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<br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br />from field readings taken during this, investigation. Flow records are from <br />routing models from flow gauges at Green River (for Green River) and Cisco (for <br />Colorado River), NOAA Colorado Basin River Forecast Center. <br /> <br />Further analyses are needed to determine if spawing time of Colorado squawfish <br />in the Cataract Canyon Region is established be water temperature, flow, or <br />both. The histograms in Figure 3 indicate that spawning occurs during an <br />increase in water temperaturres and a decrease in flows. It is hypothesized <br />that spawning time may be established by occumulated temperture degree days, <br />but that analysis has not been Operformed on these dates. Also, a relationship <br />between temperature, flow and spawning time may not exist for ~{aY captured in <br />the Cataract Canyon Region, because these fish probalby originate from dif- <br />ferent areas and spawning events that may be influenced by envi ronmental <br />factors other than those recorded in Cataract Canyon. <br /> <br />HL Survival of Year Classes. Kaeding et al. (1985) hypothesized that <br />squawfish in the Colorado River, hatched relatively late in the summer, enter <br />the winter smaller and less able to survive into the following spring. The <br />analysis of hatching dates, as presented in Figure 3, combined with lengths and <br />CPE for yay in fall compared to the following spring before runoff ,provides <br />data to partly test this hypothesis. Unfortunately the current investigation <br />is not scheduled to collect much data on these fish in the spring, and so, CPE <br />and lengths of the previous year class are based on sampling in late June and <br />July. <br /> <br />As the first phase of this analysis, we established the peak hatching dates <br />from back-calculations presented in Figure 3. Although hatching dates for the <br />three years examined generally occurred over a two-month period, the peak of <br />hatching occurred in early July in 1985, in early August in 1986, and in late <br />July in 1987. <br /> <br />The second phase of this analysis deals with the relative lengths of the yay. <br />A comparison of average lengths of yay captured during comparable sample dates <br />in 1985, 1986, and 1987 (Table 21, Figure 4), shows that the individuals of the <br />1985 year class (hatched early) were larger than those of the 1986 year class <br />(hatched late). yay collected during comparable trips 3, 4, and 5 showed an <br />increasing difference in average lengths of up to 16.5 rom. The 1985 sample for <br />trip 6 (n=8) is considered too small to provide reliable average. This <br />comparison suggests that the progeny of the 1985 year class entered the winter <br />as larger fish than the 1986 year class. A comparison of the 1985 and 1986 <br />year classes with the 1987 year class shows a similar correlation between <br />average length of yay and relative hatching time. The peak hatching time in <br />1987 was intermediate between the two previous years classes, as were the <br />average lengths of yay. Since the sample dates differed slightly for the three <br />years, average lengths of yay are plotted in Figure 4. <br /> <br />The third phase of this hypothesis deals with CPE of yay in the early summer of <br />the year after hatching (Le., the fish are 10-11 months of age). Ideally, <br />this sampling should be conducted in the pre-runoff period, during March-April <br />(Le., the fish would be 7-8 months of age) when the yay are using the rela- <br />tively warmer backwater before these habitats are inundated by runoff. <br /> <br />21 <br />