Laserfiche WebLink
<br />.... <br /> <br />Ie same seven bays of <br />NeV per bay or estuary <br />averaged 272. The range <br />J 46.6) per bay or estuary <br />'om the TPWD MDC in <br />than both the Ne1 and NeV <br />Moreover, the estimates <br />nflated given that the <br />mrvival probability per <br />Jably not met. Briefly, <br />ped yearling or older red <br />.nced" bays or estuaries <br />.equivocally identified 30 <br />om Aransas Bay as being <br />:ribution of brood dams, <br />inations to the hatchery- <br />nonrandom, as was the <br />~ned and wild fish with <br />within each bay. Karlsson <br />~se results as indicating <br />ty among releases, which <br />ases in total NeR over all <br />erations suggest that a <br />occur in Texas bays or <br />latchery-reared fish. <br />, that might be employed <br />PWD-released fish and <br />a Ryman-Laikre effect: <br />nating combinations per <br />Jer of progeny generated <br />3) increase the number of <br />ng tanks in each released <br />e accomplished by using <br />ach spawning tank, given <br />ing sires appears greater <br />ing dams. This approach <br />~r, as total egg output per <br />mpromised significantly, <br />ms than sires appear to <br />ns. The observed spawn- <br />also raises the question as <br />;eason there are dams (or <br />) progeny to any released <br />;tudying this issue and, to <br />~ dams (but not sires) in <br />ontribute negligibly, if at <br />Vlonitoring and replacing <br />, might be a strategy to at <br />the number of mating <br /> <br /> <br />practice difficult to impossible to achieve. It also would <br />likely be unproductive given that the observed <br />reduction in Ne per spawn due to variation in progeny <br />produced per mating combination was relatively small <br />(about 9%). <br />The third approach, increasing the number of spawns <br />from different spawning tanks in a released population, <br />would seem to be the optimal strategy, as the NeR of a <br />released population would on average be the product of <br />the average Ne per spawn (estimated here as 2.59) and <br />the number of spawns from different spawning tanks <br />included in the mixture. For example, if progeny from <br />five different spawning tanks were combined into a <br />single release, the average NeR would be 12.95, a 2.4- <br />fold increase in NeR. A further 33% increase in NeR (to <br />17.2) could be achieved by equalizing the number of <br />progeny from different spawning tanks mixed in a <br />released population. Even considering a pseudoequal- <br />ized mixture as simulated above, NeR would still be <br />increased to 16.1. Given the range (7-27) in the <br />number of release populations stocked from the MDC <br />in 2003, the maximum average NeR under this scenario <br />(i.e., using a pseudoequalized mixture) could range <br />from more than 110 to about 260, a substantial increase <br />relative to that estimated under the present-day <br />program and closer to the average contemporaneous <br />(NeV) and long-term (Net) effective size estimates of <br />Saillant and Gold (unpublished) and Turner et al. <br />(2002), respectively. <br /> <br />Acknowledgments <br /> <br />We gratefully acknowledge the help and assistance <br />provided by personnel, in particular R. Chavez and R. <br />Gamez of the Texas Parks and Wildlife Department <br />CCNCPL Marine Development Center in Flour Bluff. <br />We also thank C. Bradfield and M. Renshaw for help in <br />the laboratory, D. Gatlin III and W. Neill for help in <br />obtaining tissues, and T. Turner for helpful comments <br />on an early draft of the manuscript. Work was <br />supported by the Texas Sea Grant College Program <br />(award NAI6RG1078), the Coastal Fisheries Division <br />of the Texas Parks and Wildlife Department, the <br />Coastal Conservation Association-Texas, and the <br />Texas Agricultural Experiment Station (project H- <br />6703). This paper is number 60 in the series "Genetics <br />Studies in Marine Fishes" and contribution 160 of the <br />Center for Biosystematics and Biodiversity at Texas <br />A&M Universitv. <br /> <br />NOTE <br /> <br />]333 <br /> <br />University, Texas Agricultural Extension Service and Sea <br />Grant College Program, College Station. <br />Crow, 1. F, and M. Kimura. 1973. An introduction to <br />population genetics theory. Harper and Row, New York. <br />Danzmann, R. G. 1997. PROBMAX: a computer progranJ for <br />assigning unknown parentage in pedigree analysis from <br />known genotypic pools of parents and progeny. 10nffia] <br />of Heredity 88:333. <br />Efron, B. ]979. 1977 Rietz Lecture: bootstrap methods- <br />another look at the jackknife. Annals of Statistics 7:1-26. <br />Frankham, R. 1995. Effective population-size adult population <br />size ratios in wildlife: a review. Genetica] Research <br />66:95-107. <br />Gold, J. R., and L. R. Richardson. 1991. Genetic studies in <br />marine fishes, IV. An analysis of population structure in <br />the red drum (Sciaenops ocellatus) using mitochondrial <br />DNA. Fisheries Research 12:213-241. <br />Henderson-Arzapa]o, A. 1987. Red drum egg and larva] <br />incubation. Pages (II) 40--42 in G. Chamberlain, R. J. <br />Miget, and M. G. Haby, editors. Manual of red drum <br />aquaculture. Texas A&M University, Texas Agricultural <br />Extension Service and Sea Grant College ProgranJ, <br />College Station. <br />Higgins, K., and M. Lynch. 2001. Metapopulation extinction <br />caused by mutation accumulation. Proceedings of the <br />National Academy of Sciences of the USA 98:2928-2933. <br />Karlsson, S., E. Saillant, B. W. Bumguardner, R. R. Vega, and <br />J. K. Gold. 2008. Genetic identification of hatchery- <br />released red drum (Sciaenops ocellatus) in Texas bays <br />and estuaries. North American 10umal of Fisheries <br />Management 28:1294-1304. <br />Lacy, R. C. 1989. Ana]ysis of founder representation in <br />pedigrees: founder equivalents and founder genome <br />equivalents. Zoo Bio]ogy 8:111-123. <br />McCarty, C. E. 1987. Design and operation of a photoperiod- <br />temperature spawning system for red drum. Pages (Il) <br />27-31 in G. Chamberlain, R. J. Miget, and M. G. Haby, <br />editors. Manual of red drum aquaculture. Texas A&M <br />University, Texas Agricultural Extension Service and Sea <br />Grant College ProgranJ, College Station. <br />McEacmon, L. W., C. E. McCarty, and R. R. Vega. 1995. <br />Beneficial uses of marine fish hatcheries: enhancement of <br />red drum in Texas coastal waters. Pages 161-166 in H. L. <br />ScmanJm and R. G. Piper, editors. Uses and effects of <br />cultured fishes in aquatic ecosystems. American Fisheries <br />Society, Symposium 15, Bethesda, Maryland. <br />Nei, M., and F Tajima. 1981. Genetic drift and the estimation <br />of effective population size. Genetics 98:625-640. <br />Ryman, N., and L. Laikre. 1991. Effects of supportive <br />breeding on the genetically effective population size. <br />Conservation Biology 5:325-329. <br />Saillant, E., A. Fostier, P. Haffray, B. Menu, 1. Thimonier, S. <br />Laureau, and B. Chatain. 2002. Temperature effects and <br />genotype temperature interactions on sex determination <br />in the European sea bass (Dicentrarchus labrax L.). <br />Jonma1 of Experimental Zoology 292:494-505. <br />