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Effective remediation of diazinon from spent sheep dip wash by disposal on land

机译:通过在土地上处置,有效地消除了用过的绵羊浸洗液中的二嗪农

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摘要

Spent sheep dip wash (about 3500 L) containing 59 mg diazinon/L was evenly distributed onto a 450-m2 grassed, soil-bunded, sloping site near Cumnock in central New South Wales, Australia. The entire volume was contained within the bunded area but surface run-off created ponding in the lowest corner of the site. The mean concentration within the top 7 cm of soil was 2.32 mg/kg a day after application. By day 14, this had dropped to 0.4 mg/kg and by day 56, was below the limit of quantification (0.1 mg/kg). The half-life of diazinon in soil was estimated to be 7 days. Residues in the next 7 cm of soil depth were much lower and were below the limit of quantification in all samples collected at day 28 or later. This suggests that vertical leaching of diazinon within the soil profile did not occur despite more than 95 mm of rain during the trial interval. Throughout the 56-day trial interval, diazinon concentrations in the top 7 cm of soil 3 m downhill of the lowest corner of the dip disposal site were unchanged from background pre-treatment levels. No diazinon was detected in samples at 7–14 cm depth in the soil profile in this area. With neither vertical nor lateral movement of diazinon away from the initial treatment zone, we consider the disposal of spent diazinon sheep dips as described here, to be an acceptable and convenient option for Australian wool producers and dipping contractors. Suitable dip disposal sites should be situated away from sensitive locations in areas that have good grass cover over deep soil and that are contained by an effective bund. Stock and other animals should be excluded from these sensitive locations.
机译:将含59 mg diazinon / L的废绵羊浸洗液(约3500 L)均匀分配到澳大利亚新南威尔士州中部Cumnock附近一块450平方米的草丛中,土壤成束的斜坡上。整个体积都包含在捆绑区域内,但地表径流在场地的最低角处产生了积水。施用后每天土壤顶部7厘米内的平均浓度为2.32 mg / kg。到第14天时,浓度已降至0.4 mg / kg,到第56天时,已降至定量限(0.1 mg / kg)以下。二嗪农在土壤中的半衰期估计为7天。在接下来的第7天土壤深度中的残留物要低得多,并且低于在第28天或以后收集的所有样品的定量极限。这表明尽管试验间隔期间降雨超过95毫米,但在土壤剖面中并未发生二嗪农的垂直浸出。在整个56天的试验时间间隔内,在浸水处置点最低角下坡3 m处土壤的顶部7 cm处,二嗪农浓度与背景预处理水平相同。在该地区的土壤剖面中,在7–14 cm深度的样品中未检测到二嗪农。由于二嗪农既不垂直也不横向移动离开初始处理区,因此我们认为按此处所述处置已用过的二嗪农绵羊粪便是澳大利亚羊毛生产商和蘸料承包商的可接受且方便的选择。合适的浸液处置场所应远离敏感区域,这些区域的草覆盖在深厚的土壤上,并且被有效的外滩所包围。应将牲畜和其他动物排除在这些敏感地点之外。

著录项

  • 来源
    《Animal Production Science》 |2007年第1期|p.13-16|共4页
  • 作者

    G. W. Levot;

  • 作者单位

    Elizabeth Macarthur Agricultural Institute, NSW Department of Primary Industries, PMB 8, Camden, NSW 2570, Australia. Email: garry.levot@dpi.nsw.gov.au;

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

    spent sheep;

    机译:废羊;

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