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生物强化以增强厌氧条件下水中和沉积物中乙草胺和丙草胺的降解。

Bioaugmentation to enhance degradation of acetochlor and pretilachlor in water and sediment under anaerobic conditions.

作者信息

Duc Ha Danh, Oanh Nguyen Thi

机构信息

The department of Agriculture, Natural Resources and Environment, Dong Thap University, 783 Pham Huu Lau Street, Cao Lanh City, Dong Thap Province 870000, Viet Nam.

出版信息

FEMS Microbiol Lett. 2025 Jan 10;372. doi: 10.1093/femsle/fnae114.

DOI:10.1093/femsle/fnae114
PMID:39719364
Abstract

Chloroacetamide herbicides are widely used to control weeds globally. In this study, three acetochlor-degrading mixed cultures using nitrate, sulfate, and ferric iron as electron acceptors were isolated and determined for their degradation under anaerobic conditions. The degradation rates of all mixed pure cultures in a mineral medium were not much different at 1 µM, while the rates at 50 µM were in the order: mixed culture using nitrate > sulfate > ferric iron as electron acceptors, giving 6.70, 6.13, and 4.85 µM/day, respectively. During acetochlor degradation, 2-ethyl-6-methyl-N-(ethoxymethyl)acetanilide, N-2-ethylphenyl acetamide, and 2-ethylaniline were transiently produced. Interestingly, the mixture of all cultures synergistically degraded pretilachlor although no individual strains could degrade the compound. Toluene and 2-ethylaniline were metabolites of pretilachlor degradation by the acetochlor-degrading bacteria. However, pretilachlor inhibited the acetochlor degradation by acetochlor-degrading bacteria. The inoculation of both acetochlor- and pretilachlor-degrading bacteria resulted in 91.4 ± 2.1% of acetochlor and 82.4 ± 2.6% of pretilachlor being utilized for 7 days. Moreover, the introduction of these degrading bacteria accelerated the degradation of both substrates contaminating water and sediment collected from a pond. This study provides insights into anaerobic degradation by pure cultures using different electron acceptors.

摘要

氯乙酰胺类除草剂在全球范围内被广泛用于控制杂草。在本研究中,分离出了三种以硝酸盐、硫酸盐和铁离子作为电子受体的乙草胺降解混合培养物,并测定了它们在厌氧条件下的降解情况。在矿物培养基中,所有混合纯培养物在1µM时的降解速率差异不大,而在50µM时的降解速率顺序为:以硝酸盐作为电子受体的混合培养物>以硫酸盐作为电子受体的混合培养物>以铁离子作为电子受体的混合培养物,降解速率分别为6.70、6.13和4.85µM/天。在乙草胺降解过程中,会短暂产生2-乙基-6-甲基-N-(乙氧基甲基)乙酰苯胺、N-2-乙基苯基乙酰胺和2-乙基苯胺。有趣的是,尽管没有单个菌株能够降解丙草胺,但所有培养物的混合物能协同降解丙草胺。甲苯和2-乙基苯胺是乙草胺降解菌降解丙草胺的代谢产物。然而,丙草胺会抑制乙草胺降解菌对乙草胺的降解。接种乙草胺降解菌和丙草胺降解菌后7天,91.4±2.1%的乙草胺和82.4±2.6%的丙草胺被利用了。此外,引入这些降解菌加速了对从池塘采集的受污染水和沉积物中两种底物的降解。本研究为使用不同电子受体的纯培养物进行厌氧降解提供了见解。

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引用本文的文献

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Biodegradation of pretilachlor and butachlor by novel bacterial strains isolated from paddy field soil.从稻田土壤中分离出的新型菌株对丙草胺和丁草胺的生物降解作用
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