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二噁英染毒模型小鼠相关受体及代谢酶的分布 被引量:1

Distribution of dioxin receptors and metabolizing enzymes of 2,3, 7,8-tetrachlorodibenzo-p-dioxin exposure mice models
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摘要 目的 探讨引起小鼠早期妊娠毒性敏感与相关受体、代谢酶水平的关系,了解子宫组织的敏感性是否与二噁英(TCDD)代谢活化而导致局部毒性蓄积有关.方法 收集TCDD妊娠早期毒性模型小鼠的子宫、肝脏和肾脏组织,用免疫组织化学法对芳香碳氢化合物受体(AhR),受体核转位蛋白(ARNT)和细胞色素氧化酶(Cyp1a2)在组织细胞中分布进行检测.结果 正常妊娠小鼠的子宫、肝脏和肾脏组织细胞质有AhR、Cyp1a2弱阳性信号,细胞核内ARNT有强阳性信号.用不同浓度TCDD处理小鼠,各组织细胞质内的AhR阳性信号随浓度的提高而增加.50 ng/L剂量TCDD暴露使肝脏(18.038±3.0916,P<0.01),子宫(8.8140±1.4574,P<0.01)的AhR阳性面积比提高,以及吸光度(A)值显著升高(0.1143±0.0066,0.2399±0.0054,P<0.01) 而肾脏中2种指标均未见显著性差异.相同处理组Cyp1a2变化则主要表现在吸光度的变化,肝脏(0.2047±0.0150,0.31112±0.0107,P<0.01),子宫(0.1892±0.0232,0.3152±0.0432,P<0.05)和肾脏(0.2545±0.0202,0.3334±0.0168,P<0.05)A值均显著升高 组织细胞核内ARNT阳性吸光度在肝脏(0.7496±0.0469,0.2458±0.006,P<0.01)和子宫(0.4766±0.0359,0.2139±0.0253,P<0.01)显著下降,在肾脏则表现为阳性信号从细胞核进入细胞质.100 ng/L剂量TCDD暴露则引起所有组织AhR和Cyp1a2阳性显著增强 肝脏和子宫ARNT信号消失,肾脏中ARNT信号从核内转入细胞质.结论 肝脏、子宫和肾脏AhR和CYP1A2酶可受TCDD类物质诱导,细胞信号面积随TCDD暴露量的增加而增大 肝脏和子宫细胞核内的ARNT随TCDD暴露量的增加,细胞信号减弱至消失,但肾脏ARNT进入胞质.说明子宫与肝脏具有相同的TCDD诱导特征,具有活化内外源性有毒化合物的功能,这应该是引起小鼠早期生殖毒性的原因之一. Objective To investigate relationships between high sensitivity to toxicity in NIH mice during early pregnancy and level of receptors and metabolizing enzymes to 2,3,7,8-tetrachlorodibenzo-pdioxin (TCDD), and to elucidate whether the sensitivity is associated with the TCDD accumulation induced by metabolic activation in the uterus. Methods Liver, kidney and uterus tissues in mice models of toxicity exposure during the early pregnancy were collected and fixed. Distribution of the aryl hydrocarbon receptor (AhR), aryl hydrocarbon receptor nuclear translocator (ARNT) and cytochrome P4501a2 (Cyp1a2) was then determined by immunohistochemical staining. Results In unexposed mice, the tissues of liver, kidney and uterus, displayed weak-positive signal of AhR and Cyp1a2 in cytoplasma and strong-positive signal of ARNT in the nuclei. The positive signal of cytoplasma AhR in these three types of tissues was enhanced to varying degrees along with increasing dose of TCCD exposure. Exposure to 50 ng/L TCDD increased both the percentage of AhR-positive area in liver (18.038±3.0916,P〈0.01)and uterus (8.8140±1.4574,P〈0.01) and optic density of AhR signals(0.1143±0.0066,0.2399±0.0054, P〈0.01 ), while no change was found in kidney tissues. With the same treatment, changes in Cyp1a2 were mainly manifested by significant increase in optic density of Cypla2 signals in liver (0.31112±0.0107, P〈0.01 ), uterus (0.3152±0.0432, P〈0.05) and kidney (0.3334±0.0168, P〈0.05 ), while the optic density of positive ARNT signals in nuclei decreased significantly in liver (0.2458±0.006, P〈0.01 )and uterus(0.2139±0.0253, P〈0.01 ), was largely unchanged but associated with a translocation from nuclei to cytoplasma in kidney. Exposure to 100 ng/L TCDD resulted in enhanced AhR and Cyp1a2 positive signals in all the tissues examined, abolition of ARNT signals in liver and uterus,and traslocation of ARNT signal from nuclei to cytoplasma in the kidney. Conclusions The AhR and Cyp1a2 in liver, uterus and kidney induced by TCDD-like agents may show increasing percentage of signalpositive area along with higher dose of TCDD exposure. In contrast, ARNT signal is weakened and subsequently abolished in nuclei of liver and uterus cells, and displays a traslocation from nuclei to cytoplasma in the kidney. These findings indicate that liver and uterus may share the same TCDD-induced signaling pathway which activates the exogenous toxic agents and should be one of the factors causing sensitivity to TCDD during early pregnancy in mice.
出处 《中华生物医学工程杂志》 CAS 2010年第5期461-467,共7页 Chinese Journal of Biomedical Engineering
基金 广州医学院课题基金(2006ZR003) 广东省实验动物重点实验室开放课题基金(2007A060101002)
关键词 二噁英 受体蛋白 免疫组织化学 组织分布 生殖毒性 Dioxin Receptor protein Immunohistochemistry Tissue distribution Reproductive toxicity
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参考文献13

  • 1Li B, Liu HY, Dai LJ, et al. The early embryo loss caused by 2, 3, 7, 8-tetrachlorodibenzo-p-dioxin may be related to the accumulation of this compound in the uterus. Reprod Toxicol, 2006, 21: 301-306.
  • 2黄莉,王建华,戴丽军,邱剑峰,吕嘉春,李冰.2,3,7,8,-四氯苯噁英对NIH小鼠早期妊娠和生殖激素的影响[J].环境科学学报,2005,25(1):94-98. 被引量:5
  • 3黄莉,王建华,戴丽军,刘寒英,邱剑峰,文端成,冯媛瑜,李冰.酵母基因报道系统检测环境二恶英类似物的污染[J].应用与环境生物学报,2004,10(4):493-496. 被引量:7
  • 4黄莉,吕嘉春,丘剑锋,刘寒英,戴丽军,李冰.妊娠小鼠子宫对2,3,7,8-四氯苯二噁英毒性的敏感性研究[J].环境科学学报,2005,25(3):334-339. 被引量:5
  • 5王卓,张万起.芳香烃受体核转位蛋白的结构及相关功能[J].生命科学,2007,19(1):73-77. 被引量:3
  • 6MARK EH, SIBEL IK, MIRIAM A. Molecular evolution of two vertebrate aryl hydrocarbon (dioxin) receptors (AHR1 andAHR2) and the PAS family. Proc Natl Acad Sci, 1997, 12: 13743-13748.
  • 7Abalos M, Abad E, Estevez A, et, al. Effects on growth andbiochemical responses in juvenile gilthead seabream "Sparus aurata" after long-term dietary exposure to low levels of dioxins.Chemosphere. 2008, 73: 303-310.
  • 8Charles A. Miller Ⅲ. A Human Aryl Hydrocarbon Receptor Signaling Pathway Constructed in Yeast Displays AdditiveResponses to Ligand Mixtures. Toxicol Appl Pharmacol, 1999, 160: 297-303.
  • 9Xu L, Li AP, Kaminski DL, et al. 2,3,7,8-Tetrachlorodibenzo- p- dioxin induction of cytoehrome P4501A in euhured rat andhuman hepatocytes. Chem Biol Interact, 2000, 124: 173-189.
  • 10Diliberto JJ, Akubue PI, Luebke RW, et al. Dose-response relationship of tissue distribution and induction of CYPlAl andCYP1A2 emzymatic activities following acute exposure to 2,3,7, 8- tetrachlorodibenzo-p-dioxin (TCDD) in mice. Toxical ApplPharmacol, 1995, 130: 197-208.

二级参考文献58

  • 1李灵军,蒋可.^(13)C同位素稀释法测定国产多氯联苯的2,3,7,8-TCDD毒性当量[J].环境科学学报,1995,15(4):433-439. 被引量:14
  • 2周炜,姜政.低氧诱导因子-1与消化道肿瘤的研究进展[J].世界华人消化杂志,2006,14(26):2620-2625. 被引量:5
  • 3[3]ICCVAM Evaluation of in vitro Test Methods For Detecting Potential Endocrine Disruptors: Estrogen Receptor and Androgen Receptor Binding and Transcriptional Activation Assays. NIH Publication No. 03-4503.May 2003
  • 4[4]Charles A. Miller Ⅲ. A human aryl hydrocarbon receptor signaling pathway constructed in yeast displays additive responses to ligand mixtures. Toxicol & Appl Pharmacol, 1999, 160: 297 ~ 303
  • 5[5]Charles A. Miller Ⅲ. Expression of the human aryl hydrocarbon receptor complex in yeast. J Biol Chem, 1997, 272(52): 32824 ~32829
  • 6[6]Hankinson O. The aryl hydrocarbon receptor complex. Annu Rev Pharmacol Toxicol, 1995, 35:307 ~ 340
  • 7[7]Schmidt JV, Bradfield CA. Ah receptor signaling pathways. Ann Rev Cell Dev Biol, 1996, 12:55 ~89
  • 8[8]Kimberly Silvers, Ellen A Rorke. TCDD and uterine function. In: Kenneth S Korach. Reproductive and Developmental Toxicology, 1998. 413~ 430
  • 9[9]van den Berg M, Birnbaum L, Bosveld BTC, et al. Toxic equivalency factors (TEFs) for PCBs, PCDDs, PCDFs for humans and wildlife. Environ Health Perspect , 1998, 106:775 ~ 792
  • 10[10]Beck H, Eckart K, Mather W, et al. PCDD and PCDF body burden from food intake in the Federal Republic of Germany. Chemosphere,1989, 18:417~424

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