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F1 <br />1 <br />1 <br />11 <br />1 <br />mark larvae from at least 10 collections are not available at the <br />present time. <br />Genetic Characterization of Endangered Fish Produced in Protected <br />Environments. When the razorback suckers reach a total length <br />between 250-300 mm in total length, the fish will be captured and <br />PIT-tagged. Non-lethal muscle plugs will be obtained from the fish <br />for genetic characterization (using allele frequencies, genotypic <br />proportions, etc.) and compared to similar information from the wild <br />stock. <br />' If genetic characterization of the wild fish reared in protected <br />habitats is similar to the wild spawning stock, a sample of not to <br />exceed 10% of the numbers in the wild spawning stock can be released <br />near the spawning site to augment the wild stock. All released fish <br />' must be identifiable by a unique PIT tag when recaptured during <br />future studies. <br />' If only a few larvae survive in the protected environment or the <br />genetic characterization indicates that the surviving fish in the <br />protected environment originated from only a few parents, the fish <br />should not be stocked into the riverine environment to prevent <br />' genetic swamping of the wild stock. The disposition of such fish <br />will follow the guidelines in Section VI.B. <br />D. Introgressive Hybridization. Introgressive hybridization has important <br />management and evolutionary consequences and increases when allopatric <br />species or stocks are placed into sympatry through human activities and <br />' when sympatric species or stocks inhabit altered environments (Buth et <br />al. 1987). No hybridization has been documented in the Colorado <br />squawfish. However, hybridization has been documented for razorback <br />suckers and the endangered Gila in the upper basin. <br />' The frequency of introgressive hybridization of razorback suckers with <br />flannelmouth suckers (Catostomus latipinnis) is low (0 - 5% toward <br />' flannelmouth suckers; Buth et al. 1987) but may increase if the riverine <br />environment in the upper basin is altered further, forcing the two <br />species to spawn in the same areas. <br />1 Dowling and DeMarais (1993) reported that introgressive hybridization <br />played an important role in creating a high morphological diversity among <br />Gila minnows in western North America. Dowling and DeMarais stated that <br />t the Colorado River Gila represent a complex of self-sustaining, <br />genetically distinctive species that are capable of exchanging genetic <br />material, comparable to syngameons in plants. Although the phylogenetic <br />' linkages are distinct, local introgression has clearly occurred among <br />three Colorado River Gila in the past. <br />Introgressive hybridization is apparently low at present but could <br />' increase in Gila if the habitat is altered further or in the razorback <br />sucker if nonnative suckers expand their ranges in the upper basin. <br />Preservation of critical habitat for the endangered fishes should prevent <br />15