Oxidative Degradation of BPA Using TiO2 in Water, and Transition of Estrogenic Activity in the Degradation Pathways

被引:0
作者
Kei Nomiyama
Teiji Tanizaki
Toyokazu Koga
Koji Arizono
Ryota Shinohara
机构
[1] Prefectural University of Kumamoto,Graduate School of Environmental and Symbiotic Sciences
[2] Kitakyushu City Institute of Environmental Sciences,undefined
来源
Archives of Environmental Contamination and Toxicology | 2007年 / 52卷
关键词
TiO2; Degradation Pathway; Estrogenic Activity; Hexadiene; Aquatic Wildlife;
D O I
暂无
中图分类号
学科分类号
摘要
The oxidative degradation behavior of bisphenol A (BPA) using titanium dioxide (TiO2) in water was investigated. The main purposes were to clarify the relationship with estrogenic activity from the degradation pathways demonstrated by oxidation of BPA in water. Approximately 99% of the BPA decomposed within 300 min, and gas chromatography (GC) mass spectrometry (MS) and liquid chromatography (LC) MS analysis revealed many intermediates during the degradation process. Intermediates by decomposition of BPA, such as hydroxylated-BPA (OH-BPA), carboxylic intermediates, phenolic intermediates, and other intermediates produced by the cleavage of a benzene ring were identified and quantified. Estrogenic activities of the degradation pathways of the BPA in water were assessed by using a constructed yeast two-hybrid assay system for human estrogen receptor α (hERα) and Japanese medaka fish (Oryzias latipes) estrogen receptor α (medERα). Estrogenic activity for hERα and medERα was reduced to less than 20% of the initial activity for BPA after 240 min of UV irradiation. However, estrogenic activity for medERα was increased by 110% from the initial activity for BPA at 60 min of UV irradiation. It was estimated that medERα assay was more sensitive for BPA and the intermediates than was the hERα assay. From these findings, we estimate that the intermediates by the oxidation of BPA have the behaviors of xenoestrogen to the aquatic wildlife in the environment.
引用
收藏
页码:8 / 15
页数:7
相关论文
共 120 条
[1]  
Arulmozhiraja S(2005)Structural requirements for the interaction of 91 hydroxylated polychlorinated biphenyls with estrogen and thyroid hormone receptors Toxicol Sci 84 49-62
[2]  
Shiraishi F(1995)In vivo DNA adduct formation by bisphenol A Environ Molec Mutagen 26 60-66
[3]  
Okumura T(2004)Photocatalytic degradation and mineralization of bisphenol A by TiO2 and platinized TiO2 Appl Catalysis A: General 261 225-237
[4]  
Iida M(2005)Effects of Ag and Pt on photocatalytic degradation of endocrine disrupting chemicals in water Chem Eng J 113 65-72
[5]  
Takigami H(2003)Capturing of bisphenol A photodecomposition intermediates by composite TiO2-zeolite sheets Appl Catalysis B: Environmental 46 453-462
[6]  
Edmonds SJ(2004)Environmental remediation by an integrated microwave/UV-illumination technique VII. Thermal/non-thermal effects in the microwave-assisted photocatalyzed mineralization of bisphenol-A J Photochem Photobiol A 162 33-40
[7]  
Morita M(2005)Toxicity to early life stages and an estrogenic effect of a bisphenol A metabolite, 4-methyl-2,4-bis(4-hydroxyphenyl)pent-1-ene on the medaka (Oryzias latipes) Life Sci 77 2643-2655
[8]  
Atkinson A(1995)Morphology of thin anatase coating prepared from alkoxide solutions containing organic polymer, affecting the photocatalytic decomposition of aqueous acetic acid J Mater Sci 30 837-841
[9]  
Roy D(1993)Bisphenol A: an estrogenic substance is released from polycarbonate flasks during autoclaving Endocrinology 132 2279-2286
[10]  
Chiang K(1999)New screening methods for chemicals with hormonal activities using interaction of nuclear hormone receptor with coactivator Toxicol Appl Pharmacol 154 76-83