Yamamoto Hiroshi, Watanabe Mikako, Hirata Yoshiko, Nakamura Yuki, Nakamura Yudai, Kitani Chise, Sekizawa Jun, Uchida Masaya, Nakamura Hiroshi, Kagami Yoshihiro, Koshio Masaaki, Hirai Narisato, Tatarazako Norihisa
Department of Physical, Chemical, Geological and Environmental Sciences, Faculty of Integrated Arts and Sciences, The University of Tokushima, 1-1 Minamijosanjima-cho, Tokushima, Japan.
Environ Sci. 2007;14 Suppl:73-87.
Butylparaben and benzylparaben, used as preservatives mainly in cosmetic products, have recently been found to be weakly estrogenic. Batch activated-sludge treatment and batch chlorination were carried out to roughly determine the removal efficiency of a wastewater treatment plant. Combining the removal efficiency with the estimated annual consumption and the unaltered excretion ratio, the maximum predicted environmental concentration (PEC) was estimated. Conventional acute/chronic toxicity tests were conducted using Japanese medaka (Oryzias latipes), daphnia (Daphnia magna), and green algae (Pseudokirchneriella subcapitata) for n-butylparaben, i-butylparaben, and benzylparaben. Medaka vitellogenin assays were also conducted for the three compounds and DNA microarray analysis was carried out to examine the effects of benzylparaben on gene expression. The plasma vitellogenin concentration of male medaka increased for concentrations of 200, 100, and 100 microg L(-1) n-butylparaben, i-butylparaben, and benzylparaben for 14 days, respectively, while the expression levels of genes encoding proteins such as p53, cytochrome P450 3A40, and choriogenin-L increased for concentrations higher than 4 microg L(-1) of benzylparaben. Furthermore, the predicted no-effect concentration (PNEC) was calculated using the lethal or effect concentration 50 (LC50 or EC50) values and no-effect concentrations (NOECs) obtained in the toxicity tests for these compounds. The maximum concentrations found in the aquatic environment or sewage effluent (MEC eff) were used to carry out preliminary environmental risk assessment. The calculated MEC/PNEC ratio suggests the necessity of further study such as a more detailed large-scale monitoring and chronic toxicity tests including reproduction inhibition and endocrine disruption.
对羟基苯甲酸丁酯和对羟基苯甲酸苄酯主要用作化妆品中的防腐剂,最近被发现具有弱雌激素活性。进行了批次活性污泥处理和批次氯化,以大致确定污水处理厂的去除效率。将去除效率与估计的年消耗量和未改变的排泄率相结合,估算了最大预测环境浓度(PEC)。使用日本青鳉(Oryzias latipes)、大型溞(Daphnia magna)和绿藻(Pseudokirchneriella subcapitata)对正丁基对羟基苯甲酸酯、异丁基对羟基苯甲酸酯和对羟基苯甲酸苄酯进行了常规急性/慢性毒性试验。还对这三种化合物进行了青鳉卵黄蛋白原测定,并进行了DNA微阵列分析,以研究对羟基苯甲酸苄酯对基因表达的影响。雄性青鳉的血浆卵黄蛋白原浓度在分别暴露于200、100和100μg L(-1)的正丁基对羟基苯甲酸酯、异丁基对羟基苯甲酸酯和对羟基苯甲酸苄酯14天后升高,而当对羟基苯甲酸苄酯浓度高于4μg L(-1)时,编码p53、细胞色素P450 3A40和绒毛膜生成素-L等蛋白质的基因表达水平升高。此外,使用这些化合物在毒性试验中获得的致死或效应浓度50(LC50或EC50)值和无效应浓度(NOECs)计算了预测无效应浓度(PNEC)。利用在水环境或污水排放中发现的最大浓度(MEC eff)进行了初步环境风险评估。计算得出的MEC/PNEC比值表明有必要进行进一步研究,如更详细的大规模监测和包括繁殖抑制和内分泌干扰在内的慢性毒性试验。