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Trout Growth <br />In 1978, the penstock inlets of Flaming Gorge Reservoir were <br />modified to permit selective withdrawal of warmer, epilimnetic water from <br />the reservoir. As a result, growth of rainbow and cutthroat trout in the <br />tailwater increased to levels above those recorded any time prior to <br />1978. Annual growth increased approximately 3-fold over that measured in <br />1976. Consequently, trout fingerlings stocked at 100-125 mm (4-5 inches) <br />total length (TL) in May began contributing to the creel during their <br />first summer at large. In contrast, the 1976 year class of fingerlings, <br />stocked prior to the penstock modification, required two years in the <br />tailwater to reach a catchable size. Prior to the modification, growth <br />was fastest at Browns Park, the downstream extremity of the Utah <br />tailwater, and slowest at the dam. Following penstock modification, <br />growth had increased at all stations, but fastest growth was registered <br />at the tailrace. <br />The modification has, therefore, met the objectives for enhanced <br />trout growth set forth in the 1975 Environmental Assessment of the <br />penstock modification project. Growth is now comparable to that in other <br />productive western tailwaters, such as the Bighorn River below Yellowtail <br />Dam and the Beaverhead River below Clark Canyon Dam, Montana. <br />The increase in growth undoubtedly resulted from the direct effect <br />of the warmer water temperatures in summer on trout metabolic rate. <br />Other indirect mechanisms may also have been involved. Benthic <br />invertebrates, a major food for trout, increased in diversity and <br />abundance. Warmer temperatures, and the more natural synchronization of <br />temperature and photoperiod cycles, contributed to increases both in <br />macroinvertebrate biomass and species diversity. <br />-2-