Mechanism of metal sulfides accelerating Fe(II)/Fe(III) redox cycling to enhance pollutant degradation by persulfate: Metallic active sites vs. reducing sulfur species

Metal sulfides (MeSx) have been found to be effective in enhancing pollutant degradation by Fenton-like reactions, but their role in persulfate (PS)-based oxidation processes as well as underlying mechanism have not been fully explored. In this study, effects of different MeSx including WS2, MoS2, FeS2 and ZnS on pollutant degradation by Fe2+/PS or Fe3+/PS systems were examined. It was found that the maximum degradation rate of 2,4,4'-trichlorobiphenyl increased by 5.6 and 16.2 times with the addition of WS2 (0.2 g/L) in the Fe2+/PS and Fe3+/PS systems, respectively. Similar enhancement effects were also observed for MoS2, FeS2 and ZnS, which can enhance the degradation of a wide range of pollutants including sulfamethoxazole, bisphenol A and chlorophenol. The mechanism of these processes were further investigated, and it was observed that Fe(III)/Fe(II) redox cycles were dramatically accelerated on MeSx surfaces, which increased PS activation to generate sulfate radicals and hydroxyl radicals, as evidenced by the combined analyses of surface Fe species, electron paramagnetic resonance and radical probing tests. Both surface metallic active sites and reducing sulfur species contributed to Fe(II) regeneration, but the efficiencies varied with the properties of MeSx surface. This study provides a novel strategy for improving the performance of PS activation for environmental remediation and a comprehensive understanding of the mechanism of MeSx enhancing Fenton-like reactions.

Automated summary

Metal sulfides have been found to enhance pollutant degradation in persulfate oxidation processes by accelerating Fe(III)/Fe(II) redox cycles on their surfaces, leading to increased generation of sulfate and hydroxyl radicals for improved performance in environmental remediation.