...
首页> 外文期刊>Pesticide science >Off‐target deposits and buffer zones required around water for aerial glyphosate applications
【24h】

Off‐target deposits and buffer zones required around water for aerial glyphosate applications

机译:空中草甘膦应用所需的水周围脱靶沉积物和缓冲区

获取原文

摘要

AbstractOff‐target deposit has been quantified from various silvicultural glyphosate application methods and an estimate made of the buffer‐zone widths required around water to protect fish and their invertebrate food species from possible toxicological effects. To overcome the difficulty of estimating different buffer widths to meet the various use conditions encountered, a realistic worst‐case scenario was chosen for small‐drop drift and data were collected accordingly. Three glyphosate application methods were tested, employing a helicopter equipped with a ‘Microfoil’ boom, a ‘Thru Valve Boom’ and D8‐46 hydraulic nozzles respectively. Airborne glyphosate and off‐target glyphosate deposits on ground sheets and foliar surfaces were measured at downwind distances between 50 and 200 m from multiple overlaid crosswind swaths. Over this distance airborne glyphosate decreased by factors of 3‐130, ground deposits by factors of 4‐2200, and foliar deposits by factors of 5‐100. In general, airborne glyphosate and off‐target deposit was highest from the D8‐46 application, and lowest from the ‘Microfoil’ boom application. Using these measurements, mathematical equations were formulated to predict glyphosate deposits on water surfaces downwind of multiple swath applications, and calculations made for 100‐ha applications. Large‐drop drift was also calculated using a ballistic model. An estimate was then made of buffer widths required around water bodies to prevent toxicological effects from small‐ and large‐drop drift, using reported glyphosate toxicities to salmon, rainbow trout and various aquatic invertebrates. A buffer width of 25 m around water bodies limits mortality in populations of salmon, rainbow trout and aquatic invertebrates to less than 10 for the application methods employing the ‘Microfoil’ and ‘Thru Valve’ Boom. For the third ap
机译:摘要 通过各种造林草甘膦施用方法量化了脱靶沉积物,并估计了保护鱼类及其无脊椎动物食用物种免受可能的毒理学影响所需的水周围缓冲区宽度。为了克服估计不同缓冲区宽度以满足遇到的各种使用条件的困难,为小液滴漂移选择了现实的最坏情况,并相应地收集了数据。测试了三种草甘膦施用方法,分别使用配备“Microfoil”动臂、“直通阀动臂”和 D8-46 液压喷嘴的直升机。在距多个重叠侧风带50至200米的顺风距离处测量了地面和叶面上的空气传播草甘膦和脱靶草甘膦沉积物。在这段距离上,空气中的草甘膦减少了3-130倍,地面沉积物减少了4-2200倍,叶面沉积物减少了5-100倍。一般来说,空气中的草甘膦和脱靶沉积物在D8-46应用中最高,而在“微箔”动臂应用中最低。利用这些测量结果,制定了数学方程,以预测多个条带施用的下风向水面上的草甘膦沉积物,并计算了100公顷的施用。大落差漂移也是使用弹道模型计算的。然后,利用报告的草甘膦对鲑鱼、虹鳟鱼和各种水生无脊椎动物的毒性,估计了水体周围所需的缓冲区宽度,以防止小滴和大滴漂移的毒理学影响。水体周围25米的缓冲区宽度将鲑鱼、虹鳟鱼和水生无脊椎动物种群的死亡率限制在10%以下,采用“微箔”和“通阀”围栏的施用方法。对于第三个 ap

著录项

获取原文

客服邮箱:kefu@zhangqiaokeyan.com

京公网安备:11010802029741号 ICP备案号:京ICP备15016152号-6 六维联合信息科技 (北京) 有限公司©版权所有
  • 客服微信

  • 服务号