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An Analysis of the Observed Heterozygosity of Lake Trout

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An Analysis of the Observed Heterozygosity of Lake Trout
An analysis of the observed heterozygosity of Lake Trout populations from three lakes: Devil, Eagle, and Loughborough, inferred from microsatellite genotypes.

Abstract:
This study was undertaken in order to compare the heterozygosity of three Lake Trout populations at various loci. Samples of twenty-five Lake Trout were collected from three lakes: Devil, Eagle and Loughborough, all three of which are situated north of Kingston, Ontario. An autoradiograph was used to analyze the genotypes of the individuals at six different loci of microsatellites, which are repeat sequences in the DNA that are neutral and do not code for proteins. This data was used to compare the genetic diversity of the three different trout populations. Numerical values for observed heterozygosity (Ho) were then generated using the data and the Doh heterozygosity calculator. The results have indicated that the mean heterozygosity in respect of Devil Lake trout was significantly greater than that of the trout in Eagle Lake (p=2.89E-7) as well as that of Loughborough Lake (p=1.44E-19). Furthermore, the mean heterozygosity for Eagle Lake trout was significantly greater than that of Loughborough Lake (p=2.52E-6). This may be due to the fact that natural selection acts as a force to cause inbreeding to eliminate harmful genes causing low heterozygosity in a population. In addition, human and natural effects occurring in the lakes, for example, fishing and water temperature may cause differences in heterozygosity. Understanding and using these findings may help with sustaining fish populations.

Introduction:
Heterozygosity is the measure of the genetic variation in a population at a particular gene locus. Genetic variation within a population is important in maintaining or increasing the fitness of members in the population and ultimately the survival of the species.
Fitness describes the capability of an individual species of a certain genotype to reproduce, and is usually equal to



Cited: Ellstrand N., Elam R. 1993. Population genetic consequences of small population size: implications of plant conservation. Annual Review of Ecological Systems. 24: 217-242. Evans D., Casselman J., Wilcox C. 1991. Effects of Exploitation, Loss of Nursery Habitat, and Stocking on the Dynamics and Productivity of Lake Trout Populations in Ontario Lakes. Ontario Ministry of Natural Resources. 193: 1-3 Ferguson M. 1990. Enzyme Heterozygosity and growth in Rainbow Trout: Genetic and Physiological Explanations. The Genetical Society of Great Britain. 68: 115-122. Ontario Ministry of Natural Resources. 1970. Map of Eagle Lake. Map of Loughborough Lake. Map of Devil Lake. Queen’s University Map and Air Photo Library. 613. Pujolar J., Maes G., Vancoillie C., Volckaert F. 2005. Growth Rate Correlates to Individual Heterozygosity in the European Eel, Anguilla Anguilla L. Evolution. 59: 189-199. Rowe G., Beebee T., Burke T. 1999. Microsatellite heterozygosity, fitness and demography in natterjack toads Bufo calamita. Animal Conservation. 2: 85-92. Smith P., Francis R., McVeagh M. 1991. Loss of Genetic Diversity due to Fishing Pressure. Fisheries Research. 10: 309-316. Volckaert F., Zouros E. 1989. Allozyme and physiological variation in the scallop Placopecten magellanicus and a general model for the effects of heterozygosity on fitness in marine molluscs. Marine Biology. 103: 51-61 Zimmerman G., Richmond M. 1981. Increased Heterozygosity at the Mdh-B Locus in Fish Inhabiting a Rapidly Fluctuating Thermal Environment. American Fisheries Society. 110: 410-416

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