The abatement of 9 polychloro-1,3-butadienes (CBDs) in aqueous solution by ozone, UV–C(254 nm) photolysis, and the corresponding advanced oxidation processes (AOPs) (i.e., O 3 /H 2 O 2 and UV/H 2 O 2 ) was investigated. The following parameters were determined for 9 CBDs: second-order rate constants for the reactions of CBDs with ozone ( k O 3 ) (<0.1–7.9 × 10 3 M –1 s –1 ) or with hydroxyl radicals ( k • OH ) (0.9 × 10 9 – 6.5 × 10 9 M –1 s –1 ), photon fluence-based rate constants ( k ′) (210–2730 m 2 einstein –1 ), and quantum yields (Φ) (0.03–0.95 mol einstein –1 ). During ozonation of CBDs in a natural groundwater, appreciable abatements (>50% at specific ozone doses of 0.5 gO 3 /gDOC to ∼100% at ≥1.0 gO 3 /gDOC) were achieved for tetra-CBDs followed by ( Z )-1,1,2,3,4-penta-CBD and hexa-CBD. This is consistent with the magnitude of the determined k O 3 and k • OH . The formation of bromate, a potentially carcinogenic ozonation byproduct, could be significantly reduced by addition of H 2 O 2 . For a typical UV disinfection dose (400 J/m 2 ), various extents of phototransformations (10–90%) could be achieved. However, the efficient formation of photoisomers from CBDs with E / Z configuration must be taken into account because of their potential residual toxicity. Under UV–C(254 nm) photolysis conditions, no significant effect of H 2 O 2 addition on CBDs abatement was observed due to an efficient direct phototransformation of CBDs.
No takes yet. Share an insight, caveat, or question.
Lee et al. (2016) studied this question.
Synapse has enriched 5 closely related papers on similar clinical questions. Consider them for comparative context: