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双氯芬酸在河流沉积物本地微生物群落作用下的转化及一种主要中间产物的鉴定

Transformation of diclofenac by the indigenous microflora of river sediments and identification of a major intermediate.

作者信息

Gröning Janosch, Held Claudia, Garten Claudia, Claussnitzer Ute, Kaschabek Stefan R, Schlömann Michael

机构信息

TU Bergakademie Freiberg, Environmental Microbiology, IOZ, D-09596 Freiberg, Germany.

出版信息

Chemosphere. 2007 Sep;69(4):509-16. doi: 10.1016/j.chemosphere.2007.03.037. Epub 2007 May 23.

DOI:10.1016/j.chemosphere.2007.03.037
PMID:17524452
Abstract

Diclofenac is a non-steroidal anti-inflammatory drug, which tends to be relatively persistent in the environment. Now, a fixed-bed column bioreactor filled with sediment from the creek Münzbach (Freiberg/Saxony) under aerobic conditions showed rapid removal of diclofenac in a concentration range of 3-35 microM without previous adaptation. The conversion of higher concentrations up to 260 microM was accompanied by conspicuously decreased turnover rates indicating a toxic effect of this drug or its resulting metabolic burden on the indigenous microflora. A major metabolite occurred transiently and was identified by NMR and MS to be the p-benzoquinone imine of 5-hydroxydiclofenac. Abiotic adsorption to the biofilm was shown to determine the further fate of this reactive product of 5-hydroxydiclofenac (aut-)oxidation. The apparent lack of a degradative potential for this compound as well as the failure to detect an enrichment of diclofenac-depleting microbial activity both indicate a cometabolic nature of diclofenac transformation. 4'-Hydroxy-diclofenac, the favoured transformation product of eucaryotic diclofenac metabolism, could not be identified. The ability to convert diclofenac was shown to be widespread among biofilms from different river sediments, but measured rates obviously do not correlate with the total microbial activity. In addition, application of sediments from locations exposed to communal waste water effluents did not indicate any form of adaptation measured as an increased specific diclofenac depletion rate.

摘要

双氯芬酸是一种非甾体抗炎药,在环境中往往具有相对持久性。现在,一个装有明茨巴赫小溪(弗赖贝格/萨克森州)沉积物的固定床柱式生物反应器在有氧条件下,在未经预先驯化的情况下,能快速去除浓度范围为3 - 35微摩尔的双氯芬酸。对于高达260微摩尔的较高浓度的转化,其周转率显著下降,这表明该药物或其产生的代谢负担对本地微生物群落具有毒性作用。一种主要代谢产物短暂出现,通过核磁共振(NMR)和质谱(MS)鉴定为5 - 羟基双氯芬酸的对苯醌亚胺。已证明非生物吸附到生物膜上决定了5 - 羟基双氯芬酸(自)氧化的这种反应性产物的进一步归宿。该化合物明显缺乏降解潜力,以及未能检测到双氯芬酸消耗微生物活性的富集,这两者都表明双氯芬酸转化具有共代谢性质。真核生物双氯芬酸代谢的首选转化产物4'-羟基双氯芬酸无法鉴定。已证明转化双氯芬酸的能力在来自不同河流沉积物的生物膜中广泛存在,但测得的速率显然与总微生物活性无关。此外,应用来自受城市废水排放影响地点的沉积物,并未显示出以增加的双氯芬酸比消耗率衡量的任何形式的适应性。

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