Management of Coral Reefs in Gulf of Mannar
Girija Phadke and Khaimesh
Sehgal*
*Central
Institute of Fisheries Education, Seven Bunglows, Versova, Andheri (W.),
Mumbai, Maharashtra, India 400061.
Introduction:
Coral reef system as also the ecosystem of the tropical rain forest, are
the most matured marine ecosystems of our planet. The coral reefs characterize
an ecosystem of high biological diversity, having the greatest number of
species of any marine ecosystem. Livelihood of many millions of people is
dependent on this unique ecosystem as a considerable proportion of their food
and earning from the productivity of coral reef. Coral reefs are considered as
one of the most important critical resources for various ecological,
environmental and socio-economic reasons.
Uses of
Coral reefs:
They play an important role in global biochemical processes and in the
reproduction of food resources in the tropical regions. The people living along
the coast obtain a considerable proportion of their food and earnings from the
productivity of coral reefs. Coral reefs act as a barrier against wave action
along coastal areas thus preventing coastal erosion. In addition, coral reefs
protect mangroves and seagrass beds in certain areas, which are the breeding
and nursing grounds of various economically important fauna. Coral reefs are
also important breeding, spawning, nesting, and feeding areas for many
economically important varieties of fishes and other marine organisms.
Gulf of
Mannar:
Gulf of Mannar, extends from Tuticorin to Rameswaram Island in the SW-NE
direction, lies between 78° 5' & 79°30' E longitudes and 8°47' & 9°15'
N latitudes, to a length of about 140 km. There are 21 low islands situated at
an average distance of about 8 km from the coast and running almost parallel to
the coastline. These islands are broadly grouped into Tuticforin, Vembar,
Keelakkarai and Mandapam groups. These areas are endowed with a combination of
ecosystems including mangroves, seagrass, seaweeds and corals reefs. Different
types of reef formations have also been observed along the periphery of the
islands viz. fringing reef, patch reef and coral pinnacles.
In Gulf of Mannar, the coral reefs have been used as a source of calcium
carbonate, building blocks and rubble for construction of roads. In general,
coral reefs in Gulf of Mannar can be categorized as "degrading", and hence,
monitoring and management of these valuable marine resources are of prime
importance.
Blasting and dredging activities result in high sedimentation on the
coral reef of Gulf of Mannar there by leading to its degradation. The coral
reefs of Tuticorin group of Islands in Gulf of Mannar have been damaged due to
the discharge of effluents from petrochemical and other industries along the
coast, and fly ash discharges from thermal plants.
Techniques
of study:
To study coral
reefs area effectively and to monitor changes over time, accurate, rapid and
cost-effective mapping techniques are required. Satellite remote sensing is
widely used as a tool in many parts of the world for the management of
resources and activities within the continental shelf containing reefs.
Preliminary studies carried out in India by Space Application Center (SAC)
Ahmedabad, have proved the importance of remote sensing data in mapping and
monitoring of the coral reef.
Objectives of the Study:
The objectives of the present
study are to:
- Assess the
current status of coral reefs in Gulf of Mannar based on remote sensing
and GIS approach
- Assess the
changes that have occurred in the spatial distribution of coral reefs
during the period 1988-1998 using multidate remote sensing data
- Study the
coastal geomorphology and its influence on the coral reefs
- Study the
influence of land use / land cover changes on the coral reefs
- Suggest
suitable management measures for sustainable management and preservation
of coral reefs in Gulf of Mannar region
Materials and Methods:
To cover the
objectives of this study, six types of approaches have been attempted are
listed below:
- Analyse
and interpretation of optical remote sensing data for coastal
geomorphology
- Analyse
and interpretation of optical remote sensing data and Survey of India
Topographic sheets (1969) for shoreline change mapping.
- Interpolation
of Bathymetry using Naval Hydrographic charts and bathymetry survey
- Analyse
and interpretation of multidate optical remote sensing data for coastal
land use/land cover change deduction
- Socio-economic
studies
- Analyse
and interpretation of multidate optical remote sensing data for coral reef
change deduction.
Areal distribution of coral
reefs in Gulf of Mannar:
A chain of 21
low islands has been observed along the offshore region of Gulf of Mannar
(Table 1). It extends from south of Rameswaram to Tuticorin. All islands are
made up of a calcareous framework of dead reef and sand. They have a low and
narrow sandy coast and some of them have rocky coast. Around all offshore
islands, well-developed coral reefs have been noticed. Geomorphologically,
coral reefs in this area are of fringing type, though some patchy corals are
also observed in between Appa Island and Pilliyarmuni Island, and in some areas
like Bharathi nagar coast and southeast coast of Kariya Shuli Island.
Table 1: Areal
Distribution of Offshore Islands and Types of Reefs and their Areal Extent
|
Sr. No
|
Islands
|
Island Area(km²)
|
Coral Reef
|
|
Reef type
|
Area(km²)
|
|
1
|
Van Island
|
0.245
|
Fringing type
|
1.090
|
|
2
|
Koswari Island
|
0.241
|
Fringing type
|
1.474
|
|
3
|
Kariya Shuli Island
|
0.166
|
Fringing type
|
0.702
|
|
4
|
Uppu Tanni Island
|
0.377
|
Fringing type
|
0.644
|
|
5
|
Shalli Island
|
0.126
|
Fringing type
|
0.249
|
|
6
|
Nalla Tanni Island
|
1.248
|
Fringing type
|
1.250
|
|
7
|
Anaipar Island
|
0.229
|
Fringing type
|
0.888
|
|
8
|
Palliyarmunai Island
|
0.134
|
Fringing type
|
0.687
|
|
9
|
Appa Island
|
0.410
|
Fringing type
|
3.612
|
|
10
|
Talairi and Valai Island
|
1.072
|
Fringing type
|
9.268
|
|
11
|
Muli Island
|
0.170
|
Fringing type
|
1.208
|
|
12
|
Musal Island
|
1.836
|
Fringing type
|
27.73
|
|
13
|
Manalli Island
|
0.353
|
Fringing type
|
|
14
|
Manalli Putti Island
|
0.037
|
Fringing type
|
|
15
|
Pumurichan Island
|
0.187
|
Fringing type
|
8.320
|
|
16
|
Kovi Island
|
0.482
|
Fringing type
|
|
17
|
Kursadi Island
|
0.740
|
Fringing type
|
|
18
|
Shingle Island
|
0.191
|
Fringing type
|
1.023
|
|
19
|
Near Bharathi nagar
|
---
|
Patchy type
|
0.131
|
|
20
|
Between Appa Island and
Pilliyarmunai Island
|
---
|
Patchy type
|
3.981
|
|
21
|
Southeast of Kariya Shali
Island
|
---
|
Patchy type
|
0.969
|
The areal distribution of coral reefs, reef vegetation, degraded coral
reef, etc for the years 1988 and 1998 are shown in Table 2.
Table 2: Areal
distribution of coral reefs and its changes observed during the period from
1988 to 1998
|
Category
|
Area (km²)1988
|
Area (km²)1998
|
Changes1988-1998
|
|
Reef area
|
73.70
|
48.18
|
-25.52
|
|
Reef vegetation
|
12.31
|
10.15
|
-2.16
|
|
Degraded reef (Coral mining)
|
-
|
2.68
|
+2.68
|
Degradation
of coral reefs:
The degradation
of coral reefs in the Gulf of Mannar is quit severe due to the human stress
(anthropogenic) and also by natural agents. The coral mining for lime, sand
mining, pollution, sedimentation, fisheries, population pressure, commercial
shell collection and industrial development has led to the increase in coral
reef degradation in India.
The total coral
reef area in Gulf of Mannar based on the present study (1998) is about
61.01km², of which reef area covers 48.18 km², reef vegetation covers
10.15 km² and degraded coral occupies 2.68 km².
The analysis of
multi-date satellite data indicates that nearly 25.52km² area of coral
reef was lost over a period of ten years (1988-1998). Through remote sensing
the demarcation of dead coral is possible within 2 feet beyond not possible.
During the time of ground truth it was identified that nearly 67.2% of the
corals were dead corals, 13% of coral reef are directly removed by coral mining
and the remaining 19% were live corals.
Coral reef
ecosystems are very sensitive to external impacts both natural and manmade,
which violate their homeostasis. The majority of damage to coral reefs around
the world has been through direct anthropogenic stress. 57% of the worldÕs
coral reefs are potentially threated by human activity such as coastal
development, destructive fishing, over exploitation, marine pollution, runoff
from deforestation and toxic discharge from industrial and agricultural
chemicals. As a result of the increasing human population along the coastal
area, anthropogenic impacts on the coastal zone have become severe over the
past few decades. Coral ecosystem also face many threats, of which some are of
natural origin like storms and waves particularly tropical storms and cyclones
that cause major intermittent damage to reefs. The majority of damage to coral
reefs around the world has been through direct anthropogenic stress.
During the time
of ground truth, the following activities were observed to be the major causes
in degradation of coral reefs in the study area:
(I)
Anthropogenic Stresses (Human Activities)
(II) Natural Stresses
1. Anthropogenic stresses (Human activities):
Increase in
human population and economic activities in the study area have increased the
pressure on the adjacent reefs. The major causes of coral reef degradation are:
- Over
fishing and destructive fishing practices
- Sea weed
collection
- Commercial
shell collection
- Coral
mining
- Poor land
use practices
- Coastal
urban development
- Harbour
and dredging activities
- Industrial
development and pollution
1. Over fishing and destructive fishing practices:
Fishery is the primary economic activity
of the people of the coast of Gulf of Mannar. There are about 50,000 fishermen
engaged in fishing activity. The marine fish catch from Gulf of Mannar during
1992-1996 was between 0.55 and 1.02 lakh tons, with an average of 78, 511 tons.
The pelagic fishes formed 54.38%, demersal fishes 34.85%, crustaceans 5.69% and
molluscs 5.08%. Nearly 20% of total fishes in Tamilnadu are being caught from
Gulf of Mannar, of which 44,600 tons of pelagic fishes and 35,200 tons of
demersal fishes. The fishermen collect these holothurians by diving in shallow
reef areas. Much of the fishing is carried out on / and near the coral reef
area. In many areas of Gulf of Mannar, the majority of the reefs have been
destroyed by fishing due to modern fishing techniques like mechanized launches
with trawling net and gill net and also by destructive fishing practices such
as dynamite fishing near Tuticorin area. These destructive methods cause direct
damage to the corals and indirectly affect their growth by increasing turbidity
and suspended sediment in the coastal waters and reducing the clarity of
seawater and increasing sediment loads on reefs.
2. Sea weed collection: -
Seaweeds form
one of the most important marine living resources in Gulf of Mannar. Because of
their commercial value, the seaweeds are harvested by fishermen for agar
industry. More than 1000 fishermen and women are engaged in seaweed collection
in the study area and nearly 5000-7000 tons (dry weight) seaweeds are harvested
annually. The continuous harvesting of seaweeds results in the decrease in
areal extent of seaweed area, which was estimated to be about 2.16 km²
area over ten years (1988-1998). The decreasing of seaweeds may lead to coastal
erosion and removal of the coral reefs.
3. Commercial shell
collection:
Commercial shell
collection is another human activity which causes coral reef degradation to
some extent. Shell collection is one of the important economic activities of
the fishermen living in the study area. Nearly 770 fishermen are engaged in
this occupation. This activity increases the sedimentation in coastal water
leading to the death of coral.
4. Coral mining:
Coral mining
activity has caused extensive degradation of reefs, coastal erosion and
sedimentation in a number of countries all over the world. In the study area
coral mining is the major human activity, which causes coral reef degradation.
Coral reefs are used on a large scale as raw material by the lime industries.
In Tuticorin group of islands this activity is very active and the corals have
been used for building, industrial and chemical purposes. The rapid development
of lime based industries in and around Tuticorin has accelerated the coral
mining. Nearly 250 skilled divers and about 50 boats are engaged in the coral
reef mining. The use of explosives for reef mining, has produced very serious
problems to the coastal and marine ecosystems like coastal and island erosion
and sedimentation, coral reef degradation and reduction of marine faunal
population. The net result of removal of corals is that the depth has increased
to about 1m. This has also been confirmed by the bathymetry map pertaining to
Tuticorin group of islands.
5. Poor land use practices:
Another cause
for the damage of coral reefs is poor land use practices, such as agricultural
activities, changing land use practices and deforestation etc, which increases
land derived sediment flowing onto coral reef. In the present study it was
observed that nearly 470.22 km² of land behind the coast of Gulf of Mannar
has been under agriculture land, of this nearly 417.66 km² area fall under
the category of cultivated land. Cultivation in this area is poor and intensive
method of cultivation is generally practiced during rainy season. The poor
agricultural practices increase the agriculture waste like pesticides and
fertilizers, which are dumped into the coastal water through surface runoff
during rainy season and through rivers. This encourages rapid algal growth,
which chokes coral polyps and cut off the supply of light and oxygen. This
problem is common in Tuticorin group of islands, Vembar group of islands and
Keelakkarai group of islands.
Another major
cause for the coral reef degradation is changing land use practice. The
analysis of multidate satellite data indicates that nearly 2.45 km² of
cropland has been converted in to salt pan (1.86 km²) and aquaculture pond
(0.59 km²); 2.74 km² of agriculture plantation has been converted
into cropland (1.77 km²) and salt pan (0.97 km²); 10.74 km² of
forest plantation has been converted into agriculture plantation (6.19
km²) and forest blank (4.54 km²); Nearly 68.78 km² of scrubland
has been converted into settlement (7.10 km²), saltpan (2.59 km²),
aquaculture ponds (0.18 km²), forest plantation (4.31 km²),
agriculture plantation (12.10 km²), fallow land (7.60 km²) and
cropland (34.90 km²) over a period of ten years (1988-1998) along the
coast of Gulf of Mannar.
Another important human activity
encountered in Gulf of Mannar is destruction of natural forest and island
vegetation. Through remote sensing it has been clearly identified that nearly
3.80 km² of natural forest has been destroyed for fuel wood and
cultivation by human beings along the coastal plains of the study area, and
nearly 1.53 km² of island vegetation has been cut down for fuel wood over
a period of ten years (1988-1998). These changing land use practices,
destruction of natural forest and island vegetation accelerate the soil,
coastal and island erosion and increases the input of inland-suspended soil
into coastal waters. The increase in suspended soil and other suspended
materials in coastal water smothers the reefs and causes their degradation.
6. Coastal urban development:
Increasing urban
population along the coastal area has lead to pollution due to sewage discharge
into the coastal waters. Discharge of sewage is responsible also for the loss
of coral reefs in large quantities. Along the coast of Gulf of Mannar, five coastal
towns are located and due to rapid growth of population, the urban areas have
increased in area from 22.07 km² to 34.92 km² over a period of ten
years (1988-1998). As a result of this rapid urbanization there is an increase
in the amount of discharge of sewage waste into coastal waters, which has
caused the death of corals in Gulf of Mannar.
7. Harbour and dredging activities:
Dredging and
other harbour related activities like anchoring and ship grounding have
increased sedimentation in the coastal waters and caused the degradation of
coral reefs. In the study area the New Tuticorin harbour has been constructed
at the upstream side of the Tuticorin group of island. This harbour has a
breakwater, which has changed the current flow pattern and sediment movement
along the Tuticorin coast and islands. The periodic dredging operations at the
entrance of the harbour and anchoring of ships have increased the amount of
silt plume, which in turn has increased water turbidity, and lowered the light
intensity, leading to coral death. This problem has been extensively observed
in Tuticorin group of islands.
8. Industrial development and pollution:
Industrial
development and their waste discharge into coastal water affect the coral
reefs. The coast of Gulf of Mannar is experiencing an accelerated growth in the
rate of industrialization, since the New Tuticorin port became operational. The
industrial development has led to marine pollution and coral reef degradation.
The dumping of fly ash slurry into Karapad Bay by the Thermal power station
resulted not only in filling up of an extensive portion of the bay, but also
letting out of ash directly in to the sea causing extensive damage to the coral
reef. Dharangadhare Chemical Works Ltd, Plastic Resins and Chemical Ltd and
Tuticorin Alkali Chemical Ltd are the major chemical industries in Tuticorin
area, which discharge their effluents into open sea. These effluents contain
mercury, sodium carbonate, ammonium chloride and sodium bicarbonate etc. which
are harmful to the coral reefs and the environment.
II.
Natural stress:
Natural problems
are those that are not caused by man, but occur naturally over the long
history. Natural problems such as storms, waves, sea level variation, fresh
water runoff, volcanic activity etc cause the degradation of coral reefs.
Various authors have studied coral degradation due to natural activities in the
Gulf of Mannar. Through remote sensing and extensive ground truth it has been
identified that natural activities such as monsoons, waves, currents, tides and
sea level fall have caused the coral reef degradation in Gulf of Mannar.
During the
northeast monsoon period highly turbid and low saline water from Palk Bay is
transported to Gulf of Mannar by long shore current along Pamban channel. This
increases the silt in Gulf of Mannar waters and causes the death of coral reef.
Several corals die yearly during northeast monsoon period. In addition to this,
during the low tide period, the tidal current moves towards south and transport
some amount of sediment to Gulf of Mannar. Towards the seaward side of the
island, the high velocity waves hit against the reef edge (wave breaker) and a
fall in the velocity of waves cause the wave induced current forms which moves
towards the island and drop the littoral sediment on reef leading to coral
degradation. The prolonged and repetition of such action, result in the area
between island and reef edge to became shallow. The multi-date bathymetry map
analysis indicates that nearly 0.24m depth has decreased over a period of 24
years on the seaward side of Pumurichan, Kovi and Kursadi Island. This process
has also caused the coral degradation. This problem is observed mainly in the
Mandapam group of islands.
The sea level in
Gulf of Mannar is on a regression phase. The sea level fall causes rising of
coral reef. The raised reefs are the reliable indicator of sea level fall.
Raised reefs have been observed in many places of Gulf of Mannar. The
multi-date shoreline map and bathymetry map indicate that sea level has fallen
by 0.36m over a period of 24 years (1975-1999) and the shoreline has migrated
143.11m towards the seaward side over a period of 30 years (1969-1998).
Sedimentation is
a major factor controlling the distribution of reef organisms and overall reef
development. The reduced level of light due to suspended sediment in the water
column can reduce coral growth and has an impact on natural zonation patterns.
Excessive sedimentation can also discourage the settlement of coral larvae.
Most of the studies on the effects of turbidity on corals have concentrated on
anthropogenic-increased sedimentation and turbidity. According to present
study, nearly 67.2% of the coral reefs in Gulf of Mannar is not in living
condition due to sedimentation and turbidity caused by anthropogenic and
natural activities. The anthropogenic activities like destructive fishing
methods, seaweed collection, commercial shell collection, coral mining,
intensive agriculture, changing land use practices, deforestation and
industrial waste input etc. and natural activities like monsoon, wave action,
ocean current and tides were identified as the agents that increase the
sedimentation and turbidity in coastal waters of Gulf of Mannar.
Recommendations:
Based on the
present study some of the followings are the recommendation for manage the
coral reefs in Gulf of Mannar
- It is
necessary to create awareness among the coastal communities in the study
area, in order to protect and conserve the coral reefs through effective
involvement of educational institutions and NGOs.
- Stringent
measures need to be under taken with immediate effect to ban coral mining
and to take into task those involved in or those who encourage the
exploitation of corals for any purpose. Patrolling the coast to check
coral mining should be carried out.
- Law should
be enacted to regulate and stop trawl boat operation in the zone earmarked
for non-mechanized boat. The Department of Forest and the Department of
Fisheries should take steps to stop anchoring of vessels on coral reefs,
pair trawling and dynamite fishing.
- Indiscriminate
picking of budding seaweeds needs to be banned.
- Commercial
shell collection should be controlled and closely monitored.
- Marine
Resources Management Centers should be established to improve the skills
of fishermen communities in areas other than coral mining, which in turn
will lead to efficient management of coral reefs.
- Initiatives
to train the coastal fishermen in mechanized boat operation, shell
collection, seaweed collection and conservation of coral reefs need to be
taken up so that they could find alternate sources of livelihood.
- Deforestation
along the coast and islands of Gulf of Mannar should be banned. The Forest
Department should take up afforestation along the coast and islands of
Gulf of Mannar to protect soil erosion.
- Discharging
of untreated sewage and urban wastes into the coastal waters should be
totally banned.
- Dumping of
any kind of material that would affect the coral reef ecosystem should be
banned.