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Last modified
7/14/2009 5:02:34 PM
Creation date
5/20/2009 3:39:59 PM
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UCREFRP
UCREFRP Catalog Number
8251
Author
Rakowski, C. L. and J. C. Schmidt.
Title
The Geomorphic Basis of Colorado Squawfish Nursery Habitat in the Green River Near Ouray, Utah.
USFW Year
1996.
USFW - Doc Type
#93-1070,
Copyright Material
NO
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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 />
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