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由污水污泥衍生的含铁生物炭促进的细胞外电子转移对硝基苯的还原作用。

The reduction of nitrobenzene by extracellular electron transfer facilitated by Fe-bearing biochar derived from sewage sludge.

作者信息

Lu Yue, Xie Qingqing, Tang Lin, Yu Jiangfang, Wang Jingjing, Yang Zhaohui, Fan Changzheng, Zhang Shoujuan

机构信息

College of Environmental Science and Engineering, Hunan University, Changsha 410082, China; Key Laboratory of Environmental Biology and Pollution Control, Hunan University, Ministry of Education, Changsha 410082, China.

College of Environmental Science and Engineering, Hunan University, Changsha 410082, China; Key Laboratory of Environmental Biology and Pollution Control, Hunan University, Ministry of Education, Changsha 410082, China.

出版信息

J Hazard Mater. 2021 Feb 5;403:123682. doi: 10.1016/j.jhazmat.2020.123682. Epub 2020 Aug 13.

Abstract

In this work, the incorporation of Fe-bearing sludge-derived biochar greatly enhanced both biotic and abiotic reduction of nitrobenzene (NB) to aniline, which was attributed to the concomitant microbial dissimilatory iron reduction. Biogenic Fe(II) produced by Geobacter sulfurreducens dominated the anaerobic reduction of NB following the pseudo-first-order kinetic. Besides, the increase of pyrolysis temperature from 600 to 900 ℃ to generate biochar resulted in an accelerated removal rate of NB in Geobacter-biochar combined system. The morphology and structural characterization of biochar with G. sulfurreducens confirmed the formation of conductive bacteria-biochar aggregates. Electrochemical measurements suggested the presence of graphitized domains and quinone-like moieties in biochar as redox-active centers, which might play an important role in accelerating electron transfer for microbial dissimilatory iron reduction and NB degradation. This study provides a feasible way of using Fe-bearing sludge as a valuable feedstock for biochar generation and its application with electrochemically active bacteria for the bioremediation of nitroaromatic compounds-polluted wastewater.

摘要

在这项工作中,含铁污泥衍生生物炭的加入极大地增强了硝基苯(NB)向苯胺的生物和非生物还原,这归因于伴随的微生物异化铁还原。嗜硫地杆菌产生的生物源Fe(II)主导了NB的厌氧还原,遵循准一级动力学。此外,将热解温度从600℃提高到900℃以生成生物炭,导致嗜硫地杆菌-生物炭联合系统中NB的去除速率加快。嗜硫地杆菌生物炭的形态和结构表征证实了导电细菌-生物炭聚集体的形成。电化学测量表明生物炭中存在石墨化域和醌类部分作为氧化还原活性中心,这可能在加速微生物异化铁还原和NB降解的电子转移中起重要作用。本研究提供了一种可行的方法,即利用含铁污泥作为生物炭生成的宝贵原料,并将其与电化学活性细菌一起应用于硝基芳香化合物污染废水的生物修复。

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