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含氧微生物阴极监测自来水中的毒性冲击。

Oxygen-reducing microbial cathodes monitoring toxic shocks in tap water.

机构信息

Center for Microbial Ecology and Technology (CMET), Campus Coupure - Ghent University, Coupure Links 653, 9000 Ghent, Belgium.

Center for Microbial Ecology and Technology (CMET), Campus Coupure - Ghent University, Coupure Links 653, 9000 Ghent, Belgium.

出版信息

Biosens Bioelectron. 2019 May 1;132:115-121. doi: 10.1016/j.bios.2019.02.037. Epub 2019 Feb 21.

DOI:10.1016/j.bios.2019.02.037
PMID:30856427
Abstract

Electroactive biofilms (EABs) have recently attracted considerable research interest for their possible use as amperometric biosensors in environmental or bioprocess monitoring, for example for in situ detection of toxic compounds. Almost exclusively, corresponding research has focused on heterotrophic, anodic EABs. These biofilms require sufficiently high organic loads and anoxic conditions to deliver a stable baseline current. Conversely, electroautotrophic O-reducing EABs have recently been proposed to monitor toxic shocks in oxic solutions that are poor or devoid of organic substrate. This was done in optimal media and only assessed for formaldehyde as a model toxic compound. Here we show that O-reducing EABs can grow in unamended tap water on carbon electrodes at + 0.2 V vs. Ag/AgCl. They retained substantial electroactivity for at least eight months without adding exogenous compounds. The most represented operational taxonomic units were assigned to the phylum Gammaproteobacteria (25 ± 15%, n = 5 electrodes). Cyclic voltammograms showed a reproducible nernstian behavior for O reduction with a mid-wave potential at + 0.27 V and variable plateau current densities ranging from - 1 to - 22 µA cm (n = 10 electrodes). The biocatalytic current was substantially impacted by the addition of either of three tested heavy metals (Hg(II), Cr(VI) or Pb(II)) or by organic pollutants (formaldehyde, 2,4-dichlorophenol, benzalkonium chloride), with limits of detection ranging from 0.5 to 10 mg L (2.5-61 µmol L). Response times were typically around 1 min. Comparison with previous reports suggests that O-reducing microbial cathodes may be more sensitive to toxic shocks than anodic, heterotrophic EABs.

摘要

电活性生物膜(EAB)最近因其在环境或生物过程监测中的应用潜力而引起了相当大的研究兴趣,例如用于原位检测有毒化合物。几乎完全集中在异养、阳极 EAB 上。这些生物膜需要足够高的有机负荷和缺氧条件才能提供稳定的基线电流。相反,最近有人提出电自养 O 还原 EAB 可用于监测贫氧或缺乏有机基质的好氧溶液中的有毒冲击。这是在最佳培养基中完成的,并且仅评估了甲醛作为模型有毒化合物。在这里,我们表明 O 还原 EAB 可以在未加修正的自来水和碳电极上在+0.2 V 对 Ag/AgCl 下生长。它们在不添加外源化合物的情况下至少保持了 8 个月的显著电活性。最具代表性的操作分类单元被分配给γ变形菌门(25±15%,n=5 个电极)。循环伏安法显示 O 还原的可重现的能斯特行为,中波电位为+0.27 V,可变平台电流密度范围为-1 至-22 µA cm(n=10 个电极)。生物催化电流受到三种测试重金属(Hg(II)、Cr(VI)或 Pb(II))或有机污染物(甲醛、2,4-二氯苯酚、苯扎氯铵)的添加的显著影响,检测限范围从 0.5 到 10 mg L(2.5-61 µmol L)。响应时间通常约为 1 分钟。与以前的报告相比,这表明 O 还原微生物阴极可能比阳极、异养 EAB 对有毒冲击更敏感。

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