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微生物介导的磺胺甲恶唑在还原土壤条件下的非生物转化。

Microbially mediated abiotic transformation of the antimicrobial agent sulfamethoxazole under iron-reducing soil conditions.

机构信息

Department of Civil and Environmental Engineering, University of Illinois at Urbana-Champaign, Urbana, Illinois 61801, USA.

出版信息

Environ Sci Technol. 2011 Jun 1;45(11):4793-801. doi: 10.1021/es200413g. Epub 2011 May 4.

DOI:10.1021/es200413g
PMID:21542626
Abstract

Large quantities of antimicrobial agents used in livestock production are released to soils by land application of manure, but only limited information is available on mechanisms that contribute to antimicrobial fate in soils under variable biogeochemical conditions. Dissipation of the sulfonamide antimicrobial sulfamethoxazole was examined in soil microcosms incubated under different terminal electron-accepting conditions (aerobic, nitrate-reducing, Fe(III)-reducing, and sulfate-reducing). Somewhat unexpectedly, sulfamethoxazole dissipation was fastest under Fe(III)-reducing conditions, with concentrations decreasing by >95% within 1 day. The rapid transformation was attributed to abiotic reactions between sulfamethoxazole and Fe(II) generated by microbial reduction of Fe(III) soil minerals. Separate experiments demonstrated that sulfamethoxazole was abiotically transformed in Fe(II)-amended aqueous suspensions of goethite (α-FeOOH((s))), and observed rate constants varied with the extent of Fe(II) sorption to goethite. Sulfamethoxazole transformation is initiated by a 1-electron reductive cleavage of the N-O bond in the isoxazole ring substituent, and observed products are consistent with Fe(II)-mediated reduction and isomerization processes. These findings reveal potentially important, but previously unrecognized, pathways that may contribute to the fate of sulfamethoxazole and related chemicals in reducing soil environments.

摘要

大量用于畜牧业生产的抗菌剂通过粪肥的土地施用释放到土壤中,但关于在可变生物地球化学条件下土壤中抗菌剂命运的机制,只有有限的信息。在不同的末端电子接受条件(好氧、硝酸盐还原、铁还原和硫酸盐还原)下,在土壤微宇宙中培养时,考察了磺胺类抗菌药磺胺甲恶唑的消散情况。有点出人意料的是,磺胺甲恶唑在铁还原条件下的消散速度最快,在 1 天内浓度下降了>95%。这种快速转化归因于磺胺甲恶唑与微生物还原铁土壤矿物产生的 Fe(II)之间的非生物反应。单独的实验表明,磺胺甲恶唑在针铁矿(α-FeOOH((s)))的 Fe(II) 修正水悬浮液中发生非生物转化,观察到的速率常数随针铁矿对 Fe(II)的吸附程度而变化。磺胺甲恶唑的转化是由异恶唑环取代基中的 N-O 键的 1 电子还原裂解引发的,观察到的产物与 Fe(II)介导的还原和异构化过程一致。这些发现揭示了可能在还原土壤环境中磺胺甲恶唑和相关化学物质命运中起重要作用但以前未被认识到的途径。

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