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Accumulation of M1dG DNA adducts after chronic exposure to PCBs, but not from acute exposure to polychlorinated aromatic hydrocarbons.长期暴露于多氯联苯后会积累M1dG DNA加合物,但急性暴露于多氯代芳烃则不会。
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2
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3
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本文引用的文献

1
Toxicology and carcinogenesis studies of a mixture of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) (Cas No. 1746-01-6), 2,3,4,7,8-pentachlorodibenzofuran (PeCDF) (Cas No. 57117-31-4), and 3,3',4,4',5-pentachlorobiphenyl (PCB 126) (Cas No. 57465-28-8) in female Harlan Sprague-Dawley rats (gavage studies).2,3,7,8-四氯二苯并-对-二噁英(TCDD)(化学物质登记号1746-01-6)、2,3,4,7,8-五氯二苯并呋喃(PeCDF)(化学物质登记号57117-31-4)和3,3',4,4',5-五氯联苯(多氯联苯126)(化学物质登记号57465-28-8)混合物对雌性Harlan Sprague-Dawley大鼠的毒理学和致癌性研究(灌胃研究)
Natl Toxicol Program Tech Rep Ser. 2006 Sep(526):1-180.
2
Toxicology and carcinogenesis studies of a binary mixture of 3,3',4,4',5-pentachlorobiphenyl (PCB 126) (Cas No. 57465-28-8) and 2,2',4,4',5,5'-hexachlorobiphenyl (PCB 153) (CAS No. 35065-27-1) in female Harlan Sprague-Dawley rats (gavage studies).3,3',4,4',5-五氯联苯(PCB 126)(化学物质登记号:57465-28-8)与2,2',4,4',5,5'-六氯联苯(PCB 153)(化学物质登记号:35065-27-1)二元混合物对雌性哈兰·斯普拉格-道利大鼠的毒理学及致癌性研究(灌胃研究)
Natl Toxicol Program Tech Rep Ser. 2006 Aug(530):1-258.
3
Toxicology and carcinogenesis studies of 2,3,4,7,8-pentachlorodibenzofuran (PeCDF) (Cas No. 57117-31-4) in female Harlan Sprague-Dawley rats (gavage studies).2,3,4,7,8-五氯二苯并呋喃(PeCDF)(化学物质登记号:57117-31-4)对雌性哈兰·斯普拉格-道利大鼠的毒理学及致癌性研究(灌胃研究)
Natl Toxicol Program Tech Rep Ser. 2006 Sep(525):1-198.
4
NTP technical report on the toxicology and carcinogenesis studies of 2,2',4,4',5,5'-hexachlorobiphenyl (PCB 153) (CAS No. 35065-27-1) in female Harlan Sprague-Dawley rats (Gavage studies).国家毒理学计划关于2,2',4,4',5,5'-六氯联苯(多氯联苯153)(化学物质登记号:35065-27-1)对雌性哈兰·斯普拉格-道利大鼠毒理学及致癌性研究的技术报告(灌胃研究)
Natl Toxicol Program Tech Rep Ser. 2006 May(529):4-168.
5
NTP technical report on the toxicology and carcinogenesis studies of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) (CAS No. 1746-01-6) in female Harlan Sprague-Dawley rats (Gavage Studies).美国国家毒理学计划(NTP)关于2,3,7,8-四氯二苯并对二恶英(TCDD)(化学物质登记号:1746-01-6)对雌性哈兰·斯普拉格-道利大鼠毒理学及致癌性研究的技术报告(灌胃研究)
Natl Toxicol Program Tech Rep Ser. 2006 Apr(521):4-232.
6
The 2005 World Health Organization reevaluation of human and Mammalian toxic equivalency factors for dioxins and dioxin-like compounds.2005年世界卫生组织对二噁英及二噁英类化合物的人类和哺乳动物毒性当量因子的重新评估。
Toxicol Sci. 2006 Oct;93(2):223-41. doi: 10.1093/toxsci/kfl055. Epub 2006 Jul 7.
7
NTP toxicology and carcinogenesis studies of 3,3',4,4',5-pentachlorobiphenyl (PCB 126) (CAS No. 57465-28-8) in female Harlan Sprague-Dawley rats (Gavage Studies).3,3',4,4',5-五氯联苯(PCB 126)(化学物质登记号:57465-28-8)对雌性哈兰斯普拉格-道利大鼠的NTP毒理学与致癌性研究(灌胃研究)
Natl Toxicol Program Tech Rep Ser. 2006 Jan(520):4-246.
8
Pyrimido[1,2-a]-purin-10(3H)-one, M1G, is less prone to artifact than base oxidation.嘧啶并[1,2 - a] - 嘌呤 - 10(3H) - 酮,即M1G,比碱基氧化更不易产生假象。
Nucleic Acids Res. 2005 Nov 10;33(19):6426-34. doi: 10.1093/nar/gki944. Print 2005.
9
Formation of M1G-dR from endogenous and exogenous ROS-inducing chemicals.由内源性和外源性活性氧诱导化学物质形成M1G-dR。
Free Radic Biol Med. 2005 Oct 15;39(8):1021-9. doi: 10.1016/j.freeradbiomed.2005.05.018.
10
Analysis of M1G-dR in DNA by aldehyde reactive probe labeling and liquid chromatography tandem mass spectrometry.通过醛反应性探针标记和液相色谱串联质谱法分析DNA中的M1G-dR
Chem Res Toxicol. 2005 Jan;18(1):51-60. doi: 10.1021/tx049853l.

长期暴露于多氯联苯后会积累M1dG DNA加合物,但急性暴露于多氯代芳烃则不会。

Accumulation of M1dG DNA adducts after chronic exposure to PCBs, but not from acute exposure to polychlorinated aromatic hydrocarbons.

作者信息

Jeong Yo-Chan, Walker Nigel J, Burgin Deborah E, Kissling Grace, Gupta Mayetri, Kupper Lawrence, Birnbaum Linda S, Swenberg James A

机构信息

Department of Environmental Sciences and Engineering, University of North Carolina at Chapel Hill, NC 27599, USA.

出版信息

Free Radic Biol Med. 2008 Sep 1;45(5):585-91. doi: 10.1016/j.freeradbiomed.2008.04.043. Epub 2008 May 15.

DOI:10.1016/j.freeradbiomed.2008.04.043
PMID:18534201
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC2570591/
Abstract

Oxidative DNA damage is one of the key events thought to be involved in mutation and cancer. The present study examined the accumulation of M1dG, 3-(2'-deoxy-beta-D-erythro-pentofuranosyl)-pyrimido[1,2-a]-purin-10(3H)-one, DNA adducts after single dose or 1-year exposure to polyhalogenated aromatic hydrocarbons (PHAH) in order to evaluate the potential role of oxidative DNA damage in PHAH toxicity and carcinogenicity. The effect of PHAH exposure on the number of M1dG adducts was explored initially in female mice exposed to a single dose of either 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) or a PHAH mixture. This study demonstrated that a single exposure to PHAH had no significant effect on the number of M1dG adducts compared to the corn oil control group. The role of M1dG adducts in polychlorinated biphenyl (PCB)-induced toxicity and carcinogenicity was further investigated in rats exposed for a year to PCB 153, PCB 126, or a mixture of the two. PCB 153, at doses up to 3000 microg/kg/day, had no significant effect on the number of M1dG adducts in liver and brain tissues from the exposed rats compared to controls. However, 1000 ng/kg/day of PCB 126 resulted in M1dG adduct accumulation in the liver. More importantly, coadministration of equal proportions of PCB 153 and PCB 126 resulted in dose-dependent increases in M1dG adduct accumulation in the liver from 300 to 1000 ng/kg/day of PCB 126 with 300-1000 microg/kg/day of PCB 153. Interestingly, the coadministration of different amounts of PCB 153 with fixed amounts of PCB 126 demonstrated more M1dG adduct accumulation with higher doses of PCB 153. These results are consistent with the results from cancer bioassays that demonstrated a synergistic effect between PCB 126 and PCB 153 on toxicity and tumor development. In summary, the results from the present study support the hypothesis that oxidative DNA damage plays a key role in toxicity and carcinogenicity following long-term PCB exposure.

摘要

氧化性DNA损伤被认为是参与突变和癌症发生的关键事件之一。本研究检测了单剂量或经1年多卤代芳烃(PHAH)暴露后M1dG(3-(2'-脱氧-β-D-赤藓糖基)-嘧啶并[1,2-a]嘌呤-10(3H)-酮)DNA加合物的积累情况,以评估氧化性DNA损伤在PHAH毒性和致癌性中的潜在作用。最初在暴露于单剂量2,3,7,8-四氯二苯并-对-二噁英(TCDD)或PHAH混合物的雌性小鼠中探究PHAH暴露对M1dG加合物数量的影响。该研究表明,与玉米油对照组相比,单次暴露于PHAH对M1dG加合物数量无显著影响。在暴露于PCB 153、PCB 126或二者混合物1年的大鼠中,进一步研究了M1dG加合物在多氯联苯(PCB)诱导的毒性和致癌性中的作用。与对照组相比,剂量高达3000μg/kg/天的PCB 153对暴露大鼠肝脏和脑组织中M1dG加合物数量无显著影响。然而,1000ng/kg/天的PCB 126导致肝脏中M1dG加合物积累。更重要的是,以相等比例共同给予PCB 153和PCB 126,随着PCB 126剂量从300至1000ng/kg/天以及PCB 153剂量从300至1000μg/kg/天,肝脏中M1dG加合物积累呈剂量依赖性增加。有趣的是,将不同量的PCB 153与固定量的PCB 126共同给予时,随着PCB 153剂量增加,M1dG加合物积累更多。这些结果与癌症生物测定结果一致,后者表明PCB 126和PCB 153在毒性和肿瘤发生方面具有协同作用。总之,本研究结果支持以下假设:长期PCB暴露后,氧化性DNA损伤在毒性和致癌性中起关键作用。