Environmental impacts of proposed Baddegedara impounding reservoir
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This research study, "Environment Impacts of Proposed Baddegedara Impounding   Reservoir" was conducted in relation with the feasibility study for water   supply and sewerage for Koggala Export Processing Zone and the surrounding   license Zone.The project area consist of Talpe, Habaraduwa, Koggala EPZ and   Coastal belt. Ahangama, Dikkubura and Imanduwa. People living in the area   excluding Koggala EPZ have to depend on individual water sources. The majority   of the population depend on ground water drawn from shallow dug wells. The main   complaint of people living along the coast in the project area regarding the   water quality of their dug wells in salinity. Most of these wells are shallow   and not covered or protected. Water obtained from these wells is therefore at   high risk to be polluted with organic matter.Study was conducted by having field   surveys. When selecting a source for the project area whenever possible first   choise was given to ground water which requires the least treatment. But the   test drilling programme shows that it is impossible to get total water   requirement by ground water itself. Therefore we have to go for a surface water   source close to the project area.Proposed impounding reservoir at Baddegedera is   located nearest to the project area. Reservoir catchment is the upper most reign   of a tributary of Polwatta ganga which meets the main river about 2 Km upstream   of Kananka. This catchment is located near to the catchment of Hiyare impounding   reservoir which is presently supplying part of water to the Galle Municipality. Environment Impacts were assessed by using a matrix called Environment   interaction matrix. In this method a list of all potential impacts of the   project were prepared and each individual impact was assessed. The matrix was   analyzed by using the Battle's environment evaluation system. In this method the   weights of the parameters were assigned depending on the relative importance of   the parameters. Value function for the variation of environmental quality index   with the change in each of the environmental parameter had to be determined. The   environmental quality (e.q.) index with project and the e.q. index without   project were evaluated for each environment parameter. Then the environment   impact unit was obtained by getting the product of the relative weight of the   parameter and the e.q. index. In this method positive net change of product means   beneficial impacts whereas negative product means adverse impacts. The   topography of the area does not lend itself to the fashioning of a deep lake.   According to past studies done by various people the ideal wildlife lake is   shallow with gently slopping shore. This type of situation could be expected   from the proposed impoundment. These natural qualities of the habitat could be   further augmented by various management techniques such as the restriction of the   area of impoundment and catchment.
