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Buffer strip width and agricultural pesticide contamination in Danish lowland streams: Implications for stream and riparian management

机译:丹麦低地溪流中的缓冲带宽度和农业农药污染:对河流和河岸管理的影响

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摘要

According to the European Water Framework Directive, member states are obliged to ensure that all surface water bodies achieve at least good ecological status and to identify major anthropogenic stressors. Non-point source contamination of agricultural pesticides is widely acknowledged as one of the most important anthropogenic stressors in stream ecosystems.We surveyed the occurrence of 31 pesticides and evaluated their potential toxicity for benthic macroinvertebrates using Toxic Units (TU) in 14 Danish 1st-and 2nd-order streams in bed sediments and stream water during storm flow and base flow. Total pesticide concentrations and toxic potential were highest during storm flow events with maximum TU ranging from −6.63 to −1.72. We found that minimum buffer strip width in the near upstream area was the most important parameter governing TU. Furthermore, adding a function for minimum buffer strip width to the Runoff Potential (RP) model increased its power to predict measured TUs from 46% to 64%. However, including a function for tile drainage capacity is probably equally important and should be considered in future research in order to further optimise the RP model. Our results clearly emphasise the importance of considering buffer strips as risk mitigation tools in terms of non-point source pesticide contamination. We furthermore apply our results for discussing the minimum dimensions that vegetated buffer strips should have in order to sufficiently protect stream ecosystems from pesticide contamination and maintain good ecological status.
机译:根据《欧洲水框架指令》,成员国有义务确保所有地表水体至少达到良好的生态状态,并确定主要的人为压力源。农业农药的面源污染被公认为是河流生态系统中最重要的人为压力源之一。我们调查了31种农药的发生情况,并在14个丹麦1级和1级使用毒性单位(TU)评估了底栖大型无脊椎动物的潜在毒性。暴雨流和基流期间,床层沉积物中的二阶流和水流。在暴风雨期间,农药的总浓度和潜在毒性最高,最大TU值为-6.63至-1.72。我们发现在上游附近区域的最小缓冲带宽度是控制TU的最重要参数。此外,在“径流势能”(RP)模型中添加最小缓冲区条带宽度的函数可以将其预测的TU预测能力从46%提高到64%。但是,包括瓷砖排水能力的功能可能同样重要,在以后的研究中应考虑进一步优化RP模型。我们的结果清楚地强调了就非点源农药污染而言,考虑将缓冲带作为降低风险的工具的重要性。我们进一步将结果用于讨论植被缓冲带应具有的最小尺寸,以充分保护河流生态系统免受农药污染并保持良好的生态状况。

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