Centre for Water Science, Cranfield University, Bedfordshire MK43 0AL, UK.
Environ Technol. 2011 Jan;32(1-2):1-25. doi: 10.1080/09593330.2010.495138.
Formation of harmful disinfection by-products (DBPs), of which trihalomethanes (THMs) and haloacetic acids (HAAs) are the major groups, can be controlled by removal of natural organic matter (NOM) before disinfection. In the literature, removal of precursors is variable, even with the same treatment. The treatment of DBP precursors and NOM was examined with the intention of outlining precursor removal strategies for various water types. Freundlich adsorption parameters and hydroxyl rate constants were collated from the literature to link treatability by activated carbon and advanced oxidation processes (AOPs), respectively, to physico-chemical properties. Whereas hydroxyl rate constants did not correlate meaningfully with any property, a moderate correlation was found between Freundlich parameters and log K(ow), indicating activated carbon will preferentially adsorb hydrophobic NOM. Humic components of NOM are effectively removed by coagulation, and, where they are the principal precursor source, coagulation may be sufficient to control DBPs. Where humic species remaining post-coagulation retain significant DBP formation potential (DBPFP), activated carbon is deemed a suitable process selection. Anion exchange is an effective treatment for transphilic species, known for high carboxylic acid functionality, and consequently is recommended for carboxylic acid precursors. Amino acids have been linked to HAA formation and are important constituents of algal organic matter. Amino acids are predicted to be effectively removed by biotreatment and nanofiltration. Carbohydrates have been found to reach 50% of NOM in river waters. If the carbohydrates were to pose a barrier to successful DBP control, additional treatment stages such as nanofiltration are likely to be required to reduce their occurrence.
有害消毒副产物(DBP)的形成,其中三卤甲烷(THMs)和卤乙酸(HAAs)是主要的两个群组,可以通过在消毒前去除天然有机物(NOM)来控制。在文献中,即使使用相同的处理方法,去除前体物的效果也各不相同。本研究旨在概述各种水源的前体物去除策略,考察了 DBP 前体物和 NOM 的去除方法。分别从文献中整理出了活性炭和高级氧化工艺(AOP)的 Freundlich 吸附参数和羟基速率常数,以将可处理性与物理化学性质联系起来。尽管羟基速率常数与任何性质都没有明显的相关性,但在 Freundlich 参数和 log K(ow)之间发现了中等相关性,这表明活性炭将优先吸附疏水性 NOM。NOM 的腐殖质成分通过混凝有效地去除,如果腐殖质是主要的前体物来源,那么混凝可能足以控制 DBPs。如果混凝后残留的腐殖质仍然具有显著的 DBP 形成潜力(DBPFP),则认为活性炭是一种合适的工艺选择。阴离子交换是一种有效的处理方法,适用于亲脂性物质,这些物质具有高羧酸官能团,因此推荐用于羧酸前体物。氨基酸与 HAA 的形成有关,是藻类有机物的重要组成部分。据预测,氨基酸可以通过生物处理和纳滤有效地去除。在河水中,碳水化合物已经占到 NOM 的 50%。如果碳水化合物对成功控制 DBP 构成障碍,可能需要额外的处理阶段,如纳滤,以减少其含量。