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<br />4 <br /> <br />High il~~ test <br />A fourth objective was added after the first year of study <br />had been completed. This was to monitor the effects on the fish <br />(in terms of microhabitat) during a proposed test of winter high <br />flow releases during 1982. <br /> <br />Fish microhabitat data were again collected by species, life <br /> <br />stage, . and physical activity as was done in 1981. The data were <br /> <br />stratified into three time periods during the winter 1982: prior <br /> <br />to high flows (January), during high flows (February), and after <br /> <br />high flo~s ~:Idrch - April). <br /> <br />~te description <br /> <br />Phys i c a 1 <br /> <br />The study area was defined as extending from the dam down- <br /> <br />stream 18 km to Red Creek (Figure 1). Microhabitat data were <br /> <br />collected primarily from the first 7 km below the darn. <br /> <br />Releases <br /> <br />frrnn the dam normally fluctuate from 800 to 4300 cfs (22.6 - <br />... <br />121.8 m3/sec). An intensive study site was selected by USBR per- <br />sonnel approximately 0.4 km below Pipe Creek (Figures 1 and 2). <br /> <br />They established and mapped ten transects across this site to <br /> <br />provide the physical data for the IFG-4 hydraulic model. These <br /> <br />same transects were also used to provide vegetative infon~ation. <br /> <br />Water temperatures in the river are regulated during the <br /> <br />summer to 13 C at the dam by adjustable penstock intakes. During <br /> <br />the winter, temperatures drop to a minimum of 4 C at the dam. <br />The stream banks consist primarily of rock and rubble with <br /> <br />little riparian vegetation. <br /> <br />The banks are usually stable with <br />