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<br />~ <br /> <br />--...., <br /> <br />MAYNES,BRADFORD&SHPS <br /> <br />ID:303-247-8827 <br /> <br />APR 07'94 <br /> <br />14:34 No.016 P.19 <br /> <br />2 <br /> <br />co.petition and predation by introduced species. All of these <br />pro.ising .easures are outside the present scope of this draft EIS. <br />Vestern encourages Recla.ation to investigate the potential <br />effectiveness of these measures to help recover endangered fish. <br /> <br />. Flow modification can assist in beach maintlnance, at least in the <br />short tenl. Long-tenl maintenance w;ll require mar. than changes in <br />daily operations. Vestern believes that non-operational options such <br />as vegetation .anage..nt, human use restrictions, raft mooring <br />r.strictions, protection with native materials, and selectivl <br />sedi.ent augmentation Rerit serious consideration. Combined with <br />operational controls, thlY offer the most effective means for beach <br />stabilization and maintenance. Such options have significant <br />flexibility advantages; beaches could be placed or maintained where <br />they are most needed. <br /> <br />3. Because of its creation late in the process, the preferred alternative and <br />its effects have not been studied with the same level of intensity as the <br />other alternatives. Unifo~ treatment of alternatives is essential for <br />.ffective comparison of alternatives, and is reqUired by compliance with <br />section 1502.14(a) and (b) of the Council on Environmental Quality <br />regulat.ions. <br /> <br />. Vestern is troubled by the process which lead to the selection of the <br />preferred alt.rnative. After near total consensus on a preferred <br />alternative was reached by the cooperating agencies, a new preferred <br />alternative was created based on the draft Biological Opinion without <br />input fro. ihe other cooperating aglncies. <br /> <br />. lhe nlw preferred alternative is designed to postpone a jeopardy <br />opinion with regard to endangered fish. However, since most of the <br />factors limiting endangered fish are not related to flows, the <br />alternatives have very similar effects on endangered fish. The new <br />preferred alternative calls for test flows very different than thosl <br />we have slln tn the past, and we are concerned that the possibll <br />advlrse impacts to endangered ftsh are not known. Absent signtficant <br />offsetting beneftts to endangered fish, the increased risk of impact <br />is not Justifi.d. <br /> <br />. Available scientific evidence does not demonstrate that the new <br />preferred alternative wtll provide better conditions for endangered <br />ftshes than the consensus alternative deftned by the NEPA process. <br />Solid scientific information demonstrating definite benefits for <br />endangered fish at least equal to the negative impacts to other <br />resources should be available before this alternative is selected as <br />the preferred alternative. <br /> <br />. Much of the emphasis behind the development of the present alterna- <br />ttves was on sediment, as it WIS agreed that sediment was the key <br />resourcl tn the system, and that measures to conserve sediment <br />generally benefitted other resources. We are concerned that the lat. <br />shift tn emphasis to endangered fish may have rendered some provi- <br />sions or assumptions of the alternatives obsolete. <br />