| Popis: |
Halides (X−) in the industrial wastewater are usually thought to adversely affect the degradation kinetics and mineralization rates in several SO4−-based advanced oxidation processes. However, their unfavorable effects might be overestimated, particularly the heat/persulfate (PS) system as tested in the present study. Here the degradation of phenol, benzoic acid, coumarin and acid orange 7 (AO7) was examined with the presence of chloride or bromide in a heat/PS process. Cl− was found to have a dual effect (inhibition followed by enhancement) on the decomposition rates of organic pollutants, whereas the effects of Br− are insignificant within the tested concentration (0–0.2 mM). However, some chlorinated or brominated compounds were still identified in this heat/PS system. Unexpectedly, the mineralization rates of AO7, phenol, benzoic acid and coumarin were not apparently inhibited. In addition, the formation of adsorbable organic halogen (AOX) in the heat/PS system was much less than those in the peroxymonosulfate (PMS)/Cl− or PMS/Br− systems. According to the results of kinetic modeling, SO4− was the dominating radical for AO7 degradation without Cl− or Br−, but Cl2− was the main oxidant in the presence of Cl−, SO4−, Br and Br2- were responsible for the oxidation of AO7 in the presence of Br−. The present study assumes that X2/HOX, rather than halogen radicals, is responsible for the enhanced formation of organohalogens. These findings are meaningful to evaluate the PS-based technologies for the high-salinity wastewater and to develop useful strategies for mitigating the negative effects of halides in advanced oxidation processes (AOPs). Keywords: Sulfate radicals, AOX formation, Chlorinated byproducts, Mineralization |
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