LAUSR

Abstract N-containing organic wastewater is harmful to human health and ecosystem while its degradation remains a huge challenge for decarburization and denitrification simultaneously. In this paper, we proposed a new photoelectrochemical method of chlorine oxide radicals production to oxidize mixture wastewater of phenol and N-ammonia into N2 and CO2. The chlorine oxide radicals were generated via a rapid reaction of HClO with hydroxyl radicals or chlorine free radicals on a synergistic dual anode, in which hydroxyl radicals and chlorine free radicals generated on WO3 side, and HClO generated on Sb-SnO2 side, respectively. Phenol degradation rate on WO3-Sb/SnO2 was 2.54 and 4.79 times than that on WO3 and Sb/SnO2. Meanwhile, N-ammonia removal rate on WO3-Sb/SnO2 was 5.69 and 20 times greater than that on WO3 and Sb/SnO2, respectively. The effects of potential, Cl− concentration and initial pH were examined and the optimal conditions were potential 2.0 V vs Ag/AgCl, 0.05 M NaCl, pH = 5. The free radical quenching experiments and electron-spin resonance (ESR) confirmed that chlorine oxide radicals played an important role in the degradation of N-ammonia and phenol. Reasonable pathways of phenol in the WO3-Sb/SnO2 system were also proposed. This work provides an exhaustive, novel, environmental-friendly photoelectrochemical system for N-containing organic wastewater treatment.