Conservation Genetics Image of DNA double helix from Wikipedia Conservation of Genetic Diversity Image from www.tolweb.org Conservation of Genetic Diversity Evolution – allele frequency change through time in a population Some Mechanisms of Evolution Mutation Genetic accommodation – adaptive evolution Random processes (e.g., genetic drift) Gene flow via emigration & immigration Artificial selection Natural selection (Thank you, Darwin [& Wallace]!) – adaptive evolution Sexual selection (Thank you, Darwin!) – adaptive evolution Conservation of Genetic Diversity Mutations (substitutions, insertions, deletions, inversions) – ultimate sources of most genetic variation Generation 1 Generation 2 Small populations provide few opportunities for positive mutations to arise Conservation of Genetic Diversity Gene flow – exchange of genes between populations Pop. B Pop. A Genetic diversity erodes especially quickly in small, isolated populations Conservation of Genetic Diversity Inbreeding – results from mating by closely related individuals Pop. A Generation 1 Pop. B Generation 2 33% chance of mating with sibling 50% chance of mating with sibling Genetic diversity erodes especially quickly in small, isolated populations Conservation of Genetic Diversity Random processes (demographic bottlenecks, genetic drift, founder effects) Generation 1 Generation 2 Genetic diversity erodes especially quickly in small, isolated populations Conservation of Genetic Diversity Not all phenotypic diversity results from genetic diversity Genetic diversity helps determine evolutionary potential R. A. Fisher (1890 – 1962) An architect of the Modern Synthesis Fisher’s Fundamental Theorem: "The rate of increase in fitness [owing to selection] of any organism at any time is equal to its genetic variance in fitness at that time" Photo from Wikipedia Conservation of Genetic Diversity Genetic diversity occurs at 3 levels in a species’ gene pool: Within individuals (e.g., heterozygosity – the proportion of gene loci in an individual that contains alternative forms of alleles) Among individuals in a population Among populations Conservation of Genetic Diversity Genetic diversity helps determine evolutionary potential But, “gene pools are becoming diminished and fragmented into gene puddles” (Foose 1983) Image from www.brooklyn.cuny.edu Conservation of Genetic Diversity Genetically effective population size (Ne) – the number of individuals that would result in the same level of inbreeding, or decrease in genetic diversity through time, if the population were an idealized, panmictic (randomly mating) population Typically Ne < N (Because of variance in reproductive success and family sizes) Greater Yellowstone Ecosystem grizzlies: N ≈ 500 Ne ≈ 80 Image from www.time.com Extinction Vortex Small populations are at risk of extinction owing to the “onetwo punch” from demographics and genetics Image from Campbell & Reece (2008) Biology 8th ed., Benjamin Cummings Pubs. Genetic Tools for Conservation Pedigree analysis – especially useful for captive populations Estimation of relatedness (in the absence of pedigrees) Analysis of parentage and mating systems Forensics Species or population identification Estimation of population size Image of elephant ivory from www.guardian.co.uk Case Study: Eurasian wolf Vilà et al. (2003) Rescue of a severely bottlenecked wolf (Canis lupus) population by a single immigrant “We show here that the genetic diversity of the severely bottlenecked and geographically isolated Scandinavian population of grey wolves (Canis lupus), founded by only two individuals [in 1983, after centuries of persecution that extirpated them from the Scandinavian peninsula by 1960s], was recovered by the arrival of a single immigrant.” Quote from Vilà et al. (2003) Proc. R. Soc. Lond. B.; photo & map of Europe from Wikipedia Case Study: Eurasian wolf Vilà et al. (2003) Rescue of a severely bottlenecked wolf (Canis lupus) population by a single immigrant A single immigrant arrived onto the Scandinavian peninsula in 1991 12 50 8 4 0 0 1983 Figure from Vilà et al. (2003) Proc. R. Soc. Lond. B. 1991 2001 Number of breeding packs Estimated population size 100 Case Study: Eurasian wolf Vilà et al. (2003) Rescue of a severely bottlenecked wolf (Canis lupus) population by a single immigrant Individual heterozygosity (19 autosomal microsatellite loci) A single immigrant arrived onto the Scandinavian peninsula in 1991 Each circle = 1 wolf 1.0 Founding female (est. date of birth = 1978) Pups with d.o.b. < 1991 (only 1 bottlenecked, inbred pack) 0.5 Offspring of immigrant male Other pups with d.o.b. 1991 0 1978 1983 Figure from Vilà et al. (2003) Proc. R. Soc. Lond. B. 1991 2001 Case Study: North American wolf Adams et al. (2011) Genomic sweep and potential genetic rescue during limiting environmental conditions in an isolated wolf population “…a male wolf (Canis lupus)… immigrated [in 1997]… across Lake Superior ice to the small, inbred wolf population in Isle Royale National Park. The immigrant’s fitness so exceeded that of native wolves that within 2.5 generations he was related to every individual in the population… resulting in a selective sweep of the total genome.” Quote & photo from Adams et al. (2011) Proc. R. Soc. Lond. B.; map of North America from Wikipedia Case Study: North American wolf Adams et al. (2011) Genomic sweep and potential genetic rescue during limiting environmental conditions in an isolated wolf population “The population inbreeding coefficient (f) averaged over each individual present in the population from 1950 to 2009... Our results show that the beneficial effects of gene flow may be substantial and quickly manifest…” f 1950 1960 1970 Figure from Adams et al. (2011) Proc. R. Soc. Lond. B. 1980 1990 2000 2010 Case Study: Florida panther Johnson et al. (2010) Genetic restoration of the Florida panther (Puma concolor coryi) Eight females were translocated from Texas to Florida in 1995; “panther numbers increased threefold, genetic heterozygosity doubled, survival and fitness measures improved, and inbreeding correlates declined significantly” Figure from Johnson et al. (2010) Science