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Conservation Genetics: Lessons from Population & Evolutionary Genetics

Conservation Genetics: Lessons from Population & Evolutionary Genetics. Definition Conservation Genetics: The science of understanding how genetic issues affect the conservation and restoration of populations and species.

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Conservation Genetics: Lessons from Population & Evolutionary Genetics

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  1. Conservation Genetics: Lessons from Population & Evolutionary Genetics

  2. Definition • Conservation Genetics: • The science of understanding how genetic issues • affect the conservation and restoration of populations • and species.

  3. II. Major Issues (from Frankham 1995) • Inbreeding depression • Accumulation of deleterious alleles • Loss of genetic variance in small populations • Genetic adaptation to captivity and effect on • reintroduction success • -Fragmentation of populations • -Taxonomic uncertainty (unique?, novel?, hybrid?, • hybridize for successful reintroduction?) small population size

  4. III. Taxonomic Uncertainty Example: Dusky Sea Side Sparrow (Ammodramus maritimus nigrescens) Avise and Nelson 1989

  5. IV. Small Population Size -Most threatened/endangered species exist in Small Isolated Populations Gaston et al. 1997 (ECOGRAPHY) Newton 1997 (ECOGRAPHY) Must focus on consequences of small population size

  6. Genetic Consequences of Small Population Size: -Loss of Genetic Variation -Inbreeding Depression -Accumulation of Mutations All as a result of Drift and Fragmentation

  7. V. Drift History: Natural historians, including Darwin, noted that some variation among individuals would not result in differences in survivorship and reproduction

  8. e.g., Gulick, Hawaiian land snails exhibited great diversity of shell color patterns

  9. Changes in pattern across generations arises by chance • Drift (population genetic translation- Wright): Evolutionary process by which allele frequencies change by accidents of sampling

  10. VI. Origin of Accidents of Sampling Assume diploid population with 2 alleles at a locus A with frequency p a with frequency q Zygote = union of 2 independent gametes or union of 2 independent events Thus genotype frequencies represent binomial probability distribution: (p + q)2 or AA= p2, Aa = 2pq, aa = q2

  11. Assume: finite population size (N) Zygotes are a sample of gametes: A or a with frequency p and q Thus random sampling process will introduce variation of allele frequencies across gernation of Variance of binomial: pq/N Diploid organisms: pq/2N Loss of Heterozygosity is proportional to 1/2N or 1/2Ne (Population Geneticists use Ne because loss of heterozygosity is often greater than the census number)

  12. Effect of sampling variation after many generations Change in allele frequencey of Drosophila melanogaster populations

  13. VII. Consequences of Drift: -allele frequencies fluctuate randomly -populations vary by chance -increase variation among populations -decreased heterozygosity in populations -increased homozygosity in populations -increased genetic relatedness in population -SELECTION NOT AS EFFICIENT NeS < ¼ then deleterious alleles and new deleterious mutations will become fixed by drift (more later)

  14. VII. Consequences of Fragmentation A. Wahlund Effect: All of the same consequences as Drift decreases heterozygosity within populations increases homozygosity within populations increases genetic relatedness within populations

  15. Natural History Examples of Fragmentation (From Hamrick and Godt) # of P Gst species (within population) (among pop) pollen dispersal animal 164 36 0.2 wind 102 50 0.1 seed dispersal gravity 199 30 0.3 wind 105 43 0.1 P = % of loci with > 2 alleles Gst = proportion of genetic variation distributed among pop. FRAGMENTATION  LOSS OF GENETIC DIVERSITY WITHIN POPULATIONS

  16. Small Large Large High Density Low Density B. Further consequences of Fragmentation Allee Effect: As density decreases, ability to find mates also decreases e.g. Oostemeiger, Arnica montana, Netherlands Visitation rates in small and large populations:

  17. IX. Consequences of Inbreeding A. Inbreeding depression

  18. Low High Extinction Rate Low High Heterozygosity

  19. B. Loss of Genetic Variation Lakeside Daisey (hymenoxys acaulis var. glabra) M. Demauro, 1994 Last remaining population in Illinois Lakeside Daisey is Self Incompatible

  20. Number of Mating Groups

  21. Selection of D. melanogaster for resistance to ethanol fumes in Large vs. Small populations Weber, 1992 L = Large S = Small Resistance (minutes) Generation Consider response to global climate change!

  22. C. Mutation Accumulation NeS < ¼ 1. Fixation of ancestral mutations (From Lynch and Burger, 1995)

  23. 2. Introduction of new mutations

  24. 3. Extinction Risks Due to Mutational Meltdown R = Reproductive Rate; K = Carrying Capacity

  25. Consequences of Mutations for Small Populations Critically Depend on: Mutation Rate Distribution of Mutation Effects (all deleterious?)

  26. X. Genetic Manipulation to Counteract Small Population Size • Purging of “bad” mutations • Natural History Examples: Husband and Schemske, 1996

  27. Drift led to both the fixation and extinction of deleterious alleles

  28. Purging critically depends on genetic basis of inbreeding depression: Inbreeding depression: expression of recessive deleterious alleles in homozygous condition Dudash and Carr, 1998 Inbreeding depression due to recessive alleles

  29. B. Crossing Programs to Restore Genetic Variability Case Study: Fenster and Colleagues Chamaecrista fasciculata

  30. XI. Conclusion Small population size may lead to lower genetic fitness through fixation of deleterious alleles XII. Future Directions We Need: -Better estimates of mutation rates and effects -Field based experiments to determine if a population can be purged of deleterious mutations -Studies to quantify effect of adaptation to captivity -Better understanding of the genetic basis of adaptive differentiation

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