The benchmark advanced oxidation
technology (AOT) that uses UV/H2O2 integrated
with hypochlorous species exhibits
great potential in removing micropollutants and enhancing wastewater
treatability for reclamation purposes. Although efforts have been
made to study the reactions of H2O2 with hypochlorous
species, there exist great discrepancies in the order of reaction
kinetics, the rate constants, and the molecule-level mechanisms. This
results in an excessive use of hypochlorous reagents and system underperformance
during treatment processes. Herein, the titled reaction was investigated
systematically through complementary experimental and theoretical
approaches. Stopped-flow spectroscopic measurements revealed a combination
of bi- and trimolecular reaction kinetics. The bimolecular pathway
dominates at low H2O2 concentrations, while
the trimolecular pathway dominates at high H2O2 concentrations. Both reactions were simulated using direct dynamics
trajectories, and the pathways identified in the trajectories were
further validated by high-level quantum chemistry calculations. The
theoretical results not only supported the spectroscopic data but
also elucidated the molecule-level mechanisms and helped to address
the origin of the discrepancies. In addition, the impact of the environmental
matrix was evaluated by using two waters with discrete characteristics,
namely municipal wastewater and ammonium-rich wastewater. Municipal
wastewater had a negligible matrix effect on the reaction kinetics
of H2O2 and the hypochlorous species, making
it a highly suitable candidate for this integration technique. The
obtained in-depth reaction mechanistic insights will enable the development
of a viable and economical technology for safe water reuse.