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薄膜对二甲基二硫醚排放、土壤垂直分布和熏蒸后残留的影响。

Effect of films on dimethyl disulfide emissions, vertical distribution in soil and residues remaining after fumigation.

机构信息

State Key Laboratory for Biology of Plant Disease and Insect Pests, Institute of Plant Protection, Chinese Academy of Agricultural Sciences, Beijing 100193, China.

State Key Laboratory for Biology of Plant Disease and Insect Pests, Institute of Plant Protection, Chinese Academy of Agricultural Sciences, Beijing 100193, China.

出版信息

Ecotoxicol Environ Saf. 2018 Nov 15;163:76-83. doi: 10.1016/j.ecoenv.2018.07.063. Epub 2018 Jul 23.

Abstract

An improved understanding of the conditions that influence dimethyl disulfide (DMDS) emissions, distribution through the soil and residues remaining after treatment will help to optimise the use of this relatively new soil fumigant for the control of soil-borne pests and disease, and to improve the safety of DMDS use. Using soil columns in the laboratory, the cumulative emission of DMDS using doses of 40 and 80 g m were, respectively, 74.8% and 68.9% with bare soil, 4.2% and 9.6% with polyethylene (PE) film, 0.02% and 0.2% with Totally Impermeable Film (TIF). Six hours after injection DMDS was detected mostly 5 cm below the surface and very little at 25 cm when used on bare soil, compared with much higher and similar concentrations of DMDS 5 and 25 cm deep when films were used. DMDS at the injection port exceeded 1 µg cm for longer when a film was used instead of bare soil. The total DMDS soil residues remaining in the soil, as a percentage of the initial DMDS dose at 40 or 80 g m were, respectively, 1.17 and 5.58 with TIF, 0.91 and 1.18 with PE, 0.47 and 0.47 with bare soil. DMDS rose rapidly upwards and escaped from bare soil, whereas PE or TIF significantly reduced DMDS emissions, retained elevated DMDS concentrations in the soil for longer and distributed them more uniformly in the soil. TIF performed better in these respects than PE. TIF also reduced the potential environmental impact of DMDS more than PE, especially at the higher dose.

摘要

提高对影响二甲基二硫(DMDS)排放、在土壤中分布以及处理后残留的条件的认识,将有助于优化这种相对较新的土壤熏蒸剂的使用,以控制土壤传播的病虫害,并提高 DMDS 使用的安全性。在实验室中使用土壤柱,使用 40 和 80g/m2 的剂量时,DMDS 的累积排放量分别为裸土的 74.8%和 68.9%,聚乙烯(PE)膜的 4.2%和 9.6%,完全不透膜(TIF)的 0.02%和 0.2%。在裸土上使用时,注射后 6 小时 DMDS 主要检测到距离表面 5cm 以下,而在 25cm 处很少,而在使用薄膜时,DMDS 的浓度则高得多且相似,在 5 和 25cm 深处。当使用薄膜代替裸土时,在注射口处 DMDS 超过 1µg/cm 的时间更长。TIF 处理的土壤中残留的总 DMDS 量,分别为初始 DMDS 剂量的 40 或 80g/m2 的 1.17%和 5.58%,PE 处理的为 0.91%和 1.18%,裸土处理的为 0.47%和 0.47%。DMDS 迅速向上上升并从裸土中逸出,而 PE 或 TIF 则显著减少了 DMDS 的排放,使土壤中 DMDS 浓度保持在较高水平的时间更长,并更均匀地分布在土壤中。在这些方面,TIF 的性能优于 PE。TIF 还比 PE 更能减少 DMDS 的潜在环境影响,尤其是在较高剂量下。

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