Gao Lina, Mutlu Esra, Collins Leonard B, Walker Nigel J, Hartwell Hadley J, Olson James R, Sun Wei, Gold Avram, Ball Louise M, Swenberg James A
National Toxicology Program, National Institute of Environmental Health Sciences, NIH, RTP , Durham, North Carolina 27709, United States.
Department of Pharmacology and Toxicology, State University of New York at Buffalo , Buffalo, New York 14214, United States.
Chem Res Toxicol. 2017 Mar 20;30(3):794-803. doi: 10.1021/acs.chemrestox.6b00368. Epub 2017 Feb 16.
DNA oxidation damage has been regarded as one of the possible mechanisms for the hepatic carcinogenesis of dioxin-like compounds (DLCs). In this study, we evaluated the toxic equivalency factor (TEF) from the standpoint of induced DNA oxidation products and their relationship to toxicity and carcinogenicity. Nine DNA oxidation products were analyzed in the liver of female Sprague-Dawley rats exposed to 2,3,7,8-tetrachlorodibenzo-pdioxin (TCDD) alone or the tertiary mixture of TCDD, 3,3',4,4',5-pentachlorobiphenyl (PCB 126), and 2,3,4,7,8-pentachlorodibenzofuran (PeCDF) by gavage for 14, 31, and 53 weeks (5 days/week) by LC-MS/MS: 8-oxo-7,8-dihydro-2'-deoxyguanosine (8-oxo-dGuo); 1,N-etheno-2'-deoxyadenosine (1,N-εdAdo); N,3-ethenoguanine (N,3-εG); 7-(2-oxoethly)guanine (7-OEG); 1,N-etheno-2'-deoxyguanosine (1,N-εdGuo); malondialdehyde (MdGuo); acrolein (AcrdGuo); crotonaldehyde (CrdGuo); and 4-hydroxynonenal (HNEdGuo) derived 2'-deoxyguanosine adducts. Exposure to TCDD (100 ng/kg/day) significantly induced 1,N-εdAdo at 31 and 53 weeks, while no increase of 8-oxo-dGuo was observed. Significant increases were observed for 8-oxo-dGuo and 1,N-εdAdo at all time points following exposure to the tertiary mixture (TEQ 100 ng/kg/day). Exposure to TCDD for 53 weeks only significantly increased 1,N-εdAdo, while increases of N,3-εG and 7-OEG were only found in the highest dose group (100 ng/kg/day). Exposure to the tertiary mixture for 53 weeks had no effect on N,3-εG in any exposure group (TEQ 0, 22, 46, or 100 ng/kg/day), while significant increases were observed for 1,N-εdAdo (all dose groups), 8-oxo-dGuo (46 and 100 ng/kg/day), and 7-OEG (100 ng/kg/day). While no significant increase was observed at 53 weeks for 1,N-εdGuo, MdGuo, AcrdGuo, or CrdGuo following exposure to TCDD (100 ng/kg/day), all of them were significantly induced in animals exposed to the tertiary mixture (TEQ 100 ng/kg/day). This oxidation DNA product data suggest that the simple TEF methodology cannot be applied to evaluate the diverse patterns of toxic effects induced by DLCs.
DNA氧化损伤被认为是二噁英类化合物(DLCs)诱发肝癌的可能机制之一。在本研究中,我们从诱导的DNA氧化产物及其与毒性和致癌性的关系角度评估了毒性当量因子(TEF)。通过液相色谱 - 串联质谱法(LC-MS/MS)分析了单独暴露于2,3,7,8 - 四氯二苯并 - p - 二噁英(TCDD)或TCDD、3,3',4,4',5 - 五氯联苯(PCB 126)和2,3,4,7,8 - 五氯二苯并呋喃(PeCDF)的三元混合物的雌性Sprague-Dawley大鼠肝脏中的9种DNA氧化产物,这些大鼠通过灌胃给药14、31和53周(每周5天):8 - 氧代 - 7,8 - 二氢 - 2'-脱氧鸟苷(8 - 氧代 - dGuo);1,N - 乙烯基 - 2'-脱氧腺苷(1,N - εdAdo);N,3 - 乙烯基鸟嘌呤(N,3 - εG);7 - (2 - 氧代乙基)鸟嘌呤(7 - OEG);1,N - 乙烯基 - 2'-脱氧鸟苷(1,N - εdGuo);丙二醛(MdGuo);丙烯醛(AcrdGuo);巴豆醛(CrdGuo);以及源自2'-脱氧鸟苷加合物的4 - 羟基壬烯醛(HNEdGuo)。暴露于TCDD(10μg/kg/天)在31周和53周时显著诱导1,N - εdAdo,而未观察到8 - 氧代 - dGuo增加。暴露于三元混合物(TEQ 10μg/kg/天)后,在所有时间点均观察到8 - 氧代 - dGuo和1,N - εdAdo显著增加。暴露于TCDD 53周仅显著增加1,N - εdAdo,而N,3 - εG和7 - OEG的增加仅在最高剂量组(10μg/kg/天)中发现。暴露于三元混合物53周对任何暴露组(TEQ 0、22、46或10μg/kg/天)中的N,3 - εG均无影响,而1,N - εdAdo(所有剂量组)、8 - 氧代 - dGuo(46和10μg/kg/天)和7 - OEG(10μg/kg/天)均显著增加。虽然暴露于TCDD(10μg/kg/天)53周时1,N - εdGuo、MdGuo、AcrdGuo或CrdGuo未观察到显著增加,但在暴露于三元混合物(TEQ 10μg/kg/天)的动物中所有这些均显著诱导。这些氧化DNA产物数据表明,简单的TEF方法不能用于评估DLCs诱导的多种毒性效应模式。