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c - <br />stage where the species was experiencing the mast damaging problem, 3) <br />What flow condition or flow related conditian was impacting the critical <br />life stage, 4) What changes in flows had occurred at the critical areas <br />from past pre-development times to the present and 5) What flows are <br />needed and at what time at the critical areas to assure survival of the <br />target species? <br />The above determinations were made based upon findings from the <br />field, laboratory, hatchery and contracted studies under this project. <br />Analysis of present, past and needed flow levels were made using <br />the USGS flow records, 1960-1980, and the CRSS model developed by BR <br />which predicted virgin flow conditions and developed flow conditions <br />{see Appendix B for details of flow partitioning). Weighted Useable <br />Area (WUA) for squawfish YOY and humpback adults were related to flow at <br />key areas to assist in analysis of present, past and future flow needs <br />of the target species. <br />What we have determined from this study is that for Colorado <br />squawfish and humpback chub there are a number of critical areas in the <br />Upper Colorado River system (Table 2). For Colorado squawfish the <br />critical life stage is the actual spawning area including egg survival, <br />and YOY rearing areas. For humpback chub the critical life stage is the <br />actual spawning period. We could not identify what the critical life <br />stage of the bonytail chub was, but believe it may be more than one <br />stage. The razorback sucker was experiencing recruitment problems with <br />survival of larvae believed to be the primary area of impact. <br />In analyzing the needs and problems of Colorado squawfish, we had <br />to consider large sections of river and deal with a highly mobil fish <br />species. In contrast, when we evaluated humpback chub needs, we only <br />had to consider small isolated habitats where all Life stages were <br />occurring. Razorback suckers also seemed to be somewhat conf fined and <br />only a few areas are probably important for su rvival. Not enough information <br />has been acquired on the bonytail chub to determine how broad or narrow <br />the area of consideration should be for this species. Right now we are <br />proceeding with a hatchery propagation program to prevent the species <br />from becoming extinct. <br />Basic flow recommendations are made for average monthly flows and <br />are presented in Table 2. Minimum instantaneous flows should at no time <br />drop below the minimum recommended for the designated period of time and <br />the overall monthly average 'should at least fall in the range presented. <br />For humpback chub in Black Rocks and Westwater Canyons, an evaluation <br />of hybridization needs to be conducted. By WUA and 1981 field data, we <br />can show that spawning took place and adult habitat is available at <br />2,000-3,000 cfs. There is a possible need for spawning separation of <br />roundtail and humpback chub and with low flows in the spring this <br />hybridization problem may be aggravated. Temperature is believed to be <br />a possible factor in separation of the spawning time of roundtail and <br />humpback chub and when the river warms to Quickly in the spring spawning <br />