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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 />habitats and ecological requirements have existed over the same time frame to <br />support these populations. These habitat and ecological conditions need to be <br />protected in some form. The institutional programs being implemented that <br />maintain these conditions need to be formalized in long-term agreements or <br />regulations. It is also reasonable to assume that the five listing factors are being <br />adequately addressed in the current environment and any threats are only <br />potential ones that are not exerting a negative influence and causing a declining <br />trend in the species' status. Long-term agreements and conservation <br />management plans as criteria for delisting provide a mechanism for protection of <br />what has proven to be the best combinations of flow (quantity/regime) <br />management, nursery habitat protection, instream passage, and nonnative fish <br />control to sustain the populations of the listed fishes required for recovery. <br /> <br />Species Status and Trends <br /> <br />A review of the current biological status of these species is necessary to <br />evaluate their condition relative to federal definitions of "endangered" or <br />"threatened", and to place proposed recovery goals into context. Under ESA 16 <br />U.S.C. Section 1532, "endangered" is defined as "...in danger of extinction through <br />all or a significant portion of its range... ", and "threatened" is defined as ".. . likely to <br />become an endangered species within the foreseeable future throughout all or a <br />significant portion of its range." These definitions imply species documented to be <br />in declining trends toward eventual extinction, or species so limited in abundance <br />or distribution as to be vulnerable to local extirpation and extinction. A species that <br />is extirpated over a significant portion of its range, but stable or increasing and <br />secure within the remainder of its range may be interpreted under the purpose of <br />ESA and definition of "conservation" to be a candidate for delisting. The purpose <br />of this review of biological status for each of the listed fish species is to identify <br />declining trends or indices suggesting an adverse population condition, or a <br />positive status and trend indicating a change in federal listing status is warranted. <br /> <br />Colorado pikeminnow <br /> <br />Species status and trend Mark-recapture and length frequency data were. <br />available from 1990-1997 for the Colorado/Gunnison rivers and from 1991-1997 <br />for the Yampa/Little Snake, White, and Green/Duchesne/Price rivers. These data <br />enable population estimates, recruitment and length frequency distributions to be <br />developed for each population segment from 1992-1997. Attributes of data used <br />and population estimates are provided in Appendix Tables A-1through A-4. <br /> <br />This species is well distributed in Upper Basin rivers. No losses in <br />distribution have been noted, and recently, passage of late-juvenile/early adult fish <br />at the Redlands passage appears to be increasing their abundance in the <br />Gunnison River. Augmentation stocking in the San Juan River may improve the <br />distribution of Colorado pikeminnow. Estimates of population size and fish/mile for <br />Colorado pikeminnow in these rivers appear to be stable (Colorado, Yampa) or <br /> <br />7 <br />