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<br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />M{~!O <br /> <br />Blue Mesa Dam Fish Passage <br /> <br />The majority (96\) of fish being lost from the reservoir were young <br />(~120 mm) kokanee salmon. Transport rates varied from .0001 to .1400 <br />fish/acre/ft(1.135e-04 fish/m') and also showed pronounced fluctuations <br />in fish passage between day and night. The passage of kokanee during <br />the spring/summer of 1994, 1995, and 1996 was estimated at 770, <br />60, 837, and 11,007 respectively. <br /> <br />The sieve netting program provided us valuable information concerning <br />fish passage during the peak flow period in 1994 through 1996. Year <br />round sampling would have been preferable, however, winter sampling <br />would have been unsafe and impractical because of icing. <br /> <br />These transport rates are similar to the estimates made by Van Buren <br />(et al. 1981). He estimated kokanee passage of 45,500 per year <br />through stocking records, mortality assumptions and estimated <br />proportion of standing crop in the downstream Morrow Point Reservoir <br />in 1977. These estimates were used to give magnitude of loss rather <br />than specific estimates and the 1977 loss was 5 to 7 percent of the <br />initial stocked numbers. <br /> <br />Fish passage rates were intended to help determine specific fish <br />losses due to FWS flow criteria. Unfortunately, several factors <br />complicated the analysis. The most confounding problem was the <br />abundance of water during the study. It's impossible to identify any <br />flows during 1994-1996 that can be specifically attributed to FWS flow <br />recommendations. Secondly, we have an extremely limited baseline <br />which does not include any low water years and we do not have any <br />information regarding transport rates or fish distribution in the <br />intake channel during the winter. <br /> <br />The shifting of winter releases to meet spring release criteria was <br />not necessary because of.the above average runoff. The most <br />concentrated sieve netting effort was during 1995 when run off was +75 <br />percent of normal. Figure 17 shows that flows at Grand Junction, <br />Colorado met or exceeded recommended minimal flow recommendations for <br />all years and in 2 of the 4 years actually surpassed maximum flow <br />criteria for May through August. Unfortunately, during this period of <br />time, it'S impossible to identify any releases that were made <br />specifically to meet FWS test flow criteria. There was simply an over <br />abundance of water in the system. <br /> <br />26 <br />