This investigation reports the kinetics of haloacetaldehydes’ reactions with radicals in water, implying potential for advanced oxidation processes in water treatment.
Halogenated acetaldehydes (HALs) are abundant disinfection byproducts (DBPs) in drinking water with some congeners being more cyto/genotoxic than EPA-regulated DBPs. Advanced oxidation/reduction processes (AOPs/ARPs) are an attractive option for eliminating HALs from water sources; however, kinetic data for their reactions with AOP hydroxyl radicals (HO•) and ARP hydrated electrons (eaq–)/hydrogen atoms (H•), are limited. Using electron pulse radiolysis bimolecular rate constants at pH 7 and 24–25 °C for five important HALs (chloro-, dichloro-, trichloro-, bromo-, and dibromoacetaldehyde) were determined. HO• radicals react by hydrogen atom abstraction from the gem-diol (hydrate) form with kHO• values of (1.36 ± 0.07) × 109, (1.77 ± 0.01) × 109, (3.07 ± 0.14) × 109, (1.11 ± 0.01) × 109 and (3.01 ± 0.21) × 109 M–1 s–1, respectively. Corresponding HAL keaq- rate constants monitored at 720 nm were (2.45 ± 0.33) × 109, (5.81 ± 0.45) × 109, (1.50 ± 0.08) × 1010, (9.05 ± 0.53) × 109 and (1.56 ± 0.12) × 1010 M–1 s–1. These structure-dependent kinetics were consistent with electron reductive dehalogenation. Chlorinated HAL kH• values measured by electron paramagnetic resonance methods were 100× slower than for eaq–. These data successfully modeled the steady-state 60Co irradiation of an O2-saturated chloroacetaldehyde solution, validating their use for computer optimization of HO•-driven AOPs to mitigate HALs at larger scale.
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Medina-Garcia et al. (2026) studied this question.
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