4.8 Article

Radical Chemistry and Structural Relationships of PPCP Degradation by UV/Chlorine Treatment in Simulated Drinking Water

Journal

ENVIRONMENTAL SCIENCE & TECHNOLOGY
Volume 51, Issue 18, Pages 10431-10439

Publisher

AMER CHEMICAL SOC
DOI: 10.1021/acs.est.7b02059

Keywords

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Funding

  1. Natural Science Foundation of China [21677181, 51378515, 21422702]
  2. National Key Research Development Program of China [2016YFC0502803]
  3. Tip-top Scientific and Technical Innovative Youth Talents of Guangdong Special Support Program [2015TQ01Z552]
  4. Guangdong Provincial Key Laboratory of Environmental Pollution Control and Remediation Technology [2016K0004]

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The UV/chlorine process is an emerging advanced oxidation process (AOP) used for the degradation of micropollutants. However, the radical chemistry of this AOP is largely unknown for the degradation of numerous structurally diverse micropollutants in water matrices of varying quality. These issues were addressed by grouping 34 pharmaceuticals and personal care products (PPCPs) according to the radical chemistry of their degradation in the UV/chlorine process at practical PPCP concentrations (1 mu g L-1) and in different water matrices. The contributions of HO center dot and reactive chlorine species (RCS), including Cl-center dot, Cl-2(center dot-), and ClO center dot, to the degradation of different PPCPs were compound specific. RCS showed considerable reactivity with olefins and benzene derivatives, such as phenols, anilines, and alkyl-/alkoxybenzenes. A good linear relationship was found between the RCS reactivity and negative values of the Hammett Sigma sigma(+)(P) constant for aromatic PPCPs, indicating that electron-donating groups promote the attack of benzene derivatives by RCS. The contribution of HO center dot, but not necessarily RCS, to PPCP removal decreased with increasing pH. ClO center dot showed high reactivity with some PPCPs, such as carbamazepine, caffeine, and gemfibrozil, with second-order rate constants of 9.2 X 10(7), 1.03 X 10(8), and 4.16 X 10(8) M-1 s(-1), respectively, which contributed to their degradation. Natural organic matter (NOM) induced significant scavenging of ClO center dot and greatly decreased the degradation of PPCPs that was attributable to ClO center dot, with a second-order rate constant of 4.5 X 10(4) (mg L-1)(-1) s(-1). Alkalinity inhibited the degradation of PPCPs that was primarily attacked by HO center dot and Cl-center dot but had negligible effects on the degradation of PPCPs by ClO center dot. This is the first study on the reactivity of RCS, particularly ClO center dot, with structurally diverse PPCPs under simulated drinking water condition.

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