Goggin Melissa, Anderson Chris, Park Soobong, Swenberg James, Walker Vernon, Tretyakova Natalia
Cancer Center and the Department of Medicinal Chemistry, University of Minnesota, 760E CCRB, 806 Mayo, 420 Delaware Street Southeast, Minneapolis, Minnesota 55455, USA.
Chem Res Toxicol. 2008 May;21(5):1163-70. doi: 10.1021/tx800051y. Epub 2008 Apr 29.
1,3-Butadiene (BD) is an important industrial chemical used in the manufacture of rubber and plastics as well as an environmental pollutant present in automobile exhaust and cigarette smoke. It is classified as a known human carcinogen based on the epidemiological evidence in occupationally exposed workers and its ability to induce tumors in laboratory animals. BD is metabolically activated to several reactive species, including 1,2,3,4-diepoxybutane (DEB), which is hypothesized to be the ultimate carcinogenic species due to its bifunctional electrophilic nature and its ability to form DNA-DNA and DNA-protein cross-links. While 1,4- bis-(guan-7-yl)-2,3,-butanediol ( bis-N7G-BD) is the only type of DEB-specific DNA adduct previously quantified in vivo, four regioisomeric guanine-adenine (G-A) cross-links have been observed in vitro: 1-(guan-7-yl)-4-(aden-1-yl)-2,3-butanediol (N7G-N1A-BD), 1-(guan-7-yl)-4-(aden-3-yl)-2,3-butanediol (N7G-N3A-BD), 1-(guan-7-yl)-4-(aden-7-yl)-2,3-butanediol (N7G-N7A-BD), and 1-(guan-7-yl)-4-(aden-6-yl)-2,3-butanediol (N7G-N (6)A-BD) ( Park ( 2004) Chem. Res. Toxicol. 17, 1638- 1651 ). The goal of the present work was to develop an isotope dilution HPLC-positive mode electrospray ionization-tandem mass spectrometry (HPLC-ESI (+)-MS/MS) method for the quantitative analysis of G-A DEB cross-links in DNA extracted from BD-exposed laboratory animals. In our approach, G-A butanediol conjugates are released from the DNA backbone by thermal or mild acid hydrolysis. Following solid-phase extraction, samples are subjected to capillary HPLC-ESI (+)-MS/MS analysis with (15)N 3, (13)C 1-labeled internal standards. The detection limit of our current method is 0.6-1.5 adducts per 10 (8) normal nucleotides. The new method was validated by spiking G-A cross-link standards (10 fmol each) into control mouse DNA (0.1 mg), followed by sample processing and HPLC-ESI (+)-MS/MS analysis. The accuracy and precision were calculated as 105 +/- 17% for N7G-N3A-BD, 102 +/- 25% for N7G-N7A-BD, and 79 +/- 11% for N7G-N (6)A-BD. The regioisomeric G-A DEB adducts were formed in a concentration-dependent manner in DEB-treated calf thymus DNA, with N7G-N1A-BD found in the highest amounts. Under physiological conditions, N7G-N1A-BD underwent Dimroth rearrangement to N7G-N (6)A-BD ( t 1/2 = 114 h), while hydrolytic deamination of N7G-N1A-BD to the corresponding hypoxanthine lesion was insignificant. We found that for in vivo samples, a greater sensitivity could be achieved if N7G-N1A-BD adducts were converted to the corresponding N7G-N (6)A-BD lesions by forced Dimroth rearrangement. Liver DNA extracted from female B6C3F1 mice that underwent inhalation exposure to 625 ppm BD for 2 weeks contained 3.1 +/- 0.6 N7G-N1A-BD adducts per 10 (8) nucleotides ( n = 5) (quantified as N7G-N (6)A-BD following base-induced Dimroth rearrangement), while the amounts of N7G-N3A-BD and N7G-N7A-BD were below the detection limit of our method. None of the G-A cross-links was present in control animals. The formation of N7G-N1A-BD cross-links may contribute to the induction of AT base pair mutations following exposure to BD. Quantitative methods presented here may be used not only for studies of biological significance in animal models but potentially to predict risk associated with human exposure to BD.
1,3 - 丁二烯(BD)是一种重要的工业化学品,用于制造橡胶和塑料,同时也是汽车尾气和香烟烟雾中的一种环境污染物。基于职业暴露工人的流行病学证据以及它在实验动物中诱发肿瘤的能力,BD被归类为已知的人类致癌物。BD经代谢活化生成多种活性物质,包括1,2,3,4 - 二环氧丁烷(DEB),由于其双功能亲电性质以及形成DNA - DNA和DNA - 蛋白质交联的能力,DEB被认为是最终的致癌物质。虽然1,4 - 双 -(鸟嘌呤 - 7 - 基)- 2,3 - 丁二醇(双 - N7G - BD)是此前唯一在体内定量的DEB特异性DNA加合物,但在体外已观察到四种区域异构体鸟嘌呤 - 腺嘌呤(G - A)交联:1 -(鸟嘌呤 - 7 - 基)- 4 -(腺嘌呤 - 1 - 基)- 2,3 - 丁二醇(N7G - N1A - BD)、1 -(鸟嘌呤 - 7 - 基)- 4 -(腺嘌呤 - 3 - 基)- 2,3 - 丁二醇(N7G - N3A - BD)、1 -(鸟嘌呤 - 7 - 基)- 4 -(腺嘌呤 - 7 - 基)- 2,3 - 丁二醇(N7G - N7A - BD)和1 -(鸟嘌呤 - 7 - 基)- 4 -(腺嘌呤 - 6 - 基)- 2,3 - 丁二醇(N7G - N(6)A - BD)(Park(2004)《化学研究毒理学》17, 1638 - 1651)。本研究的目的是开发一种同位素稀释高效液相色谱 - 正模式电喷雾电离 - 串联质谱法(HPLC - ESI(+) - MS/MS),用于定量分析从接触BD的实验动物提取的DNA中的G - A DEB交联。在我们的方法中,通过热或温和酸水解从DNA主链释放G - A丁二醇缀合物。经过固相萃取后,样品用(15)N 3、(13)C 1标记的内标进行毛细管HPLC - ESI(+) - MS/MS分析。我们当前方法的检测限为每10(8)个正常核苷酸0.6 - 1.5个加合物。通过将G - A交联标准品(各10 fmol)加入对照小鼠DNA(0.1 mg)中,然后进行样品处理和HPLC - ESI(+) - MS/MS分析,验证了新方法。计算得出N7G - N3A - BD的准确度和精密度为105±17%,N7G - N7A - BD为102±25%,N7G - N(6)A - BD为79±11%。在DEB处理的小牛胸腺DNA中,区域异构体G - A DEB加合物以浓度依赖方式形成,其中N7G - N1A - BD的含量最高。在生理条件下,N7G - N1A - BD发生迪莫特重排生成N7G - N(6)A - BD(半衰期t1/2 = 114 h),而N7G - N1A - BD水解脱氨生成相应的次黄嘌呤损伤不明显。我们发现,对于体内样品,如果通过强制迪莫特重排将N7G - N1A - BD加合物转化为相应的N7G - N(6)A - BD损伤,可以实现更高的灵敏度。从吸入625 ppm BD 2周的雌性B6C3F1小鼠提取的肝脏DNA,每10(8)个核苷酸含有3.1±0.6个N7G - N1A - BD加合物(n = 5)(在碱基诱导的迪莫特重排后定量为N7G - N(6)A - BD),而N7G - N3A - BD和N7G - N7A - BD的含量低于我们方法的检测限。对照动物中未发现任何G - A交联。N7G - N1A - BD交联的形成可能有助于接触BD后诱导AT碱基对突变。本文提出的定量方法不仅可用于动物模型的生物学意义研究,还可能用于预测与人类接触BD相关的风险。