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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 />flannelmouth sucker composition at Clifton in 2001 (42%) was somewhat higher than the prior <br />year. Factors that could explain these minor discrepancies in species composition include that it <br />could be there was a true shift in species composition or that it could be an artifact of sampling <br />efficiency between years. It is more likely that the variation noted for 2000 is a result of <br />sampling efficiency. Sampling efficiency can be influenced by flows, visibility of water, effort, <br />and ability ofnetters. Flow conditions during sampling was fairly similar in 2000 and 2001, but <br />flows were much higher 1999 (Figure 3). In 2000 sampling after thunderstorms or during <br />reduced water visibility was more common, and there were fewer passes made in 2000 than in <br />1999 and 2001. Also shoreline habitats received proportionally more effort in 2000. Therefore, <br />it is believed that differences between years for tlannelmouth and bluehead composition is less <br />than the data in Table 3 indicates. <br /> <br />Common carp was the most common nonnative species of fish over 15 cm collected at <br />both sites in 2001. Carp were 6% at the Com Lake site and 14% at Clifton (Table 6). In 1999 <br />and 2000 carp comprised 11% and 14% of the catch, respectively so the 6% of 200 1 was much <br />lower than in the two prior years. At Clifton carp composition was 16% in 1999, 12% in 2000 so <br />the 14% in 2001 was very similar to prior years. The discrepancy in carp percentage at Com <br />Lake in 2001 (6%) could suggest more movement of carp during 2001. <br /> <br />White sucker plus white hybrids with flannel mouth and bluehead comprised 6.2% at <br />Com Lake in 2001 and 4.1 % at Clifton in 2001 (Table 6). These percentages are similar for <br />white sucker in Com Lake in 1999 and 2000 at 5.6% and 5.3%, respectively and at Clifton at 5.0 <br />and 3.7% respectively. Also white sucker were more common in backwater habitats than in the <br />main channel. Channel catfish also had similar species composition between years with 4.7% in <br />2001, 6.3% in 2000 and 4.2% in 1999 at Com Lake. In Clifton, catfish composition was 5.7% in <br />2001 and 5.1 % in 2000. <br /> <br />Fish less than 15 em <br /> <br />Since speckled dace were very common and occupy swift habitats somewhat difficult to <br />sample, dace and mottled scuplin were not netted but counted by netters. Therefore, dace and <br />sculpin composition is not based on catch rates so their composition is not proportional to their <br />actual population size. However, these counts will be very useful for documenting their <br />distribution and habitat associations in the Colorado River. In contrast, all sunfish sighted were <br />netted, and most originated in backwater habitats. Sunfish removal was tried in 2001 and 2000, <br />but not in 1999, since the recovery program was conducting sunfish removal during this time. <br />Non-native cyprinds (NNC; red shiner, sand shiner and fathead minnows) were very abundant in <br />shoreline habitat and backwater habitats, but relatively few were netted. No effort was made to <br />quantify abundance or composition ofNNC since these fish are not going to be used to justify <br />flow recommendations and numerous other sources are available for data concerning this fish <br />group, Valdez (1999), Bestgen et al (1999) and McAda (IS:MP). <br /> <br />It is highly likely that the most common fish in the under 15-cm group for the IS-mile <br />Reach belong in the NNC group. The next most abundant species is highly likely to be speckled <br />dace, which had the highest composition as reported in 2001 at both sites (Table 6). YOYand <br />juvenile flannel mouth and bluehead sucker and roundtail chub were collected in all years <br /> <br />25 <br />