Bols N C, Schirmer K, Joyce E M, Dixon D G, Greenberg B M, Whyte J J
Department of Biology, University of Waterloo, Waterloo, Ontario, N2L 3G1, Canada.
Ecotoxicol Environ Saf. 1999 Sep;44(1):118-28. doi: 10.1006/eesa.1999.1808.
Along with 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), 24 unsubstituted polycyclic aromatic hydrocarbons (PAHs) were evaluated for their ability to induce 7-ethoxyresorufin-o-deethylase (EROD) activity in the rainbow trout liver cell line RTL-W1. When the duration and cell density of exposure were increased, the EC(50) for EROD induction was relatively constant for TCDD, but increased for PAHs. Regardless of exposure conditions, EROD activity was not induced by 9 PAHs: naphthalene, phenanthrene, anthracene, pyrene, perylene, acenaphthylene, acenaphthene, fluorene, and fluoranthene. Two PAHs, benzo[g,h,i]perylene and coronene, induced EROD activity inconsistently. The remaining 13 PAHs consistently induced EROD activity. The EC(50)s for induction exhibited approximately a 110-fold range. The order of potency, from most to least potent, was benzo[k]fluoranthene, dibenzo[a,i]pyrene, dibenzo [a,h]anthracene, benzo[a]pyrene, indeno[1,2,3-cd]pyrene, benzo [b]fluoranthene, pentacene, benzo[b]anthracene, benzo[b] fluorene, chrysene, benzo[a]anthracene, benzo[e]pyrene, and triphenylene. When the induction potency was expressed relative to TCDD, the toxic equivalency factors (TEFs) ranged from 0.001 to 0.000 01. When expressed relative to benzo[a]pyrene, the TEFs ranged from 3.44 to 0. 03.
除2,3,7,8-四氯二苯并对二恶英(TCDD)外,还评估了24种未取代的多环芳烃(PAH)在虹鳟肝细胞系RTL-W1中诱导7-乙氧基异吩恶唑酮-O-脱乙基酶(EROD)活性的能力。当暴露时间和细胞密度增加时,TCDD诱导EROD的半数效应浓度(EC50)相对恒定,但PAH的EC50增加。无论暴露条件如何,9种PAH均未诱导EROD活性,它们是萘、菲、蒽、芘、苝、苊烯、苊、芴和荧蒽。两种PAH,即苯并[g,h,i]苝和晕苯,诱导EROD活性不稳定。其余13种PAH始终诱导EROD活性。诱导的EC50显示出约110倍的范围。效力顺序从最强到最弱依次为苯并[k]荧蒽、二苯并[a,i]芘、二苯并[a,h]蒽、苯并[a]芘、茚并[1,2,3-cd]芘、苯并[b]荧蒽、并五苯、苯并[b]蒽、苯并[b]芴、 Chrysene、苯并[a]蒽、苯并[e]芘和三亚苯。当诱导效力相对于TCDD表示时,毒性当量因子(TEF)范围为0.001至0.000 01。当相对于苯并[a]芘表示时,TEF范围为3.44至0.03。