Sturm A, Cravedi J P, Perdu E, Baradat M, Segner H
Department of Chemical Ecotoxicology, UFZ Centre for Environmental Research, Permoserstrasse 15, D-04318, Leipzig, Germany.
Aquat Toxicol. 2001 Aug;53(3-4):229-45. doi: 10.1016/s0166-445x(01)00168-0.
The suitability of cultured rainbow trout hepatocytes as a model system for the assessment of xenobiotic effects on hepatic biotransformation enzymes in fish was examined. Two model water pollutants, the imidazole fungicide prochloraz and the alkylphenolic compound nonylphenol diethoxylate (NP2EO), were investigated in a comparative in vitro/in vivo approach. Biotransformation enzymes were measured in cultured rainbow trout hepatocytes following exposure to xenobiotics in vitro, or in the liver of juvenile rainbow trout (Oncorhynchus mykiss) exposed in vivo. The patterns of biochemical responses to the model pollutants were generally similar between in vitro and in vivo investigations. Levels of cytochrome P4501A (CYP1A) protein and the catalytic activity of the CYP1A-dependent enzyme 7-ethoxyresorufin-O-deethylase (EROD) were induced in vitro after 24 h of exposure to 1.0 microM prochloraz. In vitro, higher prochloraz concentrations induced only the levels of CYP1A above control levels, but not EROD activity. In vivo exposure of juvenile trout to 0.27 microM prochloraz resulted in an induction of CYP1A and EROD after 7 and 14 days, while 0.027 microM prochloraz had no effects. In vitro, the 6beta- and 16beta-hydroxylation of testosterone was significantly decreased by 1.0-3.0 microM prochloraz, while in vivo these variables were significantly inhibited after exposure to 0.27 microM prochloraz for 7 and 14 days. NP2EO did not affect EROD activity in vitro. In vivo, EROD activity and CYP1A remained unchanged following 7 days of exposure to 0.32 or 1.30 microM NP2EO. NP2EO (15-50 microM) inhibited the 16beta-hydroxylation and glucuronidation of testosterone in vitro. In vivo, 7 days of exposure to 0.32 or 1.30 microM NP2EO resulted in a significant inhibition of the 6beta- and 16beta-hydroxylation of testosterone. The good qualitative correspondence between in vitro and in vivo results indicates that studies using trout hepatocytes allow the identification of biochemical targets of xenobiotic effects in fish liver. However, more research is needed before quantitative predictions, e.g. of effective concentrations, can be made from in vitro investigations.
研究了培养的虹鳟肝细胞作为评估外源化合物对鱼类肝脏生物转化酶影响的模型系统的适用性。采用体外/体内比较研究方法,研究了两种模型水污染物,即咪唑类杀菌剂咪鲜胺和烷基酚化合物壬基酚二乙氧基化物(NP2EO)。在体外将外源化合物暴露于培养的虹鳟肝细胞后,或在体内将外源化合物暴露于虹鳟幼鱼(Oncorhynchus mykiss)肝脏后,测定生物转化酶。体外和体内研究中对模型污染物的生化反应模式总体相似。暴露于1.0微摩尔/升咪鲜胺24小时后,体外诱导了细胞色素P4501A(CYP1A)蛋白水平和CYP1A依赖性酶7-乙氧基异吩恶唑酮-O-脱乙基酶(EROD)的催化活性。在体外,较高浓度的咪鲜胺仅诱导CYP1A水平高于对照水平,但不诱导EROD活性。虹鳟幼鱼体内暴露于0.27微摩尔/升咪鲜胺7天和14天后,诱导了CYP1A和EROD,而0.027微摩尔/升咪鲜胺没有影响。在体外,1.0 - 3.0微摩尔/升咪鲜胺显著降低了睾酮的6β-和16β-羟基化,而在体内,暴露于0.27微摩尔/升咪鲜胺7天和14天后,这些变量受到显著抑制。NP2EO在体外不影响EROD活性。在体内,暴露于0.32或1.30微摩尔/升NP2EO 7天后,EROD活性和CYP1A保持不变。NP2EO(15 - 50微摩尔/升)在体外抑制了睾酮的16β-羟基化和葡萄糖醛酸化。在体内,暴露于0.32或1.30微摩尔/升NP2EO 7天后,显著抑制了睾酮的6β-和16β-羟基化。体外和体内结果之间良好的定性对应表明,使用鳟肝细胞的研究能够确定外源化合物对鱼肝影响的生化靶点。然而,在能够从体外研究进行定量预测(例如有效浓度)之前,还需要更多的研究。