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Landscape Planning For Agricultural Nonpoint Source Pollution Reduction I: A Geographical Allocation Framework

机译:农业面源污染减少的景观规划I:地理分配框架

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Agricultural nonpoint source pollution remains a persistent environmental problem, despite the large amount of money that has been spent on its abatement. At local scales, agricultural best management practices (BMPs) have been shown to be effective at reducing nutrient and sediment inputs to surface waters. However, these effects have rarely been found to act in concert to produce measurable, broad-scale improvements in water quality. We investigated potential causes for this failure through an effort to develop recommendations for the use of riparian buffers in addressing nonpoint source pollution in Wisconsin. We used frequency distributions of phosphorus pollution at two spatial scales (watershed and field), along with typical stream phosphorus (P) concentration variability, to simulate benefit/ cost curves for four approaches to geographically allocating conservation effort. The approaches differ in two ways: (1) whether effort is aggregated within certain watersheds or distributed without regard to watershed boundaries (dispersed), and (2) whether effort is targeted toward the most highly P-polluting fields or is distributed randomly with regard to field-scale P pollution levels. In realistic implementation scenarios, the aggregated and targeted approach most efficiently improves water quality. For example, with effort on only 10% of a model landscape, 26% of the total P load is retained and 25% of watersheds significantly improve. Our results indicate that agricultural conservation can be more efficient if it accounts for the uneven spatial distribution of potential pollution sources and the cumulative aspects of environmental benefits.
机译:尽管为减少污染而花费了大量资金,但农业面源污染仍然是一个持续存在的环境问题。在地方范围内,农业最佳管理实践(BMP)已被证明可有效减少营养物质和沉积物向地表水的输入。但是,很少发现这些影响协同作用可产生可测量的,大规模的水质改善。我们通过努力开发建议以使用河岸缓冲带解决威斯康星州非面源污染的方法,调查了造成这种故障的潜在原因。我们使用两个空间尺度(分水岭和田地)的磷污染频率分布,以及典型的溪流磷(P)浓度变异性,来模拟四种在地理上分配保护工作的方法的收益/成本曲线。这些方法有两种不同:(1)是否将精力集中在某些流域内还是在不考虑流域边界的情况下进行了分散(分散);(2)努力是针对P污染最严重的领域还是随机分配的到田间的P污染水平。在现实的实施方案中,综合和针对性的方法可以最有效地改善水质。例如,仅需在模型景观的10%上努力,就可以保留总P负载的26%,并且流域的25%可以得到显着改善。我们的结果表明,如果考虑到潜在污染源的空间分布不均和环境效益的累积方面,那么农业保护就会更有效率。

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