In recent years, the advanced Fenton-like oxidation technology based on peracetic acid (PAA) has attracted increasing attention, while accelerating the cycle of Fe(III)/Fe(II) remains a limitation for widespread PAA/Fe(III) system application. Herein, in this study, the dual mechanism of UV synchronous acceleration of Fe(III)/Fe(II) cycling and activation of PAA was systematic investigated with the introduction of UV in PAA/Fe(III) systems. Results suggested that the target pollutant Rhodamine B (RhB) could achieve over 95% degradation within 12minutes in the Fe (III)/PAA/UV system. The crucial roles of UV radiation has been determined to activate PAA independently, and synchronously accelerates the transfer of Fe (III) to Fe (II) to generate hydroxyl radicals (·OH), while also enhancing the generation of Fe (IV), ultimately achieving a redox cycle in Fe (III)/PAA/UV system. The ·OH, Fe(IV) and organic free radicals (R-O·) were identified as the mainly active substances via the various analysis methods including characteristic product detection, quenching experiments, electron paramagnetic resonance (EPR), and fluorescence analysis, and the contribution to the RhB degradation followed as ·OH(68.61%) > Fe(IV) (17.52%) > R-O·(11.69%). 12 intermediates and two potential degradation pathways of RhB were identified by combining density functional theory (DFT) calculations and Ultra-Performance Liquid Chromatography-Quadrupole Time-of-Flight Mass Spectrometry (UPLC-QTOF-MS) analyses, and the ecotoxicity was evaluated through Ecological Structure Activity Relationships (ECOSAR) program. Response surface methodology was employed to analyze optimal degradation conditions, considering Fe(III) and PAA dosage, pH, and inhibitory effects of anions. This study systematically revealed the internal mechanism of Fe(III)/PAA/UV system for organic pollutant degradation and verified its efficiency and eco-friendliness.
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