Chappell Grace, Kobets Tetyana, O'Brien Bridget, Tretyakova Natalia, Sangaraju Dewakar, Kosyk Oksana, Sexton Kenneth G, Bodnar Wanda, Pogribny Igor P, Rusyn Ivan
*Department of Environmental Sciences and Engineering, University of North Carolina, Chapel Hill, North Carolina 27599, Division of Biochemical Toxicology, National Center for Toxicological Research, FDA, Jefferson, Arkansas 72079 and Department of Medicinal Chemistry, University of Minnesota, Minneapolis, Minnesota 55455.
*Department of Environmental Sciences and Engineering, University of North Carolina, Chapel Hill, North Carolina 27599, Division of Biochemical Toxicology, National Center for Toxicological Research, FDA, Jefferson, Arkansas 72079 and Department of Medicinal Chemistry, University of Minnesota, Minneapolis, Minnesota 55455 *Department of Environmental Sciences and Engineering, University of North Carolina, Chapel Hill, North Carolina 27599, Division of Biochemical Toxicology, National Center for Toxicological Research, FDA, Jefferson, Arkansas 72079 and Department of Medicinal Chemistry, University of Minnesota, Minneapolis, Minnesota 55455.
Toxicol Sci. 2014 Dec;142(2):375-84. doi: 10.1093/toxsci/kfu191. Epub 2014 Sep 18.
1,3-Butadiene (BD), a widely used industrial chemical and a ubiquitous environmental pollutant, is a known human carcinogen. Although genotoxicity is an established mechanism of the tumorigenicity of BD, epigenetic effects have also been observed in livers of mice exposed to the chemical. To better characterize the diverse molecular mechanisms of BD tumorigenicity, we evaluated genotoxic and epigenotoxic effects of BD exposure in mouse tissues that are target (lung and liver) and non-target (kidney) for BD-induced tumors. We hypothesized that epigenetic alterations may explain, at least in part, the tissue-specific differences in BD tumorigenicity in mice. We evaluated the level of N-7-(2,3,4-trihydroxybut-1-yl)guanine adducts and 1,4-bis-(guan-7-yl)-2,3-butanediol crosslinks, DNA methylation, and histone modifications in male C57BL/6 mice exposed to filtered air or 425 ppm of BD by inhalation (6 h/day, 5 days/week) for 2 weeks. Although DNA damage was observed in all three tissues of BD-exposed mice, variation in epigenetic effects clearly existed between the kidneys, liver, and lungs. Epigenetic alterations indicative of genomic instability, including demethylation of repetitive DNA sequences and alterations in histone-lysine acetylation, were evident in the liver and lung tissues of BD-exposed mice. Changes in DNA methylation were insignificant in the kidneys of treated mice, whereas marks of condensed heterochromatin and transcriptional silencing (histone-lysine trimethylation) were increased. These modifications may represent a potential mechanistic explanation for the lack of tumorigenesis in the kidney. Our results indicate that differential tissue susceptibility to chemical-induced tumorigenesis may be attributed to tissue-specific epigenetic alterations.
1,3 - 丁二烯(BD)是一种广泛使用的工业化学品,也是一种普遍存在的环境污染物,是已知的人类致癌物。虽然遗传毒性是BD致瘤性的既定机制,但在接触该化学品的小鼠肝脏中也观察到了表观遗传效应。为了更好地表征BD致瘤性的多种分子机制,我们评估了BD暴露在BD诱导肿瘤的靶组织(肺和肝)和非靶组织(肾)中的遗传毒性和表观遗传毒性效应。我们假设表观遗传改变可能至少部分解释了小鼠BD致瘤性的组织特异性差异。我们评估了雄性C57BL / 6小鼠吸入过滤空气或425 ppm BD(每天6小时,每周5天)2周后,N - 7 -(2,3,4 - 三羟基丁 - 1 - 基)鸟嘌呤加合物和1,4 - 双 -(鸟嘌呤 - 7 - 基)-2,3 - 丁二醇交联物的水平、DNA甲基化和组蛋白修饰。虽然在BD暴露小鼠的所有三个组织中都观察到了DNA损伤,但肾、肝和肺之间的表观遗传效应明显存在差异。在BD暴露小鼠的肝和肺组织中,表明基因组不稳定的表观遗传改变很明显,包括重复DNA序列的去甲基化和组蛋白赖氨酸乙酰化的改变。在处理小鼠的肾脏中,DNA甲基化的变化不显著,而浓缩异染色质和转录沉默的标记(组蛋白赖氨酸三甲基化)增加。这些修饰可能是肾脏缺乏肿瘤发生的潜在机制解释。我们的结果表明,化学诱导肿瘤发生的组织易感性差异可能归因于组织特异性表观遗传改变。