Facets of Lanka:
Two biodiversity 'hotspots' in the southwest
Derrick SCHOKMAN
CONVENTION: May 22 is recognised as 'World Biodiversity Day'.
It is meant to remind us that the Convention of Biological Diversity was
introduced at the Earth Summit or UN Conference on Environment and
Development held in Rio de Janeiro in 1992.
The convention was ratified by 150 nations including Sri Lanka. It
was a clear expression that biological diversity in flora and fauna was
being significantly reduced by human activity, and that action was
required to develop national strategies for their conservation.
Typical wet lowland forest with tall trees (chiefly dipterocarps)
and lianas.
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A biodiversity action plan for Sri Lanka was consequently prepared.
But as resources for this purpose were limited, it was necessary to
identify and take action in 'hotspots' where conservation was urgently
required.
'Hotspots' are locations featuring a very high level of species
diversity and endemism, which are especially threatened by human
activity.
Two hotspots were selected for priority action. Namely the wet
lowland forests in the Galle and Matara districts which are under threat
from high population density in the surrounding areas and an acute
shortage of land, and the near-shore coral reefs in the southwest which
have been severely degraded mainly due to coral mining.
Fragmented
In the Galle and Matara districts, except for the World Heritage
Sinharaja Forest (11,280 ha) and the KDN or
Kanneliya-Dediyagala-Nakadeniya forest reserve (10,139 ha), there are
only fragmented remains of a few hundred hectares each.
These forests are important because they are the last remnants of the
once widespread mid-miocene tropical rainforests in this country.
As such they are floristically the richest in biodiversity with a
high level of endemics which are rare and localised.
Ornamental fish in the fringing coral reefs of the southwest coast
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The forest master plan of 1996 and the current programmes of the
Forest Department, assisted by the IUCN, have provided the base to move
into an action phase of biodiversity conservation in this region.
These programmes include (1) protection of the Sinharaja as a
national heritage wilderness area (2) a declared moratorium on all
felling in natural forests of the wet zone until 'conservation forests'
are identified where no commercial logging will ever be allowed again
(3) a study of the KDN forest reserve for the dual purpose of logging
and biodiversity conservation and (4) a participatory form of forest
management involving local communities to prevent encroachment and
damaging use of the forest.
What is required now is for the Forest Department to strengthen its
capacity in the scientific and management aspects of biodiversity
conservation and its community mobilisation programmes to ensure the
sustainable use of forest resources.
With the support of the IUCN, the department has prepared management
plans and activities in the buffer zones of several forests to benefit
the communities living in those areas.
For centuries the coastal belt of fringing coral reefs have been a
valuable resource for coastal communities. They are important habitats
of marine fauna and flora for sustaining the coastal fishery and
containing coastal erosion.
A typical reef supports 80 to 50 species of coral dominated by
Acropora, Montipora, Porites, Favites, Echinopora, Pocillopora,
Peatygyra, Goniastrea and Leptoria.
The reefs also support about 350 species of fish eg. guorpers,
snappers, sweet-lips, parrot fish, rabbit fish, surgeon fish, butterfly
fish and damsel fish.
Also ornamental fish like Chaetodon benntti, C. unimaculata and
Balistoides conspicellum.
Mollusc, sea anemones and sea cucumbers are important invertebrates.
More recently the export of coral reef organisms has contributed
substantially to the economy.
Beaches and fringing reefs are also favoured sites for tourism.
Snorkelling, scuba-diving and the viewing of corals are popular among
tourists. The reefs from Hikkaduwa to Tangalla are now severely damaged,
mainly due to coral mining for the production of lime for building
purposes.
Annually over 7,000 tons of coral and coral debris were removed from
a 60 km stretch, and both coral and shells were collected for the
tourist industry.
The Coast Conservation Department played an important role in
addressing this problem by legislation prohibiting the mining and
processing of coral, and schemes to provide alternative livelihood for
those dependent on coral mining.
These efforts resulted in a substantial reduction of the quantity of
coral extracted. Mining, however, continues to be a serious threat owing
to poor law enforcement and the profitability of the lime industry.
A serious deficiency in the above strategy was the failure to
recognise the importance of giving a participatory role to local
stakeholders in the management of coastal resources.
The Coastal Zone Management Plan of 1996 sought to remedy this
deficiency by the formulation and implementation of Special Management
Area (SMA). Committees for selected coastal sites, comprised Government
authorities and key community groups.
A pilot SMA project was implemented in the Hikkaduwa Marine sanctuary
where many reefs were seen to be dead or dying.
It had to address problems of damage caused by pollution, boat
anchorage and divers collecting reef organisms, sedimentation and
conflicts between the economic interests of tourism and fisheries.
Several other coastal sites have been identified for such planning
and management, but they have not yet been implemented. Implementation
efforts are impaired by inadequacies in regard to institutional
cooperation, political commitment and public awareness. |