62
July 2008
Box 2: CTI Goals and Objectives.
Over-arching Commitments to Action
Goal #1: Priority Seascapes Designated and Effectively Managed
Target #1: “Priority Seascapes” designated, with investment plans
completed and sequenced
Target #2: Marine and coastal resources within all “Priority Seascapes”
are being sustainably managed
Goal #2: Ecosystem Approach to Management of Fisheries (EAFM) and Other
Marine Resources Fully Applied
Target #1: Strong legislative, policy and regulatory frameworks
in place for achieving an ecosystem approach to
management of fisheries and other marine resources
Target #2: Improved income, livelihoods and food security of 50
million people living in coastal communities across the
region through a new Sustainable Coastal Fisheries and
Poverty Reduction Initiative (“COASTFISH”)
Target #3: Sustainable management of shared tuna stocks achieved
for all species of tuna exploited in the region, with special
attention to spawning areas and juvenile growth stages
Target #4: A more effective management and more sustainable trade
in live-reef fish and reef-based ornamentals achieved
Goal #3: Marine Protected Areas (MPAs) Established and Effectively
Managed
Target #1: Region-wide Coral Triangle MPA System (CTMPAS) in place
and fully functional
Goal #4: Climate Change Adaptation Measures Achieved
Target #1:
Region-wide Early Action Climate Change Adaption
Plan for the near-shore marine and coastal environment
developed and implemented
Target #2: Networked National Centers of Excellence on Climate
Change Adaptation for marine and coastal environments
are established and in full operation
Goal #5: Threatened Species Status Improving
Target #1: Improved status of sharks, sea turtles, marine mammals
and other identified threatened species
Source: CTI-CFF. 2008.
instead of coral reef fi shes. Political support
for the work in the corridors will be built
and on-the-ground marine conservation
experiences in the corridors will inform
national and regional policies and
government budget allocations, as well as
produce a model for ocean governance
that other countries in the Coral Triangle
and beyond can follow.
Increased attention will be focused
on measuring Seascape success by
establishing milestones, results, and
deliverables for important components of
the work at the species, site, and Seascape
level. Financial sustainability, political
viability, institutional capacity, economic
viability, and information base and fl ow will
be addressed.
Beyond this next phase, implementation
of the Ecoregion Conservation Plan
will be characterized by an evolution in
intergenerational governance.
Thinking Synergy and
Convergence
Governments and stakeholders look
forward to a mature Sulu-Sulawesi
Seascape which has good governance at all
levels and is ecologically, socio-politically,
economically, and fi nancially sustainable.
The success of the Sulu-Sulawesi Seascape
and its long-term sustainability will depend
in part on the degree and extent to which
governments in the region commit
human and allocate fi nancial resources to
achieve marine conservation outcomes.
In this aspect, national governments
need to draw on the strengths of local
governments while developing new forms
of partnerships.
To implement government commitments
on the ground , an enabling framework of
laws, ordinances, regulations and policies
that facilitate marine conservation have
to be in place at the local levels. Coupled
with this are personnel, infrastructure
and equipment, to make the governance
structures work eff ectively and effi
ciently.
63
Tropical Coasts
Innovative ways of engaging the private sector
to support marine and coastal conservation
need to be explored while eff orts towards
the recovery of threatened species vigorously
pursued.
Improving governmental and
nongovernmental institutional capacities
is a continuous process, linked to marine
management interventions. To achieve
convergence between conservation and
economic development, a complex set
of interventions need to be crafted while
remaining cognizant of emerging economic
opportunities.
Reducing the threats to marine biodiversity
is everyone’s concern. Public support can be
achieved through a purposive communication
and capacity-building programme for
multistakeholders.
Whatever interventions and initiatives would
be taken by actors in coastal and marine
conservation, the next phase of the Sulu-
Sulawesi Seascape initiative entails that these
be based on the achievements and lessons
learned during the last three years.
Box 3: Goals and Plans for the Sulu-Sulawesi Seascape Project
(2008-2011).
The workplan for 2008-2011 focuses on consolidating MPA networks
with No Take Zones in three corridors and on ensuring compliance
through strengthened enforcement and targeted outreach eff orts. A
minimal investment will also be made at the Seascape-wide level to
build political and fi nancial support for the work in the corridors and
to strengthen the Seascape as a model for marine management in
the Coral Triangle.
In the Verde Island Passage Corridor – to refi ne and implement a Verde
Island Passage Framework Plan together with 21 municipalities and
three provinces. The Framework Plan will allow for the creation of
an MPA network of at least 10,000 ha with at least 1,000 ha of No
Take Zones and one contiguous No Take Zone covering 1,000 ha. For
the MPA network to be eff ective, CI and partners will build capacity
of MPA managers and implement a comprehensive enforcement
strategy. Also, CI will lead an outreach campaign to build support for
the MPA network and the enforcement eff orts.
In the Cagayan Ridge Corridor – to consolidate an MPA network,
including 97,000 ha of No Take Zones, that protects at least
20 percent of critical habitats (coral reefs, seagrass beds and
mangroves). CI and partners will train law enforcers, prosecutors
and judges to make sure enforcement is eff ective from detection,
to arrest, prosecution, and conviction. CI and partners will generate
public support for existing MPAs and No Take Zones and strengthen
enforcement through a targeted communication strategy
and campaign including broad communication of successful
prosecutions and convictions for environmental and fi sheries crimes.
In the Sea Turtle Corridor – to consolidate an MPA network, including
at least 48,000 ha of No Take Zones, that protects sea turtles and
their habitats. CI and partners will promote the development and
implementation of management plans with clear MPA management
objectives. Outside of MPAs, CI and partners will promote both
Turtle Excluder Devices to reduce by-catch of threatened sea turtles
in shrimp trawls and better joint enforcement to reduce the illegal
sea turtle egg trade.
Seascape-wide – to generate political and public support for marine
conservation in the corridors and to secure the Seascape as a model
for ocean governance in the Coral Triangle, CI and partners will work
with government offi
cials and donor agencies to secure additional
human and fi nancial resources for investments in the corridors
and for priority activities in the Seascape, including strengthened
enforcement from the Balabac Strait to Sabah, an area currently
functioning as an entry point for poachers to gain access to MPAs in
the Sulu and Sulawesi Seas.
Source: CI, 2008.
References
Conservation International (CI). 2008.
Sulu-Sulawesi Seascape. A New
Future for Marine Conservation in
the Coral Triangle, Conservation
International, 15 May 2008.
CI-Philippines. 2007. The Sulu-Sulawesi
Seascape Congress Report: June 20-
22, 2007. CI-Philippines, Quezon City,
Philippines.
Coral Triangle Initiative on Coral
Reefs, Fisheries and Food Security
(CTI-CFF). 2008. Regional Plan of
Action, Honiara Draft. Adopted
10 September 2008 at the Second
Meeting of the CTI Coordination
Committee in Honiara, Solomon
Islands.
Global Environment Facility. 2008. The
Coral Triangle Initiative: Program
Framework Document. www.
gefweb.org/uploadedFiles/Projects/
Work_Programs/April_2008_Work_
Program/PFD%20Document%20
3647.pdf
Marine Protected Areas
in the Sulu-Sulawesi
Marine Ecoregion
R.A. Abesamis and P.M. Aliño
Marine and Environment Resources
Foundation, Inc. and the Marine Science
Institute, University of the Philippines for
the World Wide Fund for Nature - Sulu-
Sulawesi Marine Ecoregion Program
There were at least 352 marine
protected areas (MPAs) established
within the SSME in 2006. Of these,
343 are in the Philippines, 5 are in
Indonesia, 3 are in Malaysia and 1 is
jointly managed by the Philippines and
Malaysia. Twelve Priority Subregions
(PSRs) were designated by grouping
together highly-ranked priority
conservation areas identifi ed for the
Sulu-Sulawesi Marine Ecoregion (SSME)
(Stakeholders of the SSME, et al., 2004)
and for the Philippines (Ong, et al.,
2002). Two hundred seventy-four (274)
of the 352 MPAs are located within the
PSRs; of these, information on MPA size
was available for 204 MPAs. Based upon
MPAs for which size information was
available, only 0.94 percent of the total
area within the 12 PSRs (447,548.6 km
2
)
are within MPAs (4,198.2 km
2
). Table
1 presents the levels of management
eff ectiveness for some MPAs as
estimated by some key informants (as
of 2006).
Table 1. Levels of management effectiveness for some MPAs
(estimate, as of 2006).
Management
is effective
Management is
well-implemented
Low or
unknown
Total
Philippines
35
23
285
343
Indonesia
0
3
2
5
Malaysia
1
2
0
3
Turtle Islands
jointly managed
by Philippines
and Malaysia
Malaysian
Turtle Islands
0
Philippine
Turtle
Islands
1
352
Cumulative area protected by MPAs versus size of PSRs.*
PSRs
Approximate
PSR Size (ha)
MPAs with available
data on size
Cumulative MPA
Size (ha)
Area of PSR protected
(percentage)
1
1,137,700
6
16,813
1.48
2
2,012,803
2
575
0.03
3
2,327,732
1
48
0.002
4
5,632,500
1
33,200
0.59
5
1,819,200
46
34,840
1.92
6
3,989,057
127
22,834
0.57
7
11,072,851
11
11,299
0.10
8
493,017
(1)
no data
no data
9 A and B
4,651,800
4
211,552
4.65
10
3,283,100
4
1,319
0.04
11
8,335,100
2
89,080
1.07
Total
44,754,860
205*
419,819
0.94
*Total of 205 MPAs includes Balabac Island TZMR (Philippines) in PSR 8 for which no data on size is available.
Source: UPMSI MPA Database
Supplementary data from key informants (2006): R. Apostol, D. Baker, A. Bautista, R. Cortez, R. dela Calzada, M.
Dygico, J. Ingles, D. Largo, C. Nañola Jr., J. Palma, J. Pontillas, A. Siahainenia, A. Songco and A. White.
References
Abesamis, R.A. and P.M. Aliño. 2006. Marine Protected
Areas in the Sulu-Sulawesi Marine Ecoregion: A
Review of their Status, and Priorities and Strategies
for Their Networking. Unpublished Technical Report
prepared by the Marine and Environment Resources
Foundation, Inc. and the Marine Science Institute,
University of the Philippines for the World Wide Fund
for Nature - Sulu-Sulawesi Marine Ecoregion Program.
Ong, P.S., L.E. Afuang, and R.G. Rosell-Ambal (eds.). 2002.
Philippine Biodiversity Conservation Priorities: A
second iteration of the National Biodiversity Strategy
and Action Plan. Department of Environment and
Natural Resources- Protected Areas and Wildlife
Bureau, Conservation International Philippines,
Biodiversity Conservation Program- University of
the Philippines Center for Integrative Studies, and
Foundation for the Philippine Environment, Quezon
City, Philippines.
Stakeholders of the SSME, Technical Working Groups of
Indonesia, Malaysia and the Philippines, WWF-SSME
Conservation Program. 2004. Conservation Plan for
the Sulu-Sulawesi Marine Ecoregion. Dumaup, J.N.B.,
R.M. Cola, R.B. Trono, J.A. Ingles, E.F.B. Miclat and
N.P. Ibuna (eds.). World Wide Fund for Nature-Sulu-
Sulawesi Marine Ecoregion Program, Quezon City,
Philippines. 168 pp.
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