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UCREFRP
UCREFRP Catalog Number
7833
Author
Ammerman, L. K. and D. C. Morizot
Title
Biochemical Genetics of Endangered Colorado Squawfish Populations
USFW Year
1989
USFW - Doc Type
Transactions of the American Fisheries Society
Copyright Material
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<br />4 <br /> <br />GENETIC VARIATION IN COLORADO SQUAWFlSH <br /> <br />439 <br /> <br />TABLE 3.-Measures of genetic variability calculated for Colorado squawfish by use of the BIOSYS-I program <br />of Swofford and Selander (1981). Standard errors are in parentheses. A locus is considered polymorphic if the <br />frequency of the most common allele does not exceed 0.95. <br /> <br /> Mean number of Polymorphic <br />Fish population Mean N per locus alleles per locus loci(%) Mean heterozygosity <br />Dexter 1981 7.0 (0.0) l.l (0.1) 13.6 0.026 (0.012) <br />Dexter 1987 30.3 (0.2) l.2 (0.1) 11.4 0.047 (0.021) <br />Colorado River 25.8 (0.1) l.2 (0.1) 13.6 0.OS3 (0.024) <br />Green River 25.4 (0.4) 1.1 (0.1) 9.1 O.Oll~.OI5) <br /> <br />(3.1-5.3%). Thus, it seems that Colorado squaw- <br />fish maintain a high level of heterozygosity <br />throughout their natural range. <br />Two loci (GPl-2* and EST-i*) deviated signif- <br />icantly (P < 0.01) from expected Hardy-Weinbefl <br />proportions in the Colorado River samples due to <br />a heterozygote deficiency (Table 2). In the Green <br />River population, EST-i'" deviation was signifi- <br />cant at the P = 0.05 level, as revealed by the pool- <br />ing procedure applied to loci with more than two <br />alleles (Swofford and Selander 1981). Such devia- <br />tions may suggest reduced gene flow between lo- <br />calities and thus bring into question the definition <br />of individuals in a river system as a single popu- <br />lation. <br />Nei's (1978) unbiased genetic identity (1) was <br />greater than 0.99 for all pairwise comparisons. The <br />cop he netic correlation coefficient was 0.896, an <br />indication of a good fit of the data to the con- <br />structed phenogram. <br />Estimates of similarity among the four popu- <br />lations of Colorado squawfish were similar to those <br />observed among geographic populations of other <br />cyprinid species. A vise and Ayala (1976) found <br />little divergence (I = 0.99) between populations <br />of Sacramento squawfish separated by compara- <br />ble river distances. However, the hatchery stocks <br />of Colorado squawfish are at most two generations <br />removed from the initial wild specimens used as <br />breeding stock. Significant effects of isolation and <br />inbreeding, such as loss of variation and rare al- <br />leles in the hatchery fish, were not evident in our <br />study. Greater divergence may be seen after sev- <br />eral more generations of breeding in these captive <br />populations unless such variability is preserved by <br />carefully designed breeding programs. <br />We were able to resolve five polymorphic loci <br />(GPl-i*, EST-i*, TPl-]*, TPl-2*, PEPS*) from <br />fift tissue. These genetic markers are ideal for <br />monitoring allele frequency changes in breeding <br />stock of Colorado squawfish. This nonlethal sam- <br />pling method has the potential to aid fishery man- <br />agers in breeding and restocking programs involv- <br /> <br />ing endangered species once informative genetic <br />markers have been identified. <br />Our data suggested that significant dri ft and bot- <br />tleneck effects, as reflected by allozyme frequen- <br />cies and average heterozygosities, have not oc- <br />curred in the captive populations of Colorado <br />squawfish. From these data, there is no reason to <br />suspect significant changes in allele frequencies at <br />loci that affect overall individual fitness. Had we <br />detected significant drift effects by use ofallozym- <br />ic markers, there might be reason to expect that <br />selective changes under hatchery conditions may <br />be lowering overall fitness (Allendorf and Ryman <br />1987). In summary, hatchery populations of Co 1- <br />orado squawfish appear to be representative of the <br />two wild populations sampled. <br /> <br />Acknowledgments <br /> <br />This research was supported by the Denver Re- <br />gional Office of Endangered Species, U.S. Fish and <br />Wildlife Service (USFWS). We thank Holt Wil- <br />liamson of USFWS, Region 2, for transporting <br />specimens. Lisa Clepper, Lela Limmer, and Rene <br />Schmidt provided laboratory assistance. Mike <br />Dixon and Brian Crother provided helpful com- <br />ments on the manuscript. <br /> <br />References <br /> <br />Allendorf, F. W., and N. Ryman. 1987. Genetic man- <br />agement of hatchery stocks. Pages 141-159 in N. <br />Ryman and F. Utter, editors. Population genetics <br />and fishery management. University of Washington <br />Press, Seattle. <br />Aquadro, C. E, and J. C. Avi5e. 1982. An assessment <br />of "hidden" heterogeneity within electromorph5 at <br />three enzyme loci in deer mice. Genetics 102: 269- <br />284. <br />Avise, J. c., and F. J. Ayala. 1976. Genetic differen- <br />tiation in specio5e versus depauperate phylads: evi- <br />dence from the California minnows. Evolution 30: <br />46-58. <br />Behnke, R. J., and D. E. Benson. 1980. Endangered <br />and threatened fishes of the upper Colorado River <br />
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