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含铁黏土矿物增强腐生脱硫弧菌 CN32 对硝基苯的生物还原。

Iron(III)-bearing clay minerals enhance bioreduction of nitrobenzene by Shewanella putrefaciens CN32.

机构信息

Department of Civil and Environmental Engineering, The Pennsylvania State University , University Park, Pennsylvania 16801-1408, United States.

出版信息

Environ Sci Technol. 2015 Feb 3;49(3):1418-26. doi: 10.1021/es504149y. Epub 2015 Jan 22.

DOI:10.1021/es504149y
PMID:25565314
Abstract

Iron-bearing clay minerals are ubiquitous in the environment, and the clay-Fe(II)/Fe(III) redox couple plays important roles in abiotic reduction of several classes of environmental contaminants. We investigated the role of Fe-bearing clay minerals on the bioreduction of nitrobenzene. In experiments with Shewanella putrefaciens CN32 and excess electron donor, we found that the Fe-bearing clay minerals montmorillonite SWy-2 and nontronite NAu-2 enhanced nitrobenzene bioreduction. On short time scales (<50 h), nitrobenzene reduction was primarily biologically driven, but at later time points, nitrobenzene reduction by biologically formed structural Fe(II) in the clay minerals became increasingly important. We found that chemically reduced (dithionite) iron-bearing clay minerals reduced nitrobenzene more rapidly than biologically reduced iron-bearing clay minerals despite the minerals having similar structural Fe(II) concentrations. We also found that chemically reduced NAu-2 reduced nitrobenzene faster as compared to chemically reduced SWy-2. The different reactivity of SWy-2 versus NAu-2 toward nitrobenzene was caused by different forms of structural clay-Fe(II) in the clay minerals and different reduction potentials (Eh) of the clay minerals. Because most contaminated aquifers become reduced via biological activity, the reactivity of biogenic clay-Fe(II) toward reducible contaminants is particularly important.

摘要

含铁粘土矿物在环境中无处不在,粘土-Fe(II)/Fe(III)氧化还原对在几种环境污染物的非生物还原中起着重要作用。我们研究了含铁粘土矿物对硝基苯的生物还原作用。在与脱硫弧菌 CN32 和过量电子供体的实验中,我们发现含铁粘土矿物蒙脱石 SWy-2 和钠蒙脱石 NAu-2 增强了硝基苯的生物还原。在短时间尺度(<50 h)内,硝基苯的还原主要是由生物驱动的,但在稍后的时间点,粘土矿物中生物形成的结构 Fe(II)对硝基苯的还原变得越来越重要。我们发现,化学还原(连二亚硫酸钠)的含铁粘土矿物比生物还原的含铁粘土矿物还原硝基苯更快,尽管这些矿物具有相似的结构 Fe(II)浓度。我们还发现,与化学还原的 SWy-2 相比,化学还原的 NAu-2 更快地还原硝基苯。粘土矿物中结构粘土-Fe(II)的不同形式和粘土矿物的不同还原电位(Eh)导致了 SWy-2 与硝基苯之间不同的反应性。由于大多数受污染的含水层通过生物活性而还原,因此生物成因的粘土-Fe(II)对可还原污染物的反应性尤为重要。

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