Department of Civil Engineering, University of Toronto, 35 St. George Street, Toronto, Ontario, Canada M5S 1A4.
Department of Civil Engineering, University of Toronto, 35 St. George Street, Toronto, Ontario, Canada M5S 1A4.
Water Res. 2015 Mar 1;70:118-29. doi: 10.1016/j.watres.2014.11.039. Epub 2014 Dec 4.
Natural organic matter (NOM) in drinking water can react with disinfectants to form disinfection by-products (DBPs). Halogenated furanones are a group of emerging DBPs that can account for 20-60% of the total mutagenicity observed in drinking water. This study examined the impacts of bench-scale coagulation and subsequent chlorination on DBP formation as well as genotoxicity using three source waters located in Ontario, Canada. Two halogenated furanones 3-chloro-4-(dichloromethyl)-2(5H)-furanone (MX) and mucochloric acid (MCA) were analyzed; along with trihalomethanes (THMs), haloacetic acids (HAAs), and absorbable organic halides (AOX). NOM was quantified using liquid chromatography-organic carbon detection (LC-OCD). Measured MX and MCA formation was 6.9-15.3 ng/L and 43.2-315 ng/L following optimized coagulation and subsequent chlorination of the three waters tested. DBP formation and speciation were evaluated as a function of the specific NOM fractions present in the source waters. Humics, building blocks, and biopolymers were highly correlated with DBP formation. Correlations between DBPs were also investigated and a potential relationship between MCA and/or MX vs. HAAs was observed. MX was the only measured DBP that contributed to genotoxicity, representing less than 0.001% of AOX by mass but responsible for 40-67% of the genotoxic response in chlorinated Ottawa River water samples. Genotoxic potential decreased with alum dosages, signifying that coagulation was effective at removing genotoxic DBP precursors.
饮用水中的天然有机物 (NOM) 可与消毒剂反应生成消毒副产物 (DBP)。卤代呋喃酮是一组新兴的 DBP,可占饮用水中总致突变性的 20-60%。本研究使用位于加拿大安大略省的三种水源,考察了实验室规模的混凝和随后氯化对 DBP 形成和遗传毒性的影响。分析了两种卤代呋喃酮 3-氯-4-(二氯甲基)-2(5H)-呋喃酮 (MX) 和粘氯酸 (MCA) ;以及三卤甲烷 (THMs)、卤乙酸 (HAAs) 和可吸收有机卤化物 (AOX)。使用液相色谱-有机碳检测 (LC-OCD) 定量 NOM。在优化混凝和随后氯化三种测试水源后,测量到 MX 和 MCA 的形成分别为 6.9-15.3 ng/L 和 43.2-315 ng/L。根据水源中存在的特定 NOM 分数评估了 DBP 的形成和形态。腐殖质、建筑块和生物聚合物与 DBP 的形成高度相关。还研究了 DBPs 之间的相关性,并观察到 MCA 和/或 MX 与 HAAs 之间存在潜在关系。MX 是唯一被测量到的与遗传毒性相关的 DBP,其质量仅占 AOX 的 0.001%以下,但对氯化渥太华河水样品中的遗传毒性反应贡献了 40-67%。遗传毒性潜力随铝盐剂量的降低而降低,这表明混凝对去除遗传毒性 DBP 前体有效。