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Last modified
7/14/2009 5:02:35 PM
Creation date
5/22/2009 4:53:39 PM
Metadata
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UCREFRP
UCREFRP Catalog Number
9378
Author
Nesler, T. P.
Title
Recovery of the Colorado River Endangered Fishes
USFW Year
2000.
USFW - Doc Type
Biological recovery goals and criteria for Colorado pikeminnow, Humpback chub, Razorback sucker & Bonytail.
Copyright Material
NO
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<br />26 <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 />Annual recruitment into the adult populations of humpback chub in both <br />Black Rocks and Westwater Canyon appear relatively similar and stable, ranging <br />between 11-16%. <br /> <br />Recovery Goals and Criteria At the time of this species' consideration and <br />inclusion under ESA as an endangered species, the reasons for decline were <br />"unknown." Threats were obvious to the two known existing humpback <br />populations due to the construction of Glen Canyon and Flaming Gorge Dams in <br />the early 1960s. Other potential threats were perceived in the Recovery Plan, but <br />not documented, including predation/competition from introduced, nonnative fish <br />species and hybridization. Presently, a list of potential threats for each population <br />segment can be identified (Valdez et al. 2000), but the contributions of any of <br />these threats to an ongoing population or species decline toward extirpation or <br />extinction have not been documented. <br /> <br />Five populations or population complexes are proposed as necessary to <br />recovery. Among the seven population segments that currently exist, data on chub <br />movements indicate the Black Rocks-Westwater Canyon and Little Colorado- <br />Grand Canyon populations are genetically linked (Valdez and Ryel 1995, Chart <br />and Lentsch 1999, Valdez and Clemmer 1982, Kaeding et al. 1990). Considering <br />the objective of achieving an effective population size to maintain genetic diversity, <br />these four population segments can be linked as two population complexes. <br />Linkages with or between the other existing populations have not been <br />documented via movement data, but identification of ecologically credible <br />population complexes can be proposed. <br /> <br />Given movement data for humpback chub between Yampa Canyon and the <br />Little Snake River (Wick et al. 1991), it is proposed here to identify a population <br />complex inhabiting of Yampa-Whirlpool-Split Mountain canyons within Dinosaur <br />National Monument. Even though the only population segment known to exist is <br />found in Yampa Canyon (Karp and Tyus 1990), it is feasible to postulate the <br />movement of these fish into suitable habitats in the downstream canyon reaches. <br />Historical presence data in Tyus (1998), Smith (1960), Bosley (1960, Gaufin et al. <br />(1960), McDonald and Dotson (1960), and Vanicek et al. (1970) suggest that <br />humpback chub were more widely distributed in the Green River segment of <br />Dinosaur National Monument prior to the construction and operation of Flaming <br />Gorge Dam. This presents the best opportunity for expansion of an existing <br />population if operation of Flaming Gorge Dam and amelioration of other limiting <br />factors can be achieved. Desolation-Gray Canyons may form their own complex <br />despite lack of corroborating data. Only the Cataract Canyon population lacks a <br />basis for multiple population segments or a credible link with another known <br />humpback chub population. <br /> <br />The existence of 7 population segments aggregated into 5 populations or <br />population complexes is proposed to be adequate in number and necessary as a <br />foundation upon which to base further recovery goals. The only documented loss <br />
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