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Kinetics of paracetamol oxidation by ozone and hydroxyl radicals, formation of transformation products and toxicity

机译:扑热息痛被臭氧和羟基自由基氧化的动力学,转化产物的形成和毒性

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Paracetamol oxidation by ozonation and H2O2/UV processes was investigated. The second-order rate constant for the reaction of paracetamol with ozone was determined at pH 7.2 (ko_(3/PRC) = 2.57 × 10~6 M~(-1) s~(-1)). The rate constant of the elementary reaction of ozone with the ionized form of PRC was then calculated and the pH dependence of the ozonation reaction of PRC was estimated. The second-order rate constant of the reaction of paracetamol with HO~· radicals was also determined at pH 5 through the H2O2/UV oxidation system (k_(HO~·/PRC) = 4.94 × 10~9 M~(-1) s~(-1)). In the light of the high rate constants obtained, two conclusions on the kinetics of paracetamol ozonation in real water were drawn: (i) hydroxyl radicals do not have any impact on the removal of paracetamol during ozonation of real waters; (ii) a half-life of 0.03 s can be estimated for paracetamol, for a residual ozone concentration of 0.4 mg L~(-1). Hydroquinone and two other ozonation transformation products were identified by LC/UV, LC/MS and MS/MS analyses. In parallel, for the first time, toxicity was measured in ozonated paracetamol solutions with the luminescent bacteria Vibrio fisheri test. The results showed an increase in toxicity as paracetamol degraded. This toxicity could not be assigned to hydroquinone formation only. One or several other transformation products more toxic than paracetamol might be formed.
机译:通过臭氧化和H2O2 / UV工艺研究了扑热息痛的氧化作用。在pH 7.2下确定对乙酰氨基酚与臭氧反应的二级速率常数(ko_(3 / PRC)= 2.57×10〜6 M〜(-1)s〜(-1))。然后计算了离子化的PRC形式的臭氧元素反应的速率常数,并估算了PRC臭氧化反应的pH依赖性。还通过H2O2 / UV氧化系统在pH 5下确定了扑热息痛与HO〜·自由基反应的二级速率常数(k_(HO〜·/ PRC)= 4.94×10〜9 M〜(-1) s〜(-1))。鉴于所获得的高速率常数,得出了对对乙酰氨基酚在真实水中臭氧氧化动力学的两个结论:(i)羟基自由基在对真实水中进行臭氧氧化期间对扑热息痛的去除没有任何影响; (ii)对于扑热息痛,对于残留臭氧浓度为0.4 mg L〜(-1)的半衰期可以估计为0.03 s。通过LC / UV,LC / MS和MS / MS分析鉴定了对苯二酚和其他两种臭氧氧化转化产物。同时,首次使用发光细菌费氏弧菌测试在臭氧化对乙酰氨基酚溶液中的毒性。结果显示,随着扑热息痛降解,毒性增加。该毒性不能仅归因于对苯二酚的形成。可能会形成一种比对乙酰氨基酚毒性更高的一种或几种其他转化产物。

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