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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 />Samples were preserved in 70% ethanol and transported to BIO/WEST laboratories for processing <br />and analysis. <br /> <br />4.0 RESULTS <br /> <br />4.1 Summary of Fish Collections <br /> <br />A total of 14 species of fish representing 5 families were captured in the Dolores River in 1990 <br />(Table 4). This list is similar to that reported by Holden and Stalnaker (1975) and Valdez et al. <br />(1982) except that black bullhead and bluegill were not reported in 1975 and bluegill were not <br />reported in 1982. White sucker (Catostomus commersoni), rainbow trout (Oncorhynchus mvkiss) and <br />brown trout (Salmo trutta) were report by Valdez et al. (1982) but were not captured in 1990. <br /> <br />Table 5 presents a summary of fish species captured in 1990 by trip and total for the year. Table 6 <br />presents a summary of life stages captured for each species in 1990. As percentage of total catch, <br />the most common species of fish captured in 1990 were red shiner (37.5), fathead minnow (23.6) and <br />sand shiner (22.7). These three non-native fish comprised 83.8% of the catch. Of the 14 species <br />reported, 10 are non-native and 4 are native or endemic to the Colorado River system (Tyus et aI. <br />1982). Native species comprised 13% of the total catch including flannelmouth sucker (7.0), roundtail <br />chub (3.0), bluehead sucker (1.5) and speckled dace (1.5). No endangered species (Colorado <br />squawfish, bonytail, humpback chub or razorback sucker) were captured in the Dolores River in 1990. <br /> <br />Native species as a percentage of the total species captured by electrofishing and netting for each of <br />the subreaches are presented in Figure 3. Increases in percentage composition of flannelmouth <br />sucker and roundtail chub in higher subreaches of the study area suggest that these species may be <br />more prevalent in the upstream reaches. Percentage composition of bluehead suckers and specked <br />dace remains relatively constant throughout the study area Small sample size in Reach 4 precludes <br />interpretation of results. Figure 4 presents percentage composition of catch for native species versus <br />non-natives. Strong trends are apparent indicating that native species were more prevalent in the <br />upper portion of the study area <br /> <br />Figure 5 presents native species as a percentage of total catch for seining in the Dolores River. <br />These data also indicate that natives were more prevalent in the upper portions of the study area <br />Figure 6 presents composition of natives versus non-natives. <br /> <br />4.2 Summary of Fish Collections by Gear Type with CPE Statistics <br /> <br />A summary of all fish sampling efforts by gear type is presented in Table 2. An attempt was made <br />to expend similar effort during each of the 3 sampling trips for electrofishing, gill and trammel nets, <br />and seining. Variation in effort is reflective of variable conditions present during each sampling trip. <br />Also, time spent conducting reconnaissance and habitat assessment during Trip 1 reduced time <br />available for sampling. Summaries of fish species collected by life stage and CPE for each of the <br />principal gear types are presented in Tables 7-12. <br /> <br />4.2.1 EIectrofishing <br /> <br />The highest catch rates for the electrofishing canoe (Table 7), were for flannelmouth sucker (121.0 <br />fish/l0 hours), roundtail chub (11 0.1), carp (47.1) and bluehead sucker (37.8). The highest catch rates <br /> <br />8 <br />