Gilbert Mark A, Gaffney Eamonn A, Bullock James M, White Steven M
Wolfson Centre for Mathematical Biology, Mathematical Institute, Radcliffe Observatory Quarter, Woodstock Road, Oxford, Oxfordshire OX2 6GG, UK; Centre for Ecology & Hydrology, Benson Lane, Wallingford, Oxfordshire OX10 8BB, UK.
Wolfson Centre for Mathematical Biology, Mathematical Institute, Radcliffe Observatory Quarter, Woodstock Road, Oxford, Oxfordshire OX2 6GG, UK.
J Theor Biol. 2014 Dec 21;363:436-52. doi: 10.1016/j.jtbi.2014.08.022. Epub 2014 Aug 21.
Characterising the spread of biological populations is crucial in responding to both biological invasions and the shifting of habitat under climate change. Spreading speeds can be studied through mathematical models such as the discrete-time integro-difference equation (IDE) framework. The usual approach in implementing IDE models has been to ignore spatial variation in the demographic and dispersal parameters and to assume that these are spatially homogeneous. On the other hand, real landscapes are rarely spatially uniform with environmental variation being very important in determining biological spread. This raises the question of under what circumstances spatial structure need not be modelled explicitly. Recent work has shown that spatial variation can be ignored for the specific case where the scale of landscape variation is much smaller than the spreading population׳s dispersal scale. We consider more general types of landscape, where the spatial scales of environmental variation are arbitrarily large, but the maximum change in environmental parameters is relatively small. We find that the difference between the wave-speeds of populations spreading in a spatially structured periodic landscape and its homogenisation is, in general, proportional to ϵ(2), where ϵ governs the degree of environmental variation. For stochastically generated landscapes we numerically demonstrate that the error decays faster than ϵ. In both cases, this means that for sufficiently small ϵ, the homogeneous approximation is better than might be expected. Hence, in many situations, the precise details of the landscape can be ignored in favour of spatially homogeneous parameters. This means that field ecologists can use the homogeneous IDE as a relatively simple modelling tool--in terms of both measuring parameter values and doing the modelling itself. However, as ϵ increases, this homogeneous approximation loses its accuracy. The change in wave-speed due to the extrinsic (landscape) variation can be positive or negative, which is in contrast to the reduction in wave-speed caused by intrinsic stochasticity. To deal with the loss of accuracy as ϵ increases, we formulate a second-order approximation to the wave-speed for periodic landscapes and compare both approximations against the results of numerical simulation and show that they are both accurate for the range of landscapes considered.
描述生物种群的扩散对于应对生物入侵和气候变化导致的栖息地转移至关重要。扩散速度可以通过数学模型来研究,如离散时间积分差分方程(IDE)框架。实施IDE模型的通常方法是忽略人口统计学和扩散参数的空间变化,并假设这些参数在空间上是均匀的。另一方面,实际景观很少在空间上是均匀的,环境变化在决定生物扩散方面非常重要。这就提出了一个问题,即在什么情况下不需要明确建模空间结构。最近的研究表明,对于景观变化尺度远小于扩散种群扩散尺度的特定情况,可以忽略空间变化。我们考虑更一般类型的景观,其中环境变化的空间尺度任意大,但环境参数的最大变化相对较小。我们发现,在空间结构化的周期性景观中扩散的种群的波速与其均匀化之间的差异,一般与ε(2)成正比,其中ε控制环境变化的程度。对于随机生成的景观,我们通过数值证明误差的衰减速度比ε快。在这两种情况下,这意味着对于足够小的ε,均匀近似比预期的要好。因此,在许多情况下,可以忽略景观的精确细节,而采用空间均匀的参数。这意味着野外生态学家可以将均匀IDE用作相对简单的建模工具——在测量参数值和进行建模本身方面。然而,随着ε的增加,这种均匀近似会失去其准确性。由于外在(景观)变化导致的波速变化可以是正的或负的,这与内在随机性导致的波速降低形成对比。为了应对随着ε增加而出现的精度损失,我们为周期性景观的波速制定了二阶近似,并将这两种近似与数值模拟结果进行比较,结果表明它们在所考虑的景观范围内都是准确的。