Spatial sorting and range shifts: Consequences for evolutionary potential and genetic signature of a dispersal trait
Introduction
Species are shifting their ranges under climate change (Chen et al., 2011, Parmesan and Yohe, 2003), which has genetic and evolutionary consequences (Excoffier et al., 2009, Kubisch et al., 2014, Parmesan, 2006). The genetic diversity present at the expanding range margin is smeared across the landscape on the expansion wave (Excoffier and Ray, 2008). This is the case for neutral as well as adaptive genetic variation (Cobben et al., 2012a, Cobben et al., 2011, Edmonds et al., 2004, Hewitt, 1996, Ibrahim et al., 1996, Klopfstein et al., 2006, Travis et al., 2007, Travis et al., 2010). Under these conditions, the genetic configuration of the newly colonised populations is largely the result of the demographic process under range expansion, and not of selection (Travis et al., 2007), although some traits are selected for under range expansion, particularly the ability to disperse and traits related to population growth rate (Hill et al., 2011, Moreau et al., 2011, Phillips et al., 2010).
With regard to the ability to disperse, both theoretical and empirical studies report an increased dispersal capacity as a result of spatial sorting under range expansions (e.g. Burton et al., 2010, Phillips et al., 2006, Thomas et al., 2001, Travis and Dytham, 2002, Travis et al., 2013). Good dispersers gather at the range margin and from there they colonise new territory, while the poor dispersers lag behind. This eventually leads to a spatial gradient in dispersal capacity across the species’ range, which can be regarded as a genetic signature of range expansion (Phillips et al., 2010). After the range stops expanding, it takes time for such a genetic signature of range expansion to decay, especially when the variation for these traits needs to migrate from the centre of the range or to develop through de novo mutations (Dytham et al., 2014, Phillips et al., 2010). During that time period populations are in spatial disequilibrium as a result of the past range expansion. In a time when many investigators are gathering genetic data from natural populations to study selection pressures and micro-evolution, accounting for different explanations of genetic make-up is crucial (Currat et al., 2006, Ray and Excoffier, 2009). Investigating the genetic signature of range expansion is therefore of importance for the interpretation of contemporary spatial patterns in genetic diversity.
Particularly for a dispersal trait, it can be expected that the decay of this genetic signature of range expansion may take a long time: after the range expansion stops the net effect of selection will be for lower dispersal capacity, yet low dispersal genotypes are by definition slow dispersers. Kubisch et al. (2010) showed that the establishment of genotypes with low dispersal rates after range expansion is the result of the migration of variation, and does not involve the establishment of new, beneficial mutations. In their study we see a slow return to equilibrium dispersal rate values at the expanding range margin after range expansion, but this result is not specifically quantified or discussed. In contrast, Henry et al. (2014) claimed a fast return to equilibrium values after range expansion, resulting from selection for beneficial mutations. In a mechanistically more realistic model, Dytham et al. (2014) showed that the state of spatial disequilibrium can last for a substantial time period after the range expansion. In addition, they observed that the speed of range expansion depends on selection for existing variation rather than for new variation due to mutations, even under a high mutation rate (Dytham et al., 2014). This is in line with theory and empirical data on micro-evolution, in which evolutionary changes that are relevant at ecological timescales depend on changes in allele frequencies rather than on new mutations. However, none of the above studies have explicitly discussed or tried to quantify the time period during which populations are in spatial disequilibrium.
Under a climate change scenario with continued temperature increase, many species’ ranges are expected to retract at the margin with the deteriorating thermal conditions, resulting in a range shift rather than a range expansion (Gillings et al., 2015, Thomas et al., 2006). This means that slow dispersers might be lost as a result of spatial sorting and subsequent extinction of populations at the retracting margin (Cobben et al., 2012a, Cobben et al., 2011), while return to equilibrium values after range expansion likely depends on such existing genetic diversity as argued above (Dytham et al., 2014, Kubisch et al., 2010). Many studies have reported increased dispersal under range expansion (e.g. Burton et al., 2010, Phillips et al., 2006, Thomas et al., 2001, Travis and Dytham, 2002, Travis et al., 2013), but little attention has been given to the consequences of a retracting range margin for dispersal traits (but see Henry et al., 2014).
In this paper we investigated how range shifts affect the distribution of different genotypes coding for low, medium and high rates of dispersal across the species range. In addition, we studied the duration of the ephemeral genetic signature of range expansion. For both, we used a mechanistically realistic model of a range shifting species under climate change. We simulated a period of temperature increase in several scenarios, during and after which we registered the distribution of the different dispersal rate genotypes in the landscape up until 5000 years after model initialisation. To warrant sufficient variation in the existing genetic diversity under stationary conditions, we employed diploid inheritance, fragmented habitat and temperature variability. The genetic architecture was designed to get a clear signature of spatial sorting as well as distinct differences between phenotypes.
Section snippets
Methods
We used a spatially explicit, individual-based simulation model of a sexually reproducing species with overlapping generations. The model is called METAPHOR (Verboom et al., 2001, Vos et al., 2001) and has previously been extended to allow for stochastic temperature increase (Schippers et al., 2011) and with a genetic module for neutral (Cobben et al., 2011, Cobben et al., 2012b) and adaptive traits (Cobben et al., 2012a). It was parameterised based on empirical data for the middle spotted
Loss of the A allele at the trailing edge
At the end of the burn-in phase, so under equilibrium conditions, the metapopulation consisted of individuals with dispersal rates of 0, 0.1 and 0.2 (genotypes AA, AB and BB respectively; Fig. 1 year 0). All three genotypes were present in the total range but the individuals with 0 dispersal rate (AA) dominated the centre of the range, while the 0.2 individuals (BB) had the highest frequency in the margins, where habitat quality and population densities were lower. The 0.1 individuals (AB) took
Discussion
We have investigated how range shifts affect the distribution of genotypes of different dispersal rates across the species range. The combination of spatial sorting and range retraction could lead to the extinction of the A allele, coding for low dispersal rate. When the temperature stabilised before the extinction of the A allele, the equilibrium spatial distribution of genotypes was able to recover. This, however, took an extensive amount of time, dependent on the total displacement of the
Acknowledgements
We like to thank several anonymous referees for constructive and useful comments that have contributed to the improvement of this manuscript. This research was supported by the Netherlands’ Ministry of Economic Affairs, Agriculture, and Innovation through its strategic research program: “Sustainable spatial development of ecosystems, landscapes, seas and regions” (Projects KB-01–007-001 and KB-01–007-013), by the Netherlands’ National Research Programme Climate changes Spatial Planning (//www.klimaatvoorruimte.nl/
References (66)
- et al.
Surfing during population expansions promotes genetic revolutions and structuration
Trends Ecol. Evol.
(2008) Some genetic consequences of ice ages, and their role in divergence and speciation
Biol. J. Linn. Soc.
(1996)Oaks (Quercus sp.) and only oaks? Relations between habitat structure and home range size of the middle spotted woodpecker (Dendrocopos medius)
Biol. Conserv.
(2000)Extinction of an isolated population of the Middle Spotted Woodpecker Dendrocopos-Medius (L) in Sweden and its relation to general theories on extinction
Biol. Conserv.
(1985)- et al.
Range retractions and extinction in the face of climate warming
Trends Ecol. Evol.
(2006) - et al.
Introducing the key patch approach for habitat networks with persistent populations: an example for marshland birds
Biol. Conserv.
(2001) - et al.
Contemporary evolution, allelic recycling, and adaptive radiation of the threespine stickleback
Evol. Ecol. Res.
(2013) - et al.
Between migration load and evolutionary rescue: dispersal, adaptation and the response of spatially structured populations to environmental change
Proc. R. Soc. Biol. Sci. Ser. B
(2014) - et al.
Invasion, stress, and spinal arthritis in cane toads
Proc. Natl. Acad. Sci. USA
(2007) - et al.
Trade-offs and the evolution of life-histories during range expansion
Ecol. Lett.
(2010)
Trajectories to extinction: spatial dynamics of the contraction of geographical ranges
J. Biogeogr.
Rapid range shifts of species associated with high levels of climate warming
Science
Causes, mechanisms and consequences of dispersal
Wrong place, wrong time: climate change-induced range shift across fragmented habitat causes maladaptation and decreased population size in a modelled bird species
Glob. Change Biol.
Landscape prerequisites for the survival of a modelled metapopulation and its neutral genetic diversity are affected by climate change
Landsc. Ecol.
Projected climate change causes loss and redistribution of genetic diversity in a model metapopulation of a medium-good disperser
Ecography
Comment on “Ongoing adaptive evolution of ASPM, a brain size determinant in Homo sapiens” and “Microcephalin, a gene regulating brainsize, continues to evolve adaptively in humans”
Science
Seed dispersal as a maternally influenced character: mechanistic basis of maternal effects and selection on maternal characters in an annual plant
Am. Nat.
Changes in species׳ distributions during and after environmental change: which eco‐evolutionary processes matter more?
Ecography
Mutations arising in the wave front of an expanding population
Proc. Natl. Acad. Sci. USA
Genetic consequences of range expansions
Annu. Rev. Ecol. Evol. Syst.
Directionality of recent bird distribution shifts and climate change in Great Britain
Glob. Change Biol.
A candidate locus for variation in dispersal rate in a butterfly metapopulation
Proc. R. Soc. Biol. Sci. Ser. B
Conserving biodiversity under climate change: the rear edge matters
Ecol. Lett.
Inter-annual variability influences the eco-evolutionary dynamics of range-shifting
PeerJ.
Climate change and evolutionary adaptations at species׳ range margins
Annu. Rev. Entomol.
Spatial patterns of genetic variation generated by different forms of dispersal
Heredity
Phenotypic plasticity for dispersal ability in the seed heteromorphic Crepissancta (Asteraceae)
Oikos
The fate of mutations surfing on the wave of a range expansion
Mol. Biol. Evol.
Climate change reduces genetic diversity of Canada lynx at the trailing range edge
Ecography
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