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<br /> <br />r, <br />1 <br /> <br />1 <br />1 <br /> <br /> <br />1 <br />1 <br />1 <br />1 <br /> <br />F1 <br />L <br /> <br />7 <br />anonymous single-copy nuclear DNA techniques. This purpose followed previous (FY91, #24; FY92, <br />425) but similar proposals to describe biochemical genetic analyses of Mendelian polymorphisms. <br />The broad goal of this investigation is to provide genetic information required to more effectively <br />recover and manage the Colorado pikeminnow. Additional genetic data are required to allow more accurate <br />population identification and characterization. Determination of variability is needed for fish throughout <br />the present geographical range. In combination with ecological, distributional, morphological, <br />demographic, and behavioral data, genetic conservation or management units need to be identified by <br />examination of genetic structure within and among populations, river tributaries, and river basins. A <br />standardized and centralized database of genetic markers to use in planning, monitoring, and evaluating <br />management actions such as founding genetic refugia, production of broodfish populations, and fish <br />production and stocking will assist Colorado pikeminnow management efforts. Genetic hazards, such as <br />excessive inbreeding and/or outbreeding associated with various management strategies and actions, need <br />to be identified. Hypotheses of chemoreception, migration, and homing and assumptions associated with <br />various management actions also need to be examined. <br />Objectives included determinations of whether or not there is genetic differentiation within the <br />species and, if so, the genetic relationships among populations. This task included measuring the amount <br />and pattern of genetic variation within and among populations, or purported populations; defined as genetic <br />structure. Hypotheses tested were Ho: Colorado pikeminnow are genetically homogeneous or panmictic <br />and Ha: genetically differentiated populations of Colorado pikeminnow exist. Specific objectives to be <br />addressed include: 1) Genetic identification and characterization of the species; 2) Definition of genetic <br />profiles for management units; 3) Determination of genetic status of management units; 4) Identification of <br />genetic markers for management purposes; 5) Generation of genetic data required to develop breeding <br />strategies and broodfish populations; and 6) Production of a management document with recommendations. <br />We also intended to investigate an additional genetic method examining genomic DNA and develop <br />nonlethal and economical methods of genetic analyses. Some specific tasks in the present study were: 1) to <br />detect genetic variability within and among indigenous and captive Colorado pikeminnow spawning <br />populations; 2) to examine the feasibility of locating or detecting genomic DNA variability within and <br />among Colorado pikeminnow spawning populations; 3) to estimate allozyme allele frequencies in adult and <br />young-of-the-year populations associated with known spawning areas; 4) to further evaluate and maximize <br />the use of non-lethal tissues to obtain genetic information; and 5) to consider the management implications <br />of our findings. <br />Methods <br />Samples from throughout the presently recognized range of Colorado pikeminnow were obtained <br />from the upper mainstem Colorado River, Yampa River, Green River, and San Juan River by personnel <br />from the U. S. Fish and Wildlife Service, Colorado Department of Wildlife, New Mexico Game and Fish <br />Department, Utah Department of Natural Resources, and BioWest Incorporated (Logan UT). Hatchery <br />broodfish populations were sampled from Dexter NFH&TC. One broodfish population was derived from <br />Yampa River fish (Yampa River DX-F, (74)) and the other from Colorado/Green River fish <br />(Colorado/Green DX-F, (81)). For histories of these hatchery fish see Ammerman and Morizot (1989) and <br />Appendix I, Table 1.). We also re-examined the data from fish sampled by Ammerman and Morizot <br />(1989) (Colorado/Green River DX-F,(81) and Yampa River DX-F2(87)). Another population maintained <br />at Dexter NFH&TC (Yampa River DX-F2(91)) was sampled. A recent addition to the populations at <br />Dexter NFH&TC, one consisting of 10 wild fish captured from the Colorado River, was also sampled <br />(Colorado DX-F0 (91). Populations and sampling locations were selected by biologists for the Upper <br />Colorado River Recovery Implementation Program as locales where adult and young-of-the-year Colorado <br />pikeminnow feasibly could be collected in association with spawning. Sample sizes, locations of fish <br />collected or sampled, and populations sampled are presented in Appendix I (Tables 2 and 3). Adult and <br />juvenile fish were collected by using trammel nets and electroshocking from 1990 through 1993 and tissue <br />samples were obtained non-lethally. For purposes of this study, juveniles were defined by field biologists. <br />Il