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Last modified
7/14/2009 5:02:35 PM
Creation date
5/22/2009 5:19:10 PM
Metadata
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UCREFRP
UCREFRP Catalog Number
9463
Author
Badame, P. V. and J. M. Hudson.
Title
Reintroduction and Monitoring of Hatchery-reared Bonytail in the Colorado and Green Rivers; 1996-2001.
USFW Year
2001.
USFW - Doc Type
03-13,
Copyright Material
NO
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<br />Reintroduction concerns <br /> <br />Hybridization <br /> <br />For successful reintroduction ofbonytail into the UCRB, potential hybridization with humpback <br />and roundtail chubs must be addressed. Evidence indicates that hybridization takes place to some <br />degree in the wild between these closely related congeners (Holden and Stalnaker 1970). Vanicek <br />and Kramer (1969) suggested that during spawning periods, spatial not temporal mechanisms <br />separate bonytail from other Gila species. Kaeding et al. (1990) also believe that the isolating <br />mechanism is spatial, based on their sampling protocol and studied design. Hamman (1982) was <br />able to artificially produce a viable offspring from bonytail x roundtail chub crosses and bonytail x <br />humpback chub crosses. However, these crosses did not occur in a hatchery environment without <br />being induced. Although hybridization may be a natural part of the evolutionary history of the <br />Gila complex, a successful reintroduction (as defined by the Recovery Program) can only occur if <br />at least some bonytail can remain isolated until the population is stable. <br /> <br />Nonnative fish interactions <br /> <br />Successful bonytail reintroduction also requires minimizing impacts from nonnative fishes. <br />Unfortunately, these impacts have only been minimally assessed to date. An in-depth <br />understanding of community dynamics would allow a more effective reintroduction effort (Chart <br />and Cranney 1993). Besides competing for resources, nonnative fishes exert pressure as <br />predators. Low numbers of wild bonytail may be the reason nonnative predation on bonytail has <br />not been documented. However, nonnative predation on humpback chub, tlannelmouth sucker <br />and other native fish has been confirmed in the Colorado River system and should be considered <br />as contributing to past and future losses of bonytail (Marsh and Douglas 1994; Valdez and Ryel <br />1995). <br /> <br />Practical methods of minimizing predation impacts through theoretical modeling of gape <br />limitation theory were examined by Alder and Crowl (1995). Using known predator size <br />distributions within the upper Colorado River basin, it was theorized that bonytail are beyond <br />most existing predation risk at 150 mm total length. This became the basis for the ideal stocking <br />length for bonytail released into the basin. Although this may alleviate much of the predation risks <br />for stocked bonytail, their progeny will still face the growing problem of nonnative predators. <br /> <br />Conditioning: of hatchery fish <br /> <br />It has been demonstrated that fish reared in captivity can become domesticated with respect to <br />physiological parameters (Wiley et al. 1990). These effects may be minimized through shortened <br />captivity (Nehring 1991). However, prolonged rearing may be necessary to grow bonytail to the <br />recommended stocking size. Therefore, physical and behavioral conditioning of young bonytail <br />before release has been considered as a potential strategy for minimizing the effects of <br />domestication (Meyer 1992; Chart and Cranney 1993). Laboratory experiments were conducted <br /> <br />2 <br />
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