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Advanced oxidation of dodecyl dimethyl benzyl ammonium chloride by VUV/UV/chlorine: Synergistic effect, radicals, and degradation pathway

化学 氯化铵 激进的 降级(电信) 氯化物 无机化学 反应速率常数 光化学 核化学 有机化学 动力学 物理 电信 量子力学 计算机科学
作者
Zhuo-Yuan Xiao,Nan Huang,Qi Wang,Wenlong Wang,Qian‐Yuan Wu,Hong‐Ying Hu
出处
期刊:Separation and Purification Technology [Elsevier BV]
卷期号:292: 121012-121012 被引量:18
标识
DOI:10.1016/j.seppur.2022.121012
摘要

• VUV/UV/chlorine showed synergistic effect on DDBAC degradation than chlorine, UV, VUV/UV, UV/chlorine. • DDBAC degraded through both UV photolysis and radical oxidation during VUV/UV/chlorine. • The concentration and contribution of OH and Cl during VUV/UV/chlorine oxidation were calculated. • Degradation pathway of DDBAC during VUV/UV/chlorine oxidation was proposed. Quaternary ammonium compounds (QACs) are crucial ingredients in many cleaning agents, disinfectants and personal care products. They are widely detected in aquatic environments. In this study, vacuum ultraviolet (VUV)/UV/chlorine was used to degrade dodecyl dimethyl benzyl ammonium chloride (DDBAC, a typical QAC). The degradation efficiency of VUV/UV/chlorine on DDBAC was the highest among chlorine, UV, VUV/UV, UV/chlorine and VUV/UV/chlorine. During the VUV/UV/chlorine process, with chlorine concentration increasing from 0 to 700 μM, the degradation rate constant of DDBAC increased from 0.16 to 0.22 min −1 then decreased to 0.17 min −1 . When the chloride concentration was 10 mM and 50 mM, the degradation rate constant of DDBAC decreased by 31% and 55%, respectively. Inorganic anions and organic compounds in the reverse osmosis concentrate inhibited the degradation of DDBAC by quenching radicals. The degradation mechanisms of DDBAC degradation during the VUV/UV/chlorine process include UV photolysis and oxidation by OH, Cl and other reactive species. With the increase in pH from 5 to 10, the OH concentration decreased from 18.7 × 10 −14 M to 7.5 × 10 −14 M, and the Cl concentration decreased from 8.8 × 10 −14 M to 2.1 × 10 −14 M. At pH 5–10, contributions of OH and Cl to DDBAC degradation were 30%−44% and 18%−37%, respectively. Degradation mechanisms of DDBAC mainly include hydrogen abstraction, hydroxylation, and cleavage of the C-N bond. The concentrations of four chlorinated products (trichloromethane, monochloroacetic acid, dichloroacetic acid, and trichloroacetic acid) mostly initially increased and then decreased.
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