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<br />0061 <br /> <br />3.13 <br /> <br />".II, . <br />: " ;. J i <br /> <br />volj1Jlles ranging between 50,000 acre-feet and 80iOOO acre,..feet usually occur in <br /> <br />the winter. The maKimj1Jll depth of the reservoir 'is 276 feet with yearly fluc- <br /> <br /> <br />tuations in water levels ranging between 20 and 60 feet. MaKimum surface <br /> <br /> <br />water te~peratures of 640 to 680 F usually ocpur in late July or August, wh~le <br /> <br /> <br />bottom temperatures during this sa~e period ran~e from 400 to 500 F (Finnell, <br /> <br /> <br />1977; Nesler, 1979). The reservoir usually becqmes stratified between May and <br /> <br /> <br />July with a thermal gradient formed at depths o~ 12 to 30 feet (Nesler, 1979). <br /> <br /> <br />Due to an abundance of gypSj1Jll in the reservoir basin, the water chemistry is <br /> <br />characterized by relatively high alkalinity, hardness, pI!, and conductivity <br /> <br /> <br />(Finnell, 1977; Yahnke, 1982). Measured nutrient levels are relatively low in <br /> <br /> <br />the reservoir, maKimj1Jll concentrations usually occur in the spring or fall near <br /> <br /> <br />the bottom; minimj1Jll values usually occur in July (Nesler, 1979). <br /> <br /> <br />The configuration of the reservoir is infl~enced by the steep shoreline <br /> <br /> <br />and the location of tributaries. The north shore of the reservoir is modera"" <br /> <br /> <br />tely steep and has four large bays (Ruedi/Pond Creeks, Hanson Gulch, Smith <br /> <br /> <br />Creek, and Freeman Creek). These bays provide important habitat for aquatic <br /> <br /> <br />organisms as a result of more diverse bottom sUQstrates and eKtensive <br /> <br /> <br />macrop~yte growth. In contrast, the south shor~ of the reservoir is steep <br /> <br />with fewoperennial tribut~ies. <br /> <br /> <br />The section of the Fryingpan River in the project study area is a 14-mil,e <br /> <br /> <br />segment eKtending from Ruedi Dam at an elevation of 7,766 feet downstream to <br /> <br /> <br />its confluence with the ~aring Fork River near,Basalt at an elevation of <br /> <br /> <br />approKimately 6,600 feet (Figure 3,2). GeneraltY, the physical and chemical <br /> <br />I <br /> <br />characteristics of this section of the Fryingpa1 River represent good quality <br /> <br /> <br />habitat for trout. Based on a system that rate$ important habitat features in <br /> <br /> <br />Rocky Mountain trout streams (Binns, 1982), the!Fryingpan River ranks as,a <br /> <br /> <br />good quality stream for most attributes (Table 3.7). A brief description of <br /> <br /> <br />the more i~ortant 'physical/chemical characteristics is provided below. <br /> <br /> <br />Of the physical and chemical. parameters mei!.sureC! in the Fryingpan River <br /> <br /> <br />(Appendix B, Table B.1), temperature appears tojbe the only potential limiting <br /> <br />, <br />factor to the fisheries. Due to the deep relea~e of water from the reservoir, <br /> <br /> <br />mean monthly summer temperatures in the river h~ve decreased about 150 F at <br /> <br />the dam site and 90 F near Basalt compared to Pre-dam records (Nehring and <br /> <br /> <br />Anderson, 1981). Low water temperatures in the spring (370 F to 410 F) <br /> <br />> <br />