Abstract
Geographic ranges of communities of species evolve in response to environmental, ecological, and evolutionary forces. Understanding the effects of these forces on species’ range dynamics is a major goal of spatial ecology. Previous mathematical models have jointly captured the dynamic changes in species’ population distributions and the selective evolution of fitness-related phenotypic traits in the presence of an environmental gradient. These models inevitably include some unrealistic assumptions, and biologically reasonable ranges of values for their parameters are not easy to specify. As a result, simulations of the seminal models of this type can lead to markedly different conclusions about the behavior of such populations, including the possibility of maladaptation setting stable range boundaries. Here, we harmonize such results by developing and simulating a continuum model of range evolution in a community of species that interact competitively while diffusing over an environmental gradient. Our model extends existing models by incorporating both competition and freely changing intraspecific trait variance. Simulations of this model predict a spatial profile of species’ trait variance that is consistent with experimental measurements available in the literature. Moreover, they reaffirm interspecific competition as an effective factor in limiting species’ ranges, even when trait variance is not artificially constrained. These theoretical results can inform the design of, as yet rare, empirical studies to clarify the evolutionary causes of range stabilization.
Similar content being viewed by others
Data Availability
References to all datasets used in this study are provided in this article.
Notes
It is argued that normal distribution of phenotypes, which is also assumed in the ancestors of our model, is a reasonable assumption when most of the genetic variation in a species is maintained by migration (gene flow) rather than by mutation (Barton 1999, 2001). This is often the case when a species adaptively expands its range over an environmental gradient, as we primarily study here.
In our model, the reproduction of individuals with phenotype p has been modeled through a logistic growth term that depends on the population density of individuals only with phenotype p ; see Eqs. (17) and (25) in “Appendix A.” Although this logistic population growth fits in with an asexual reproduction system more trivially, it can also approximately accommodate a sexual reproduction system as long as the rate of production of offspring with phenotype p is predominantly proportional to the density of parents with phenotype p. This can approximately occur under our assumption of normal (unimodal) phenotype distribution within each population, provided the populations are sufficiently panmictic.
Here, we define the amplitude of a population’s traveling wave solution as the (steady) peak value of the population’s density during its range expansion regime. In the results presented in Fig. 4b, the traveling wave amplitudes are approximately calculated as the density of the population at its center when it has reached a nearly steady value.
References
Ackerly DD, Cornwell WK (2007) A trait-based approach to community assembly: partitioning of species trait values into within- and among-community components. Ecol Lett 10(2):135–145. https://doi.org/10.1111/j.1461-0248.2006.01006.x
Alleaume-Benharira M, Pen I, Ronce O (2006) Geographical patterns of adaptation within a species’ range: interactions between drift and gene flow. J Evol Biol 19(1):203–215. https://doi.org/10.1111/j.1420-9101.2005.00976.x
Angert AL, Bontrager MG, Ågren J (2020) What do we really know about adaptation at range edges? Annu Rev Ecol Evol Syst 51(1):341–361. https://doi.org/10.1146/annurev-ecolsys-012120-091002
Barton NH (1999) Clines in polygenic traits. Genet Res 74(3):223–236. https://doi.org/10.1017/S001667239900422X
Barton N (2001) Adaptation at the edge of a species range. In: Silvertown J, Antonovics J (eds) Integrating ecology and evolution in a spatial context, chapter 17. Blackwell, Oxford, pp 365–392
Behrman K, Kirkpatrick M (2011) Species range expansion by beneficial mutations. J Evol Biol 24(3):665–675. https://doi.org/10.1111/j.1420-9101.2010.02195.x
Benning JW, Eckhart VM, Geber MA, Moeller DA (2019) Biotic interactions contribute to the geographic range limit of an annual plant: herbivory and phenology mediate fitness beyond a range margin. Am Nat 193(6):786–797. https://doi.org/10.1086/703187
Birch LC (1948) The intrinsic rate of natural increase of an insect population. J Anim Ecol 17(1):15–26. https://doi.org/10.2307/1605
Bridle JR, Vines TH (2007) Limits to evolution at range margins: when and why does adaptation fail? Trends Ecol Evol 22(3):140–147. https://doi.org/10.1016/j.tree.2006.11.002
Bridle JR, Gavaz S, Kennington WJ (2009) Testing limits to adaptation along altitudinal gradients in rainforest Drosophila. Proc R Soc B Biol Sci 276(1661):1507–1515. https://doi.org/10.1098/rspb.2008.1601
Bridle JR, Polechová J, Kawata M, Butlin RK (2010) Why is adaptation prevented at ecological margins? New insights from individual-based simulations. Ecol Lett 13(4):485–494. https://doi.org/10.1111/j.1461-0248.2010.01442.x
Case TJ, Taper ML (2000) Interspecific competition, environmental gradients, gene flow, and the coevolution of species’ borders. Am Nat 155(5):583–605. https://doi.org/10.1086/303351
Case TJ, Holt RD, McPeek MA, Keitt TH (2005) The community context of species’ borders: ecological and evolutionary perspectives. Oikos 108(1):28–46. https://doi.org/10.1111/j.0030-1299.2005.13148.x
Colautti RI, Lau JA (2015) Contemporary evolution during invasion: evidence for differentiation, natural selection, and local adaptation. Mol Ecol 24(9):1999–2017. https://doi.org/10.1111/mec.13162
Colwell RK, Futuyma DJ (1971) On the measurement of niche breadth and overlap. Ecology 52(4):567–576. https://doi.org/10.2307/1934144
Dawson MN, Grosberg RK, Stuart YE, Sanford E (2010) Population genetic analysis of a recent range expansion: mechanisms regulating the poleward range limit in the volcano barnacle tetraclita rubescens. Mol Ecol 19(8):1585–1605. https://doi.org/10.1111/j.1365-294X.2010.04588.x
Dillingham PW, Moore JE, Fletcher D, Cortés E, Curtis KA, James KC, Lewison RL (2016) Improved estimation of intrinsic growth rmax for long-lived species: integrating matrix models and allometry. Ecol Appl 26(1):322–333. https://doi.org/10.1890/14-1990
Duputié A, Massol F, Chuine I, Kirkpatrick M, Ronce O (2012) How do genetic correlations affect species range shifts in a changing environment? Ecol Lett 15(3):251–259. https://doi.org/10.1111/j.1461-0248.2011.01734.x
Emiljanowicz LM, Ryan GD, Langille A, Newman J (2014) Development, reproductive output and population growth of the fruit fly pest Drosophila suzukii (Diptera: Drosophilidae) on artificial diet. J Econ Entomol 107(4):1392–1398. https://doi.org/10.1603/EC13504
Estes S, Arnold SJ (2007) Resolving the paradox of stasis: models with stabilizing selection explain evolutionary divergence on all timescales. Am Nat 169(2):227–244. https://doi.org/10.1086/510633
Filin I, Holt RD, Barfield M (2008) The relation of density regulation to habitat specialization, evolution of a species’ range, and the dynamics of biological invasions. Am Nat 172(2):233–247. https://doi.org/10.1086/589459
Gaston KJ et al (2003) The structure and dynamics of geographic ranges. Oxford University Press, Oxford
Godsoe W, Holland NJ, Cosner C, Kendall BE, Brett A, Jankowski J, Holt RD (2017) Interspecific interactions and range limits: contrasts among interaction types. Theor Ecol 10(2):167–179. https://doi.org/10.1007/s12080-016-0319-7
Goldberg E, Lande R (2006) Ecological and reproductive character displacement of an environmental gradient. Evolution 60(7):1344–1357. https://doi.org/10.1111/j.0014-3820.2006.tb01214.x
Haldane JBS (1956) The relation between density regulation and natural selection. Proc R Soc Lond Ser B Biol Sci 145(920):306–308. https://doi.org/10.1098/rspb.1956.0039
Hatch JM, Haas HL, Richards PM, Rose KA (2019) Life-history constraints on maximum population growth for loggerhead turtles in the northwest Atlantic. Ecol Evol 9(17):9442–9452. https://doi.org/10.1002/ece3.5398
Hendry AP (2016) Eco-evolutionary Dynamics. Princeton University Press, Princeton
Holt RD, Keitt TH (2005) Species’ borders: a unifying theme in ecology. Oikos 108(1):3–6. https://doi.org/10.1111/j.0030-1299.2005.13145.x
Houle D, Morikawa B, Lynch M (1996) Comparing mutational variabilities. Genetics 143(3):1467–1483. https://doi.org/10.1093/genetics/143.3.1467
Hundsdorfer W (2002) Accuracy and stability of splitting with stabilizing corrections. Appl Numer Math 42(1):213–233. https://doi.org/10.1016/S0168-9274(01)00152-0
in ’t Hout KJ, Welfert BD (2007) Stability of adi schemes applied to convection–diffusion equations with mixed derivative terms. Appl Numer Math 57(1):19–35. https://doi.org/10.1016/j.apnum.2005.11.011
Kanarek AR, Webb CT (2010) Allee effects, adaptive evolution, and invasion success. Evol Appl 3(2):122–135. https://doi.org/10.1111/j.1752-4571.2009.00112.x
Kimura M (1965) A stochastic model concerning the maintenance of genetic variability in quantitative characters. Proc Natl Acad Sci 54(3):731–736. https://doi.org/10.1073/pnas.54.3.731
Kingsolver JC, Hoekstra HE, Hoekstra JM, Berrigan D, Vignieri SN, Hill CE, Hoang A, Gibert P, Beerli P (2001) The strength of phenotypic selection in natural populations. Am Nat 157(3):245–261. https://doi.org/10.1086/319193
Kingsolver JC, Hoekstra HE, Hoekstra JM, Berrigan D, Vignieri SN, Hill CE, Hoang A, Gibert P, Beerli P (2008) Data ftom: the strength of phenotypic selection in natural populations. Dryad. https://doi.org/10.5061/dryad.166
Kirkpatrick M, Barton NH (1997) Evolution of a species’ range. Am Nat 150(1):1–23. https://doi.org/10.1086/286054
Lande R (1979) Quantitative genetic analysis of multivariate evolution, applied to brain:body size allometry. Evolution 33(1Part2):402–416. https://doi.org/10.1111/j.1558-5646.1979.tb04694.x
Lande R, Arnold SJ (1983) The measurement of selection on correlated characters. Evolution 37(6):1210–1226. https://doi.org/10.1111/j.1558-5646.1983.tb00236.x
Leimar O, Doebeli M, Dieckmann U (2008) Evolution of phenotypic clusters through competition and local adaptation along an environmental gradient. Evol Int J Org Evol 62(4):807–822. https://doi.org/10.1111/j.1558-5646.2008.00334.x
Louthan AM, Doak DF, Angert AL (2015) Where and when do species interactions set range limits? Trends Ecol Evol 30(12):780–792. https://doi.org/10.1016/j.tree.2015.09.011
Macarthur R, Levins R (1967) The limiting similarity, convergence, and divergence of coexisting species. Am Nat 101(921):377–385. https://doi.org/10.1086/282505
Mayr E (1963) Animal Species and Evolution. Harvard University Press, Cambridge
Micheletti SJ, Storfer A (2020) Mixed support for gene flow as a constraint to local adaptation and contributor to the limited geographic range of an endemic salamander. Mol Ecol 29(21):4091–4101. https://doi.org/10.1111/mec.15627
Miller JR (2019) Invasion waves and pinning in the Kirkpatrick-Barton model of evolutionary range dynamics. J Math Biol 78(1):257–292. https://doi.org/10.1007/s00285-018-1274-2
Miller JR, Zeng H (2014) Range limits in spatially explicit models of quantitative traits. J Math Biol 68(1):207–234. https://doi.org/10.1007/s00285-012-0628-4
Miller TEX, Angert AL, Brown CD, Lee-Yaw JA, Lewis M, Lutscher F, Marculis NG, Melbourne BA, Shaw AK, Szűcs M, Tabares O, Usui T, Weiss-Lehman C, Williams JL (2020) Eco-evolutionary dynamics of range expansion. Ecology 101(10):e03139. https://doi.org/10.1002/ecy.3139
Mirrahimi S, Raoul G (2013) Dynamics of sexual populations structured by a space variable and a phenotypical trait. Theor Popul Biol 84:87–103. https://doi.org/10.1016/j.tpb.2012.12.003
Niel C, Lebreton J (2005) Using demographic invariants to detect overharvested bird populations from incomplete data. Conserv Biol 19(3):826–835. https://doi.org/10.1111/j.1523-1739.2005.00310.x
Ohashi H, Hasegawa T, Hirata A, Fujimori S, Takahashi K, Tsuyama I, Nakao K, Kominami Y, Tanaka N, Hijioka Y, Matsui T (2019) Biodiversity can benefit from climate stabilization despite adverse side effects of land-based mitigation. Nat Commun 10(1):5240. https://doi.org/10.1038/s41467-019-13241-y
Paul JR, Sheth SN, Angert AL (2011) Quantifying the impact of gene flow on phenotype-environment mismatch: a demonstration with the scarlet monkeyflower Mimulus cardinalis. Am Nat 178(S1):S62–S79. https://doi.org/10.1086/661781
Pease CM, Lande R, Bull J (1989) A model of population growth, dispersal and evolution in a changing environment. Ecology 70(6):1657–1664. https://doi.org/10.2307/1938100
Phillips PC, Arnold SJ (1989) Visualizing multivariate selection. Evolution 43(6):1209–1222. https://doi.org/10.1111/j.1558-5646.1989.tb02569.x
Pianka ER (1973) The structure of lizard communities. Annu Rev Ecol Syst 4(1):53–74. https://doi.org/10.1146/annurev.es.04.110173.000413
Pianka ER (1974) Niche overlap and diffuse competition. Proc Natl Acad Sci 71(5):2141–2145. https://doi.org/10.1073/pnas.71.5.2141
Pianka ER (2000) Evolutionary ecology, 6th edn. Benjamin Cummings, San Francisco
Pigot AL, Tobias JA (2013) Species interactions constrain geographic range expansion over evolutionary time. Ecol Lett 16(3):330–338. https://doi.org/10.1111/ele.12043
Polechová J (2018) Is the sky the limit? On the expansion threshold of a species’ range. PLoS Biol 16(6):e2005372. https://doi.org/10.1371/journal.pbio.2005372
Polechová J, Barton NH (2015) Limits to adaptation along environmental gradients. Proc Natl Acad Sci 112(20):6401–6406. https://doi.org/10.1073/pnas.1421515112
Polechová J, Barton N, Marion G (2009) Species’ range: adaptation in space and time. Am Nat 174(5):E186–E204. https://doi.org/10.1086/605958
Roughgarden J (1979) Theory of population genetics and evolutionary ecology: an introduction. Macmillan, New York
Sanford E, Holzman SB, Haney RA, Rand DM, Bertness MD (2006) Larval tolerance, gene flow, and the northern geographic range limit of fiddler crabs. Ecology 87(11):2882–2894. https://doi.org/10.1890/0012-9658(2006)87[2882:LTGFAT]2.0.CO;2
Sexton JP, McIntyre PJ, Angert AL, Rice KJ (2009) Evolution and ecology of species range limits. Annu Rev Ecol Evol Syst 40(1):415–436. https://doi.org/10.1146/annurev.ecolsys.110308.120317
Stinchcombe JR, Agrawal AF, Hohenlohe PA, Arnold SJ, Blows MW (2008) Estimating nonlinear selection gradients using quadratic regression coefficients: double or nothing? Evolution 62(9):2435–2440. https://doi.org/10.1111/j.1558-5646.2008.00449.x
Takahashi Y, Suyama Y, Matsuki Y, Funayama R, Nakayama K, Kawata M (2016) Lack of genetic variation prevents adaptation at the geographic range margin in a damselfly. Mol Ecol 25(18):4450–4460. https://doi.org/10.1111/mec.13782
Violle C, Jiang L (2009) Towards a trait-based quantification of species niche. J Plant Ecol 2(2):87–93. https://doi.org/10.1093/jpe/rtp007
Visscher PM, Hill WG, Wray NR (2008) Heritability in the genomics era—concepts and misconceptions. Nat Rev Genet 9(4):255–266. https://doi.org/10.1038/nrg2322
Whitmee S, Orme CDL (2013) Predicting dispersal distance in mammals: a trait-based approach. J Anim Ecol 82(1):211–221. https://doi.org/10.1111/j.1365-2656.2012.02030.x
Willi Y, Van Buskirk J (2019) A practical guide to the study of distribution limits. Am Nat 193(6):773–785. https://doi.org/10.1086/703172
Acknowledgements
The authors would like to thank J. Goodman and the Courant Institute of Mathematical Sciences, New York University, for their hospitality during part of the preparation of this research. The authors would also like to thank the anonymous reviewers of this paper for their time, comments, and helpful suggestions.
Author information
Authors and Affiliations
Corresponding author
Ethics declarations
Code Availability
The implementation of the numerical simulations in MATLAB R2021a is available on https://github.com/Farshad-Shirani/2022-BMB-FS-JRM.
Additional information
Publisher's Note
Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
This work was supported by the NSF Grant DMS 1615126 to JRM.
Appendices
Appendix A: Model Derivation
To derive the equations of the model given by (1)–(7), we first formulate the intrinsic growth rate of the individuals within each species, which determines the local dynamics of the evolution of the species. For this, at position \(x \in \varOmega \) and time \(t \in [0,T]\), let \(\phi _i(x,t,p)\) denote the relative frequency of a quantitative phenotypic trait with phenotype value \(p \in {\mathbb {R}}\) within the ith species. Moreover, let \(\alpha _{ij}(p,p')\) denote the competition kernel that captures the per capita effect of phenotype \(p'\) in the jth species on the frequency of phenotype p in the ith species. The exact definition of this competition kernel is given in “Competition Kernels” section of “Appendix A” below. Finally, let \(g_i(x,t,p)\) denote the intrinsic growth rate of the population of individuals with phenotype p within the ith species.
Intrinsic Growth Rates
For a community of \(\mathrm {N}\) competing species, we define the intrinsic growth rate of each species as (Case and Taper 2000, Eq. (2)),
The first term in (17) is a Lotka–Volterra model of competing species in which the convolution term with \(j=i\) expresses the effect of intraspecific phenotypic competition on the frequency of phenotype p, whereas the convolution terms with \(j \ne i\) account for the effect of interspecific competition from the phenotypes in the other species. The second term in (17) incorporates the effect of directional and stabilizing selection on individuals with phenotype p. A local population of a species at position x that has a phenotypic trait value different from the environmental optimal value \(\mathrm {Q}(x)\) can only reach an equilibrium density that is lower than its carrying capacity. This penalizing effect of the phenotypic selection is made stronger by choosing larger values for \(\mathrm {S}\).
Competition Kernels
As proposed by Case and Taper (2000, Eq. (3)), we obtain the competition kernels \(\alpha _{ij}\) in (17) using the MacArthur-Levins overlap formula between resource utilization curves of each species (Macarthur and Levins 1967), along with the total resource consumption law given by Roughgarden (1979, Eq. (24.50)). Suppose the environmental resources vary continuously along a resource axis denoted by variable r. Moreover, suppose that individuals with phenotype p within each species possesses a resource utilization curve of the form
where \(\psi _{i,p}(r)\) is a probability density function, which gives the probability density that the individuals obtain a unit of resource from point r. The term \(\varPsi e^{\kappa p}\) gives the total amount of resource consumed by an individual with phenotype p. This power law is proposed by Roughgarden (1979, Eq. (24.50)) based on the assumption that energy consumption by an individual is proportional to its weight. This interpretation, however, does not necessarily hold for the general trait-based model presented in this paper, and this specific form of resource consumption form is mainly adopted for the simplicity of derivations and for providing the model with the flexibility of incorporating asymmetric intraspecific competitions with \(\kappa \ne 0\).
The resource utilization functions \(\xi _{i,p}(r)\) are used to obtain the competition kernels \(\alpha _{ij}\) by the following overlap formula (Roughgarden 1979, Eq. (24.5))
Calculation of \(\alpha _{ij}(p,p')\) based on this formula involves having precise information about resource values. However, it is convenient to assume that the resource axis can be identified by phenotype axis, as proposed by Roughgarden (1979, Eq. (24.51)). For this, let \(r_p\) denote the point on the r-axis from which individuals of phenotype p obtain their average amount of resources. We assume that \(r_p\) does not depend on which species the individuals belong to, that is, \(r_p = \int _{{\mathbb {R}}} r \psi _{i,p}(r) \mathrm{d} r\) for all \(i= 1,\dots ,\mathrm {N}\). We further assume that there is a smooth one-to-one map \(I:p \mapsto r_p\), which can be used to identify the r-axis with the p-axis, that is, for every \(r \in {\mathbb {R}}\) there exist a unique phenotype \({\tilde{p}}\in {\mathbb {R}}\) such that \(r=I({\tilde{p}})\equiv {\tilde{p}}\). Therefore, the resource utilization functions and competition kernels can be written only based on trait values, as
Note that, by the definition of I we have \(\int _{{\mathbb {R}}} {\tilde{p}} \psi _{i,p}({\tilde{p}}) \mathrm{d} {\tilde{p}} = p\). We refer to \(\xi _{i,p}\) in (18) as phenotype utilization function of individuals with phenotype p within the ith species.
The identification stated above can represent the empirical relationship between functional response traits and environments. In addition to simplifying the mathematical derivations, this identification allows estimation of the parameters of the utilization functions using trait-based approaches to niche quantification (Violle and Jiang 2009; Ackerly and Cornwell 2007). This was further discussed in Sect. 3.
Changes Due to Mutation
Let \(\nu (\delta p)\) denote the probability density that by mutation a phenotype p changes to a phenotype \(p + \delta p\). We use the equation provided by Kimura (1965), but at the level of phenotypic effects, to approximately model the rate of mutational changes in the frequency of phenotypes as
where \(\eta \ge 0\) is the mutation rate per capita per generation. The first term in (20) gives the reduction rate in the frequency of phenotype p within the ith species due to mutation to other phenotypic values. The second term gives the growth rate in the frequency of phenotype p due to mutations to p from other phenotypic values within the ith species.
Model Assumptions
As stated in Sect. 2, the following major assumptions are made on the populations’ dispersal and reproduction, and on the elements of the intrinsic growth rates and competition kernels described above. These assumptions are used in “Derivation of Equations” section of “Appendix A” to derive the equations of the model based on (17).
-
(i)
Each species disperses in the habitat by diffusion.
-
(ii)
Nonlinear environmental selection for the optimal phenotype \(\mathrm {Q}(x)\) is stabilizing for all \(x\in \varOmega \).
-
(iii)
Frequency of trait values follows a normal distribution for all \(x \in \varOmega \) and \(t \in [0,T]\), that is,
$$\begin{aligned} \phi _i(x,t,p) := \frac{1}{\sqrt{2 \pi v_i(x,t)}} \exp \left( -\frac{(p - q_i(x,t))^2}{2 v_i(x,t)} \right) , \quad i =1,\dots , \mathrm {N}.\quad \end{aligned}$$(21) -
(iv)
Within each species, the reproduction rate of individuals with phenotype p depends on the population density of individuals with the same phenotype p.
-
(v)
Phenotype utilization distribution \(\psi _{i,p}\) in (18) is normal, that is,
$$\begin{aligned} \psi _{i,p}({\tilde{p}}) = \frac{1}{\sqrt{2 \pi \mathrm {V}_i}} \exp \left( -\frac{({\tilde{p}} - p)^2}{2 \mathrm {V}_i} \right) , \quad i =1,\dots , \mathrm {N}. \end{aligned}$$(22)Therefore, competition kernels given by (19) can be calculated as
$$\begin{aligned} \alpha _{ij}(p,p')= & {} \varLambda _{ij} \exp (\kappa ^2 {\bar{\mathrm {V}}}_{ij}) \exp \left( -\frac{(p - p' + 2 \kappa {\bar{\mathrm {V}}}_{ij})^2}{4 {\bar{\mathrm {V}}}_{ij}} \right) ,\nonumber \\&\qquad \qquad \qquad \qquad i=1, \dots , \mathrm {N}, \quad j=1, \dots , \mathrm {N}, \end{aligned}$$(23)where \(\varLambda _{ij}:=\sqrt{\smash [b] { \mathrm {V}_i / {\bar{\mathrm {V}}}_{ij}}}\) with \({\bar{\mathrm {V}}}_{ij} := \frac{1}{2}(\mathrm {V}_i + \mathrm {V}_j)\), as in (7).
-
(vi)
The mutation kernel \(\nu \) in (20) is the probability density function of a probability distribution with constant zero mean and constant variance \(\mathrm {V}_{\textsc {m}}\). That is, in particular, \(\nu \) is independent of population density, trait mean, or baseline trait variance.
Remark 6
(Symmetric competition kernel) The MacArthur-Levins overlap formula (19) gives asymmetric competition kernels (23), wherein \(\alpha _{ij}(p,p') \ne \alpha _{ji}(p,p')\) when \(\mathrm {V}_i \ne \mathrm {V}_j\) or \(\kappa \ne 0\). A symmetric alternative to (19) is proposed in the literature (Pianka 1973), which can be written as
With the normal density function \(\psi _{i,p}\) given in (22), this symmetric overlap formula yields
where \(\varLambda _{ij}:=\sqrt{\mathring{\mathrm {V}}_{ij} /{\bar{\mathrm {V}}}_{ij}} \) with \(\mathring{\mathrm {V}}_{ij} := \sqrt{\mathrm {V}_i \mathrm {V}_j}\) and \({\bar{\mathrm {V}}}_{ij} := \frac{1}{2}(\mathrm {V}_i + \mathrm {V}_j)\). In “Derivation of Equations” section of “Appendix A,” however, the asymmetric kernels (23) are used to derive the equations of the model given in (7). Note that, (23) can be easily transformed to (24) by setting \(\kappa =0\) and replacing \(\mathrm {V}_i\) with \(\mathring{\mathrm {V}}_{ij}\). \(\square \)
Derivation of Equations
The derivation of Eqs. (1)–(7) begins with the following equation
wherein, within each species the variation in the population density of individuals with phenotype p over a small time interval \(\tau \rightarrow 0\) is assumed to result from the contributions of three factors, namely, the diffusive migration of individuals to and from neighboring locations, the intrinsic growth of the population, and the mutational changes in the relative frequency of p.
Integrating both sides of (25) with respect to p over \({\mathbb {R}}\), we obtain
where
denotes the mean value of the intrinsic growth rate of the population of individuals with phenotype p within the ith species. Note that in writing (27) we have used (20) to obtain \(\int _{{\mathbb {R}}} \partial _t^{(\mathrm {M})} \phi _i(x,t,p) \mathrm{d} p =0\). Moreover, we have implicitly presumed that the mean value of \(g_i(x,t,p)\) can be written in terms of x and the variables of the model, u. This is indeed true by the calculations that follow below. In addition, note that (1) is obtained immediately by dividing both sides of (26) by \(\tau \) and taking the limit as \(\tau \rightarrow 0\), provided \(G_i(x,u)\) is shown to be given by (4).
Next, to derive (2), we multiply both sides of (25) by p and integrate the result with respect to p over \({\mathbb {R}}\). Note that the zero-mean assumption (vi) on the mutation distribution, along with (20), gives \(\int _{{\mathbb {R}}} p \partial _t^{(\mathrm {M})} \phi _i(x,t,p) \mathrm{d} p =0\). Therefore, we obtain
which further implies, after dividing by \(\tau \) and taking the limit as \(\tau \rightarrow 0\), that
Now, using the chain rule on the left hand side of the above equation and substituting (1) into the result, we obtain
For the first term within the brackets we can write
Therefore, it follows that
where
This gives (2), provided we show \(H_i(x,u)\) can be given by (5).
Finally, to derive (3), we multiply both sides of (25) by \((p-q_i(x,t+\tau ))^2\) and integrate the result with respect to p over \({\mathbb {R}}\). For the mutation term in (25), it follows from (20) and assumption (vi) that \(\int _{{\mathbb {R}}} (p-q_i(x,t+\tau ))^2 \partial _t^{(\mathrm {M})} \phi _i(x,t,p) \mathrm{d} p = \mathrm {U}\), where \(\mathrm {U}:= \eta \mathrm {V}_{\textsc {m}}\). Therefore, we obtain
Dividing both sides of the above equation by \(\tau \) and taking the limit as \(\tau \rightarrow 0\), we obtain
Note that,
Moreover, \(\partial _t(n_i(x,t) q_i^2(x,t))\) can be calculated using the chain rule and Eqs. (1) and (2), wherein \(G_i(x,u)\) and \(H_i(x,u)\) are given by (27) and (30), respectively. Therefore, (31) gives
Now, note that
Therefore, using the chain rule on the left hand side of (32) and substituting (1) into the result, we obtain
where
This gives (3) provided \(W_i(x,u)\) is shown to be given by (6).
Now, to complete the derivation of (1)–(3), it remains to show that \(G_i(x,u)\), \(H_i(x,u)\), and \(W_i(x,u)\) can be given by (4), (5), and (6), respectively. For simplicity of exposition, the dependence of functions \(n_i\), \(q_i\), \(v_i\), \(g_i\), and \(\phi _i\) on variables x and t, as well as the dependence of \(\mathrm {R}_i\), \(\mathrm {K}_i\), and \(\mathrm {Q}\) on x, are not explicitly shown in the rest of this section.
We begin with calculating \(g_j(p)\). Using (21) and (23), the integral in (17) can be written as
where
and
with
Note that \(\int _{{\mathbb {R}}} {\hat{A}}_j(p',u) \mathrm{d} p' = \sqrt{2 \pi }{\hat{\sigma }}_j(u)\). Therefore, substituting the results into (17), we obtain
Now, we substitute (38) into (27) to calculate \(G_i(x,u)\). Note that,
Moreover, the integral associated with the term inside the summation in (38) can be calculated using similar calculation as given for (34). Specifically, as compared with (34)–(37),
where \(M_{ij}(u)\) is given in (7) and
with
Now, note that \(\int _{{\mathbb {R}}} A_{ij}(p,u) \mathrm{d} p = \sqrt{2 \pi } \sigma _{ij}(u)\). Therefore, substituting (38) into (27), using (39)–(43), and letting \(C_{ij}(u)\) be defined as in (7), the mean growth rate \(G_i(x,u)\) is obtained as given by (4).
Next, we substitute (38) into (30) to calculate \(H_i(x,u)\). We can write
Note that (45) is equal to \(E_i(x,u)\) as defined in (7). Moreover, as compared with (34)–(37),
where \(M_{ij}(u)\) and \(A_{ij}(p,u)\) are given by (7) and (42), respectively. Therefore, we have \(\int _{{\mathbb {R}}} p A_{ij}(p,u) \mathrm{d} p = \sqrt{2 \pi } \sigma _{ij}(u) \mu _{ij}(u)\), where \(\mu _{ij}(u)\) and \(\sigma _{ij}(u)\) are given by (43). Now, letting \(L_{ij}(u)\) be defined as in (7), Eq. (30) along with (38) and (43)–(46) gives \(H_i(x,u)\) as in (5).
Finally, we use (33) with (38) and (30) to calculate \(W_i(x,u)\). Note that,
and, as compared with (34)–(37),
where \(M_{ij}(u)\) and \(A_{ij}(p,u)\) are given by (7) and (42), respectively. It follows that \(\int _{{\mathbb {R}}} p^2 A_{ij}(p,u) \mathrm{d} p = \sqrt{2 \pi } \sigma _{ij}(u) [\sigma _{ij}^2(u) + \mu _{ij}^2(u)]\), where \(\mu _{ij}(u)\) and \(\sigma _{ij}(u)\) are given by (43). Therefore, the first integral in (33) can be written as
where \({\hat{Y}}_i(x,u)\) is given by (48) and
Moreover, the second integral in (33) can be calculated immediately using (30) and (5). The result along with (50) gives \(W_i(x,u)\) as in (6), wherein \(P_{ij}(u) = {\hat{P}}_{ij}(u) - 2 q_i L_{ij}(u)\) and \(Y_i(x,u) = {\hat{Y}}_i(x,u) - 2 q_i E_i(x,u) { +\mathrm {U}}\). Note that, using (48) and (51), we obtain \(P_{ij}(u)\) and \(Y_i(x,u)\) as given in (7). This completes the derivation of the model.
Finally, the homogeneous Neumann boundary conditions (8) are obtained by assuming no phenotypic flux through the boundaries, that is,
Integrating this condition with respect to p over \({\mathbb {R}}\) and noting that in general \(\mathrm {D}_i\) is nonzero on the boundary, we obtain the boundary condition \(\partial _xn_i = 0\) as in (8). Moreover, it follows from multiplying (52) by p, integrating the result over \({\mathbb {R}}\), and using the condition \(\partial _xn_i = 0\), that \(\partial _x(n_i q_i) = n_i \partial _xq_i = 0\) on the boundary. This gives the boundary condition \(\partial _xq_i = 0\) given in (8), since \(n_i\) is not required to be zero on the boundary under a no-flux condition. The boundary condition \(\partial _xv_i = 0\) given in (8) is obtained similarly by multiplying (52) by \((p - q_i(x,t))^2\) and integrating the result over \({\mathbb {R}}\).
Appendix B: Numerical Methods and Discretization Parameters
The numerical solutions presented in Sects. 4 and 5 have been computed using an Alternating Direction Implicit (ADI) scheme with two stabilizing correction stages, as presented by Hundsdorfer (2002, Eq. (20)). The parameter \(\theta \) in the formulation of this scheme is set to \(\theta = 1/2\). The function F in the formulation has two components when we consider a one-dimensional geographic space. One of these components is associated with the terms involving spatial derivatives, and the other component is associated with the reaction terms. For the two-dimensional space considered in Sect. 5.4, the function F has three components, first component associated with derivatives with respect to \(x_1\), second component associated with derivatives with respect to \(x_2\), and third component associated with the reaction terms. We treated all components in both spatial dimensions implicitly. For further details of this numerical method, see the results developed by Hundsdorfer (2002) and in ’t Hout and Welfert (2007).
In each iteration of the scheme, instead of solving the nonlinear algebraic equations of the scheme using Newton’s method, we have solved the linearized version of these equations. This is in fact equivalent to performing only one Newton iteration. The required changes in the formulations to incorporate this linearization step are also provided by Hundsdorfer (2002). The computational time that is saved by solving linearized equations can then be used to allow for smaller time steps, which can in turn compensate for the loss of accuracy due to the linearization. Linearizing the scheme has the advantage of providing a better control over the total computation time of the simulations, as the computation time will then become almost linearly proportional to the time steps.
Finally, we have used fourth-order centered difference approximations for both first and second derivatives in each spatial direction. In one-dimensional space, we have considered a uniform discretization mesh of size \(\varDelta x = 0.1 \, \mathtt {X}\), as well as uniform time steps of length \(\varDelta t = 0.002 \, \mathtt {T}\). For the two-dimensional problem of Sect. 5.4, we have used a rectangular mesh of size \(\varDelta x_1 \times \varDelta x_2 = 0.5 \times 0.5 \, \mathtt {X}^2\), and a time step of \(\varDelta t = 0.01 \, \mathtt {T}\).
Rights and permissions
About this article
Cite this article
Shirani, F., Miller, J.R. Competition, Trait Variance Dynamics, and the Evolution of a Species’ Range. Bull Math Biol 84, 37 (2022). https://doi.org/10.1007/s11538-022-00990-z
Received:
Accepted:
Published:
DOI: https://doi.org/10.1007/s11538-022-00990-z