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<br />I. INTRODUCTION <br /> <br />An important goal of Region 6, U. S. Fish and Wildlife Service (FWS), is to <br />recover the endangered fishes in the Upper Colorado River Basin (UCRB). Three <br />species, the Colorado squawfish (Ptvchocheilus lucius), humpback chub (Gila <br />~), and bony tail chub (Gila eleaans), have been listed as endangered under <br />the Endangered Species Act of 1973. A fourth species, the Razorback sucker <br />(Xvrauchen texanus), is extremely rare and is a candidate for Federal listing <br />under the Act. The ultimate goal of the Recovery Implementation program in <br />the UCRB is to recover and delist the three endangered species and manage the <br />razorback so it will not need the protection of the Endangered Species Act <br />(FWS 1987). <br /> <br />Two tasks necessary for recovery of the endangered fish involves: <br />1) quantifying the amount of stream flow needed to support self-sustaining <br />populations and 2) legally protecting such flows. A necessary ingredient for <br />the Green River (part of the UCRB) is to refine the operation of Flaming Gorge <br />dam such that the continued survival and recovery of the endangered fishes is <br />insured. At present, an interim agreement between FWS and the Bureau of <br />Reclamation, initiated by larvae produced in the Yampa River entering the <br />Green River, constrains the summer releases from the dam not to exceed 2600 <br />cubic feet/second (cfs) near Jensen (RM 302) in an effort to increase <br />backwater areas for larvae and young-of-year squawfish (memorandum to: <br />Regional Planning Officer, Salt Lake City, UT from: Randall Peterson, 20 OCT <br />1987). Such contraints remain in effect until the end of October. <br /> <br />During the 1987 field season, the Upper Colorado River Basin Instream Flow <br />Team established two instream flow study sites within Segment 3 of the Green <br />River (Figure 1) in an attempt to determine flow needs for adult and spawning <br />life stages of Colorado squawfish, and adult Razorback suckers. This report <br />documents the results of the 1987 study efforts as well as the 1985/86 work at <br />a site within Ouray National Wildlife Refuge. <br /> <br />II. PHYSICAL HABITAT SIMULATION METHODOLOGY (PHABSIM) <br /> <br />MethodoloQV <br /> <br />The PHABSIM model output displays effects of streamflow alterations on <br />existing riverine fishery habitat (Milhous et al. 1984). The effects are <br />expressed through changes of an index value called weighted-useable-area <br />(WUA)--total surface area of the study area expressed as an equivalent surface <br />area of optimal fish habitat. <br /> <br />The model is based on the assumption that changes in physical habitat (WUA) <br />conditions can be predicted and are connected to a corresponding response of a <br />species with respect to such measureable streamflow dependant variables as <br />water depth, mean column velocity, and substrate. Thus it is intended for use <br />in situations where the flow regime and channel structure are the major <br />factors controlling the abundance and distribution of the fishery resource and <br />where field conditions are compatible with the assumptions of the methodology. <br />These assumptions state that steady flow conditions exist within a rigid <br /> <br />1 <br />