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Treatment of groundwater containing Mn(II), Fe(II), As(III) and Sb(III) by bioaugmented quartz-sand filters

机译:生物强化石英砂滤池处理含Mn(II),Fe(II),As(III)和Sb(III)的地下水

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摘要

High concentrations of iron (Fe(II)) and manganese (Mn(II)) often occur simultaneously in groundwater. Previously, we demonstrated that Fe(II) and Mn(II) could be oxidized to biogenic Fe-Mn oxides (BFMO) via aeration and microbial oxidation, and the formed BFMO could further oxidize and adsorb other pollutants (e.g., arsenic (As(III)) and antimony (Sb(III))). To apply this finding to groundwater remediation, we established four quartz-sand columns for treating groundwater containing Fe(II), Mn(II), As(III), and Sb(III). A Mn-oxidizing bacterium (Pseudomonas sp. QJX-1) was inoculated into two parallel bioaugmented columns. Long-term treatment (120 d) showed that bioaugmentation accelerated the formation of Fe-Mn oxides, resulting in an increase in As and Sb removal. The bioaugmented columns also exhibited higher overall treatment effect and anti-shock load capacity than that of the non-bioaugmented columns. To clarify the causal relationship between the microbial community and treatment effect, we compared the biomass of active bacteria (reverse-transcribed real-time PCR), bacterial community composition (Miseq 16S rRNA sequencing) and community function (metagenomic sequencing) between the bioaugmented and non-bioaugmented columns. Results indicated that the QJX1 strain grew steadily and attached onto the filter material surface in the bioaugmented columns. In general, the inoculated strain did not significantly alter the composition of the indigenous bacterial community, but did improve the relative abundances of xenobiotic metabolism genes and Mn oxidation gene. Thus, bioaugmentation intensified microbial degradation/utilization for the direct removal of pollutants and increased the formation of Fe-Mn oxides for the indirect removal of pollutants. Our study provides an alternative method for the treatment of groundwater containing high Fe(II), Mn(II) and As/ (C) 2016 Elsevier Ltd. All rights reserved.
机译:高浓度的铁(Fe(II))和锰(Mn(II))通常在地下水中同时发生。以前,我们证明了通过曝气和微生物氧化可将Fe(II)和Mn(II)氧化为生物型Fe-Mn氧化物(BFMO),并且形成的BFMO可以进一步氧化和吸附其他污染物(例如砷(As( III))和锑(Sb(III))。为了将这一发现应用于地下水修复,我们建立了四个石英砂柱用于处理含Fe(II),Mn(II),As(III)和Sb(III)的地下水。将锰氧化细菌(Pseudomonas sp。QJX-1)接种到两个平行的生物强化柱中。长期处理(120 d)表明,生物强化作用加速了Fe-Mn氧化物的形成,从而增加了As和Sb的去除。生物强化柱也比非生物强化柱具有更高的整体处理效果和抗冲击负荷能力。为了阐明微生物群落与治疗效果之间的因果关系,我们比较了生物强化菌和活性菌之间活性细菌的生物量(逆转录实时PCR),细菌群落组成(Miseq 16S rRNA测序)和群落功能(元基因组测序)。非生物强化色谱柱。结果表明,QJX1菌株稳定生长并附着在生物增强柱中的过滤材料表面上。通常,接种的菌株并没有显着改变本地细菌群落的组成,但是确实改善了异种代谢基因和Mn氧化基因的相对丰度。因此,生物强化增强了微生物的降解/利用,以直接去除污染物,并增加了铁锰氧化物的形成,以间接去除污染物。我们的研究提供了一种处理含高Fe(II),Mn(II)和As /(C)的地下水的替代方法。2016 Elsevier Ltd.保留所有权利。

著录项

  • 来源
    《Water Research》 |2016年第1期|126-134|共9页
  • 作者单位

    Chinese Acad Sci, Res Ctr Ecoenvironm Sci, Key Lab Drinking Water Sci & Technol, Beijing 100085, Peoples R China;

    Chinese Acad Sci, Res Ctr Ecoenvironm Sci, Key Lab Drinking Water Sci & Technol, Beijing 100085, Peoples R China|Univ Chinese Acad Sci, Beijing 100049, Peoples R China;

    Chinese Acad Sci, Res Ctr Ecoenvironm Sci, Key Lab Drinking Water Sci & Technol, Beijing 100085, Peoples R China|Univ Chinese Acad Sci, Beijing 100049, Peoples R China;

    Chinese Acad Sci, Res Ctr Ecoenvironm Sci, Key Lab Drinking Water Sci & Technol, Beijing 100085, Peoples R China;

    Chinese Acad Sci, Res Ctr Ecoenvironm Sci, Key Lab Drinking Water Sci & Technol, Beijing 100085, Peoples R China;

  • 收录信息 美国《科学引文索引》(SCI);美国《工程索引》(EI);
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

    Bioaugmentation; Biogenic Fe-Mn oxides; As; Sb; Community composition and function;

    机译:生物强化;生物Fe-Mn氧化物;As;Sb;群落组成与功能;

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