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<br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br />summer/fall/winter flows. High spring flows maintain channel and habitat diversity, flush <br />s from spawning areas, rejuvenate food production, and form flooded bottomlands used <br />ry backwaters. High spring flows also disadvantage nonnative fishes (Hoffnagle et al. <br />1999), reducing predation and competition. Low base flows also increase shoreline food <br />production. <br />3.1.2 Habitat Alteration <br />It is believed that the four endangered fishes once inhabited the larger streams ofthe <br />Colorado River Ba . m Wyoming and Colorado to northwestern Mexico. The historic <br />abundance and dist . n of the species were never documented, but a precipitous decline <br />occurred in known popu ations concurrent with extensive habitat alterations. These alterations <br />led to a loss of the contiguous complement of habitats used by the various life history phases of <br />the species. Since 1905, numerous man-made dams have been constructed throughout the <br />Colorado River Basin, fragmenting habitat and blocking migration corridors. These dams have <br />also reduced river flow, altered temperature and flow regimes, trapped sediments and nutrients, <br />changed water quality, and created rese s as a source of nonnative fishes (Maddux et al. <br />1993). In the lower basin, 15 major d_ s e restricted fish movement through the Colorado, <br />Gila, Salt, and Verde rivers since completion of Hoover Dam in 1935; other dams on the <br />Colorado River include Davis, Parker, Palo Verde Diversion, Imperial, and Laguna. Glen <br />Canyon Dam approximately divides the lower from the upper basin and also is a barrier to fish <br />movement. <br /> <br /> <br /> <br />Seven barriers are identified in the upper basin abov <br />Kaeding 1990) and five on the San Juan River (Masslich and <br />of the upper basin structures are classified as medium or high- <br />seasonal barriers to fish movement. The Price-Stubbs Diversion presently prevents upstream <br />movement of fish in the upper Colorado River; a second structure, the Government Highline <br />Diversion, is immediately upstream. Passage by these diversions could reestablish contiguous <br />habitat, expand the range of several native fish species, and allow greater opportunities for <br />recovery. The Redlands Fishway on the lower Gunnison River has already been mo e for <br />fish passage, and the Gunnison River provides additional habitat opportunities. <br /> <br /> <br />Canyon Dam (Burdick and <br />en 1996, Holden 1999). Five <br /> <br />13 <br />