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Conclusion and Recommendations <br />Due to low numbers of adult captures and poor juvenile identification, meeting <br />study objectives proved difficult. In light of historic and current study data distribution of <br />the population has been defined in Dinosaur National Monument, but humpback chub <br />may be present in other nearby areas. Length frequency, while quantified, is weak <br />considering the low number of juveniles. Similarly, a low number of captures made adult <br />abundance estimates impossible. The ability to differentiate juvenile G. cypha from G. <br />robusta in this population limited the ability to draw inference from these data. <br />The Yampa population of humpback chub has declined and is nearly extirpated. <br />The low number of individuals makes a population estimate impossible. However, some <br />level of monitoring should be continued to determine if the population has increased <br />enough to support a population estimate. If humpback chub in Yampa Canyon prove to <br />be genetically unique, their genetic diversity should be preserved by moving fish to a <br />refuge. Recommendations are as follows: <br />1) Eliminate Lodore Canyon and Split Mountain Canyon from further attempts to <br />study the Yampa population. If incidental capture of humpback chub occur in the <br />future in these areas, effort should be expanded. <br />2) Annually monitor Gila spp.nursery areas in Yampa Canyon, Whirlpool Canyon, <br />and Island Park. <br />3) Sample Cross Mountain Canyon and the Little Snake River for the presence of <br />humpback chub. <br />4) Fish should be immediately removed from the canyon to refugia to preserve <br />genetic material. <br />5) The population estimation element of recovery for this population should be <br />suspended until more individuals are available for sampling. <br />13 <br />