Abstract
Reaction–diffusion models for the dynamics of a biological population in a fragmented landscape can incorporate detailed descriptions of movement and behavior, but are difficult to analyze and hard to parameterize. Patch models, on the other hand, are fairly easy to analyze and can be parameterized reasonably well, but miss many details of the movement process within and between patches. We develop a framework to scale up from a reaction–diffusion process to a patch model and, in particular, to determine movement rates between patches based on behavioral rules for individuals. Our approach is based on the mean occupancy time, the mean time that an individuals spends in a certain area of the landscape before it exits that area or dies. We illustrate our approach using several different landscape configurations. We demonstrate that the resulting patch model most closely captures persistence conditions and steady state densities as compared with the reaction–diffusion model.
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References
Artiles W, Carvalho PGS, Kraenkel RA (2008) Patch-size and isolation effects in the Fisher-Kolmogorov equation. J Math Biol 57:521–535
Cantrell R, Cosner C (1999) Diffusion models for population dynamics incorporating individual behavior at boundaries: applications to refuge design. Theor Popul Biol 55:189–207
Cantrell R, Cosner C (2003) Spatial ecology via reaction-diffusion equations. Mathematical and computational biology. Wiley
Cantrell R, Cosner C (2007) Density dependent behaviour at habitat boundaries and the allee effect. Bull Math Biol 69(7):2339–2360
Cantrell R, Cosner C, Fagan W (2012) The implications of model formulation when transitioning from spatial to landscape ecology. Math Biosci Eng 9(1):27–60
Cobbold C, Lewis M, Lutscher F (2005) How parasitism affects critical patch size in a host-parasitoid system: application to Forest Tent Caterpillar. Theor Popul Biol 67(2):109–125
Fagan W, Lutscher F (2006) The average dispersal success approximation: a bridge linking home range size, natal dispersal, and metapopulation dynamics to critical patch size and reserve design. Ecol Appl 16(2):820–828
Frair J, Merrill E, Visscher D, Fortin D, Beyer H, Morales J (2005) Scales of movement by elk (Cervus elaphus) in response to heterogeneity in forage resources and predation risk. Landsc Ecol 20:273–287
Hadeler K (2000) Reaction transport equations in biological modeling. Math Comput Model 31:75–81
Hanggi P, Talkner P, Borkovec M (1990) Reaction rate theory: fifty years after Kramers. Rev Modern Phys 62(2):251–342
Hanski I, Ovaskainen O (2000) The metapopulation capacity of a fragmented landscape. Nature 404:755–758
Kierstead H, Slobodkin LB (1953) The size of water masses containing plankton blooms. J Mar Res 12:141–147
Kolpas A, Nisbet R (2010) Effects of demographic stochasiticity on population persistence in advective media. Bull Math Biol 72(5):1254–1270
Kot M (2001) Elements of mathematical ecology. Cambridge University Press, Cambridge
Ludwig D, Aronson DG, Weinberger HF (1979) Spatial patterning of the spruce budworm. J Math Biol 8:217–258
Lutscher F, Lewis MA (2004) Spatially-explicit matrix models. A mathematical analysis of stage-structured integrodifference equations. J Math Biol 48:293–324
Maciel G, Lutscher F (2013) How individual response to habitat edges affects population persistence and spatial spread (Submitted)
Matkowsky B, Schuss Z (1977) The exit problem for randomly perturbed dynamical systems. SIAM Appl Math 33(2):365–382
McKenzie H (2006) Linear features impact predator-prey encounters: analysis with first passage time. Master’s thesis, University of Alberta
McKenzie H, Lewis M, Merrill E (2009) First passage time analysis of animal movement and insights into the functional response. Bull Math Biol 71(1):107–129
Othmer H, Adler F, Lewis M, Dallon J (1997) Mathematical modeling in biology: case studies in ecology, physiology and cell biology. Prentice Hall
Ovaskainen O (2008) Analytical and numerical tools for diffusion-based movement models. Theor Popul Biol 73:198–211
Ovaskainen O, Cornell S (2003) Biased movement at a boundary and conditional occupancy times for diffusion processes. J Appl Prob 40(3):557–580
Redner S (2001) A guide to first-passage processes. Cambridge University Press, Cambridge
Samia Y, Lutscher F (2012) Persistence probabilities for stream populations. Bull Math Biol 74(7):1629–1650
Schultz C, Crone E (2001) Edge-mediated dispersal behavior in a prairie butterfly. Ecology 82(7):1879–1892
Shigesada N, Kawasaki K, Teramoto E (1986) Traveling periodic waves in heterogeneous environments. Theor Popul Biol 30:143–160
Singer A, Schuss Z, Osipov A, Holcman D (2008) Partially reflected diffusion. SIAM J Appl Math 28(3):844–868
Skellam JG (1951) Random dispersal in theoretical populations. Biometrika 38:196–218
Strohm S, Tyson R (2012) The effect of habitat fragmentation on cyclic population dynamics: a reduction to ordinary differential equations. Theor Ecol. doi:10.1007/s12080-011-0141-1
Turchin P (1998) Quantitative analysis of movement: measuring and modeling population redistribution of plants and animals. Sinauer, Sunderland
Van Kirk RW, Lewis MA (1997) Integrodifference models for persistence in fragmented habitats. Bull Math Biol 59(1):107–137
Van Kirk RW, Lewis MA (1999) Edge permeability and population persistence in isolated habitat patches. Nat Resour Model 12:37–64
Vasilyeva O, Lutscher F (2012) Competition of three species in an advective environment. Nonlinear Anal: Real World Appl 13(4):1730–1748
Wakano J, Ikeda K, Miki T, Mimura M (2011) Effective dispersal rate is a function of habitat size and corridor shape: mechanistic formulation of a two-patch compartment model for spatially continuous systems. Oikos 120(11):1712–1720
Weins J, Stenseth N, Van Horne B, Ims R (1993) Ecological mechanisms and landscape ecology. Oikos 66:369–380
Acknowledgments
Some of this work was carried out while the first author visited Ottawa, funded by the Carnegie Trust for the Universities of Scotland. Additional support came from a grant to FL by the Canadian research network MITACS. FL is partially funded by a Discovery Grant from the Natural Sciences and Engineering Research Council of Canada.
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Appendices
Appendix A: Core and buffer habitat
We consider a core habitat, say a reserve, of length \(2L_1,\) with a buffer zone of length \(L_2\) attached to the core on either side (Cantrell and Cosner 1999). Since the one-dimensional model is symmetric with respect to the middle of the core habitat, we use this symmetry to reduce the model to the core (\(\varOmega _1=[0,L_1]\)) and the buffer (\(\varOmega _2=[-L_2,0]\)). The linearized equations for the density of individuals in the core and buffer are
with \(r_i=b_i-m_i\) and \(r_1>r_2.\) We have a hostile boundary at \(x=-L_2\) and, due to symmetry, no-flux conditions at \(x=L_1,\) i.e.
At the interface between core and buffer, we require the flux to be continuous, but the density can be discontinuous if either there is movement preference by the individuals or if the diffusion rates differ between core and buffer (Ovaskainen and Cornell 2003), i.e.
where superscripts \(\pm \) stand for right- and left-sided limits. Parameter \(k\) summarizes bias and changes in movement. If individuals prefer the core habitat with probability \(p,\) then either (I) \(k=\frac{p\sqrt{D_2}}{(1-p) \sqrt{D_1}}\) or (II) \(k=\frac{p D_2}{(1-p)D_1},\) see (38).
We denote \(\mathcal M \) as the operator defined by (70–72) with \(b_1=b_2=0.\) To determine the adjoint operator, we use the definition
We find that \(\mathcal M ^*\) is given by \(D_iv_{xx}-m_iv\) for \(x\in \varOmega _i\) with interface and boundary conditions,
Occupancy time in the core (\(T_{\varOmega _1}\)) and buffer (\(T_{\varOmega _2}\)) satisfy (20), which yields the following ODEs
Setting \(m_1=0,\) and using the boundary condition at \(x=L_1,\) we obtain
A convenient representation of the solution on \(\varOmega _2\) that takes the boundary at \(x=-L_2\) into account, is
The interface condition for \(T_{\varOmega _1}\) gives
whereas the condition on \(T_{\varOmega _1}^{\prime }\) gives
The calculations for \(T_{\varOmega _2}\) are similar.
The definitions in (23) now give the elements of the matrix \(\mathcal T .\) Finally, the average population growth rate is given by the eigenvalues of the matrix
Appendix B: MFPT of a rectangle
We consider the rectangular domain \(\varOmega =[0,a]\times [0,b]\) and the diffusion equation
with hostile boundary conditions \(u=0\) for \(x\in \{0,a\}\) and \(y\in \{0,b\}.\)
The dominant eigenvalue can be calculated by standard separation of variables as
When we keep the area of the rectangle constant, we set \(b=1/a.\) In that case, the dominant eigenvalue is maximal when \(a=1.\)
The MFPT is given by the equation
The ansatz
leads to the condition
The coefficients must satisfy \(\hat{B}_{m,n}=16/(nm\pi ^2)\) when \(n\) and \(m\) are odd and \(\hat{B}_{m,n}=0\) otherwise. Accordingly, we obtain
After integrating, we find
We evaluate this expression numerically with \(b=1/a\) and plot the result as a function of \(a\in [0,1]\) in Fig. 8.
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Cobbold, C.A., Lutscher, F. Mean occupancy time: linking mechanistic movement models, population dynamics and landscape ecology to population persistence. J. Math. Biol. 68, 549–579 (2014). https://doi.org/10.1007/s00285-013-0642-1
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DOI: https://doi.org/10.1007/s00285-013-0642-1