Key Biodiversity Area Special Series
Key Biodiversity Areas in the
Philippines: Priorities for Conservation
R.G.R.
Ambal 1, M.V. Duya 2, M.A. Cruz 3, O.G. Coroza4, S.G. Vergara 5, N. de Silva 6, N. Molinyawe7 & B. Tabaranza 8,9
13G
Sunvar Condominiums, 2135 A. Luna St. Pasay City 1300, Philippines
2Institute
of Biology, University of the Philippines, Diliman, Quezon City 1101,
Philippines
367(9A)
Dao St., Marikina Heights, Marikina City 1810, Philippines
4Conservation
International Philippines, 6 Maalalahanin St., Teachers Village, Diliman,
Quezon City 1101, Philippines
5ASEAN
Centre for Biodiversity, 3rd Floor ERDB Building, University of the Philippines
, Forestry Campus, Los Banos, Laguna 4031, Philippines
6Conservation
International, 2011 Crystal Drive, Suite 500, Arlington, VA 22202, USA
7 Protected Areas and
Wildlife Bureau-Department of Environment and Natural Resources, Diliman,
Quezon City 1101, Philippines
8 Haribon Foundation, 2/F
Santos and Sons Building 973 Aurora Boulevard, Quezon City 1109 Philippines
9 Current address: 1/9
Patricia Avenue, Hilcrest, South Australia 5086, Australia
Email:1 rgrambal@gmail.com (corresponding author), 2 lizavduya@gmail.com, 3 mrabella@gmail.com, 4 ocoroza@conservation.org, 5 sheila_vergara@yahoo.com,6 ndesilva@conservation.org, 7 normsmolinyawe@yahoo.com, 8 tabaranzablas@yahoo.com
Date of publication (online): 06 August 2012
Date of publication (print): 06 August 2012
ISSN 0974-7907 (online) | 0974-7893 (print)
Manuscript details:
Ms
# o2995
Received
08 November 2011
Final
revised received 15 January 2012
Finally
accepted 24 May 2012
Citation: Ambal, R.G.R., M.V. Duya, M.A. Cruz, O.G. Coroza, S.G. Vergara,
N. de Silva, N. Molinyawe & B. Tabaranza (2012). Key Biodiversity Areas in
the Philippines: Priorities for Conservation. Journal of Threatened Taxa 4(8): 2788–2796.
Copyright: © R.G.R. Ambal, M.V. Duya, M.A. Cruz, O.G. Coroza, S.G. Vergara,
N. de Silva, N. Molinyawe & B. Tabaranza 2012. Creative Commons Attribution
3.0 Unported License. JoTT allows unrestricted use of this article in any
medium for non-profit purposes, reproduction and distribution by providing
adequate credit to the authors and the source of publication.
Author Details: Ruth
Grace Ambal is a
wildlife biologist that has been involved the past 10 years in identifying
conservation priorities in the Philippines.
Melizar Duya is a Senior Research Associate
of the project entitled “Comprehensive Biodiversity Conservation and Monitoring
Program of the Pantabangan-Carranglan Watershed, Pantabangan, Nueva Ecija,
Luzon Island, Philippines” funded by the First Gen Hydro Power Corporation
under the Institute of Biology, College of Science, UP Diliman, Quezon City,
Philippines.
Margaux Cruz has a degree in MS Remote
Sensing from the University of the Philippines-Diliman. She has been working
part-time as a remote sensing and GIS consultant for various projects for the
past three years. She is currently affiliated with the Bureau of Fisheries and
Aquatic Resources as a remote sensing consultant.
Oliver Coroza is with Conservation
International Philippines. He has 22 years of experience in applying
cartographic modeling and GIS for natural resources management, remote sensing
applications, biodiversity conservation, land use and protected area planning,
real estate management and facilities/utilities management.
Sheila Vergara, a marine ecologist by
training, mobilized the marine KBA process with colleagues in the course of
implementing the Sulu Sulawesi Seascape Initiative. She is now the Director for
Biodiversity Information Management at the ASEAN Centre for Biodiversity.
Naamal De Silva is Director of Conservation
Priorities and Outreach in the Science + Knowledge Division of Conservation
International. She is also a
doctoral student in Curriculum and Instruction at the George Washington
University Graduate School of Education and Human Development.
Norma Molinyawe is the Chief of the
Biodiversity Management Division of the Protected Areas and Wildlife Bureau of
the Department of Environment and Natural Resources, Philippines.
Blas Tabaranza was Haribon Foundation’s
resident scientist and Chief Operating Officer before his retirement. He is a
member of Birdlife International’s Global Council 2008-2012 and president
emeritus of the Wildlife Conservation Society of the Philippines.
Author Contribution: RGA spearheaded the process of
identifying marine and terrestrial KBAs in the Philippines. MD, MC, and OC was
part of the team that identified the Philippine KBAs. NDS provided advice and
technical input. SV provided support and input to the marine KBA
identification. NM and BT provided support and input in the terrestrial KBA
identification.
Acknowledgements: The identification of
Philippine KBAs was made possible through the financial support of the Critical
Ecosystem Partnership Fund for the terrestrial KBA process, and the generous
support provided by the Walton Family Foundation through the Sulu-Sulawesi
Seascape Project, implemented by Conservation International Philippines, for
the marine KBA process. The KBA definition process would not have been
completed without the support and input of all the experts/individuals who have
been generous in sharing information, participated in the numerous
meetings/workshops and have unselfishly shared their data: J.M. Acebes, M.N.
Alava, A.C. Alcala, E. Alcala, P.M. Aliño, R.A.N. Altamirano, A. Alvaran, P.A.
Alviola, M.T.R. Aquino, D.S. Balete, F.B. Barangan, A.B. Barcelona, C.B. Batoy,
P.D. Beldia, T. Blastique, D. Bravo, J.M.A. Bringas, R.M. Brown, G.L. Bueser,
D. Cabahug, J.P.B. Cabansag, W. Campos, E. Capuli, A. Cariño, L. Casten, L.L. Co,
C.C. Custodio, J.D. De Alban, A. De Guzman, G. dela Rosa Jr., M. Deocadez, A.C.
Diesmos, M.L. Dolar, M.M. Duya, E.G. Fortes, M. Fortes, H. Froyalde, J. Gatus,
J.P. Gaudiano, J.C.T. Gonzalez, L.R. Heaney, V. Hilomen, J.C. Ibañez, N. Ingle,
A.E. Jensen, S.M. Licuanan, W. Licuanan, N.A.D. Mallari, J.D. Matillano, T.
Mildenstein, C. Nañola, S.P. Oliver, P.S. Ong, L.M. Paguntalan, M.J. Palomar,
J. Pontillas, J. Primavera, H.R. Quiaoit, M.C. Quibilan, R.R. Quidlat, F.T.
Quimpo, N. Ramoso, C. Reboton, E.L. Rico, E. Sabater, R. Sadaba, R.A. Salinas,
B.R. Samaniego, M.R. Silvosa, D.G. Tabaranza, F. Torres Jr., G.C. Trono Jr.,
R.B. Trono, B. Vallejo, M. van Weerd, C.L. Villanoy, R.B. Villanueva, A. White,
I. Widmann, P. Widmann, and A.A. Yaptinchay. Invaluable support was also
provided by the following institutions: Conservation International Philippines
(CIP), Protected Areas and Protected Areas and Wildlife Bureau of the
Department of Environment and Natural Resources (PAWB-DENR), Haribon
Foundation, Foundation for the Philippine Environment (FPE), University of the
Philippines – Center for Integrative Studies (UP-CIDS), Department of
Agriculture - Bureau of Fisheries and Aquatic Resources (DA-BFAR), and
University of the Philippines – Marine Science Institute (UP-MSI). The
authors would like to thank two anonymous reviewers for their insightful review
and valuable comments. We would also like to extend our gratitude to Dr. Thomas
Brooks for all his comments, inputs and support in the drafting and completion
of this paper.
Abstract: A process for identifying Key Biodiversity Areas (KBAs) for the
Philippines was undertaken in two phases. The 128 terrestrial and freshwater KBAs were identified in 2006 and the
123 marine KBAs were identified in 2009. A total of 228 KBAs resulted from the
integration of the terrestrial, freshwater and marine KBAs. These KBAs
represent the known habitat of 855 globally important species of plants,
corals, molluscs, elasmobranchs, fishes, amphibians, reptiles, birds and
mammals in the country. Inclusion
of these KBAs in the country’s protected area system will be a significant step
towards ensuring the conservation of the full scope of the country’s natural
heritage.
Keywords: Conservation priorities, irreplaceability, key biodiversity areas,
Philippines, vulnerability.
The Key
Biodiversity Area series documents the application of the concept and showcases
the results from various parts of the world. The series is edited
under the auspices of the IUCN World Commission on Protected Areas/Species
Survival Commission Joint Task Force on ‘Biodiversity and Protected Areas’,
with the editors supported by BirdLife International, Conservation
International, IUCN, National Fish & Wildlife Foundation, NatureServe,
Parks Canada, and Plantlife International.
For images, tables -- click here
INTRODUCTION
The
Philippines is the world’s second largest archipelago with more than 7,100
distinct islands covering an estimated 30 million hectares. It lies in the western Pacific Ocean and
is geographically part of Southeast Asia, a region that occupies a mere three
percent of the earth’s total surface, yet is home to 20 percent of all known
species of plants and animals.
The
complex geological history of the Philippines has resulted in an extraordinary
wealth of biodiversity, one of the highest concentrations of terrestrial
vertebrate life on earth (Brown & Diesmos 2009). The country’s marine ecosystems are
equally diverse and unique. The archipelago is surrounded by shallow, warm seas
that support the richest coral reef community on the planet, labeled the
“center of marine diversity” by Carpenter & Springer (2005). With more than 20,000 endemic species,
the Philippines is recognized as a megadiverse country, one of 17 nations that,
together, hold two-thirds of earth’s biological diversity (Mittermeier et al.
1999).
However,
continued exploitation and destruction of natural resources has led to the
depletion of the country’s unique and valuable biodiversity. Despite the greater understanding of
Philippine biodiversity gained in the last decade, the onslaught of
biodiversity loss has continued, albeit compensated by some conservation
successes (Posa et al. 2008). Without timely intervention, further degradation of resources will
continue and may eventually result in species extinction.
Defining
conservation priorities is essential to minimizing biodiversity loss (Brooks et
al. 2006) as it ensures that conservation action focuses on the species at the
greatest risk of extinction and on the sites that are most important for their
protection. The key biodiversity
area (KBAs) approach was initiated in the Philippines to help the government
and stakeholders prioritize conservation action and devise geographically
specific strategies that protect the individual species and safeguard
representative habitats (Edgar et al. 2008).
This
paper integrates and summarizes the results of the KBA identification process
undertaken for the country.
METHODS
The
KBA definition process in the Philippines was initiated by Conservation
International Philippines (CIP), Haribon Foundation and the Protected Areas and
Wildlife Bureau (PAWB) of the Department of Environment and Natural Resources
(DENR), with support from the Critical Ecosystem Partnership Fund (CEPF), a
global program that provide grants for non-governmental and private sector
organizations to help protect Earth’s most biologically rich yet threatened
areas. KBAs have become the
standard conservation target definition for CEPF Investments, not only in the
Philippines but in other countries as well.
KBA
identification in the Philippines involved two separate initiatives to identify
terrestrial, freshwater and marine KBAs. The terrestrial and freshwater KBA identification process was completed
in 2006 with KBAs identified based on the presence of globally threatened
and/or restricted-range species of freshwater fish, amphibians, reptiles,
birds, mammals and congregatory species of birds. This built on the process led by the
Haribon Foundation to identify Important Bird Areas (IBA) (Mallari et al. 2001)
and was also informed by specialist-driven identification of conservation
priority areas (CPA) through the Philippine Biodiversity Conservation Priority
Process (Ong et al. 2002). Terrestrial plants were not included in the analysis, because
comprehensive data on their distributions and conservation status has not yet
been compiled. In 2008, the marine
KBA identification process was initiated and was completed in 2009. Marine KBAs were identified for seaweeds
and seagrasses, corals, molluscs, elasmobranchs, reef fishes, marine turtles,
sea- and small island-specialist birds, and marine mammals. The results of the two KBA definition
processes were then combined and further refined to derive an integrated set of
KBAs.
Identification
of KBAs for both terrestrial and marine areas followed the process outlined in
Langhammer et al. (2007). The
criteria of vulnerability and irreplaceability were both applied. Vulnerability
was triggered by the confirmed presence of one or more globally threatened
species, classified as Critically Endangered (CR), Endangered (EN), and
Vulnerable (VU) based on the IUCN Red List of Threatened Species (http://www.iucnredlist.org). The suggested threshold of 10 pairs or
30 individuals for species classified as VU (Langhammer et al. 2007) was not
applied due to the lack of population data for majority of the trigger species.
The 2004 IUCN Red List was used in the terrestrial KBA definition process,
while the 2008 IUCN Red List was used in the marine KBA definition
process. Irreplaceability was
triggered by the confirmed presence of geographically concentrated species. Only two of the four sub-criteria of
irreplaceability were used in both processes: the presence of species with
restricted ranges and globally significant congregations. The restricted-range sub-criterion was
used to identify sites for species of known conservation concern from taxonomic
groups which had not at the time been assessed for the IUCN Red List of
Threatened Species. The
congregations sub-criterion was only utilized for birds, based on Important
Bird Area data (Mallari et al. 2001).
An
initial analysis of trigger species, species that satisfies the criteria of
vulnerability and/or irreplaceability, was done through a review of the
pertinent literature and initial talks with experts on both processes. Species occurrence and distribution data
for the trigger species were obtained from survey/assessment reports,
scientific reports, published literature, museum records and expert
accounts. Point locality data for
each trigger species were then plotted on a map and overlaid with data for
other trigger species belonging to the same taxonomic group. KBA boundaries were delineated primarily
based on whatever information was available on the habitat requirements and
affinities of the trigger species. Initial KBA maps for each taxonomic group were then produced and were
reviewed and validated through a series of meetings with experts. The final terrestrial, freshwater and
marine KBA maps are the result of the overlays of the KBA maps of the different
taxonomic groups.
For
the terrestrial KBA boundaries, in most cases the IBA and CPA boundaries were
followed (Conservation International et al. 2006). However, refinements and adjustments
were made in areas where the IBA or CPA boundaries did not cover the habitat of
other trigger species or to exclude areas that had been cleared or converted
for human use since they were originally identified (e.g. farms, settlements,
and major transportation corridors) or for management considerations (e.g.
municipal boundaries or adjacent protected areas). For trigger species found within
existing protected areas, the KBA followed the protected area boundary.
Marine
KBA boundaries mostly followed natural features such as reef edges or depth
contours, to include the largest extent possible of remaining habitat of the
trigger species (Conservation International et al. 2009). In some cases, the boundaries correspond
to existing management units, e.g. marine protected areas, designated
sanctuaries, or follow municipal boundaries. The boundaries were also refined to
exclude, as much as possible, areas that have been converted to human use, such
as fish farms, port areas and major transportation corridors. Land areas were excluded from marine KBA
boundaries. Exceptions include the
nesting sites of sea turtles, wherein the beach and some inland mangrove areas were included.
Integration
of the terrestrial KBAs and marine KBAs involved the overlay of the two map
layers in ArcView. Overlapping
terrestrial and marine KBAs were identified and a larger boundary, encompassing
all the overlapping individual KBAs, was established to merge them into a
single KBA. In some cases, two or
more adjacent KBAs were also merged as a single KBA to support the habitat
requirements of some of the trigger species. Socio-political parameters were also
considered in the boundary delineation where information was available or
applicable. Google Earth was used
as an additional tool for refining the boundaries of the KBAs. Using the high resolution Quickbird
imagery available for some areas in Google Earth, areas that have been cleared
or converted to other land use were excluded, including ports and high density
human settlements along the coast while, in some cases, existing KBA boundaries
were expanded to include adjacent areas of suitable habitat.
RESULTS
A
total of 228 key biodiversity areas were identified based on the integrated
results of the 128 terrestrial KBAs identified in 2006 and the 123 marine KBAs
identified in 2009. The terrestrial
KBAs cover 20% of the country’s land area, which includes the majority of the
remaining terrestrial natural habitats, while the marine KBAs covered only
1.93% of the country’s marine area or Exclusive Economic Zone (EEZ). Some 44% of the sites identified are
terrestrial KBAs, 34% are marine and 22% include both marine and terrestrial
areas (Table 1). Fifty (22%) of the
KBAs are existing protected areas, 41 (18%) are partially protected, and the
remaining 60% are unprotected (Table 1, Image 1).
The
Philippine KBAs represent the known habitat of 855 species, 396 globally
threatened and 398 restricted-range species of plants, corals, molluscs,
elasmobranchs, fishes, amphibians, reptiles, birds and mammals and 61 species
of congregatory birds (Table 2). The majority of the globally threatened species would also have triggered
the irreplaceability criteria had these been comprehensively applied, but for
threatened species, we only identified sites under the vulnerability criterion,
not the irreplaceability criterion. Corals have the highest number of species which trigger site
identification under the vulnerability criterion, with 176 species triggering a
total of 49 KBAs. The
irreplaceability trigger species list is dominated by birds (partly because the
congregations sub-criterion was applied for birds but not other taxonomic
groups), with 228 species triggering a total of 93 KBAs (Table 2 & 3).
A
total of 243 species are found at only a single KBA while 40 KBAs were
identified based on the presence of a single trigger species (Table 4). Two species of globally threatened birds
triggered the greatest number of KBAs; Spizaetus philippensis (VU)
occurs at 48 KBAs while Cacatua haematuropygia (CR) triggers 44
KBAs. The KBAs with the greatest
number of trigger species are Balayan Bay, with 172 species, followed by
Tingloy with 167. Both sites are
marine KBAs. Large numbers of
globally threatened corals, 169 and 166 species respectively, have been
documented occurring within these two sites. A third of the total number of KBAs were
triggered by 20 or more species. Only two percent of the trigger species are found in 20 or more KBAs
(Table 4).
DISCUSSION
The
identification of Philippine KBAs builds on the previous conservation
priority-setting initiatives in the country. Conservation Priority Areas (CPA) were identified
and delineated in 2000 based on the combined inputs and consensus of experts
making best use of available data. The resulting priority areas encompassed large areas that did not
consider management potential, and lacked quantitative data to show presence of
target species needing conservation action. In 2001, Haribon Foundation and BirdLife
International identified 117 Important Bird Areas (IBAs). The IBAs were identified by spatially
referencing all relevant existing information on globally threatened,
restricted range, and congregatory bird species. The KBA process built from these two
priority-setting initiatives by refining the previous results by using the most
recent, spatially referenced, and validated information on a wide range of taxa
requiring conservation intervention.
KBA
identification has facilitated the identification of gaps in the national
protected area system, with more than half of the KBAs unprotected. The KBAs which do not overlap with
protected areas can be considered as “representation gaps” whereas KBAs which
only have partial or incomplete overlap with protected areas can be considered
as “ecological gaps”. These
analyses therefore, provide a guide for investments by government and civil
society towards a truly representative protected area system that encompasses
the full scope of the country’s natural heritage.
The
KBAs are currently being used by the Philippine government as means of
identifying where biodiversity conservation projects are to be
implemented. A milestone in the
conservation effort in the country is the signing by the President of Executive
Order 578 in 2006 declaring all KBAs to be “critical habitats” and directed the
DENR to promulgate guidelines for their management and protection. The
government has also taken the KBA initiative one step further by prioritizing
efforts in developing an agreed set of criteria that can be used to assess and
prioritize conservation action and investments in KBAs. Conservation investments have declined
in recent years, and knowing that the safeguarding of some KBAs is more urgent
than others, has necessitated the need to prioritize conservation action
amongst KBAs identified till date. The actual prioritization of KBAs and planning the appropriate
conservation action on the ground requires more detailed socio-political and
economic data that this analysis has not been able to provide. Further studies should be initiated to
gather information that would help assess the levels of threat within each KBA
and the opportunities available to be able to focus investments in areas where
conservation impacts would be greater.
The
network of KBAs identified by this analysis does not mean that all priority
sites in the country have been identified. Many globally important and restricted-range species have not been
included in this analysis. Most
plants have not yet been considered and it is known that the country is home to
some of the most threatened habitats and species of plants in the world, with
at least 694 taxa of vascular plants and mosses included in the threatened
plants list of Fernando et al. (2008).
Furthermore,
a number of additional candidate KBAs have been identified, although they are
not included in this analysis. A
total of 51 terrestrial and freshwater sites were identified as candidate
KBAs. These are sites that have
been identified as conservation priority areas by previous priority-setting
initiatives that need further validation as to the presence of trigger species. The 126 marine candidate KBAs were identified
for mangroves, seagrass and seaweeds, corals, echinoderms, molluscs,
elasmobranchs, sea snakes, marine turtles, sea birds, and marine mammals. These
sites are suspected to be important for conservation but at present do not have
adequate data. These sites are
currently targeted as priorities for research and it is hoped that soon new
data will become available to validate and confirm the presence of trigger
species in these areas.
KBA
identification is an iterative process. As new data become available KBA boundaries are likely to be modified
and new KBAs identified. Some species may also undergo changes in their
conservation status that can also affect the priority status of the KBAs they
trigger. For example, the subset of
KBAs identified as AZE sites in the country has undergone major changes, with
six sites removed from the 2010 AZE list. These include Mt. Mantalingahan, Mt. Malindang, Mt. Isarog, Northern
Sierra Madre Natural Park, Siburan, and Ilin Is. This change is mainly due to new information
on distribution or conservation status of the trigger species that has resulted
on the species no longer satisfying the AZE criteria (although all six remain
as KBAs). Nevertheless, the KBA list represents the best current assessment of
those sites where safeguard mechanisms are necessary in order to allow the
Philippines’ unique but threatened biodiversity to persist into the future.
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