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[Transformation mechanism of carbon tetrachloride and the associated micro-ecology in landfill cover, a typical functional layer zone].

作者信息

Wang Yongqiong, Xing Zhilin, Chen Shangjie, Su Xia, Cao Kun, Cao Ludan, Liao Shushu, Dong Langlang, Ai Shuo, Zhao Tiantao

机构信息

School of Chemistry and Chemical Engineering, Chongqing University of Technology, Chongqing 400054, China.

Chongqing Shiji Ecological Environment Technology Co., Ltd., Chongqing 404100, China.

出版信息

Sheng Wu Gong Cheng Xue Bao. 2022 May 25;38(5):1874-1888. doi: 10.13345/j.cjb.210564.

DOI:10.13345/j.cjb.210564
PMID:35611735
Abstract

Landfill is one of the important sources of carbon tetrachloride (CT) pollution, and it is important to understand the degradation mechanism of CT in landfill cover for better control. In this study, a simulated landfill cover system was set up, and the biotransformation mechanism of CT and the associated micro-ecology were investigated. The results showed that three stable functional zones along the depth, i.e., aerobic zone (0-15 cm), anoxic zone (15-45 cm) and anaerobic zone (> 45 cm), were generated because of long-term biological oxidation in landfill cover. There were significant differences in redox condition and microbial community structure in each zone, which provided microbial resources and favorable conditions for CT degradation. The results of biodegradation indicated that dechlorination of CT produced chloroform (CF), dichloromethane (DCM) and Cl in anaerobic and anoxic zones. The highest concentration of dechlorination products occurred at 30 cm, which were degraded rapidly in aerobic zone. In addition, CT degradation rate was 13.2-103.6 μg/(m·d), which decreased with the increase of landfill gas flux. The analysis of diversity sequencing revealed that , and were potential CT-degraders in aerobic, anaerobic and anoxic zone, respectively. Moreover, six species of dechlorination bacteria and eighteen species of methanotrophs were also responsible for anaerobic transformation of CT and aerobic degradation of CF and DCM, respectively. Interestingly, anaerobic dechlorination and aerobic transformation occurred simultaneously in the anoxic zone in landfill cover. Furthermore, analysis of degradation mechanism suggested that generation of stable anaerobic-anoxic-aerobic zone by regulation was very important for the harmless removal of full halogenated hydrocarbon in vadose zone, and the increase of anoxic zone scale enhanced their removal. These results provide theoretical guidance for the removal of chlorinated pollutants in landfills.

摘要

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