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Chromium-Resistant Bacteria Promote the Reduction of Hexavalent Chromium in Soils

机译:耐铬细菌促进土壤中六价铬的减少

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Knowledge of the chromium (Cr) redox process in soil is important in addressing Cr bioavailability and risk assessment of contaminated soils. In this study, seven representative agricultural soils with different physicochemical properties were used to investigate the importance of microbially mediated Cr(VI) reduction and the response of soil bacterial community to Cr contamination. Chromium application increased soil bacterial diversity in Periudic Argosols, Calcaric Regosols, Stagnic Anthrosols, Mollisols, Typic Haplustalfs, and Ustic Cambosols, with an exception of Udic Ferrisols. The soil bacterial community responded to Cr contamination through changes in bacterial community structure, with Cr-resistant bacteria becoming the dominant species, and the percentage of Cr-resistant bacteria of total cultivable bacteria was 89.9, 75.2, 92.8, 65.3, 72.8, 77.3, and 65.4%, respectively, for Periudic Argosols, Udic Ferrisols, Calcaric Regosols, Stagnic Anthrosols, Mollisols, Typic Haplustalfs, and Ustic Cambosols. Bacillus, Escherichia, Deinococcus, Micromonospora, Methylobacterium, Massilia, Acidobacterium, Comamonas, Bradyrhizobium, and Arthrobacter were identified as the Cr-resistant bacteria. Moreover, our results demonstrated that microbial reduction was an important Cr(VI) reduction pathway, and the relative contribution of microorganisms to Cr(VI) reduction was 14.4, 44.0, 20.6, 34.9, 21.9, 21.7, and 22.0%, respectively for Periudic Argosols, Udic Ferrisols, Calcaric Regosols, Stagnic Anthrosols, Mollisols, Typic Haplustalfs, and Ustic Cambosols. Soil properties, especially Fe(II) and soil particle distribution, affected the microbially mediated Cr(VI) reduction. These results provide useful information for the bioremediation of Cr-contaminated soils under a wide range of environmental conditions.
机译:了解土壤中的铬(Cr)氧化还原过程对于解决Cr的生物利用度和污染土壤的风险评估非常重要。在这项研究中,使用七种具有不同理化特性的代表性农业土壤来研究微生物介导的六价铬还原的重要性以及土壤细菌群落对铬污染的响应。铬的施用增加了Perodidic Argosols,钙质Regosols,Stagnic Anthrosols,Mollisols,Typic Haplustalfs和Ustic Cambosols中土壤细菌的多样性,但Udic Ferrisols除外。土壤细菌群落通过改变细菌群落结构而对Cr污染作出反应,其中Cr抵抗细菌成为优势种,可培养细菌中Cr抵抗细菌的百分比为89.9、75.2、92.8、65.3、72.8、77.3, Periodic Argosols,Udic Ferrisols,Calcaric Regosols,Stagnic Anthrosols,Mollisol,Typic Haplustalfs和Ustic Cambosols分别为65.4%。芽孢杆菌,大肠埃希氏菌,狄氏球菌,微小单孢菌,甲基杆菌,马塞利亚,嗜酸杆菌,Comamonas,缓生根瘤菌和节杆菌被鉴定为抗Cr细菌。此外,我们的研究结果表明,微生物减少是Cr(VI)减少的重要途径,微生物对Cr(VI)减少的相对贡献分别为14.4%,44.0、20.6、34.9、21.9、21.7和22.0%。 Argosols,Udic Ferrisols,Calcaric Regosols,Stagnic Anthrosols,Mollisols,Typic Haplustalfs和Ustic Cambosols。土壤特性,特别是Fe(II)和土壤颗粒分布,影响了微生物介导的Cr(VI)的减少。这些结果为在广泛的环境条件下对铬污染的土壤进行生物修复提供了有用的信息。

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