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实验室条件下两种土壤中乙草胺的矿化及其两种主要代谢产物的归宿

Acetochlor mineralization and fate of its two major metabolites in two soils under laboratory conditions.

作者信息

Dictor Marie-Christine, Baran Nicole, Gautier Anne, Mouvet Christophe

机构信息

BRGM, Avenue Claude Guillemin, BP 6009, 45060 Orléans cedex 2, France.

出版信息

Chemosphere. 2008 Mar;71(4):663-70. doi: 10.1016/j.chemosphere.2007.10.066. Epub 2008 Feb 20.

Abstract

The degradation of the herbicide acetochlor, in a neoluvisol and in a calcosol were studied as a function of depth (0-25cm and 25-50cm) and temperature (25 degrees C and 15 degrees C) under controlled laboratory conditions during 58 and 90 days, respectively. The surface and sub-surface soil samples were respectively spiked with 1 and 0.01mgkg(-1) of 14C-acetochlor, the concentrations observed in previous field monitoring. The half-lives (DT50) varied from 1.4 to 14.9 days depending on the soil, temperature and applied concentration. The maximal mineralization (24%) was observed for the surface calcosol at 25 degrees C. The comparison of results obtained for sterilized and non-sterilized soils, the decrease of DT50 with the increase of temperature, the shape of CO2 emissions and the increase of number of aerobic endogenous microflora through the experiment suggested that biological process are dominant in degradation. A particular attention was paid to the formation and dissipation of metabolites ESA (ethanesulphonic acid) and OA (oxanilic acid) during the whole experiment. At 25 degrees C, ESA and OA were observed after three days, but as ESA concentration decreased over time in surface calcosol, it remained constant in surface neoluvisol. A difference in ESA/OA ratio depends on the soil with a predominance of OA in surface neoluvisol and a disappearance of OA in surface calcosol.

摘要

在可控的实验室条件下,分别研究了除草剂乙草胺在新淋溶土和钙质土中的降解情况,该降解过程作为深度(0 - 25厘米和25 - 50厘米)和温度(25摄氏度和15摄氏度)的函数,持续时间分别为58天和90天。表层和亚表层土壤样本分别添加了1毫克/千克和0.01毫克/千克的14C - 乙草胺,这是先前田间监测中观察到的浓度。半衰期(DT50)在1.4至14.9天之间变化,具体取决于土壤、温度和施加浓度。在25摄氏度时,表层钙质土的矿化率最高(24%)。对灭菌土壤和未灭菌土壤所得结果的比较、DT50随温度升高而降低、二氧化碳排放的形状以及整个实验中好氧内源微生物数量的增加表明,生物过程在降解中占主导地位。在整个实验过程中,特别关注了代谢物ESA(乙磺酸)和OA(草酰苯胺酸)的形成和消散。在25摄氏度时,三天后观察到了ESA和OA,但随着时间的推移,表层钙质土中ESA浓度下降,而在表层新淋溶土中保持不变。ESA/OA比值的差异取决于土壤,表层新淋溶土中以OA为主,而表层钙质土中OA消失。

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