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臭氧在饮用水中对环磷酰胺和甲氨蝶呤的氧化动力学。

Oxidation kinetics of cyclophosphamide and methotrexate by ozone in drinking water.

机构信息

Department of Chemistry, Université de Montréal, Succ. Centre-ville, Montréal, QC, Canada.

出版信息

Chemosphere. 2010 May;79(11):1056-63. doi: 10.1016/j.chemosphere.2010.03.032. Epub 2010 Apr 18.

Abstract

This study investigates the aqueous degradation by ozone of two target cytostatic drugs, cyclophosphamide and methotrexate. A column switching technique for on-line solid phase extraction (SPE) coupled to electro-spray ionization-tandem mass spectrometry (LC-ESI-MS/MS) was used for the simultaneous detection of the trace contaminants. The second-order kinetic rate constants for the reaction of cyclophosphamide with molecular ozone and hydroxyl radicals were determined in bench-scale experiments at pH 8.10. The molecular ozone oxidation kinetics was studied in buffered ultrapure water and compared to the oxidation kinetics in natural water from a municipal drinking water treatment plant in the province of Quebec (Canada). For cyclophosphamide, the degradation rate constant with molecular ozone in ultrapure water was low (k(O3)=3.3+/-0.2M(-1)s(-1)) and the extent of oxidation was linearly correlated to the ozone exposure. The impact of water quality matrix on oxidation efficacy was not significant during direct ozone reaction (k(O3) =2.9+/-0.3M(-1)s(-1)). The rate constant with hydroxyl radicals was higher at 2.0 x 10(9) M(-1)s(-1). Methotrexate reacted quickly with molecular ozone at dosages typically applied in drinking water treatment (k(O3)>3.6 x 10(3)M(-1)s(-1)). Overall, the results confirmed that organic compounds reactivity with ozone was dependent of their chemical structure. Ozone was very effective against methotrexate but high oxidant concentration x contact time (CT) values were required to completely remove cyclophosphamide from drinking water. Further studies should be conducted in order to identify the ozonation by-products and explore the impact of ozone on their degradation and toxicity.

摘要

本研究考察了两种目标细胞毒性药物环磷酰胺和甲氨蝶呤在水中的臭氧降解情况。采用柱切换技术在线固相萃取(SPE)与电喷雾串联质谱(LC-ESI-MS/MS)联用,用于痕量污染物的同时检测。在 pH 8.10 的台式实验中,测定了环磷酰胺与分子臭氧和羟基自由基反应的二级动力学速率常数。在缓冲超纯水中研究了分子臭氧氧化动力学,并将其与魁北克省(加拿大)市政饮用水处理厂天然水中的氧化动力学进行了比较。对于环磷酰胺,在超纯水中与分子臭氧的降解速率常数较低(k(O3)=3.3+/-0.2M(-1)s(-1)),氧化程度与臭氧暴露量呈线性相关。在直接臭氧反应过程中(k(O3)=2.9+/-0.3M(-1)s(-1)),水质基质对氧化效果的影响并不显著。与羟基自由基的反应速率常数更高,为 2.0 x 10(9) M(-1)s(-1)。甲氨蝶呤与分子臭氧反应迅速,在饮用水处理中通常使用的剂量下(k(O3)>3.6 x 10(3)M(-1)s(-1))。总的来说,结果证实了有机化合物与臭氧的反应性取决于其化学结构。臭氧对甲氨蝶呤非常有效,但需要高氧化剂浓度 x 接触时间(CT)值才能将环磷酰胺从饮用水中完全去除。应进一步研究以确定臭氧化产物,并探讨臭氧对其降解和毒性的影响。

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