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Last modified
7/14/2009 5:02:33 PM
Creation date
5/22/2009 4:52:15 PM
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UCREFRP
UCREFRP Catalog Number
8114
Author
Nesler, T. P.
Title
Five-year Stocking Plan for Endangered Colorado River Fish Species in Colorado.
USFW Year
1998.
USFW - Doc Type
Denver, CO.
Copyright Material
NO
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<br />of bonytail inhabiting larger riverine habitat like the Colorado River near Moab, <br />Utah, where floodplain habitat was more likely to exist. <br /> <br />It is obvious the above two reaches are quite different from a habitat perspective. Similar to <br />other aspects of setting stocking objectives for bonytail, considerable guesswork is involved. <br />Depending upon whether this species is a generalist in its habitat needs or not, which <br />monitoring the above two reaches will provide guidance, river reaches in Colorado <br />designated for bonytail stocking may be revised considerably. <br /> <br />Further, the following species interactions and recovery actions are anticipated: <br /> <br />1) Biomass and production occupied by common carp and other nonnative fish in the <br />Grand Valley may be reduced by control efforts, lessening competitive pressure <br />within floodplain habitats, and perhaps expand expansion of bonytail biomass. <br /> <br />2) With successful establishment of an adult bonytail population, general abundance of <br />other native species may be reduced as a result of some competition. <br /> <br />Achievement of the stocking objective would result in an adult population of 20,000 <br />4-6-year-old (adult) fish in each reach, and two geographically distinct populations in the <br />Upper Colorado River subbasin. Due to the uncertainties associated with habitat needs of <br />bonytail, specific definitions of their probable distribution and abundance cannot be presented <br />as is being done for razorback sucker and Colorado pikeminnow. Clearly, monitoring will <br />be required to refme the speculative objectives that serve as a starting point. Interim <br />management objectives (IMO) for bonytail (Lentsch et al. 1998) indicate at least 2,000 adult <br />fish are necessary as an effective population size to maintain long term genetic diversity. <br />Using a demographic model developed by Crowl and Bouwes (1998), simulation results show <br />a mean population or subpopulation size of 4,800 bonytail (:t800 fish) are necessary to be <br />95 % confident the population will be maintained over a 100 year period. No river reaches <br />were designated within the IMOs to direct reintroduction efforts, so it may be interpreted that <br />the IMO objective for this species is one population of about 5,000 adult fish anywhere in <br />the Upper Colorado River Basin. The stocking objectives here are considerably greater than <br />the IMO population objective, though neither can be judged as more reasonable than the <br />other due to the species' unknowns. <br /> <br />Reintroduction of bonytail into the upper Colorado River Basin has been assessed by <br />several studies (Chart and Cranney 1992, Meyer 1992, Wydoski 1994, Lentsch et al. 1996). <br />Recommendations included the necessity of reintroduction of bonytail in the wild to <br />determine it's ecological requirements, but concerns have been expressed about reintroducing <br />bonytail because of the potential hybridization with the other Yili species, especially <br />humpback chub. While acknowledged as a potential risk associated with reintroduction and <br />establishment of bonytail near existing humpback chub populations (e.g. Black Rocks), this <br />risk appears to be overemphasized based on the evidence of historic hybridization within the <br />Gila complex that predates human modification of the river system (Dowling and DeMarais <br /> <br />10 <br />
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