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二氧化氯对不同微生物的灭活特性及其对群落结构特征的影响
引用本文:徐闯,巫寅虎,胡洪营,徐傲,倪欣业. 二氧化氯对不同微生物的灭活特性及其对群落结构特征的影响[J]. 环境工程, 2021, 39(10): 57-63. DOI: 10.13205/j.hjgc.202110008
作者姓名:徐闯  巫寅虎  胡洪营  徐傲  倪欣业
作者单位:清华大学环境学院环境模拟与污染控制国家重点联合实验室国家环境保护环境微生物利用与安全控制重点实验室,北京100084;清华大学环境学院环境模拟与污染控制国家重点联合实验室国家环境保护环境微生物利用与安全控制重点实验室,北京100084;清华-伯克利深圳学院深圳环境科学与新能源技术工程实验室,广东深圳518055;清华苏州环境创新研究院,江苏苏州215163
基金项目:国家自然科学基金(52000114);国家自然科学基金重点项目(51738005)。
摘    要:二氧化氯是一种性能优良、应用广泛的消毒剂,可通过破坏细胞或病毒的组成结构、阻碍细胞代谢等方式实现微生物灭活.在自配水条件下,以二氧化氯投加量×消毒时间计算,二氧化氯剂量在15 (mg·min)/L时,可实现对常见病毒(包括肠病毒71型、大肠杆菌噬菌体MS2等)31og以上灭活率,在60 (mg·min)/L时,可实现对...

关 键 词:二氧化氯  消毒  影响因素  群落结构  再生长
收稿时间:2021-01-16

CHLORINE DIOXIDE'S INACTIVATION ON DIFFERENT MICROORGANISMS AND ITS INFLUENCE ON THE CHARACTERISTICS OF MICROBIAL COMMUNITY STRUCTURE
XU Chuang,WU Yin-hu,HU Hong-ying,XU Ao,NI Xin-ye. CHLORINE DIOXIDE'S INACTIVATION ON DIFFERENT MICROORGANISMS AND ITS INFLUENCE ON THE CHARACTERISTICS OF MICROBIAL COMMUNITY STRUCTURE[J]. Environmental Engineering, 2021, 39(10): 57-63. DOI: 10.13205/j.hjgc.202110008
Authors:XU Chuang  WU Yin-hu  HU Hong-ying  XU Ao  NI Xin-ye
Affiliation:1. State Key Joint Laboratory of Environmental Simulation and Pollution Control, State Key Laboratory of Environmental Microbial Utilization and Safety Control, School of Environment, Tsinghua University, Beijing 100084, China;2. Laboratory of Environmental Science and New Energy Technology Engineering, Tsinghua-Berkeley Shenzhen College, Shenzhen 518055, China;3. Research Institute for Environmental Innovation(Suzhou), Tsinghua, Suzhou 215163, China
Abstract:Chlorine dioxide is a kind of disinfectant with excellent performance and wide application. Chlorine dioxide disinfects microbe by means of damaging the structure of cells and viruses and inhibiting cell metabolism. Calculated by multiplying chlorine dioxide dosage by the contact time, chlorine dioxide was able to inactivate many common viruses (for example, Enterovirus 71, coliphage MS2, etc.) for more than 3log inactivation rate with a dose of 15 (mg·min)/L, and effectively inactivate bacteria (for example, Escherichia coli, Staphylococcus aureus, etc.) for more than 1.5 log with a dose of 60 (mg·min)/L; however, more doses of chlorine dioxide were needed to achieve efficacious disinfection of Cryptosporidium parvum oocysts (for instance, achieving 1.9 log inactivation rate with about 600 (mg·min)/L dose); in wastewater treatment plant (WWTP) influent, only 0.8 log of Escherichia coli and 0.5 log of total coliform inactivation rate were achieved with 30 (mg·min)/L chlorine dioxide dose. The efficiency of chlorine dioxide inactivation was improved as the temperature rise, but the impact of pH for chlorine dioxide inactivation efficiency of different microbe may be different. Usually, organic matter in water samples weakened chlorine dioxide effect for disinfection by consuming chlorine dioxide. However, there were exceptions in natural waters with better inactivation efficiency than that in pure water which may result from the influence of natural organic matter. Research on microbial community structure after chlorine dioxide disinfection was insufficient with only a few studies concerning municipal sewage, reclaimed water and drinking water, etc. In a certain time after chlorine dioxide disinfection, both suspended and attached microbe may regrow, but changes of microbial community structure and secretion characteristics still remained to be studied.
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