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Effects of a Simulated Agricultural Runoff Event on Sediment Toxicity in a Managed Backwater Wetland

机译:模拟的农业径流事件对管理型回水湿地沉积物毒性的影响

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We examined the effects of an amended mixture of three pesticides, atrazine (72.7 g), 5-metolachlor (54.5 g), and permethrin (both cis and trans isomers; 11.4 g), on 10-day sediment toxicity to Hyalella azteca in a managed natural backwater wetland after a simulated agricultural runoff event. Sediment samples were collected at 10, 40, 100, 300, and 500 m from inflow 13 days prior to amendment and 1,5,12,22, and 36 days post-amendment. Background pesticide concentrations ranged from <1 to 977, <1 to 119, and <1 to 2 μg kg~(-1), for atrazine, 5-metolachlor, and permethrin, respectively. Average post-amendment atrazine and 5-metolachlor were 2,915-3,927 and 3-20 μ.g kg~(-1) respectively at 10-40 m and 538-872 and <1 μg kg~(-1), respectively at 300-500 m. Average post-amendment permethrin was 65-200 μg kg~(-1) at 10-40 m and 1-10 μg kg~(-1) at 300-500 m. H. azteca 10-day survival varied spatially and temporally up to 100 m from inflow. Animal growth, independent of survival, was reduced 40 and 100 m from inflow on day 36, showing continued sediment toxicity of up to 100 m from inflow more than 1 month after amendment. Animal survival and growth were unaffected at 300 and 500 m from inflow throughout the study period. Correlations of pesticide concentrations and H. azteca responses indicated that observed sediment toxicity was primarily from permethrin with potential additional synergistic toxicity from atrazine and methyl parathion. Study results indicate that natural backwater wetlands can be managed to ameliorate pesticide mixture 10-day sediment toxicity to H. azteca within 300 m of inflow and smaller wetlands (<100 m) may require several months of effluent retention to mitigate effects.
机译:我们检查了三种农药的改良混合物阿特拉津(72.7 g),5-甲草胺(54.5 g)和苄氯菊酯(顺式和反式异构体; 11.4 g)对10天沉积物对Hyalella azteca的毒性。在模拟的农业径流事件发生后,对天然回水湿地进行管理。修正前13天,修正后1、5、12、22和36天,分别在进水口10、40、100、300和500 m处收集沉积物样品。阿特拉津,5-异丙甲草胺和氯菊酯的本底农药浓度分别为<1至977,<1至119和<1至2μgkg〜(-1)。修正后的r去津和5-甲草胺在10-40 m处分别为2,915-3,927和3-20μgkg〜(-1),在300下分别为<1μgkg〜(-1) -500米苄氯菊酯的平均修正后浓度在10-40 m时为65-200μgkg〜(-1),在300-500 m时为1-10μgkg〜(-1)。 H. azteca 10天生存期在距流入量100 m的位置在时间和空间上变化。在第36天,动物的生长(与生存无关)从流入量减少了40和100 m,显示出在改良后超过1个月的时间里,流入量高达100 m的持续沉积物毒性。在整个研究期间,动物的存活和生长在流入300和500 m时均不受影响。农药浓度和H. azteca反应的相关性表明,观察到的沉积物毒性主要来自氯菊酯,而at去津和甲基对硫磷具有潜在的附加协同毒性。研究结果表明,天然回水湿地可在入水300 m以内改善农药混合物10天沉积物对阿兹台克人的毒性,较小的湿地(<100 m)可能需要保留几个月的废水以减轻影响。

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