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Stream-flow needs of native fishes in the Yampa River are influenced by many <br />factors including time of year, life history stage, and flow requirements of <br />sympatric species. Reproductive activities of the target fishes, (i.e., <br />Colorado squawfish, razorback sucker, and humpback chub) are closely associated <br />with flow, temperature and other parameters associated with normal spring <br />runoff conditions. Alteration of this hydrologic event may affect initiation <br />of Colorado squawfish and razorback sucker migrations, and spawning of these <br />and other native fishes, including bluehead (Catostomus discobolus) and <br />flannelmouth (C. lat_ ipinnis) suckers. Maintenance of low, stable flows in late <br />summer and fall is conducive to growth and survival of young Colorado <br />squawfish, and young of other species as well. Stable winter flows through ice <br />breakup are considered important to overwinter survival of young and adults in <br />some locations. Abrupt fluctuations of water level from late summer to spring <br />could strand larvae, stress adults, and influence reproduction. Life histories <br />of target fishes are associated with natural flow events that comprise the <br />Yampa River hydrograph. <br />Quantification of Instream Flows <br />The Service, and others, have expended substantial amounts of time and manpower <br />in making instream flow recommendations using physical simulations of habitats, <br />in developing temperature and flow models, in analyzing stream sediment-water <br />flow relationships using historic and current flow patterns, and others. <br />Physical modelling to date has not demonstrated predictive capability relative <br />to cause-effect relationship with the distribution and abundance of the <br />endangered fishes in the Green River basin (Rose and Hahn 1989). This is <br />attributed to the variability of the environment (e.g. seasonal fluctuations in <br />discharge, temperature, food base, species abundance, etc.) and interactions <br />among environmental variables; logistical problems associated with studying <br />fishes in large, turbid rivers; changing environmental conditions during study <br />periods; and the introductions of nonnative fishes. In addition, where <br />physical habitats have been measured, their use by the fish may only reflect <br />temporary, seasonal, or marginal habitat use. Thus, caution must be exercised <br />in determining flow requirements of fishes in decline. Ecological data and <br />professional judgement must be recognized as critical in interpreting fish <br />requirements in complex systems. <br />Flow recommendat"ions to provide needed habitat and to satisfy life history <br />requirements of endangered fishes in the Yampa-Green River system must be <br />approached with great caution. Decline of the Colorado squawfish in other <br />rivers of the upper basin apparently continues, as evidenced by very low <br />numbers of young fish, and failure in detecting spawning areas. Recruitment of <br />the razorback sucker is not sufficient to sustain the species anywhere at this <br />time, but higher numbers of the fish, and the identification of two spawning <br />areas in the Yampa and Green rivers offer some promise for recovery. <br />Experimentation with flows to which the endangered fishes may not respond <br />favorably should be conducted elsewhere; not in the Yampa River. A reduction <br />in the 1989 year-class of Colorado squawfish in the upper Green River suggests <br />that additional factors may influence successful recruitment in this species <br />even if flow conditions in nursery habitats are presumably adequate. This is <br />indicative of the precarious existence of the endangered Colorado River fishes. <br />2 <br />