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<br />. <br /> <br />,. <br /> <br />. ..... <br /> <br />_,-,,' ,"-..-_.e_\"~,~>.,..~.)_r"",",,",,~':.,". ,~,-~,_--'"'__-.",_^,A<~,_,,~ <br /> <br />- <br /> <br />e <br /> <br />e <br /> <br />.. <br /> <br />impoundment seasonal temperature pattern resembled the pre- <br />impoundment pattern, but temperatures after 1962 were slightly lower <br />in the summer months and higher in the winter months than before <br />impoundment (Table 2)_ <br />Maximwn summer water temperature, was inversely related to <br />stream flow. In 1963 and 1965, summer discharges from the dam were <br />relatively low (102-1,439 cfs; Table 1), and water temperatures from <br />Bridgeport downstream to Jensen approximated pre-impoundment con- <br />ditions (Table 2). The temperatures of the Green and Yampa Rivers <br />were nearly identical at their confluence at Echo Park in 1965 (Figure <br />2). In 1964 and 1966, however, sununer discharges from Flaming <br />Gorge Dam were higher (1,466-2,441 cms; Table 1), and water tem- <br />peratures were lowered a greater distance downstream. At Echo Park <br />the Yampa River inflow was much warmer than the receiving Green <br />River waters (Figure 2). In these years the Green River at Island Park <br />had warmed considerably (Figure 2) but had not reached pre- <br />impoundment mean temperatures at the end of the study area at <br />Jensen (Table 2). <br />The inverse relationship between discharge and water temperature <br />was especially apparent at Little Hole and Bridgeport, 7 and 17 miles <br />below the dam, respectively (data from Utah State Department of <br />Fish and Game recording thermometers). During the summers of <br />1963 and 1965, maximum water temperature at Little Hole was 63 F <br />and 59 F, respectively, while during summers of 1964 and 1966, maxi- <br />mwn temperature was 53 F and 55 F. At Bridgeport, maximwn swn- <br />mer water temperature in 1963 and 1965 was 76 Fand 68 F, respec- <br />tively, and in 1964 and 1966, 58 F and 60 F. <br />Water Chemistry.-A comparison of pre-impoundment and post- <br />impoundment water chemistry data from USGS records on mean an- <br />nual values of bicarbonates, total dissolved solids, specific conductance, <br />and pH at Greendale and Jensen did not reveal any permanent change <br />in these aspects after dam completion (Table 3). In the 1963 water- <br />year, the first year after dam closure, however, the values of bicar- <br />bonates, total dissolved solids and specific conductance were much <br />higher than in the other years. These high values were probably the <br />result of the extremely low flow of that year (mean flow =231 cfs) <br />due to the fIlling of Flaming Gorge Reservoir. In general, the water <br />chemistry determinations made during the fish collections in the pres- <br />ent study gave results similar to those reported ~y pre-impoundment <br />surveys. <br />Suspended Sediment and Turbidity.-The Green River at Green- <br />dale was nearly sediment-free but increased in silt load progressively <br /> <br />303 <br /> <br />Ii <br />11 <br />L <br />,! <br />,1 <br /> <br />'1 <br /> <br />" <br /> <br />+- <br /> <br />J <br /> <br />, <br />