Water ApS, Farum Gydevej 64, 3520 Farum, Denmark; Department of Environmental Engineering, Technical University of Denmark, Miljøvej, Building 113, 2800 Kongens Lyngby, Denmark.
Department of Environmental Engineering, Technical University of Denmark, Miljøvej, Building 113, 2800 Kongens Lyngby, Denmark.
Sci Total Environ. 2015 Jul 1;520:96-105. doi: 10.1016/j.scitotenv.2015.03.044. Epub 2015 Mar 22.
Formation of disinfection by-products (DBPs) during experimental UV treatment of pool water has previously been reported with little concurrence between laboratory studies, field studies and research groups. In the current study, changes in concentration of seven out of eleven investigated volatile DBPs were observed in experiments using medium pressure UV treatment, with and without chlorine and after post-UV chlorination. Results showed that post-UV chlorine consumption increased, dose-dependently, with UV treatment dose. A clear absence of trihalomethane formation by UV and UV with chlorine was observed, while small yet statistically significant increases in dichloroacetonitrile and dichloropropanone concentrations were detected. Results indicate that post-UV chlorination clearly induced secondary formation of several DBPs. However, the formation of total trihalomethanes was no greater than what could be replicated by performing the DBP formation assay with higher chlorine concentrations to simulate extended chlorination. Post-UV chlorination of water from a swimming pool that continuously uses UV treatment to control combined chlorine could not induce secondary formation for most DBPs. Concurrence for induction of trihalomethanes was identified between post-UV chlorination treatments and simulated extended chlorination time treatment. Trihalomethanes could not be induced by UV treatment of water from a continuously UV treated pool. This indicates that literature reports of experimentally induced trihalomethane formation by UV may be a result of kinetic increase in formation by UV. However, this does not imply that higher trihalomethane concentrations would occur in pools that apply continuous UV treatment. The bromine fraction of halogens in formed trihalomethanes increased with UV dose. This indicates that UV removes bromine atoms from larger molecules that participate in trihalomethane production during post-UV chlorination. Additionally, no significant effect on DBP formation was observed due to photo-inducible radical forming molecules NO3- (potentially present in high concentrations in pool water) and H2O2 (added as part of commercially employed DBP reducing practices).
在以往的研究中,实验室研究、现场研究和研究小组之间很少同时发现泳池水中紫外线处理过程中消毒副产物(DBP)的形成。在当前的研究中,在使用中压紫外线处理、有氯和无氯以及紫外线后氯化的实验中,观察到 11 种挥发性 DBP 中有 7 种的浓度发生了变化。结果表明,紫外线处理剂量依赖性地增加了紫外线后氯的消耗。紫外线和含氯紫外线处理明显没有形成三卤甲烷,而二氯乙腈和二氯丙酮的浓度略有但具有统计学意义的增加。结果表明,紫外线后氯化明显诱导了几种 DBP 的二次形成。然而,总三卤甲烷的形成并不大于通过使用更高的氯浓度来模拟延长氯化以进行 DBP 形成测定来复制的形成。对连续使用紫外线处理来控制结合氯的游泳池水进行紫外线后氯化,对于大多数 DBP 都不能诱导二次形成。紫外线后氯化处理与模拟延长氯化时间处理之间存在三卤甲烷的诱导一致性。连续紫外线处理的游泳池水中的紫外线处理不能诱导三卤甲烷的形成。这表明,文献中报道的紫外线实验诱导三卤甲烷形成可能是由于紫外线动力学增加形成的结果。然而,这并不意味着在连续使用紫外线处理的游泳池中会出现更高的三卤甲烷浓度。形成的三卤甲烷中卤素的溴部分随着紫外线剂量的增加而增加。这表明紫外线从参与紫外线后氯化过程中三卤甲烷产生的较大分子中去除了溴原子。此外,由于光诱导自由基形成分子 NO3-(可能在游泳池水中高浓度存在)和 H2O2(作为商业采用的 DBP 还原实践的一部分添加),没有观察到对 DBP 形成的显著影响。