06-bioresourcesstatu.. - M. S. Swaminathan Research Foundation
06-bioresourcesstatu.. - M. S. Swaminathan Research Foundation
06-bioresourcesstatu.. - M. S. Swaminathan Research Foundation
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Vembanad Lake<br />
cyprinoides (Grey). As mentioned in the<br />
preceding columns with a length of 60 km north to<br />
south from Cochin to alleppy and an area of 21,053<br />
ha. with the commission of salt-water barriers, the<br />
lake is divided into two entirely different<br />
ecosystems. The northern sector downstream is<br />
estuarine while the southern upstream is<br />
freshwater.<br />
The main demand for lime from clam resources is<br />
for brick laying, plastering and white washing. At<br />
present, number of industries such as the<br />
Govetnment owned Travancore Cements and<br />
Travllllcore Electrochemicals use clam shells<br />
(Mammen, 1984). According to a rough estimate<br />
they consume nearly one lakh tonnes of clam<br />
shells annually. The clam resources of the lake<br />
have been estimated by Rasalam and Sebastian<br />
(1976) and Achary (1987) based on the data<br />
gathered from co-operative societies. The clam<br />
beds were located by Kurup et at. (1990). This<br />
study is important as it pertains to more than a<br />
decade after the commissioning of the barrier ..<br />
The species Vellorita cyprinoides supports<br />
sustenance fisheries in the estuaries and<br />
backwaters of Kerala, Karnataka, Goa, Tamilnadu<br />
and Andhra Pradesh and contributes 67% to the<br />
clam fishery. The meat is locally consumed and it<br />
is also used in supplementing various aquacultue<br />
feeds (Kizhakundan and Narasimhan, 1995). This<br />
species plays an important role in the rural<br />
economy of Kerala.<br />
Exploitation Pattern : The Department of Mining<br />
and Geology controls the clam collection and<br />
periodically leases out areas for dredging and also<br />
issues licenses to divers to collect surface deposits<br />
of live (black) and dead (white) clam shells. There<br />
has been lot of agitation from the divers who feel<br />
that dredging leads to depletion of live clams. The<br />
fisherfolk operating stake and Chinese dip net also<br />
feel that dredging has lead to depletion of their<br />
catch. These allegations are not entirely without<br />
basis (Mammen, 1984).<br />
Cutter suction dredgers are used in Vembanad<br />
Lake. As the dredger cuts through the soil, the<br />
90<br />
suction pump takes the soil and clam shells along<br />
with water to the floating washery, where the<br />
shells are separated and delivered to a barge<br />
while the clay water slurry is allowed to flow into<br />
the lake. Initially the dredger used to collect about<br />
50 tonnes of sub fossil clam deposit in two hours<br />
later as the resource declined due to<br />
overexploitation, it took upto six hours to get 50 t<br />
of clam shell (Mammen, 1984). However, even at<br />
this rate the factories are finding it economical to<br />
dredge the shell rather than buy from the divers.<br />
The factories claim that they are dredging in<br />
deeper waters and thus do not come in the way of<br />
collection of clams by the divers. According to<br />
them, if the divers get the sole licence for<br />
collection, they are likely to dictate the terms.<br />
Estimates of the exploited clam population: The<br />
population of clam in Vernban ad lake has been<br />
estimated by Kurup et at. (1990). They had<br />
divided the regions into ten zones comprising five<br />
zones each on the northern and southern side of<br />
the Thanneermukkam barrier. They reported the<br />
presence of extensive clam beds in the regions<br />
where the lake bottom is sandy. The clams avoid<br />
the areas' where high percentage of silt is present.<br />
The important live clam beds of different zones as<br />
reported by Kurup et at. (1990), are presented in<br />
Tables 1 & 2.<br />
Size distribution of clam : The size of the<br />
exploited clams varies from 9 to 59 mm. However,<br />
size below 10 mm and above 39 mm were rarely<br />
represented. The dominant modal groups were 15<br />
- 19, 20 - 24 & 10- 14 mm, in that order. The sizes<br />
prevalent in different zones of the lakes were<br />
analysed. It appears that the dominant mode in<br />
zone I was that of 30-34 mm. Here the clam is<br />
present in semi-enclosed lake with low salinity. In<br />
zone II and III where higher salinity is prevalent<br />
the modal groups 15 - 19 and 10 - 14 mm were<br />
dominant. Zone IV had almost all the three groups<br />
15 - 19, 20 - 24 and 25 - 29 mm equally<br />
represented. Zone V had modal group 20 - 24 mm,<br />
which was not apart from all other zones with a<br />
dominant modal group of 30 - 34 mm.