在氯转换过程中,配水和供水系统内的微生物和物理化学水质变化

Helen Y. Buse, Jatin H. Mistry
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引用次数: 0

摘要

在氯化饮用水系统 (CDWS) 中控制硝化的一种策略是暂时将氯胺二次消毒转换为游离氯,也称为游离氯转换 (FCC)。然而,游离氯转换的长期和有益影响尚不明确,尤其是在机会性病原体的发生方面。在这项研究中,对实施了自由氯转换的 CDWS 的整个过程中微生物和理化参数的影响进行了监测。在催化还原反应之前、期间和之后的 4-6 周内,每周在八个地点采集水样:四个配水系统和四个居民点。在所有地点,催化还原反应前后的一氯胺残留量(平均值± 标准偏差)分别为 1.8±0.9 和 1.6±1.0 百万分之一(ppm)。游离氯含量平均为 2.3±0.9 ppm。在三个时间段内,每个地点的浑浊度和硬度没有明显差异,但 pH 值、温度和正磷酸盐水平在不同地点和采样时间段内存在一些差异。与之前和之后的时间段相比,所有地点在催化裂化时间段的异养细胞计数水平都较低。一个居民点的所有样本均对铜绿微囊藻培养呈阳性,铜绿微囊藻在催化还原反应前含量较高,在催化还原反应期间含量下降,在催化还原反应后含量稳步上升。此外,在催化裂化时间前一周,对来自两个高架储罐(ET-1 和 ET-2)的沉积物样本进行了分析,与 ET-2 相比,ET-1 的可培养异养菌和分子检测细菌总数、军团菌属、非结核分枝杆菌 (NTM) 以及可培养铜绿假单胞菌和总大肠菌群的含量更高。对 14 个铜绿假单胞菌和总大肠菌群分离物进行了全基因组测序,观察到基因差异取决于采样地点和时间点。总之,观察到的化学和微生物参数差异有助于更好地了解实施催化还原剂的相关影响,以确定其有效性以及对水质的潜在风险/回报。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Microbial and physicochemical water quality changes within distribution and premise plumbing systems during a chlorine conversion
A strategy for nitrification control within chloraminated drinking water systems (CDWSs) is to temporarily switch from chloramine secondary disinfection to free chlorine, also known as a free chlorine conversion (FCC). However, the long-term and beneficial effects of FCCs are unclear, especially regarding opportunistic pathogen occurrence. In this study, the impacts to microbial and physicochemical parameters were monitored throughout a CDWS implementing a FCC. Water samples were collected weekly for 4–6 weeks before, during, and after a FCC at eight locations: four distribution system and four residential sites. Monochloramine residual (mean±standard deviation) before and after the FCC averaged 1.8±0.9 and 1.6±1.0 parts per million (ppm) for all sites, respectively. Free chlorine levels averaged 2.3±0.9 ppm. There were no significant differences in turbidity and hardness at each location during the three time periods, but some were noted for pH, temperature, and orthophosphate levels across various sites and sampling periods. For all locations, heterotrophic plate count levels were lower during the FCC compared to the periods before and after. All samples from one residence were culture positive for P. aeruginosa which exhibited high levels before the FCC, decreasing levels during, and steadily increasing levels after. Additionally, one week prior to the FCC, sediment samples from two elevated storage tanks, ET-1 and ET-2, were analyzed with ET-1 displaying higher levels of culturable heterotrophic bacteria and molecularly detected total bacteria, Legionella spp., and nontuberculous mycobacteria (NTM), as well as presence of culturable P. aeruginosa and total coliforms compared to ET-2. Fourteen P. aeruginosa and total coliform isolates were whole genome sequenced with genetic differences observed depending on the sampling location and timepoint. Collectively, the observed differences in chemical and microbial parameters advocates for a better understanding of the effects associated with implementing FCCs to determine both their effectiveness and potential risks/rewards to water quality.
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