Marine
Protected Area (MPA) is defined as any area of inter-tidal
or sub-tidal terrain, together with its overlying waters
and associated flora, fauna, historical and cultural features,
which has been reserved by legislation to protect part
or all of the enclosed environment (IUCN 1988). This review
will focus on sub-tidal areas and inter-tidal areas essential
for marine species, such as coral reefs and turtle nesting
beaches.
The Review follows the
biogeographic division system adopted by the IUCN/CNPPA
MPA Programme, which has classified the globe into 18
regions, each of which is further subdivided biogeographically
(Kelleher et al. 1995). The IUCN East Asian Seas Region
encompasses all of the nine Pacific Ocean countries/territories
except Papua New Guinea, which falls under the IUCN South
Pacific Ocean Region. The East Asian Seas Region is divided
into 8 first-order and 22 second-order subdivisions. For
this overview, the region of the Western Coast of Myanmar
is included even though it is considered under the Central
Indian Ocean region (see Map
7).
In order to gather local
knowledge and perception on the conservation values of
and human-induced threats to the MPAs (declared and undeclared)
of the region, a questionnaire has been designed for national
experts to rank the different values of and threats to
individual MPAs in their own countries. These data are
presented in the form of tables listing the main habitats,
species of significance and threats of high/medium/ low
intensities to each MPA. Data on threats are added and
averaged over the number of sites analysed, thus giving
the overall relative frequency of different types of threats
in that particular country. To make comparisons more meaningful,
only coral reef sites with good knowledge are analysed
and the results presented in the form of histograms (e.g.
Figure i.1).
The total impact (I) of a particular threat (T) of different
intensities is obtained
by the following:
Impact
= 3xH + 2xM + L
Where:
H = averaged frequency of high intensity T
M = averaged frequency of medium intensity T
L = averaged frequency of low intensity T
As
different types of threats cause different types and levels
of impacts under different environmental conditions, the
total impact derived from this formula is a hypothetical
figure designed to emphasize the differences in the intensities
of threats and to facilitate comparisons between threats.
Instead of seeking a definitive measurement, the analysis
seeks to understand and display the perceptions of the
informants. These include the problems of their marine
areas, which reflect not only the actual situation of
the sites, but also, to some extent, the persons’
cultural, academic and political background. To reduce
the effects of the latter, an equal number of representatives
both from the government and NGO/scientific communities
have been asked to complete the questionnaire wherever
possible.
Histograms
derived from Reefs at Risks exercises undertaken for the
Southeast Asian region provide a context of how these
threats on MPAs relate to the overall national risk level
perceived and modelled through the World Resources Institute
(WRI) and its collaborators (Burke et al. 2001).
For
comparisons among countries, the 13 types of threats are
grouped into major
categories related to the following and presented in pie
charts:
a) Fisheries (overexploitation and destructive methods;
dynamite & poison fishing, coral mining)
b) Ornamental trade (including aquarium fish and coral
and shell souvenirs)
c) Hunting of endangered species (mainly turtles, also
dugongs, whales and sharks)
d) Tourism (damage of habitats by tourists, anchors, pollution,
and constructions)
e) Environmental degradation (siltation, pollution, coastal
development, mining, dredging, etc.)