Oxidation of bisphenol A by ozone in aqueous solution

被引:192
作者
Deborde, Marie [1 ,2 ]
Rabouan, Sylvie [1 ,2 ]
Mazellier, Patrick [1 ,2 ]
Duguet, Jean-Pierre [3 ]
Legube, Bernard [1 ,2 ]
机构
[1] Univ Poitiers, Lab Chim & Microbiol Eau, UMR 6008, Ecole Super Ingenieurs Poitiers,Fac Med & Pharm, F-86022 Poitiers, France
[2] CNRS, Lab Chim & Microbiol Eau, UMR 6008, Poitiers, France
[3] Direct Qual & Environm, EAU DE PARIS, F-75675 Paris 14, France
关键词
Endocrine disruptors; Bisphenol A; By-products; LC-MS; Ozonation; Reaction pathways;
D O I
10.1016/j.watres.2008.07.015
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Based on the literature data, an efficient removal of bisphenol A (BPA) during ozonation can be expected under water treatment conditions. However, up to now, the degradation products have not been identified. This has been the main point of this study. Aqueous solutions of BPA have been analyzed by LC-UV, LC-MS or MS/MS at different ozone doses. Under our experimental conditions, up to five major transformation products were evidenced. According to UV, MS and MS/MS spectra characteristics, chemical structures are consistent with catechol, orthoquinone, muconic acid derivatives of BPA, benzoquinone and 2-(4-hydroxyphenyl)-propan-2-ol. Moreover, three additional minor transformation products have been observed for which chemical structures have been tentatively proposed. in the case of major transformation products, the reaction pathway may involve an initial ozone reaction by electrophilic substitution or 1,3-dipolar cycloaddition. In the presence of ozone, these primary transformation products were shown to be unstable. Further transformation products, with smaller molecular weight and more polar character such as aliphatic acids or aldehydes, are then expected during ozonation. The identification of minor transformation products was more complex to assess. However, oligomeric structures have been evidenced, certainly arising from secondary reaction between various oxidation products of BPA. The formation of these latter products would not be favored under water treatment conditions. (C) 2008 Elsevier Ltd. All rights reserved.
引用
收藏
页码:4299 / 4308
页数:10
相关论文
共 30 条
[1]  
ASH M, 1995, HDB PLASTIC RUBBER A
[2]   DETERMINATION OF OZONE IN WATER BY THE INDIGO METHOD [J].
BADER, H ;
HOIGNE, J .
WATER RESEARCH, 1981, 15 (04) :449-456
[3]  
BAILEY PS, 1982, OZONATION ORGANIC CH, V39
[4]   Kinetics of aqueous ozone-induced oxidation of some endocrine disruptors [J].
Deborde, M ;
Rabouan, S ;
Duguet, JP ;
Legube, B .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2005, 39 (16) :6086-6092
[5]  
*EUR COMM, 1996, 17549 EUR EUR COMM
[6]   Chlorination of bisphenol A:: kinetics and by-products formation [J].
Gallard, H ;
Leclercq, A ;
Croué, JP .
CHEMOSPHERE, 2004, 56 (05) :465-473
[7]   Liquid chromatography/multi-stage mass spectrometry of bisphenol A and its halogenated derivatives [J].
Gallart-Ayala, Hector ;
Moyano, Encarnacion ;
Galceran, Maria T. .
RAPID COMMUNICATIONS IN MASS SPECTROMETRY, 2007, 21 (24) :4039-4048
[8]   The occurrence of xenoestrogens in the Elbe river and the North Sea [J].
Heemken, OP ;
Reincke, H ;
Stachel, B ;
Theobald, N .
CHEMOSPHERE, 2001, 45 (03) :245-259
[9]  
HOIGNE J, 1983, WATER RES, V17, P185, DOI 10.1016/0043-1354(83)90099-4
[10]   Products of aqueous chlorination of bisphenol A and their estrogenic activity [J].
Hu, JY ;
Aizawa, T ;
Ookubo, S .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2002, 36 (09) :1980-1987