2018
DOI: 10.1016/j.cej.2017.08.117
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Investigation of clofibric acid removal by UV/persulfate and UV/chlorine processes: Kinetics and formation of disinfection byproducts during subsequent chlor(am)ination

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Cited by 94 publications
(46 citation statements)
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“…Figures 9 and 10 display the decomposition of CIP at different HA dosages (0.1 to 10 mg/L) in UV/chlorine and UV/PS, respectively, at initial CIP concentration of 1 μM, oxidant dosage of 1 mM, and pH 0 7.4. The presence of HA inhibited the degradation of the target pollutant in both the UV-based AOPs, consistent with the reports of most studies (Kong et al, 2016;Liu et al, 2016;Lu et al, 2018). The CIP degradation was significantly obstructed with an increasing HA concentration.…”
Section: Research Articlesupporting
confidence: 90%
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“…Figures 9 and 10 display the decomposition of CIP at different HA dosages (0.1 to 10 mg/L) in UV/chlorine and UV/PS, respectively, at initial CIP concentration of 1 μM, oxidant dosage of 1 mM, and pH 0 7.4. The presence of HA inhibited the degradation of the target pollutant in both the UV-based AOPs, consistent with the reports of most studies (Kong et al, 2016;Liu et al, 2016;Lu et al, 2018). The CIP degradation was significantly obstructed with an increasing HA concentration.…”
Section: Research Articlesupporting
confidence: 90%
“…Compared to Cl − , HCO 3 − had a more apparent inhibitory effect on the degradation of CIP as the reaction of HCO 3 − with either HO · or Cl · generates CO 3 · − (Equations () and ()) (Lu et al, ), which had a weaker oxidation capacity with a redox potential of 1.59–1.63V (Bennedsen, Muff, & Søgaard, ). In addition, the reaction solution becomes alkaline upon addition of HCO 3 − , and as explained previously in Section 3.3, an alkaline condition obstructs the degradation of CIP.…”
Section: Resultsmentioning
confidence: 99%
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