Enhanced degradation of organic contaminants by thermally activated peroxymonosulfate in the presence of chloride ion

The effect of chloride ion (Cl-) on the degradation of organic contaminants (OCs) by thermally activated peroxymonosulfate (TAP) was assessed in this study. P-aminobenzoic acid (PABA), sulfadiazine (SDZ), bisphenol A (BPA), and chloramphenicol (CAP) were employed as model OCs with different structure. The degradation efficiencies of PABA, SDZ, BPA, and CAP were respectively 76.4 %, 90.8 %, 10.1 %, and 14.5 % by TAP (70 degrees C) after 60 mM treatment, further raised to 97.6 %, 97.4 %, 55.2 %, and 30.5 % in the presence of Cl- (1 mM). When Cl- concentration increased to 10 mM, PABA and SDZ were completely degraded respectively after 7 min and 10 min, 97.1 % of BPA and 59.5 % of CAP were removed within 60 mM. In TAP system, PABA and SDZ were primarily degraded by direct peroxymonosulfate (PMS) oxidation, while BPA and CAP were mostly removed by hydroxyl radical and sulfate radical oxidation. In Cl-/TAP mixtures, the degradation of PABA and BPA was mainly attributed to hypochlorous acid oxidation, SDZ was chiefly removed via direct PMS oxidation, and CAP was principally oxidized by radicals. Furthermore, the intermediate products of OCs degradation during Cl-/TAP oxidation were identified, and primary degradation pathways were proposed. The removal efficiencies of total organic carbon were markedly improved from 19.3 % to 25.3 % by TAP to 52.6 %-69.0 % in Cl-/TAP system. The concentrations of typical chlorinated by-products after OCs oxidation were 17.2 mu g/L-86.3 mu g/L in Cl-/TAP system. Considering the complexity of actual wastewater, 51.3 %-100 % removal efficiencies of OCs by TAP oxidation were achieved in Cl--containing secondary effluent. Understanding the role of Cl(- )in OCs degradation is essential for the practical application of Cl-/TAP oxidation in advanced wastewater treatment.

Automated summary

This study assessed the impact of chloride ion on the degradation of organic contaminants by thermally activated peroxymonosulfate. The results showed that chloride ion significantly increased the degradation efficiency of organic contaminants and the primary degradation pathways depended on the structure of the contaminants.