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地下水中四氯化碳的生物降解:微生物群落变化及参与强化还原脱氯的功能基因

Biodegradation of Carbon Tetrachloride in Groundwater: Microbial Community Shifts and Functional Genes Involvement in Enhanced Reductive Dechlorination.

作者信息

Liu Zhengwei, Sun Mingbo, Wang Wei, Zhao Shaolei, Xie Yan, Lin Xiaoyu, Liu Jingru, Zhang Shucai

机构信息

State Key Laboratory of Chemical Safety, Qingdao 266061, China.

SINOPEC Research Institute of Safety Engineering Co., Ltd., Qingdao 266061, China.

出版信息

Toxics. 2025 Aug 21;13(8):704. doi: 10.3390/toxics13080704.

DOI:10.3390/toxics13080704
PMID:40863980
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC12390548/
Abstract

Carbon tetrachloride (CT) is a toxic volatile chlorinated hydrocarbon, posing a serious hazard to ecosystem and human health. This study discussed the bioremediation possibility of groundwater contaminated by CT. Enhanced reductive dechlorination bioremediation (ERD) was used to promote the reductive dechlorination process of CT by adding yeast extract as a supplementary electron donor. The microcosm samples of the Control and Experi group were setup in the experiment, and the CT degradation efficiency and microbial community structure changes over 150 days were monitored. The results showed that the Experi group achieved complete degradation of CT within 40 days, while the control group had no significant change. By analyzing the physical and chemical indexes such as VFAs, sulfate ions, oxidation-reduction potential, pH value and so on, the key changes in the degradation process of CT were revealed. Microbial community analysis showed that specific microorganisms such as , and played a significant role in the degradation of CT. They may produce hydrogen through fermentation to provide electron donors for the reductive dechlorination of CT. In addition, the genes of reductive dehalogenase synthase related to CT degradation were also identified, which provided molecular evidence for understanding the biodegradation mechanism of CT. The results deliver a scientific basis for optimizing the bioremediation strategy of CT-contaminated groundwater.

摘要

四氯化碳(CT)是一种有毒的挥发性氯代烃,对生态系统和人类健康构成严重危害。本研究探讨了受CT污染的地下水的生物修复可能性。通过添加酵母提取物作为补充电子供体,采用强化还原脱氯生物修复(ERD)来促进CT的还原脱氯过程。实验设置了对照组和实验组的微观样本,并监测了150天内CT的降解效率和微生物群落结构变化。结果表明,实验组在40天内实现了CT的完全降解,而对照组没有显著变化。通过分析挥发性脂肪酸、硫酸根离子、氧化还原电位、pH值等理化指标,揭示了CT降解过程中的关键变化。微生物群落分析表明,特定微生物如 、 和 在CT的降解中发挥了重要作用。它们可能通过发酵产生氢气,为CT的还原脱氯提供电子供体。此外,还鉴定了与CT降解相关的还原脱卤酶合酶基因,为理解CT的生物降解机制提供了分子证据。研究结果为优化CT污染地下水的生物修复策略提供了科学依据。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a366/12390548/d01e8226938a/toxics-13-00704-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a366/12390548/fad47068b99e/toxics-13-00704-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a366/12390548/34cce5b8f693/toxics-13-00704-g002a.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a366/12390548/f143c86859d9/toxics-13-00704-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a366/12390548/1387b2ccec5d/toxics-13-00704-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a366/12390548/01ec4c746283/toxics-13-00704-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a366/12390548/a9f912415fe8/toxics-13-00704-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a366/12390548/0af380fabb3f/toxics-13-00704-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a366/12390548/d01e8226938a/toxics-13-00704-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a366/12390548/fad47068b99e/toxics-13-00704-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a366/12390548/34cce5b8f693/toxics-13-00704-g002a.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a366/12390548/f143c86859d9/toxics-13-00704-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a366/12390548/1387b2ccec5d/toxics-13-00704-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a366/12390548/01ec4c746283/toxics-13-00704-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a366/12390548/a9f912415fe8/toxics-13-00704-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a366/12390548/0af380fabb3f/toxics-13-00704-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/a366/12390548/d01e8226938a/toxics-13-00704-g008.jpg

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