首页> 外文期刊>Journal of Environmental Science and Health, Part B: Pesticides, Food Contaminants, and Agricultural Wastes >Dissipation of herbicides chlorsulfuron and imazosulfuron in the soil and the effects on the soil bacterial community
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Dissipation of herbicides chlorsulfuron and imazosulfuron in the soil and the effects on the soil bacterial community

机译:除草剂氯磺隆和咪唑磺隆在土壤中的消散及其对土壤细菌群落的影响

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Dissipation of Sulfonylurea herbicides has rarely been studied due to their low application dosage. In this study, two herbicides, chlorsulfuron and imazosulfuron, were applied to both Podu (Pu) and Wolylin (Wl) soils at concentrations of 10 mg kg−1 or 50 mg kg−1 with soils at filled water holding capacity and incubation under 30°C. Changes in the soil bacterial community were examined with denaturing gradient gel electrophoresis (DGGE), whereas the residue of the herbicides was measured by high performance liquid chromatography (HPLC). The dissipation mechanisms of the two herbicides were both chemical and biological. The half-life of chlorsulfuron is 6.8-28.4 days and that of imazosulfuron is 6.4-14.6 days. These both dissipate faster in a more acidic soil. A higher dosage inhibited 48 % of the dissipation of the chlorsulfuron in Wl soil. However, larger differences were not observed in other treatments. The half-lives of both herbicides for 10 mg kg−1 or 50 mg kg−1 concentrations were less than one month. The microbial community was changed after the chlorsulfuron and imazosulfuron were spiked. Two sulfonylurea herbicides changed the soil bacterial composition after they were amended, and the change was larger with imazosulfuron under 50 mg kg−1 of concentration.
机译:磺酰脲类除草剂的消散由于其低施用量而很少被研究。在这项研究中,两种除草剂氯磺隆和咪唑磺隆分别以10 mg kg -1或50 mg kg 的浓度施用于Podu(Pu)和Wolylin(Wl)土壤。 ˆ’1 ,土壤保持充水,并在30°C下孵育。用变性梯度凝胶电泳(DGGE)检测土壤细菌群落的变化,而除草剂的残留通过高效液相色谱(HPLC)测量。两种除草剂的耗散机理是化学的和生物的。氯磺隆的半衰期是6.8-28.4天,咪唑磺隆的半衰期是6.4-14.6天。它们都在更酸性的土壤中更快地消散。较高的剂量抑制了W1土壤中氯磺隆消散的48%。然而,在其他治疗中未观察到较大的差异。两种除草剂在10 mg kg -1 或50 mg kg -1 浓度下的半衰期均少于一个月。加标氯磺隆和咪唑磺隆后,微生物群落发生了变化。两种磺酰脲类除草剂经过修改后改变了土壤细菌的组成,而咪唑磺隆在50 mg kg 1 浓度下的变化更大。

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