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Use of habitat-contamination spatial correlation to determine when to perform a spatially explicit ecological risk assessment

机译:利用生境污染空间相关性确定何时进行空间明确的生态风险评估

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Anthropogenic contamination is typically distributed heterogeneously through space. This spatial structure can have different effects on the cumulative doses of wildlife exposed to contamination within the environment. These effects are accentuated when individual organisms pursue different movement strategies, and movement strategies can be affected by how individual organisms and species value habitat. Habitat quality is often neglected when ecological risk assessments are performed, despite evidence that inclusion of a quantitative habitat measure can have a significant effect on the overall exposure estimate. We couple an exposure model with habitat data to examine the interactions between habitat preferences, the spatial distribution of contamination, and the resulting impact on dose estimates. Dose distributions are constructed for pronghorn (Antilocapra americana) exposed to fluoride when foraging on desert sagebrush. The results show the magnitude of the difference between simulated doses when foraging concentrations are positively or negatively correlated with different spatial distributions of habitat preferences. Mean estimated exposures obtained from non-spatial versus spatial methods can vary by a factor greater than two, and variation within the movement model, due to different habitat preferences, can vary by an order of magnitude. Such differences in calculated exposures can change a remediation decision from no-action to remediation, or vice-versa, and impact the remedial design when cleanup is required. In addition, information concerning which endpoint species are more orless likely to be exposed to chemical contamination in a given spatial setting can be used by stakeholders in the endpoint selection process. Results presented here are generally applicable to other situations where terrestrial wildlife is exposed to chemical contaminants. These simple model results demonstrate that examining the strength of the spatial correlation between habitat preference and contaminant data can be quickly used to determine when the implementation of a spatially explicit ecological risk assessment is useful. (C) 2007 Elsevier B.V. All rights reserved.
机译:人为污染通常在空间中分布不均。这种空间结构可能会对环境中暴露于污染的野生生物的累积剂量产生不同的影响。当个体生物采取不同的移动策略时,这些影响就会加剧,并且个体生物和物种如何珍惜栖息地会影响移动策略。尽管有证据表明采用定量生境措施可能会对总体接触估计产生重大影响,但在进行生态风险评估时,生境质量常常被忽略。我们将暴露模型与栖息地数据相结合,以检查栖息地偏好,污染物的空间分布以及对剂量估算的最终影响之间的相互作用。当在沙漠鼠尾草上觅食时,会暴露于氟化物的叉角羚(Antilocapra americana)的剂量分布。结果表明,当觅食浓度与生境偏好的不同空间分布成正相关或负相关时,模拟剂量之间的差异幅度。从非空间方法与空间方法获得的平均估计接触量可以相差大于两倍,并且由于生境偏好的不同,运动模型内的变化也可以相差一个数量级。计算出的暴露量中的此类差异可能将补救决策从无采取措施更改为采取补救措施,反之亦然,并在需要清理时影响补救设计。此外,利益相关者可以在端点选择过程中使用有关在给定空间设置中哪些端点种类或多或少可能遭受化学污染的信息。此处提供的结果通常适用于陆生野生生物暴露于化学污染物的其他情况。这些简单的模型结果表明,检查栖息地偏好和污染物数据之间空间相关性的强度可快速用于确定何时实施空间明确的生态风险评估是有用的。 (C)2007 Elsevier B.V.保留所有权利。

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