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950 <br />OSMUNDSON ET AL. <br />TABLE 3.-Length-weight regression coefficients (SEs <br />in parentheses) used in calculation of relative condition of <br />Colorado squawfish captured from the Colorado River <br />during 1990-1994. Relative condition (Kn) was expressed <br />as Kn = 100 x M?/Me, where M, is the observed mass <br />(g) and MQ is the expected mass (g) as calculated from <br />log10Me = log10(length)-m + b. Length is measured in <br />millimeters. <br />Month N Slope (m) y-Intercept (b) R2 <br />Apr 81 3.17326 (0.061) -5.54824 (0.167) 0.972 <br />May 257 3.25981 (0.030) -5.77281 (0.083) 0.978 <br />Jun 128 3.20661 (0.038) -5.60323 (0.010) 0.983 <br />120 <br />90 <br />related to fish size. Mean displacement between <br />consecutive captures was 43.8 km (SE = 15.5; N <br />= 17) for Colorado squawfish less than 500 mm <br />(at time of second capture), 13.3 km (SE = 3.5; <br />N = 68) for fish 500-599 mm (between first and <br />second captures), and 3.1 km (SE = 0.8; N = 34) <br />for fish 600 mm and longer (at first capture). Mean <br />displacement was not significantly different be- <br />tween fish 500-599 mm and those 600 mm and <br />longer, but displacements for both groups were <br />significantly less than for fish smaller than 500 mm <br />(ANOVA, Tukey-Kramer multiple comparison, P <br />< 0.05). Also, mean displacement of fish 550 mm <br />and longer (7.5 km; SE = 2.5; N = 70) was sig- <br />nificantly less (t-test, P = 0.008) than that of fish <br />smaller than 550 mm (33.6 km; SE = 10.2; N = <br />30). The proportion of total displacements con- <br />sisting of long-distance displacements (>10 km) <br />was significantly different between all size-groups <br />(test of proportions, all P < 0.003) and was in- <br />versely related to length: for fish smaller than 500 <br />mm, 59% of displacements were farther than 10 <br />km; for fish 500-599 mm long, 28%; and for fish <br />600 mm and longer, 6% were long distance. <br />Body Condition <br />Mean relative body condition (K„) of Colorado <br />squawfish varied with river reach and fish length- <br />class (month-specific constants are shown in Table <br />3). In the lower reach, fish condition declined with <br />increasing length (Figure 6): mean condition fac- <br />tors of fish 500-599 and 600-699 mm were sig- <br />nificantly lower (ANOVA, Tukey-Kramer multi- <br />ple comparison, P < 0.05) than those of fish 200- <br />299, 300-399, or 400-499 mm. Also, mean K. of <br />fish 400-499 mm was significantly lower than that <br />of fish 300-399 mm (P < 0.05). In contrast, body <br />condition of upper-reach fish increased with fish <br />length, and mean K. was highest in fish 700-799 <br />mm. Mean K. of fish 600-699 mm was signifi- <br />cantly higher than those of fish 400-499 or 500- <br />115 <br />C 110 <br />O <br />a <br />C 105 <br />O <br />U <br />> 100 <br />95 <br />Upper reach <br />85 11 1 <br />200-299 400-499 600-699 800-899 <br />300-399 500-599 700-799 <br />Length-class (mm TL) <br />FIGURE 6.-Mean relative condition (K) of Colorado <br />squawfish by length-class and Colorado River reach. Error <br />bars represent 95% confidence intervals. <br />599 mm, and mean Kn of fish 700-799 mm was <br />significantly higher than that of fish 600-699 mm <br />(P < 0.05). <br />Mean Kn began to differ between reaches once <br />fish attained 500-599 mm. However, reach com- <br />parisons could not be made for all length-classes <br />because no fish 200-299 mm and only two 300- <br />399-mm fish were captured in the upper reach, and <br />in the lower reach, no fish 700 mm or larger was <br />captured. Significant differences were detected be- <br />tween reaches within length-classes of 500-599 <br />and 600-699 mm (t-test, P < 0.0004 for both), <br />but not for fish 400-499 mm long (P = 0.14). <br />Relative Abundance of Forage Fish <br />Small fish (<100 mm) densities in backwaters <br />were generally higher in the lower reach than in <br />the upper reach: mean annual CPUE (fish per area <br />seined) during fall surveys (1991-1995) was 5.7/ <br />m2 (SE = 0.4) in the lower reach and 3.3/mz (SE <br />= 0.4) in the upper reach. Results from ANOVA <br />and multiple comparison (obtained by using log- <br />transformed data) indicated that the difference for <br />the 5-year period was significant (ANOVA, P < <br />0.0000001); however, within years, the only sig- <br />nificant difference was in 1994 (Tukey-Kramer <br />multiple comparison, P < 0.05). Three introduced <br />species, red shiner Cyprinella lutrensis, fathead <br />minnow Pimephales promelas, and sand shiner No- <br />tropis stramineus, together made up 84-99% of all <br />fish within annual reach samples. Though fish den- <br />sities within backwaters were lower in the upper