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新型菌株芽孢杆菌Cr02对Cr(VI)的生物修复机制:通过好氧/厌氧同步还原作用将土壤中的Cr(VI)去除至地下水中。

Cr(VI)-bioremediation mechanism of a novel strain Bacillus sp. Cr02 with simultaneous aerobic/anaerobic reduction for Cr(VI) from soil to groundwater.

作者信息

Liu Liping, Liu Rui, Wang Fang, Wu Yujun, Ge Fei, Tian Jiang, Li Feng, Xue Shengguo

机构信息

Hunan Provincial University Key Laboratory for Environmental and Ecological Health, College of Environment and Resources, Xiangtan University, Xiangtan 411105, China.

Hunan Provincial University Key Laboratory for Environmental and Ecological Health, College of Environment and Resources, Xiangtan University, Xiangtan 411105, China.

出版信息

J Hazard Mater. 2025 Sep 5;495:139034. doi: 10.1016/j.jhazmat.2025.139034. Epub 2025 Jun 23.

Abstract

Microbial remediation strategies have been developed to alleviate chromium (Cr) contamination in soil and groundwater. However, the complex redox conditions resulting from variations in oxygen content at different depths of the soil-groundwater system limit the ability of most microorganisms to achieve aerobic/anaerobic sustained bioreduction of Cr(VI) from topsoil to groundwater in contaminated industrial sites. This work screened a novel strain, Bacillus megaterium Cr02, investigated its unique Cr(VI) reduction mechanisms under aerobic and anaerobic conditions, and evaluated its performance in practical soil-groundwater remediation. The results showed that strain Cr02 could rapidly reduce Cr(VI) at an initial concentration of 100 mg/L in groundwater under both conditions. The ChrR enzyme was identified as a key player in aerobic Cr(VI) reduction, with molecular docking showing its hydrophobic interaction with Cr(VI). Conversely, the extracellular reducing metabolite cysteine became the major contributor to anaerobic Cr(VI) reduction. Moreover, their reduction products were further demonstrated to comprise soluble Cr(III) and Cr(OH) precipitates. In soil redox alternations, strain Cr02 stably converted > 90 % of Cr(VI) to residual chromium. These findings highlight the strain's ability to synergistically remediate soil and groundwater, positioning it as a promising candidate for the bioremediation of Cr pollution in dynamic oxygen-containing environments.

摘要

微生物修复策略已被开发用于减轻土壤和地下水中的铬(Cr)污染。然而,土壤 - 地下水系统不同深度处氧含量变化所导致的复杂氧化还原条件限制了大多数微生物在受污染工业场地中实现从表土到地下水的Cr(VI)需氧/厌氧持续生物还原的能力。这项工作筛选了一种新型菌株巨大芽孢杆菌Cr02,研究了其在需氧和厌氧条件下独特的Cr(VI)还原机制,并评估了其在实际土壤 - 地下水修复中的性能。结果表明,菌株Cr02在两种条件下都能迅速还原地下水中初始浓度为100 mg/L的Cr(VI)。ChrR酶被确定为需氧Cr(VI)还原的关键参与者,分子对接显示其与Cr(VI)存在疏水相互作用。相反,细胞外还原代谢物半胱氨酸成为厌氧Cr(VI)还原的主要贡献者。此外,进一步证明它们的还原产物包括可溶性Cr(III)和Cr(OH)沉淀物。在土壤氧化还原交替过程中,菌株Cr02能将> 90%的Cr(VI)稳定转化为残留铬。这些发现突出了该菌株协同修复土壤和地下水的能力,使其成为动态含氧环境中Cr污染生物修复的有前途候选者。

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