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<br />If conducted in a scientifically sound manner, captive propagation of <br />' endangered fish will prevent: (1) extinction of the species; (2) loss of <br />genetic diversity within a species, stock, or population; (3) loss of <br />genetic diversity among stocks or populations; and (4) inadvertent <br />' artificial selection that may lead to directional succession from <br />inbreeding or genetic swamping of wild stocks (Busak 1990; Kapuscinski et <br />al. 1993). The genetic processes that may be affected by these risks and <br />the hatchery activities that may cause the risks are summarized in Box 4. <br />' The extinction of indigenous fish stocks can be caused by stocking <br />captive-reared fish but is generally preceded by the loss of genetic <br />diversity within and between populations. <br />' C. Guidelines for Stocking Captive-Reared Endangered Fishes. Suitable <br />habitat must be available in river reaches that are proposed for stocking <br />' to increase the likelihood of successful stocking. The reasons for <br />holding, rearing, and stocking endangered fishes are summarized in Box 5. <br />Criteria for holding, rearing, or stocking captive-reared endangered <br />fish, criteria for when to stock, and action required are provided in Box <br />' 6. Guidelines for preparation of stocking plans for release of captive- <br />reared endangered fish into the Upper Colorado River Basin are summarized <br />in Box 7. <br />' D. Reasons for Maintaining Genetic Diversity in Captive Propagation <br />Programs. The major objective in captive propagation of threatened and <br />endangered fish species is (1) to develop broodstocks and to produce <br />' offspring that have genetic characteristics similar to those of the <br />founding population. Two additional objectives for captive propagation <br />of endangered fishes are (2) to use captive propagation and stocking when <br />' necessary as temporary fishery management tools to facilitate recovery <br />(i.e., development of self-sustaining populations) of endangered fishes <br />in their natural habitats in the upper basin while preserving the genetic <br />diversity of wild endangered fish stocks and (3) to maintain artificial <br />genetic refugia for endangered fish species or stocks that may be <br />susceptible to extinction from declining numbers and from catastrophic <br />risk in the wild, until such risks are removed. Breeding, rearing, and <br />' maintaining captive stocks such that genetic diversity similar to wild <br />stocks is maintained from generation to generation is important in <br />achieving this objective. Managing captive populations to maintain <br />existing natural genetic diversity preserves future options for effective <br />management and recovery of the taxon by fish and wildlife managers (Ralls <br />and Ballou 1992; Thomas 1990). <br />' The natural genetic diversity within a population is associated with its <br />evolutionary history and is important for adaptation, long-term survival, <br />and maximum production in the wild. Protecting genetic diversity within <br />a hatchery broodstock prevents artificial selection, inbreeding, and <br />genetic drift which frequently occurs in hatchery programs (Allendorf <br />1993). The concept of "maximally protecting genetic diversity" within a <br />hatchery stock assumes that a sufficient number of randomly sampled <br />individuals from the appropriate donor stock or population were used such <br />that the broodstock truly reflects the genetic characteristics of the <br />donor population. Proper broodstock development during the founding <br />' 17