Department of Environmental and Occupational Health, School of Public Health, Texas A&M University, College Station, TX 77843, USA; Department of Environmental Science, Baylor University, Waco, TX 76798, USA.
Department of Environmental Science, Baylor University, Waco, TX 76798, USA.
Environ Int. 2020 May;138:105641. doi: 10.1016/j.envint.2020.105641. Epub 2020 Mar 20.
Disinfection is an essential process of drinking water treatment to eliminate harmful pathogens, but it generates potentially toxic disinfection byproducts (DBPs). Ferrate (FeO, Fe(VI)) was used to pre-oxidize natural organic matter (NOM, the precursor of DBPs) in source water to control DBP formation in subsequent chlorine or chloramine disinfection. Currently, it is unclear how Fe(VI) changes the structure of NOM, and no information details the effect of Fe(VI) pretreatment on the aromatic DBPs or the speciation of overall DBPs generated in subsequent disinfection of drinking water. In the present paper, Fe(VI) was applied to pretreat simulated source water samples at a Fe(VI) to dissolved organic carbon mole ratio of 1:1 at pH 8.0. C nuclear magnetic resonance spectroscopy was newly employed to characterize NOM in simulated source waters with and without Fe(VI) treatment, and it was demonstrated that Fe(VI) converted unsaturated aromatic C functional groups in NOM to saturated aliphatic ones. High-resolution mass spectrometry (HRMS) and high performance liquid chromatography/triple quadrupole MS were applied to analyze the DBPs generated in chlorination and chloramination of the source waters with and without Fe(VI) pretreatment. It was confirmed that Fe(VI) pretreatment followed by chlorination (or chloramination), generated DBPs containing less unsaturated, halogenated, and aromatic moieties than chlorination (or chloramination) without pretreatment by Fe(VI). Finally, the cytotoxicity of disinfected drinking water samples were assessed with the human epithelial colorectal adenocarcinoma Caco-2 cell line (a model of the intestinal barrier for ingested toxicants), and the results show that Fe(VI) pretreatment detoxified the chlorinated and chloraminated drinking waters.
消毒是饮用水处理的一个重要环节,用于消除有害病原体,但它会产生潜在的有毒消毒副产物(DBPs)。高铁酸盐(FeO,Fe(VI))被用于预氧化原水中的天然有机物(NOM,DBPs 的前体),以控制后续氯或氯胺消毒过程中 DBP 的形成。目前,尚不清楚 Fe(VI)如何改变 NOM 的结构,也没有信息详细说明 Fe(VI)预处理对芳香族 DBP 或后续饮用水消毒过程中生成的总 DBP 形态的影响。在本研究中,将 Fe(VI)以 Fe(VI)与溶解有机碳摩尔比为 1:1 在 pH 值为 8.0 的条件下应用于模拟原水样品的预处理。¹³C 核磁共振波谱法(¹³C-NMR)被新用于表征经 Fe(VI)处理和未经 Fe(VI)处理的模拟原水中的 NOM,结果表明 Fe(VI)将 NOM 中的不饱和芳香族 C 官能团转化为饱和脂肪族 C 官能团。高分辨率质谱(HRMS)和高效液相色谱/三重四极杆质谱(HPLC/MS/MS)被用于分析经 Fe(VI)预处理和未经 Fe(VI)预处理的原水在氯化和氯胺化过程中生成的 DBP。结果证实,与未经 Fe(VI)预处理的氯化(或氯胺化)相比,Fe(VI)预处理后再进行氯化(或氯胺化)生成的 DBP 中含有较少的不饱和、卤化和芳香族部分。最后,用人结肠癌细胞系(一种用于摄入毒物的肠道屏障模型)评估消毒后饮用水样品的细胞毒性,结果表明 Fe(VI)预处理可使氯化和氯胺化饮用水解毒。