Hiebeler David E, Houle Jennifer, Drummond Frank, Bilodeau Peter, Merckens Jeffery
Department of Mathematics and Statistics, University of Maine, Orono, ME 04469, United States.
Department of Mathematics and Statistics, University of Maine, Orono, ME 04469, United States.
J Theor Biol. 2016 Oct 21;407:212-224. doi: 10.1016/j.jtbi.2016.07.031. Epub 2016 Jul 25.
Locally dispersing populations are generally favorably affected by increasing the scale of habitat heterogeneity because they can exploit contiguous patches of suitable habitat. Increasing the spatial scale of landscape disturbances (such as by applying a pesticide to control an unwanted species) drives down population density because of reasons including dispersal-limited recolonization and the resulting increase in temporal variability. Here, we examine how population density changes as the spatial scale of landscape disturbance increases: does it increase due to increases in spatial correlations in landscape habitat type, or does it decrease due to the various spatial and temporal effects of larger-scale disturbances? We use simulations, mean field approximations, pair approximations, landscape-improved pair approximations (LIPA), and block probabilities to investigate a model of a locally dispersing species on a dynamic landscape with spatiotemporally structured heterogeneous habitat. Pesticide is applied at a given spatial scale, leaving habitat unsuitable for some time before dissipating and allowing the habitat to revert to a suitable state. We found that increasing the spatial scale of disturbances (while keeping the overall disturbance rate fixed) can increase population density, but generally only when landscape turnover is slow relative to population dynamics and when the population is somewhat close to its extinction threshold. Applying control measures at larger spatial scales may allow them to be more effective with the same overall treatment rate. The optimal spatial strategy for applying disturbances depends on both habitat availability as well as the turnover rate of the control measure being used. For the large-scale habitat dynamics in our model, it is possible to analytically calculate spatial correlations in habitat types over arbitrary scales. However, including exact habitat correlations at the triplet scale but approximating population correlations at that scale still neglects information needed to accurately predict simulation results, showing that larger-scale correlations in the population distribution have an important effect on dynamics.
局部扩散种群通常会因栖息地异质性规模的增加而受到有利影响,因为它们能够利用相邻的适宜栖息地斑块。增加景观干扰的空间尺度(例如通过施用杀虫剂来控制有害物种)会降低种群密度,原因包括扩散受限的重新定殖以及由此导致的时间变异性增加。在此,我们研究随着景观干扰的空间尺度增加种群密度如何变化:它是由于景观栖息地类型空间相关性的增加而增加,还是由于更大尺度干扰的各种时空效应而降低?我们使用模拟、平均场近似、配对近似、景观改进配对近似(LIPA)和块概率来研究一个在具有时空结构异质栖息地的动态景观上局部扩散物种的模型。在给定的空间尺度上施用杀虫剂,使栖息地在消散并恢复到适宜状态之前的一段时间内不适合生存。我们发现,增加干扰的空间尺度(同时保持总体干扰率不变)可以增加种群密度,但通常只有在景观更替相对于种群动态较慢且种群 somewhat 接近其灭绝阈值时才会如此。在更大的空间尺度上应用控制措施可能会使它们在相同的总体处理率下更有效。应用干扰的最佳空间策略取决于栖息地可用性以及所使用控制措施的更替率。对于我们模型中的大规模栖息地动态,可以解析计算任意尺度上栖息地类型的空间相关性。然而,在三重态尺度上包含精确的栖息地相关性但在该尺度上近似种群相关性仍然忽略了准确预测模拟结果所需的信息,这表明种群分布中的更大尺度相关性对动态有重要影响。