Sarangani Bay
Connie Portugal College of
Fisheries, MSU Fatima, General Santos City
GEOGRAPHIC LOCATION
Sarangani Bay is
located at coordinates 6 degrees 07’ N latitude and 125 degrees 06’ E longitude. It is
bounded by some of the coastal towns of Sarangani Province, namely: Maasim
on the west, Alabel on the north, and, Malapatan and Glan on the east.
General Santos City which is a chartered city of South Cotabato Province
also borders the Bay on the north. The Bay is under the legal jurisdiction
of both Sarangani Province and General Santos City.
PHYSICAL FEATURES
Sarangani Bay encloses
an area of 449.22 sq.km from Tampuan Pt. in Maasim to Sumbang Pt. in Glan
and opens into the Mindanao and Celebes Sea. Portions of the
municipalities of Glan, Maitum, and Kiamba not enclosed within the bay but
part of the Celebes Sea are referred to as "adjoining waters" of the bay.
The coastline length of the bay from Glan extending to Maasim is about 79
km with an average depth of 350 m. The waters in Sarangani Bay are
strongly oceanic in salinity. Tide-generated currents are generally weak,
except near the mouth of the bay. The reefs around the bay are narrow
and support only small patches of seagrasses. Mangrove areas along the bay
have been converted to fish and prawn ponds and utilized for firewood,
especially along the coastal communities of General Santos City, Alabel
and Malapatan.
REEF STRUCTURES AND CORALS
In the study conducted by Dames and
Moore (for Louis Berger International Inc. (LBII)), a total of 42 coral
genera were identified from the various survey sites established in the
different municipalities of Sarangani Province and General Santos City.
Dominant genera include Acropora, Porites, Diploastrea, Goniopora,
Montipora and Favites.
The condition of coral reefs surveyed
varies, from exceptionally good to heavily degraded. Maasim, Glan, Alabel
and Malapatan have sites with live hard coral cover exceeding 50%. In
terms of dead coral cover, ten sites exceeded 10% and seven of these are
in Glan. Ten sites showed high rubble cover; five in Glan, four in Maasim
and one in General Santos City (Table 1). The reefs on the northern part
of the bay were exposed to sedimentation causing the loss of diversity and
degradation of the reefs. Only soft coral patches are found sparsely
distributed in the area.
NOTEWORTHY FAUNA AND FLORA
A total of 230 coral reef fish
species belonging to 33 families have been recorded from the different
sites. The most numerous fishes in order of the number of species are:
damselfishes (Pomacentridae), wrasses (Labridae), groupers (Serranidae),
surgeonfishes (Acanthuridae) and butterflyfishes (Chaetodontidae). The
target fishes in decreasing order of standing stock are: surgeonfishes,
fusiliers, parrotfishes, goatfishes, snappers, emperor breams and jacks.
Most fishes were small (<15 cm), with only few commercially important
species. On the whole, large predators were very few in the site,
implicating the exploited condition of these sites and an inability to
support large fish biomass.
The steepness of the subtidal area in
most of the coastline prevents the establishment of any seagrass meadows.
The dominant species in Maasim is Enhalus while Halophila
and Thalassia are dominant in other areas.
Squids are caught in large volumes in
the bay. Rare endangered marine mammals (e.g., dugongs and whales) have
been sighted in Sarangani Bay.
SCIENTIFIC IMPORTANCE AND RESEARCH
In depth study of the coral reefs and
related resources has yet to be conducted. Assessment of coral reef was
first conducted by Dames and Moore for LBII as part of the US-AID funded
coastal management plan of SOCSARGEN last 1993. The Marine Biology
Department of the MSU-College of Fisheries has an on-going study of
specific coral reef sites in the bay. The bay is also a station for the
landed catch and effort monitoring (LCEM) of the DA-BFAR/FSP Tuna Research
Project from 1993 to 1995 conducted jointly by BFAR, PRIMEX and SPC.
ECONOMIC VALUE AND SOCIAL BENEFITS
Fishing on the coral reefs of
Sarangani Bay is commonly practiced by the municipal fishermen from
different areas. Tourism in the coastal area is not yet developed but
there are already eight existing beach resorts that cater to the residents
and local visitors. Glan and Kiamba have white sandy beaches with reef
diving attractions ideal for the promotion of tourism.
Sarangani Bay is the richest tuna
fishing ground in the country. Results of the fish monitoring conducted by
Mindanao State University-General Santos Foundation (MSU-GSF) revealed
that 168 species are caught within the bay itself, 97% of the catch
comprised of pelagic species. In 1995 for example, total catch for October
and November was valued at PhP 4.8 M (MSU-GSF). There are approximately 49
corporations into fishing, 5,400 commercial fishers and 32,000 municipal
fishermen (LBII 1993). Fishes landed in the bay are small (e.g., frigate
mackerels, roundscads) and large pelagics (tunas, mackerels, marlins and
flying fishes), and demersal fishes (snappers, breams, groupers and
moonfishes). Throughout the year, the most abundant catch are the tunas,
scads and flying fishes.
DISTURBANCES AND BENEFITS
Throughout the coastal area, there
was evidence of destruction of corals due to rampant practice of dynamite
fishing. Furthermore, heavy sedimentation is evident at the mouths of
rivers particularly those entering the north of the bay. Silway, Buayan
and Malabulan rivers have major impacts on the fringing reefs. Formerly
extensive fringing reefs in the mouth of the bay have been heavily silted
and now contain a very low diversity of corals (LBII, 1993). Seagrass
areas on the north and east of the bay are subject to periodic and heavy
sedimentation from the major rivers. Although, the bay is ideal for ports
because of the general lack of typhoon, the absence of wind prevents
vertical mixing and dilution making entrainment of pollutants and
sediments along the coast more likely.
Fishing intensity in coral reefs and
coastal areas is extremely high and fishermen who resorted to destructive
methods, such as, blast fishing have left large areas of reef physically
destroyed as a viable habitat for fish.
LEGAL PROTECTION
Sarangani Bay was declared as a
Protected Seascape under the NIPAS act (RA 7586) giving management
authority to DENR. An existing Memorandum of Agreement empowers local
government agencies and other departments (e.g., DENR) to manage the area,
as well.
RECOMMENDATIONS
Reefs retaining high
percentage of coral cover should be protected while degraded reefs should
be rehabilitated to maintain or improve the condition of the habitat. Laws
against blast fishing and other destructive methods should be strictly
implemented coupled with environmental information and education
campaign.
(Editor’s Note: Considerable
amendments were provided by Mr. Ramon Miclat and Ms. Hilly Ann
Roa-Quiaoit.)
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