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应用生态学报 ›› 2022, Vol. 33 ›› Issue (12): 3395-3402.doi: 10.13287/j.1001-9332.202212.030

• 研究论文 • 上一篇    下一篇

厌氧微生物菌群XH-1对2,4,6-三氯苯酚的降解特性

孙百惠1,2, 宋雪英1, 严俊2, 杨毅2, 吕燕3, 王晶晶2, 宋玉芳2, 李秀颖2*   

  1. 1沈阳大学区域污染环境生态修复教育部重点实验室, 沈阳 110044;
    2中国科学院沈阳应用生态研究所污染生态与环境工程重点实验室, 沈阳 110016;
    3甘肃省科学技术情报研究所, 兰州 730099
  • 收稿日期:2021-11-08 接受日期:2022-07-01 出版日期:2022-12-15 发布日期:2023-07-05
  • 通讯作者: * E-mail: lixiuying@iae.ac.cn
  • 作者简介:孙百惠, 女, 1996年生, 硕士研究生。主要从事污染环境微生物修复技术研究。E-mail: sunbaihui00@163.com
  • 基金资助:
    国家自然科学基金项目(41907220)、环境化学与生态毒理学国家重点实验室开放基金项目(KF2017-08)和沈阳市中青年人才科技支持计划项目(RC190371)

Degradation characteristics of 2,4,6-trichlorophenol by the anaerobic consortium XH-1

SUN Bai-hui1,2, SONG Xue-ying1, YAN Jun2, YANG Yi2, LYU Yan3, WANG Jing-jing2, SONG Yu-fang2, LI Xiu-ying2*   

  1. 1Key Laboratory of Ecological Restoration of Regional Polluted Environment, Ministry of Education, Shenyang University, Shenyang 110044, China;
    2Key Laboratory of Pollution Ecology and Environmental Engineering, Institute of Applied Ecology, Chinese Academy of Sciences, Shenyang 110016, China;
    3Gansu Institute of Science and Technology Information, Lanzhou 730099, China
  • Received:2021-11-08 Accepted:2022-07-01 Online:2022-12-15 Published:2023-07-05

摘要: 有机污染物2,4,6-三氯苯酚(2,4,6-TCP)普遍存在于地下水和河流底泥等厌氧环境中。为了探究厌氧微生物菌群XH-1对2,4,6-TCP的降解能力,本研究以2,4,6-TCP为底物,接种XH-1建立微宇宙培养体系,并以中间产物4-氯苯酚(4-CP)和苯酚为底物分别进行分段富集培养,利用高效液相色谱分析底物的降解转化,同时基于16S rRNA基因高通量测序分析微生物群落结构变化。结果表明: 2,4,6-TCP(122 μmol·L-1)以0.15 μmol·d-1的速率在80 d内被完全降解转化,降解中间产物分别为2,4-二氯苯酚(2,4-DCP)、4-氯苯酚和苯酚,所有中间产物最终在325 d被完全降解。高通量测序结果表明,脱卤杆菌和脱卤球菌可能驱动2,4,6-TCP还原脱氯,其中,脱卤球菌可能在4-CP的脱氯转化中发挥重要作用,并与丁酸互营菌和产甲烷菌联合作用彻底降解2,4,6-TCP。

关键词: 氯代苯酚, 厌氧生物降解, 富集培养, 还原脱氯

Abstract: Organic pollutant 2,4,6-trichlorophenol (2,4,6-TCP) is commonly found in anaerobic environments such as sediments and groundwater aquifers. To investigate the ability of the anaerobic consortium XH-1 to degrade 2,4,6-TCP, we established anaerobic incubations using 2,4,6-TCP as the substrate and inoculated the incubations with XH-1. Additional subcultures were established by amending with intermediate product 4-chlorophenol (4-CP) or phenol as the substrate. The transformation products of 2,4,6-TCP were analyzed and determined using high-performance liquid chromatography (HPLC). Microbial community structure and key microbial groups involved in the degradation of 2,4,6-TCP were analyzed based on 16S rRNA gene high-throughput sequencing. The results showed that the initial 122 μmol·L-1 2,4,6-TCP was completely transformed after a 80-day incubation at a rate of 0.15 μmol·d-1. 2,4-dichlorophenol (2,4-DCP), 4-CP and phenol were identified as the intermediate products. All intermediate products generated from 2,4,6-TCP transformation were completely degraded after being incubated for 325 days. The main microbial groups responsible for the reductive dechlorination of 2,4,6-TCP might be the organohalide respiring Dehalobacter and Dehalococcoides. The subsequent reductive dechlorination of 4-CP to phenol was likely driven by Dehalococcoides. The cooperation between the organohalide respiring bacteria, Syntrophorhabdus and methanogens (e.g. Methanosaeta and Methanofolis) was responsible for the complete degradation of 2,4,6-TCP.

Key words: chlorophenol, anaerobic biodegradation, enrichment cultivation, reductive dechlorination