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Temporal variation <br />All fish.--Riverwide, mean total catch rate in fall 1994 was significantly higher (T-K, P < 0.05) <br />than in spring or fall 1995. Within some strata, mean total catch rates (all fish combined) were <br />fairly similar among sampling periods; in others, they were not. In downstream strata 1-6, <br />where catch rates were generally low, the mean total catch rate appeared to decline between <br />fall 1994 and fall 1995 in strata 2 and 3 (Figure 5), but not in other strata (no within-stratum <br />differences were significant; T-K, P < 0.05). In upstream strata, mean catch rates were <br />generally more variable through time. In Stratum 9, mean total catch rate was significantly <br />lower (T-K, P < 0.05) in spring 1995 than in spring and fall 1994 (Figure 6). Also, in <br />Stratum 12, mean total catch rate in spring 1995 was significantly lower than in fall 1994 and <br />fall 1995. The species with greatest catch rate variation over time appeared to be bluehead <br />sucker (variation by species was not statistically tested). <br />Prey-size fish.--In comparison to total fish, there was generally more temporal variation in <br />numbers of forage-size fish. Riverwide, the three primary sampling periods were significantly <br />different (T-K, P < 0.05) from one another in mean total catch rates of fish 100-300 mm TL. <br />For the four strata sampled during all four study periods (strata 4, 6, 9 and 11), catch rates in <br />fall 1994 were significantly higher than in the other three periods. <br />In downstream strata, variability in mean catch rate among sampling periods was largely <br />determined by fluctuations in numbers of young blueheads (Figure 7), the species with the <br />most forage-size individuals. However, mean total catch rates were not significantly different <br />among periods within any of the downstream strata. <br />In upstream strata, where several species had forage-size individuals, variability in catch rate <br />among sampling periods resulted from changes in abundance of each species, and each <br />stratum displayed a somewhat different sequence of changes (Figure 8). However, only in <br />strata 9, 10, and 11 were there significant differences among sampling periods. In Stratum 9, <br />catch rate in fall of each year was significantly higher than in the preceding spring. Increases <br />in both fall periods were due largely to increases in young flannelmouth and bluehead suckers. <br />In Stratum 10, the mean total catch rate in spring 1995 was significantly lower than in the <br />previous fall. This decline involved all species. In Stratum 11, the catch rate in fall 1994 was <br />significantly higher than in the other three periods. There, catch rates of forage-size bluehead <br />suckers were very low through all periods and catch rates of flannelmouth and white suckers <br />and roundtail chubs varied very little. Temporal changes in total catch rate in Stratum I 1 was <br />primarily influenced by changes in the number of salmonids (mostly mountain whitefish). In <br />fact, with the exception of fall 1994 when there was a pulse of young mountain whitefish, <br />catch rates of forage-size fish in Stratum 11 were comparatively low. Catch rates in the <br />Gunnison River study stratum were high during both fall sampling periods, and significantly <br />lower during the intervening spring (1995). There, catch rates of white suckers, roundtail <br />chub and trout (no mountain whitefish were captured in the Gunnison River) were essentially <br />stable between each fall, while numbers of young flannelmouth and bluehead suckers were <br />more varied. <br />13