Mao Guannan, Song Yuhao, Bartlam Mark, Wang Yingying
Key Laboratory of Pollution Processes and Environmental Criteria (Ministry of Education), Tianjin Key Laboratory of Environmental Remediation and Pollution Control, College of Environmental Science and Engineering, Nankai University, Tianjin, China.
State Key Laboratory of Medicinal Chemical Biology, Nankai University, Tianjin, China.
Front Microbiol. 2018 May 3;9:879. doi: 10.3389/fmicb.2018.00879. eCollection 2018.
Residual chlorine is often required to remain present in public drinking water supplies during distribution to ensure water quality. It is essential to understand how bacteria respond to long-term chlorine exposure, especially with the presence of assimilable organic carbon (AOC). This study aimed to investigate the effects of chlorination on in low AOC medium by both conventional plating and culture-independent methods including flow cytometry (FCM) and quantitative PCR (qPCR). In a simulated chlorinated system using a bioreactor, membrane damage and DNA damage were measured by FCM fluorescence fingerprint. The results indicated membrane permeability occurred prior to DNA damage in response to chlorination. A regrowth of was observed when the free chlorine concentration was below 0.3 mg/L. The bacterial response to long-term exposure to a constant low level of free chlorine (0.3 mg/L) was subsequently studied in detail. Both FCM and qPCR data showed a substantial reduction during initial exposure (0-16 h), followed by a plateau where the cell concentration remained stable (16-76 h), until finally all bacteria were inactivated with subsequent continuous chlorine exposure (76-124 h). The results showed three-stage inactivation kinetics for at a low chlorine level with extended exposure time: an initial fast inactivation stage, a relatively stable middle stage, and a final stage with a slower rate than the initial stage. A series of antibiotic resistance tests suggested long-term exposure to low chlorine level led to the selection of antibiotic-resistant . The combined results suggest that depletion of residual chlorine in low AOC medium systems could reactivate , leading to a possible threat to drinking water safety.
在公共饮用水供应的分配过程中,通常需要残留氯来确保水质。了解细菌如何应对长期氯暴露至关重要,尤其是在存在可同化有机碳(AOC)的情况下。本研究旨在通过传统平板培养法以及包括流式细胞术(FCM)和定量聚合酶链反应(qPCR)在内的非培养方法,研究氯化作用对低AOC培养基中细菌的影响。在使用生物反应器的模拟氯化系统中,通过FCM荧光指纹图谱测量膜损伤和DNA损伤。结果表明,响应氯化作用时,膜通透性在DNA损伤之前发生。当游离氯浓度低于0.3mg/L时,观察到细菌的再生长。随后详细研究了细菌对长期暴露于恒定低水平游离氯(0.3mg/L)的反应。FCM和qPCR数据均显示,在初始暴露阶段(0 - 16小时)细菌数量大幅减少,随后进入平台期,细胞浓度保持稳定(16 - 76小时),直到最终随着后续持续氯暴露所有细菌被灭活(76 - 124小时)。结果显示,在低氯水平且延长暴露时间的情况下,细菌呈现三阶段失活动力学:初始快速失活阶段、相对稳定的中间阶段以及最终失活速率比初始阶段慢的阶段。一系列抗生素抗性测试表明,长期暴露于低氯水平会导致抗生素抗性细菌的选择。综合结果表明,低AOC培养基系统中残留氯的消耗可能会使细菌重新激活,从而对饮用水安全构成潜在威胁。