Abusallout Ibrahim, Rahman Shamimur, Hua Guanghui
Department of Civil and Environmental Engineering, South Dakota State University, Brookings, SD, 57007, USA.
Department of Civil and Environmental Engineering, South Dakota State University, Brookings, SD, 57007, USA.
Chemosphere. 2017 Nov;187:11-18. doi: 10.1016/j.chemosphere.2017.07.149. Epub 2017 Jul 29.
Disinfection byproduct (DBP) concentrations in drinking water distribution systems and indoor water uses depend on competitive formation and degradation reactions. This study investigated the dehalogenation kinetics of total organic chlorine (TOCl), bromine (TOBr) and iodine (TOI) produced by fulvic acid under different pH and temperature conditions, and total organic halogen (TOX) variations in a treated drinking water under simulated distribution system and heating scenarios. TOX dehalogenation rates were generally in the order of TOI ≅ TOCl(NHCl) > TOBr > TOCl(Cl). The half-lives of different groups of TOX compounds formed by fulvic acid varied between 27 and 139 days during incubation at 20 °C and 0.98-2.17 days during heating at 55 °C. Base-catalyzed reactions played a major role in TOX degradation as evidenced by enhanced dehalogenation under high pH conditions. The results of heating of a treated water in the presence of residuals showed that TOX concentrations of chlorinated samples increased rapidly when chlorine residuals were present and then gradually decreased after chlorine residuals were exhausted. The final TOX concentrations of chlorinated samples after heating showed moderate decreases with increasing ambient water ages. Chloraminated samples with different ambient water ages exhibited similar final TOX concentrations during simulated distribution system and heating experiments. This study reinforces the importance of understanding DBP variations in indoor water uses as wells as in distribution systems to provide more accurate DBP information for exposure assessment and regulatory determination.
饮用水分配系统和室内用水中消毒副产物(DBP)的浓度取决于竞争性的生成和降解反应。本研究调查了富里酸在不同pH和温度条件下产生的总有机氯(TOCl)、溴(TOBr)和碘(TOI)的脱卤动力学,以及模拟分配系统和加热场景下处理后饮用水中总有机卤素(TOX)的变化。TOX的脱卤速率一般为TOI≅TOCl(NHCl)>TOBr>TOCl(Cl)。富里酸形成的不同组TOX化合物在20℃孵育期间的半衰期在27至139天之间,在55℃加热期间为0.98 - 2.17天。高pH条件下脱卤增强表明碱催化反应在TOX降解中起主要作用。处理后水在有残余物存在时加热的结果表明,有氯残余物时氯化样品的TOX浓度迅速增加,氯残余物耗尽后逐渐降低。加热后氯化样品的最终TOX浓度随着环境水龄增加呈适度下降。在模拟分配系统和加热实验中,不同环境水龄的氯胺化样品表现出相似的最终TOX浓度。本研究强化了了解室内用水以及分配系统中DBP变化对于为暴露评估和监管判定提供更准确DBP信息的重要性。