Title: Conservation Genetics
1Conservation Genetics
- Lecture Outline
- Basic Population Genetics
- How is genetic variation measured?
- How are evolutionary processes inferred from
patterns of genetic variation? - Scope of Conservation Genetics
- Conservation Genetics of Populations
- Is genetic variation important for evolutionary
potential? - Does genetic variation influence extinction risk?
- What are the consequences of genetic drift and
inbreeding depression in wildlife populations? - Does increasing gene flow help mitigate the
negative genetic effects of fragmentation? - Are demographic and genetic factors equally
important for understanding extinction?
2Words Well Use A Lot Today!
- Locus / Loci
- position on a chromosome
- Gene
- segment of DNA whose sequence codes for protein,
or regulates other genes - Diploid
- cell/individual has two copies of each
(homologous) chromosome - Allele
- alternative form of a gene or locus
- Homozygous
- individual with two copies of the same allele
- Heterozygous
- organism with different alleles
- Genotype
- an organisms genetic composition
3Genetic Variation
- Types
- Neutral
- Adaptive
- Detrimental
- Measures of Genetic Variation
- Polymorphism proportion of loci that are
polymorphic in a population - Heterozygosity (H) proportion of individuals in
a population that are heterozygotes at a
particular locus - Allelic Diversity number of alleles at a locus
Hawaiian Happy-face Spiders, Theridion grallator
4Data Collection
- Tissue samples
- Genetic markers
- Loci useful for distinguishing individuals and
populations - Basic methods
- PCR
- Amplify DNA
- Gel Electrophoresis
- Visualize alleles for a locus
Negative Charge
Fragments migrate
Positive Charge
5Measuring Genetic Variation
6 individuals
- Is locus A polymorphic? Locus B?
- If the locus is polymorphic, how many individuals
are heterozygotes? - Calculate H for the polymorphic loci
locus A
locus B
Kemps Ridley Sea Turtle, Lepidochelys kempii
6Measuring Genetic Variation
6 individuals
- Is locus A polymorphic? Locus B?
- Locus B only
- If the locus is polymorphic, how many individuals
are heterozygotes? - 4 individuals
- Calculate H for the polymorphic loci
- H 4/6 0.667
locus A
locus B
7Measuring Genetic Variation
6 individuals
- Allele Frequencies
- Genotype Frequencies
- Locus B
- Close allele B1
- Far allele B2
-
- F(B1) 6/12 0.5
- F(B2) 6/12 0.5
- F(B1B1) 1/6 0.167
- F(B1B2) 4/6 0.67
- F(B2B2) 1/6 0.167
locus A
locus B
8Evolution
- Change in allele frequencies across generations
- Hardy-Weinberg Principle
- Allele frequencies in a population will not
change over time unless an evolutionary process
is acting on the population - Genotype frequencies remain constant after 1
generation of random mating
Weinberg
9Hardy-Weinberg Equilibrium
- Can calculate genotype frequencies for a given
set of allele frequencies when the following
assumptions are met - Hardy-Weinberg model as an animated question
mark
Departure from HW equilibrium suggests that
important evolutionary processes are acting on
the population of interest.
10Hardy-Weinberg
- Consider a single locus with 2 alleles A1 and A2
-
- Allele Frequencies p freq. of A1
- q
freq. of A2 - p q 1
-
- Genotype Frequencies p2 freq. of A1A1
- 2pq freq. of A1A2
- q2 freq. of A2A2
- p2 2pq q2 1
11Rana pipiens Example
- 2000 Individuals
- Observed Genotype Frequencies
- BB 600/2000 0.3
- Bb 400/2000 0.2
- bb 1000/2000 0.5
-
- Observed Allele Frequencies
- B 1600/4000 0.4 p
- b 2400/4000 0.6 q
- Expected Genotype Frequencies
- BB p2 0.16 320 ind.
- Bb 2pq 0.48 960 ind.
- bb q2 0.36 720 ind.
b allele
Wild Type
B allele
Burnsi
Observed N Expected N BB 600
320 Bb 400 960 Bb 1000 720
12Daphnia obtusa
- Spitze (1993)
- PGI Locus
- Genotyped 127 individuals from Nothing Pond in
Morton, IL -
- RR 11
- Rr 55
- rr 61
- Calculate the observed genotype and allele
frequencies. - Calculate the expected genotype frequencies under
HWE. - Is this population in HWE?
13Daphnia obtusa
- Observed Genotype Frequencies
- RR 11 11/127 0.087
- Rr 55 55/127 0.43
- rr 61 61/127 0.48
- Observed Allele Frequencies
- R 77 77/254 0.30
- r 177 177/254 0.70
- Expected Genotype Frequencies
- F N
- RR p2 0.302 0.09 ? 11.43
- Rr 2pq 20.30.7 0.42 ? 53.34
- rr q2 0.702 0.49 ? 62.23
- Is this population in HWE? Yes
14Conservation Genetics
- Otto Frankel 1974 Genetic conservation our
evolutionary responsibility. - Key contribution to conservation biology focus
on long-term evolutionary potential in species -
First we should get to know much more about
the structure and dynamics of natural populations
and communities Second, even now the geneticist
can play a part in injecting genetic
considerations into the planning of reserves of
any kind Finally, reinforcing the grounds for
nature conservation with an evolutionary
perspective may help to give conservation a
permanence which a utilitarian, and even an
ecological grounding, fail to provide in mens
minds.
15Topics in Conservation Genetics
- Management and Reintroduction of Captive Species
- Individual and Species Identification
- Species ID, population of origin, sex,
mark-recapture - Genealogies and Kin Relationships
- Parentage, reproductive success
- Taxonomic and Phylogenetic Relationships
- USFWS Priority taxonomic distinctiveness
- ESA Evolutionary Significant Units
- Genetic Population Structure
- Effects of habitat loss, fragmentation, and
isolation on distribution of genetic variation - Historical effects, effective population size,
movement rates and connectivity - Hybridization and Introgression
- ESA policy
- Genetics of Adaptation
- Relationships between adaptation, fitness, and
the genetic basis of traits influencing fitness
16Genetic Variation and Adaptation
- Of all forces that influence population genetic
structure, natural selection is the only force
producing adaptive change - Acts on heritable, phenotypic variation
Genetic variation is the raw material for
adaptive evolution. Maintaining evolutionary
potential is achieved by maintaining genetic
variation.
17Genetic Variation and Extinction Risk
- Extinction is a demographic process, caused by
two main types of threats - Deterministic ? e.g., habitat destruction
- Stochastic ? random changes in genetic,
demographic, or environmental factors - Two types of genetic stochasticity
- Drift ? random change in allele frequencies
- Inbreeding ? mating with relatives
- Genetic stochasticity erodes genetic variation
- Qualitative effect loss of alleles
- Quantitative effect decline in heterozygosity
18Genetic Drift
- Allele frequencies change from generation to
generation due random sampling error - Some alleles get passed on, some dont
Drift erodes genetic variation within
populations, and increases variation between
populations
19Effect of N on Genetic Drift
N 15
N 500
Strength of genetic drift is inversely related to
population size.
s selective disadvantage of a detrimental
allele ( reduction in fitness) Ne
effective population size
20Selection and Drift
Miller and Lambert 2004
Chatham Island black robin
- Two consequences of drift overwhelming selection
in small populations - Deleterious alleles not weeded out by selection
- Local adaptation is compromised
21Genetic Drift and Fragmentation
- Habitat Loss
- Crash in population size
- population bottleneck
- Isolation
- Metapopulation structure
- Extinction-colonization dynamics
- Colonization of resource patch
- founder event
Regal Fritillary Butterfly
22Genetic Drift and Fragmentation
Allelic Differentiation MW gt GP Genetic
Differentiation (FST) MW gt GP Greatest
between MW/GP E Allelic Diversity E
9.00 MW 16.15 GP 22.65
GP unfragmented MW recently fragmented E
historically isolated
HT heterozygosity in metapopulation HS
heterozygosity in subpopulation
Williams et al. 2003
23Fitness Effects of Genetic Drift
- Large changes in allele frequency
- Deleterious alleles occur at low frequency, and
most rare alleles are lost following bottlenecks - BUT, every individual carries harmful alleles,
and these alleles increase in frequency following
bottlenecks - Recovery time is critical
- Loss of allelic diversity
- Greater effect than on heterozygosity
- E.g., loss of MHC alleles more susceptible to
disease
24Inbreeding
- Inbreeding ? mating between individuals that are
more closely related than expected by chance
Inbreeding increases homozygosity at all loci.
The most extreme form of inbreeding is selfing
Generation Heterozygotes 0 100
1 50 2 25 3 12.5
25Inbreeding Depression
- Reduction in fitness of progeny from matings
between related individuals relative to progeny
of unrelated individuals - Can contribute to population extinction
- Causes
- Increased homozygosity
- Reduces fitness due to expression of deleterious
recessive alleles - Decreased heterozygosity
- Reduces fitness in cases when heterozygotes have
selective advantage
26Inbreeding Depression and Extinction
- Inbreeding depression must affect traits
influencing population viability - Saccheri et al. 1998
- Glanville fritillary butterfly, 42 populations,
Finland
Factors Influencing Extinction Model Parameters
Variation Population size
24 Regional trend in N 20 Flower
abundance 12 Heterozygosity
26
low N
Extinction Probability
high N
Fitness Traits Affected Larval survival Adult
longevity Egg hatching rate
27Drift, Inbreeding, and Fragmentation
- Habitat loss and decreased connectivity lead to
loss of genetic variation due to drift and
inbreeding - Inbreeding depression
- Reduced heterozygosity due to drift
- Increased homozygosity due to inbreeding
- Loss of rare alleles
- Inefficiency of selection
- Mutational meltdown
- Decreased evolutionary potential
Mills
28Conservation Measures
- Facilitate an increase in population size
- Translocation
- Gene flow via increased connectivity
- Improve matrix, construct corridors
- Gene flow effective dispersal
- Disadvantages of increasing movement
- Demographic
- Disease, social structure
- Genetic
- Outbreeding depression ? reduction in fitness of
hybrids - Parents from different populations are locally
adapted - Disruption of coadapted gene complexes
- One-Migrant-Per-Generation Rule (Mills and
Allendorf 1993)
29Greater Prairie Chicken in Illinois
Mean Alleles Per Locus Illinois
3.67 Kansas 5.83 Minn.
5.33 Nebraska 5.83 Illiinos
5.12 before bottleneck
Inbreeding depression due to Drift Inbreedin
g Counteracted by translocations in 1992.
Westemeier et al. 1998
30Genetics and Demography
- Lande (1988) argues that basic demography has
been neglected, and the effect of genetic
structure on extinction has been over-emphasized - Consider why demography may be of more immediate
importance than genetics in small populations. - What demographic factors influence extinction?
- Are there interactions between demographic and
genetic effects of habitat loss and isolation
that can increase extinction probability?
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