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the river. A small outlet drained a flooded river bottom located to the <br />east. At low flows, a backwater was created by the eddy and water from <br />the river bottom was discharged near the upper end of that eddy. At <br />high flows, the eddy current from the main channel flowed into the lower <br />end of the backwater forming two small islands. <br />When flows stabilized at 800 and 4000 cfs, major habitats at each site <br />were staked and measured. Fish population changes were studied by <br />seining these various habitats in relation to the varying river flows. <br />No major difference was observed between the numbers of fish collected <br />at the DNM and Bonanza sites at both high and low flows. At the Ouray <br />site, the number of fish collected increased as the flow in the river <br />decreased. Colorado squawfish were not collected at any location which <br />conf irmed the findings of our YOY monitoring program since we expected <br />YOY Colorado squawfish to seek their preferred backwater habitats. Fish <br />data are preliminary at this time. Fish species and habitat associations <br />at different flows will be further compared to YOY monitoring data and <br />the 1984 habitat study. The results of these data comparisons will be <br />provided in the final report. <br />There was an approximate lag-time of 24 hours in water delivery from <br />Flaming Gorge Dam to the Bonanza site for the 4000 cfs discharge, and a <br />52 hour lag-time to the Ouray site. This Iag time was far shorter than <br />predicted by BR hydrologists during the 1980 peaking power exercise and <br />the water level fluctuation was also greater than predicted with a <br />change of water level between high and low flows as great at 1.79 ft <br />(0.6 m) at DNM, 2.12 ft (0.9 m) at Bonanza ,and 1.94 ft (0.6 m) at <br />Ouray. This water level change was rather constant with little dampening <br />effect noted. <br />28 <br />