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EFFECTS OF CHRONIC PESTICIDE STRESS ON WILDLIFE POPULATIONS IN COMPLEX LANDSCAPES: PROCESSES AT MULTIPLE SCALES

机译:慢性杀虫剂胁迫对复杂景观中野生动植物种群的影响:多种尺度的过程

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Populations exposed to pesticides may often be divided into subpopulations, where some subpopulations are exposed to pesticides and others are not. We consider three models for such populations. The first is a simple discrete time model with no density-dependent reproduction. The second is a continuous time model that includes density- dependence for populations not exposed to pesticides. In both models, populations exposed to pesticides are assumed to decline geometrically (exponentially in the continuous time model). Migration between exposed and safe habitat patches is symmetric, so that all individuals leaving safe patches enter exposed patches and vice versa. The rate is assumed to be the same for both kinds of patches. The conditions for persistence of the population in the landscape are the same for both models. Increasing migration rate between patches decreases the ability of the population to persist. Populations that have low rates of increase in safe habitat patches have greater difficulty persisting than those with high rates of increase in safe patches. The toxicity of the pesticide also affects population persistence. More toxic pesticides that result in higher rates of death and/or lower rates of birth in exposed habitat patches lower the ability of the population to persist in the landscape. We consider an additional set of models of a metapopulations that persist because of a balance between colonization and local extinction. In such systems, pesticides may endanger regional persistence by reducing the pool of sites available for colonization. We conclude with an outline of important future directions for theoretical research intended to elucidate the impact of pesticides on populations spatially complex landscapes.
机译:接触农药的人群通常可以分为亚群,其中一些亚群接触农药,而另一些则不。我们考虑了针对此类人群的三种模型。第一个是简单的离散时间模型,没有依赖于密度的复制。第二个是连续时间模型,其中包括未接触农药的人群的密度依赖性。在这两个模型中,都假定接触农药的种群呈几何下降趋势(在连续时间模型中呈指数下降)。裸露的和安全的栖息地斑块之间的迁移是对称的,因此所有离开安全斑块的个人都可以进入裸露的斑块,反之亦然。假定两种补丁的速率相同。对于这两种模型,景观中人口的持久性条件相同。斑块之间的迁移率增加会降低种群的持久能力。安全栖息地斑块增加率低的种群比安全斑块增加率高的种群难于生存。农药的毒性也影响人口的持久性。在裸露的栖息地中导致较高死亡率和/或较低出生率的毒性较大的农药会降低人口在景观中的生存能力。我们考虑了由于定居和局部灭绝之间的平衡而持续存在的另一组种群的模型。在这样的系统中,杀虫剂可能会通过减少可用于定居的地点池而危害区域的持久性。最后,我们概述了理论研究的重要未来方向,以阐明农药对空间复杂景观种群的影响。

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