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金头鲷(Sparus aurata)暴露于水体和饲料中的苯并(a)芘及2,3,7,8-四氯二苯并对二恶英后CYP1A的细胞分布及诱导:免疫组织化学方法

Cellular distribution and induction of CYP1A following exposure of gilthead seabream, Sparus aurata, to waterborne and dietary benzo(a)pyrene and 2,3,7,8-tetrachlorodibenzo-p-dioxin: an immunohistochemical approach.

作者信息

Ortiz-Delgado J B, Segner H, Sarasquete C

机构信息

Institute of Marine Sciences of Andalucía, CSIC, Polígono Río San Pedro Apdo, Oficial, 11510 Puerto Real, Cádiz, Spain.

出版信息

Aquat Toxicol. 2005 Oct 15;75(2):144-61. doi: 10.1016/j.aquatox.2005.07.010.

DOI:10.1016/j.aquatox.2005.07.010
PMID:16139902
Abstract

The present study aimed to investigate cellular expression of cytochrome P4501A (CYP1A) protein in the seabream, Sparus aurata, exposed to one of two CYP1A-inducing contaminants, benzo(a)pyrene (B(a)P) or 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). Male adult fish were exposed to several concentrations of TCDD or B(a)P either via water or via food. Fish were sampled after 0, 5, 10, 15 or 20 days of treatment and the time- and concentration-dependent induction of CYP1A protein in cells and tissues was studied using immunohistochemistry. A general site of CYP1A induction was the vascular endothelium. Aqueous exposures resulted in elevation of CYP1A immunoreactivity in gill pillar cells, heart endothelium, renal tubular epithelium, hepatocytes, and gut mucosal epithelium. In contrast, dietary exposure resulted in strong CYP1A immunostaining in gut epithelium but in only mild to moderate staining elsewhere. Both B(a)P and TCDD induced CYP1A in similar cellular response patterns in most organs examined, although TCDD generally led to higher staining intensity and frequency (i.e. the number of CYP1A-positive cells within an organ), an effect that is likely to be related to compound-specific differences in induction potency, metabolism and penetration. Contaminant-specific staining patterns were observed in the gills, where TCDD exposure evoked CYP1A immunostaining in the endothelial pillar cells, while B(a)P induced CYP1A staining in the branchial epithelial cells. This work points to the importance of immunohistochemical identification of cell-specific CYP1A responses in assessing the toxicology of CYP1A-inducing xenobiotics.

摘要

本研究旨在调查暴露于两种诱导细胞色素P4501A(CYP1A)的污染物之一——苯并(a)芘(B(a)P)或2,3,7,8-四氯二苯并对二恶英(TCDD)的金头鲷中CYP1A蛋白的细胞表达情况。成年雄性鱼通过水或食物暴露于几种浓度的TCDD或B(a)P。在处理0、5、10、15或20天后对鱼进行采样,并使用免疫组织化学研究细胞和组织中CYP1A蛋白的时间和浓度依赖性诱导情况。CYP1A诱导的一个常见部位是血管内皮。通过水暴露导致鳃柱状细胞、心脏内皮、肾小管上皮、肝细胞和肠道黏膜上皮中CYP1A免疫反应性升高。相比之下,通过食物暴露导致肠道上皮中CYP1A免疫染色强烈,但在其他部位仅为轻度至中度染色。在大多数检查的器官中,B(a)P和TCDD均以相似的细胞反应模式诱导CYP1A,尽管TCDD通常导致更高的染色强度和频率(即器官内CYP1A阳性细胞的数量),这种效应可能与诱导效力、代谢和渗透方面的化合物特异性差异有关。在鳃中观察到污染物特异性染色模式,TCDD暴露引起内皮柱状细胞中CYP1A免疫染色,而B(a)P诱导鳃上皮细胞中CYP1A染色。这项工作指出了在评估诱导CYP1A的外源化学物的毒理学时,通过免疫组织化学鉴定细胞特异性CYP1A反应的重要性。

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