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<br /> e <br /> hiE <br /> wa <br /> re( <br /> me <br /> reI <br /> (1 <br /> th <br /> 7J <br /> nc <br /> fi~ <br /> et <br />~ m <br />. of <br /> te <br />, 1IIIl ej <br /> 1\ <br /> aJ <br /> b <br /> 1 <br /> 0 <br />,~-'- b <br /> ( <br />GO C <br /> 1 <br /> <; <br /> .. <br /> I <br /> I <br /> <br />e <br /> <br />eddies, pools, and runs. Bottom substrates are boulder, rubble, sand, <br />and silt. <br /> <br />METHODS AND MA TERIALS.-Continuous recordings of water <br />temperature were made at Echo Park and Island Park. Temperature <br />readings were also made at all stations with a pocket thermometer <br />when fish samples were taken. Water quality analyses (dissolved <br />oxygen, alkalinity, conductivity, pH, and turbidity) were made at <br />least once each visit to a sampling station. Water-flow, water tempera- <br />ture, and water-quality data were obtained from the U.S. Geological <br />Survey records for Greendale and Jensen, Utah, gauging stations. <br />From July, 1963, to October, 1966,667 collections containing 24,040 <br />fish were made. Most sampling was done from June through Septem- <br />ber, but several weekend collecting trips were made in April, May, <br />October, and November, Location of sampling sites was limited by <br />vehicle and boat access to the river. Sites for intensive sampling were <br />located at Lodore, Echo Park, Island Park, and Split Mountain. Supple- <br />mental sampling stations were located at Little Hole, Bridgeport, <br />Willow Creek, and Ouray (Figure 1). Fish populations were sampled <br />with various types of collecting gear, including gill nets (223 collec- <br />tions) , . seines of various mesh sizes (264 collections ) aad a boat- <br />mounted 230-volt a-c electric shocker (121 collections). Tow nets, food <br />strainers, and a modified scoop shovel with window-screen inserts were <br />used to collect larval and small fish (59 collections). <br /> <br />ECOLOGICAL IMPACT OF RESERVOIR OPERATION.-The <br />Green River below Flaming Gorge Dam has changed greatly since the <br />closure of the dam in late 1962. Chemical and physical characteristics <br />of the river immediately below the dam are now dependent upon <br />reservoir conditions at the level of the penstocks and upon the amount <br />of discharge, Downstream from the dam, tributary streams join the <br />river, which gradually attains pre-impoundment conditions. To assess <br />changes caused by the dam, chemical and physical features of the river <br />at increasing distances below the dam before and after impoundment <br />were compared. <br />Flow.-Before impoundment of the Green River by Flaming Gorge <br />Dam, flow was the lowest during the winter months and increased <br />gradually until peak run-off was reached in Mayor June. Following <br />peak run-off, the flow receded during the summer months and was <br />uniformly low during the fall months, Since completion of Flaming <br />Gorge Dam, however, characteristic high spring flows and low winter <br />flows have been replaced by a relatively stabilized seasonal flow pat- <br />tern (Table 1). Monthly and daily flow rates have varied because <br /> <br />30:) <br /> <br />1'-' IP"'''''''''''' <br /> <br />"_^.--",,,,__~,_.,,----,'.''''''''''_----'_''_r____~.>U <br /> <br />+- <br /> <br />/' <br /> <br />, <br />