Li Zheng-Tao, Song Xin, Yuan Songhu, Zhao He-Ping
MOE Key Lab of Environmental Remediation and Ecosystem Health, College of Environmental and Resource Sciences, Zhejiang University, Hangzhou 310030, PR China.
CAS Key Laboratory of Soil Environment and Pollution Remediation, Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, PR China.
Water Res. 2024 Apr 1;253:121328. doi: 10.1016/j.watres.2024.121328. Epub 2024 Feb 16.
Chromium and organochlorine solvents, particularly trichloroethene (TCE), are pervasive co-existing contaminants in subsurface aquifers due to their extensive industrial use and improper disposal practices. In this study, we investigated the microbial dechlorination kinetics under different TCE-Cr(Ⅲ/VI) composite pollution conditions and elucidated microbial response mechanisms based on community shift patterns and metagenomic analysis. Our results revealed that the reductive dechlorinating consortium had high resistance to Cr(III) but extreme sensitivity to Cr(VI) disturbance, resulting in a persistent inhibitory effect on subsequent dechlorination. Interestingly, the vinyl chloride-respiring organohalide-respiring bacteria (OHRB) was notably more susceptible to Cr(III/VI) exposure than the trichloroethene-respiring one, possibly due to inferior competition for growth substrates, such as electron donors. In terms of synergistic non-OHRB populations, Cr(III/VI) exposure had limited impacts on lactate fermentation but significantly interfered with H-producing acetogenesis, leading to inhibited microbial dechlorination due to electron donor deficiencies. However, this inhibition can be effectively mitigated by the amendment of exogenous H supply. Furthermore, being the predominant OHRB, Dehalococcoides have inherent Cr(VI) resistance defects and collaborate with synergistic non-OHRB populations to achieve concurrent bio-detoxication of Cr(VI) and TCE. Our findings expand the understanding of the response patterns of different functional populations towards Cr(III/VI) stress, and provide valuable insights for the development of in situ bioremediation strategies for sites co-contaminated with chloroethene and chromium.
铬和有机氯溶剂,特别是三氯乙烯(TCE),由于其广泛的工业用途和不当的处置方式,是地下含水层中普遍存在的共存污染物。在本研究中,我们调查了不同TCE-Cr(Ⅲ/Ⅵ)复合污染条件下的微生物脱氯动力学,并基于群落变化模式和宏基因组分析阐明了微生物响应机制。我们的结果表明,还原脱氯菌群对Cr(Ⅲ)具有高抗性,但对Cr(Ⅵ)干扰极为敏感,导致对后续脱氯产生持续抑制作用。有趣的是,与三氯乙烯呼吸型的相比,氯乙烯呼吸型的有机卤化物呼吸细菌(OHRB)对Cr(Ⅲ/Ⅵ)暴露更为敏感,这可能是由于对生长底物(如电子供体)的竞争较弱。就协同非OHRB种群而言,Cr(Ⅲ/Ⅵ)暴露对乳酸发酵的影响有限,但显著干扰了产氢产乙酸过程,由于电子供体不足导致微生物脱氯受到抑制。然而,通过补充外源氢气可以有效减轻这种抑制作用。此外,作为主要的OHRB,脱卤球菌具有固有的Cr(Ⅵ)抗性缺陷,并与协同非OHRB种群协作,实现Cr(Ⅵ)和TCE的同时生物解毒。我们的研究结果扩展了对不同功能种群对Cr(Ⅲ/Ⅵ)胁迫响应模式的理解,并为开发氯乙烯和铬共污染场地的原位生物修复策略提供了有价值的见解。