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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.

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