Department of Biomedical Sciences and Veterinary Public Health, Swedish University of Agricultural Sciences, Box 7028, SE-750 07, Uppsala, Sweden.
Department of Thematic Studies-Environmental Change, Linköping University, SE-581 83, Linköping, Sweden.
Water Res. 2019 May 15;155:182-192. doi: 10.1016/j.watres.2019.02.052. Epub 2019 Feb 28.
Disinfection of drinking water using chlorine can lead to the formation of genotoxic by-products when chlorine reacts with natural organic matter (NOM). A vast number of such disinfection by-products (DBPs) have been identified, making it almost impossible to routinely monitor all DBPs with chemical analysis. In this study, a bioanalytical approach was used, measuring oxidative stress (Nrf2 activity), genotoxicity (micronucleus test), and aryl hydrocarbon receptor (AhR) activation to evaluate an innovative water treatment process, including suspended ion exchange, ozonation, in-line coagulation, ceramic microfiltration, and granular activated carbon. Chlorination was performed in laboratory scale after each step in the treatment process in order to investigate the effect of each treatment process to the formation of DBPs. Suspended ion exchange had a high capacity to remove dissolved organic carbon (DOC) and to decrease UV absorbance and Nrf2 activity in non-chlorinated water. High-dose chlorination (10 mg Cl L) of raw water caused a drastic induction of Nrf2 activity, which was decreased by 70% in water chlorinated after suspended ion exchange. Further reduction of Nrf2 activity following chlorination was achieved by ozonation and the concomitant treatment steps. The ozonation treatment resulted in decreased Nrf2 activity in spite of unchanged DOC levels. However, a strong correlation was found between UV absorbing compounds and Nrf2 activity, demonstrating that Nrf2 inducing DBPs were formed from pre-cursors of a specific NOM fraction, constituted of mainly aromatic compounds. Moreover, high-dose chlorination of raw water induced genotoxicity. In similarity to the DOC levels, UV absorbance and Nrf2 activity, the disinfection-induced genotoxicity was also reduced by each treatment step of the innovative water treatment technique. AhR activity was observed in the water produced by the conventional process and in the raw water, but the activity was clearly decreased by the ozonation step in the innovative water treatment process.
饮用水的消毒过程中,当氯与天然有机物(NOM)发生反应时,可能会形成遗传毒性的副产物。已经鉴定出了大量此类消毒副产物(DBP),这使得通过化学分析来常规监测所有 DBP 几乎成为不可能。在这项研究中,采用了一种生物分析方法,通过测量氧化应激(Nrf2 活性)、遗传毒性(微核试验)和芳烃受体(AhR)激活来评估一种创新的水处理工艺,包括悬浮离子交换、臭氧氧化、在线混凝、陶瓷微滤和颗粒活性炭。在处理过程的每一步之后,都在实验室规模上进行氯化,以研究每个处理过程对 DBP 形成的影响。悬浮离子交换具有高容量去除溶解有机碳(DOC)和降低未氯化水中的紫外吸光度和 Nrf2 活性的能力。高剂量氯化(10mgCl/L)原水导致 Nrf2 活性急剧诱导,而经过悬浮离子交换后氯化的水则降低了 70%。臭氧氧化和伴随的处理步骤进一步降低了氯化后的 Nrf2 活性。尽管 DOC 水平保持不变,但臭氧氧化处理导致 Nrf2 活性降低。然而,在紫外吸收化合物和 Nrf2 活性之间发现了很强的相关性,表明 Nrf2 诱导的 DBP 是由特定 NOM 部分的前体形成的,该部分主要由芳香族化合物组成。此外,高剂量氯化原水诱导遗传毒性。与 DOC 水平、紫外吸光度和 Nrf2 活性相似,创新水处理技术的每个处理步骤都降低了消毒诱导的遗传毒性。在常规工艺生产的水中和原水中都观察到了 AhR 活性,但在创新水处理工艺的臭氧氧化步骤中,该活性明显降低。