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<br />, 0(14'7 <br /> <br />2.19 <br /> <br />N <br /><I' ',' . , <br />Effects on recreation usage were considered to result f,om the tim~ng(.pa <br /> <br /> <br />degree of drawdown of the reservoir during the peak season, effects on the <br /> <br /> <br />physical recreation facilities, and number of months with either greatly <br /> <br />reduced or greatly increased streamflows which,would hamper fishing. Reser- <br /> <br /> <br />voir drawdown during the summer recreation mont.hs 'in an average year also <br /> <br /> <br />showed the alternatives grouped into two groups; one, Alternatives 2, 4, and 5 <br /> <br /> <br />with 14 to 22 feet of drawdown, and two, Alternatives 3 and 6, through 10 plus <br /> <br />the Preferred, with less than 8 feet of drawdown. The corresponding decrease <br /> <br /> <br />in surface area as a result of the drawdown is 64 to 85 acres for group one <br /> <br />and 37 to 50 acres for group two. The alt.ernatives' fell into three groups <br /> <br /> <br />when evaluating the probability that pool levets would be at or below certain <br /> <br />levels, i.e., either 85,000 acre-feet or 52,000 acre-feet which were optimal <br /> <br /> <br />and minimal levels for'recreation recommended by the Forest Service, respec~ <br /> <br /> <br />tively. The probability of 'being below those pool levels was highest for <br /> <br /> <br />Alternatives 4 and 5, intermediate for Alternatives 2 and 3, and lowest for <br /> <br /> <br />Alternatives 6 through 10 plus the Preferred. ; The same pattern, of groups of <br /> <br />alternatives occurred when evaluating <br />reduced (less than 50 ~fs) or greatly <br /> <br />the number of months <br />, <br />increased (more t.han <br /> <br />with either greatly <br />250, 'cfs ~ stream <br /> <br />flows. Again Alternatives 4 and 5 had the mOat months with these extreme <br /> <br />stream jlows, closely followed by Alternatives 2, 3 and the Preferred, and <br /> <br /> <br />with Alternatives 6 through 10 having the fewe~t months of extreme stream <br /> <br />flows. summarizing all the recreation evaluat~ons, it was determined that <br /> <br />Alternatives 4 and 5 could caUSe a major <br />area, Alternatives 2,and,3 could cause a <br /> <br />'decre~se in recreation ,usage, in the <br />, -!. , ' <br />minor decrease, and all other alter- <br /> <br />natives would' have no significant, change. <br /> <br />.'!:.', ~, <br />Effects ~n sali~ity in the colorado"'Ri~~r were felt to be insignificant <br /> <br />for all alternat'lves because the flow ch<!-nges :at Cameo were so small (approxi- <br /> <br />mately 1 to 2 percent ,of Colorado River flows);. This same reasoning was the <br /> <br /> <br />rationale behind the determination that any p~oject eff~cta on the continued <br /> <br /> <br />survival of the threatened 9r endangered fish iin the Colorado River would not <br /> <br /> <br />be significant. (A separate biological asses$ment will be prepared for the <br /> <br /> <br />preferred alternative,which'will examine ,J.n detail the effects of flow changes <br /> <br /> <br />on threatened and endangered fishes at selected points in the Colorado River.) <br /> <br /> <br />None of the alternatives would have any signi~icant effects on riparian vege- <br /> <br /> <br />tation or on wildlife, or on the bald eagle o~ peregrine falcon. <br /> <br />; <br />