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Plant of the Day
Drosera
rotundifolia
... a miniscule,
carnivorous
sundew living in
bogs in Tofino, BC.
Gene flow is the transfer of genetic material
between populations resulting from the movement
of individuals (migration) or their gametes.
Gene flow may add new alleles to a population or
change the frequencies of alleles already present
Gene flow connects the populations of a species,
enabling them to evolve collectively (as a unit).
Reductions in gene flow may lead to speciation.
•Gene flow in plants
•Dispersal mechanisms
•Measuring gene flow directly & indirectly
•Pollen versus seed dispersal
•Gene flow and evolution
•From species cohesion to speciation
•The spread of beneficial alleles
•Applications
•Conservation implications
•Transgene escape
Gene flow: lecture outline
Plants disperse their genes during two independent life
cycle stages.
Pollen
dispersal
Seed
dispersal
Solitary
bee Cleopatra
butterfly
Hawkmoth Sunbird
Hummingbird
Honey possum
Thynnid wasp
Bees Lepidoptera
Other insects
Vertebrates
Blister
beetle
Long-nosed bat
Tchinid fly
Beetle
Water
Wind
Ragweed
Ponderosa pine
Scirpus microcarpus
Water Starwort
Black bean
Animal Water
Wind Explosive
Dandelion
Blackberry Pond iris
Gorse
Impatiens
(1) Observe movement of pollen dispersal agents
•Shortcomings: may e.g. underestimate dispersal because
of pollen and seed carryover. Can’t tell if pollen is
successfully incorporated into new population.
(2) Mark pollen with dyes, paint, rare earth
magnets or radioactive tracers and monitor
movement
•Alternative: naturally polymorphic pollen.
•Shortcomings: marking may affect dispersal. Can’t tell if
pollen is successfully incorporated into new population.
(3) Track unique molecular marker from source
plant(s) in progeny of nearby plants
Data from first three methods indicates that most pollen and seeds
are dispersed close to source. These results suggested that gene
flow rates between plant populations were very low (< 1% per gen.).
Leptokurtic dispersal curve in Scots Pine
4.3% seeds sired by individuals outside of
the population
Robledo-Arnuncio & Gi 2005
(4) Parentage analyses: highly polymorphic markers are
used to screen seeds to determine what fraction of seeds
had fathers or mothers from outside the population.
Paternity analyses suggest that populations spatially
isolated by hundreds or thousands of meters are not
genetically isolated and gene flow rates often are high
(> 1% per gen.)
Measuring dispersal from a source (i.e. as in Methods 1-3)
misses rare, long distance dispersal events. The tails of
these dispersal curves were missing.
How to resolve this conflict?
Final caveat: all direct methods provide contemporary
estimates of gene flow only and are not easily related to
historical gene flow levels, which is what we really care
about from an evolutionary standpoint.
Historical gene flow can be inferred from population
genetic structure (e.g. from Fst). Greater genetic
differentiation implies lower gene flow and vice versa.
Statistical methods exist to relate genetic distance
estimates to a parameter called Nm, which is the
average number of immigrants per generation.
1
4Nm +1
Fst =
Island model
Wright’s Fst
Caveats:
1) Tells us about historical gene flow not contemporary gene flow.
2) The real world is not like the island model (assumptions of equal
population size, equal contributions to migrant pool, no spatial
structure, everything is at equilibrium, no selection, and no mutation
all are violated in all species).
Thus, indirect estimates must be viewed with caution.
Nm is a critical value because it tells us how much gene flow is
required to overcome the effects of genetic drift.
Nm > 4 gene flow wins
Nm < 1 genetic drift wins and populations diverge
Nm between 1 and 4 (neither prevails)
Indirect estimates of gene flow in plants
(Hamrick and Godt,1996)
Selfing
Species
Mixed-
Mixed-
Mating
Mating
Outcrossing
Outcrossing
Species
Species
Nm = 0.24
Nm = 0.24 Nm = 0.90
Nm = 0.90 Nm = 1.43
Nm = 1.43
Nm=0.24 Nm=0.90 Nm=1.43
Selfers Mixed maters Outcrossers
Hamrick and Godt 1996
•Most direct estimates of gene flow measure pollen
dispersal only
•Indirect estimates measure both, but do not
discriminate between them.
Direct estimates from parentage analyses have generally
documented fairly high rates of seed immigration rates,
ranging from 2.1% in honey locust to 40% in Magnolias
Contribution of seed dispersal to overall gene flow can be
estimated by comparing levels of interpopulational
differentiation (e.g.Fst or Gst) for maternal versus
biparentally inherited genes
Chloroplast and mitochondrial are typically inherited
maternally in plants, whereas nuclear genes are inherited
through both parents.
Ratios of pollen to seed flow from indirect measures (i.e.,
Gst or Fst) range from 4 (for selfing annual, wild barley) to
400 for wind-pollinated sessile oak.
wild barley
CONSERVATIVE ROLE (emphasized by Mayr):
Prevents differentiation due to random processes
(i.e. genetic drift) unless the number of migrants
(Nm) between populations is < 1 per generation.
Prevents adaptive genetic differentiation if m>s.
CREATIVE ROLE:
Enables the spread of favorable mutations.
Traditional View:
• Species held together by gene flow
Opposing View (Ehrlich and Raven, 1969):
• Species-wide gene flow is too low
• Populations are the units of evolution
• Species are merely aggregates of evolving units
How strong is gene flow in nature?
0
0.1
0.2
0.3
0.01 0.1 1 10 100 1000
Nem
Frequency
Plant
Animal
Conclusion: in many species, gene flow is not high
enough to prevent differentiation at neutral loci.
Morjan & Rieseberg 2004
Common sunflower, Helianthus annuus,
and its primary dispersal agent
Prehistorical range of
common sunflower
Advantageous mutation
Strength of selection
S = 0.10
Number of migrants
Nm = 1
Generation
0
Generation
0
Near neutral mutation
Strength of selection
S = 0.0001
Number of migrants
Nm = 1
Advantageous mutation
Strength of selection
S = 0.10
Number of migrants
Nm = 1
Generation
50
Generation
50
Near neutral mutation
Strength of selection
S = 0.0001
Number of migrants
Nm = 1
Advantageous mutation
Strength of selection
S = 0.10
Number of migrants
Nm = 1
Generation
500
Generation
500
Near neutral mutation
Strength of selection
S = 0.0001
Number of migrants
Nm = 1
Generation
10,000
Near neutral mutation
Strength of selection
S = 0.0001
Number of migrants
Nm = 1
Generation
50,000
Near neutral mutation
Strength of selection
S = 0.0001
Number of migrants
Nm = 1
Generation
100,000
Near neutral mutation
Strength of selection
S = 0.0001
Number of migrants
Nm = 1
Generation
200,000
Near neutral mutation
Strength of selection
S = 0.0001
Number of migrants
Nm = 1
< 100
100 - 1000
1000 - 10000
> 10000
0.45
0.2
0.1
0.05
0.01
0.001
0.1
1
10
10
100
1000
10000
100000
1000000
Fixation
time
Nm
0.5
2
1
< 100
100 - 1000
1000 - 10000
> 10000
Time to fixation of beneficial mutations
in a stepping-stone model
Selection coefficient
Conclusion: Gene flow is high enough in virtually all species to
allow spread of advantageous mutations, if not neutral ones.
< 100
100 - 1000
1000 - 10000
> 10000
Data from Slatkin 1976
Small populations become inbred more rapidly than large populations
outbred inbred
Gene flow reduces inbreeding depression:
migration rates into small populations are higher than into
large populations
Gene flow may create heterosis or 'hybrid vigour,' which is
manifested as increased size, growth rate or other
parameters resulting from the increase in heterozygosity
Hybrid corn Hybrid sunflower
Gene flow between species (or hybridization) may result in
outbreeding depression or genetic assimilation
Reduced pollen
viability in
interspecific
hybrids
Example of genetic assimilation:
Catalina Island Mahogany
Rieseberg et al. 1989
Gene flow from crop
plants into their wild
relatives may lead to
the escape of
engineered genes.
Prevalence of Crop x Wild
Hybridization
Yes
Sorghum
Yes
Sugar Cane
Yes
Cotton
Yes
Sunflower
Yes
Barley
No
Groundnut
Yes
Soybean
Yes
Rapeseed
Yes
Maize
Yes
Common
Bean
Yes
Rice
Yes
Millet
Yes
Wheat
Ellstrand et al. (1999)
Gene escape is inevitable for most crops.
Bt protein Cry1Ac
toxic to Lepidopteran Insects
Suleima helianthana
Sunflower Bud Moth (stem/developing bud)
Plagiomimicus spumosum
(developing bud; > 50% seed loss)
Experimental Design
• backcrossed Bt transgene into wild background
• planted backcross plants that segregated for transgene at
two localities
• compared fitness of plants with or without transgene
Bt-/F Bt-/SBt+/S
damage in Nebraska
Cochylis
0
0.10
0.15
0.05
NS
**
Cochylis damage in Colorado
0
0.10
0.15
0.05
Bt-/F Bt-/SBt+/S
**
*
Seeds per plant in Nebraska Seeds per plant in Colorado
Bt-/F Bt-/S Bt+/S Bt-/F Bt-/S Bt+/S
0
800
1200
400 **
*
0
1600
2400
800
NS
*
RESULTS:
55% more seeds in NE
14% more seeds in CO
Snow et al 2003
Bt transgenes are highly advantageous and
will spread rapidly into wild sunflower
populations.
– Decisions on environmental release should be
made on a case-by-case basis.
– Consideration of the potential ecological impacts
should be made.
Transgenes: conclusions

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Gene Flow.pptx

  • 1. Plant of the Day Drosera rotundifolia ... a miniscule, carnivorous sundew living in bogs in Tofino, BC.
  • 2.
  • 3. Gene flow is the transfer of genetic material between populations resulting from the movement of individuals (migration) or their gametes. Gene flow may add new alleles to a population or change the frequencies of alleles already present Gene flow connects the populations of a species, enabling them to evolve collectively (as a unit). Reductions in gene flow may lead to speciation.
  • 4. •Gene flow in plants •Dispersal mechanisms •Measuring gene flow directly & indirectly •Pollen versus seed dispersal •Gene flow and evolution •From species cohesion to speciation •The spread of beneficial alleles •Applications •Conservation implications •Transgene escape Gene flow: lecture outline
  • 5. Plants disperse their genes during two independent life cycle stages. Pollen dispersal Seed dispersal
  • 6. Solitary bee Cleopatra butterfly Hawkmoth Sunbird Hummingbird Honey possum Thynnid wasp Bees Lepidoptera Other insects Vertebrates Blister beetle Long-nosed bat Tchinid fly Beetle
  • 8. Black bean Animal Water Wind Explosive Dandelion Blackberry Pond iris Gorse Impatiens
  • 9. (1) Observe movement of pollen dispersal agents •Shortcomings: may e.g. underestimate dispersal because of pollen and seed carryover. Can’t tell if pollen is successfully incorporated into new population. (2) Mark pollen with dyes, paint, rare earth magnets or radioactive tracers and monitor movement •Alternative: naturally polymorphic pollen. •Shortcomings: marking may affect dispersal. Can’t tell if pollen is successfully incorporated into new population.
  • 10. (3) Track unique molecular marker from source plant(s) in progeny of nearby plants Data from first three methods indicates that most pollen and seeds are dispersed close to source. These results suggested that gene flow rates between plant populations were very low (< 1% per gen.).
  • 11. Leptokurtic dispersal curve in Scots Pine 4.3% seeds sired by individuals outside of the population Robledo-Arnuncio & Gi 2005 (4) Parentage analyses: highly polymorphic markers are used to screen seeds to determine what fraction of seeds had fathers or mothers from outside the population.
  • 12. Paternity analyses suggest that populations spatially isolated by hundreds or thousands of meters are not genetically isolated and gene flow rates often are high (> 1% per gen.) Measuring dispersal from a source (i.e. as in Methods 1-3) misses rare, long distance dispersal events. The tails of these dispersal curves were missing. How to resolve this conflict?
  • 13. Final caveat: all direct methods provide contemporary estimates of gene flow only and are not easily related to historical gene flow levels, which is what we really care about from an evolutionary standpoint.
  • 14. Historical gene flow can be inferred from population genetic structure (e.g. from Fst). Greater genetic differentiation implies lower gene flow and vice versa. Statistical methods exist to relate genetic distance estimates to a parameter called Nm, which is the average number of immigrants per generation. 1 4Nm +1 Fst = Island model Wright’s Fst
  • 15. Caveats: 1) Tells us about historical gene flow not contemporary gene flow. 2) The real world is not like the island model (assumptions of equal population size, equal contributions to migrant pool, no spatial structure, everything is at equilibrium, no selection, and no mutation all are violated in all species). Thus, indirect estimates must be viewed with caution. Nm is a critical value because it tells us how much gene flow is required to overcome the effects of genetic drift. Nm > 4 gene flow wins Nm < 1 genetic drift wins and populations diverge Nm between 1 and 4 (neither prevails)
  • 16. Indirect estimates of gene flow in plants (Hamrick and Godt,1996) Selfing Species Mixed- Mixed- Mating Mating Outcrossing Outcrossing Species Species Nm = 0.24 Nm = 0.24 Nm = 0.90 Nm = 0.90 Nm = 1.43 Nm = 1.43 Nm=0.24 Nm=0.90 Nm=1.43 Selfers Mixed maters Outcrossers Hamrick and Godt 1996
  • 17. •Most direct estimates of gene flow measure pollen dispersal only •Indirect estimates measure both, but do not discriminate between them.
  • 18. Direct estimates from parentage analyses have generally documented fairly high rates of seed immigration rates, ranging from 2.1% in honey locust to 40% in Magnolias Contribution of seed dispersal to overall gene flow can be estimated by comparing levels of interpopulational differentiation (e.g.Fst or Gst) for maternal versus biparentally inherited genes Chloroplast and mitochondrial are typically inherited maternally in plants, whereas nuclear genes are inherited through both parents.
  • 19. Ratios of pollen to seed flow from indirect measures (i.e., Gst or Fst) range from 4 (for selfing annual, wild barley) to 400 for wind-pollinated sessile oak. wild barley
  • 20. CONSERVATIVE ROLE (emphasized by Mayr): Prevents differentiation due to random processes (i.e. genetic drift) unless the number of migrants (Nm) between populations is < 1 per generation. Prevents adaptive genetic differentiation if m>s. CREATIVE ROLE: Enables the spread of favorable mutations.
  • 21. Traditional View: • Species held together by gene flow Opposing View (Ehrlich and Raven, 1969): • Species-wide gene flow is too low • Populations are the units of evolution • Species are merely aggregates of evolving units How strong is gene flow in nature?
  • 22. 0 0.1 0.2 0.3 0.01 0.1 1 10 100 1000 Nem Frequency Plant Animal Conclusion: in many species, gene flow is not high enough to prevent differentiation at neutral loci. Morjan & Rieseberg 2004
  • 23. Common sunflower, Helianthus annuus, and its primary dispersal agent Prehistorical range of common sunflower
  • 24. Advantageous mutation Strength of selection S = 0.10 Number of migrants Nm = 1 Generation 0 Generation 0 Near neutral mutation Strength of selection S = 0.0001 Number of migrants Nm = 1
  • 25. Advantageous mutation Strength of selection S = 0.10 Number of migrants Nm = 1 Generation 50 Generation 50 Near neutral mutation Strength of selection S = 0.0001 Number of migrants Nm = 1
  • 26. Advantageous mutation Strength of selection S = 0.10 Number of migrants Nm = 1 Generation 500 Generation 500 Near neutral mutation Strength of selection S = 0.0001 Number of migrants Nm = 1
  • 27. Generation 10,000 Near neutral mutation Strength of selection S = 0.0001 Number of migrants Nm = 1
  • 28. Generation 50,000 Near neutral mutation Strength of selection S = 0.0001 Number of migrants Nm = 1
  • 29. Generation 100,000 Near neutral mutation Strength of selection S = 0.0001 Number of migrants Nm = 1
  • 30. Generation 200,000 Near neutral mutation Strength of selection S = 0.0001 Number of migrants Nm = 1
  • 31. < 100 100 - 1000 1000 - 10000 > 10000 0.45 0.2 0.1 0.05 0.01 0.001 0.1 1 10 10 100 1000 10000 100000 1000000 Fixation time Nm 0.5 2 1 < 100 100 - 1000 1000 - 10000 > 10000 Time to fixation of beneficial mutations in a stepping-stone model Selection coefficient Conclusion: Gene flow is high enough in virtually all species to allow spread of advantageous mutations, if not neutral ones. < 100 100 - 1000 1000 - 10000 > 10000 Data from Slatkin 1976
  • 32. Small populations become inbred more rapidly than large populations outbred inbred Gene flow reduces inbreeding depression: migration rates into small populations are higher than into large populations
  • 33. Gene flow may create heterosis or 'hybrid vigour,' which is manifested as increased size, growth rate or other parameters resulting from the increase in heterozygosity Hybrid corn Hybrid sunflower
  • 34. Gene flow between species (or hybridization) may result in outbreeding depression or genetic assimilation Reduced pollen viability in interspecific hybrids
  • 35. Example of genetic assimilation: Catalina Island Mahogany Rieseberg et al. 1989
  • 36. Gene flow from crop plants into their wild relatives may lead to the escape of engineered genes. Prevalence of Crop x Wild Hybridization Yes Sorghum Yes Sugar Cane Yes Cotton Yes Sunflower Yes Barley No Groundnut Yes Soybean Yes Rapeseed Yes Maize Yes Common Bean Yes Rice Yes Millet Yes Wheat Ellstrand et al. (1999) Gene escape is inevitable for most crops.
  • 37. Bt protein Cry1Ac toxic to Lepidopteran Insects Suleima helianthana Sunflower Bud Moth (stem/developing bud) Plagiomimicus spumosum (developing bud; > 50% seed loss)
  • 38. Experimental Design • backcrossed Bt transgene into wild background • planted backcross plants that segregated for transgene at two localities • compared fitness of plants with or without transgene
  • 39. Bt-/F Bt-/SBt+/S damage in Nebraska Cochylis 0 0.10 0.15 0.05 NS ** Cochylis damage in Colorado 0 0.10 0.15 0.05 Bt-/F Bt-/SBt+/S ** * Seeds per plant in Nebraska Seeds per plant in Colorado Bt-/F Bt-/S Bt+/S Bt-/F Bt-/S Bt+/S 0 800 1200 400 ** * 0 1600 2400 800 NS * RESULTS: 55% more seeds in NE 14% more seeds in CO Snow et al 2003
  • 40. Bt transgenes are highly advantageous and will spread rapidly into wild sunflower populations. – Decisions on environmental release should be made on a case-by-case basis. – Consideration of the potential ecological impacts should be made. Transgenes: conclusions