Effect of Thermal Pollution on the Hydrobiological

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Effect of Thermal Pollution on the Hydrobiological Effect of thermal pollution on the hydrological parameters of River Jhelum (J & K) Item Type article Authors Qureshi, T.A. Download date 02/10/2021 00:41:42 Link to Item http://hdl.handle.net/1834/33374 159 J. Indian Fish Assoc., 35: 159- 166, 2008 EFFECT OF THERMAl POllUTION ON THE HYDROlOGICAl PARAMETERS OF RIVER JHELUM (J & K) T.A. Qureshi Consultant and Head Department of Applied Aquaculture, Barkatul!ah University, Bhopal, M.P. ABSTRACT The Buniyar hydroelectric project and the lower Jhelum Barrier at Gantamulla constructed across river Jhelum are in operation from several years. The two power stations have changed the hydrological features of the area where dam is situated. Therefore, the impact of hydroelectric projects on fishery resources of river Jhelum is a matter of great concern. The treated water from the power house is released through turbines, having cooling effect on them. The change in the hydrological parameters such as increase in temperature, depletion of oxygen etc. might have brought fishes under stress which is the main cause in decreased population of finfishes from site to site. The golden Mahseer, Tor putitora which was once an abundant species in River Jhelum has disappeared due to human intervention. The prevailing water quality around hydroelectric projects is unsuitable for finfishes of river Jhelum. Keywords: Hydroelectric projects, Hydrological Parameters, River Jhelum. INTRODUCTION constructed across the river from where the water is led to turbines, beside the main river. River Jhelum is lifeline of Kashmir The water is then allowed to join the main river, and is the only source of water which drains after cooling the turbines. In case of Lower the valley from South to North. It is the only Jhelum hydropower station, the water is led ultimate source of water, which inhabits all through an open channel of few kilometres, species of fishes of valley, being the most while in case of Buniyar barrage water is led resourceful water body. But due to various through an eleven kilometre long tunnel in the anthropogenic activities it is bringing up mountains, achieving a difference in altitude of threat to its fauna and flora. The most about 210m., before water is again allowed to precarious and deteriorative is construction join the main river. of dams which have affected the hydrological features of region surrounding the dam. The two hydroelectric projects have caused thermal pollution in the dam area. The Buniyar barrage and the Lower Change in the hydrological parameters might Jhelum barrier at Gantamulla constructed affect the metabolic activities of fishes and across river Jheium, are in operation from may result in stress, which will result in several years. Both hydropower stations have decreased distribution and population of affected the hydrological features of dam area fishes. of river Jhelum. The dam has been 160 T.A. Qureshi Devi et a/., (1979L has envisaged thermal Site-3: pollution as one of the factors responsible for It lies near the Uri Dam (BoniyarL causing environmental hazard. Most where the water of river Jhelum is again researchers have worked on the fish fauna of blocked. On left bank, it is lined by Buniyar and Jammu and Kashmir. Some of the recent on the right bank by Pringal. efforts are that of (Qureshi et a/., 2006; Salman eta!., 2006; Arjumand et al., 2006). Site-4 Scientists have also worked on the temperature regime of the water bodies of It is situated at the end of Uri Kashmir valley (Wanganeo eta/., 1992, Yousuf hydroelectric power project. The area is eta/., 1995) but very less work is available on guarded by Bandhi on the left bank and the effect of thermal pollution on the Paranpela on the right bank. hydrobiological aspects of these water bodies as well as availability of different fishes in this Physico-chemical Parameters area. Therefore, this piece of work was undertaken for investigating the same in river Monthly samples of water were Jhelum in Jammu and Kashmir. collected from selected sites of River Jhelum, for a period of six months from June, 2006 to MATERIAl AND METHODS November, 2006. The water parameters such as temperature, total dissolved solids, pH, free Study Sites carbon dioxide, and total alkalinity were measured at sampling site it self. The Four sites from various locations on estimation of dissolved oxygen, chloride, total River Jhelum were selected for the study of hardness and COD was done in laboratory. All physico-chemical parameters. the parameters were analysed following the methods of Golterman et a/. (1978), Boyd Site-1 (1979) and APHA {1995). The first site was selected near the RESUlTS Jheium entering the Lower Jhelum Hydroelectric Power Project (LJHP). The site is Physio-chemical parameters of any lined by Gantamulla on the left bank and water body assume importance since slight Zehanpora on the right bank. disturbance in any one of them may alter the whole ecological picture of the water which Site-2 may create disaster to all aquatic lives inhabiting it. The physico-chemical parameters It lies near outlet of L.J.H.P towards evaluated exhibited marked variation through the Uri barrage. The area is lined by Warikha out the study period which is shown in fig 1-8. on the left side and Chahal on the right side. The physico-chemical parameters were evaluated in from sampling stations fixed at River Jhelum which exhibited marked variation EFFECT OF THERMAL POLLUTION ON THE HYDROLOGICAL PARAMETERS OF RIVER JHELUM. p & K}. 161 throughout the study period which is shown pH in fig.l-8. (Fig.-3} During the study period the Water temperature (Fig.-1) During maximum pH recorded at site I was to be 9.6 in the study period the maximum temperature November. While the minimum pH was at site I was recorded to be 24°C in June and recorded to be 8.9 in August. The maximum pH July. While the minimum temperature was recorded at Site II was to be 9.0 in November. recorded to be 12°C in November. The While the minimum pH was recorded to be maximum temperature at site II was recorded 8.20 in August. The maximum pH recorded at to be 24°C in July and August. While the site Ill was to be 8.3 in August. While the minimum temperature was recorded to be minimum pH was recorded to be 7.76 in June. 13°C in November.The maximum temperature The maximum pH recorded at site IV was to be at site Ill was recorded to be 23.93°C in 8.1 in August. While the minimum pH was August. While the minimum temperature was recorded to be 7.42 in June. recorded to be 13.1°C in November. The maximum temperature at site IV was Dissolved oxygen recorded to be 23.92°C in August. While the minimum temperature was recorded to be (Fig-4) During the study period the maximum 12.02°C in November. dissolved oxygen recorded at site I was to be 10.1 mg/1 in January. While the minimum Total Dissolved solids dissolved oxygen was recorded to be 8.0 mg/1 in November. The maximum dissolved oxygen (Fig. 2) During the study period the recorded at site II was to be 9.9 mg/1 in January. maximum total dissolved solids at site I were While the minimum dissolved oxygen was recorded to be 150mg/l in June. While the recorded to be 7.8 mg/1 in November. The minimum total dissolved solids were recorded maximum dissolved oxygen recorded at site Ill to be 58 mg/1 in August. Maximum total was to be 10.0 mg/1 in June. While the dissolved solids at site II were recorded to be minimum dissolved oxygen was recorded to be 135 mg/1 in June. While the minimum total 8.9 mg/1 in September. The maximum dissolved dissolved solids at site II were recorded to be oxygen recorded at site IV was to be 9.6 mg/1 in 51 mg/1 in August. Maximum total dissolved June. While the minimum dissolved oxygen solids at site Ill were recorded to be 135 mg/1 was recorded to be 7.8 mg/1 in September. in June. While the minimum total dissolved solids a site Ill were recorded to be 49 mg/1 in Free Carbon dioxide August. Maximum total dissolved solids at site IV were recorded to be 154 mg/1 in June. (Fig-5)During the study period the While the minimum total dissolved solids at maximum free carbon dioxide recorded at site 1 site IV were recorded to be 56 mg/1 in August. was to be 21.6 mg/1 in June. While the minimum free carbon dioxide was recorded to be 9.3 mg/1 in August. The maximum free 162 T.A. Qureshi carbon dioxide at site II was recorded to be hardness was recorded to be 150 mg/1 in 27.5 mg/1 in June. While the minimum free October at site II. While the minimum total carbon dioxide was recorded to be 12.5 mg/1 hardness was recorded to be 80.2 mg/1 in in August. The maximum free carbon dioxide November. The maximum total hardness was recorded at site Ill was to be 21.6 mg/1 in June. recorded to be 140 mg/1 in October at site Ill. While the minimum free carbon dioxide was While the minimum total hardness was recorded to be 10.5 mg/1 in August. The recorded to be 80 mg/1 in November.
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