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Pendimethalin and oxyfluorfen degradation under two irrigation conditions over four years application

机译:两年灌溉条件下二甲戊灵和氧氟芬的降解

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摘要

A four-year field study was conducted to determine the effect of pluviometric conditions on pendimethalin and oxyfluorfcn soil dynamics. Adsorption, dissipation and soil movement were studied in a sandy loam soil from 2003 to 2007. Pendimethalin and oxyfluorfen were applied every year on August at 1.33 and 0.75 kg ha"~(-1), respectively. Herbicide soil concentrations were determined at 0, 10, 20, 40, 90 and 340 days after application (DAA), under two pluviometric regimens, natural rainfall and irrigated (30 mm every 15 days during the first 90 DAA). More than 74% of the herbicide applied was detected at the top 2.5 cm layer for both herbicides, and none was detected at 10 cm or deeper. Pendimethalin soil half-life ranged from 10.5 to 31.5 days, and was affected mainly by the time interval between application and the first rain event. Pendimethalin soil residues at 90 DAA fluctuated from 2.5 to 13.8% of the initial amount applied, and it decreased to 2.4 and 8.6% at 340 DAA. Oxyfluorfen was more persistent than pendimethalin as indicated by its soil half-life which ranged from 34.3 to 52.3 days, affected primarily by the rain amount at the first rainfall after application. Oxyfluorfen soil residues at 90 DAA ranged from 16.7 to 34.8% and it decreased to 3.3 and 17.9% at 340 DAA. Based on half-life values, herbicide soil residues after one year, and soil depth reached by the herbicides, we conclude that both herbicides should be considered as low risk to contaminate groundwater. However, herbicide concentration at the top 2.5 cm layer should be considered in cases where runoff or soil erosion could occur, because of the potential for surface water contamination.
机译:进行了为期四年的现场研究,确定了测光条件对二甲戊乐灵和氧氟土壤动力学的影响。研究了2003年至2007年沙质壤土的吸附,耗散和土壤运动。每年八月分别以1.33和0.75 kg ha-(-1)施用二甲戊灵和氧氟芬。测定的除草剂土壤浓度为0,施用(DAA)后10、20、40、90和340天,在两种测雨方案下,自然降雨并灌溉(在头90个DAA期间每15天30毫米),在施用量达到74%时发现了除草剂。两种除草剂的最大2.5 cm层,在10 cm或更深处均未检测到。二甲戊灵土壤半衰期为10.5至31.5天,主要受施用和第一次降雨事件之间的时间间隔影响。 90 DAA从最初施用量的2.5波动至13.8%,在340 DAA时下降至2.4和8.6%,氧氟苯胺比戊二甲灵更持久,其土壤半衰期为34.3至52.3天,主要受到影响由施用后第一次降雨时的降雨量。 90 DAA处的氟草醚土壤残留量介于16.7%至34.8%之间,340 DAA时减少至3.3%和17.9%。根据半衰期值,一年后的除草剂土壤残留以及除草剂达到的土壤深度,我们得出结论,应将两种除草剂都视为污染地下水的低风险。但是,由于地表水的潜在污染,在可能发生径流或水土流失的情况下,应考虑顶层2.5厘米处的除草剂浓度。

著录项

  • 来源
    《Journal of environmental science and health》 |2009年第4期|337-343|共7页
  • 作者单位

    Centro de Investigation Agricola y Ambiental (CIAA), Universidad de Vina del Mar, Vina del Mar, Chile;

    Centro de Investigation Agricola y Ambiental (CIAA), Universidad de Vina del Mar, Vina del Mar, Chile;

    Centro de Investigation Agricola y Ambiental (CIAA), Universidad de Vina del Mar, Vina del Mar, Chile;

    Centro de Investigation Agricola y Ambiental (CIAA), Universidad de Vina del Mar, Vina del Mar, Chile Facultad de Agronomia e Ingenieria Forestal, Universidad Catolica de Chile, Santiago, Chile;

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  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

    herbicides; adsorption; dissipation; leaching; vineyards;

    机译:除草剂吸附耗散;浸出葡萄园;
  • 入库时间 2022-08-18 01:47:14

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