Photodegradation of halogenated organic disinfection by-products: Decomposition and reformation.

• The main photodegradation mechanism of 33 different DBPs was dehalogenation. • Photodegradation efficiency followed the order of I-DBP > Br-DBPs > Cl-DBPs. • UV 254 treatment effectively removed halogenated organic DBPs. • The subsequent use of disinfectants (Cl 2 and NH 2 Cl) reformed photodegraded DBPs. In this study, the photodegradation of 33 different DBPs (trihalomethanes, haloacetic acids, haloacetaldehydes, and haloacetonitriles) and TOX with low pressure UV light and the subsequent reformation of DBPs with chlorine and monochloramine were investigated. Results indicated that photodegradation followed the order of TOI > TOBr > TOCl, and treated surface water with low SUVA 254 background did not impact the photodegradation of highly UV susceptible DBPs such as triiodomethane (TIM), diiodobromomethane (DIBM), tribromomethane (TBM). The mass balance results of chloride, bromide and iodide showed that the main photodegradation mechanism of TOBr and TOI was dehalogenation supported by halide releases (i.e., Cl−, Br− and/or I− ion). In addition, the photodegradation removal effect was higher, when brominated DBPs formation was high. Although low pressure UV light effectively removed halogenated organic DBPs, subsequent use of disinfectants (Cl 2 and NH 2 Cl) reformed photodegraded DBPs, and the overall DBPs concentrations were increased, which suggested that the released Br− and I− ions will reform DBPs in distribution systems, with oxidants present or added (e.g., booster chlorination) in distribution systems. This study showed that although UV photodegradation will reduce halogenated organic DBPs in distribution systems, especially more toxic iodinated and brominated DBPs, it will be a more effective technology towards the end of the distribution system or a point of entry solution rather than in distribution system with post-disinfection and residence time. [Display omitted] [ABSTRACT FROM AUTHOR]