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Last modified
7/14/2009 5:02:35 PM
Creation date
5/17/2009 11:51:39 PM
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UCREFRP
UCREFRP Catalog Number
9411
Author
Williamson, J. H., D. C. Morizot and G. J. Carmichael.
Title
Biochemical Genetics of Endangered Colorado Pikeminoow from the Green, Yampa, Colorado, and San Juan Rivers.
USFW Year
1998.
USFW - Doc Type
\
Copyright Material
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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
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