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with brook trout. Cutthroat trout have hybridized with rainbow trout <br />throughout their range. <br />Dowling and DeMarais (1993) reported that hybridization played an important <br />role in creating a high morphological diversity among Gila sp. in western <br />North America. They stated that the Colorado River Gila so. represent a <br />complex of self-sustaining, genetically distinctive species that are capable <br />of exchanging genetic material. Although the phylogenetic linkages are <br />distinct, local introgression has clearly occurred among three Colorado <br />River Gila S. in the past. <br />Hybridization is apparently low at present but could increase in Gila sR. if <br />the habitat is altered further or in the razorback sucker if nonnative <br />sucker expand ranges in the upper basin. Preservation of habitat for listed <br />and candidate fishes should prevent increased hybridization (Maddux et al. <br />1993) Wild stocks should be monitored and actions taken to reduce <br />hybridization. <br />Hybridization between bull trout and brook trout typically results in <br />infertile offspring (Leary et. al. 1983). However, brook trout mature at a <br />younger age and have a higher reproductive rate, life history differences <br />that tend to work in concert with hybridization to favor brook trout and <br />result in the elimination of bull trout. <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 maintain a self-sustaining population. (Williams et al. <br />1988). Captive-reared fish can be used for (1) genetic refugia and <br />broodstock development, (2) research and development, (3) information and <br />education, and (4) augmentation or restoration (Wydoski 1994). <br />Captive-reared fish are needed for research to conduct laboratory and field <br />experiments related to ecological requirements, habitat use, interactions <br />with nonnative fishes, response to contaminants, olfaction and <br />chemoreception studies, fish passage, taxonomy, anatomy, physiology, <br />performance, and fitness. Fish specimens are also needed for use in public <br />education programs. Augmentation may be required to provide a "jump-start" <br />mechanism to supplement fish in habitats where wild populations are depleted <br />and restoration stocking may be necessary in river reaches where stocks have <br />been extirpated. <br />B. Genetic Riczkc dccnrin+nA w;+1, <br />wr:rv .?a: ., v1 VY 4?.4 1 V11 <br />Planning for restoration and recovery will be accomplished following a <br />systematic approach to minimize potential genetic risks (See Box 3). A <br />genetic risk is broadly defined as the sum of critical uncertainties <br />associated with any management action or inaction that may change genetic <br />• <br />13