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<br />Draft Fmal Completion Report to UDWR for Contract #93-1070. Amendment 3 <br /> <br />15 <br /> <br />amount of fish habitat during base flows (for example, Tennant, 1975). More recent work suggests that a suite of flows <br /> <br />are necessary to maintain ecological integrity of fish habitat rather than just protecting the habitat at base flows (Hill and <br /> <br />others, 1991). This approach is based on the assumption that habitat and nutrient availability for the fishes requires <br /> <br />mllintemlllr.e of the linkages of the stream with riparian, floodplain and upland areas. <br /> <br />Two philosophies have shaped the design of instream flow for Colorado River native fishes (Tyus, 1992). The <br /> <br />first philosophy is to prov ide minimum flows needed for species survival during periods of low river discharge. These <br /> <br />minimum flows do not ensure availability of optimal habitat, but seek to maintain and maximize the availability of <br /> <br /> <br />existing habitat. The second philosophy is to assist species recovery by increasing the availability of optimal habitats, <br /> <br />The latter philosophy requires that existing habitat be improved and that "lost" habitats (i.e., habitats that are no longer <br /> <br />formed and/or available as a consequence of flow regulation) be restored. "Optimal" habitat for fishes considers the <br /> <br /> <br />river under regulated conditions, inclucJing changes in river hydrology and the presence of exotic species, rather than <br /> <br />pristine river conditions prior to regulation. For example, a habitat that was optimal prior to river regulation may no <br /> <br /> <br />longer be optimal due to its use by a predatory species. For species recovery to occur in a system as altered, both <br /> <br /> <br />physically and biologically, as the Green River, the second philosophy is the only viable option for species recovery. <br /> <br />Other Flow Recommendation Research <br /> <br />ligon and others (1995) noted the need for multi-scale, interdisciplinary studies to quantify and mitigate the <br /> <br />downstream effects of dams. Hill and others (1991) integrated several standard assessment methods into a methodology <br /> <br /> <br />for determining the suite of flows necessary to mllintaip ecological integrity and applied their methodology to the Salmon <br /> <br />River at Whitebird, Idaho. They noted the need for four flow components: base flows for fish, and channel-, riparian- <br /> <br />and valley-process maintenance flows. Each of these flows inundated different ecosystems (for example, stream channel <br /> <br /> <br />vs. riparian), and combinations of methodologies were necessary to evaluate the appropriate flow regime for each <br /> <br /> <br />component. <br /> <br />The Physical Habitat Simulation system (pHABSIM), a part of the Instream Row Incremental Methodology <br /> <br /> <br />(IF1M) (Bovee, 1982), was used by Hill and others (1991) to quantify the low flow habitat needs of the targeted fish <br /> <br /> <br />species. IFIM was used to develop a relationship between stream discharge and the area of available habitat for a given <br /> <br /> <br />stream, particularly during summer low flows (Hill and others, 1991). Physical parameters for utilized microhabitat, <br /> <br />such as depth, velocity, cover, substrate and distance to cover, were measured by marking targeted fish species locations <br />