the lower
canopy. Even the dipterocarps planted under
canopy gaps in Bislig, Surigao del Sur were
smaller than those planted in the open conditions at Caliraya. Furthermore, narra shed
leaves completely during summer, exposing
the dipterocarps to full sunlight. Since their
leaves are attuned to shade most of the year,
intense sunlight during summer is stressful
in addition to water deficiency resulting to
lower height and smaller diameter. According
to ERDS Davao, the Nabunturan, Davao del
Norte field trial under eucalypts is also an
exceptional trial.
Since eucalypts have small, thin leaves, it is a
suitable nurse tree for dipterocarps. Appanah
and Weinland (1993) noted the same for
Paraserianthes falcataria, wherein it has a
sparse foliage and flat crown high above the
ground, allowing sunlight to penetrate fairly
uniformly to the forest floor.
43
Another possible explanation may also be that,
as stated by Becker (1983), plants growing
under high light intensity have more abundant
mycorrhizal roots than those growing in the
shade. He found that under natural conditions,
the number of mycorrhizal infections was
higher in open areas than for seedling growing
under closed canopy. Soil analysis has yet to
be conducted to be able to determine the soil
status of the sites. Ashton, et al. (1988) stated
that distribution of dipterocarps is correlated
with a number of soil factors, but primarily with
magnesium and phosphorus.
Mangrove ecosystems have been another
active area of research in the Philippines.
For example, an inventory and assessment
on mangrove biodiversity was conducted in
Central Visayas. The study included research
to better understand the stand structure, phenology, species composition, pests and diseases, silvicultural attributes and environmental
factors which affect the survival and growth
of mangrove plantation. In addition, seed
sources of selected mangrove and associated
species were established. Other studies on
mangroves include the provenance studies of
various mangrove species in Western Visayas
(Malabanan, 1992), rehabilitation of the
coastal areas of the National Capital Region
(Esteban, 1998), and documentation and
assessment of mangrove reforestation using
indigenous practices in Bohol (Mantanilla and
Melana, 1992).
The first work on the characterization of
timber species using molecular markers in
the Philippines was a dissertation produced
on Swietenia macrophylla populations in
the Luzon Island using Random Amplified
Polymorphic DNA (Quimado, 2002). The study
showed high polymorphism (80%) of the large
leaf mahogany trees in Mt. Makiling, Laguna
and in Atimonan, Quezon. Within population
diversity (90%) was significantly higher than
variation between populations (10%). The
study also showed two major groupings and
the distinctness of one population from the
rest. As noted, this study is the first of its kind
and more such studies are needed.
Philippines
44
Country Report on Forest Genetic Resources
In another study, the mating system of
Pterocarpus indicus (narra) population in a
mixed planted forest at Mt Makiling, Luzon
Island, was investigated using five polymorphic isozyme loci. The population was noted to
have a predominantly outcrossing nature (De
Guzman, 1996). Pollen competition or early
selection against selfed progenies, or both,
were suggested as possible reasons for the low
estimates of selfing rates. The estimated outcrossing rates of the isolated trees showed that
the unidentified pollinators of P. indicus were
very efficient to ensure a high degree of crosspollination even for spatially isolated trees.
Future research to investigate the taxonomy
of P. indicus through isozyme analysis, and
studies to elucidate mating patterns of other
tropical trees were suggested (De Guzman,
1996). Using isozyme analysis, Parashorea
malaanonan was confirmed to be outcrossing
(Gamboa-Lapitan & Hyun, 2005). The same
study also observed biparental inbreeding in
the species in some individuals in the Makiling
Forest Reserve. Abasolo (2007) used a satellite
marker derived from Shorea species to study
the genetic diversity of Parashorea malaanonan. The results showed that diversity within
sites was 64% while diversity among sites
was 36%, indicating a high diversity between
sites in the Makiling Forest Reserve. There
was no significant correlation between genetic
and geo-graphical distances in the four sites
studied.
In 2009-2010, routine laboratory procedures
for determining genetic variation within
and among population of narra (P. indicus),
Benguet pine (Pinus kesiya), molave (V. parviflora), limuran (Calamus ornatus var.philippinensis) and tagiktik (Calamus filispadix) were
conducted using isozyme analysis.Isozyme
analysis of five provenances of narra showed
that Cebu has high genetic diversity thus a
good source of quality seeds for plantation
development. Limuran leaf samples randomly
collected from Camarines Norte, Bataan and
Quezon revealed low genetic variation in Quezon and those in Bataan as the most diverse,
making it the most probable good source of
quality seeds.
Mass Propagation of Improved Varieties
For macropropagation technique, the protocols
for rooting of Gmelina shoot tip and nodal cuttings were developed by Umali-Garcia as early
as 1990. The importance of clonal testing was
demonstrated in several Gmelina provenances
(Umali-Garcia et al., 1998). The propagation
of several endangered Philippine species,
such as Diospyros philippinensis (Oporto and
Umali-Garcia, 1999) and Dracontomelon dao
(Oporto and Umali-Garcia, 1998a) has been
successfully demonstrated. There are already
available protocols for rooting of stem cuttings
of certain species of dipterocarps (Pollisco,
1995; Dela Cruz, 1996; Oporto and UmaliGarcia, 1998c), Paraserianthes falcataria,
(Umali-Garcia, 1989), Eucalyptus hybrid
(Siarot 1991), Swietenia macrophylla, Vitex
parviflora (Umali-Garcia, 1995), Pittosporum
pentandrum (Oporto and Umali-Garcia,
1998b) and Pinus merkusii (Garcia, 1999).
For the last decade, macropropagation using
rooted cuttings were successfully attained
by ERDB for 13 dipterocarp species namely
Shorea contorta. S. contortis, S. guiso S.
almon, Parashorea malaanonan, Dipterocarpus
grandiflorus, D. gracilis, Hopea plagata, H.
philipinnensis, H. foxworthyi, Vatica odorata,
Anisoptera aurea and A. thurifera. Clonal propagation was conducted on dipterocarp species
because production of planting materials by
seeds is difficult due to irregularity of seed
production supply and short seed viability period.
Indigenous species which include premium
and endangered species like narek (Hopea
cagayanensis), batikuling (Litsea leytensis),
dangula (Teijsmanniodendron ahernianum),
molave (Vitex parviflora), toog (Petersianthus
quadrialatus), and dungon (Heritiera sylvatica)
were also macropropagated.
As to micropropagation, tissue culture
propagation of various tree and plant species
in the Philippines has been done on some
forest tree species (Table 13). So far, plantlets
of Eucalyptus deglupta, Paraserianthes falcataria, Endospermum peltatum, Acacia mangium, E. camaldulensis and Pterocarpus indicus
Philippines
Country Report on Forest Genetic Resources
have been successfully produced in test tubes
in the laboratory (Crizaldo, 1980; Capuli and
Calinawan, 1999; De la Cruz, 2003). Except
for E. deglupta, P. falcataria and Cratoxylon
sumatranum, the clones have not found their
way in the nursery. A programme on forest
biotechnology based at the University of the
Philippines, Los Baños (UPLB), under the
College of Forestry and Natural Resources
(UPLB–CFNR) focused on tissue culture of
industrial plantation species such as Acacia
mangium, Gmelina arborea, Pterocarpus indicus, P. falcataria and Swietenia macrophylla
using explants from selected plus trees.
45
ERDB has successfully developed protocols
for plantlet production of Acacia mangium,
Eucalyptus deglupta, and E. pellita-urophylla
using the tissue culture method. Samples of
tissue cultured seedlings of E. deglupta were
planted in the ERDB Experiment Station in Mt.
Makiling, Los Banos, Laguna and in Llavac,
Quezon. Two years after planting, the seedlings were observed to be exhibiting good
growths and straight boles.
Tissue culture of various rattan species has
also been worked on. An ongoing project on
‘Research and Development Program and
Table 13. Tree species studied using tissue culture in the Philippines (adapted from
Lapitan and Garcia, 1993).
Species
Agathis philippinensis,
Pseudocarpus philippinensis
Status of research
Sterilization procedure and medium for callus
initiation protocol developed
Plantlets developed
Callus and bud formation and rooting
Paraserianthes falcataria
Pterocarpus indicus
Media identified for callus and shoot formation
Shorea contorta, Eucalyptus camaldulensis,
E. deglupta, Pogostemon cablin
Nutritional requirements for callus initiation
established
Callus formation, shoot and root formation
Plantlets acclimatized in the nursery
Callus induction, plantlet regeneration, shoot
formation, survival of plantlets
Citrofortunella mitis, Citrus spp.
Multiple shoot formation in defined medium
Cratoxylon sumatranum
Plantlets acclimatized under nursery condition
and some were planted out in the field
Rattans:
Daemonorops mollis, Dendrocalamus
latiflorus, Calamus merrillii, C. ramulosus,
C. ornatus, C. caesius, C. manilensis
Plantlets, regeneration, problem in callus
maintenance protocols established
Bamboos:
Dendrocalamus latiflorus, Bambusa
blumeana, B. vulgaris, D. merrillianus,
Gigantochloa levis, G. aspera
Protocol for spindle, node and ground tissue
established. Species differed in nutritional
requirements
Schizostachyum lumampao
Cultured clones acclimatized in nursery,
established in grasslands
Philippines
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Country Report on Forest Genetic Resources
Capability Building on the Mass Propagation
of Rattan through Tissue Culture collected
seeds of different provenances of rattan from
Bukidnon (Mindanao) and Aklan (Visayas),
and from Makiling and Ilocos (Luzon). The
project utilizes embryos and tissues from in
vitro-germinated seeds as explants (Garcia,
2002).
Capuli, F.A. and N.M. Calinawan. 1999. Micropropagation of bagras leaflet. ERDB,
College,Laguna.
Catibog-Sinha, C.S. and L. R. Heaney. 2006.
Philippine Biodiversity: Principles and
Practice. Quezon City: Haribon Foundation for the Conservation of Natural
Resources, Inc.
References:
Abasolo M.A. 2007. Genetic diversity of Parashorea malaanonan (Blanco) Merr.
(Dipterocarpaceae) in the Mt. Makiling
Forest Reserve Philippines using microsatellite markers derived from Shorea
species. MSc Plant Genetic Resources
Conservation and Management, Graduate
School, University of the Philippines Los
Baños, College, Laguna. 117 pp.
Agpaoa A.C. 1980. Murray red gum: A drought
and fire resistant species for reforestation. Canopy International 6(20):1.
_______. Tangan F. 1981. Provenance trial of
Eucalyptus camaldulensis Dehn. Canopy 3(1):8–10. 2). Los Baños, Laguna,
Philippines.
Appanah, S. and G. Weinland. 1993. Planting quality timber trees in Peninsular
Malaysia – a review Malayan Forest
Record No. 38. FRIM and GTZ. Kuala
Lumpur, Malaysia. 221 p.
Ashton, P. S., Givnish, T. J. & Appanah, S.
(1988) Staggered flowering in the
Dipterocarpaceae: New insights into
floral induction and the evolution of
mast fruiting in the aseasonal tropics.
American Naturalist 132 (1): 44-66.
Becker, P. 1983. Mycorrhizas of Shorea (Dipterocarpaceae) seedlings in a lowland
Malaysian rain forest. The Malaysian
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Crizaldo, E.N. 1999. R & D agenda for
Philippine forest tree genetic resources. Paper for the National Symposium
and Workshop on Philippine Forest Tree
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Cuevas E.B. 1999. Tree improvement and genetic conservation efforts of Bukidnon
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Paper presented during the National
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Forest Tree Genetic Resources held
at TREES, CFNR, Los Baños, Laguna,
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Status Reports 129.
Dayan, Ma. dP. and R. Reaviles. 2001. Malapapaya seed technology leaflet. ERDB.
College, Laguna.
De Guzman N.M. 1996. Mating system of narra
(Pterocarpus indicus Willd.) in Mt.
Makiling, Philippines. MS thesis, UPLBCFNR, College, Laguna, Philippines.
Dela Cruz L.U. 1996. Asexual Propagation and
Appropriate Mycorrhizal Inoculation
Techniques for Selected Bamboo and
Dipterocarp Species. DOST–PCARRD.
Terminal Report. Los Baños, Laguna,
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DENR–PAWB. 2006. Framework for Philippine
Plant Conservation Strategy and Action
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Faculty
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University, Yogyakarta.
and Wildlife Bureau. Quezon Avenue,
Diliman, Quezon City.
Dimayuga, M. and L. Pader. 2006a. Clonal
propagation of selected high premium
tree species Terminal Report.
_______ 2006b. Increased production of high
quality seeds and other propagules
from Seed Production Areas of Acacia
mangium and Eucalyptus urophylla.
ERDB. 2010. Development and Management of
Forest Plantations in the Philippines: A
Guidebook. Ecosystems Research and
Development Bureau – Department of
Environment and Natural Rerources,
College, Laguna. 246 pp.
Ellis R.H., T. Hong and E. H. Roberts. 1990. An
intermediate category of seed behaviour I. Coffee.
_______. T. Hong and U. Soetisna. 1991. Seed
storage behaviour in Elaeis guineensis.
Seed Science Research I. pp. 99–104.
Esteban E.B. 1998. R and D study of nilad and
other mangrove species to rehabilitate
NCR coastal region. Department of
Environment and Natural Resources
(DENR–ERDS). Terminal Report. Los
Baños, Laguna, Philippines.
Eusebio EC. 1983. Provenance trial of Pinus
caribaea var. hondurensis. DENR–
ERDS. Terminal Report. Los Baños,
Laguna, Philippines.
Favila D.P. 1996. National provenance trial for
narra. DENR–ERDS. Terminal Report.
Los Baños, Laguna, Philippines.
Fernando, E.S. 2001. Genetic resources conservation for timber in the Philippines.
Pp 69-82 in In situ and Ex situ conservation of Commercial Tropical Trees
(B.A. Thielges, S.D. Sastrapradja and
A Rimbawanto, eds.) International
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Fernando E.S, Balatibat J.B. 1998. Resource
inventory and assessment of biodiversity
in the Subic Bay Metropolitan Authority.
Annual Report. DOST–PCARRD–SBMA,
Philippines.
_______, A. C. Manila and T. M. S. Lim. 2009.
Framework for the Philippine Plant Conservation Strategy and Action Plan. In:
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Southeast Asian Countries. Editors K.Y.
Choo, R. Jalonen, L.T. Hong and H.C.
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APAFRI. pp 92-105.
Gamboa-Lapitan P, Hyun J.O. 2005. Mating
system of Parashorea malaanonan (M.
Blanco) Merr. (Bagtikan) in Mt Makiling, Laguna, Philippines. Philippinese
Agricultural Scientist 88(1): 109–121.
Garcia, M.U. 1995. Forest Tree Improvement in
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Advances in Tree Breeding and
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Garcia M.U. 1999. State of the art review on
conservation of forest tree species in
the Philippines. Paper presented in the
Regional Workshop on “Strategies for
Genetic Resource Conservation of Tropical Timber Species, 3–7 May 1999,
Kuala Lumpur and Working Paper for
the National Symposium and Workshop
on Philippine Forest Tree Genetic Resources, 30–31 August, 1999, Makiling
Center for Mountain Ecosystems, UPLB-CFNR College, Laguna, Philippines.
_______. 2000. State-of-the-Art review on
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species in the 130 National Status
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_______. 2002. Research and development
project and capability building on the
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tissue culture. DOST–PCARRD–UPLB.
Annual Report. Laguna, Philippines.
Iqbal, Lutfi. 2009. “Sustainable Forest Management” In. Proc. of an International Conference on the Outlook for
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2007. Chiang Mai, Thailand. Ed. Robin
N. Leslie. FAO Bangkok.
Koffa, S.N. and Garrity, D.P. 2001. ‘Grassroots empowerment and sustainability
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Koshy, M.P., G. Namkoong, P. Kageyama, A.
Stella, F. Gandara, and W.A. Neves do
Amaral. 2002. Decision-making strategies for conservation and use of forest genetic resources. In: J.M.M. Engels, V.A. Rao, A.H.D. Brown and M.T.
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Lanting M, de Chavez S.M. 2002. Seed source
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Ternate, Cavite. DENR–ERDB. Terminal
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Lapitan P.G, Garcia M.U. 1993. Application of
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Lauricio F.M. Jr. 1997. Species trial of selected reforestation species from different
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Lizardo L. 1960. Results of trial planting of
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Malabanan A. 1992. Provenance studies of
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Mantanilla C.L, Melana E.M. 1992. Documentation of mangrove reforestation folk
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Matusalem R.M. 1993. Species trial of selected
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Nasayao E, German E. 1993. Growth and development of mankono (Xanthostemon
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Los Baños, Laguna, Philippines.
Nuevo C.C. 1997. The role of clonal propagation in compensatory forest plantations
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75–79
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Oporto D.A, Umali-Garcia M. 1998a. Clonal
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49
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Quimado M.O. 2002. Characterization of
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_______. 1999. Propagation of Kamagong.
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Lumberman 38(6):25–28. Los Baños,
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_______. 2000. Macro-propagation of dipterocarps through seedlings, wildlings and
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_______. 2006. Developments in dipterocarp
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Tolentino, E. L. Jr. 2009. Status of Philippines
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APAFRI. pp 103-135.
Umali-Garcia M. 1989. Paraserianthes falcataria: Southeast Asia’s growth champion. NFT Highlights September 1989.
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_______. 1995. Forest tree improvement in
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_______. Melegrito L, dela Cruz R.E. 1998.
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_______. 1996. Proposal for a National Tree
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Philippines
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51
Chapter 5
The State of National Programs, Research,
Education, Training and Legislation
T
here are several types of organizations
that are known to be conducting activities
on forest genetic resources conservation.
These are the Department of Environment
and Natural Resources through its Ecosystems
Research and Development Bureau and its
regional field research units (Ecosystems
Research and Development Services, the
academic institutions (e.g., the University of
the Philippines Los Baños, other state colleges
and universities, and private educational
institutions), non-government organizations,
and a few private wood industries in the past.
Fig. 5. Forest genetic conservation and
management framework showing both the
Conservation of forest genetic resources is regarded as constituting the actions and policies
that assure the continued existence, evolution
and availability of these resources in the future.
in situ and ex situ strategies (Pollisco, 2009).
The Department of Environment and
Natural Resources
shows both in situ and ex situ conservation
(botanical gardens, old reforestation projects,
plantations, CSOs, SSOs, SPAs, protected
areas and other forest reserves) on the two
wheels of the bicycle, implying equal attention
to both strategies (Pollisco, 2009).
The DENR management of forest genetic
resources is anchored in its mandate as the
primary government agency responsible for
the conservation, management, development
and proper use of the country’s environment
and natural resources.
The spokes of the driving wheel become the
planting stock production techniques. The
support frame, supporting tree improvement,
conservation, production and management,
consists of research and development, administration and communication.
Forest genetic resources management is likened to a vehicle by which a forestry project
can arrive at the goal set by its management.
The management (DENR) steers the vehicle to
the direction it deems fit. ERDB, PAWB and FMB
have proper places in the driver’s seat. Fig. 5
Funding is necessary to make the vehicle
move while management has both feet planted on the pedals. Apart from funding, support
and strong frames, a forest genetic resources
management program also needs flexible
planning, determination and capacitation from
its staff in order to move towards success.
Philippines
52
Country Report on Forest Genetic Resources
Communities, NGOs, OGAs and other stakeholders are support groups themselves who
eventually become recipients of these forest
genetic resources.
The overall objective is to contribute to the
sustainable management and conservation
of forest genetic resources for the benefit of
stakeholders and end-users.
Specific objectives include the following:
1. integration of forest genetic resources
conservation and management in national
forestry management plans and overall
development plans;
2. enhanced capabilities of manpower resources to use existing innovative technologies for propagation and conservation;
3. increased production of improved planting
materials for production forests;
4. increased planting stocks for biodiversity
conservation; and
5. increased planting materials, especially
indigenous species for urban and highways
greening
The University of the Philippines Los Baños
(UPLB) through its College of Forestry and
Natural Resources, the College of Agriculture,
through the Institute of Plant Breeding with its
National Plant Genetic Resources Laboratory
and the Seed Science and Technology Division,
help promote forest genetic resources conservation and management through education and
extension programs. UPLB has well-equipped
laboratory and field facilities and links with
other research both local and abroad. They
conduct research on germplasm collection,
nursery propagation techniques, micropropagation, evaluation of local and exotic species
for fodder production and socioeconomics.
National Programs on Forest Genetic
Conservation
There are three national program that are
currently being implemented in the country
that have direct and indirect influences on the
conservation of our forest genetic resources.
1. The National Integrated Protected
Areas System (Republic Act No. 7586)
The National Integrated Protected Areas
System (NIPAS) Act of 1992 is the classification
and administration of all designated protected
areas to maintain essential ecological processes
and life-support systems, to preserve genetic
diversity, to ensure sustainable use of resources
found therein, and to maintain their natural
conditions to the greatest extent possible. The
protected areas refer to identified portions of
land and water proclaimed, designated or set
aside by reason of their unique physical and
biological significance, managed to enhance
biological diversity and protected against
destructive human exploitation. These may
be national parks, game refuges, bird/wildlife/
fish sanctuary, wilderness areas, mangrove/
strict nature reserves, watersheds, natural and
historical landmarks, managed landscapes.
The NIPAS Act serves as the legal basis for the
“In Situ” conservation of biological diversity
through the appropriate management of
ecologically important areas for conservation
and sustainable development. It is the
conservation of genetic resources of target
species “on site” within the natural or original
ecosystem in which they occur, or on the site
previously occupied by that ecosystem; it is
with the community of interacting organisms
(with pollinators, seed dispersers, microbial
symbionts) in its natural location.
The objective of NIPAS is to “integrate and
protect outstanding remarkable areas and
biologically important public lands that are
habitats of rare and endangered species
of plants and animals representative of
biogeographic zones and related ecosystems.
Philippines
Country Report on Forest Genetic Resources
According to Sinha (1994), although the NIPAS
Act does not explicitly or directly mention the
term “conservation of genetic resources” (or
any of its variants), such conservation is not
excluded from the management strategy for a
protected area.
Projects for the management of the protected
areas include the Conservation of Priority
Protected Areas Project (CPPAP) funded by
the World Bank and the Global Environmental
Facility (WB–GEF), the National Integrated
Protected Areas Program (NIPAP) funded by
the European Union (EU), and the Samar
Island Biodiversity Project (SIBP) funded by
the United Nations Development Programme
(UNDP) and the GEF. Subsequently, other
conservation projects have come into reality: Administration and Development of
Hinulugang Taktak Protected Landscape, and
Mt. Apo Restoration and Development Project.
Non-government organizations such as the
Haribon Foundation, Inc. and the Conservation
International, the Foundation for Philippine
Environment, and the Philippine Tropical Forests
Conservation Foundation are actively involved
in the restoration and protection works.
As of 2008, there are 234 PAs under the
National Integrated Protected Areas System
(NIPAS) covering a total area of about
5,234 million hectares and a buffer zone of
222,634 hectares. Terrestrial PAs occupy a
total of 4,092,635.87 hectares and a buffer
zone of 202,922.08 hectares while marine
PAs cover about 1,141,918.68 hectares and
a buffer zone of about 19,712.86 hectares
(DENR-PAWB, 2008). Six PAs covering a total
area of 121,668 are under the jurisdiction
of other government agencies, such as
the National Power Corporation, Philippine
National Oil Corporation, and the National
Irrigation Administration. So far, only 10 have
completed the process of establishment by
enactment of site-specific laws. (http://chm.
ph, 30dec2011).
53
2. The National Greening Program
(Executive Order No. 26)
Issued on February 24, 2011, the National
Greening Program (NGP) aims to:
• Implement
sustainable
management
of natural resources through resource
conservation, protection, and productivity
enhancement
• Provide food, goods and services such as
timber, fiber, non-timber forest products,
aesthetic values, air enhancement values,
water regulation values, and mitigate
climate change by expanding forest cover
that serve as carbon sink
• Promote public awareness as well as instill
social and environmental consciousness on
the value of forests and watersheds
The goal of the National Greening Program is
to plant 1.5 billion trees in 1.5 million hectares
of lands of the public domain for a period of six
years from 2011 to 2016.
Premium and indigenous tree species shall be
planted primarily to rehabilitate and/or restore
degraded forestlands and protected areas/
zones while fast-growing and production/
protection forest tree species and fruit trees
shall be planted in agroforestry and production
areas and multiple use zones.
Among the areas targeted for planting under
the program are open forest lands, mangrove
and protected areas, ancestral domains, civil
and military reservations, urban areas under
the Greening Plan of local government units,
inactive and abandoned mines and other
suitable lands.
3. Tree Improvement Activities
The DENR research sector is implementing
various tree improvement activities in the
country which aim to upgrade and enhance
the sustainable sources of quality germplasm
and vegetative materials for planting stock
production of some priority indigenous/
Philippines
54
Country Report on Forest Genetic Resources
endangered species nationwide. While there
is no tree improvement program as yet, the
activities in general are geared towards the
following:
•
Establishment of clonal seed orchard,
ramet/multiplication gardens and conduct
provenance study from the best plus trees/
provenance of identified indigenous/endangered species;
• Development of propagation protocols
(sexual or asexual) of species as guide for
its mass production ;
•
Conduct of monitoring and assessment of
the established clonal seed orchard, ramet
multiplication areas/hedge gardens, and
provenance cum progeny testing in the
regions; and
• Development of database for all verified
seed sources, established clonal seed
orchards,
ramet
multiplication
areas
and provenance/progeny testing sites of
indigenous/endangered species.
To upgrade the quality of seed stands as
source of propagules for breeding and mass
propagation, provenance/progeny trials of
narra (Pterocarpus indicus), molave (Vitex
parviflora), and yemane (G. arborea) were
established in Quezon, Bohol and Davao,
respectively by ERDB in 2009 under its tree
improvement program.
4. Forest and Mountain Biodiversity:
Samar Island Biodiversity Project
(SIBP) (http://chm.ph.,30dec2011)
The project would establish the Samar Island
Natural Park (SINP), a new protected area
zoned for multiple uses centering on protection, but providing for sustainable harvests
of non-timber forest products, and institute a
comprehensive range of ancillary conservation
measures to insulate the Park from human
pressures. Park management would be operationalized in partnership with forest-edge
communities to conserve biodiversity and
reduce poverty among the local communities.
Interventions will strengthen participatory
planning, process-response monitoring, surveillance and enforcement functions, enhance
the conservation management capacities of
communities, impart conservation values
to wider Samareño society, backstop advocacy operations, and abet development of
conservation-compatible village livelihoods.
Implementation will be phased to nurture
nascent conservation processes through to
maturity.
Implementation under Phase 1 was between
the Department of Environment and Natural
Resources, through the Protected Areas and
Wildlife Bureau and the DENR Regional Office
VIII, and the Samar Island NGOs (through
an umbrella organization the Samar Island
Biodiversity Foundation (SIBF). Phase 2
is implemented by the DENR, through the
Protected Areas and Wildlife Bureau, and the
DENR Regional Office VIII through the Samar
Island Natural Park-Protected Area Office.
The implementation of the project was designed to produce the following project outputs: (1) An adaptive management framework
for conservation management is established
and operational; (2) Conservation functions
are fully operationalized; (3) A communitybased conservation framework is tested and
effective; (4) Broad-based awareness of conservation values and management needs is imparted to forest-edge communities and other
key Samareño stakeholders; (5) Conservation
objectives are internalized in sectoral development planning, budgeting and activity delivery
at the provincial and municipal levels; (6)
Alternative, conservation enabling livelihoods
are in place, and the sustainability of wild
resource use is assured, and; (7) Sustainable
financing for recurrent costs of conservation
activities are in place.
5. The Philippine Clearing House
Mechanism for Biodiversity (CHM)
The CHM is established to facilitate the sharing
of data and information on the conservation
and sustainable use of biological diversity
between and among the various stakeholders
Philippines
Country Report on Forest Genetic Resources
in the country. This is part of the Philippine
commitment to the Convention on Biological
Diversity (CBD) which created the Clearing
House Mechanism pursuant to Article 18.3 of
the Convention. The CHM aims to contribute
significantly to the implementation of the CBD
by promoting and facilitating technical and
scientific cooperation among Parties, other
Governments and stakeholders.
Research, Education and Training
Several institutions in the Philippines provide research, education and trainings in
forest genetic resources conservation. Some
are government research institutions. Many
are academic institutions while others are
nongovernment organizations involved in environmental conservation and protection and
sustainable development.
Research
The DENR administration considers Forest
Genetic Resources Conservation and Management as a kind of war which needs to be fought
both at the frontline and at the rearguard at
the same time. In the frontline we need to
meet the demand for fuelwood, construction
materials for housing, furniture and a lot of
other needs, and non-timber resources that
serve as food, raw materials for industries and
others. At the rearguard, we need to be on
the lookout that the remaining forests are protected and conserved. To meet future needs
for wood, the forestry sector must increase
production per unit area without destroying
the natural resource base. Sustainable forest
management is defined in the Helsinki Process
as the stewardship and use of forests and forest land in such a way, and at a rate, that
maintains their biodiversity, productivity and
regenerative capacity, vitality and the potential to fulfill, now and in the future, relevant
ecological, economic and social functions, at
local, national and global levels, and that does
not cause damage to other ecosystems.’
55
fast-gro-wing and high-yielding plantations
are established. The concern for species which
can produce wood with desired properties
requi-ring stability or strength needs should
also be addressed. The production of planting materials for endangered, indigenous
and other forest genetic resources shall be a
primary priority.
The present need is a holistic strategy for wood
production and at the same level prevents the
eminent danger of the irreversible loss of forest genetic resources. The fundamental problem to be addressed at this point is the lack
of supply of improved planting materials for
production purposes, and of planting materials
for conservation of endangered indigenous
and other forest genetic resources.
The DENR research sector is currently implementing research, development and extension
(RDE) projects which can address the abovementioned issues and concerns.
1. Development of strategies for the production
of good quality planting materials:
(a)
for agroforestry and plantations —
Innovative production strategies for
the different priority species should
be operationalized. The propagation
populations (i.e. Seed Sources, Seed
Production Areas, Seedling Seed Orchards,
Clonal Seed Orchards) of the different
priority species for production of improved
planting materials should be maintained.
Land races of exotic species that have
already adapted to local conditions and
endemic/indigenous species and provenances with fast-growth potential
should be identified and tested. Improved
planting stocks (seeds, rooted cuttings,
marcots) should be promoted. Trainings
at different levels/technology transfer
through meetings, publications, etc.
should be pursued.
(b)
for restoration and rehabilitation — Seed
technology and non-mist systems of
propagation by rooted cuttings and the
wildling recovery chamber should be
In order to alleviate the shortage of wood
supply, lighten the pressure from natural
forests and conserve the existing forests,
Philippines
56
Country Report on Forest Genetic Resources
used as applicable or as needed. Hedge
gardens for priority species should be
esta-blished. Seed sources for abundant
seed and other reproductive materials
should be maintained.
11.
12.
(c)
for urban and highways greening
—
Nursery-grown planting materials
through seedlings, wildlings and rooted
cuttings of shrubs and ornamental trees
are produced for distribution to concerned
entities. Technical assistance to sectors
engaged in urban greening is provided
if necessary. Remnants of urban vegetation in wetlands, lakes, streams and
coastal areas have to be inventoried and
protected. The urban populace should be
educated on the role of trees and related
plants in the urban ecosystem.
1. Rehabilitation and ecological restoration
of marginal and degraded landscapes
and seascapes.
2. Determination of carrying capacities of
various areas/sites for resources conservation, ecotourism and sustainable development (e.g. PAs, CBFMAs, CEP)
3. Vulnerabililty assessment of priority watersheds in the Philippines
4. Tissue culture of genetically superior
narra (Pterocarpus indicus)
5. Molecular level analyses of some tree
species and non-wood forest species
6. Determination of growth, structure and
composition of third-growth dipterocarp
forest in areas under active Timber License Agreement and Industrial Forest
Management Agreement
7. Tree improvement of indigenous and
endangered species to upgrade and enhance the sustainable sources of quality
germplasm and vegetative materials for
planting stock production
8. Application of mycorrhiza and other
soil amelioration measures to improve
refo-restation and agroforestry in upland
areas
9. Tree health assessment of important forest tree species as seed sources
10. Biosafety measures for the protection of
biodiversity against the potential impacts
of products of modern biotechnology or
GMOs
Biosecurity measures for the protection
of biodiversity from invasive species
In situ conservation of rare and endangered flora and fauna species in selected
protected areas in the Philippines.
Likewise, academic institutions also conduct their own RDEs. The University of the
Philippines Los Banos College of Forestry and
Natural Resources conducts researches on
seed technology, vegetative propagation and
other aspects of forest production especially
on indigenous trees like the dipterocarps. The
Leyte State University (LSU) developed the
technology on rainforestation, a strategy of
forest restoration that uses indigenous tree
species in combination with agricultural crops.
Nueva Vizcaya State University (NVSU),
in collaboration with the local Ecosystems
Research and Development Sector (ERDS)
in Bayombong, Nueva Vizcaya also conducts
establishment of arboretum and dipterocarp
plantation. Gascon (2005) reported that
the Southern Luzon Polytechnic University
(SLPU) is establishing the database for the
Mt. Banahaw protected area, a nursery of
indigenous tree species, conducts species trials using indigenous species, and are active
members of the Protected Area Management
Board (PAMB) of Quezon. The Misamis Oriental
State College of Agriculture and Forestry
(MOSCAT), the Central Visayas State College
of Agriculture, Forestry and Technology
(CVSCAFT), The Mindanao State University
(MSU), Central Mindanao University (CMU)
and even the Camarines Sur State College
of Agriculture and Forestry (CSSAC), Isabela
State University (ISU), DMMSU and a lot of
other state universities and colleges are very
active in doing different aspects of research
in FGRs. The De La Salle University system is
also doing work on ex situ conservation and
even in situ conservation of Philippine teak,
in collaboration with the Mindoro Biodiversity
Conservation Foundation.
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Country Report on Forest Genetic Resources
57
Education
4. Visayas State University
Education on FGR is available in academic
institutions through courses that are related in
forestry or environment, in general. Government
institutions as well as nongovernment organizations also provide training activities pertaining to FGR to a certain extent, depending on
their programs/projects.
The programs of the Visayas State University
(VSU) in instruction, research, extension and
production converge and complement each
other to help make Philippine agriculture globally competitive and sustainable. VSU started
rainforestation as a farming technology developed by its Applied Tropical Ecology Program
through a joint research project of the Philippine-German Applied Tropical Program. Realizing that reforestation failed to restore the
lost forests and created a negative impact on
biodiversity, VSU saw the need to restructure
the ideology behind reforestation by planting
native species instead of exotic ones. In addition, the Q-seedling project of CNFR VSU with
support from ACIAR established field trials of
combined species of dipterocarps, gmelina,
mahogany, falcata and other indigenous species in five sites in Southern Mindanao and Leyte
Island. The Q-seedling project research also
contributed in the development of a national
policy on nursery accreditation and qua-lity
seedling production (DAO 2010-11 known as
“Revised Regulations in Governing Forest Tree
Seed and Seedling Production, Collection and
Disposition).” Hands-on trainings on nursery
establishment and quality seedling production
were also conducted in Southern Leyte, Leyte
province, Region 10 and Southern Mindanao,
thereby contributing to the FGR conservation
initiative of the Philippine go-vernment.”
Academe
Private Schools
1. Silliman University (SU)
SU is known for its biological research activities. Biodiversity has already been integrated
in most of their courses. It has the Center for
Tropical Conservation Studies and the Museum
of Natural History.
State Colleges and Universities
2. Southern
(SLPU)
Luzon
Polytechnic
University
SLPU’s main campus is located at the foothills
of Mt. Banahaw in Lucban, Quezon. It has
been active in biodiversity conservation of
the Mt. Banahaw-San Cristobal National Park.
Many indigenous plant species have been documented in these areas with the leadership
of SLPU.
5. Mindanao State University – Iligan
Institute of Technology (MSU-IIT)
3. Central Bicol State University of
Agriculture (CBSUA)
Formerly the Camarines Sur State Agricultural
College, CBSUA is one of the premier institutes of higher learning in the Bicol Region.
Biodiversity conservation has already been
integrated in some of its courses. It has formulated protocols for biodiversity research
grants and developed training courses on biodiversity conservation education and research
methodology.
MSU-IIT has conducted research projects
related to the biodiversity conservation in Mt.
Malindang and the Agusan Marsh in Mindanao.
6. Central Mindanao University (CMU)
CMU has a broad capacity and experience in
forestry and natural resources management.
Its Department of Biology conducted an
inventory of all plant species in the Kitanglad
Philippines
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Country Report on Forest Genetic Resources
National Park under the Sustainable Agriculture
and Natural Resources Management Project
with the World Agroforestry Centre (ICRAF) as
the principal investigator.
the Department of Science and Technology. It
is also accredited with the DENR and the United
States Agency for International Development
as a private voluntary organization.
7. Misamis Oriental State College of
Agriculture and Technology (MOSCAT)
In the pursuit of conservation through community-based resource management, Haribon
adopts an integrated, multidisciplinary approach that is participatory and scientifically
sound. Its programmes include science and
research, community-based resource management, environmental defense, and membership development.
MOSCAT’s College of Agriculture has a fouryear degree program on forestry. It is involved
in the domestication of fruit, timber and
multipurpose tree species as well as in the
diversification of timber species to include
indigenous ones. It has extensive field facilities
for research.
8. University of the Philippines Los Baños
(UPLB)
This university offers a four-year course on
forestry with different specializations. It also
has other courses on environment and natural
resources. It has both undergraduate and
graduate programs. The College of Forestry
and Natural Resources offers on Forest
Genetics, Forest Tree Improvement (Basic
and Advanced Courses), Clonal Forestry,
Conservation Biology, and a few others that
have bearing on forest genetic resources
conservation. Graduate programs on Forest
Tree Improvement and the Master of Science in
Natural Resources Conservation are curricular
programs that relate directly to FGR. The
College of Agriculture on the one hand has also
instituted a curricular program on Plant Genetic
Resources, and has for a long time already
been offering courses on Plant Breeding and
related sciences. It has also started a program
on Agricultural Biotechnology.
Non- Government Organizations
1. Haribon Foundation, Inc.
Haribon is regarded as a pioneer of the
environmental movement and one of the
most active environmental organizations in
the Philippines. In 1984, it was registered as
a science and research foundation conducting
floral and faunal studies and is accredited by
On December 21, 2005, the European
Commission (EC) awarded a five-year project
grant (2005-2010) to the Haribon Foundation.
The project is entitled Governance and Local
Development for Endangered Forests or
GOLDEN Forests.
The project aims to reduce the rate of
deforestation in Mts. Irid-Angelo in the provinces of Quezon, Aurora, Bulacan and Rizal;
Mts. Hilong-Hilong and Diwata in Agusan,
and Surigao; and Zambales mountains in
Zambales, Tarlac and Pangasinan. Economic
support for the marginalized forest-dependent
communities living in these areas is part of the
project assistance package. (www.haribon.
org)
2. Soil and Water Conservation Foundation,
Inc.
SWFC promotes natural and human resource
development through implementation of projects and programs which are participatory,
cooperative, community-building and sustainable. One of its goals is the establishment and
perpetuation of comprehensive environmental
ethics in individuals and communities which
leads to wise use, management, and conservation of the country’s resources.
3. Bantay Kalikasan
Bantay Kalikasan (Nature Watch) or BK,
ABS-CBN Foundation Incorporation’s environmental arm, started on July 21, 1998. It is
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Country Report on Forest Genetic Resources
a media-based project supported by a multisector network of government agencies, private institutions, and non-government organizations. It was launched to serve as a catalyst
in addressing the concern over the worsening
state of the Philippine environment characterized by air and water pollution, denudation of
forests, irresponsible waste disposal and their
life-threatening effects.
BK was one of the prime-movers of Mt Banahaw
rehabilitation and protection. It made possible
the temporary suspension of visits to Mt.
Banahaw because of the destruction to the
area.
BK is also known for its successful rehabilitation
and protection of the 2700-hectare La Mesa
Watershed, the last forest of its size within
Metro Manila and the source of water for over
12 million people in Metro Manila.
When BK first arrived in La Mesa, there were
only about eight plant species in existence:
Acacia auriculiformis, A. mangium, Gmelina
arborea, Mahogany (Sweitenia macrophylla),
African tulip (Spathodea campanulata),
Eucalyptus, and Teak (Tectona grandis).
Today, there are 73 different endemic species
planted in the La Mesa Forest – Nature Reserve
with an over-all survival rate of 92.5%, the
first reforestation project in the country
to plant that number of Philippine species.
(http://www.bantaykalikasan.com).
.
4. Agroforestry Tree Seed Association of
Lantapan
ATSAL operates in Bukidnon province, southern
Philippines. The association was organized in
1998 through the help of the World Agroforestry Centre (ICRAF). Farmers were trained
on germplasm collection, processing and
marketing of agroforestry tree seeds and
seedlings. ATSAL has been marketing various
tree seeds and seedlings with apparent success,
and has provided training on appropriate seed
collection and nursery management to farmers, government technicians, and workers
from nongovernment organizations (NGOs).
59
5. Philippine Tropical Forest Conservation
Foundation, Inc.
PTFCF was established under two bilateral
agreements between the governments of the
United States (US) of America and the Republic
of the Philippines (RP) under the US Tropical
Forest Conservation Act. These agreements,
signed on September 19, 2002, leveraged a
$5.5 million USG appropriate to treat $41.5
million in RP-US debt and divert $8.25 million
in peso-denominated interest payments over
14 years, to the Tropical Forest Conservation
Fund. The Fund is administered by an NGOled Board comprising five representatives of
the non-governmental sector appointed by
the RP, two representatives of the US, two
representatives of the RP.
This organization aims to, in the spirit of
service and stewardship, improve the status of
Philippine forests by working with communities,
catalyzing local and national actions for their
sustainable management.
6. BINHI Program of the Energy Development
Corporation
The Energy Development Corporation launched
in 2008 the BINHI Program, a forest revegetation scheme that focuses on the planting of
endangered tree species. The program has
four project components namely: Trees for
Life, Trees for Food, Trees for the Future, and
Trees for Leisure. The first component adopts
the practice of rainforestation farming, giving
emphasis on assisted natural regeneration
with the basic intent of bridging forest gaps.
The establishment of the forest bridges are
being undertaken in the Northern part of the
Sierra Madre Natural Park and the Mt. Kanlaon
Natural Park.
The Trees for Food attempts to revegetate open
and denuded lands through forest plantations
and agroforestry. This is with the recognition
that agroforestry brings about farm diversification and makes possible as well tree domestication. Agroforestry, likewise, can increase
connectivity in patches within a fragmented
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Country Report on Forest Genetic Resources
forest landscape which benefits biodiversity.
Enrichment of species and genetic diversity
can be achieved under this project.
The Trees for the Future concentrates on urban
reforestation making use of endangered tree
species. Public parks, school premises, leisure
estates and residential areas, and other open
spaces in urban areas are target for this
reforestation scheme. Last but not the least is
the Trees for Leisure project which establishes
ecotourism forest parks. Focus again will be
the planting of native endangered species in
such areas.
7. Foundation for Philippine Environment
The Foundation for the Philippine Environment
(FPE) was organized to help reverse the rapid
destruction of the Philippine natural resource
base through a strategic and integrated conservation program. Its mandate is to help
fund the initiatives of Philippine civil society
(i.e. non-governmental organizations (NGOs),
people’s organizations (POs) and other
related sectors in conserving biodiversity and
intervening to stop the further degradation
of priority biodiversity sites. Over the recent
10 years, FPE continuously supported the
implementation of community-based resource
management (CBRM) framework in 22 sitefocused projects in Mindanao, Visayas and
Luzon. FPE, from time to time, engages and
also funds research institutions to collaborate
with civil society and local project partners.
The resulting experiences, including data and
information, are used by FPE to plan, decide,
fund and implement present and future
biodiversity projects.
Training
Institutions concerned with forest genetic
resources are given opportunities for free education and training on forest genetic resources
mostly offered by international organizations
such as the ASEAN Centre for Biodiversity,
among others. There are also local institutions
that provide education and trainings in FGR.
DENR has always been involved in educating and
communicating to the public the importance of
biodiversity conservation. State colleges and
universities, on the other hand, continue to
promote programs on biodiversity conservation
through instruction, research and extension.
Many publications on the conservation of forest
genetic resources or even the conservation
publications are in technical form which prevents ordinary citizens and uneducated locals
to comprehend the message. Efforts are now
underway to produce information, education
and communication materials in local dialects to promote a widespread education
and communication of FGR conservation.
Hopefully, these efforts, which are done on a
national scale, will inculcate the importance of
biodiversity conservation among the general
public and lead to support for more in-depth
studies at the species and genetic levels.
Based on an earlier assessment by Zabala
(1996), there is a dearth of capable personnel
to tackle the challenging task of tree breeding
and improvement. Intuitively, the situation is
similar for the conservation of forest genetic
resources, as these two concerns are closely
related. Prior to 1996, there were hardly any
researcher trained either on tree improvement, or the conservation and management of
forest genetic resources. After 1996, a number of graduate students have enrolled at the
College of Forestry and Natural Resources and
specialized in tree improvement. With a global
and national concern for biodiversity conservation, the interests of younger scientists are
slowly catching up with the trend to major in
the conservation of forest genetic resources.
The UPLB has a graduate program focusing
on Plant Genetic Resources Conservation, but
most of the students and faculty involved are
agriculture-based.
Capability-building needed by institutions to
promote and enhance FGR Conservation are
as follows:
• Education and Training on plant genetic
diversity and conservation of FGR
Philippines
Country Report on Forest Genetic Resources
• Public Awareness (Information Education,
Campaign) through improved libraries,
popular and technical publications, lectures,
seminars, workshops and conferences
• Resource mobilization to support FGR
Conservation activities
• Management Information System (MIS)
• Inclusion of FGR Conservation in academic
curriculum
• Other extension programmes – demo
farms, cross site visits
• Establish a system, including websites,
which will ensure a constant exchange of information on the genetic resources of Philippine plants between and among concerned
institutions and organizations, and make
this information accessible to all interested
parties
Training obstacles and what can be done
In the report of Tolentino (2009) on the status
of conservation and management practices
of FGR in the Philippines, the result of the
2007 national consultative workshop on FGR
identified the country’s capability building
needs on FGR conservation as follows:
1. Capability building:
• Education and training
• Public awareness (information, education,
and communication)
• Resource mobilization to support FGR
conservation activities
• Management information system
• Inclusion of FGR conservation in academic
curriculum
• Other extension programs – demonstration
farms, cross site visits
2. Training courses
• Strategies on FGR conservation (in situ, ex
situ) and results of R&D technology
• Stakeholders’ participation in FGR conservation
• Advocacy of FGR conservation – policy
makers, implementers of conservation activities, e.g., forest managers, community,
academe
61
• Product utilization, processing and marketing
• Policy issues on FGR conservation – bioprospecting, biosafety
Tolentino (2009) further enumerated the
following critical gaps in research and development that were identified in the said
national consultative workshop:
1. Continuing assessment of conservation status of all FGRs (e.g., inventory, taxonomy,
database of FGR on in situ conservation
sites)
2. Conservation biology (reproductive biology)
3. Ecological studies of FGRs (carbon sink,
watershed and environmental services,
ecotourism genetic diversity)
4. Policy assessment and formulation in support of FGRs (e.g., bio-prospecting, rescue
centers)
5. Development of a guidebook for identifying
FGRs
6. Valuation studies of FGRs (for bio-prospecting purposes, ecological services, etc.)
7. Assessment of socio-economic and cultural practices and their impacts to FGR
conservation (e.g., ethnobotany)
8. Production technologies or silvicultural requirements for FGRs
Strategy to address education and training
needs
In 2003, the Philippine Plant Conservation
Committee prepared the Framework for the
Philippine Plant Conservation Strategy and
Action Plan to serve as the National Red List
Authority of the Philippines on plants. It has
been formulated in response to the Global
Strategy for Plant Conservation and the
country’s commitment to the Convention on
Biological Diversity.
In the Framework, capacity building is the
focus of Objective 8 which includes physical
and technological infrastructure and financial
support for plant conservation. Specifically, its
actions aim to:
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Country Report on Forest Genetic Resources
1. Establish a roster of plant experts and
agencies, research institutions and organizations involved in plant conservation in
the country
2. Provide career opportunities for botanists
and plant taxonomists
3. Assess the plant taxonomic needs of the
Philippines
4. Develop centers of excellence on plant
conservation
5. Implement technical capacity building
programs on plant conservation and
management (e.g., trainings on plant
identification, preservation, etc., at the
national, regional and local levels)
6. Identify and implement appropriate community training programs.
Legislation
The Philippines has promulgated several
national policies and legislations concerning
conservation, protection and proper utilization
of its natural resources. The following are
examples of government laws which are
directly or indirectly related to the protection
and conservation of forest genetic resources.
The Philippine Constitution
The Philippine constitution includes provisions
related to forest resources:
(1)
Protection and achievement by the
State of the right of all Filipino people
to a balanced and healthful ecology in
accordance with the rhythm and harmony
of nature (Sec. 16, Art. II); framework
of national unity and development (Sec.
22, XI);
(2)
State of ownership of all natural resources
and inalienability, except for agricultural
lands (Sec. 2, XII);
(3)
Full control and supervision by the
State on exploration, development, and
utilization of natural resources either by
directly undertaking such activities or by
entering into co-production, joint venture
or production-sharing agreements with
Filipino citizens or Filipino owned or
controlled corporations or associations
(Sec. 2, XII);
(4)
Small scale utilization of natural resources
(Sec. 2, XIII);
(5)
Determination by Congress of the specific
limits of forest lands by marking of their
boundaries on the ground (Sec. 4, XII);
(6) Protection of the rights of indigenous
cultural communities (ICC) by the State
to their ancestral lands to ensure their
economic, social, and cultural well being
(Sec. 5, XII).
Of the seven provisions by the Philippine
constitution, Article XII of the sections 4 and
5 are relevant to the conservation of tree
species.
National Legislations and Policies
Affecting Genetic Resources
Conservation
The growing concern for the environment and
proper utilization of the natural resources for
economic development have resulted in the
enactment of policies which advocate the
protection of the country’s resource base.
Specific policies and legislations and the status
of their implementation are briefly listed in the
following:
Act No. 315 and the Republic Act No. 826
Enacted in 1932, Act No. 315 is one of the
earliest legislations related to biodiversity
conservation and management. It provides for
the establishment of national parks; for example, game refuges with panoramic, historical,
scientific or aesthetic values for the benefit
and enjoyment of the Philippine people. The
law prohibits occupation of the national parks
and harvesting of timber or other forest products and wildlife resources therein without
permit or license. It was one of the earlier accounts on natural resources management that
Philippines
Country Report on Forest Genetic Resources
consi-dered the principle of inter-generational
res-ponsibilities.
Through the Republic Act No. 826, a
Commission on Parks and Wildlife was created in 1952 under the supervision of the
President in order to promote effective planning, development, maintenance and supervision of natio-nal parks, monuments, wildlife
and game re-fuges and bird sanctuaries. The
same act also promotes the establishment and
conservation of provincial, city and municipal
parks to comply with the fundamental purpose
of national parks for the benefit and enjoyment of the future generations. It was one
of the earlier accounts on natural resources
management that considered the principle of
inter-generational responsibilities.
Presidential Decree No. 705
This law, enacted in 1975, provides the major
framework for the management, conservation
and utilization of the forest resources in the
country. The law mandated the Bureau of Forestry
Development (BFD) with the responsibility for
protection, development, management and
preservation of national parks, game refuges
and wildlife. The law declares the occupation
of national parks and recreation and vandalism
activities therein illegal.
The Philippine Forestry Code or PD 705
remains as the primary legal instrument guiding the conservation and utilization of forest
resources in the country. Legal issuances cover
the protection of specific areas with rich natural resources. These include RA 7611 (1991)
which declared a Strategic Environmental Plan
(SEP) for Palawan. The Plan calls for the conservation, utilization and development of such
natural resources in tandem with the provision
of optimum yield on a continuing basis. This was
followed by the DENR AO 45 (1992) which declared a moratorium on all commercial logging
in Palawan. Proclamation No. 926 is another
conservation-oriented legal issuance establishing the Subic Watershed Forest Reserve. The
DENR AO No. 25 (1991) prohibited logging from
old-growth or virgin forests and declared these
63
areas as part of the integrated protected areas
systems. Likewise, large tracts of mangrove
areas all over the country have been declared
wilderness areas, thus, limiting the extraction of
forest resources in these areas.
In 2000, the DENR AO 2000-44 allowed the
sustainable use of forest resources inside
multiple-use and buffer zones, except any
form of logging or timber cutting involving the
natural forest. Subsequently, the DENR AO
2002-02 provided an opportunity to organized
tenured migrant communities and interested
indigenous peoples to manage, develop, utilize, conserve and protect the resources in
designated Community-based Program (CBP)
area. These opportunities are subject to prior
vested rights, with activities consistent with
the Protected Area Management Plan (PAMP).
Additional guidelines were later spelled out in
the DENR AO 2004-32 which provide tenured
migrant communities and interested peoples
within protected areas and buffer zones tenure
over established CBP areas, provided that the
activities to be undertaken are consistent with
PAMP.
Memorandum Circular (MC) 2004-06 of DENR
adopts the so-called rainforestation technology
to restore, manage and rehabilitate degraded
and secondary forest in protected areas and
other appropriate forest lands. Indigenous
and endemic tree species are the recommended species for planting. The DENR MC 200702 provides the guidelines for the establishment and management of critical habitats in
the country which will cover public lands (terrestrial and wetland areas) outside protected
areas as well as privately-owned lands where
threatened species are found.
Executive Order No. 192
Through the Executive Order No. 192, the
Department of Environment and Natural
Resources (DENR) is tasked with the primary
res-ponsibility to promote the well-being
of the Filipino people through sustainable
development of natural resources, optimal
utilization of forest lands, social equity and
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Country Report on Forest Genetic Resources
efficiency of forest resource use and effective
forest management. The Order created,
among others, the Protected Area and Wildlife
Board (PAWB). The aim was to consolidate
governmental efforts in the conservation
of natural biological resources, specifically
through the institutionalization of the National
Integrated Protected Areas System (NIPAS).
The enactment of the NIPAS Law or Republic
Act (RA) of No 7586 of 1992 was pursued by
PAWB.
Republic Act No. 7586 (the NIPAS Law)
The most important piece of legislation on
biodiversity in the country is the RA 7586,
enacted in 1992, otherwise known as the
National Integrated Protected Areas System
(NIPAS) law, which mandated DENR in its implementation. It contained the twin objectives
of biodiversity conservation and sustainable
development.
As early as 1998, 34 protected areas were
proclaimed under the NIPAS category, encompassing 1,443,000 ha. The regional offices of
DENR also identified 25 old-growth and mossy
forests that have been proposed for inclusion
in the protected area system. In the same
year, the Protected Area and Wildlife Board
(PAWB) designed the Biodiversity Monitoring
System (BMS) for data collection focusing
on priority species and their utilization. In
2000, the BMS was institutionalized through
the issuance of the Administrative Order (AO)
No. 13 of DENR, entitled “Guidelines on the
Implementation of the Biodiversity Monitoring
System in Protected Areas”. The system serves
to improve the participation of communities in
the protected areas and other stakeholders in
the management of protected areas.
Executive Order No. 247 (the Bioprospecting
Law)
The Executive Order No. 247, enacted in 1995,
meant to provide a regulatory framework
for bioprospecting, the exploitation of indigenous knowledge on natural resources or the
search for previously unknown compounds for
medi-cinal use. Also called the Bioprospecting
Law, it prescribes the guidelines and establishes a regulatory framework for the bioprospecting of biological and genetic resources, their
by-products and derivatives for scientific,
commercial and other purposes. This law is
in line with the provisions of the Convention
on Biological Diversity (CBD) to which the
Philippines is a signatory. The law declares:
“It shall be the policy of the State to regulate
the prospecting of biological and genetic
resources to the end that these resources
are protected and conserved, are developed
and put to the sustainable use and benefit of
the national interest. Further, it shall promote
the development of local capability in science
and technology to achieve technological selfreliance in selected areas.”
Republic Act No. 9147 (the Wildlife Resources
Conservation and Protection Act)
This legislation, enacted in 2001, provides
for the conservation and protection of wildlife
resources in protected areas and critical
habitats. It is also known as the Wildlife
Resources Conservation and Protection Act.
The law assigns jurisdiction over terrestrial
plants and animal species to DENR and over
aquatic plants and animals to the Department
of Agriculture (DA). The DENR Secretary will
determine whether any wildlife species or
subspecies are threatened and classify them as
critically endangered, endangered, vulnerable
or under other categories based on scientific
data and internationally accepted criteria. The
act allows the collection of wildlife for scientific
or breeding propagation purposes, and for the
breeding or propagation of threatened species
to enhance their populations in natural habitats
(restoration purposes) and establishment
and protection of critical habitats outside
protected areas where the threatened species
are found. The National List of Threatened
Philippine Plants and their categories, and the
List of Other Wildlife Species were established
through the DENR AO 2007-01. Subsequently,
the DENR AO 2007-02 was issued to provide
the guidelines on the establishment and
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Country Report on Forest Genetic Resources
management of critical habitat for species
under the jurisdiction of DENR.
Republic Act (RA) No. 7942 or the Mining Act
of 1995
This RA identified areas closed to mining
operations. These include all areas expressly
prohibited by RA No. 7586 and its implementing rules and regulations (DAO No. 25 series
of 1992) and other laws. These areas closed to
mining include old growth forests, proclaimed
watershed, wilderness areas, mangrove
forests, mossy forests, national parks, provincial and municipal forest, greenbelts, game
refuges and bird sanctuaries among others.
65
on field observations, the actual implementation of these policies is the big hindrance to
successful conservation efforts.
Executive Order 578
Issued in the latter part of 2006, this is the
policy of the state on biological diversity. It
specifically states that “it is the policy of the
state to protect, conserve, and sustainably
use biological diversity to ensure and secure
the well-being of the present and future
generations of Filipinos. This state policy
extends to all the components of biodiversity
– ecosystem, species and genes.”
Executive Order 26
Republic Act No. 7303 (the Seed Industry
Development Act)
The Seed Industry Development Act of 1992
promotes and accelerates the development
of seed industry and mandates the conservation, preservation and development of plant
genetic resources in the Philippines. It vests
the University of the Philippines, Los Baños
(UPLB), with leadership in plant biotechnology activities related to plant improvement,
conservation of genetic resources and in vitro
mass production of planting materials including biotechnology.
Executive Order No. 318
Issued on June 9, 2004, this order declared the
policy of government to pursue the sustainable management of forests and forestlands
in watersheds. Watersheds shall be deemed
as ecosystem management units and shall
be managed in a holistic, scientific, rightsbased manner and observing the principles of
multiple-use, decentralization and devolution,
and active participation of Local Government
Units (LGUs), synergism of economic, ecological, social, cultural objectives, and the rational
utilization of all resources found therein.
Clearly, policies are set in place to insure
protection of biodiversity in the Philippines
including forest genetic resources but based
Issued on February 24, 2011, the National
Greening Program (NGP) aims to:
•
Implement sustainable management of
natural resources through resource conservation, protection, and productivity
enhancement
• Provide food, goods and services such as
timber, fiber, non-timber forest products,
aesthetic values, air enhancement values,
water regulation values, and mitigate climate change by expanding forest cover
that serves as carbon sink
• Promote public awareness as well as instill
social and environmental consciousness on
the value of forests and watersheds
The goal of the National Greening Program is
to plant 1.5 billion trees in some 1.5 million
hectares of lands of the public domain for
a period of six years from 2011 to 2016. In
2011, the Department of Environment and
Natural Resources, other state agencies, local
governments, private sector and civil society
planted 83,096,223 seedlings in more than
118,939.93 hectares of land nationwide under
the national greening program.
Premium and indigenous tree species shall
be planted primarily to rehabilitate or restore
degraded forestlands and protected areas/
zones while fast-growing and production/
Philippines
66
Country Report on Forest Genetic Resources
protection forest tree species and fruit trees
shall be planted in agroforestry and production
areas and multiple use zones.
Among the areas targeted for planting under
the program are forestlands, mangrove and
protected areas, ancestral domains, civil and
military reservations, urban area under the
Greening Plan of local government units,
inactive and abandoned mines and other
suitable lands.
Executive Order No. 514 - The National
Biosafety Framework (March 17, 2006)
The Framework prescribes its implementation guidelines, strengthening the National
Committee on Biosafety of the Philippines and
for other purposes. It covers all work involving genetic engineering and the importation,
introduction, field release and breeding of organisms that are potentially harmful to people
and environment. The departments concerned
shall allocate from their present budgets such
amount as may be necessary to implement
the NBF, including the support in the operations of the National Committee on Biosafety
of the Philippines and its secretariat.
Administrative Order No. 1 - Guidelines for
Bioprospecting in the Philippines (January 14,
2005)
It is a joint order among the Department of
Environment and Natural Resources (DENR),
Department of Agriculture (DA), Philippine
Council for Sustainable Development (PVSD),
and the National Commission on Indigenous
People (NCIP). The Guidelines set a uniform
procedure for evaluating and granting access
to biological resources and avoid the potential
problem of inconsistency of bioprospecting
regulations for various components of biodiversity under the management jurisdiction of
different government agencies. It provides
equitable sharing scheme for benefits derived
from bioprospecting activities among the government and the host communities or resource
providers.
DENR Administrative Order No. 2004-32 Revised Guidelines on the Establishment and
Management of Community-Based Program
in Protected Areas (August 31, 2004)
It emphasizes the use of endemic and/or indigenous plant species in specific areas within
the protected areas or buffer zone to return
them back to the original vegetation type.
DENR Administrative Order No. 2004-15
This AO established the list of threatened
species and their categories and the list of
other wildlife species under the jurisdiction of
the DENR pursuant to RA 9147, the Wildlife
Resources Conservation and Protection Act.
DENR Memorandum Circular No. 2004-06
This MC promulgated the guidelines in the
integration of rainforestation farming strategy
in the development of open and denuded areas
within protected areas and other appropriate
forest lands (August 5, 2004).
It defines rainforestation as a concept in
forest restoration, wherein only indigenous
and endemic tree species are used as planting
materials which include but is not limited to
dipterocarp species, premium tree species,
etc. it aims to preserve biodiversity and
expand Philippine forests and simultaneously
sustain human food production.
DENR Administrative Order No. 2003-05
This revoked Memorandum Order No. 9929 and DAO No. 2001-03: It provides the
Guidelines in the implementation of rights in
tree farming.
The other policy issuances of the government
in relation to the use and conservation of
forest genetic resources in the country over
the period 2000 -2011 appears as Appendix
Table 8 of this report.
Philippines
Country Report on Forest Genetic Resources
Center Project, MuakLek,
Thailand. pp. 214–220.
Needs for Developing Forest Genetic
Resources Legislation
Although there are already existing legislations
and policies affecting forest genetic resources
conservation, there are still needs to further
develop or strengthen forest genetic resources
legislation in the country. The identified needs
are given in Table 14.
References
Sinha, C.C. 1994. Implications of the NIPAS
law for the conservation of forest
genetic resources in the Philippines. In:
Drysdale R. M., John S.E.T. and Yapa
A.C. (Eds.). Proceedings: International
Symposium on genetic conservation
and production of tropical forest tree
seed. ASEAN-Canada Forest Tree Seed
Saraburi,
Tolentino, E. L. Jr. 2009. Status of Philippines
forest genetic resources: their conservation and management practices. In:
Forest Genetic Resources Conservation
and Management: Status in seven South
and Southeast Asian countries. Editors
R. Jalonen, K.Y. Choo, L.T. Hong and
H.C. Sim. A publication of APFORGEN.
FRIM, Bioversity International and
APAFRI. pp. 103-135.
Pollisco, M.T. 2009. Research and Development
Initiatives on Forest Genetic Resources
Conservation in the Philippines. In:
Forest Genetic Resources Conservation
and Management: National Consultative
Workshops of Seven South and
Table 14. Needs for developing forest genetic resources legislation.
Priority Level
Needs
67
Not
applicable
Low
Improve forest genetic resources
legislation
Moderate
High
√
√
Improve reporting requirements
√
Consider sanction for non-compliance
Create forest genetic resources targeted regulations
√
Improve effectiveness of forest genetic
resources regulation
√
Enhance cooperation between forest
genetic resources authorities
√
Create a permanent national commission for conservation and management
of forest genetic resources
√
Others (please specify)
Philippines
68
Country Report on Forest Genetic Resources
Southeast Asian Countries. Editors K.Y.
Choo, R. Jalonen, L.T. Hong and H.C.
Sim.FRIM, Bioversity International and
APAFRI. pp. 106-125.
Internet
http://chm.ph/index.php?option=com_co
ntent&view=article&id=68:for
est-and-mountain-biodiversityo v e r v i e w & c a t i d = 3 6 : b i o d i v e r s i t yi n-the-phi l i ppi nes&Itemi d= 90_30
dec2011
http://chm.ph/index.php?option=com_co
ntent&view=article&id=185%3Af
orest-and-mountain-biodiversityprojects&catid=87&Itemid=90
http://forestry.denr.gov.ph/ncfp.htm
http://ptfcf.org/
http://www.asiaforestnetwork.org/pub/
pub05.htm
http//www.bantaykalikasan.com/about.
php?section=1
http://www.fao.org/docrep/005/AC648E/
ac648e09.htm
http://www.haribon.org
http://www.worldagroforestry.org/downloads/publications/PDFs/WP08153.pdf
Philippines
Country Report on Forest Genetic Resources
69
Chapter 6
The State of Regional and
International Collaboration
Regional and Sub-Regional Collaboration
T
he DENR’s Ecosystems Research and
Development Bureau (ERDB) implemented
the UNDP/FAO/RAS/91/004 Regional Project
on Improved Productivity of Man-Made Forests
through the Application of Technological
Advances in Tree Breeding and Propagation
(FORTIP) in 1991 which became the avenue
in ERDB’s international linkages regarding
forest genetic resources. The country has
developed linkages with CIFOR, IDRC, JICA,
IPGRI, AIDAB, INBAR, ASEAN FTSC, DANIDA
FSC, FORSPA, APAN, etc. The Project paved
the way for the ASEAN member countries do
develop/establish international linkages with
the Regional/International Networks, Centers,
and donor agencies.
The Philippines hosts the ASEAN Centre for
Biodiversity (ACB). As an intergovernmental
regional centre of excellence, ACB facilitates
cooperation and coordination among the 10
ASEAN Member States (Brunei Darussalam,
Cambodia, Indonesia, Lao PDR, Malaysia,
Myanmar, the Philippines, Singapore, Thailand,
and Vietnam) and with relevant national governments, regional, and international organizations on the conservation and sustainable
use of biological diversity, and the fair and
equitable sharing of benefits arising from the
use of such natural treasures.
Over the years since its creation as the progeny
of the ASEAN Regional Centre for Biodiversity
Conservation, the ACB has become and is still
the primary venue for the discussion and resolution of cross-country biodiversity conservation issues. It has been the leading force in
capacity development of the ASEAN Member
States, for policy development and coordination through education on key biodiversityrelated multilateral environment agreements,
as well as increased knowledge and skills to
assess regional/national situations and develop appropriate response mechanisms. ACB
also aims to enhance competence of Protected
Area managers of the ASEAN Member States
through the conduct of capacity building series workshops and conferences with partner
institutions.
In collaboration with CSIRO Division of
Forestry’s Australian Tree Seed Centre
(ATSC) in 1996-1998, ERDB was able to
establish seed production areas (SPAs)
and seedling seed orchard (SSO) of Acacia
mangium and Eucalyptus urophylla as follows:
1.5 ha A. mangium SPA (ATSC seedlots); 1.5
ha E. urophylla var wetarensis SPA (ATSC
seedlots); 1.125 ha E. urophylla var. urophylla
SPA (ATSC seedlots); 1.5 ha A. mangium SPA
(MSBFI seedlots); and 3.5 ha A. mangium SSO
(ATSC seedlots) in Oriental Mindoro. The initial
phase of the project was completed in December
2000. It covered site selection and delineation,
production of planting stocks, plantation
site preparation/establishment, plantation
protection and maintenance, and monitoring of
early growth performance. All activities such as
assessments, thinning and other management
operations were accomplished in the duration
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Country Report on Forest Genetic Resources
of the study. From the selected parent trees,
seeds were collected and 9.5 kg were provided
to ATSC for establishing genetic gain trials of
both species.
The country’s involvement in the conservation
and management of bamboo and rattan resources is governed by its membership at the
International Network for Bamboo and Rattan
(INBAR) which is an inter-governmental organization established in 1997 with head-quarters
in Beijing, China and regional offices in Asia,
Africa, Latin America and Europe. It is dedicated to improving the social, economic, and
environmental benefits of bamboo and rattan.
INBAR connects a global network of partners
from the government, research institutions,
NGOs, rural communities, private, and notfor-profit sectors in over 50 countries to define
and implement a global agenda for sustainable
development through bamboo and rattan.
Among its environmental goals related to forest genetic resources is to identify threatened
bamboo and rattan species and take actions to
foster their conservation. With its partners it
intends to explore and demonstrate new ways
to reverse the depletion of the world’s rattan
resources, while encouraging their sustainable
use in poverty alleviation. It has undertaken
development projects and provided trainings
to member countries such as the Philippines
on the conservation, diversity, ecogeography,
germplasm, resource utilization and taxonomy
of bamboo and rattan.
The ERDB also implemented the International
Tropical Timber Organization funded project
“Demonstration and Application of Production
and Utilization Technologies for Rattan Sustainable Development in the ASEAN Member
Countries (ITTO) [ITTO PD 334/05 Rev 2
(1)] in 2005-2010. The project aimed to
strengthen ASEAN collaboration that would
promote the sustainability of rattan resources
through demonstration and application of
rattan production and utilization technologies
to uplift the socio-economic status of local
communities. Twenty training programs were
conducted separately in the different areas
of the Philippines, Vietnam, Lao PDR, and
Cambodia. A total of 220 hectares of rattan
plantations were established and maintained
by the respective participating countries.
With the ITTO, the Philippines through the
Forest Management Bureau of the DENR
implemented the project “Development of
Criteria and Indicators (C&I) for Sustainable
Forest Management (SFM) in the Philippines”
(PD 225/03 Rev. 1) from 2002 to 2003. It
aimed to promote sustainable management
of the tropical resources in the Philippines
in accordance with the year 2000 objective
through the formulation of criteria and
indicators for sustainable forest management
at the national and forest management unit
levels, including appropriate monitoring,
assessment and reporting systems. The
project has produced some useful documents
including the baseline report on C&I in 2003
and the first progress report in 2005. It also
has developed a GIS-compatible database
system for C&I, which will allow for the easy
management of data, reporting, updating,
retrieval and analysis to determine progress
towards SFM.
The Association of Southeast Asian Nations
(ASEAN) at which the Philippines is a member,
the policy coordination and decision-making
on regional cooperation in the forestry sector
is the task of the ASEAN Senior Officials
on Forestry (ASOF) guided by the ASEAN
Ministers on Agriculture and Forestry (AMAF).
In the Blueprint for the ASEAN Socio-Cultural
Community (ASCC), ensuring environmental
sustainability is a major area. This includes,
among others, intensified regional cooperation
on global environmental issues, conservation
of biological diversity, as well as promotion
of sustainable forest management (SFM)
and eradication of unsustainable practices
including combating illegal logging and its
associated trade.
International Collaborations
The
Philippines
collaborates
with
the
International Plant Genetic Resources Institute
(IPGRI) now the Bioversity International in the
Philippines
Country Report on Forest Genetic Resources
management of its forest genetic resources.
It backs the IPGRI’s mission to encourage,
support and undertake activities to improve the
management of genetic resources worldwide
so as to help eradicate poverty, increase food
security and protect the environment. IPGRI
focuses on the conservation and use of plant
genetic resources important to developing
countries and has an explicit commitment to
specific crops. The country is an active partner
in undertaking research and training, and the
provision of scientific and technical advice and
information.
The Philippines is also a party to a number of
multilateral environmental agreements (MEAs)
which aims to conserve and sustainably use
biological diversity. These include the United
Nations Environment Programme (UNEP)
Convention on Biological Diversity (CBD),
the Cartagena Protocol on Biosafety, and
the Convention on International Trade of
Endangered Species of Wild Fauna and Flora
(CITES). With all these MEAs the Philippines
is mandated to comply with all the provisions
to ensure the conservation of the country’s
biodiversity resources within and outside the
PAs.
The International Union for the Conservation
of Nature and Natural Resources(IUCN) with
which the Philippines is a member since 1968,
is a union of sovereign states, government
agencies and NGO’s with the initiation and
promotion of scientifically-based action that
will ensure the perpetuation of man’s natural
environment. It maintains close working
relations with many inter-governmental
organizations and it maintains close working
relations with the World Wide Fund for
Nature (WWF). Its mission is to provide
international leadership for the conservation
and management of living resources. The
Philippines has prior involvement with the
IUCN dating back in the mid-60s. The agency
extended consultancy assistance to the
country in the survey of national parks and
other equivalent reserves of the then Parks
and Wildlife Office. IUCN member countries
submit data on the status of endangered
71
species and on traffic in wildlife through the
union’s specialized monitoring centers based
in the United Kingdom.
The ERDB together with the University of
the Philippines Los Baños (UPLB) and the
Forest Products Research and Development
Institute (FPRDI) under the Department of
Science and Technology (DOST) is a member
of the International Union of Forest Research
Organizations (IUFRO). Its mission is to
promote global cooperation in forest-related
research and to enhance the understanding of
the ecological, economic and social aspects of
forests and trees; as well as to disseminate
scientific knowledge to stakeholders and
decision-makers and to contribute to forest
policy and on-the-ground forest. IUFRO attains
its objectives by networking activities including
the generation, exchange and dissemination
of scientific knowledge, the provision of access
to relevant information, and the assistance to
scientists and institutions to strengthen their
research capacities.
The Asia Pacific Association of Forestry
Research Institutions (APAFRI) is an independent non-profit body, which aims to enhance
research and technology development capabilities in support of conservation and management of forest resources in the Asia-Pacific
region. The member agencies in the Philippines
are the Philippine Council for Agriculture,
Forestry and Natural Resources Development
(PCARRD, FPRDI, ERDB, the University of
the Philippines Los Baňos-College of Forestry
and Natural Resources (UPLB-CFNR), and the
University of the Northern Philippines (UNP).
The establishment of APAFRI was prompted
by the need to provide a viable institutional
framework for research collaboration in the
region. Since 1991, the Forestry Research
Support Programme for Asia and the Pacific
(FORSPA) has been fulfilling the networking
function. APAFRI, a follow-up of FORSPA, is an
outcome of the desire of the countries in the
region and the donor community to develop a
more self-reliant and sustainable mechanism
to strengthen research networking. It was
Philippines
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Country Report on Forest Genetic Resources
launched during the meeting of the Heads of
Forestry Research Organizations in the AsiaPacific held in Bogor, 20-23 February 1995.
The International Union of Forest Research
Organizations (IUFRO) has recognized APAFRI as
its Asia-Pacific chap-ter. APAFRI has been
collaborating closely with the IUFRO Special
Programme for Developing Countries (SPDC)
in strengthening research in the Asia-Pacific
region.
The Philippines became a collaborator of
the International Neem Network which was
coordinated by the Food and Agriculture
Organization of the United Nations (FAO) in
1993 with the long-term objective to conserve
genetic resources and to improve the genetic
quality, adaptability, and utilization of the
species. Provenance trials were established in
San Manuel, Pangasinan and Bansud, Oriental
Mindoro on August 1996 and November 1996
respectively.
International Collaboration
The following tables shows the country’s
needs and priorities for future international
collaboration (Table 15). There is a clear
perceived need for advanced knowledge and
skills on both the methodologies of in-situ and
ex-situ conservation of forest genetic resources
in the Philippines. The establishment and
maintenance of seed banks and in vitro banks
for forest species will be top priorities as these
are completely lacking in the country. Training
is also deemed as a priority to enhance the
conduct of research on the various aspects of
FGR, as well as ways to further the awareness
on the value, conservation and sustainable
use of FGR among the public.
Since the latter part of the last century, the
Philippines has been involved with the ASEAN
Peatland Forests Project (APFP) which aims
to demonstrate, implement and scale up the
sustainable management and rehabilitation of
peatland forests in Southeast Asia. The Project focuses on strengthening institutional
capacity and frameworks, reducing the rate
of degradation on peatlands in Southeast
Asia, demonstrating integrated management
and rehabilitation of peatlands at target
sites, and engaging the private sector and
local communities in sustainable peatland
management. It fits within the framework of
the ASEAN Peatland Management Initiative
(APMI), and directly supports the ASEAN
Peatland Management Strategy (APMS), and
associated National Action Plans on Peatlands.
Together with the Philippines, the other
Southeast Asian nations participating in the
project are Malaysia, Thailand, and Vietnam.
So far, ground surveys have been undertaken
in two areas in the Philippines, namely, in the
Leyte Sab-a Basin and the Peatland Forests of
the Agusan Marsh in the Island of Mindanao.
Needs and Priorities for Future
Philippines
73
Country Report on Forest Genetic Resources
Table 15. Needs and priorities of the Philippines for international collaboration on
forest genetic resources.
Priority Level
Needs and Priorities
Not
applicable
Low
Medium
High
√
Understanding the state of diversity
Enhancing in situ management and conservation
√
Enhancing ex situ management and conservation
√
Enhancing use of forest genetic resources
√
Enhancing research
√
Enhancing education and training
√
Enhancing legislation
√
Enhancing information management and early
warning systems for forest genetic resources
√
√
Enhancing public awareness
Philippines
Country Report on Forest Genetic Resources
75
Chapter 7
Access to Forest Genetic Resources and
Sharing of Benefits Arising from their Use
T
he 1987 Constitution of the Philippines
provides that access to natural resources
including forest (and genetic resources) can
only be done through joint venture (with the
government), co-production, or production
sharing
agreements.
In
1993,
DENR
established the Industrial Forest Management
(IFM) Program that issued the Industrial
Forest Management Agreement (IFMA) as the
tenure instrument under DAO No. 60 series of
1995. This is a production sharing agreement
that grants tenure holders the privilege to
harvest second growth natural forest and
requires them to help in the development and
protection of forest areas. The provisions of
the DAO have undergone several revisions and
amendments and its final form is contained in
DAO No. 99-53. The tenure has a duration of
25 years renewable for another 25 years. The
maximum area granted under this agreement
is 40,000 ha. A grantee can have more than
one IFMA area as long as the combined area
does not exceed 40,000 ha. The minimum
area that may be granted is 500 ha.
For the medium investors and small farmers,
the Socialized Industrial Forest Management
Agreement (SIFMA) was instituted (DAO No.
24, 1996). The area that may be granted is
as low as 1 ha for individuals or families to
a maximum of 500 ha for cooperatives and
associations. The responsibilities given to the
IFMA holder of developing, managing and
protecting the forest are also mandated to the
SIFMA holder.
In 1998, the Philippine government through
the DENR, established the Community-Based
Forest Management Program (CBFM), which
can provide the mechanism for improving
access to sustainable use of forest genetic
resources in the Philippine uplands. The
CBFM is an application of the principle of
“People first and sustainable forestry will
follow.” The program seeks to promote among
other things the sustainable management of
forest resources, social justice and improved
well-being of local communities, and strong
partnership among local communities and
the Department of Environment and Natural
Resources. CBFM is implemented in all areas
classified as forest lands, including allowable
zones within protected areas not covered
by prior vested rights. The implementation
further seeks to integrate and unify all peopleoriented forestry activities of the Integrated
Social Forestry Program, Community Forestry
Program, Coastal Environment Program, and
Recognition of Ancestral Domains.
The access to and sharing of benefits in
the use of FGR are incorporated in the
following key features of the CBFM namely:
security of tenure, social equity, and market
linkage.
The
Community-Based
Forest
Management Agreement (CBFMA) entitles
forest communities to use and develop the
forestland and resources for a duration of 25
years. Furthermore, the Program grants forest
communities the comprehensive rights to use
and develop forest resources. Finally, the DENR
and the LGUs provide technical assistance
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Country Report on Forest Genetic Resources
to CBFM participants to help them attain
sustainable forest management in addition
to proving help to the communities in terms
of accessing investment capital, identifying
markets, and building marketing capabilities.
International Agreements
Over the past 10 years, the country subscribed
to many international agreements relevant to
access to forest genetic resources, transfer
and sharing of benefit arising from their use.
The Philippines is a signatory to the World
Trade Organization (WTO) that intends to
supervise and liberalize international trade
and provides a framework for negotiating and
formalizing trade agreements, and a dispute
resolution process. The agreements include
provisions on the trade of environmental
goods and services, standards and certification
procedures with possible implications on
forest genetic resources. Some environmental
goods require forest genetic resources as raw
materials such as timber and non-timber forest
products. These goods may also require forest
genetic resources as components or inputs in
manufacturing.
The Philippines is also a signatory to the
United
Nations
Framework
Convention
on Climate Change (UNFCCC), The Kyoto
Protocol (COP3) and succeeding Conferences
of the Parties (Since 1992 and on-going).
With the objective of the treaty to stabilize
greenhouse gas concentrations in the
atmosphere at a level that would prevent
dangerous anthropogenic interference with
the climate system, it provides that credit
would be granted for broad activities that
absorb carbon from the atmosphere or store
it, including forest and cropland management,
and re-vegetation, with no over-all cap on the
amount of credit that a country could claim
for carbon sink activities. Hence, depending
on eligible projects, national priorities, and
forest management policies and decisions,
this will entangle with the management and
conservation of forest genetic resources.
Development of forest plantations as carbon
sink will enhance forest genetic conservation,
not just on the aspect of trees but the adjoining
vegetation during the plantation development.
However, such endeavors should not solely
consider commercial production. The biological
objective of such plantation development
activities should take into serious consideration
the enrichment of the genetic structure of the
species that will be used.
The Convention on Biological Diversity (CBD)
is another international agreement which the
Philippines subscribes to and supports since
its inception. Here, the Conference of the
Parties (COP) adopted the Bonn Guidelines
to facilitate the implementation of the Access
and Benefit Sharing System (ABS). The ABS is
similarly applicable to traditional knowledge of
indigenous and local communities associated
to genetic resources. The Philippines, being
one of the countries in the world with diverse
traditional knowledge systems that are in many
cases based on forest genetic resources has
much stake in the provisions of the agreement
to protect said resources.
The Cartagena Protocol on Biosafety under
the CBD also known as the Biosafety Protocol
was adopted in January 2000. The Biosafety
Protocol seeks to protect biological diversity
from the potential risks posed by living
modified organisms resulting from modern
biotechnology. Since most of the country’s
biological diversity rests on forest areas and its
genetic resources, the country has many wide
areas of specific concerns on Biosafety. The
Philippines has since developed its Biosafety
Framework and created its Biosafety Committee
that looks on the possible implications of the
products of modern genetic technologies not
just on the agricultural domain but also on
forest genetic resources.
Since 2003, the Philippines has been participating in the ASEAN Free Trade Area (AFTA)
organized by the Association of Southeast
Asian Nations. The AFTA is meant to increase
ASEAN’s competitive edge as a production base
in the world market through the elimination,
within ASEAN, of tariffs and non-tariff barriers,
Such should attract more foreign direct
Philippines
Country Report on Forest Genetic Resources
investments to ASEAN. It includes provisions
on the change of tariffs on wood-based
products that in one way or another will have
effects on the utilization of forest biological
resources.
National Legislations and Policies
The country has also promulgated national
legislations and policies in terms of access
to forest genetic resources and sharing of
benefits arising out of their use. Although
enacted much earlier, the country observes
the provisions of Presidential Decree No.
1151 (Philippine Environmental Policy) and
subsequently, the Department of Environment
and Natural Resources Administrative Order
2003-30 (Detailed Guidelines and Procedures
in the Implementation of the Philippine EIS
System) which requires all agencies and
instrumentalities of the national government,
including government-owned or controlled
corporations, as well as private corporations,
firms and entities to make a detailed statement
on environmental impacts of any proposed
undertaking which significantly affects the
environment. Hence, forestry and thus forest
genetic resources are covered by this law
in the sense that areas declared by law as a
national park, watershed, reserve, wildlife
preserves or sanctuary, areas which constitute
the habitat for any endangered or threatened
species of indigenous Philippine wildlife (flora
and fauna), and mangrove areas, among
others, are declared as Environmentally Critical
Projects (ECP). Utilization and exploitation
of these have critical environmental impacts
and therefore need to undergo environmental
impact assessments and need to acquire
Environmental Compliance Certificates (ECC)
prior to implementation. This law in many
ways can provide for the conservation of forest
genetic resources in the country if properly and
judiciously implemented.
Another old law, the Presidential Decree No.
705 Revised Forestry Code of the Philippines
still governs the forest management system
in the country. Presidential Decree No. 705 or
the Revised Forestry Code of the Philippines
77
emphasizes proper classification and survey of
all lands of the public domain, management
and utilization, as well as the protection,
development and rehabilitation of forest lands
to ensure continuity of productive condition.
Presidential Decree No. 1433 (Promulgating
the Plant Quarantine Law of 1978, Thereby
Revising and Consolidating Existing Plant
Quarantine Laws to Further Improve and
Strengthen the Plant Quarantine Service of
the Bureau Of Plant Industry) restricts the
importation and/or introduction into the
Philippines of plants, plant products, soil,
packing materials of plant origin capable
of harboring and are a source of medium of
infection/infestation of plant pests subject to
such quarantine orders, rules and regulations
as may be promulgated, from time to time.
Executive Order 23 (February 1, 2011) declares
a moratorium on the cutting and harvesting
of timber in the natural and residual forests
and creating the anti-illegal logging task force,
among others. The DENR is prohibited from
issuing logging contracts/agreements in all
natural and residual forests, such as Integrated
Forest Management Agreements (IFMA),
Socialized Integrated Forest Management
Agreements
(SIFMA),
Community-Based
Forest Management Agreement (CBFMA)
and other agreements/contracts with logging
components in natural and residual forests.
One policy issuance with direct implication
on access to forest genetic resources is
Executive Order No. 247 (May 18, 1995)
and its Implementing Rules and Regulations
(DENR DAO 96-20). It prescribes guidelines
and establishes a regulatory framework for
the prospecting of biological and genetic
resources, their by-products and derivatives,
for scientific and commercial purposes; and
for other purposes. Prospecting of biological
and genetic resources shall be allowed
within the ancestral lands and domains of
indigenous cultural communities only with the
prior informed consent of such communities
obtained in accordance with the customary
laws of the concerned community.
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The prospecting of biological and genetic
resources shall be allowed when the person,
entity or corporation, foreign or domestic,
undertaking such activities, on recommendation of the Inter-Agency Committee on
Biological and Genetic Resources executes
a Research Agreement. If the research and
collection of biological and genetic resources
is intended, directly or indirectly, for
commercial purposes, the agreement must
be a Commercial Research Agreement. If the
prospecting of biological and genetic materials
is intended primarily for academic purposes,
the agreement shall be an Academic Research
Agreement.
Cultural Communities (ICC) / Indigenous
People (IP), Creating a National Commission of
Indigenous People, Establishing Implementing
Mechanisms, Appropriating Funds Therefore,
and for Other Purposes) recognizes, promotes
and protects the rights of ICCs/ IPs to
their ancestral domains, autonomy and
self determination and cultural integrity. It
further recognizes full ownership, control and
protection of their cultural and intellectual
property - including special measures to
control, develop and protect their sciences,
technologies and cultural manifestations,
including human and other genetic resources,
seeds, medicines, indigenous knowledge
system and practices, knowledge of the
properties of fauna and flora, oral traditions,
literature, designs, visual and performing
arts and the right to the protection of their
traditional medicines and health practices, the
protection of vital medicinal plants, animals
and minerals.
Republic Act No. 7586 enacted in July 1991,
An Act Providing for the Establishment and
Management of National Integrated Protected
Areas System, Defining Its Scope and
Coverage, and for Other Purposes provides
that hunting, destroying, disturbing, or mere
possession of any plant or animal or products
derived there from without a permit from the
Management Board is prohibited (Section
20). Executive Order 578 November 8, 2006
established the National Policy on Biological
Diversity and prescribed its implementation
throughout the country, particularly in the
Sulu Sulawesi Marine Ecosystem and the
Verde Island Passage Marine Corridor. The EO
provides that the DENR shall, in accordance
with law and subject to public consultations,
develop and promulgate rules, and regulations
for the establishment of critical habitats within
key biodiversity areas which are known to
harbor habitats and ecosystems critical for
the survival of threatened, restricted-range,
and congregatory species, and provide
the guidelines for their management and
protection. Biodiversity impact assessment
shall be integrated into the Environmental
Impact Assessment and the Environmental
Risk Assessment Processes, taking into
consideration guidelines adopted under the
United Nations Convention on Biological
Diversity (Section 3).
In July 31, 2001, the country enacted Republic
Act No. 9147 or the Wildlife Act (An Act Providing
for the Conservation and Protection of Wildlife
Resources and Their Habitats, Appropriating
Funds Therefore and for Other Purposes).
Among other provisions, local transport of
wildlife, by-products and derivatives collected
or possessed through any other means shall
be authorized unless the same is prejudicial to
the wildlife and public health. Wildlife species
may be exported to or imported from another
country as may be authorized by the Secretary
or the designated representative, subject to
strict compliance with the provisions of this
Act and rules and regulations promulgated
pursuant thereto: Provided, that the recipient
of the wildlife is technically and financially
capable to maintain it. Bio-prospecting shall
be allowed upon execution of an undertaking
by any proponent, stipulating therein its
compliance with and commitment(s) to
reasonable terms and conditions that may be
imposed by the Secretary which are necessary
to protect biological diversity.
Republic Act No. 8371 (An Act to Recognize,
Protect and Promote the Rights of Indigenous
Germplasm exchange rules are defined in
Article 42, Section 5 of the Implementing Rules
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Country Report on Forest Genetic Resources
and Regulations (IRR) of Republic Act No.
7308, otherwise known as the Seed Industry
Development Act of 1992. This applies more
on agricultural plant genetic resources but
the general purpose is to conserve, preserve,
and develop the plant genetic resources of the
nation. Access to forest genetic resources over
the past ten years has been defined by strict
laws and regulations. Difficulty depends on the
nature of gaining access and the purpose for
obtaining said resources. There are reasons to
believe that the country encountered difficulty
in maintaining or enhancing access to forest
genetic resources located outside the country
considering that these countries too, made
parallel legislations and rules of access with
reference to CBD.
The Philippines may not really depend on access
to forest genetic resources outside the country
considering its rich source of indigenous
genetic materials. Forest development goals
of the country can be attained using local
sources.
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81
Chapter 8
The Contribution of Forest Genetic Resources to
Food and Health Security, Poverty Alleviation, and
Sustainable Development
T
he Philippine forests, particularly the genetic resources, remain an important
element of the natural environment that
performs invaluable ecological services vital
to the survival of the Filipino people. Clean
water, good soil, and fresh air are some of
the major services provided by the forests.
Thus, the Philippine government is committed
to protecting and sustainably managing its
remaining forest genetic resources.
While the contribution of the forest sector
to GDP is dwindling, it remains significant,
especially if looked at in tandem with the
agriculture and fisheries sectors. From 20042009, the agriculture, fisheries and forestry
(AFF) sector accounted for 18.7 percent of
total GDP1. Ironically, lack of protection and
improper use over the years brought about
the deterioration of the natural ecosystems,
resulted in the decline of the AFF contribution
to GDP by 1.5% during the same period (NEDA
2011).
The poor state of the country’s forest resources
is felt most intensely by the poor, especially the
rural communities which remain the poorest in
the country2. The strong link between poverty
and forest degradation cannot be denied as
continuous degradation of this important
resource poses a threat to life itself.
1 Average AFF contribution to GDP from 2004-2009.
Source: NSCB
2 2006
Poverty
incidence
farmers as the poorest
identified
fisherfolks
and
There are approximately 20 million people
living in upland and forest areas, half of whom
are dependent on shifting cultivation for
their livelihood (Cruz and Zosa-Feranil, 1998
as cited by NEDA 2011). Inequitable land
distribution, insecure tenure and rural poverty
are often cited as causes of deforestation and
forest degradation in the Philippines, which is
linked to increases in rural populations both as
a result of fertility and in-migration (Kummer,
1992; Liché, 1997 as cited by NEDA 2011).
FGR Contribution to Food and Health
Security, Poverty Alleviation, and
Sustainable Development
With the rich diversity in terms of species that
the Philippine forests has, it is no wonder that
they yield plants, plant parts, exudates, and
plant derivatives that have proven to be of
immense value to Philippine society. Philippine
customs and traditions are interwoven with
FGR which more than highlight the biological
and economic importance of FGR to the Filpino
way of life. This part of the report provides the
highlights for the multifarious contributions
that FGR have been providing to the well being
of the Filipinos.
Philippine Wild Food Plants
The Philippine forest has a rich reserve of wild
and semi-wild food plants, which many of the
country’s indigenous groups depend on for
subsistence, and to some extent, as source of
additional income.
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Some of these wildfood plants can be eaten
raw, while some need cooking. Others can
be processed as delicacies or made into
preserves that could be stocked for future
needs. The cultivation of these wildfood plants
as alternative to agricultural crops can help
provide livelihood options to many upland
and forest dwelling Filipinos (Polinag, 2003;
Dichoso, 2010). In the northern region of the
Philippines, over 49 wild species have been
recorded in the 11 municipalities of Cordillera
and the young shoots, tops, stalks, flowers,
leaves, bulbs and fruit reported to be eaten
as vegetables. Many of these belong to the
Asteraceae
(Compostitae),
Solanaceae,
Amaranthaceae and Brassicaceae families.
Gagattang is the local name for several thistlelike species - including Sonchus oleraceus L
(common sow thistle) and S. arvensis (perennial sow thistle) - which, although rather bitter, are consumed by local communities. The
plants are high in flavonoids and are also used
to treat indigestion, fever and asthma. Puriket
(Bidens pilosa), another popular wild plant, is
rich in iodine and is reported to prevent goitre
(enlarged thyroid). The young roots are also
used to cure rheumatism and treat wounds
and, in some areas, puriket is used in the
preparation of sake (rice wine).
(http://www.new-ag.info)
A list of these wildfood plants with their
corresponding food values is in Appendix
Table 9.
Contribution to Health and Security
The Philippine forests also abound with
medicinal plants. Many have been proven to
be fast and relatively inexpensive cures to
common physical ailments and entails simple
preparation either as concoctions for skin
diseases or taken as tea. There are quite a
number of these species whose air dried leaves
are pounded and encapsulated and are being
sold in the local market. An example is akapulko
(Cassia alata), a shrub known to be a diuretic,
sudorific and purgative. The medicinal uses of
akapulko are to treat fungal infection of the
skin and for the treatment of ringworms. Then
there is the banaba (Lagerstroemia speciosa),
a tree found throughout the Philippines
whose leaves, roots, fruit and flowers a have
medicinal uses. The species is used in the
treatment of diabetes and other ailments. It is
also a purgative and a diuretic.
There are also herbal products from the forests that include natural products for food
that are processed with natural raw material
ingredients, additives, and processing supplements to protect the sensory qualities of
food. Herbal products for personal care or
‘cosmeceuticals’ contain natural ingredients
from plant, animal or mineral sources that
have been minimally processed for soap,
lotion and other beauty care.
Forest-based Industries/Activities
Supporting Poverty Alleviation
Furniture Industry. Philippine furniture
ranks among the world’s best, earning for the
country the honor of being the “Milan of Asia”
for elegance and high quality craftsmanship.
The wooden furniture manufacturers in the
Philippines used to export only sanded items
and parts, but have now penetrated the
global market with finished products that
showcase local skills in carving, marquetry
and inlaying. Philippine-made wooden pieces
were previously reproduction or period pieces.
However, several firms are now producing
modern and contemporary style furniture.
Other manufacturers have also ventured
into the use of particleboards and medium
density fiberboards for panel furniture (http://
philexport.ph/furniture.html).
An estimated 15,000 local furniture companies
are actively supporting the industry and
providing employment to a total of 481,500
direct workers and 300,000 from subcontractors. Only 2% of these establishments
are considered large companies. The remaining
98% are classified as small and medium size
enterprises. Notably, Small and Medium
Enterprises (SME) make up much of the 2,500
furniture companies engaged in exports.
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Country Report on Forest Genetic Resources
The three main centers of furniture production
in the country are Metro Manila, Pampanga
and Cebu. The Southern Tagalog Region,
Iloilo and Mindanao (i.e. Davao, Cagayan
de Oro City and Butuan City) are becoming
furniture centers too. The largest-sized rattan,
stonecraft and metal furniture manufacturers
are located in Cebu. Lately however, several
rattan factories in Cebu have shifted to wood
furniture production.
Handicrafts-Making. The industry produces
an assortment of wares such as basketwork,
shell craft articles, ceramics, metal wares,
textiles, stone wares, wood crafts, hand made
paper products, biojewels, and others. Most
of the new and smaller handicraft firms use
manual production while a few of the larger
and progressive firms are already mechanized.
The industry requires minimal capital investment wherein the bulk of investment is in
working capital for raw materials and labor.
Raw materials used are mostly locally sourced
and usually from areas around the production
centers. Raw materials such as natural fiber,
agricultural wastes, and indigenous plants are
spread around the country.
Majority of the handicraft manufacturers in the
Philippines are small and medium enterprises
(SMEs), with a capitalization of less than PhP1
M and less than 20 employees. The employees
are often family members, relatives and
neighbors. These handicrafts include baskets,
holiday decors, body wearables like earrings,
food and ash trays, and many other novelty
items. A list of these species which are used
as raw materials for such handicraft products
is shown in Appendix Table 10.
The basketware sub-sector of the handicrafts
industry is 90% labor intensive. At present,
there are more than 5,000 firms who are
into basket production. Seventy-one firms
are registered with the BOI, 150 are largescale, while the remaining firms are micro
and small-scale companies. This sub-sector
provides direct employment to about 40,000
workers. An additional one million workers
are indirectly employed, spread out over the
83
major basket producing regions. Majority of
basket producers are into sub-contracting
arrangement with other firms. On the average,
a major manufacturer subcontracts 50% of
its production, and an exporter has three
major subcontractors. Subcontracting in the
basketry sub-sector provides employment to
about 100,000 individuals. Examples of these
species are Bulakan (Merremia peltata (L.)
Merr.), Hinggiw kalabaw (Streptocaulon baumii
Decne.), Lukmoy (Rhaphidophora monticola
Krause), Malagayaman (Pothos scandens L.),
and Silong pugo (Pericampylus glaucus (Lam)
Merr.).
Majority of the basket manufacturers and
subcontractors are found in the provinces of
Quezon, Ilocos, Albay, Pangasinan, Pampanga,
Cagayan, Cebu, Bohol, and Negros, where raw
materials are readily available. Other areas
have specialized basket products depending
on the materials available. Central Visayas
is known for baskets made of bamboo, coco
midrib and buri. Producers in the Bicol region
are known for their abaca products.
The wooden toy sub-sector is more capitalintensive. While most firms utilize a number
of machinery and equipment, at least 50%
of the total number of equipment of the
industry is imported. Production workers vary
from as few as three workers to as many
as 200 workers, 90% of whom are women.
The number excludes subcontractors who
are summoned when there are big volume
orders (http://tradeline phil.dti.gov.ph/betp/
toys). The main materials for the wooden
toy sub-sector include kiln dried mahogany
(Swietennia macrophylla), and soft solid wood
such as almaciga (Agathis spp.).
The handmade paper subsector is another
handicraft industry with barely 10 years in
existence. Although young, the yearly average
value of exports, within a period of five
years from 1995 to 1999, amounted to FOB
US$120.22 M for HMP sheets and converted
items. Except for the biggest one, the mills
operate on micro- and small scale, with
production capacity range of 1,000–30,000
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Country Report on Forest Genetic Resources
sheets of varied sizes and 100-50,000 pieces
of converted items per month. The industry
consists of about 100 firms, each employing
some five to more than a hundred workers,
mostly underemployed and out-of-school
youths in the community. The industry is faced
with problems on slow production, high cost of
labor, materials and machines, low qualities of
paper, inadequate promotion and marketing of
products, among others. Main raw materials
for handmade production include agricultural
fibers like abaca fibers, cogon grasses, salago,
banana fibers, etc.
Non-wood forest products. As mentioned
above, they are also valuable sources of
essential oils, dyestuffs, tannins, and animal
products such as honey and beeswax. These
include resins and exudates, palm and
palm by-products, fibers, natural dyes and
colorants, natural herbals, tannins, medicinal
plants (leaves, roots, barks).
Resins and resinoids produced from almaciga
(Agathis spp.) known as Manila copal, is
processed for paints, varnishes and lacquers.
Another exudate, Manila elemi, comes from
Canarium species and processed similarly as
Manila copal.
Palm products and by products are extracted from
kaong (Arenga pinnata) and sago (Metroxylon
sagu) fruits, specialty wine from nipa (Nypa
fruticans) and fibers, raffia and buntal from buri
(Corypha utan syn. Corypha elata).
Bast fibers from salago (Wikstroemia spp.)
forests are used in the manufacture of bank
notes and special types of paper products.
These fibers can likewise be used for fishlines
and nets, clotheslines, sacks, and woven in
intricate designs for bags, wallets and hats.
Wood fuels can come from the forest, wooded
lands, agricultural lands, and homesteads.
The World Bank/ESMAP Philippine Household
Energy Strategy Study in 1991 showed that
the share of forest and non-forest land supplied
fuelwood is about 14% and 86%, respectively.
This indicates that the non-forest lands are
the important woodfuel supply source in the
Philippines, particularly the household use.
The main process of woodfuel conversion is
resizing where wood is cut and split into sizes
that are easy to handle and transport, and
drying before being used directly as fuel wood.
Woodfuel could also undergo the following
processes: carbonization, gasification, densification, liquid fuel production, and combustion.
Charcoal briquette is being promoted to use
low quality biomass fuel into a high-density
fuel. Wood chipping technologies are available
but are not yet widely used in the country.
Charcoal briquettes produced from twigs, saw
dusts and other biomass are comparable if not
better than the heating values of coconut shell
indicating the potential of charcoal briquettes
to supplement woodfuels in satisfying the
demand.
The distribution and marketing system of
woodfuels is performed by two distinct groups
of traders: the rural and urban groups. The
rural traders are the persons responsible
for bringing woodfuels from the rural areas
to the urban users. They are composed
of transporters and dealers. This group of
traders may procure woodfuel directly from
the source, i. e., from fuelwood gatherers and
charcoal makers, from sawmill operators and
from local agents or assemblers of woodfuels
in a particular area. Rural traders can also be
fuelwood gatherers and charcoal makers who
market their goods by themselves.
Urban traders, on the other hand, are sellers
of woodfuel operating in the city. This category
includes the wholesaler-assembler, wholesalerassembler-retailer, wholesaler-retailer, and
retailer. A wholesaler sells fuelwood in large
quantities at a time. An assembler is involved
in gathering or bringing together woodfuel from
different sources to accumulate large volumes.
A retailer on the other hand, sells woodfuel in
small quantities directly to consumers.
For many of the poor rural households with
limited sources of income opportunities, the
urban woodfuel trade is a vital component of
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Country Report on Forest Genetic Resources
their household economy. UNDP/WB ESMAP
disclosed that there are 536,000 households
dependent on gathering and selling wood,
158,000 households are charcoal makers,
40,000 households act as traders in rural
areas, and an additional estimated 100,000
households are urban traders. The traders are
mainly storeowners or market stall operators
selling fuelwood and or charcoal as part of the
range of goods offered for sale.
In the Philippines, about 86% of the rural
households were reported to be predominantly
using fuel wood as source of energy. The
amount of wood-based energy consumed by
households depends on the household size
and income, type of energy applications being
used, efficiencies and cost of devices, and
accessibility to wood-based fuels.
The industrial sector, on the other hand,
accounts for about one-third of all biomass
fuel consumption in the Philippines with most
of its usage accounted for by bakeries, sugar
factories, tobacco curing barn, eateries, brick,
pots and ceramics making, and lime factory.
Demand is concentrated in urban and semiurban areas as well as in the rural areas
with large concentration of rural industries
(i.e. brick, pots and ceramic making, lime
factory and the like). With the distance
between
production/conversion
area
to
consumption, charcoal is preferred in terms
of transportation cost and ease of handling
compared to fuel wood. Wood-based fuels are
used as compliments for conventional sources
of energy. Urban users have the propensity to
substitute wood-based fuels with conventional
fuel sources as their income increases.
Initiatives Towards Sustainable
Development and People-Oriented
Forest Management Programs
Sustainable development has always been the
overarching policy of the Philippine government
in the management of the country’s forest
resources. This policy ensures that in addition
to ensuring economic viability, forest resources
85
management initiatives also factor in the social
equity and ecological stability considerations.
These initiatives are incorporated in most
of the recent forest resource management
programs and projects of the Philippines.
While the programs are primarily designed
to increase both in quantity and quality of
timber production to support the forestbased industries, the programs also contain
strategies that will accelerate rehabilitation of
degraded forest ecosystem and at the same
time help uplift the socio-economic condition
of the upland/forest occupants.
These strategies center on maximizing the
involvement of upland communities and other
forest resource-dependent families in the
implementation forest management projects
not only as laborer but also as key implementer
as well.
The Community-Based Forest Management Program (CBFM). Executive Order
263 issued in 1995 adopts CBFM as a major
strategy for sustainable management of the
Philippine resources (EO 263). This was further
reiterated in EO 318 “promoting Sustainable
Forest Management in the Philippines”.
CBFM integrates and unifies all people-oriented
forestry programs including the Integrated
Social Forestry Program, Upland Development
Project, Community Forestry Program, LowIncome Upland Community Project and the
Forestry Sector Project. In accord with the
intent and purpose of the people-oriented forestry programs, the CBFM also aims to improve
the socio-economic conditions of the upland
communities through the promotion of social
justice, equitable access to and sustainable
development of forestlands resources.
Under CBFM, organized communities or
people’s organization can enter into a production sharing agreement (CBFMA) with
the DENR to give them the right to occupy
posses, develop and utilize resources within
a designated CBFMA area for a period of
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Country Report on Forest Genetic Resources
25 years renewable for another 25 years.
EOs 263 and 318 likewise call on various
relevant instrumentalities of the government
including the LGUs, civil society organizations
and private business entities to assist in the
implementation of CBFM.
In 2008, the DENR has already entered into
CBFM Agreement with 1, 783 POs covering an
area of about 1,622,404 has. About 321,638
households have been benefitting from this
program.
Integrated Forest Management Program
(IFMP). The declining supply of the raw
materials for the wood industries of the country
has compelled the government to promote the
establishment of Industrial Tree plantations.
In, 1999, the DENR has issued Administrative
Order No. 99-53 providing the regulations for
the implementation of IFMP. From a mere forest
tree plantation, IFMP expands the scope and
coverage and introduces other strategies to
encourage participation of the industry sectors
as well as the support of the communities.
Under the guidelines, qualified applicants
may enter into a production sharing contract
with the DENR wherein he/she (the qualified
applicant) will be granted the right to develop,
manage, protect and utilize a specified area
of forestland and forest resources therein for
a period of 25 years and may be renewed for
another 25-year period.
Other provisions that are explicitly stated in
the IFMP regulation include the requirement
to plant principally timber-producing species
compatible with the ecological and biophysical
characteristics of the area, including rubber,
durian and/or non-timber species like rattan
and bamboo. The program also allows the
use of not more than 10% of the area for
agricultural purposes to supplement income or
food requirements of the plantation workers.
However, the number of IFMA holders has been
declining from as high as 188 in its initial year
covering to a low of 146 in 2008. On the other
hand, the area under IFMA has continued to
increase from a low of 508,000 hectares to as
high as 833,000 hectares in 2007. In 2008,
the area has gone down to about 767,094 ha.
Socialized Industrial Forest Management
Program (SIFMP). Pursuant to the forest
management principle of ensuring equitable
opportunities and access to forest resources,
the DENR has implemented the Socialized
Industrial Forest Management Program.
This is to allow upland individual/family
and community association/cooperatives to
participate in the establishment of industrial
forest plantation.
Under this program, the qualified individual
family, community associations/cooperatives
may enter into an agreement (SIFMA) with the
DENR wherein the latter grants to the former
the right to develop, utilize and manage a
small tract of forestland consistent with the
principle of sustainable development (DENR
Administrative Order No. 96-24). In 2008,
about 35,587 hectares have been placed
under 1,803 SIFMA.
National Greening Program. In the face of
the worsening problem on forest denudation,
the President of the Philippines has issued EO
23 declaring a moratorium on the cutting and
harvesting of timber in the natural and residual
forests of the entire country. The EO aims to
protect the remaining forest cover areas not
only to prevent damages to life and properties
due to natural calamities such as flashfloods
and land/mudslides, but also to preserve
biodiversity by protecting the habitats and
sanctuaries of endangered and rare species,
and to allow for the natural regeneration
of residual forests and the development of
plantation forests.
The National Greening Program is one of the
priority strategies specified under EO 23,
series of 2011. This is intended to address
the government’s goal of poverty reduction,
food security, and climate change adaptation
and mitigation. The EO has likewise mandated
the various government agencies with specific
tasks in support to the effective implementation
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Country Report on Forest Genetic Resources
of the NGP. Among others, the EO directed the
Department of Education and the Commission
on Higher Education (to initiate the necessary
educational drive campaign), the Department
of Interior and Local Government (to help in
establishing communal tree farms for firewood
and other purposes), the Department of
Social Welfare and Development (to identify
the upland farmers covered by the NGP as
priority beneficiaries of the conditional cash
transfer program), the Department of Budget
and Management (to provide the funds
for the production of quality seedlings for
reforestation programs from available funds
of the government), and the private sector
and other concerned agencies and institutions
(to raise funds and resources for tree planting
activities).
The NGP aims to plant 1.5 billion trees in
1.5 million hectares over a period of 6 years
starting 2011. This is quite a gargantuan task.
In order to establish a standard for its effective
and efficient implementation of the programs,
the DENR has issued Memorandum Circular No.
2011-01. The Circular provides the scope and
coverage of the program. It also enumerates the
priority areas for reforestation and rehabilitation
that includes forestlands, mangrove, ancestral
lands, military reservations, abandoned mining
area, urban parks and open spaces and other
suitable public lands such as river banks and
stream banks.
NGP is comprised of the seven components
including the production of seedling materials;
development of upland farms through agroforestry; reforestation of marginal lands and
rehabilitation of mangrove areas in communitymanaged forestlands; rehabilitation of degraded areas in priority watershed and
protected areas; rehabilitation of river and
streambanks; development of forest/tree
parks and greenbelts in suitable sites in urban
areas; and, maintenance and protection of
planted trees and established plantations by
partner implementers.
It should be emphasized that NGP recognizes
the use of quality planting materials for the
87
reforestation and rehabilitation component
of the project. As such, it mandated all the
participating/partner agencies to conform with
the guidelines on the collection, production and
disposition of forest tree seeds and seedlings
as provided for under Administrative Order no.
2010-11.
Likewise, the Program also requires the use of
premium and indigenous tree species in the
reforestation and rehabilitation of degraded
forestlands and protected areas. In line with
this requirement, the DENR taps its clonal
nursery nationwide as a major source of
planting materials.
Confronting Tenurial Problem. In addition
to the above people-oriented programs and
to help address the tenurial problem in the
uplands, approximately 11.6 million ha of
forestlands are now covered by some form of
tenurial instruments under various government
programs that somehow provided security to
upland occupants (Table 16).
Other specific strategies being implemented to
protect the remaining forest genetic resources
are the following:
a. Transform open, denuded and degraded
areas into protection forests and/or
economically-productive asset.
b. Encourage communities to develop multipurpose forests in on open, denuded and
degraded areas including into protection
forests and economically-productive asset;
c. Develop a portfolio approach for forest
investment in collaboration with the LGUs
and NCIP. They shall jointly prepare a forest
land use plan identifying areas for protection
and areas for investment and provide all
necessary permits and clearances prior to
development
d. Ensure that CDM/REDD plus programs
truly benefit Filipinos and reduce CO2 in the
atmosphere.
e. Encourage
communities
to
enhance
protection and sustain productivity of
reforestation and upland areas for livelihood
and poverty alleviation
Philippines
88
Country Report on Forest Genetic Resources
Table 16. Various forest tenurial instruments implemented, as of 2010 (NEDA, 2011).
No.
LTI Type
Number
Area (has)
4
252,510.00
1
Timber License Agreement (TLA)
2
Integrated Forest Management Agreement
(IFMA)
145
1,017,654.76
3
Socialized Industrial Forest Management
Agreement (SIFMA)
1,822
36,941.08
4
Agroforestry Farm Lease Agreements (AFFLA)
17
4,776.00
88
9,742.00
364
97,019.00
198
2,063.02
18
98.51
31
967.89
11
2,580.39
1,790
1,633,892.11
3,314
3,200,024.02
414
4,276,639.25
58
22,240.03
5
6
7
8
9
10
11
12
Tree Farm Lease Agreement (TFLA)
Forestland Grazing Management Agreement
(FLGMA & FLGA)
Special Land Use Permit (SLP)
Special Land Use Lease Agreement (SPLULA)
Forest Land Use Agreements for Tourism
Purposes (FLAgT)
Special Forest Land Use Agreement (FLAg)
Community-Based Forest Management Program (CBFMP)
CBFM Agreement
14
Other CBFM Tenure (CSC, FLMA, CFSA, CFP,
etc)
Approved CADT and CALT
15
PACBRMA
16
17
18
Areas under Management Arrangements
Philippine National Oil Corporation (PNOC)
National Power Corporation (NPC)
19
National Irrigation Administration
20
Co-Management Agreement with LGUs
13
266,326.00
337,721.00
22,243.00
TOTAL
Total forestland
153
485,536.65
8,427
11,668,974.71
15,805,325.00
11,668,974.71
Tenured
4,136,350.29
Untenured
f. Undertake completion of forestland boundary delineation and assessment and push
for the enactment of bills, and placing
all untenured /open access area under
management regime
g. Carry out collaborative watershed management planning cum vulnerability assessment
and implementation among DENR, LGUs
and other watershed stakeholders towards
responsible forest management.
h. Manage, protect, and develop natural forest,
established plantation, and economically
important non timber forest products and
species
i. Conduct Monitoring and Evaluation using
Criteria and Indicators, Third Party Monitoring,
and Forest Certification, among others.
j. Strengthen Decision Support System
Philippines
Country Report on Forest Genetic Resources
89
through Inventory of forest resources,
Baseline Data generation & GIS mapping
and Forest valuation & natural resource
accounting
k. Integrate the Conservation Farming Village
approach in the development of upland
farming communities in the Philippines
inevitably make efforts towards conservation
of FGR very attractive. Developments in the
methodologies for valuing FGR will certainly
go a long way in promoting the conservation
and sustainable of FGR in the Philippines.
Issues and Challenges
Dichoso, Wilma. 2010. Some Familiar Philippine
Palms that Produce High Value Food.
RISE, Research Information Series on
Ecosystems, Vol. 22 No.1, Ecosystems
Research and Development Bureau,
January-April 2010.
The aforementioned discussions have brought
to the fore the multifarious benefits that can
be derived from the country’s forest genetic
resources. Obvious is the fact that there
is strong appreciation of these uses and
benefits. But there is more that we can get
when such genetic resources are managed on
a sustainable basis. Tangible goods are only
half of the benefits derived from FGR. The
other half are the environmental services that
the sustainable use of FGR can bring about.
The potential of this other half has just begun
to be understood, and the methods to realize
such potential is just starting to evolve.
The full ecological and environmental values of
FGR is now again brought into the limelight with
the new program on Reducing Emissions from
Deforestation and Forest Degradation which is
recognized as an effort to create a financial
value for the carbon stored in forests, offering
incentives for developing countries to reduce
emissions from forested lands and invest in
low-carbon paths to sustainable development.
“REDD+” goes beyond deforestation and
forest degradation, and includes the role of
conservation, sustainable management of
forests and enhancement of forest carbon
stocks. With the huge outflows of funds from
industrialized countries to the less developed
ones, there can really be meaningful emission
reduction efforts with the conservation of
biodiversity and securing vital ecosystem
services as indirect results.
In relation to REDD+ providing a boost to FGR
conservation, another evolving approach is
the Payment for Environmental Services (PES)
which now being regarded as an indispensable
sustainable development mechanism. PES will
References
NEDA 2011. Draft Medium Term Philippine
Development Plan (MTPDP) 20112016. Regional Consultation Meeting,
Region IV-A (CALABARZON), YazakiTorres Manufacturing Inc.. Calamba
City, 6 January 2011
Polinag, Mercedita 2003. Food from the Wilderness, a Guidebook., Published
by the Ecosystems Research and
Development Bureau, DENR, College,
Laguna and the Bureau of Agricultural
Research, DA, Quezon City.
UNDP/World Bank 1991. The Philippines
Household Energy Strategy. Energy
Sector Management Assistance Program (ESMAP), c/o Energy and Water
Department. The World Bank Group,
1818 H Street, NW, Washington, D.C.
20433, U.S.A.
Internet
http://denr.gov.ph/
http://forestry.denr.gov.ph/
http://philexport.ph/furniture.html
http://tradeline phil.dti.gov.ph/betp/toys
http://www.new-ag.info/en/focus/focusItem.
php?a=456
Philippines
Country Report on Forest Genetic Resources
91
Appendix Tables
Appendix Table 1. Forest species in the Philippines with economic importance and/
or uses.
Tree (T)
or other
species
(O)
Native
(N) or
Exotic
(E)
Acacia auriculiformis A.
Cunn. Ex Benth.
T
E
used in pulp and
fuelwood, charcoal
Acacia mangium Willd.
T
E
used in general construction and furniture
industry
Anthocephalus chinensis
(Lamb) A. Rich. Ex Walp.
T
N
for plywood, pulp and paper
Casuarina equisitifolia L.
T
N
firewood, windbreak, erosion control, tanin, pulp
Scientific Name
Reasons for Priority
Trees
paper,
furniture,
Endospermum peltatum
Merr.
T
N
important source of lightweight hardwood;
wood is especially used for matches,
various kinds of sticks and wooden shoes;
used in reforestation
Eucalyptus deglupta Blume
T
N
used for pulp and paper, lumber, poles,
boxes, furniture, mine timber
Gmelina arborea Roxb.
T
E
pulp, veneer, light construction lumber,
fuelwood, furniture, posts, particle board,
poles, plywood
Paraserianthes falcataria (L.)
Nielsen
T
E
used in pulp, blackboard, fuelwood,
corestock, furniture, toys, handicrafts
Pinus kesiya Royle ex Gordon
T
N
long-fibers for quality paper production,
mine props, wood construction
Philippines
92
Country Report on Forest Genetic Resources
Pterocarpus indicus Willd.
T
N
used as structural timber for light to
heavy construction, considered among
the best for furniture, panelling, musical
instruments, high grade cabinet work,
decorative flooring, and novelties
Samanea saman (Jacq.)
Merr
T
E
furniture and panelling, cabinet, wood,
construction, veneer, plywood, wood
carving
Swietenia macrophylla King
T
E
regarded as the world’s finest timber for
high-class furniture and cabinet work
Tectona grandis L. f.
T
E
construction, wood carving
N
used especially for furniture, musical
instruments, cigar boxes and plywood;
the wood has a pleasant smell, bark and
flower are used in local medicine
Toona calantas Merr. & Rolfe
T
Bamboo
Bambusa blumeana J.A.
Schultes & J.H. Schultes
O
E
culms are used in building construction,
manufacture of furniture, produces
excellent pulp for paper making, and
common source of shoots
Dendrocalamus asper
(Schultes f.) Backer ex
Heyne
O
E
used in house construction, pulp and
paper making, bamboo plywood and tiles,
produces one of the best shoots
Gigantochloa levis (Blanco)
Merr.
O
E
culms used in building
basketry and furniture
Schizostachyum lumampao
(Blanco) Merr.
O
E
used for making bamboo mats or sawali,
plyboo, basket, fences, spears and flutes
Calamus dimorphacanthus
Becc.
O
N
used for
industries
Calamus manillensis (Mart.)
H. Wendl.
O
N
good source of material for weaving
Calamus merrillii Becc.
O
N
utilized in furniture making
Calamus mindorensis Becc.
O
N
furniture, basketry and cordage
Calamus ornatus Becc. var.
philippinensis Becc.
O
N
furniture, cane, handles for implements
and flooring, leaves and roots as medicine,
fruits occasionally eaten
construction,
Rattan
Philippines
baskets,
bags,
for
home
Country Report on Forest Genetic Resources
93
Calamus ornatus Blume var.
Philippinensis Becc.
O
N
good source of material for furniture
industry and the stem is cut into strips
for handicraft purposes
Calamus siphonospathus
Mart. var. dransfieldii BajaLapis
O
N
basketry and tying
Calamus symphysipus Mart.
O
N
chairs, pack saddles for animals
Daemonorops ochrolepis
Becc.
O
N
furniture, baskets, bags, for home
industries and local commercial use
Daemonorops pedicelaris
Becc.
O
N
Handicrafts
Appendix Table 2. Forest species used for plantation, agroforestry or enrichment
planting in natural forests.
Scientific Name
Native (N)
or Exotic
(E)
Current
Uses*
Acacia auriculiformis A. Cunn. Ex
Benth.
E
1, 2, 3
plantation
Acacia mangium Willd.
E
1, 2, 3
plantation
Anthocephalus chinensis (Lamk.)
A. Rich. Ex Walp
N
1, 2
plantation
Artocarpus blancoi (Elmer) Merr.
N
1, 4
agroforestry
Callophylum inophyllum L.
N
1, 3
natural forest
Casuarina equisitifolia L.
N
2, 3, 4, 5
Dipterocarpus grandiflorus
Blanco
N
1
natural forest
Endospermum peltatum Merr.
N
1
natural forest
Eucalyptus camaldulensis Dehnh.
E
1, 2, 3
plantation
Eucalyptus deglupta Blume
N
1, 2
plantation
Gliricidia sepium (Jacq.) Kunth ex
Walp.
E
1, 3, 4, 5
Gmelina arborea Roxb.
E
1, 2
plantation
Hevea brasiliensis (HBK.) Muell.Arg.
E
1, 4
plantation
Leucaena leucocephala (Lam.) de
Wit
E
1, 4, 5
Litsea perrottetii
N
1, 4
If managed, type of management system
Trees
Philippines
plantation
agroforestry
plantation, agroforestry
agroforestry
94
Country Report on Forest Genetic Resources
Mangifera indica L.
N
1, 4, 5
plantation, agroforestry
Octomelis sumatrana Miq.
N
1
natural forest
Palaquium luzoniense (F.-Vill)
Vidal
N
1
natural forest
Paraserianthes falcataria (L.)
Nielsen
N
1, 2
Parashorea malaanonan (Blanco)
Merr.
N
1
Petersianthus quadrialatus
(Merr.) Merr.
N
1, 2
plantation
Pinus kesiya Royle ex Gordon
N
1, 2
plantation, reforestation
Pterocarpus indicusWilld.
N
1
plantation, natural forest
Samanea saman (Jacq.) Merr
E
1
Shorea almon Foxw.
N
1
plantation, open areas,
ornamental
natural forest
Shorea contorta Vidal
N
1
natural forest
Shorea negrosensis Foxw.
N
1
natural forest
Shorea polysperma (Blanco)
Merr.
N
1
natural forest
Shorea squamata (Blanco) Merr.
N
1
natural forest
Swietenia macrophylla King
E
1
plantation, natural forest,
ornamental
Tectona grandis L. f.
E
1
plantation, natural forest
N
4, 5
Bambusa blumeana J.A. Schultes
& J.H. Schultes
E
2, 4, 6
plantation
Bambusa philippinensis (Gamble)
McClure
N
2, 4 ,6
plantation
Bambusa vulgaris Schrader ex
Wendl.
E
2, 4 ,6
natural forest
Dendrocalamus asper (Schultes
f.) Backer ex Heyne
E
2, 4, 6
plantation
Gigantochloa atter (Hassk.) Kurz
E
2, 4 ,6
plantation
Gigantochloa levis Merr.
N
2, 4 ,6
plantation
Schizostachyum lumampao
(Blanco) Merr.
N
2, 4 ,6
natural forest
plantation
natural forest
Shrub
Vitex negundo L.
plantation/agroforestry
Bamboo
Philippines
Country Report on Forest Genetic Resources
Palm
Cocos nucifera L.
E
1,3, 4, 5
Corypha elata Roxb.
N
4, 5
natural forest
Metroxylon sagu Rottb.
N
1, 4, 5
natural forest
Arenga pinnata (Wurmb) Merr.
1, 4
plantation/agroforestry
plantation/agroforestry
Rattan
Calamus caesius Blume
N
6
natural forest
Calamus dimorphacanthus Becc.
N
6
natural forest
Calamus filispadix Becc.
N
6
natural forest
Calamus javensis Blume
N
6
natural forest
Calamus manillensis (Mart.) H.A.
Wendl.
N
6
natural forest
Calamus merrillii Becc.
N
6
natural forest
Calamus microcarpus Becc. var.
microcarpus
N
6
natural forest
Calamus microsphaerion Becc.
N
6
natural forest
Calamus mindorensis Becc.
N
6
natural forest
Calamus ornatus Becc. var.
philippinensis Becc.
N
6
natural forest
Calamus ramolosus Becc.
N
6
natural forest
Calamus scipionum Lour.
N
6
natural forest
Daemonorops mollis (Blanco)
Merr.
N
6
natural forest
Daemonorops pedicellaris Becc.
N
6
natural forest
* Currrent Use:
1 Solid wood products
4 Non wood forest products (food, fodder, medicine, etc.)
2 Pulp and paper
5 Used in agroforestry systems
3 Energy (fuel)
6 Others
Philippines
95
96
Country Report on Forest Genetic Resources
Appendix Table 3. Main tree and other woody forest species providing
environmental services or social values.
Scientific Name
Native (N) or Exotic (E)
Environmental
Service or Social
Value*
N
6
Trees
Agathis philippinensis Warb.
Alnus nepalensis D. Don
E
1
Alstonia scholaris R. Br.
N
5
Amherstia nobilis Wall.
E
5
Calliandra calothyrsus Meissner
E
1, 2
Cananga odorata (Lamk) Hook.f & Thomson
N
5, 6
Cassia fistula L.
E
5
Casuarina equisitifolia L.
N
1, 2
Cynometra ramiflora L.
N
5
Desmodium gyroides DC. Home
N
1
Elaeis guineensis Jacq.
E
5,7
Flemengia macrophylla (Willd.) Merr.
N
1, 2
Leucaena diversifolia Benth.
E
1, 2
Leucaena leucocephalla (Lam.) de Wit
E
1
Muntingia calabura L.
N
5
Piliostigma malabaricum (Roxb.) Benth.
N
1
Pinus kesiya Royle ex Gordon
N
1, 5
Pinus merkusii Jung 7 de Vriese
N
1, 5
Pithecelobium dulce (Roxb.) Benth.
E
2,7
Psidium guajava L.
E
2,7
Samanea saman (Jacq.) Merr
E
5
Saraca declinata Miq.
E
5
Saraca thaipengensis Prain
E
5
Senna siamea (Lam.) Irwin et Barneby
N
2
Sesbania grandiflora (L.) Poiret
E
1
Syzygium cumini (L.) Skeels
N
5
Gliricidia sepium (Jacq.) Walp.
E
1
Bambusa blumeana J.A. Schultes & J.H. Schultes
E
1, 2, 3
Gigantochloa atroviolaceae Widjaja
E
5
Bambusa vulgaris var. striata Schrad. Ex Wendl.
cv. vitata Mcll.
E
5
Bamboo
Philippines
Country Report on Forest Genetic Resources
Schizostachyum brachycladum (Kurz)
E
5
Livistonia rotundifolia (Lam.) Mart.
E
5
Licuala grandis H. Wendl.
E
5
Roystonia regia (HBK) O.F. Cook
E
5
Cryptostachys renda Bl.
E
5
Mascarena lagenicaulis L.H. Bailey
E
5
97
Palm
* Services and values include:
1 Soil and water conservation including watershed
management
2 Soil fertility
3 Biodiversity conservation
5 Aesthetic values
6 Religious values
7 Food
4 Cultural values
Appendix Table 4. List of tree and other woody forest species considered to be
critically endangered in all or part of their range from genetic
conservation point of view.
Scientific Name
Family
Distribution in
the country:
Widespread
(W), Rare (R)
or Local (L)
Type of
Threat*
Threat
Category**
Kibatalia longifolia Merr.
Apocynaceae
Rare
1,2,6,7
Critically
Endangered
Cyathea microchlamys
Holtt.
Cyatheaceae
Rare
1,2,6,7
Critically
Endangered
Hopea acuminata Merr.
Dipterocarpaceae
Rare
1,2,6,7
Critically
Endangered
Hopea basilanica (Foxw.)
Slooten
Dipterocarpaceae
Rare
1,2,6,7
Critically
Endangered
Hopea cagayanensis
(Foxw.) Slooten
Dipterocarpaceae
Rare
1,2,6,7
Critically
Endangered
Hopea foxworthyi Elmer
Dipterocarpaceae
Rare
1,2,6,7
Critically
Endangered
Hopea malibato Foxw.
Dipterocarpaceae
Rare
1,2,6,7
Critically
Endangered
Hopea mindanensis
Foxw.
Dipterocarpaceae
Rare
1,2,6,7
Critically
Endangered
Philippines
98
Country Report on Forest Genetic Resources
Hopea philppinensis
Dyer
Dipterocarpaceae
Rare
1,2,6,7
Critically
Endangered
Hopea quisumbingiana
Gutierrez
Dipterocarpaceae
Rare
1,2,6,7
Critically
Endangered
Hopea samarensis
Gutierrez
Dipterocarpaceae
Rare
1,2,6,7
Critically
Endangered
Shorea astylosa Foxw.
Dipterocarpaceae
Rare
1,2,6,7
Critically
Endangered
Shorea malibato Foxw.
Dipterocarpaceae
Rare
1,2,6,7
Critically
Endangered
Vatica elliptica Foxw.
Dipterocarpaceae
Rare
1,2,6,7
Critically
Endangered
Vatica pachyphylla Merr.
Dipterocarpaceae
Rare
1,2,6,7
Critically
Endangered
Ctenitis paleolata Copel.
Dryopteridaceae
Rare
1,2,6,7
Critically
Endangered
Diospyros blancoi A DC.
Ebenaceae
Rare
1,2,6,7
Critically
Endangered
Diospyros brideliifolia
Elmer
Ebenaceae
Rare
1,2,6,7
Critically
Endangered
Diospyros ceulifom
Blume
Ebenaceae
Rare
1,2,6,7
Diospyros poncei Merr.
Ebenaceae
Rare
1,2,6,7
Rhododendron
javenicum (Blume)
Benn. var. schadenbergii
(Warb.) Sleum.
Ericaceae
Rare
1,2,6,7
Critically
Endangered
Rhododendron kochii
Stein
Ericaceae
Rare
1,2,6,7
Critically
Endangered
Rhododendron
taxifolium Merr.
Ericaceae
Rare
1,2,6,7
Critically
Endangered
Reutealis trisperma
(Blanco) Airy Shaw
Euphorbiaceae
Rare
1,2,6,7
Critically
Endangered
Hypericum pulogense
Merr
Hypericaceae
Rare
1,2,6,7
Critically
Endangered
lsoetes philippinensis
Merr. & Peny
Isoetaceae
Rare
1,2,6,7
Critically
Endangered
Cinnamomum cebuense
Kosterrn.
Lauraceae
Rare
1,2,6,7
Critically
Endangered
Pterocarpus indicus
Willd. forma indicus
Fabaceae
Rare
1,2,6,7
Critically
Endangered
Philippines
Critically
Endangered
Critically
Endangered
Country Report on Forest Genetic Resources
Pterocarpus indicus
Willd. forma echinatus
(Pers.) Rojo
Fabaceae
Rare
1,2,6,7
Critically
Endangered
Thaumasianthes
amplifolia (Merr.) Danser
Loranthaceae
Rare
1,2,6,7
Critically
Endangered
Aglaia pyriformis Merr.
Meliaceae
Rare
1,2,6,7
Critically
Endangered
Toona calantas Merr. &
Rolfe
Meliaceae
Rare
1,2,6,7
Critically
Endangered
Syzygium nitidum
Benth.
Myrtaceae
Rare
1,2,6,7
Critically
Endangered
Tristaniopsis decorticata
(Merr.) Peter G. Wilson &
Waterhouse
Myrtaceae
Rare
1,2,6,7
Critically
Endangered
Xanthostemon
bracteatus Merr.
Myrtaceae
Rare
1,2,6,7
Critically
Endangered
Xanthostemon
philippinensis Merr.
Myrtaceae
Rare
1,2,6,7
Critically
Endangered
Nepenthes argentii M.
Jebb & M Cheek
Nepenthaceae
Rare
1,2,6,7
Critically
Endangered
Nepenthes memilliana
Macfarlane
Nepenthaceae
Rare
1,2,6,7
Critically
Endangered
Nepenthes sibuyanensis
J Nerz
Nepenthaceae
Rare
1,2,6,7
Critically
Endangered
Chionanthus clementis
(Quisumb. & Merr.) Kiew
Oleaceae
Rare
1,2,6,7
Critically
Endangered
Chionanthus
remotinervius (Merr.)
Kiew
Oleaceae
Rare
1,2,6,7
Critically
Endangered
Olea palawanensis Kiew
Oleaceae
Rare
1,2,6,7
Critically
Endangered
Amesiella monticola J.
Cootes & DP Banks
Orchidaceae
Rare
1,2,6,7
Critically
Endangered
Ascoglossum calopterum
(Reichb. f.) Schlecter
Orchidaceae
Rare
1,2,6,7
Critically
Endangered
Ceratocentron fesseli
Senghas
Orchidaceae
Rare
1,2,6,7
Critically
Endangered
Dendrobium schuetzei
Rolfe
Orchidaceae
Rare
1,2,6,7
Critically
Endangered
Euanthe sanderiana
(Reichb. f ) Schltr.
Orchidaceae
Rare
1,2,6,7
Critically
Endangered
Philippines
99
100
Country Report on Forest Genetic Resources
Gastrochilus calceolaris
(Buch.- Ham. ex J.E.
Sm.) D.Do
Orchidaceae
Rare
1,2,6,7
Critically
Endangered
Paphiopedilum
acrnodontum Schoser ex
MW Wood
Orchidaceae
Rare
1,2,6,7
Critically
Endangered
Paphiopedilum
adductum Asher
Orchidaceae
Rare
1,2,6,7
Critically
Endangered
Paphiopedilum anitum
Golamco
Orchidaceae
Rare
1,2,6,7
Critically
Endangered
Paphiopedilum argus
(ReichbX) Stein
Orchidaceae
Rare
1,2,6,7
Critically
Endangered
Paphiopedilum fowliei
Birk
Orchidaceae
Rare
1,2,6,7
Critically
Endangered
Paphiopedilum
haynaldianum (Reich b.
f.) Stein
Orchidaceae
Rare
1,2,6,7
Critically
Endangered
Orchidaceae
Rare
1,2,6,7
Critically
Endangered
Orchidaceae
Rare
1,2,6,7
Critically
Endangered
Paphiopedilum
urbanianum Fowlie
Orchidaceae
Rare
1,2,6,7
Critically
Endangered
Paphiopedilum usitanum
O Gruss & J Roeth
Orchidaceae
Rare
1,2,6,7
Critically
Endangered
Phalaenopsis micholitzi
Rolfe
Orchidaceae
Rare
1,2,6,7
Critically
Endangered
Phmgmorchls teretffolia
LO Williams
Orchidaceae
Rare
1,2,6,7
Critically
Endangered
Vanda lamellata Lindl.
var. calayan Valmayor &
D. Tiu
Orchidaceae
Rare
1,2,6,7
Critically
Endangered
Areca parens Becc.
Arecaceae
Rare
1,2,6,7
Critically
Endangered
Calamus batanensis
(Becc.) Baja-Lapls
Arecaceae
Rare
1,2,6,7
Critically
Endangered
Calamus jenningsianus
Becc.
Arecaceae
Rare
1,2,6,7
Critically
Endangered
Calamus vinosus Becc.
Arecaceae
Rare
1,2,6,7
Critically
Endangered
Daemonorops affinis
Becc.
Arecaceae
Rare
1,2,6,7
Critically
Endangered
Paphiopedilum
hennisianum (MW
Wood) Fowlie
Paphiopedilum randii
Fowlie
Philippines
Country Report on Forest Genetic Resources
101
Daemonorops oligolepis
Becc.
Arecaceae
Rare
1,2,6,7
Critically
Endangered
Daemonorops pannosus
Becc.
Arecaceae
Rare
1,2,6,7
Critically
Endangered
Heterospathe calihons
Fernando
Arecaceae
Rare
1,2,6,7
Critically
Endangered
Heterospathe dransfieldii
Fernando
Arecaceae
Rare
1,2,6,7
Critically
Endangered
Heterospathe scitula
Fernando
Arecaceae
Rare
1,2,6,7
Critically
Endangered
Heterospathe
sibuyanensis Becc.
Arecaceae
Rare
1,2,6,7
Critically
Endangered
Heterospathe trispatha
Fernando
Arecaceae
Rare
1,2,6,7
Critically
Endangered
Arecaceae
Rare
1,2,6,7
Arecaceae
Rare
1,2,6,7
Pinanga samarana Becc.
Arecaceae
Rare
1,2,6,7
Pinanga sclerophylla
Becc.
Arecaceae
Rare
1,2,6,7
Pinanga sibuyanensis
Becc.
Arecaceae
Rare
1,2,6,7
Critically
Endangered
Plectocomia elmeri Becc.
Arecaceae
Rare
1,2,6,7
Critically
Endangered
Peranema cyatheoides
D. Don var. luzonicum
(Copel.) Ching & S. H.
Wu
Peranemaceae
Rare
1,2,6,7
Critically
Endangered
Platycerium coronarium
(Koenig ex Miller) Desv.
Polypodiaceae
Rare
1,2,6,7
Critically
Endangered
Platycerium grande
(Fee) Kunze
Polypodiaceae
Rare
1,2,6,7
Critically
Endangered
Podosorus angustatus
Holtt.
Polypodiaceae
Rare
1,2,6,7
Critically
Endangered
Pteris calocarpa (Copel.)
M. G. Price
Pteridaceae
Rare
1,2,6,7
Critically
Endangered
Pteris pachysora
(Copel.) M. G. Price
Pteridaceae
Rare
1,2,6,7
Critically
Endangered
Rafflesia manillana
Teschem.
Rafflesiaceae
Rare
1,2,6,7
Critically
Endangered
Rafflesia speciosa
Barcelona B Fernando
Rafflesiaceae
Rare
1,2,6,7
Critically
Endangered
Pinanga batanensis
Becc.
Pinanga bicolana
Fernando
Philippines
Critically
Endangered
Critically
Endangered
Critically
Endangered
Critically
Endangered
102
Country Report on Forest Genetic Resources
Rafflesia
schadenbergiana
Goppert ex Hieron
Rafflesiaceae
Rare
1,2,6,7
Critically
Endangered
Greeniopsis pubescens
Merr.
Rubiaceae
Rare
1,2,6,7
Critically
Endangered
Villaria acutifolia (Elmer)
Merr.
Rubiaceae
Rare
1,2,6,7
Critically
Endangered
Swinglea glutinosa
(Blanco) Merr
Rutaceae
Rare
1,2,6,7
Critically
Endangered
Gongrospermum
philippinense Radlk.
Sapindaceae
Rare
1,2,6,7
Critically
Endangered
Guioa palawanica
Welzen
Sapindaceae
Rare
1,2,6,7
Critically
Endangered
Guioa parvifoliola Merr.
Sapindaceae
Rare
1,2,6,7
Critically
Endangered
Guioa reticulata Radlk.
Sapindaceae
Rare
1,2,6,7
Critically
Endangered
Coryphopteris borealis
Holtt.
Thelypteridaceae
Rare
1,2,6,7
Critically
Endangered
Clerodendrum
guadriloculare (Blanco)
Merr.
Lamiaceae
Rare
1,2,6,7
Critically
Endangered
Tectona philippiinensis
Benth. B Hook. f.
Lamiaceae
Rare
1,2,6,7
Critically
Endangered
* Type of threat:
1 Forest cover reduction and degradation
2
3
4
5
6
Forest ecosystem diversity reduction and degradation
Unsustainable logging
Management intensification
Competition for land use
Urbanization
7 Habitat fragmentation
9 Acidification of soil and water
10
11
12
13
14
Pollutant emissions
Pests and diseases
Forest fires
Drought and desertification
Rising sea level
15 Others
8 Uncontrolled introduction of alien species
**Threat categories are based on DENR Administrative Order No. 2007-01.
Philippines
Country Report on Forest Genetic Resources
103
Appendix Table 5. List of forest species whose genetic variability has been evaluated.
Scientific
Name
Swietenia
macrophylla
King
Calamus
merrillii
Becc.
Calamus
ornatus
Becc.
Pinus kesiya
Royle ex
Gordon
Morphological Traits
Adaptive and
Production
Characters
Assessed
Molecular
Characterization
E
large tree, reaching a
height of 30-40 m and girth
of 3-4 m; trunk straight,
cylindrical, with a buttressed
base; bark rough, flaking
off in small patches
Young leaves
Random Amplified
Polymorphic
N
large-diameter, clustering,
dioecious; dense sheath
spines, fibrous brown to
black; leaves alternate,
grows up to 50-100 m
Young leaves
and shoots
Isozyme analysis
N
Dull green sheaths, densely
spiny, brown; stems 4-7 cm
diameter, 20 m tall; canes
2-4 cm diameter; leaves
coarse 3 m long, horizontal
and recurved, alternatingly
scattered
Young leaves
and shoots
Isozyme analysis
N
large tree up to 45 m tall
with a bole free of branches
for 15-20 m and up to 100
cm in diameter, a thick,
reticulately
and
deeply
fissured bark; needles in
bundles of (2-)3(-4), very
slender and flexible
Native
(N) or
Exotic (E)
DNA
Young needles
(microsatellite
analysis)
Isozyme analysis
Pterocarpus
indicus
Willd.
N
big tree, growing to 33 m in
height and 2 m diameter;
trunks usually fluted and
buttressed to 7-m diameter
at the base; crowns are
large and bear many long
branches;
leaves
are
compound-pinnate, bearing
about 12 alternate leaflets;
leaflets are rather large, 7 x
3.5 to 11 x 55 cm and ovate
to elliptic in shape
Philippines
Young leaves
from seedlings
Young leaves
from trees
Isozyme analysis
104
Country Report on Forest Genetic Resources
N
Parashorea
malaanonan
(Blanco)
Merr.
A very large tree to 45
m tall; stem to 2 m in
diameter, with large planklike buttresses to 4 m
high, spreading to over 2.5
m., outer bark fissured;
inner bark reddish. Leaves
simple, elliptical or ovate,
8-16 x 3-12 cm, sometimes
plicate, glabrous on both
sides, the lower surface
distinctly glaucous. Flowers
white, in terminal or axillary
racemes, the petals falling
off separately. Fruit winged,
the wings (calyx lobes)
much longer than the nut,
three longer wings 9-16 x
0.7-1.7 cm, the two shorter
wings to 10 cm long; the
nut ellipsoid or ovoid, 1.7 x
1.4 cm, finely pubescent.
Leaves
Isozyme analysis
Mature leaves
DNA (microsatellite) analysis
Reference: Abasolo (2007), Abasolo et al. (2009), Delos Reyes et al. (2010), Gamboa-Lapitan
and Jo. (2005), Quimado (2002) and Quimado et al. (2011).
Philippines
Country Report on Forest Genetic Resources
Appendix Table 6. Priority areas for plant conservation (Important Plant Areas or
Important Plant Sites (DENR–PAWB, CI, & UP–CIDS 2002).
Island & important plant area
Province
Batanes Islands
Batanes Islands Protected Landscape & Seascape
Luzon
Peaks of Central Cordillera (1000 m a.s.l.)
Abra, Mt Province, Benguet, Ifugao,
and Ilocos Sur Provinces
Mt Arayat National Park
Tarlac, Pampanga and Nueva Ecija
Bataan Natural Park & Subic Bay Forest
Reserve
Bataan and Zambales
Mt Makiling Forest Reserve
Batangas and Laguna
Mt Palaypalay – Mt Mataas na Gulod National
Park
Cavite and Batangas
Mt Isarog National Park
Camarines Sur
Isabela – Sierra Madre
Isabela
Aurora –Sierra Madre
Aurora
Mt Tapulao
Zambales
Northern Quezon (Central Sierra Madre)
Quezon
Southern Quezon (Central Sierra Madre)
Quezon
Bicol National Park – Mt Labo
Camarines Sur
Mindoro
Mt Halcon
Mindoro Occidental and Mindoro
Oriental
Naujan Lake National Park
Mindoro Oriental
Sibuyan Island
Sibuyan Island
Romblon
Panay
Central Panay Mountains: Madjaas–Baloi
Complex
Aklan, Capiz, Antique, and Iloilo
Negros
Mt Canlaon National Park
Negros Occidental and Negros
Oriental
Cuernos de Negros Region
Negros Oriental
Philippines
105
106
Country Report on Forest Genetic Resources
Samar
Mt Cabalantian – Mt Capotoan Complex
Samar, Eastern Samar and Northern
Samar
Sohoton – Loquilocon area
Eastern and Western Samar
Mindanao
Dinagat (Mt Kambinlio & Mt Redondo)
Surigao del Norte
Mimbilisan Protected Landscape
Misamis Oriental
North Diwata (Bislig, Mt Agtuuganon – Mt
Pasian)
Agusan Del Sur, Compostela Valley,
Davao Oriental, and Surigao del Sur
Mt Kaluayan – Kinabalian (Kimangkil Ridge),
Bukidnon – Agusan del Norte border
Misamis Oriental, Bukidnon, Davao,
Davao del Sur, Agusan del Norte and
Agusan del Sur
Mt Kitanglad
Bukidnon
Mt Kalatungan Range
Misamis Oriental, Bukidnon, Lanao
del Norte and Lanao del Sur
Munai Tambo Complex (Kolambugan uplands
& associated mountains
Lanao del Norte and Lanao del Sur
Lake Lanao
Lanao del Sur
Mt Piagayungan (Ragang) Complex
Bukidnon, North Cotabato, Lanao del
Sur and Maguindanao
Mt Butig / Lake Butig National Park
Lanao del Sur and Maguindanao
Marilog Forest Reserve, Bukidnon – Davao
boundary
Davao and Davao del Sur
Mt Apo Range
North Cotabato and Davao del Sur
Mt Matutum
Davao del Sur, Sarangani, and South
Cotabato
Mt Latian Complex (Sarangani Mountains)
Davao del Sur and Sarangani
Mt Malindang & Lake Duminagat
Misamis Occidental and Zamboanga
del Norte
Calamian Islands
Calamianes
Palawan
Palawan
Northern Palawan
Central Palawan
Palawan
Philippines
Country Report on Forest Genetic Resources
Southern Palawan, including Balabac Group of
Islands
Palawan
Leyte
Mt Pangasugan & Anonang – Lobi Range
Camiguin Island
Mt Hibok-hibok
Misamis Oriental
Tawi-tawi
Tawi-tawi
Philippines
107
108
Country Report on Forest Genetic Resources
Appendix Table 7. Potential seed production areas/Seed Sources by region.
Region
CAR
R-1
R-2
Province
Location/Barangay
Benguet
Bokod
Yapes Community
Watershed/Bobok
Benguet
Tuba
Camp 4
Benguet
Itogon
Binga
Benguet
Baguio City
Busol Watershed
Pterocarpus
indicus
Eucapyptus
camaldulensis
P. kesiya
Benguet
Baguio City
Forbes Park
P. kesiya
35
Benguet
Baguio City
Camp John Hay
P. kesiya
27
Ilocos
Norte
Ilocos
Norte
Pasuquin
PFDPIN, Tadao
Red gum
8
Gmelina
arborea
12
Marcos
Species
No. of Candidate
Plus Trees
Town/City
Pinus kesiya
30
26
30
30
Ilocos
Norte
Nueva Era
Nueva Era Refo
Project/ Poblacion
Swietenia
macrophylla
25
Ilocos Sur
Bantay
Refo Project/Caniaw
P. indicus
12
Pangasinan
Manleluag Spring
Dipterocarpus
Mangatarem Protected Landscape/
grandiflorus
Malabobo
2
Pangasinan
Manleluag Spring
Pentacme
Mangatarem Protected Landscape/
contorta
Malabobo
4
Pangasinan
Manleluag Spring
Anisoptera
Mangatarem Protected Landscape/
thurifera
Malabobo
6
Pangasinan
Manleluag Spring
Mangatarem Protected Landscape/ P. indicus
Malabobo
20
Cagayan
Solana
Maquirig
G. arborea
55
Cagayan
Peñablanca
Callao
S. macrophylla
75
Cagayan
Claveria
Claveria Experimental Forest/Kikiling
Mixed
Dipterocarps
Bambang
Salinas
S. macrophylla
64
G. arborea
67
Nueva
Vizcaya
Nueva
Vizcaya
Nueva
Vizcaya
Quirino
San Luis
San Luis
Nagtipunan
Lower Magat Forest
Reserve/Diadi
Lower Magat Forest
Reserve/Diadi
Dipantan
Philippines
S. macrophylla
G. arborea
202
108
54
Country Report on Forest Genetic Resources
Region
R-3
R-4A
R-4B
Province
No. of Candidate
Plus Trees
Town/City
Location/Barangay
Mariveles
Mariveles Refo
Project/ Alas-asin
Acacia
auriculiformis
30
Nueva Ecija Carranglan
Puncan
P. indicus
24
Pampanga
Arayat
Mt. Arayat National
Vitex
Park/ San Juna Banio parviflora
13
Pampanga
Angeles City
Airforce City,
Clarkfield
V. parviflora
60
Tarlac
Mayantoc
Calao/San Jose
S. macrophylla
36
Tarlac
Mayantoc
Calao/San Jose
G. arborea
105
Batangas
San Juan
Imelda
V. parviflora
100
Batangas
Lobo
Teak
76
Cavite
Ternate
Sawang
Mt. Palaypalay
National Park/
Malauyas, Sapang
G. arborea
25
Cavite
Ternate
Mt. Palaypalay
National Park/
Malauyas, Sapang
A. auriculiformis
Cavite
Ternate
Mt. Palaypalay
National Park/
Malauyas, Sapang
A. mangium
Quezon
Dolores
Kinabuhayan
S. macrophylla
95
Quezon
Lucban
Palola
S. macrophylla
31
Quezon
Lucban
Palola
P. indicus
37
Quezon
Pagbilao
Quezon National
Park/ Malicboy
S. macrophylla
Quezon
Lucena
Quan’s Worth Farm/
Silangan Mayao
V. parviflora
20
Mamburao
Tagum/ San Luis
P. indicus
29
Sta. Cruz
Tagbungan
Pinus merkusii
33
Bataan
Occ.
Mindoro
Occ.
Mindoro
Species
117
5
109
R-5
Albay
Guinobatan
Agpay
Polyscias
nodosa
16
R-6
Aklan
Tangalan
Jawili
Casuarina equisetifolia
35
Iloilo
Dingle
Bulabog Putian Nat.
Park
V. parviflora
11
Iloilo
Dingle
Bulabog Putian Nat.
Park
S. macrophylla
Philippines
109
8
110
Country Report on Forest Genetic Resources
Region
R-7
R-8
R-9
Province
Location/Barangay
Iloilo
Dingle
Bulabog Putian Nat.
Park
G. arborea
10
Iloilo
Leon
Omambong
P. indicus
34
Iloilo
Lemery
San Jose
Pittrosporum
pentandrum
23
Negros
Occ.
Bacolod City
Bacolod Tree Park/
Alangilan
C. equisetifolia
30
Cebu
Minglanilla
Camp 7
S. macrophylla
250
Cebu
Minglanilla
Camp 7
P. indicus
30
Cebu
Minglanilla
Camp 7
Dipterocarp
species
25
Cebu
Talisay City
Juanay
C. equisetifolia
28
Cebu
Talisay City
Juanay
E. deglupta
43
Cebu
Tabuelan
Danison,Tigbawan
C. equisetifolia
3
Cebu
Tabuelan
Danison,Tigbawan
E. deglupta
4
Cebu
Cebu City
Cantipla
A. mangium
29
Negros
Oriental
Mabinay
Bulwang
G. arborea
26
Siquijor
Bogo
V. parviflora
31
Siquijor
Maria
Umpas Liloan
V. parviflora
29
Leyte
Baybay
VSU Forest
Reservation Area
Diospyrus
philipinensis
5
Eastern
Samar
Quinapondan
Buenavista
D. grandiflorus
4
Eastern
Samar
Quinapondan
Buenavista
P. indicus
4
Eastern
Samar
Quinapondan
Buenavista
P. falcataria
Eastern
Samar
Quinapondan
Buenavista
S. macrophylla
Zamboanga Zamboanga
City
City
Pasonanca Park
P. plicata
9
Zamboanga Zamboanga
City
City
Pasonanca Park
S. macrophylla
7
Zamboanga Zamboanga
Pasonanca Park
City
City
Philippines
Species
No. of Candidate
Plus Trees
Town/City
P. indicus
302
53
25
Country Report on Forest Genetic Resources
Region
R-10
R-11
R-13
Province
Town/City
Location/Barangay
Species
111
No. of Candidate
Plus Trees
Zamboanga Zamboanga
City
City
Zamboanga City
Water District
(ZCWD)/P.
indicus Outpost,
Upper Dulian
P. plicata
Bukidnon
Impasugong
Impalutao Refo
Project
S. macrophylla
50
Bukidnon
Impasugong
Impalutao Refo
Project
P. contorta
48
Bukidnon
Impasugong
Impalutao Refo
Project
Agathis
philippinensis
32
Bukidnon
Kitaotao
East Poblacion
V. parviflora
88
Camiguin
Guinsiliban
So. Kibila, Cantaan
V. parviflora
60
Compostela
Nabunturan
Valley
G. arborea
25
Compostela
Nabunturan
Valley
S. macrophylla
25
Compostela
Nabunturan
Valley
E. deglupta
22
2
Compostela
Mawab
Valley
Sta. Ana
P. contorta
23
Compostela
Mawab
Valley
Sta. Ana
A. mangium
13
Davao del
Norte
Davao City
New Loon, Mintal
S. macrophylla
23
Davao del
Norte
Davao City
New Loon, Mintal
Tectona grandis
28
Davao del
Norte
Davao City
New Loon, Mintal
P. indicus
23
Davao del
Norte
Davao City
New Loon, Mintal
P. Contorta
47
Surigao
del Sur
Bislig City
PICOP Resources/
Maharlika
P. falcataria
28
Surigao
del Sur
Bislig City
PICOP Resources/
Maharlika
E. deglupta
17
Surigao
del Sur
Bislig City
PICOP Resources/
Maharlika
P. contorta
10
Agusan del
Sur
Butuan City
Mandakpan
P. falcataria
30
Reference: Development and Management of Forest Plantations in the Philippines: A guidebook. ERDB-DENR. 2010
Philippines
112
Country Report on Forest Genetic Resources
Appendix Table 8. Policy issuances related to forest genetic resources conservation
and sustainable use promulgated by the Philippine government
Policy
Nature of Policy
DENR Administrative
Order (DAO)
No. 2011-10
Declaring Cabusao Wetland Area Situated in Barangays Pandan
and Biong in the Municipality of Cabusao, Camarines Sur as Critical
Habitat pursuant to Section 25 of Republic Act No. 9147, otherwise
known as the “Wildlife Resources Conservation and Protection Act”,
Rules 25.1-25.5 of Joint DENR-DA-PCSD Administrative Order No.
01, Series of 2004; and DENR Memorandum Circular No. 2 Series of
2007 “Guidelines on the Establishment and Management of Critical
Habitat”, and in order to protect the habitat and population of the
endemic and threatened Anas luzonica (Philippine duck) along with
other species of wild fauna and flora, Cabusao Wetland Area situated
in Barangays Pandan and Biong in the Municipality of Cabusao,
Camarines Sur is hereby declared as Critical Habitat and shall be
known as the “CABUSAO WETLAND CRITICAL HABITAT”.
Executive Order (EO)
No. 23
February 01, 2011
Declaring a Moratorium on the Cutting and Harvesting of Timber in
the Natural and Residual Forests and Creating the Anti-illegal Logging
Task Force
Presidential
Proclamation (PP)
No.2011-139
Declaring Aliwagwag as as protected area under the category of
protected landscape and its peripheral areas as buffer zone situated
in the municipalities of Boston and Cateel, province of Davao Oriental
and in the municipality of Compostela, Province of Compostela Valley
and in the municipalities of Boston and Cateel, province of Davao
Oriental pursuant to R.A. 7586 (NIPAS ACT of 1992
DENR Administrative
Order No. 2010-03
Implementing Rules and Regulations of Republic Act No. 9237 or
“The Mount Apo Protected Area (MAPA) Act of 2003”
Pursuant to Section 28 of Republic Act No. 9237, otherwise known as
the Mount Apo Protected Area Act of 2003, this Administrative Order
setting forth the rules and regulations governing the implementation
of the Act is hereby promulgated
DENR Administrative
Order No. 2010-04
Implementing Rules and Regulations of Republic Act No. 9154
Pursuant to Section 23 of Republic Act No. 9154, otherwise known
as the Mount Kanlaon Natural Park Act of 2001, this Administrative
Order sets the rules and regulations governing the implementation
of RA
DAO 2010-11
Revised Regulations Governing Forest Tree Seed and Seedling Production, Collection and Disposition
DAO 2010-16
Establishing the “Adopt-A-Wildlife Species Program” and Providing
the Guidelines Governing the Implementation Thereof” Pursuant to
the provisions of R. A. No. 9147, otherwise known as the Wildlife
Resources Conservation and Protection Act, particularly on its avowed
policy to conserve and protect wildlife species and their habitats to
promote ecological balance and enhance biological diversity, and in
order to provide additional avenues for the Local Government Units
(LGUs), the private sector, Non-Government Organizations (NGOs),
Peoples’ Organizations (POs), civil society groups and other interested
individuals to participate in the government’s campaign to conserve
biodiversity and prevent species extinction
Philippines
Country Report on Forest Genetic Resources
113
DAO 2010-20
Revising the Technical Description of the Boundaries of Central
Cebu Protected Landscape (CCPL) and Designating its Buffer Zones
pursuant to Section 4 of RA No 9486 otherwise known as the Central
Cebu Protected Landscape Act of 2007 and Section 10(d) of RA 7586
or the National Integrated Protected Areas System Act of 1992 and
its Revised Implementing Rules and Regulations, and in line with
Resolution No. 2010-05-01 of the CCPL Management Board, the
following is hereby promulgated and adopted to set the final limits
of the CCPL
DAO No. 2009-01
Guidelines in Establishing the Wild Fauna Marking and Identification
System Pursuant to the objectives of Republic Act 9147, otherwise
known as the Wildlife Resources Conservation and Protection Act of
2001, and its Joint DENR-DA-PCSD Administrative Order No. 01, the
Implementing Rules and Regulations of RA 9147, and in compliance
to Article VI of the Convention on International Trade in Endangered
Species of Wild Fauna and Flora (CITES), a wild fauna marking and
identification system is hereby established
DAO No. 2009-09
Standard Design and Specification of Signs, Buildings, Facilities and
Other Infrastructure That May Be Installed and/or Constructed Within Protected Areas Pursuant to Section 10 (l) and (m) of Republic
Act No. 7586, otherwise known as the NIPAS Act of 1992 and its
Implementing Rules and Regulations, and Executive Order No. 111,
“Establishing the Guidelines for Ecotourism Development in the Philippines,” and all other laws/decrees, and to provide guidelines on the
design and specification of signs, buildings, facilities
PP
No. 2009-1815
Designating Mt. Mantalingahan Mountain Range as Protected
Landscape Area Upon recommendation of the Secretary of the
Department of Environment and Natural Resources (DENR) and the
Palawan Council for Sustainable Development (PCSD) hereby set
aside and designate Mt. Mantalingahan Mountain Range situated in
the Municipalities of Bataraza, Brooke’s Point, Sofronio Española,
Quezon and Rizal, all in the Province of Palawan as “Protected Area
under NIPAS and shall be known as Mt. Mantalingahan Protected
Landscape, subject to prior rights and without prejudice to the rights
of indigenous peoples as provided for in RA 8371, DENR Administrative
Order No. 93-02 and other related rules and regulations
DAO 2008-08
Guidelines on Self-Regulation of the Floriculture Industry for the
Sustainable Management of Philippine Wild Flora
Pursuant to
Republic Act No. 9147, otherwise known as the “Wildlife Resources
Conservation and Protection Act”, its implementing rules and
regulations, the Philippine Plant Conservation Strategy and Action
Plan, and the Philippine commitments under the Convention on
Biological Diversity (CBD) and the Convention on International Trade
in Endangered Species of Wild Fauna and Flora (CITES), promulgated
to encourage and support the floriculture industry to adopt selfregulation for the conservation and sustainable utilization of the
Philippine wild flora.
Philippines
114
Country Report on Forest Genetic Resources
DAO 2008-17
Amending Section 10 of DAO No. 25 Series of 1992 and Providing
Criteria in the Identification and Procedures in the Delineation and/or
Demarcation of Management Zones within Protected Areas Pursuant
to Republic Act No. 7586 otherwise known as the National Integrated
Protected Areas System Act (NIPAS Act) and its Implementing Rules
and Regulations, and to rationalize the designation of management
zones within protected areas, Section 10 of DAO 25, series of 1992
DAO 2008-18
Amending Section 8 of DENR Administrative Order No. 200445 - In
order to further streamline the procedure for the issuance of Wildlife export/import-export clearance for non-CITES species, second
sentence of paragraph 2, Section 8. ‘Exportation and Importation of
Wildlife” of DENR Administrative Order (DAO) No. 2004-55
DAO 2008-21
Amending DENR Administrative Order No. 2002-08 “Strengthening
the Coastal Environment Program (CEP) through the Establishment
of the Coastal and Marine Management Office (CMMO) - Pursuant to
Executive Order No. 192 and consistent with the Integrated Coastal
Management Strategy provided under Executive Order No. 533, the
coastal and marine management functions of the CMMO pursuant to
DENR A0 2002-08 are hereby transferred to the Protected Areas and
Wildlife Bureau (PAWB)
DAO 2008-24
Guidelines for the Assessment and Delineation of Boundaries Between
Forestlands, National Parks and Agricultural Lands - Pursuant to the
provisions of Section 4, Article XII of the 1987 Philippine Constitution,
Executive Order No. 192, Republic Act No. 3092, Republic Act No.
7586 and Presidential Decree No. 705, as amended, Executive Order
No. 318, DENR Administrative Order No. 2000-24 and other pertinent
laws, rules and regulations
DAO 2008-26
Revised Implementing Rules and Regulations of RA No. 7586 or the
NIPAS Act of 1992 - Pursuant to Section 10(d) of the NIPAS Act and
consistent with the Wildlife Resources Conservation and Protection
Act (R.A. No. 9147), Caves and Cave Resources Management and
Protection Act (R.A. No. 9072), Philippine Mining Act of 1995 (R.A.
No. 7942), and other laws establishing the specific components of
the NIPAS, DENR Administrative Order 25, Series of 1992 which is
the Implementing Rules and Regulations of the NIPAS Act
DAO 2007-01
Establishing the National List of Threatened Philippine Plants and
their Categories, and the List of Other Wildlife Species - Pursuant
to Section 22 of Republic Act No. 9147, otherwise known as the
“Wildlife Resources Conservation and Protection Act”, the National
List of Threatened Philippine Plants and their categories
DAO 2007-17
Rules and Regulations Governing Special Uses Within Protected Areas
- Pursuant to RA 7586 otherwise known as the National Integrated
Protected Areas System (NIPAS) Act of 1992 and its Implementing
Rules and Regulations
Philippines
Country Report on Forest Genetic Resources
115
DAO 2007-24
Amending DAO 2007-01, “Establishing the National List of Threatened
Philippine Plants and their Categories, and the List of Other Wildlife
Species” - In order to ensure effective implementation of the
provisions of DAO 2007-0 1
DAO 2007-34
Guidelines on Treasure Hunting in Caves Pursuant to Section 14 of
the National Caves and Cave Resources Management and Protection
Act (Republic Act No. 90723 and Sections 12, 13, 14 and 15 of its
Implementing Rules and Regulations
DMC 2007-02
Guidelines on the Establishment and Management of Critical Habitat
- Pursuant to Sections 4 and 25 of Republic Act No. 9147, otherwise
known as the “Wildlife Resources Conservation and Protection Act”,
Rules 25.1-25.5 of Joint DENR DA-PCSD Administrative Order No.
01, Series of 2004, and Executive Order No. 578 of 2006
DMC 2007-04
Procedure in Cave Classification - Pursuant to Republic Act No.
9072, otherwise known as the National Caves and Cave Resources
Management and Protection Act of 2001, and Sections 10, 12 and
13 of its lmplementing Rules and Regulations, (DAO 2003-29), a
Manual on Cave Classification is prescribed and adopted for all caves
within public domain and private lands, including those found within
protected areas for the guidance of all concerned
Republic Act (RA)
No. 9486
Central Cebu Protected Landscape Act of 2007 An act establishing
Buhisan Watershed Forest Reserve, the Mananga Watershed Forest
Reserve, the Sudlon National Park, the Central Cebu National Park
and the Kotkot Lusaran Watershed Forest Reserve into one protected
area to be known as the Central Cebu Protected Landscape and for
other purposes
EO 2006-533
Adopting Integrated Coastal Management as a National Strategy to
Ensure the Sustainable Development of the Country’s Coastal and
Marine Environment and Resources and Establishing Supporting
Mechanisms for its Implementation
EO 2006-578
Establishing the National Policy on Biological Diversity, Prescribing
its Implementation Throughout the Country, Particularly in the Sulu
Sulawesi Marine Ecosystem and the Verde Island Passage Marine
Corridor
RA No. 9494
Mimbilisan Protected Landscape Act - An act declaring the Mimbilisan
Watershed as a protected area under the category of protected
landscape, providing for its management and for other purposes
DAO 2005-21
Revised Guidelines on the Establishment and Management of
Integrated Protected Areas Fund (IPAF) - Pursuant to Section 10
of RA 7586 otherwise known as the National Integrated Protected
Areas System (NIPAS) Act of 1992 and its Implementing Rules and
Regulations and in order to provide flexibility in accessing the IPAF
DAO 2005-24
Guidelines on the Grant of Coastal Area Special Use Agreement
- Pursuant to Executive Order No. 192 and pertinent provision of
Republic Act No. 9 147(Wildlife Resources Act)
Philippines
116
Country Report on Forest Genetic Resources
Joint DENR-DA-PCSDNCIP AO No. 2005-01
Guidelines for Bioprospecting Activities in the Philippines 10/20/2009
Pursuant to the obligations of the Philippines under the Convention
on Biological Diversity and other relevant international agreements,
the provisions of Executive Order No. 247 (1995) as amended by
Section 14 of the Wildlife Act (Republic Act No. 9147) and Section
35 of IPRA (Republic Act No. 8371), in relation to the NIPAS Act
(Republic Act No.7586), the Local Government Code (Republic Act No.
7160), the SEP for Palawan Act (Republic Act No. 7611), the Fisheries
Code (Republic Act No. 8550), the Seed Industry Development Act
(Republic Act No. 7308), the Traditional and Alternative Medicine Act
(Republic Act No. 8423) and other relevant laws
DAO 2004-01
Implementing Rules and Regulations (IRR) Pursuant to Republic Act
No. 9147 otherwise known as the Wildlife Resources Conservation
and Protection Act of 2001.
DAO No. 2004-15
Establishing the List of Terrestrial Threatened Species and Other
Wildlife Species - Pursuant to Sections 5 22 of Republic Act No. 9147
otherwise known as the “Wildlife Conservation and Protection Act
DAO No. 2004-17
Determining and Delineating the Actual Metes and Bounds of the
Samar 10/05/2009 Specifying the Guidelines and Reference Points
In Determining and Delineating the Actual Metes and Bounds of the
Samar Island Natural Park (SINP), as established under Presidential
Proclamation 442 date d August 13,2003
DAO No. 2004-32
Revised Guidelines on the Establishment and Management of
Community-Based Program in Protected Areas - Pursuant to Republic
Act No. 7586 (National Integrated Protected Areas System (NIPAS)
Act of 1992), DENR Administrative Order No. 25, Series of 1992
(Implementing Rules and Regulations of NIPAS Act) and Executive
Order No. 263 (Adopting Community-Based Forest Management
as the National Strategy to Ensure the Sustainable Development
of the Country’s Forestlands Resources and Providing Mechanisms
for its Implementation), and to facilitate the implementation of the
Community Based Program (CBP) in Protected Areas, DAO 2002-02
(Guidelines on the Establishment and Management of CommunityBased Program in Protected Areas) is revised
DAO No. 2004-55
DENR Streamlining/Procedural Guidelines Pursuant to RA 9147 ;
Pursuant to the provisions of the Joint DENR-DA-PCSD Administrative
Order No. 01 Series of 2004
DAO No. 2004-62
Prescribing Fees and Other Guidelines on the Implementation of
DENR A. O. Nos. 2004-55 and 2004-58
DAO No. 2004-65
Waiving Certain Provisions of DENR Administrative Order (DAO) No.
2004-62 - Promulgated to give zoo owners, hobbyist, pet owners
and private wildlife collectors the opportunity to have their wildlife
stock and facilities registered with the DENR, the corresponding fees
for the registration of threatened, non-threatend and exotic faunal
species, as provided for under Section 3 of the DAO 2004-62
Philippines
Country Report on Forest Genetic Resources
117
DENR Memorandum
Circular (DMC)
2004-06
Guidelines in the Integration of Rainforestation Farming Strategy
Pursuant to the provisions of Executive Order No. 192 and in line
with our commitment to the UN Convention on Biological Diversity,
the Framework Convention on Climate Change, the UN Convention
to Combat Desertification and the United Nations Forum on Forests,
and to the principle of Sustainable Forest Management, the following
guidelines for the integration of rainforestation farming strategy in
the development of open areas and denuded forests to promote
biodiversity conservation and sustainable development in protected
areas and other appropriate forest lands
DMC 2004-09
Amending DMC 35, Series of 1993 - Pursuant to Republic Act No. 7586
or the NlPAS Act and in order to provide a more appropriate criteria
that will suit the present biophysical and socio-economic conditions
of protected areas in the country, the criteria and guidelines for the
categorization of protected areas under NlPAS as provided under
Annex A of DMC35 Series of 1993 is hereby amended
DAO No. 2003-29
Implementing Rules and Regulations of the Republic Act No. 9072
Pursuant to Section 11 of Republic Act No. 9072 otherwise known as
the “National Caves and Cave Resources Management and Protection
Act”, this Administrative Order setting forth the rules and regulations
governing the implementation of this Act
DMC 2003-01
Harmonization IPRA and ENR Laws and Policies - issued in order
to address the issues affecting the rights of the Indigenous Cultural
Communities/Indigenous Peoples (ICCs/IPs)in relation to the
implementation of the IPRA and ENR laws and policies
PP 2003-426
Amending Proclamation No. 2152 Which Declared Parts of the
Country as Mangrove Swamp Forest Reserves; by segregating there
from certain portions of the Island of Panglao, Province of Bohol
and reserving the same as a protected area pursuant to Republic
Act No.7586 (NIPAS Act of 1992) to be known as Panglao Island
Protected Seascape, under the administration of the Department of
Environment and Natural Resources, subject to valid private rights, if
any there be, and actual ground survey.
PP 2003-441
Central Cebu Protected Landscape - set aside, declare and consolidate
the aforecited five reservations into one protected area, located in
the Cities of Cebu, Talisay, Toledo and Danao and in the Municipalities
of Minglanilla, Consolacion, Liloan, Compostela and Balamban,
Province of Cebu, as Protected Area under the category as Protected
Landscape, subject to private rights and without prejudice to the
rights of the Indigenous People as provided for in R.A. 8371, DENR
Administrative Order No. 93-46902 and other rules and regulations
if any
PP 2003-442
Declaring the Samar Island Forest Reserve as a Protected Area and
its Peripheral Area as a Buffer Zone
Philippines
118
Country Report on Forest Genetic Resources
PP 2003-484
Amending Proclamation No. 416 and Re-naming as the “Peñablanca
Protected Landscape and Seascape” - amends ProclamationNo.416
dated 29 June 1994 which established the “Peñablanca Protected
Landscape” by expanding its coverage to include certain parcels of
lands of the public domain situated in the Municipality of Peñablanca,
Province of Cagayan, embracing the forest, agricultural, caves and
coastal ecosystems therein. and renaming the same as “Peñablanca
Protected Landscape and Seascape”, subject to existing recognized,
and valid private rights and without prejudice to the rights of the
indigenous people as provided for in RA 8371, DENR Administrative
Order No. 93-02, and other relevant rules and regulations
RA No. 9237
Mount Apo Protected Area Act of 2003 - act establishing Mount Apo as
a protected area under the category of natural park and its peripheral
areas as buffer zones, providing for its management, and for other
purposes
DAO 2002-31
Amending DENR Administrative Order No. 2000-83 - Pursuant to
the Department’s thrust on the sustainable development of our
natural resources and to generate revenues from the operation of
the existing establishments in the form of fees and charges, DENR
Administrative Order No. 2000-83 “Guidelines for the Management
and Development of Small Islands, Including its Coastal Areas” is
amended
DAO No. 2002-02
Establishment and Management of Community-Based Program in
Protected Areas - Pursuant to Republic Act No. 7586, otherwise
known as the National Integrated Protected Areas Act (NIPAS Act) as
implemented by DAO No. 25 series 1992, requiring a management
planning strategy of protected areas and providing protection to
qualified tenured migrant communities and interested indigenous
people; and, EO No. 263 entitled “Adopting Community-Based Forest
Management as the National Strategy to Ensure the Sustainable
Development of the Country’s Forestlands Resources and Providing
Mechanisms for its Implementation,” this Administrative Order is
promulgated
DAO No. 2001-02
Amending Relevant Provisions of DAO 2000-68 - issued to effectively
implement the coastal and marine environment and biodiversity
conservation programs and projects of the Department of
Environment and Natural Resources (DENR) the relevant provisions
of the aforementioned Department Orders are hereby amended and
other related programs/ projects and activities, be placed within the
Protected Areas and Wildlife Bureau
DMO 2001-06
Adoption of Prescribed Methods in Monitoring Biodiversity - All
concerned Offices, officials, and personnel are directed to adopt
the methods prescribed in the attached Biodiversity Monitoring
System Manual in monitoring biodiversity in terrestrial and wetlands
(freshwater and marine). The Manual was jointly prepared by
Protected Areas and Wildlife Bureau and the WB-Technical Assistance
for Improving Biodiversity Conservation in Protected Areas of the
Philippines Project through NORDECO.
Philippines
Country Report on Forest Genetic Resources
119
DMC 2001-11
Status of Biodiversity Monitoring System (BMS) Implementation
and Results - prescribed the standard format which shall be used by
PAWB and the Regional Offices, specifically PAWD, in the quarterly
monitoring and evaluation of BMS implementation and results. The
Regional Offices shall submit the accomplished forms to PAWB
RA No. 9125
Northern Sierra Madre Natural Park (NSMNP) Act of 2001 - An act
establishing the northern sierra madre mountain range within the
province of isabela as a protected area and its peripheral areas as
buffer zones providing for its management and for other purposes
RA No. 9154
Mt. Kanlaon Natural Park Act of 2001 - An act establishing Mt. Kanlaon
as a protected area and a peripheral area as a buffer zone providing
for its management, and for other purposes
DAO 2000-13
Guidelines on the Implementation of the Biodiversity Monitoring
System (BMS) in Protected Areas - promulgated pursuant to
Republic Act No. 7586 (NIPAS Act) and its Implementing Rules and
Regulations, in line with the Philippine commitment to the Convention
on Biological Diversity, and in order to provide up-to-date and
comparable information on resources as basis for the management
of protected areas
DAO 2000-44
Provisions of DAO 96-29 and Guidelines for Community-Based Projects
Within Protected Areas - issued pursuant to the action agenda of
consolidating all forestry programs into an over-arching Sustainable
Forest Management Program, DAO 96-29, the Rules and Regulations
for the implementation of Executive Order No. 263, otherwise known
as the Community-Based Forest Management Strategy, is hereby
amended to align it with the provisions of Republic Act 7586, otherwise
known as the National Integrated Protected Areas Systems (NIPAS)
Act of 1192, and specifically to provide the following guidelines on
the establishment and management of Community-Based Projects
(CBP) within protected areas
DAO 2000-51
Determining Fees for Access to and Sustainable Use of Resources in
Protected Area - promulgated pursuant to the, provisions of Republic
Act 7586 otherwise known as the National Integrated Protected
Areas System (NIPAS). Act of 1992 and its Implementing Rules and
Regulations, and in order to provide guidelines and principles in
accessing and sustainably using resources in protected areas
DAO 2000-89
Amending Sections 7, 8.2 and 9 of DAO No. 97-36, Series of 1997
Pursuant to Section 4 of E.O. 192, Series of 1987 of which the
DENR is mandated to provide nature conservation awareness for the
protection of the natural resources and in order to further strengthen
the Dalaw-Turo capability, Sections 7,8.2 and 9 of DAO 97-36 dated
December 15, 1997 is amended
RA No. 8978
Mt. Katinglad Range Protected Area Act of 2000 - An act declaring
that Mt. Kitanglad Range in the province of Bukidnon as a protected
area and its peripheral areas as buffer zones, providing for its management and for other purposes
Philippines
120
Country Report on Forest Genetic Resources
RA No. 8991
Batanes Protected Area Act of 2000 - An act to establish the Batanes
Group of Islands and Islets as a protected area, and its peripheral
waters as buffer zones, providing for its management and for other
purposes
RA No. 9106
Sagay Marine Reserve Law - An act for the establishment and
management of sagay marine reserve, defining its scope coverage,
and for other purposes
Appendix Table 9. Wildfood plants in the Philippines forest
Wildfood
Plant Species
Scientific Name
Specific Food Value
1.
Lubigan
Acorus calamus L.
Powdered rhizomes used as condiments
2.
Biga
Alocasia macrorrhiza
(L.)
Stems and corms are eaten after roasting
or boiling. Heating helps in destroying the
harmful substance raphides.
3.
Langkauas
Alpinia pyramidata
Blanco
The rhizome is used as a condiment. Its flavor
is similar to ginger, but much less pungent. It is
also cooked with the sap of sugar cane or with
honey and water produce an antitoxicating
beverage. The young rhizome and tender
underdeveloped shoots are eaten, as are also
the flower and flowers buds.
4.
Kulitis
Amaranthus tricolor
Young leaves and stems are boiled and eaten
as vegetables. It is also used as a substitute
for spinach.
Pongapong
Amorphophallus
campanulatus
(Roxb) Bl. ex Decne
The petioles of young, unexpanded leaves are
edible, when thoroughly cooked. When food
is scarce, the corm is sometimes eaten. The
leaves and corms are common feed for hogs.
Antidesma bunius
(L.) Spreng
The fruits are seldom utilized in the Philippines
and are left to be eaten by birds. However,
they may be eaten out of the hand or made
into an excellent wine and refreshing drink.
They are also sometimes used in the preparation of various dishes as a substitute for tomato as vinegar. Leaves are eaten with rice
when young.
5.
6.
Bignai
Philippines
Country Report on Forest Genetic Resources
121
7.
Aunasin
Ardisia pyramidalis
(Cav.) Pers.
The young leaf tips are used as greens,
or cooked with meat or fish and eaten as
vegetable. The flowers and fruits are cooked
as flavoring for fish, as salad, the young
leaves are blanched, then mixed with onions,
tomatoes, garlic and salt. The young leaves
are eaten by deer and the fruits by monkeys,
wild pigs and birds.
8.
Kaliso
Areca caliso
Becc.
Bud is cooked and eaten as vegetables. Sap
for inferior beverage. Fruits substitute for
betel nut.
Kaong
Arenga pinnata
(Wurmb) Merr.
Kaong seeds are edible. The fleshy kernels of
the right stage of endosperm are coked and
eaten or made into sweets. The buds are
eaten raw as an excellent salad or cooked
as vegetables. The sweet sap is used in the
production of sugar starch, vinegar and “tuba”
(a native drink).
10. Gumayaka
Arenga tremula
Peduncles tapped for sap known as “tuba”.
Buds eaten in large quantities cause profound
sleep.
11. Zamboangita
Asystasia gangetica
Leaves and flowers are pot herbs, adjunct to
fish and meat stew.
12. Api-api
Avicennia officinalis
The fruits or leaves are eaten raw or cooked.
13. Kawayan tinik
Bambusa blumeana
Schultes
The young shoots are fairly tender are used
for food. Bamboo shoots or labong are source
of calcium and iron. It can also be cooked into
dinengdeng together with saluyot or jute.
14. Botong
Barringtonia asiatica
(L.) Kurz
The young shoots of this plant are eaten fresh.
It is however slightly astringent.
15. Alibangbang
parang
Bauhinia malabarica
Roxb.
The leaves of this species are sour, and are
used considerably by the Filipinos for flavoring
meats and fish. Young leaves are eaten raw
as a side dish to rice or cook with soups and
stews.
16. Puriket
Bidens pilosa
Seeds are used in making Igorot wine called
“sinitsit”. In the Mt. Province it is considered
as vegetable.
9.
Philippines
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Country Report on Forest Genetic Resources
17. Tuai
Bischofia javanica
Blume.
The young soft leaves are cooked and eaten
as vegetables.
18. Busaing
Bruguiera
gymnorrhiza
(L.) Lam.
Fruits boiled in water twice, the whole fruit,
the second with its outer covering removed
and eaten. Hypocotyl of germinating seed is
edible.
19. Himbabao
Allaenthus luzonicus
(Blanco) F. Vill
The young leaves and male inflorescence of
Himbabao are cooked and eaten as vegetable.
It could be cooked solely or in mixture with
other vegetables such as eggplant, bitter
melon, cabbage, sweet potatoes, etc., and
seasoned with fish and tomatoes. Flowers
are blanched and make a good salad. Alukon
flowers can be mixed with moist and vegetable
recipes. It tastes best when used in nilagang
baboy, manok or baka, pinakbet and stir-fries
with either meat or fish.
20. Limuran
Calamus ornatus
This palm species is a source of raw materials
for the manufacture of furniture, basketry,
fishtrap, hats, fans, and hats.
Caryota cumingii
Lodd.
The seed of this species is used as a substitute
for chewing. The sap is a source of “tuba” or
palm wine. The bud is collected and used as
vegetable. It is cooked with coconut milk or
sometimes sauted with fish and meat.
22. Takip-kuhol
Centella asiatica
Eaten whole, raw or steamed, as salad, for
stew or potherb and soup. Widely used as food
because of high vitamin and mineral content
in addition to carbohydrates and proteins.
23. San Francisco
Codiaeum variegatum
Young leaves are blanched for salad. It has a
nutty flavor especially the yellow ones.
24. Adlai/Tigbi
Coix lacryma-jobi
The hulled grain analyses about the same
as wheat but with a somewhat higher face
content. It may be eaten like rice, and cracked
as oatmeal. The flour mixed with one-third
to one half wheat flour makes good bread,
biscuits and hotcakes. It is considered as
reserves for food in times of scarcity.
25. Alikbangon
Commelina benghalensis
Young leaves
vegetables.
21. Pugahan
Philippines
are
cooked
and
eaten
as
Country Report on Forest Genetic Resources
123
Corchorus olitorius
Cooked into dinendeng, pakbet or adobo. In
Bengal it is very common to add a few leaves
of the plant to the daily diet with rice, as it
is considered to be tonic. Slaves from India
made much use of it as vegetable. When
cooked they are very mucilaginous and slimy.
The flavor is very good.
Corypha elata
Roxb.
Starch is obtained from the trunk like sago
palm, sugar, syrup, vinegar and wine from the
sap of the tender inflorescence, and excellent
preserves are made from the immature seeds
boiled in sugar.
Cycas circinalis L.
Young rolled leaves are cooked and eaten
as a vegetable. Ripe seeds are crushed and
soaked in several changes of water to remove
the poisonous substance and died flourlike product is cooked into small cakes or as
porridge.
29. Katmon
Dillenia philippinensis
Rolfe.
The fruit is rounded and contains soft, fleshy,
green pulp, with a flavor resembling that of
the apple. It used for flavouring fish and it
makes an excellent sauce or jam. It can also
be eaten raw.
30. Balubo/Balobo
Diplodiscus
paniculatus Turcz.
The seeds are starchy and eaten boiled like
lima beans.
31. Paco
Diplazium esculentum
The young fronds are much desired and are
eaten in all parts of the Islands, either raw or
cooked. They are used as leafy vegetable or as
an ingredient of stew or even pickled. Young
fiddle heads are eaten as salad.
32. Apulid
Eleocharis dulcis
The tuber of this species are dark-colored, 2
to 3 cm in diameter and are boiled and eaten
as a vegetable.
Ficus nota
(Blanco) Merr.
The young leaves are cooked as vegetables
and the fruits are eaten raw when ripe. The sap
of the freshly cut stems also yields drinkable
water. The fresh of the cyconium fruits are
used for ice cream flavour.
26. Saluyot
27. Buri
28. Pitogo
33. Tibig
34. Balete
35. Pakiling
Ficus balete Merr.
Ficus ororata
(Blanco) Merr.
The young folded leaves are cooked as
vegetables. Seeds are roasted and used as
substitute for coffee.
The fleshy portion of the fruit and seed are
eaten raw.
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Country Report on Forest Genetic Resources
36. Niog-niogan
Ficus pseudopalma
Blanco
Young leaves are cooked and eaten as
vegetable with coconut milk, meat or fish.
37. Bitongol
Flacourtia rukam
Zoll. & Mor. (Flac.)
Bitongol is eaten off-head when fully ripe. It
also make a good jam, pies and preserve and
is popular in making pickle.
38. Kakawate
Gliricidia sepium
(Jacq.)
Leaves used as adjunct to Filipino dish, adobo.
39. Bago
Gnetum gnemon L.
Young leaves, flowers and fruits are cooked
with sea foods, an excellent side-dish. Ripe
fruits are roasted and while hot, pounded into
thin round cakes. These are cooked in boiling
oil where they puff into a porous, crisp cake
called “ Krupuk”.
40. Gumamela
Hibiscus rosa-sinensis
Pickles from the petals of the flowers and torta.
Flower buds and leaves for salad, omelet and
potherb.
41. Roselle/Red
sorrel
Hibiscus sabdariffa
Young leaves may be used as substitute
for spinach, or may be cooked with fish for
meat in making sinigang. The calyx which is
thick, fleshy and sour makes excellent jelly.
The unripe fruit is adapted for pickles and a
refreshing beverage is made from it. Roselle
is used for making tarts, jellies, wine and a
variety of other products.
42. Anahau
Livistona rotundifolia
(Lam.) Mart.
The soft endosperm of this species is eaten
raw or is made into preserves. The buds are
cooked and eaten as vegetables with coconut
milk.
43. Binunga
Macaranga tanarius
(L.) Muell-Arg.
The bark, leaves and fruit are used in
fermenting drink known as “basi”. The fruit is
sometimes used for the same purpose.
44. Gabing-uak,
upi-upi
Monochoria vaginalis
Tubers are eaten in the mountain of Luzon. In
Malaysia the leaves are eaten raw or cooked.
45. Bangkoro
Morinda citrifolia
The fruit of this plant is eaten raw young leaves
may leaves may serve as vegetable.
46. Pulau/Lauas
Nymphaea nouchaii
Seeds are eaten raw, petiole and corm cooked
and eaten as a vegetable salad with various
dressing, or as ingredients of stews.
47. Nipa
Nypha fruticans
The flesh of the young nuts makes good
desserts or may be eaten raw. Sap is a source
of vinegar and sugar. Heat cabbage (bud).
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48. Beach
pandan,
screw pine
Pandanus tectorius
Soland.
Fleshy portion of lower part of mature fruit
eaten raw.
49. Pansitpansitan
Peperomia pellucida
Eaten as green salad
50. Iba
Phyllanthus acida
The fruit is about as large as a small grape,
ribbed, pale green. Excellent for jelly and
varying preserves and makes a good “ade”.
Pisonia grandis
The tender leaves make good greens, boiled,
eaten with meat, butter and vinegar, when
they resemble spinach, sometimes cooked
with coconut milk.
51. Maluko/kolis
Young leaves are eaten as vegetables. It
is boiled to destroy the stinging crystals
or raphides which are very abundant in the
leaves. This is a famine food in India, while the
Chinese eat the young leaves cooked.
52. Kiapo or
Quiapo
Pistia stratiotes L.
53. Hanapol
Poikilospermum
suaveolens
Freshly cut stem exude water for drinking and
cooking.
54. Golasiman,
olasiman
Portulaca oleracea
Young leaves and stems are used as adjuncts
to stews, meat and fish sinigang. It can be
eaten as salad. The fatty or slimy quality of
purslane is sometimes objectionable, but
by chopping the cooked tip and then baking
with bread crumbs and beaten egg, their
disagreeable quality is entirely disguised.
55. Alagau
Premna odorata
Blanco
Young leaves mixed with “hito”, a fresh water
fish, when cooked with coconut milk.
56. Tangolon
Quisqualis indica
The tender shoots are cooked and eaten.
57. Sundang hari
Rhoeo spathacea
Young leaves potherb
58. Bakauan-babae
Rhizophora
mucronata Lam.
Young leaves for potherb. Bark is used for
flovouring of local wine “tuba”.
59. Atibulnak
Rubus pectinelllus
The fleshy pulp of the riped fruit is eaten raw
by man, birds and deers.
60. Bikal
Schizostachyum
diffusum
Freshly cut stems gives water for drinking
61. Malabulak
Salmalia malabarica
Schott & Endl.
Buds, young pods and roots of seedlings are
cooked and eaten.
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62. Balatong
aso, mongomongohan,
andasasi
Senna tora
Young leaves for potherb and roasted seeds
for coffee substitute.
63. Katuray
Sesbania grandiflora
(L.) Pers.
The flowers and pods can be eaten raw or
cooked in steam and prepared as an excellent
salad.
64. Dampalit
Sesuvium portulacastrum
The stems and leaves when boiled are eaten as
a vegetable. It is mixed with fish or meat. The
leaves give a sour flavouring in the mixture. It
could also be blanched and served as a salad
dish with sliced tomatoes and fish sauce or
salt.
65. Talongtalongan,
tarumbulo
Solanum cuminggi
Dun.
The unripe fruits are cooked with either fish
or meat and eaten as vegetable. No analysis
has been made so far on the constituents of
its edible parts.
66. Kunti
Solanum nigrum
The riped fruits are picked and eaten raw.
It is also prepared into jams and pies in the
rural areas. The leaves and young shoots are
cooked and eaten as vegetables like spinach.
67. Pagatpat
Sonneratia alba J.
Sm.
The fruit is used for food and also for making
vinegar.
68. Pedada
Sonneratia caseolaris
(L.) Engl.
The fruits are cooked and eaten and are also a
source of vinegar.
69. Malunggayhapon
Souropus androgynus
Leaves for stew or salad.
70. Kandikandilaan
Stachytarfetta
jamaicensis
Leaves are for stew or omelette. The dried
leaves are made to Brazilian tea.
71. Tuhod-manok
Synedrella nodiflora
Young shoots are eaten raw as salad or cooked.
72. Kalubkob
Syzygium calubcob
(C.B. Rob) Merr.
The fruit when ripe is delicious and are eaten
raw.
73. Lipote
Syzygium
polycephaloides
(C.B. Rob) Merr.
The edible part of this species is the fleshy
portion of the fruit which is eaten raw. Fruits
are mixed with wine for flavouring lambanog
in Quezon.
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74. Yabyaban
Maranta arundinaceae
Corm and rhizomes are baked. Starch should
be washed several times to eliminate bitter
substance in the corm. Tacca flour or starch
formed an agreeable food when eaten with
sugar. And that mixed with white wine flour
it is used in making bread. In preparing the
flour, rub the tubers under water with rough
stone, allow the starch to settle, pour out the
water, and then dry the product.
75. Talinum
Talinum triangulare
Young leaves or stems are used as adjuncts to
stews, meat and fish sinigang. It can be eaten
as salad.
76. Kalumpit
Terminalia microcarpa
Decne.
The fruit is eaten raw when ripe (violet-black
color) and because of its fleshy and acidic
characteristics, they are good for preserves.
The ripe fruit are boiled and cooked with sugar,
oftentimes fruits are sun-dried for longer
storage. They can also be dehydrated or made
into wine.
77. Toston
Trianthema
portulcastrum
The plant is eaten as a leafy vegetable.
78. Gabigabihan, gabing
nuno
Typhonium trilobatum
Rootstocks boiled, are eaten alone or with
stems.
79. Hilagok,
susong
kalabau
Uvaria rufa
Fruits are eaten raw or cooked as vegetables.
80. Lagundi
Vitex negundo
Seeds are boiled and eaten.
81. Ambung
Arenga ambong Becc.
Buds are edible and can be eaten as salad.
82. Anahaw
Livistonia rotundifolia
(Lam.) Mart
Anahaw buds are highly esteemed as a
vegetable. Nuts are eaten when young and
green. The rind is tasty when ripe.
83. Anibong
Oncosperma
gracilipes
The young shoot buds (ubud) are edible.
Corypha elata Roxb.
Buri buds are eaten cooked or raw as salads.
The kernels of the young fruits are processed
into sweets. The trunk of the buri tree contains
a good quality of starch even during its growing
stage. The starch is collected when the tree
dies. Buri sap is one of the sources of the
fermented drink locally known as “tuba”. The
fresh sweet sap is a good source of beverage
and can be made into a good cidar when
fermented. Fermentation takes place within
32 hours after the sap is obtained.
84. Buri
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85. Sago
The trunk contains plenty of starch deposits
with high food value. A healthy mature tree
may have about 6-7m long trunk containing
starch. During World War II, sago starch served
as a good substitute for rice and corn (staple
food) in places where this plant abounds. At
present, the starch also serves as substitute
doe flour and has high demand in the world
market. Sarawak (an island in Borneo) is the
chief exporter of sago starch.
Metroxylon sagu
The pith can also be toasted and eaten
although the taste is somewhat bitter. The
shoot in some other palms is also edible. Sago
palm can be extracted and made into wine,
vinegar, or sugar.
86. Takipan
Caryota rumphiana
Mart.
The young shoot bud (ubod) can be eaten raw
or cooked.
87. Niog
Cocos nucifera L.
Fruits of coconut are edible and can be
preserved as sweets. It yields oil for food and
lard.
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Appendix Table 10. Forest species used as raw materials for holiday decors,
wearables, gifts, and other novelty items.
Common name/ Scientific
name Scientific name
Economic importance
FOREST VINES
Abuhab-baging
(Strophantus caudatus (L.)
Kurz)
The stems are suitable for handicraft production. The species
is also employed in traditional medicine, specially as a diuretic.
Bulakan
(Merremia peltata (L.) Merr.)
Stems are collected for basket and handicraft production.
Because of relatively inferior appearance and strength, the
stem is utilized as substitute materials whenever the preferred
species become scare or unavailable.
In traditional medicine the species is employed as a purgative
and a remedy of cough, diarrhea and worms. Leaves are used
when washing hair and applied as poultices to sore breasts,
ulcers and wounds. The leaf extract has antibacterial properties
and a positive reaction to alkaloids. A drink from the juice of
leaves is reputed to treat hernia.
It is considered as one of the most damaging weed species in
some industrial forest plantation in Indonesia (Narif Prantini,
1991).
Hinggiw kalabaw
(Streptocaulon baumii Decne.)
An inherent strength and durability make hinggiw-kalabaw a
preferred species in the vinecraft industry. The stems are made
into basket and other handicraft products.traditionally, they
have been used for tying purposes. However, the supply has
significantly dwindled due to over harvesting and uncontrolled
exploitation. Although not observed ion a 2002 field study in
Tayabas, Quezon, the species may still be available in adjacent
areas such as Dolores, Pagbilao and Mauban. In 1992 an
estimated 1,117 lineal meters per hectare was recorded in
Quezon ( Aragones et al. 1992).
The latex of hinggiw-kalaban is used as a vulnerary.
Lukmoy
(Rhaphidophora monticola
Krause)
The aerial roots are ideal for weaving into baskets, handicrafts
and other novelty items because of their uniform width.
Leaf extracts have some traditional medicinal properties.
Malagayaman
(Pothos scandens L.)
The aerial roots are good materials for making baskets and
other handicrafts because of their uniform width.
Malayaman is used in Thailand as a blood coagulant for wounds.
Fruits and leaves are made into a compress. In Myanmar, the
infusion of stems and leaves is drunk as “tea” (Boyce, 2000).
Silong pugo
(Pericampylus glaucus (Lam)
Merr.)
The stems are favorite raw materials for woven handicrafts
such as baskets and bags because of their small diameter and
uniform width.
The species is also used in traditional medicine. The barks and
roots are rich in the alkaloids menisidine and menisine and
used as narcotic. The leaves are used to cure headache, cough
and asthma. The sap is applied as an eye medicine.
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Tagolaway
(Parameria laevigata
(A.L.Juss) Moldenke)
The stems are used in basket and handicraft production.
The species is used in traditional medicine. It yields good quality rubber although the quantity obtained is not on a commercial scale.
Wood rose
(Merremia tuberose (L.)
Rendle)
In Europe,the woody fruits are used in flower arrangement.
In the Philippines, the fruits are collected while still buds, air
dried until they open and varnished or painted for flower arrangement and decoration purposes.
Wood rose is employed in traditional medicine in Southeast
Asia. The tuber is used as a drastic purgative. The roots contain 12-25% resin, which show allelopathic activity on the
radicle of Amaranthus sp. wheat and oats. No antibacterial activity has been reported, however, against Bacillus subtilis and
Escherichia coli. The species is also planted as an ornamental
in Africa.
SEEDS
Gugo
(Entada phaseoloides (L.)
Merr.)
Job`s tears
(Coix lacryma-jobi L.)
Kansasaga
(Abrus precatorius L.)
The bark fibers are strong and durable and converted into rope
and raw materials for baskets and handicraft. The large and
hard seeds are used for novelty items, while the large pods are
made into coin purses.
The plant is one of the chief sources of traditional hair wash
throughout Southeast Asia. However, when using as hair wash,
contact with the eyes should be avoided because the juice is
irritating, painful and may even cause conjunctivitis.
Gugo is widely employed in traditional medicine as remedial
wash for pityriasis, wounds and itch and externally applied as
a remedy for filariasis or elephantiasis. It is used to treat many
other illnesses and complaints throughout Southeast Asia. Its
medicinal use is traced to the presence of saponins in the bark,
wood and seeds.
Job`s tears is cultivated as an ornamental plant and more
importantly for its beads, which are used in rosaries and
jewelry. The soft shelled false fruit are easily husked, while the
large kernels are eaten in the same way as rice. Job`s tears
can substitute for rice in rice based recipes. Flour is produced
from the kernels. The whole grains are fed to poultry. The
species is also cultivated as fodder for cattle and horses. It
reportedly has medicinal application.
The peculiar beautiful and hard seeds are used for ornaments
and handicrafts, particularly as beads in rosaries and necklaces
and also in soldering jewelry.
The species is widely used in traditional medicine to treat a
variety of illnesses and diseases. It has a high reputation in
the Ayurvedic, homeopathic, Unani and allopathic system of
medicine. Seeds are used to treat conjunctivitis, malaria and
dysentery in various parts of the world. The juice extracted
from the roots and leaves are used to treat aphtha.
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FIBERS
Abang abang
[Curculigo capitulate (Lour.)
Kuntze]
It has been recently used as accents on basket and other
handicraft products. False hair from the leaf fibers has been
made by natives of the Camarines Province (Luzon, Philippines).
It is used by children in Ifugao province (Luzon, Philippines)
for warp in toy looms. The tough and thin leaves are used
by natives of northern Thailand for wrapping just like banana
leaves. Abang abang fibers are relatively hard in contrast to
the cotton fibers and durable in humid, warm climate because
they naturally resist fungi. Strong and durable garments have
bee made from the fibers by natives of Borneo.
The species is widely used in traditional medicine to treat
several illnesses. In Peninsular Malaysia, an infusion of the
leaves, stem tips and roots is used internally against fever.
The flower and root decoction is taken as a cure for stomach
aches and as a diuretic. The rhizome decoction is used to treat
menorrhagia and applied as lotion against ophthalmia.
It is widely employed as an ornamental plant in the Philippines.
Indonesia, India, Africa, Europe, and the United States because
of its inflorescence that resembles that of ground orchids.
The fruit are known to be edible, taste like sweetened
cucumber, and increase appetite. They are not extremely
sweet by themselves, but leave a very sweet aftertaste. This
is most noticeable when a sour substance is consumed after
eating the fruits. The sweetness is provided by a protein known
as curculin, which is synthesized in the fruits a week after
pollination. Curculin`s sweet taste disappears rapidly after
about 10 minutes.
Anubing
(Artocarpus ovatus Blanco)
Bast fibers from the bark matted, dull, strong and durable,
pinkish brown to yellowish brown with time, soft and pliable.
Acquired after retting the bark for 3-4 weeks, they are beaten
well to obtain uniform layered. Sheets or mats suitable for
crude clothing or other novelty items. An appropriate volume
of strips is twisted together to form tying materials.
Latex (also known as anubing gum) from the species is a
promising material for chewing gum. The species is suitable
for purposes of requiring strength and durability such as house
posts, telegraph poles and bridges based on its wood density.
The bark decoction is applied against stomach ache.
Mais
(Zea mays L.)
The modified leaves enclosing the ear (also known as husk)
and the cob are made into ladies bags, hats, decors, novelty
items and display items.
Corn is widely used as a staple food. It is also used as a
main raw materials and poultry feeds and in many industrial
products.
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Patola
(Luffa aegyptiaca Mill.)
Mature and fibrous fruits are used as display items and for
other handicraft products.
Patola is a well known vegetable especially in the tropics. The
immature fruits, young leaves and flower buds are cooked and
used in soups, or sliced and dried for later use. Sweet cultivars
are now available. Young fruits are eaten pickled. The plant
also yields constituents for traditional medicine and cosmetic
purposes especially in China and Japan. The seeds produce
edible oil. The mature and ripe fruit are fibrous and very bitter due to the development of purgative substances, rendering them inedible. However, their internal fibrous network
makes very good sponges. The sponges are easily extracted
by removing the rind and the seeds, before and during World
War II. The sponges were commercially important as filters
in several kinds of engines because of good shock and sound
absorbing properties. They were also used as lining in steel
helmets and armored vehicles during the war. At present, they
are harnessed as insulating materials (sound, shock and temperature), and as component of potholders, table mats, door
and bath mats, insoles, sandals and gloves.
DYE PLANTS
Achuete
(Bixa orellana L.)
The red dye obtained from the seeds is widely used for coloring
fabrics and for cosmetic purposes. Commonly sold in the local
markets. It is often utilized as a food colorant in various parts
of the country, particularly in rural areas. It is also used to tint
butter and polishes for russet leather.
The seeds contain a primary coloring material known as bixin,
a carotenoid carboxylic acid and a harmless organic dye. The
ethyl ester of bixin is used as a suspension in vegetable oil
to color food a golden yellow. The dye obtained is sensitive
to light and contains sulphur dioxide, limiting its use in food
products and beverages. Although the color fades with light
exposure, it is resistant to soap, alkaline and acids.
A bark decoction is employed in febrile catarrhs and considered
as an efficient remedy for some skin diseases. It has anticancer
potential, according to Angeles (1986). The dye from the
seeds is reported to purge gently. The leaves are said to be
febrifugal.
Cordage can be made from the bark fibers. The gum extracted
from the bark is similar to gum Arabi. Achuete is also an
ornamental tree and is often planted in home gardens and
public parks.
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Binunga
[Macaranga tanarius (L.)
Muell.-Arg.]
The bark yields a brown dye. The poles are frequently used
for temporary construction and especially as parts of native
houses not in contact with the ground. In southern Sumatra
the poles serve as ladders for pepper growers. The wood is a
favorite material for wooden shoes aside from being a good
fuel wood. It also yields high quality pulp and may be used for
particleboard, cement-bonded board, wood-wool board and
plywood production.
Binunga is used in traditional medicine in many ways. The
powdered roots is an emetic for fevers. The root decoction is
administered against haemoptysis. The leaf or root decoction
is used in internal medicine. The root bark decoction is drank
to treat diarrhea dysentery and fever, to clean wounds or
applied after childbirth. The medicinal effects may be due to
the tannins obtained from the bark and leaves.
Hagonoy
[Chromolaena odorata (L.)
R.M.King & H. Robinson]
The leaves produce a yellow dye. The species is now considered
as a very noxious weed in agriculture and range management.
It is used as green manure and mulch crop and has also been
employed in traditional medicine. The leaves are reportedly
useful in controlling the weevil Cylus formacarius and the
butterfly Phtorimae operculella in sweet potato, the nematode
Heterosera marioni in black pepper, as well as the nematodes
in sugarcane and tomato.
Ipil Ipil
[Leucaena leucoephala
(Lam.) de Wit.]
A dye has been extracted from the seed, pods and bark in
Central America. In the Philippines, the brown dye obtained
from the bark us used to color fishing nets. The dried pods are
made into accents/decoration of polymer resin laminated trays
and jewelry boxes.
Ipil ipil is a multipurpose tree in Southeast Asia; fuel wood,
shade, fodder, green manure, mulch, post, food, and often
combination of these products. It is also turned into live fences,
fire breaks, shelter belts, live support for vines such as pepper,
vanilla, yam and passion fruits, and shade tree for coffee
and cacao. The leaves are fed to ruminant animals or mixed
with other green fodders. They are milled as a supplement to
poultry feeds and the pelletized form is exported. The wood is
used as fuel in households and industries such as ceramics;
converted into charcoal, and processed into furniture and
parquet flooring, chipboard, and plywood and pulp paper. The
bole serves as post and prop for other crops like banana. The
young shoots including the young leaflets and green seeds are
eaten raw, cooked or mixed with other ingredients; substituted
for soya beans, or used as additives to coffee after roasting.
The species is also tapped in traditional medicine as an
anthelmintic especially against ascaris and trichina. In
the Philippines, the tree has been used for reforestation,
afforestation, soil improvement, shade plant and nurse crop
for a wide range of tropical trees and crops.
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Kakawate
[Gliricidia sepium (Jacq.)
Kunth.ex Walp.]
The leaves contain a brown dye coumarin. Kakawate is a widely
known multipurpose tree. Before, it was mainly harnessed as
a shade tree in crop plantations. But is has been integrated
in several cropping systems as a shade tree in tea, cocoa, or
coffee plantation; as live stake to support black pepper, vanilla
and yam, and as soil stabilizer. The wood is used as firewood,
charcoal, or sports and farm implements, and locally for
furniture, construction and many other, the tree is also planted
to stabilize soil prevent erosion and to reclaim denuded lands.
Its leaves green stems and bark are used as forage for goats
and cattle. The flowers are a source of nectar for bees. It is
also employed in traditional medicine as antipuritic, antifungal
and antirheumatism.
Kamote
[Ipomoea batatas (L.) Lamk.]
The leaves and stem yield a purple to reddish dye when boiled
in water; kamote is widely cultivated for its edible tuber. The
young leaves are used as vegetable; the young shoots are
eaten as salad and also used as poultice.
Lantana
[Lantana camara (L.)]
The leaves yield beige dye. Lantana is also employed in
traditional medicine in Southeast Asia to heal cuts, ulcers and
swelling and to treat rheumatism. A leaf flower decoction is
used to treat constipation, as a febrifuge, diaphoretic and
stimulant, and to relieve catarrh and bronchitis. A roots
decoction is used to treat toothache, headache, inflammation,
gonorrhea and leucorrhoea. Lantana is widely preferred as an
ornamental plant in parks and as hedges.
Lipay
[Mucuna pruriens (L.) DC.]
The leaves are sources of brown to violet dye. The species
is also widely used in traditional medicine. The root infusion
and ointment are used to cure cholera and elephantiasis,
respectively. The root decoction acts as a diuretic, while syrup
made from the hair of the pods is an anthelmintic. The plant
extract exhibits analgesic and antipyretic effects. (Lauk et al.,
1993). Mature seeds contain large amount of globulins and
albumins, potassium, phosphorus, and calcium (Siddhuraju et
al., 1996). The stems are suitable for handicraft manufacture.
Breeding of lipay has been done such that cultivars, as the
annual hervaceous vine M. pruriens cv. Group utilis is presently
utilized as a cover crop and green manure throughout the
tropics, as well as subtropical areas. It is one of the most
widely used crops for reclaiming weed infested lands.
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Luyang dilaw
(Curcuma longa L.)
The bright yellow inner part of the rhizomes is a source of
yellow dye for coloring and flavoring rice. The dye is also used
to tint abaca fibers woven into the “tinalak” cloth of the Tibolis,
but not as commonly used as the dyes from Morinda bracteata
and Piper nigrum. To collect the rhizomes, the plant is uprooted
and the rhizomes cut oof the stems, cleaned, pounded with
mortar and boiled water. Abaca fibers are boild in the rhizome
solution for several hours until the desired hue is obtained. The
Ubo tribe of South Cotabato in Mindanao, Philippines cultivates
luyang dilaw in their surroundings.
Luyang dilaw is a widely known medicinal plant. The main
rhizomes are used as a stomachic, carminative, haematic or
styptic, hemorrhage jaundice and other liver troubles. It is also
applied to relieve itch, small wounds, insects’ bites and many
others. It has some insecticidal fungicidal and nematicidal
properties making it a potential biocide.
Makahiya
(Mimosa pudica L.)
The leaves are a source of a light green dye. The entire plant
is extensively used as anti asthmatic, while the roots decoction
is given as diuretic and also to treat dysmenorrhoea. The plant
contains tannins that can be used in leather production. The
young stems and leaves can cause poisoning. Makahiya can be
used as a green manure, although it is regarded as a noxious
weed especially in grazing lands.
Prickly chaff flower
(Achyranthes aspera L.)
The leaves are source of light green dye suitable for coloring
fabrics and other porous materials. The roots, seeds, and
whole plant are widely used for medicinal purposes. The
leaves are applied to wounds and to mature abscesses and
boils. The root decoction is drank for rheumatism, stomach
ache, menstruation pains, absence of menstruation or as
an abortifacient. The plant sap is taken for dysentery and
rheumatism. In Papua New Guinea, the leaves or roots are
applied on boils and swollen legs. In Thailand, the roots serve
as anti inflammatory and diuretic.
Tayung tayungan
(Indigofera tinctoria L.)
It is a source of the indigo blue dye through touts in the
tropics. It contains glucoside indicant, which is transformed by
enzymatic hydrolosis into indoxyl (indigo white) and glucoside
after soaking the plant in water. Indoxyl can then be oxidized to
indigo blue. Tayung tayungan is also used as cover crop and as
green manure, especially in tea, coffee and rubber plantation,
the leaves are used in traditional medicine for epilepsy and
nervous disorders and to heal sores and ulcers.
Ulasiman
(Portulaca oleracea L.)
A beige dye is extracted from the leaves. Ulasiman is employed
in various ways in traditional medicine. It is also a host to
root knot nematodes Meloidogyne arenaria M. incognita and
M.incognita var. acrita, damping off fungus Rhizoctonia solani,
curly top virus, and white fungus Albugo portulaceae. The plant
is believed to be among the earliest vegetable. The leaves and
tips are cooked as vegetable, and sometimes eaten as green
salad.
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BAMBOOS
Buddha`s belly bamboo
(Bambusa vulgaris Schrad. Ex
Wendl. Cv wamin McClure)
The culms are made for handicrafts such as candle holders
and pencil holders and also furniture. It is preferred as an
ornamental plant and much used for landscaping or cultivated
in pots.
Puser
[Cyrtochloa fenixii (Gamble)
S. Dransf.]
It is presently utilized as raw materials (although unknowing by
the furniture and handicraft industries) in a variety of products
such as decorative hats, mats, fans, baskets and “kaings and
bilaos”. It also serves as fences and crop trellises.
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COMMON NAME/
SCIENTIFIC NAME
137
ECONOMIC USES
FERNS
Kabkab
[Drynaria quercifolia (L.)
J.Smith]
Foliage leaves are used in floral arrangement. Species are widely
grown as an ornamental plant even as hanging plant. Rhizome
decoction used as an astringent and said to be anthelminthic
in concentrated form. Pounded leaves are applied to swellings
as poultice; diluted juice sprinkled over a patient head to treat
fever, also remedy for stomach aches and cough. Alkaloids are
found in leaves and rhizomes; saponins and oxalic and formic
acids are also found in leaves.
Lagolo
(Acrostichum speciosum
Wild.)
Split or whole stems are used in making Venetian blinds,
partition walling and similar items and handicrafts. Rhizome
with medicinal properties as vulnerary especially in healing
ulcers and as emollient. Powdered rhizomes topically applied
to wounds and boils in Malaya and Borneo. Fertile fronds mixed
with rhizomes are used against syphilitic ulcers.
Tilob
(Dicranopteris linearis
(Burm.) Underw.)
A favorite weaving material are handicrafts owing to its durability and strength. Fronds sometimes used as accents in
floral arrangement. Splints from rachises laces into excellent
necklaces, bags, bracelets, placemats, and belts. Stems are
also woven into partition walls for houses, fish traps, chair or
stool seats, caps, and pouches. Oldest stems make the best
pens for domestic animals. Young leaves are applied as poultice.
Leaf infusion and decoction have antifungal activities; sometime
drank to cure fever; laxative; antiasthmatic; also a cure for
thrush.
HERBS
Bamban
[Donax canniformis
(G.Forster) K. Schumann]
Stems are made into hats, laundry and waste baskets, bags,
mats, trays, flower pots, holders, tables, magazine racks,
bookshelves, musical instruments and fish traps. Also used
in stitching thatch and for tying purpose. Stems formed
into blowpipe darts in Malaysia. Pith of the stem suitable for
papermaking, and leaves for cigarette paper in New Guinea.
All plant parts with medicinal properties and used especially by
inhabitants of areas where the plant is available. Rhizomes are
said to be edible. Flesh portion of the fruit is eaten raw.
Guinea grass
(Panicum maximum Jacq.)
Inflorescence is used in floral décor. Leaf stalks are used purely
or in combination with other materials to make mats, Venetian
blinds, partition and handicrafts items. A preferred forage
species owing to its good quality and palatability to ruminants
in grazed pastures or in cut and carry systems.
Gumi gumi
(Xyris complanata R. Br)
Flowers are dried and used as floral décor. The naturally twisted
scapes (Floral stem/stalks) are woven with other materials into
mats, blinds and partition inflorescence with medicinal values.
Cultivated as an ornamental species.
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Country Report on Forest Genetic Resources
Lubigan
(Lepironia articulate (Retz.)
Domin)
Whole or split stems are made into mats, bags, basket, window
blind, and other similar items. Stems pounded with hard and
heavy objects until flat and ready for weaving. In Borneo and
South Sumatra, the mats are used in packing tobacco, rubber,
kapok, cotton, cane sugar and other products and for transporting food items such as rice, salts, and dried fish. Rhizome is
reported to be edible.
Ragiw
[Rhynchospra corymbosa
(L.) Britton]
Inflorescence are used in floral décor. Whole or split fibers from
the stems are fashioned into mats, sandals, baskets, screens,
novelties, and similar items. It is also plowed in the fields as
green manure for rice.
Vetiver
[Vetiveria zizanioides (L.)
Nash]
Leaves are woven into bags, mats, mail holders, and other
handicraft items. Leafstalks also made into hats. Leaves
sometimes used as thatching; young leaves good forage
material. Rhizomes and roots the sources of the well known
“vertiver oil” obtained by steam distillation and used in perfumes,
deodorants, soaps, and toiletries. Vetiver oil with medicinal
value as a carminative, diaphoretic, diuretic, emmenagogue,
refrigerant, stomach, tonic, antispasmodic and sudorific. Also
has an insecticidal and insect repellant property. Roots woven
into prized fans for their agreeable odor. Rhizomes and roots
moistened to five pleasant smells to a room moistened to give
a pleasant smell to a room and cooling screen. Dry powdered
roots and rhizomes inserted in between clothes as deodorize
and insect repellant. Species used in erosion control owing to
its dense downward root system up to 4 m deep that effectively
anchors strips of plant behind it.
Pandan
Pandan dagat
(Pandanus odoratissimus
L.f.)
Leaves converted into strips that are woven into small handbags
and containers to large floor mats or light interior wall panels.
Also made into strong and durable “sabotan” hats and sometimes used for thatching. Leaf fibers suitable for hand made
papermaking. Fragrant oil from the male florescence known as
“kewda oil”. Characteristic aroma of kewda oil due to 2 phenylethyl methyl ether (about 66-85% and terpinen-4-ol (9-21). Oil
a stimulants and antispasmodic. Also used to flavor tobacco and
betel and to scent clothes, bouquets, lotion, cosmetics, soaps,
hair oil and incense sticks. Roots with diuretic effects. Species
planted as live fence, coastal windbreaks and soil stabilizer.
Vayasubas
(Freycinetia formosan
Hemsl.)
Aerial or prop roots made into high quality handicrafts such as
baskets, fans, hats, coin purses and similar items. Sustainable
as strong ropes. Inflorescence sometimes used as emergency
food.
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Country Report on Forest Genetic Resources
139
SEED FRUIT LEAVES
Araucaria
(Araucaria spp.)
Leaves as components in floral décor. Timber used in all kinds
of construction and interior works like mouldings, linings, paneling, domestic flooring, furniture and cabinet work and other
special application such as matches, match boxes, broom handle, chopstick, agricultural implement and aircraft frames. Several species used as ornamental and Christmas trees. Seed of
several species edible.
Auri
(Acacia auriculiformis A.
Cunn. Ex Benth.)
Dried fruits(pods) used in floral decors. Timber suitable for
furniture and cabinet making, construction, floor and window
frames, moulding, boat building, carts, wheels, joinery, turnery,
oil crusher, tool handle and agricultural implements. Auri a reforestation and an afforestaion species. Planted as an ornamental tree along roads for its beautiful, bright yellow inflorescence.
Used for erosion control and as a shade tree in western Malesia
including the Philippines.
Balitbitan
(Cynometra ramiflora)
Dried fruits used in floral décor. Wood heavy, hard, only moderately durable but still suitable for interior construction, tool handles and woodcraft. Species an ornamental wayside tree owing
to the beautiful juvenile leaves.
Banaba
[Lagerstroemia speciosa (L.)
Pers.]
Dried fruit used for novelty items, interior décor, hanging décor, and similar items. Wood used for medium heavy construction under cover ( post, beams, scantlings, door and window
frames), bridge and wharf building, boat building, and others.
Also suitable for sliced veneer and plywood production. Species
cultivation for ornamental purposes and as a nature park tree.
Bark with medicinal properties.
Bitaog
(Calophyllum inophyllum L.)
Dried fruits used in floral decors. Oil from the seed used for
lighting purposes, soap making, and skin care product such as
creams, lotions ad cosmetic. Timber obtained in fairly quantities and suitable for construction, furniture and cabinets’ works,
cartwheel hubs, vessels, musical instruments, canoes and boats.
Fruit edible.
Dungon late
(Heritiera littoralis Aiton)
Dried fruits used together with other materials for floral décor
and similar items. Wood heavy and suitable for uses requiring
strength and durability; has high energy value and ideal for firewood and charcoal. Tannins from the bark used in toughening
fishing nets. Seeds edible; seed extract used to treat diarrhea
and dysentery. Root used as fish poison.
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Country Report on Forest Genetic Resources
Fringon
(Bauhinia spp.)
Seeds used in floral décor. Species planted as an ornamental
or road side tree for its beautiful flowers. Leave and barks
with medicinal properties, and well known for their astringent,
anthelmintic, carminative and diuretic effects. Also use against
diarrhea and cough. Flowers said to be a laxative and used
in curries and pickles. Bark a source of bast fiber. Species a
source of a lectin with an affinity to galactose and lactose,
which are widely applied in biochemical, histochemical and
immunochemical studies in medicine. Also reported to have
stimulatory effects on thyroid function without hepatotoxic
effects.
Kalumpang
(Sterculia foetida L.)
Fruits crafted into novelty items and seeds into necklaces and
beads for handicrafts. Wood used for temporary construction
and also for sidings, ceilings, and partitions. Seeds may be
slightly poisonous when fresh but edible and may also be a
source of oil for illuminants and paints. Leaves and flowers with
some medicinal properties. Trees planted for shade. Natural dye
extracted from the fruit rind. Beautiful, ribbon-like bast fibers,
suitable for handicrafts.
Lipay
(Macuna spp.)
Seeds hard and made into bead chain (charms key chains) and
other novelty items. Seeds with traditional medicinal properties.
M. pruniens widely grown as a cover crop and green manure.
Its stem likewise used in handicraft production such as basket,
bags and similar items.
Narra
(Pterocarpus indicus Willd.)
Fruits as components in floral décor. Wood used as structural
timber for light to heavy construction, joist, rafters, beams and
interior finish. Ranks among the finest for furniture, paneling,
musical instruments, high grade cabinets work, high class
interior joinery, billiard tables, decorative flooring for both
light and heavy traffic and many other purposes. A resinous
substance called “kino” or “sangre de drago” exuded by the bark
and considered as a powerful stringent. Boiled, shredded bark
used against diarrhea and dysentery, sometimes as diuretic.
Also has tanning properties and yields a reddish or yellowish
dye. Tree extensively used for ornamental purposes or for shade
especially in Peninsular Malaysia, Singapore, Indonesia, and
the Philippines. Also reforestation species to stabilize denuded
and marginal soils since the roots can fix atmospheric nitrogen.
Flowers and young leaves reported edible.
Palosanto
(Triplaris cumingiana Fisch.
& Mey)
Dried flower used in floral décors. Species planted for ornamental
purposes.
Philippines
Country Report on Forest Genetic Resources
Pili
(Canarium ovatum Engl.)
Talisai
(Terminalia catappa L.)
141
Fruit nut shield crafted into novelty items and decors and make
for excellent cooking fuel. Wood used for temporary construction
and as firewood. Kernels or nuts used for various confectionary
and bakery product. Boiled pulp edible and yield oil for cooking
and illumination. Resin suitable for similar purposes as Manila
elemi. Young shoot and leaves edible. Trees planted as wind
breaks, as ornamental and for shade along roads and highways.
Bark a source of tannin. Roasted kernels serve as laxative.
Oleoresin applied to relieve pain from arthritis and rheumatism
and also n boils, abscesses and furuncles.
Dried fruits used with other materials in floral décor. Wood,
suitable for house and boat construction furniture and cabinet
making. Bark and leaves used for tanning leather, dyeing cloth
and making ink. Seeds edible. Trees commonly planted for
shade and as ornamental along roads and in gardens. Oil from
seed used medicinally as a substitute for true almond oil. Leaves
sudorific and aookued ti rheumatic joints. Tannins from the
leaves and bark used as astringent in dysentery gastric fever,
bilious diarrhea and thrush; also as diuretic and cardiotonic and
applied externally on eruptions. A decoction of old leaves (red
leaves) used as vermifuge. Fruits purgative. Crushed flowers
mixed with water and drank to incude sterility. Sap of young
leaves mixed and cooked with the seed oil said to be specific
against leprosy.
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Country Report on Forest Genetic Resources
Voyavoy
(Phoenix loureiroi Kunth var.
loureiroi)
The hard, durable and rain resistant leaves used as fence. Leaflets
with a variety of domestic application such as the production of
mats, hats, baskets, brooms, and the famous raincapes “vakol”
and “suot” , the latter being the hooded capes worn by women.
Apical bud eaten as vegetable. Fruits sweet and commonly
eaten by children, the floury pith cooked in many ways.
Wades pitogo
(Cycas wadei Merr.)
Seeds used as hanging décor. Species as an ornamental tree
gardens and parks.
TREES
Kaitana
(Zanthoxylum limonella
(Dennst.) Alston)
Wood is a favorite material for carvings and small decorative
novelty items. Also for house, building (planking, rafters,
scantings),furniture, small articles such as jewelry box, kris
handle and sheaths, axe handle, walking sticks, inlay works and
gun stock. Fruits used as spice and yields an essential oil with
medicinal properties. Pounded bark mixed with oil externally
used for stomach ache; a bark decoction used fro chest pains.
Chewed bark applied to snake bite. Fibrous materials from the
roots used to caulk canoes.
Raintree (Acacia)
[Samanea saman (Jacq.)
Merr.]
Wood is good for wood carving, wall paneling, furniture, cabinet,
kitchen utensils and boat building. Also planted as an ornamental
tree for shade and forage. Leaf and bark decoction used as
medicine. Alkaloids found in barks, stems, leaves, and seeds.
Philippines
Prepared and published by the
Ecosystems Research and Development Bureau
College, Laguna, Philippines
February 2012
Department of Environment and Natural Resources