Curtin Water Quality Research Centre, Resources and Chemistry Precinct, Department of Chemistry, Curtin University, Kent Street, Bentley, GPO Box U1987, Perth, WA 6845, Australia.
Water Res. 2013 Feb 1;47(2):535-46. doi: 10.1016/j.watres.2012.10.014. Epub 2012 Oct 23.
N-Nitrosamines are a class of disinfection by-products (DBPs) that have been reported to be more toxic than the most commonly detected and regulated DBPs. Only a few studies investigating the formation of N-nitrosamines from disinfection of natural waters have been reported, and little is known about the role of natural organic matter (NOM) and the effects of its nature and reactivity on the formation of N-nitrosamines. This study investigated the influence of the molecular weight (MW) characteristics of NOM on the formation of eight species of N-nitrosamines from chlorination and chloramination, and is the first to report on the formation of eight N-nitrosamines from chlorination and chloramination of MW fractions of NOM. Isolated NOM from three different source waters in Western Australia was fractionated into several apparent MW (AMW) fractions using preparative-scale high performance size exclusion chromatography. These AMW fractions of NOM were then treated with chlorine or chloramine, and analysed for eight species of N-nitrosamines. Among these N-nitrosamines, N-nitrosodimethylamine (NDMA) was the most frequently detected. All AMW fractions of NOM produced N-nitrosamines upon chlorination and chloramination. Regardless of AMW characteristics, chloramination demonstrated a higher potential to form N-nitrosamines than chlorination, and a higher frequency of detection of the N-nitrosamines species was also observed in chloramination. The results showed that inorganic nitrogen may play an important role in the formation of N-nitrosamines, while organic nitrogen is not necessarily a good indicator for their formation. Since chlorination has less potential to form N-nitrosamines, chloramination in pre-chlorination mode was recommended to minimise the formation of N-nitrosamines. There was no clear trend in the formation of N-nitrosamines from chlorination of AMW fractions of NOM. However, during chloramination, NOM fractions with AMW <2.5 kDa were found to produce higher concentrations of NDMA and total N-nitrosamines. The precursor materials of N-nitrosamines appeared to be more abundant in the low to medium MW fractions of NOM, which correspond to the fractions that are most difficult to remove using conventional drinking water treatment processes. Alternative or advanced treatment processes that target the removal of low to medium MW NOM including activated carbon adsorption, biofiltration, reverse osmosis, and nanofiltration, can be employed to minimise the formation of N-nitrosamines.
N-亚硝胺是一类消毒副产物(DBPs),其毒性被报道比最常见的检测和监管的 DBPs 更高。只有少数研究报告了天然水消毒过程中亚硝胺的形成,而对天然有机物(NOM)的作用及其性质和反应性对亚硝胺形成的影响知之甚少。本研究调查了 NOM 分子量(MW)特征对氯和氯胺消毒形成八种亚硝胺的影响,并且是首次报道 MW 分数的 NOM 氯和氯胺消毒形成八种 N-亚硝胺。从西澳大利亚的三种不同水源中分离出的 NOM 采用制备规模的高性能尺寸排阻色谱法分离成几个表观 MW(AMW)级分。然后,用氯或氯胺处理这些 NOM 的 AMW 级分,并分析八种 N-亚硝胺。在这些 N-亚硝胺中,N-亚硝基二甲胺(NDMA)是最常检测到的。所有 NOM 的 AMW 级分在氯化和氯胺化后都产生了 N-亚硝胺。无论 AMW 特征如何,氯胺化比氯化更有形成 N-亚硝胺的潜力,并且在氯胺化中也观察到 N-亚硝胺种类的更高检测频率。结果表明,无机氮可能在 N-亚硝胺的形成中起重要作用,而有机氮不一定是其形成的良好指标。由于氯化形成 N-亚硝胺的潜力较小,因此建议在预氯化模式下使用氯胺化以最大程度地减少 N-亚硝胺的形成。从 NOM 的 AMW 级分的氯化形成 N-亚硝胺没有明显的趋势。然而,在氯胺化过程中,发现 AMW<2.5 kDa 的 NOM 级分产生更高浓度的 NDMA 和总 N-亚硝胺。N-亚硝胺的前体物质似乎在 NOM 的低至中等 MW 级分中更为丰富,这与使用常规饮用水处理工艺最难去除的级分相对应。可以采用替代或先进的处理工艺,针对去除低至中等 MW NOM,包括活性炭吸附、生物过滤、反渗透和纳滤,以最大程度地减少 N-亚硝胺的形成。