Yoshikawa Miho, Zhang Ming, Toyota Koki
Geological Survey of Japan, National Institute of Advanced Industrial Science and Technology (AIST), 1-1-1, Higashi, Tsukuba, Ibaraki 305-8567 Japan.
Graduate School of Bio-Applications and Systems Engineering, Tokyo University of Agriculture and Technology, 2-24-16, Nakacho, Koganei, Tokyo Japan.
Water Air Soil Pollut. 2017;228(1):25. doi: 10.1007/s11270-016-3216-1. Epub 2016 Dec 14.
Complete bioremediation of soils containing multiple volatile organic compounds (VOCs) remains a challenge. To explore the possibility of complete bioremediation through integrated anaerobic-aerobic biodegradation, laboratory feasibility tests followed by alternate anaerobic-aerobic and aerobic-anaerobic biodegradation tests were performed. Chlorinated ethylenes, including tetrachloroethylene (PCE), trichloroethylene (TCE), -dichloroethylene (-DCE), and vinyl chloride (VC), and dichloromethane (DCM) were used for anaerobic biodegradation, whereas benzene, toluene, and DCM were used for aerobic biodegradation tests. Microbial communities involved in the biodegradation tests were analyzed to characterize the major bacteria that may contribute to biodegradation. The results demonstrated that integrated anaerobic-aerobic biodegradation was capable of completely degrading the seven VOCs with initial concentration of each VOC less than 30 mg/L. Benzene and toluene were degraded within 8 days, and DCM was degraded within 20 to 27 days under aerobic conditions when initial oxygen concentrations in the headspaces of test bottles were set to 5.3% and 21.0%. sp., generally considered sensitive to oxygen, survived aerobic conditions for 28 days and was activated during the subsequent anaerobic biodegradation. However, degradation of -DCE was suppressed after oxygen exposure for more than 201 days, suggesting the loss of viability of sp., as they are the only known anaerobic bacteria that can completely biodegrade chlorinated ethylenes to ethylene. Anaerobic degradation of DCM following previous aerobic degradation was complete, and yet-unknown microbes may be involved in the process. The findings may provide a scientific and practical basis for the complete bioremediation of multiple contaminants in situ and a subject for further exploration.
对含有多种挥发性有机化合物(VOCs)的土壤进行完全生物修复仍然是一项挑战。为了探索通过厌氧-好氧联合生物降解实现完全生物修复的可能性,先进行了实验室可行性测试,随后进行了交替厌氧-好氧和好氧-厌氧生物降解测试。使用包括四氯乙烯(PCE)、三氯乙烯(TCE)、二氯乙烯(-DCE)和氯乙烯(VC)在内的氯化乙烯以及二氯甲烷(DCM)进行厌氧生物降解,而使用苯、甲苯和DCM进行好氧生物降解测试。对参与生物降解测试的微生物群落进行了分析,以确定可能有助于生物降解的主要细菌。结果表明,厌氧-好氧联合生物降解能够完全降解初始浓度均低于30mg/L的七种VOCs。当测试瓶顶部空间的初始氧气浓度设定为5.3%和21.0%时,苯和甲苯在8天内降解,DCM在好氧条件下20至27天内降解。通常认为对氧气敏感的sp. 在好氧条件下存活了28天,并在随后的厌氧生物降解过程中被激活。然而,-DCE在暴露于氧气超过201天后降解受到抑制,这表明sp. 的活性丧失,因为它们是唯一已知的能够将氯化乙烯完全生物降解为乙烯的厌氧细菌。先前好氧降解后的DCM厌氧降解是完全的,可能有未知微生物参与了这一过程。这些发现可能为原位完全生物修复多种污染物提供科学和实践依据,并为进一步探索提供课题。