利用加州农田施用农药的高时空分辨率数据来确定减毒机会

Nicol Parker, Ashley Larsen, P. Banerjee, A. Keller
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引用次数: 1

摘要

农药仍然是一种主要的环境危害,危及水生和陆地生态系统。在很大程度上评估毒性的能力、农药使用数据的时空分辨率、评估累积毒性的能力以及确定不同农药施用地点对健康/经济的贡献,阻碍了降低农药毒性。我们引入了环境释放工具,这是农药缓解优先模型的一个子工具,以推进这四个领域。利用加利福尼亚州农业施用者所需的每日农药使用报告,我们量化了农药对鱼类、水生无脊椎动物、无血管植物和血管植物的施用毒性。利用该工具能够同时量化数百种农药和流域的施用毒性,我们探索了计算全州施用地点和流域累积施用农药毒性的重要性。我们的研究结果表明,14种农药的施用毒性占99.9%,432种施用地点类型中有16种对所调查的类群具有90%的毒性。我们还发现,在所有分类群中,流域内的累积施用毒性明显大于最大影响农药(p<1.0 E-16),平均年差异为460–630%。虽然累积施用毒性很大,而且各个流域的来源各不相同,但净施用毒性可以用活性成分和场地类型的简短列表来近似。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Leveraging high spatiotemporal resolution data of pesticides applied to agricultural fields in California to identify toxicity reduction opportunities
Pesticides remain a leading environmental hazard, imperiling aquatic and terrestrial ecosystems. Reducing pesticide toxicity is hampered by the ability to evaluate toxicity over large extents, the spatiotemporal resolution of pesticide use data, the ability to assess cumulative toxicity, and the identification of health/economic contributions of different pesticide application sites. We introduce the Environmental Release Tool, a sub-tool of the Pesticide Mitigation Prioritization Model, to advance these four areas. Using daily pesticide use reports required for agricultural applicators in California, we quantify the applied toxicity of pesticides to fish as well as aquatic invertebrates, nonvascular plants, and vascular plants. With the tool’s ability to quantify applied toxicity for hundreds of pesticides and watersheds simultaneously, we explore the significance of accounting for cumulative applied pesticide toxicity for application sites and watersheds statewide. Our results show that 14 pesticides account for 99.9% of applied toxicity, and 16 of 432 application site types introduce 90% of toxicity for taxa investigated. We also find cumulative applied toxicity within watersheds was significantly greater (p <1.0 E-16) than the maximum impact pesticide for all taxonomic groups, with a mean-annual difference of 460–630%. While cumulative applied toxicity was significant, and sources varied in individual watersheds, the net applied toxicity can be approximated with a short list of active ingredients and site types.
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