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SYNTHESIS <br />This study was unable to show that fluctuating winter flows due to releases from Flaming Gorge <br />Dam to meet hydropower needs added additional stressors to overwintering young Colorado pikeminnow. <br />Several investigators have hypothesized that winter operations of Flaming Gorge Dam influence age-0 <br />fish survival (Carlson and Muth 1989; U. S. Fish and Wildlife Service 1992; Valdez and Cowdell 1996; <br />Haines et al. 1999). A 24-hr hydropower release from Flaming Gorge Dam during this study fluctuated <br />about 600 to 800 cfs, producing stage changes at the Jensen gage <0.1 m (93 miles downstream of <br />Flaming Gorge) and about <0.01 m at the Ouray bridge. These stage changes had only minimal affect on <br />backwater habitats and were limited to the upper end of the nursery area. These flow fluctuations did not <br />alter the physical morphology of backwaters studied in the Ouray Backwater Complex. The formation of <br />ice jams, however, had a far greater affect on the backwater nursery habitats, increasing stage by 0.75- <br />1.50 m, resulting in the transformation of many backwater habitats into flow-through areas. The role of <br />fluctuating winter flows from Flaming Gorge Dam in the creation of ice jams is unclear. Valdez and <br />Cowdell (1999) speculated that fluctuating winter flows may dismantle ice cover which acts an insulator, <br />allow the creation of frazil, and may result in ice jams that increase river stage several meters and <br />inundate many backwaters. Hayse et al. (2000), however, found that fluctuating winter flows from <br />Flaming Gorge Dam did not dismantle ice cover thereby promoting formation of frazil ice and ice jams. <br />Whatever the cause, it is likely that ice jams form at several locations on the middle Green River nursery <br />area in most years (Valdez and Masslich 1989; Valdez and Cowdell 1999; Hayse et al. 2000). <br />As a result, stage changes due to ice jams and frazil ice formation may force young fish to <br />redistribute and seek alternate low-velocity channel-margin habitats (Muth et al. 2000). Young Colorado <br />pikeminnow prefer low velocity backwater habitats (Tyus and Haines 1991); when these habitats are <br />inundated, the fish abandon them and move to other low velocity habitats, sometimes to other backwaters <br />several miles away and sometimes to low-velocity micro-habitats within close proximity of the inundated <br />xvi