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Last modified
8/11/2009 11:32:57 AM
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8/10/2009 4:17:29 PM
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UCREFRP
UCREFRP Catalog Number
7890
Author
U.S. Fish and Wildlife Service.
Title
Region 6, Fish and Wildlife Service Guidelines Directing Captive Propagation Of Listed And Candidate Fish.
USFW Year
1996.
USFW - Doc Type
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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
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