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Enhanced biodegradation of PAHs in historically contaminated soil by M. gilvum inoculated biochar

机译:吉尔伯氏菌接种的生物炭增强了历史污染土壤中PAHs的生物降解

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摘要

The inoculation of rice straw biochar with PAH-degrading Mycobacterium gilvum (1.27 x 10(11) +/- 1.24 x 10(10) cell g(-1)), and the subsequent amendment of this composite material to PAHs contaminated (677 mg kg(-1)) coke plant soil, was conducted in order to investigate if would enhance PAHs biodegradation in soils. The microbe-biochar composite showed superior degradation capacity for phenanthrene, fluoranthene and pyrene. Phenanthrene loss in the microbe-biochar composite, free cell alone and biochar alone treatments was, respectively, 62.6 +/- 3.2%, 47.3 +/- 4.1% and non-significant (P > 0.05); whereas for fluoranthene loss it was 52.1 +/- 23%; non-significant (P > 0.05) and nonsignificant (P > 0.05); and for pyrene loss it was 62.1 +/- 0.9%; 19.7 +/- 6.5% and 13.5 +/- 2.8%. It was hypothesized that the improved remediation was underpinned by i) biochar enhanced mass transfer of PAHs from the soil to the carbonaceous biochar "sink", and ii) the subsequent degradation of the PAHs by the immobilized M. gilvum. To test this mechanism, a surfactant (Brij 30; 20 mg g(-1) soil), was added to impede PAHs mass transfer to biochar and sorption. The surfactant increased solution phase PAH concentrations and significantly (P < 0.05) reduced PAH degradation in the biochar immobilized M. gilvum treatments; indicating the enhanced degradation occurred between the immobilized M. gilvum and biochar sorbed PAHs. (C) 2017 Elsevier Ltd. All rights reserved.
机译:用降解PAH的分枝杆菌(1.27 x 10(11)+/- 1.24 x 10(10)细胞g(-1))接种稻草生物炭,随后将该复合材料修正为被污染的PAHs(677 mg为了研究是否会增强土壤中PAHs的生物降解性,进行了kg(-1))焦炭厂土壤研究。微生物-生物炭复合材料对菲,荧蒽和pyr具有优异的降解能力。微生物-生物炭复合物,单独的游离细胞和单独的生物炭处理中的菲损失分别为62.6 +/- 3.2%,47.3 +/- 4.1%和不显着(P> 0.05);而荧蒽的损失为52.1 +/- 23%;不显着(P> 0.05)和不显着(P> 0.05); pyr损失为62.1 +/- 0.9%; 19.7 +/- 6.5%和13.5 +/- 2.8%。据推测,改善的修复是通过以下方式来支撑的:i)生物炭增强了PAHs从土壤向碳质生物炭“沉”的传质,ii)随后固定化的吉氏甲烷八叠球菌降解了PAHs。为了测试此机制,添加了表面活性剂(Brij 30; 20 mg g(-1)土壤),以阻止PAHs传质至生物炭和吸附。表面活性剂增加了溶液相多环芳烃的浓度,并显着(P <0.05)减少了生物炭固定化的金缕梅处理中多环芳烃的降解。这表明降解的增强发生在固定化的吉氏支原体和生物炭吸附的PAH之间。 (C)2017 Elsevier Ltd.保留所有权利。

著录项

  • 来源
    《Chemosphere》 |2017年第9期|316-324|共9页
  • 作者单位

    Chinese Acad Sci, Inst Urban Environm, Key Lab Urban Environm & Hlth, Xiamen 361021, Peoples R China|Univ Chinese Acad Sci, Beijing 100049, Peoples R China;

    Chinese Acad Sci, Inst Urban Environm, Key Lab Urban Environm & Hlth, Xiamen 361021, Peoples R China;

    Huaqiao Univ, Dept Environm Sci & Engn, Xiamen 361021, Peoples R China;

    NGI, POB 3930, N-0806 Oslo, Norway;

    Chinese Acad Sci, Inst Urban Environm, Key Lab Urban Environm & Hlth, Xiamen 361021, Peoples R China|Univ East Anglia, Sch Environm Sci, Norwich NR4 7TJ, Norfolk, England;

    Chinese Acad Sci, Inst Urban Environm, Key Lab Urban Environm & Hlth, Xiamen 361021, Peoples R China;

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

    PAHs; Biochar; Microbe immobilization; Soil; Degradation;

    机译:多环芳烃;生物炭;微生物固定;土壤;降解;

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