The
MPAs (declared and proposed) have been classified as global/regional
(A), national (B) and local (C) priorities based on the
following: i) the biodiversity and ecological values of
MPAs; ii) consideration of the threats (existing and potential)
imposed upon them, and iii) feasibility of management
(i.e. including the social environments that will determine
the likelihood of success). An absolute distinction between
global and regional priorities was not made because comparison
of sites on the global scale is beyond the scope of this
Review. The majority of the A sites refers to regional
priority areas except for those that have been internationally
recognised (e.g. Mu Ko Similan, Surin and Tubbataha as
World Heritage Sites; Khao Sam Roi Yot and Olango as RAMSAR
Sites). The prioritisation process provides guidelines
for resource allocation especially at the international
levels. International or bilateral programmes should support
MPAs of global/regional priority that contain high biodiversity
values with a good chance of being successfully conserved,
and hence contribute effectively to global biodiversity
conservation. Greater national efforts, with or without
foreign assistance, should be exerted on sites rated as
nationally important to strengthen their management. Rather
than being obsolete or unimportant, the remaining MPAs
of local priority are essential in forming a healthy network
of sites needed for marine conservation nationally and
regionally, as well as for sustaining fisheries resources
that local villagers depend upon (Aliño et al.
2000).
Several
of the reviewed countries have already begun their own
process of MPA prioritisation. The Biodiversity Action
Plans for Indonesia (Haeruman 1993, as cited by Cheung
1995) and Vietnam (BAP Planning Team, 1995 draft), for
example, present the national views on the priority sites
and actions needed for biodiversity conservation. The
Philippines has recently reviewed its priority areas (including
MPAs) for protection under the National Priority Setting
for Biodiversity Conservation (DENR 2000). Care is needed
during the MPA rating process of the Review so that local
and national opinions would be well-represented while
regional expertise would be brought in to verify sites
that have been rated globally or regionally important.
Other regional programmes with shared objectives such
as the IUCN/CNPPA Global MPA Programme have been consulted
during the rating process.
Some 27 “A” and 41 “B”
priority MPAs or marine areas have been identified in
the region (Table
i.4). At least one regional priority site has been
chosen from each country to encourage national conservation
efforts and regional exchange and cooperation. Indonesia,
being at the centre of marine biodiversity and having
the widest spread geographically, has the most “A”
sites. The Philippines also has a large number of priority
sites. Note that some of the MPAs are very small and may
be grouped to form a single priority site of greater size
and sustainability (see also Figure
i.2).

Table
i.5 presents the list of Existing (E) and Proposed
(P) MPAs of regional (A) and national (B) conservation
priorities. In addition to their high biodiversity, complexity
of ecosystems, habitat extensiveness as well as intactness
(e.g. islands of the Spratly and Tubbataha Reef), some
sites are rated highly due to their significance for endangered
migratory species (e.g. turtles and dugongs). Some are
situated close to national borders and hence require trans-frontier
cooperation in management (e.g. Pulau Semama and Sangalaki
in Indonesia, the Turtle Islands in Eastern Malaysia and
SW Philippines and the disputed islands in the Spratlys).
The list of priority sites is not definitive or complete
as there are still many unexplored areas and sites with
insufficient data for assessment. For example, Teluk Raja
Ampat and Kepuluan Karimata are believed to be high priority
areas but very little is known about them. Such sites
require urgent field surveys in order to re-assess their
importance. Similarly, many of the marine areas in Myanmar
fall under this category. It is just as important to note
these “unknown” areas as to identify well-accepted
priority sites. This prioritisation process serves to
provide a broad overview of the conservation priorities
of the region, pinpoint gaps in information and forgotten
areas, and emphasize priority actions needed. Protected
area establishment thus requires institutional, policy
and scientific support both within and beyond the site
boundary.
In
addition to the priority sites of the East Asian Seas
region, the Spratly Archipelago is one of the richest
in terms of marine biodiversity, extensiveness and fisheries
resources, and hence a site of very high regional priority
if political obstacles could be overcome. Currently, six
countries lay claim on the archipelago: China, Philippines,
Taiwan, Vietnam, Malaysia and Brunei. Frequent disputes
arise among China, Philippines and Malaysia. An international
marine park has been proposed at Spratly as a means to
sustain fisheries and prevent environmental disasters
due to oil exploration in the area (McManus 1994). A study
on pelagic larval movements suggested that the area, which
is comparable to the size of the Great Barrier Reef Marine
Park, could play an important role in replenishing fisheries
stocks in nearby countries of the South China Sea. If
political hurdles can be overcome to materialize the proposal,
marine conservation in the region would benefit to a large
extent.

