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<br />v <br /> <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 />protected over the long term to insure populations of the listed fish species <br />continue to be sustained at or better than the biological recovery goals. <br /> <br />Population-level data describing the status and trend assessment of the four <br />endangered fish species and for use as a contextual basis for determination of <br />recovery goals was deemed adequate only for Colorado pikeminnow and some <br />populations of humpback chub. Colorado pikeminnow is well distributed in the <br />Upper Basin and population estimates for the Green, Yampa, White, and Colorado <br />rivers appear stable or increasing. These trends are corroborated by catch per <br />unit effort data collected through standardized monitoring. The Green and <br />Colorado rivers support larger populations than the tributary Yampa and White <br />Rivers. Passage and augmentation stocking may improve the distribution and <br />abundance of the Colorado pikeminnow in the Gunnison and San Juan Rivers. <br />Recruitment rates for the Green and Colorado river populations of Colorado <br />pikeminnow demonstrated decreasing trends, but were not considered causes for <br />concern given the magnitude and trend observed in abundance estimates. <br />Recruitment rates for pikeminnow populations in the Yampa and White rivers <br />appeared variable, but no declining trends were apparent. Length frequency <br />distributions for the Green, Yampa, White, and Colorado River populations reflect <br />the influence of variable year class strength annually, but appear stable in their <br />overall size structures with neither lack of recruitment or progressive loss of adults <br />evident in the distributions. <br /> <br />Population-level data were considered adequate only for Black Rocks and <br />Westwater Canyon populations of humpback chub in the Colorado River. <br />Population estimates from other studies were available for Black Rocks, <br />Westwater Canyon, Little Colorado River, Colorado River in Grand Canyon, <br />Yampa Canyon, Cataract Canyon, and Desolation-Gray Canyon. At the time of <br />federal listing, only two humpback chub populations were documented, and were <br />located in the Grand Canyon of the Colorado River and Hideout Canyon in the <br />Flaming Gorge basin of the Green River. Both were threatened by major dam <br />construction. Presently, six populations are known to exist in approximately 68% <br />of their historic habitat. Interpretation of trends using independent population <br />estimates for the Black Rocks and Westwater Canyon populations are not clear, <br />but the former population appears stable and a declining trend is possible for the <br />latter population though abundance remains substantial. Both length frequency <br />distributions and annual recruitment rates appear stable for both the Black Rocks <br />and Westwater Canyon populations. Populations of humpback chub have <br />persisted in all of the known locations since their initial discovery. <br /> <br />The status of razorback sucker and bony tail are clearly endangered. The <br />information available for razorback sucker demonstrates only one wild population <br />remains in the middle Green River and recruitment is inadequate to offset a <br />declining trend in abundance. A relatively large population in Lake Mojave is <br />maintained by augmentation stocking. Bony tail is functionally extinct in the wild, <br />and is represented almost entirely by captive broodstock. Available historic data <br />