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reflective of the needs or preferences of the species under optimum conditions more likely to allow <br />the population to thrive. Thus, our recommendations are based on the habitat-selection behavior of <br />adult squawfish observed during the higher, somewhat more normal flow conditions. <br />Ranking Flow Levels by Weighted Area of Preferred Summer Habitats (Objective No. 3) <br />Among the moderate discharge levels (1,240, 1,530, 1,630 and 2,870 cfs) a flow of 1,630 cfs <br />provided both the highest total area and the highest total weighted area of the habitat types <br />preferred at those flow levels (Fig. 16). Total weighted area at 1,630 cfs was 26% higher than at <br />the discharge level with next highest TWA value (1,530 cfs). The highest weighted area occurred <br />at a discharge of 557 cfs. However, because these habitats are not preferred when the water is that <br />low, weighted area of backwaters, eddies and pools is irrelevant at the lower flow levels. Based on <br />this analysis, 1,630 cfs is the best flow level during summer. <br />For slow and fast runs, preferred at low flow levels, total area and total weighted area increases <br />with increasing discharge. However, as before, weighted area at moderate discharge levels is <br />irrelevant because slow and fast runs are preferred only at the lower flow levels. Of the discharge <br />levels studied here, 810 cfs provided a 20% increase in weighted area over that at 557 cfs (Fig. 16). <br />We recommend a minimum of 810 cfs during drought years. <br />Winter Habitat Use and Availability <br />For winter, no comparison could be made between habitat use during low-flow and moderate-flow <br />conditions. All winter, habitat-use data were collected during moderate-flow levels because in <br />winter no water is withdrawn for irrigation, and upstream dams often release additional water to <br />increase reservoir storage capacity in anticipation of spring runoff. When habitat-use data were <br />collected (November-March 1986-1988), flows in the 15-mile reach were 1,654-3,452 cfs <br />(Appendix Table IX). <br />Adult Colorado squawfish used fewer habitat types during winter than during summer (Fig. 17). In <br />the study sites where fish were located during winter, no rapids or gravel-pit ponds were available. <br />Also, unlike summer, fast runs and riffles were not used in winter. Colder water temperatures <br />resulting in lower metabolic rates during winter may account for avoidance of high velocity sites. <br />During winter, Colorado squawfish were located largely in pools (53%) and backwaters (27%). <br />Again, to determine availability, percent total area of each habitat type was averaged across those <br />flows that most closely approximated those that occurred at the time when habitat use data were <br />collected. Maps made at 1,630 and 2,870 cfs were used to calculate mean percent area Again, <br />slow runs (51 %) and riffles (23%) accounted for about 74% of all water surface area at this flow <br />range. <br />Winter Habitat Preference (Objective No. 2) <br />As in summer, backwaters, eddies and pools were the preferred types of habitat in winter (Fig. 18). <br />Unlike summer, however, pools rather than eddies were the most preferred type. The preference <br />rating (mean difference between use and availability) for pools was twice that for backwaters and <br />five times higher than that for eddies. Slow runs were also used but were not preferred. <br />33