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Last modified
7/14/2009 5:02:34 PM
Creation date
5/17/2009 11:52:58 PM
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UCREFRP
UCREFRP Catalog Number
9314
Author
Wick, E. J. and J. A. Hawkins.
Title
Colorado Squawfish Winter Habitat Study.
USFW Year
1989.
USFW - Doc Type
Fort Collins.
Copyright Material
NO
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hybridization (Maddux et <br />through routine sampling <br />levels of hybridization. <br />al. 1993). Wild fish stocks will be monitored <br />and necessary actions taken to avoid unnatural <br />V. GENETICS MANAGEMENT OF CAPTIVE STOCKS <br />A. Determining the Need for Captive Propagation and Reintroduction Captive <br />propagation may be necessary if a fish stock does not have sufficient <br />recruitment to achieve or maintain a self-sustaining population. Stocks may <br />require captive propagation to produce fish for research and for approved <br />augmentation or restoration programs (Williams et al. 1988). <br />Captive-reared fish can be used for (1) genetic refugia and broodstock <br />development, (2) research and development, (3) information and education, <br />and (4) augmentation or restoration (Wydoski 1994). Refuges serve a vital <br />function in maintaining fish that may become extinct due to declines in wild <br />populations, catastrophic risks, and broodstock development. Captive-reared <br />fish are needed for research to conduct laboratory and field experiments <br />related to ecological requirements, habitat use, interactions with nonnative <br />fishes, response to contaminants, olfaction and chemoreception studies, fish <br />passage, taxonomy, anatomy, physiology, performance, fitness. and <br />hereditary trials. Fish specimens are also needed for use in public <br />relations programs and to educate the public. Augmentation may be required <br />to provide a "jump-start" mechanism to supplement fish in habitats where the <br />wild populations are very depressed. Restoration stocking may be necessary <br />in river reaches where stocks have been extirpated. <br />B. Genetic Risks Associated with Captive Propagation and Reintroduction. <br />Planning recovery/restoration efforts for endangered and candidate fishes <br />will be accomplished following a logical and systematic approach that will <br />minimize potential genetic risks(See Box 3). A genetic risk is broadly <br />defined as the sum of critical uncertainties associated with any management <br />action or inaction that may change the genetic diversity both within and <br />among wild stocks. Risk assessment consists of (1) estimating risk, and (2) <br />managing risk (Lichatowich and Watson 1993). Major genetic risks associated <br />with captive propagation can be identified and reduced through a careful <br />assessment. Risk assessment will be addressed in each specific <br />reintroduction or augmentation plan. The potential to manage genetic risks <br />to wild stocks will be essential for a "no jeopardy opinion" under Section 7 <br />consultation of the Endangered Species Act. <br />If conducted in a scientifically sound manner, captive propagation will <br />prevent: (1) extinction of the species: (2) loss of genetic diversity <br />within a species, stock, or population: (3) loss of genetic diversity among <br />stocks or populations; and (4) inadvertent artificial selection that may <br />lead to directional succession from inbreeding or genetic swamping of wild <br />stocks (Busack 1990; Kapuscinski et al. 1993). The genetic processes that <br />14
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