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Adaption to Climate Change: A Genetic Perspective
from a Small Mammal in the Coast Mountains of BC.
Philippe Henry & Michael Russello
Talk Outline
• Conservation Biology
• Population genetics
• Population genomics
• Application to American pikas
Conservation Biology
• C
Intro
• Scientific study of the nature and status of
the Earth’s biodiversity
• Aim to preserve ecosystems, species and
evolutionary potential (genetics)
• Termed coined in 1978 at UCSD by Michael
Soulé and others
Conservation Biology
• C
Intro
• Scientific study of the nature and status of
the Earth’s biodiversity
• Aim to preserve ecosystems, species and
evolutionary potential (genetics)
• Termed coined in 1978 at UCSD by Michael
Soulé and others
Conservation Biology
• C
Intro
• Scientific study of the nature and status of
the Earth’s biodiversity
• Aim to preserve ecosystems, species and
evolutionary potential (genetics)
• Termed coined in 1978 at UCSD by Michael
Soulé and others
Why conservation ?
• C
Intro
• Habitat loss, degradation and fragmentation
• Invasive species
• Overexploitation of natural resources
• Pollution and diseases
• Climate change
Why conservation ?
• C
Intro
• Habitat loss, degradation and fragmentation
• Invasive species
• Overexploitation of natural resources
• Pollution and diseases
• Climate change
Why conservation ?
• C
Intro
• Habitat loss, degradation and fragmentation
• Invasive species
• Overexploitation of natural resources
• Pollution and diseases
• Climate change
Why conservation ?
• C
Intro
• Habitat loss, degradation and fragmentation
• Invasive species
• Overexploitation of natural resources
• Pollution and diseases
• Climate change
Why conservation ?
• C
Intro
• Habitat loss, degradation and fragmentation
• Invasive species
• Overexploitation of natural resources
• Pollution and diseases
• Climate change
Why conservation ?
• C
Intro
• Sixth mass extinction crisis
- 1 in 4 mammal
- 1 in 4 conifer
- 1 in 3 amphibian
- 1 in 8 birds are threatened
- extinction rates are 1000 times the norm
- at this pace, mass extinction will occur in 200 - 500
years
Why conservation ?
• C
Intro
• Sixth mass extinction crisis
- 1 in 4 mammal
- 1 in 4 conifer
- 1 in 3 amphibian
- 1 in 8 birds are threatened
- extinction rates are 1000 times the norm
- at this pace, mass extinction will occur in 200 - 500
years
Why conservation ?
• C
Intro
• Sixth mass extinction crisis
- 1 in 4 mammal
- 1 in 4 conifer
- 1 in 3 amphibian
- 1 in 8 birds are threatened
- extinction rates are 1000 times the norm
- at this pace, mass extinction will occur in 200 - 500
years
Why conservation ?
• C
Intro
• Sixth mass extinction crisis
- 1 in 4 mammal
- 1 in 4 conifer
- 1 in 3 amphibian
- 1 in 8 birds are threatened
- extinction rates are 1000 times the norm
- at this pace, mass extinction will occur in 200 - 500
years
Why conservation ?
• C
Intro
• Sixth mass extinction crisis
- 1 in 4 mammal
- 1 in 4 conifer
- 1 in 3 amphibian
- 1 in 8 birds are threatened
- extinction rates are 1000 times the norm
- at this pace, mass extinction will occur in 200 - 500
years
Why conservation ?
• C
Intro
• Sixth mass extinction crisis
- 1 in 4 mammal
- 1 in 4 conifer
- 1 in 3 amphibian
- 1 in 8 birds are threatened
- extinction rates are 1000 times the norm
- at this pace, mass extinction will occur in 200 - 500
years
Why conservation ?
• C
Intro
• Sixth mass extinction crisis
- 1 in 4 mammal
- 1 in 4 conifer
- 1 in 3 amphibian
- 1 in 8 birds are threatened
- extinction rates are 1000 times the norm
- at this pace, mass extinction will occur in 200 - 500
years (Barnosky et al 2011, Nature)
Why conservation ?
• C
Intro
• Philosophical / Ethical
- Estetics
- Biophilia
• Ecosystem services
- Clean water / air
- Economical benefits
Why conservation ?
• C
Intro
• Philosophical / Ethical
- Estetics
- Biophilia
• Ecosystem services
- Clean water / air
- Economical benefits
Why conservation ?
• C
Intro
• Philosophical / Ethical
- Estetics
- Biophilia
• Ecosystem services
- Clean water / air
- Economical benefits
Why conservation ?
• C
Intro
• Philosophical / Ethical
- Estetics
- Biophilia
• Ecosystem services
- Clean water / air
- Economical benefits
Why conservation ?
• C
Intro
• Philosophical / Ethical
- Estetics
- Biophilia
• Ecosystem services
- Clean water / air
- Economical benefits
Conservation Genetics
• Arose in the 1980’s as a crisis discipline
• With the aim to preserve species
evolutionary potential (genetic variation)
• Under the central tenet that small, isolated
populations are at risk of genetic erosion
Intro
Conservation Genetics
• Arose in the 1980’s as a crisis discipline
• With the aim to preserve species
evolutionary potential (genetic variation)
• Under the central tenet that small, isolated
populations are at risk of genetic erosion
Intro
Conservation Genetics
• Arose in the 1980’s as a crisis discipline
• With the aim to preserve species
evolutionary potential (genetic variation)
• Under the central tenet that small, isolated
populations are at risk of genetic erosion
Intro
Conservation Genetics
• Small population size:
- Dominated by genetic drift and inbreeding
- Genetic drift: random fixation and loss of
alleles, whether adaptive or deleterious
- Inbreeding: increasing homozygosity
Intro
Conservation Genetics
• Small population size:
- Dominated by genetic drift and inbreeding
- Genetic drift: random fixation and loss of
alleles, whether adaptive or deleterious
- Inbreeding: increasing homozygosity
Intro
Conservation Genetics
• Small population size:
- Dominated by genetic drift and inbreeding
- Genetic drift: random fixation and loss of
alleles, whether adaptive or deleterious
- Inbreeding: increasing homozygosity
Intro
Conservation Genetics
• Small population size:
- Dominated by genetic drift and inbreeding
- Genetic drift: random fixation and loss of
alleles, whether adaptive or deleterious
- Inbreeding: increasing homozygosity
Intro
Conservation Genetics
• Genetic drift and inbreeding:
- Inbreeding depression
- Reduction in individual fitness
- Compromised evolutionary potential
Intro
Conservation Genetics
• Genetic drift and inbreeding:
- Inbreeding depression
- Reduction in individual fitness
- Compromised evolutionary potential
Intro
Conservation Genetics
• Genetic drift and inbreeding:
- Inbreeding depression
- Reduction in individual fitness
- Compromised evolutionary potential
Intro
Conservation Genetics
• Genetic drift and inbreeding:
- Inbreeding depression
- Reduction in individual fitness
- Compromised evolutionary potential
Intro
Conservation Genetics
• Genetic variation = evolutionary potential of
populations or species
• There are two principal types of genetic
variation:
- Neutral  (reflects demographic patterns)
- Adaptive  (reflects variation under natural
selection)
Intro
Conservation Genetics
• Genetic variation = evolutionary potential of
populations or species
• There are two principal types of genetic
variation:
- Neutral  (reflects demographic patterns)
- Adaptive  (reflects variation under natural
selection)
Intro
Conservation Genetics
• Genetic variation = evolutionary potential of
populations or species
• There are two principal types of genetic
variation:
- Neutral  (reflects demographic patterns)
- Adaptive  (reflects variation under natural
selection)
Intro
Conservation Genetics
• Genetic variation = evolutionary potential of
populations or species
• There are two principal types of genetic
variation:
- Neutral  (reflects demographic patterns)
- Adaptive  (reflects variation under natural
selection)
Intro
• Neutral genetic variation:
- population genetic structure
- demographic events, (bottlenecks and population
expansions)
- migration and gene flow
 Valuable information to help prioritize
populations for conservation efforts
X. Does not generally inform on long term
evolutionary potential of populations
Conservation Genetics
Intro
• Neutral genetic variation:
- population genetic structure
- demographic events, (bottlenecks and population
expansions)
- migration and gene flow
 Valuable information to help prioritize
populations for conservation efforts
X. Does not generally inform on long term
evolutionary potential of populations
Conservation Genetics
Intro
• Neutral genetic variation:
- population genetic structure
- demographic events, (bottlenecks and population
expansions)
- migration and gene flow
 Valuable information to help prioritize
populations for conservation efforts
X. Does not generally inform on long term
evolutionary potential of populations
Conservation Genetics
Intro
• Neutral genetic variation:
- population genetic structure
- demographic events, (bottlenecks and population
expansions)
- migration and gene flow
 Valuable information to help prioritize
populations for conservation efforts
X. Does not generally inform on long term
evolutionary potential of populations
Conservation Genetics
Intro
• Neutral genetic variation:
- population genetic structure
- demographic events, (bottlenecks and population
expansions)
- migration and gene flow
 Valuable information to help prioritize
populations for conservation efforts
X. Does not generally inform on long term
evolutionary potential of populations
Conservation Genetics
Intro
• Neutral genetic variation:
- population genetic structure
- demographic events, (bottlenecks and population
expansions)
- migration and gene flow
 Valuable information to help prioritize
populations for conservation efforts
X. Does not generally inform on long term
evolutionary potential of populations
Conservation Genetics
Intro
Genetics -> Genomics
Intro
• Complement conservation genetics with the use of
a large number of molecular markers
• Concerned with the characterization of adaptive
genetic variation
- shed light on the evolutionary potential of
populations
- assist management decisions, especially with
regard to adaptation to environmental changes
Conservation Genomics
Intro
• Complement conservation genetics with the use of
a large number of molecular markers
• Concerned with the characterization of adaptive
genetic variation
- shed light on the evolutionary potential of
populations
- assist management decisions, especially with
regard to adaptation to environmental changes
Conservation Genomics
Intro
• Complement conservation genetics with the use of
a large number of molecular markers
• Concerned with the characterization of adaptive
genetic variation
- shed light on the evolutionary potential of
populations
- assist management decisions, especially with
regard to adaptation to environmental changes
Conservation Genomics
Intro
• Complement conservation genetics with the use of
a large number of molecular markers
• Concerned with the characterization of adaptive
genetic variation
- shed light on the evolutionary potential of
populations
- assist management decisions, especially with
regard to adaptation to environmental changes
Conservation Genomics
Intro
• Impact of habitat fragmentation or climate change
on selectively important variation
• Mechanisms underlying inbreeding depression
• Role of gene-environment interaction
• Gene expression
Conservation Genomics
Intro
• Impact of habitat fragmentation or climate change
on selectively important variation
• Mechanisms underlying inbreeding depression
• Role of gene-environment interaction
• Gene expression
Conservation Genomics
Intro
• Impact of habitat fragmentation or climate change
on selectively important variation
• Mechanisms underlying inbreeding depression
• Role of gene-environment interaction
• Gene expression
Conservation Genomics
Intro
• Impact of habitat fragmentation or climate change
on selectively important variation
• Mechanisms underlying inbreeding depression
• Role of gene-environment interaction
• Gene expression
Conservation Genomics
Intro
Climate change and the
American pika
• Species sensitive to high ambient temperatures
• Contemporary climate warming may be partly
responsible for extirpation of its southern
populations
• Good candidate to study the genetic basis of
local adaptation since it is distributed along
altitudinal gradients in BC
Climate change and the
American pika
• Species sensitive to high ambient temperatures
• Contemporary climate warming may be partly
responsible for extirpation of its southern
populations
• Good candidate to study the genetic basis of
local adaptation since it is distributed along
altitudinal gradients in BC
Climate change and the
American pika
• Species sensitive to high ambient temperatures
• Contemporary climate warming may be partly
responsible for extirpation of its southern
populations
• Good candidate to study the genetic basis of
local adaptation since it is distributed along
altitudinal gradients in BC
Study species
Study species
Taxonomy
• American Pika: Ochotona princeps
• 5 ssp found throughout western NA
• 2 ssp described in BC
• Taxonomy based on morphology, mitochondrial DNA
lineage and call dialects (Hafner & Smith, 2010)
Study species
Taxonomy
• American Pika: Ochotona princeps
• 5 ssp found throughout western NA
• 2 ssp described in BC
• Taxonomy based on morphology, mitochondrial DNA
lineage and call dialects (Hafner & Smith, 2010)
Study species
Taxonomy
• American Pika: Ochotona princeps
• 5 ssp found throughout western NA
• 2 ssp described in BC
• Taxonomy based on morphology, mitochondrial DNA
lineage and call dialects (Hafner & Smith, 2010)
Study species
Taxonomy
• American Pika: Ochotona princeps
• 5 ssp found throughout western NA
• 2 ssp described in BC
• Taxonomy based on morphology, mitochondrial DNA
lineage and call dialects (Hafner & Smith, 2010)
Study species
Distribution
Study species
Life History
• Habitat specific to Talus slopes
• Do not hibernate and make hay-piles
• Defend individual territories
• 2-3 young successfully weaned per year
• Relatively long-lived (5-7 years)
Study species
Life History
• Habitat specific to Talus slopes
• Do not hibernate and make hay-piles
• Defend individual territories
• 2-3 young successfully weaned per year
• Relatively long-lived (5-7 years)
Study species
Life History
• Habitat specific to Talus slopes
• Do not hibernate and make hay-piles
• Defend individual territories
• 2-3 young successfully weaned per year
• Relatively long-lived (5-7 years)
Study species
Life History
• Habitat specific to Talus slopes
• Do not hibernate and make hay-piles
• Defend individual territories
• 2-3 young successfully weaned per year
• Relatively long-lived (5-7 years)
Study species
Life History
• Habitat specific to Talus slopes
• Do not hibernate and make hay-piles
• Defend individual territories
• 2-3 young successfully weaned per year
• Relatively long-lived (5-7 years)
Study species
Dispersal
• Young are generally philopatric
• If no territories are available, young will disperse
• Mortality during dispersal is high
• Evidence for gene-flow up to 3km
Study species
Dispersal
• Young are generally philopatric
• If no territories are available, young will disperse
• Mortality during dispersal is high
• Evidence for gene-flow up to 3km
Study species
Dispersal
• Young are generally philopatric
• If no territories are available, young will disperse
• Mortality during dispersal is high
• Evidence for gene-flow up to 3km
Study species
Dispersal
• Young are generally philopatric
• If no territories are available, young will disperse
• Mortality during dispersal is high
• Evidence for gene-flow up to 3km
Study species
Susceptibility to climate change
• Widespread distribution during Pleistocene
• Contemporary climate warming may be responsible
for the extirpation of one quarter of Pika
populations in the Great Basin USA
• Their distribution has shifted 100m upslope per
decade
Study species
Susceptibility to climate change
• Widespread distribution during Pleistocene
• Contemporary climate warming may be responsible
for the extirpation of one quarter of Pika
populations in the Great Basin USA
• Their distribution has shifted 100m upslope per
decade
Study species
Susceptibility to climate change
• Widespread distribution during Pleistocene
• Contemporary climate warming may be responsible
for the extirpation of one quarter of Pika
populations in the Great Basin USA
• Their distribution has shifted 100m upslope per
decade
Objectives
• Shed light on population genetic
structure and demographic history
• Identify genomic region under
selection
Objectives
• Shed light on population genetic
structure and demographic history
• Identify genomic region under
selection
Study site
Methods
Study site
10 KM
The Hill
~ 1500 m
~ 800 m
~ 300 m
2 km
Methods
Nusatsum
~ 1500 m
~ 800 m
2 km
Methods
Clayton Falls – M. Gurr
~ 1500 m
~ 0 m
2 km
Methods
Sampling design
25 m25 m
Methods
Sampling design
25 m25 m
- 15 - 30 hair snares set up at each site
- Collected 300 individual hair samples
- 270 high quality DNA samples
Methods
Sampling
Sampling
Sampling
Labwork
• DNA extracted from 300 hair samples
collected in the summers 2008, 2009 and
2010
• 2 types of genetic markers amplified by
PCR:
- microsatellites
- AFLP
Microsatellite genotyping
Methods
- Popular marker in population genetics
- Neutral
- Highly variable
Microsatellite genotyping
-10 microsatellite loci amplified in our 270 DNA samples
- Resulting in a probability of identity of 0.00029
Methods
AFLP genotyping
- Markers distributed throughout the genome (genome scan)
- Anonymous bands
Methods
AFLP genotyping
- 20 selective primer pairs
- 1509 bands amplified in our 270 DNA samples
Methods
Analyses
• Identify individuals based on multilocus
genotypes = DNA fingerprint
• Assessment of population genetic structure
• Calculations of genetic diversity indices
• Estimates of demographic history
Methods
Microsatellites
Analyses
• Identification of “outlier” loci (under
selection)
• Identification of main driving force through
which selection acts
Methods
AFLP
Natural History
25 m
- Up to 7 different individuals sampled
in the same hair snare
Results
Natural History
25 m
- Up to 7 different individuals sampled
In the same hair snare
- Neighboring hair snares recovered
the same individuals in 4 cases
Results
Natural History
25 m
- Up to 4 different individuals
sampled in the same hair snare
- Neighboring hair snares recovered
the same individuals in 4 cases
- In one case, the same individual
was sampled 155m apart
Results
Population Structure
Results
Population Structure
Results
Genetic variability
Results
* * * 
Inbreeding
Results
Bottleneck
Test High 1+2 Mid Low 1 Low 2
Wilcoxon * * * NS
Mode Shift * NS NS NS
M-ratio NS NS NS NS
Results
No evidence for reduction
in population size
~ 1500 m
~ 800 m
~ 300 m
2 km
Outliers Hill
Results
~ 1500 m
~ 800 m
~ 300 m
2 km
Outliers Hill
Results
Outliers Nusatsum
~ 1500 m
~ 800 m
2 km
Methods
Outliers Nusatsum
~ 1500 m
~ 800 m
2 km
Methods
Outliers Clayton – M. Gurr
~ 1500 m
~ 0 m
2 km
Methods
Outliers Clayton – M. Gurr
~ 1500 m
~ 0 m
2 km
Methods
Summary Outliers
Methods
TTC________E33T37_58_________ACT
TCG________E38T37_289_______ACT
Summary Outliers
Methods
6.4°C
2183mm
2.2°C
2863mm
2.4°C
2889mm
3.8°C
2571mm
4.7°C
711mm
2.7°C
706mm
0.3°C
848mm
Next step
• Cloning of outlier AFLP fragments
• BLAST against rabbit genome to identify genomic
region under selection
• Next generation transcriptome sequencing
- SNP discovery
Next step
• Cloning of outlier AFLP fragments
• BLAST against rabbit genome to identify genomic
region under selection
• Next generation transcriptome sequencing
- SNP discovery
Next step
• Cloning of outlier AFLP fragments
• BLAST against rabbit genome to identify genomic
region under selection
• Next generation transcriptome sequencing
- SNP discovery
Overall significance
• Hill and Nusatsum / Clayton- M.Gurr represent
two different “populations”
• Lowest genetic variability found at Clayton-
M.Gurr
-> Priority population
• Different outliers found in the different
transects. Need to investigate the effect of
environmental variables on genes
Overall significance
• Hill and Nusatsum / Clayton- M.Gurr represent
two different “populations”
• Lowest genetic variability found at Clayton-
M.Gurr
-> Priority population
• Different outliers found in the different
transects. Need to investigate the effect of
environmental variables on genes
Overall significance
• Hill and Nusatsum / Clayton- M.Gurr represent
two different “populations”
• Lowest genetic variability found at Clayton-
M.Gurr
-> Priority population
• Different outliers found in the different
transects. Need to investigate the effect of
environmental variables on genes
Acknowledgements
- Russello Lab
- Mary Peacock
- Kurt Galbreath
- Tweedsmuir Provincial Park

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Adaptation to climage change: a genetic perspective

  • 1. Adaption to Climate Change: A Genetic Perspective from a Small Mammal in the Coast Mountains of BC. Philippe Henry & Michael Russello
  • 2. Talk Outline • Conservation Biology • Population genetics • Population genomics • Application to American pikas
  • 3. Conservation Biology • C Intro • Scientific study of the nature and status of the Earth’s biodiversity • Aim to preserve ecosystems, species and evolutionary potential (genetics) • Termed coined in 1978 at UCSD by Michael Soulé and others
  • 4. Conservation Biology • C Intro • Scientific study of the nature and status of the Earth’s biodiversity • Aim to preserve ecosystems, species and evolutionary potential (genetics) • Termed coined in 1978 at UCSD by Michael Soulé and others
  • 5. Conservation Biology • C Intro • Scientific study of the nature and status of the Earth’s biodiversity • Aim to preserve ecosystems, species and evolutionary potential (genetics) • Termed coined in 1978 at UCSD by Michael Soulé and others
  • 6. Why conservation ? • C Intro • Habitat loss, degradation and fragmentation • Invasive species • Overexploitation of natural resources • Pollution and diseases • Climate change
  • 7. Why conservation ? • C Intro • Habitat loss, degradation and fragmentation • Invasive species • Overexploitation of natural resources • Pollution and diseases • Climate change
  • 8. Why conservation ? • C Intro • Habitat loss, degradation and fragmentation • Invasive species • Overexploitation of natural resources • Pollution and diseases • Climate change
  • 9. Why conservation ? • C Intro • Habitat loss, degradation and fragmentation • Invasive species • Overexploitation of natural resources • Pollution and diseases • Climate change
  • 10. Why conservation ? • C Intro • Habitat loss, degradation and fragmentation • Invasive species • Overexploitation of natural resources • Pollution and diseases • Climate change
  • 11. Why conservation ? • C Intro • Sixth mass extinction crisis - 1 in 4 mammal - 1 in 4 conifer - 1 in 3 amphibian - 1 in 8 birds are threatened - extinction rates are 1000 times the norm - at this pace, mass extinction will occur in 200 - 500 years
  • 12. Why conservation ? • C Intro • Sixth mass extinction crisis - 1 in 4 mammal - 1 in 4 conifer - 1 in 3 amphibian - 1 in 8 birds are threatened - extinction rates are 1000 times the norm - at this pace, mass extinction will occur in 200 - 500 years
  • 13. Why conservation ? • C Intro • Sixth mass extinction crisis - 1 in 4 mammal - 1 in 4 conifer - 1 in 3 amphibian - 1 in 8 birds are threatened - extinction rates are 1000 times the norm - at this pace, mass extinction will occur in 200 - 500 years
  • 14. Why conservation ? • C Intro • Sixth mass extinction crisis - 1 in 4 mammal - 1 in 4 conifer - 1 in 3 amphibian - 1 in 8 birds are threatened - extinction rates are 1000 times the norm - at this pace, mass extinction will occur in 200 - 500 years
  • 15. Why conservation ? • C Intro • Sixth mass extinction crisis - 1 in 4 mammal - 1 in 4 conifer - 1 in 3 amphibian - 1 in 8 birds are threatened - extinction rates are 1000 times the norm - at this pace, mass extinction will occur in 200 - 500 years
  • 16. Why conservation ? • C Intro • Sixth mass extinction crisis - 1 in 4 mammal - 1 in 4 conifer - 1 in 3 amphibian - 1 in 8 birds are threatened - extinction rates are 1000 times the norm - at this pace, mass extinction will occur in 200 - 500 years
  • 17. Why conservation ? • C Intro • Sixth mass extinction crisis - 1 in 4 mammal - 1 in 4 conifer - 1 in 3 amphibian - 1 in 8 birds are threatened - extinction rates are 1000 times the norm - at this pace, mass extinction will occur in 200 - 500 years (Barnosky et al 2011, Nature)
  • 18. Why conservation ? • C Intro • Philosophical / Ethical - Estetics - Biophilia • Ecosystem services - Clean water / air - Economical benefits
  • 19. Why conservation ? • C Intro • Philosophical / Ethical - Estetics - Biophilia • Ecosystem services - Clean water / air - Economical benefits
  • 20. Why conservation ? • C Intro • Philosophical / Ethical - Estetics - Biophilia • Ecosystem services - Clean water / air - Economical benefits
  • 21. Why conservation ? • C Intro • Philosophical / Ethical - Estetics - Biophilia • Ecosystem services - Clean water / air - Economical benefits
  • 22. Why conservation ? • C Intro • Philosophical / Ethical - Estetics - Biophilia • Ecosystem services - Clean water / air - Economical benefits
  • 23. Conservation Genetics • Arose in the 1980’s as a crisis discipline • With the aim to preserve species evolutionary potential (genetic variation) • Under the central tenet that small, isolated populations are at risk of genetic erosion Intro
  • 24. Conservation Genetics • Arose in the 1980’s as a crisis discipline • With the aim to preserve species evolutionary potential (genetic variation) • Under the central tenet that small, isolated populations are at risk of genetic erosion Intro
  • 25. Conservation Genetics • Arose in the 1980’s as a crisis discipline • With the aim to preserve species evolutionary potential (genetic variation) • Under the central tenet that small, isolated populations are at risk of genetic erosion Intro
  • 26. Conservation Genetics • Small population size: - Dominated by genetic drift and inbreeding - Genetic drift: random fixation and loss of alleles, whether adaptive or deleterious - Inbreeding: increasing homozygosity Intro
  • 27. Conservation Genetics • Small population size: - Dominated by genetic drift and inbreeding - Genetic drift: random fixation and loss of alleles, whether adaptive or deleterious - Inbreeding: increasing homozygosity Intro
  • 28. Conservation Genetics • Small population size: - Dominated by genetic drift and inbreeding - Genetic drift: random fixation and loss of alleles, whether adaptive or deleterious - Inbreeding: increasing homozygosity Intro
  • 29. Conservation Genetics • Small population size: - Dominated by genetic drift and inbreeding - Genetic drift: random fixation and loss of alleles, whether adaptive or deleterious - Inbreeding: increasing homozygosity Intro
  • 30. Conservation Genetics • Genetic drift and inbreeding: - Inbreeding depression - Reduction in individual fitness - Compromised evolutionary potential Intro
  • 31. Conservation Genetics • Genetic drift and inbreeding: - Inbreeding depression - Reduction in individual fitness - Compromised evolutionary potential Intro
  • 32. Conservation Genetics • Genetic drift and inbreeding: - Inbreeding depression - Reduction in individual fitness - Compromised evolutionary potential Intro
  • 33. Conservation Genetics • Genetic drift and inbreeding: - Inbreeding depression - Reduction in individual fitness - Compromised evolutionary potential Intro
  • 34. Conservation Genetics • Genetic variation = evolutionary potential of populations or species • There are two principal types of genetic variation: - Neutral  (reflects demographic patterns) - Adaptive  (reflects variation under natural selection) Intro
  • 35. Conservation Genetics • Genetic variation = evolutionary potential of populations or species • There are two principal types of genetic variation: - Neutral  (reflects demographic patterns) - Adaptive  (reflects variation under natural selection) Intro
  • 36. Conservation Genetics • Genetic variation = evolutionary potential of populations or species • There are two principal types of genetic variation: - Neutral  (reflects demographic patterns) - Adaptive  (reflects variation under natural selection) Intro
  • 37. Conservation Genetics • Genetic variation = evolutionary potential of populations or species • There are two principal types of genetic variation: - Neutral  (reflects demographic patterns) - Adaptive  (reflects variation under natural selection) Intro
  • 38. • Neutral genetic variation: - population genetic structure - demographic events, (bottlenecks and population expansions) - migration and gene flow  Valuable information to help prioritize populations for conservation efforts X. Does not generally inform on long term evolutionary potential of populations Conservation Genetics Intro
  • 39. • Neutral genetic variation: - population genetic structure - demographic events, (bottlenecks and population expansions) - migration and gene flow  Valuable information to help prioritize populations for conservation efforts X. Does not generally inform on long term evolutionary potential of populations Conservation Genetics Intro
  • 40. • Neutral genetic variation: - population genetic structure - demographic events, (bottlenecks and population expansions) - migration and gene flow  Valuable information to help prioritize populations for conservation efforts X. Does not generally inform on long term evolutionary potential of populations Conservation Genetics Intro
  • 41. • Neutral genetic variation: - population genetic structure - demographic events, (bottlenecks and population expansions) - migration and gene flow  Valuable information to help prioritize populations for conservation efforts X. Does not generally inform on long term evolutionary potential of populations Conservation Genetics Intro
  • 42. • Neutral genetic variation: - population genetic structure - demographic events, (bottlenecks and population expansions) - migration and gene flow  Valuable information to help prioritize populations for conservation efforts X. Does not generally inform on long term evolutionary potential of populations Conservation Genetics Intro
  • 43. • Neutral genetic variation: - population genetic structure - demographic events, (bottlenecks and population expansions) - migration and gene flow  Valuable information to help prioritize populations for conservation efforts X. Does not generally inform on long term evolutionary potential of populations Conservation Genetics Intro
  • 45. • Complement conservation genetics with the use of a large number of molecular markers • Concerned with the characterization of adaptive genetic variation - shed light on the evolutionary potential of populations - assist management decisions, especially with regard to adaptation to environmental changes Conservation Genomics Intro
  • 46. • Complement conservation genetics with the use of a large number of molecular markers • Concerned with the characterization of adaptive genetic variation - shed light on the evolutionary potential of populations - assist management decisions, especially with regard to adaptation to environmental changes Conservation Genomics Intro
  • 47. • Complement conservation genetics with the use of a large number of molecular markers • Concerned with the characterization of adaptive genetic variation - shed light on the evolutionary potential of populations - assist management decisions, especially with regard to adaptation to environmental changes Conservation Genomics Intro
  • 48. • Complement conservation genetics with the use of a large number of molecular markers • Concerned with the characterization of adaptive genetic variation - shed light on the evolutionary potential of populations - assist management decisions, especially with regard to adaptation to environmental changes Conservation Genomics Intro
  • 49. • Impact of habitat fragmentation or climate change on selectively important variation • Mechanisms underlying inbreeding depression • Role of gene-environment interaction • Gene expression Conservation Genomics Intro
  • 50. • Impact of habitat fragmentation or climate change on selectively important variation • Mechanisms underlying inbreeding depression • Role of gene-environment interaction • Gene expression Conservation Genomics Intro
  • 51. • Impact of habitat fragmentation or climate change on selectively important variation • Mechanisms underlying inbreeding depression • Role of gene-environment interaction • Gene expression Conservation Genomics Intro
  • 52. • Impact of habitat fragmentation or climate change on selectively important variation • Mechanisms underlying inbreeding depression • Role of gene-environment interaction • Gene expression Conservation Genomics Intro
  • 53. Climate change and the American pika • Species sensitive to high ambient temperatures • Contemporary climate warming may be partly responsible for extirpation of its southern populations • Good candidate to study the genetic basis of local adaptation since it is distributed along altitudinal gradients in BC
  • 54. Climate change and the American pika • Species sensitive to high ambient temperatures • Contemporary climate warming may be partly responsible for extirpation of its southern populations • Good candidate to study the genetic basis of local adaptation since it is distributed along altitudinal gradients in BC
  • 55. Climate change and the American pika • Species sensitive to high ambient temperatures • Contemporary climate warming may be partly responsible for extirpation of its southern populations • Good candidate to study the genetic basis of local adaptation since it is distributed along altitudinal gradients in BC
  • 57. Study species Taxonomy • American Pika: Ochotona princeps • 5 ssp found throughout western NA • 2 ssp described in BC • Taxonomy based on morphology, mitochondrial DNA lineage and call dialects (Hafner & Smith, 2010)
  • 58. Study species Taxonomy • American Pika: Ochotona princeps • 5 ssp found throughout western NA • 2 ssp described in BC • Taxonomy based on morphology, mitochondrial DNA lineage and call dialects (Hafner & Smith, 2010)
  • 59. Study species Taxonomy • American Pika: Ochotona princeps • 5 ssp found throughout western NA • 2 ssp described in BC • Taxonomy based on morphology, mitochondrial DNA lineage and call dialects (Hafner & Smith, 2010)
  • 60. Study species Taxonomy • American Pika: Ochotona princeps • 5 ssp found throughout western NA • 2 ssp described in BC • Taxonomy based on morphology, mitochondrial DNA lineage and call dialects (Hafner & Smith, 2010)
  • 62. Study species Life History • Habitat specific to Talus slopes • Do not hibernate and make hay-piles • Defend individual territories • 2-3 young successfully weaned per year • Relatively long-lived (5-7 years)
  • 63. Study species Life History • Habitat specific to Talus slopes • Do not hibernate and make hay-piles • Defend individual territories • 2-3 young successfully weaned per year • Relatively long-lived (5-7 years)
  • 64. Study species Life History • Habitat specific to Talus slopes • Do not hibernate and make hay-piles • Defend individual territories • 2-3 young successfully weaned per year • Relatively long-lived (5-7 years)
  • 65. Study species Life History • Habitat specific to Talus slopes • Do not hibernate and make hay-piles • Defend individual territories • 2-3 young successfully weaned per year • Relatively long-lived (5-7 years)
  • 66. Study species Life History • Habitat specific to Talus slopes • Do not hibernate and make hay-piles • Defend individual territories • 2-3 young successfully weaned per year • Relatively long-lived (5-7 years)
  • 67. Study species Dispersal • Young are generally philopatric • If no territories are available, young will disperse • Mortality during dispersal is high • Evidence for gene-flow up to 3km
  • 68. Study species Dispersal • Young are generally philopatric • If no territories are available, young will disperse • Mortality during dispersal is high • Evidence for gene-flow up to 3km
  • 69. Study species Dispersal • Young are generally philopatric • If no territories are available, young will disperse • Mortality during dispersal is high • Evidence for gene-flow up to 3km
  • 70. Study species Dispersal • Young are generally philopatric • If no territories are available, young will disperse • Mortality during dispersal is high • Evidence for gene-flow up to 3km
  • 71. Study species Susceptibility to climate change • Widespread distribution during Pleistocene • Contemporary climate warming may be responsible for the extirpation of one quarter of Pika populations in the Great Basin USA • Their distribution has shifted 100m upslope per decade
  • 72. Study species Susceptibility to climate change • Widespread distribution during Pleistocene • Contemporary climate warming may be responsible for the extirpation of one quarter of Pika populations in the Great Basin USA • Their distribution has shifted 100m upslope per decade
  • 73. Study species Susceptibility to climate change • Widespread distribution during Pleistocene • Contemporary climate warming may be responsible for the extirpation of one quarter of Pika populations in the Great Basin USA • Their distribution has shifted 100m upslope per decade
  • 74. Objectives • Shed light on population genetic structure and demographic history • Identify genomic region under selection
  • 75. Objectives • Shed light on population genetic structure and demographic history • Identify genomic region under selection
  • 78. The Hill ~ 1500 m ~ 800 m ~ 300 m 2 km Methods
  • 79. Nusatsum ~ 1500 m ~ 800 m 2 km Methods
  • 80. Clayton Falls – M. Gurr ~ 1500 m ~ 0 m 2 km Methods
  • 82. Sampling design 25 m25 m - 15 - 30 hair snares set up at each site - Collected 300 individual hair samples - 270 high quality DNA samples Methods
  • 86. Labwork • DNA extracted from 300 hair samples collected in the summers 2008, 2009 and 2010 • 2 types of genetic markers amplified by PCR: - microsatellites - AFLP
  • 87. Microsatellite genotyping Methods - Popular marker in population genetics - Neutral - Highly variable
  • 88. Microsatellite genotyping -10 microsatellite loci amplified in our 270 DNA samples - Resulting in a probability of identity of 0.00029 Methods
  • 89. AFLP genotyping - Markers distributed throughout the genome (genome scan) - Anonymous bands Methods
  • 90. AFLP genotyping - 20 selective primer pairs - 1509 bands amplified in our 270 DNA samples Methods
  • 91. Analyses • Identify individuals based on multilocus genotypes = DNA fingerprint • Assessment of population genetic structure • Calculations of genetic diversity indices • Estimates of demographic history Methods Microsatellites
  • 92. Analyses • Identification of “outlier” loci (under selection) • Identification of main driving force through which selection acts Methods AFLP
  • 93. Natural History 25 m - Up to 7 different individuals sampled in the same hair snare Results
  • 94. Natural History 25 m - Up to 7 different individuals sampled In the same hair snare - Neighboring hair snares recovered the same individuals in 4 cases Results
  • 95. Natural History 25 m - Up to 4 different individuals sampled in the same hair snare - Neighboring hair snares recovered the same individuals in 4 cases - In one case, the same individual was sampled 155m apart Results
  • 100. Bottleneck Test High 1+2 Mid Low 1 Low 2 Wilcoxon * * * NS Mode Shift * NS NS NS M-ratio NS NS NS NS Results No evidence for reduction in population size
  • 101. ~ 1500 m ~ 800 m ~ 300 m 2 km Outliers Hill Results
  • 102. ~ 1500 m ~ 800 m ~ 300 m 2 km Outliers Hill Results
  • 103. Outliers Nusatsum ~ 1500 m ~ 800 m 2 km Methods
  • 104. Outliers Nusatsum ~ 1500 m ~ 800 m 2 km Methods
  • 105. Outliers Clayton – M. Gurr ~ 1500 m ~ 0 m 2 km Methods
  • 106. Outliers Clayton – M. Gurr ~ 1500 m ~ 0 m 2 km Methods
  • 109. Next step • Cloning of outlier AFLP fragments • BLAST against rabbit genome to identify genomic region under selection • Next generation transcriptome sequencing - SNP discovery
  • 110. Next step • Cloning of outlier AFLP fragments • BLAST against rabbit genome to identify genomic region under selection • Next generation transcriptome sequencing - SNP discovery
  • 111. Next step • Cloning of outlier AFLP fragments • BLAST against rabbit genome to identify genomic region under selection • Next generation transcriptome sequencing - SNP discovery
  • 112. Overall significance • Hill and Nusatsum / Clayton- M.Gurr represent two different “populations” • Lowest genetic variability found at Clayton- M.Gurr -> Priority population • Different outliers found in the different transects. Need to investigate the effect of environmental variables on genes
  • 113. Overall significance • Hill and Nusatsum / Clayton- M.Gurr represent two different “populations” • Lowest genetic variability found at Clayton- M.Gurr -> Priority population • Different outliers found in the different transects. Need to investigate the effect of environmental variables on genes
  • 114. Overall significance • Hill and Nusatsum / Clayton- M.Gurr represent two different “populations” • Lowest genetic variability found at Clayton- M.Gurr -> Priority population • Different outliers found in the different transects. Need to investigate the effect of environmental variables on genes
  • 115. Acknowledgements - Russello Lab - Mary Peacock - Kurt Galbreath - Tweedsmuir Provincial Park