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fish in specific river reaches and collecting larval fishes downstream <br />from documented or suspected spawning sites. For example, in the Upper <br />Colorado River Basin all major tributaries have been sampled to <br />determine the distribution and abundance of endemic and introduced <br />fishes (Bestgen 1990; McAda et al. 1993; Miller et al. 1982; U.S. Fish <br />and Wildlife Service 1990a, 1990b, 1991). Additional work of this type <br />needs to be done in the other major river systems in Region 6. <br />3. Migration. Movement and Interchange between Stocks. Some listed and <br />candidate fishes are known to migrate to specific spawning areas but <br />return to a home area during the remainder of the year. The Colorado <br />squawfish migrates long distances to spawning sites and is considered <br />the most mobile of the endangered Colorado River fishes (Tyus 1991). <br />The razorback sucker exhibits moderate migrational movements (Tyus and <br />Karp 1991). Some humpback chub stocks (e.g., the stocks in Black Rocks <br />and Westwater Canyons in the Colorado River) do not migrate for spawning <br />(Kaeding et al. 1990) but a lower basin humpback chub stock spawns in <br />the Little Colorado River and uses the mainstem Colorado River in the <br />Grand Canyon during the remainder of the year (Kaeding and Zimmerman <br />1983). The greenback cutthroat trout returns to a specific spawning <br />stream or river. Migratory bull trout spawn and rear in tributary <br />streams and return to lakes to mature, while resident bull trout <br />complete all life stages in one stream location. Migratory bull trout <br />may move 100 miles or more to spawning sites (Fraley and Shepard, 1989). <br />Dams fragment habitat and prevent free movement of fishes. Some <br />geographic separation among stocks is due to such habitat alteration. <br />In most cases, fish are known to move between different river reaches <br />during the spawning season. A small amount of interchange between <br />stocks is a natural phenomenon that facilitates evolution. Stocks with <br />limited interchange will be classified separately until information is <br />available to justify combining them. This conservative classification <br />will prevent or minimize the risk of losing unique genetic attributes of <br />any stock that may be important in their restoration and recovery. <br />4. Genetic Identification and Characterization of Stocks. Genetic markers <br />are useful in the restoration of species. They can be used to <br />characterize the genetic diversity among stocks and maintain diversity <br />in a captive propagation program similar to the parent wild stocks <br />(Allendorf and Phelps 1987; Allendorf and Ryman 1987; Gauldie 1991; <br />Hynes et al. 1981). It is extremely important to verify inheritance <br />patterns and genetic characters to ensure that the markers have a <br />genetic basis and that they are not due to other factors such as <br />environment, development stage, or sample treatment (Kapuscinski and <br />Jacobson 1987). Diversity will be characterized by identifying genetic <br />markers via protein and DNA analysis. In some cases, morphometric <br />analyses will be used. Early detection of inadvertent hybridization due <br />to stocking will allow changes in the procedures that could preserve the <br />genetic integrity of remaining wild stocks (Hynes et al. 1981). <br /> <br />7