Troxel C M, Buhler D R, Hendricks J D, Bailey G S
Toxicology Program, Oregon State University, Corvallis, Oregon, 97331, USA.
Toxicol Appl Pharmacol. 1997 Sep;146(1):69-78. doi: 10.1006/taap.1997.8219.
This study investigated the inductive response of cytochrome P4501A (CYP1A) in the zebrafish (Danio rerio) following exposure to Aroclor 1254, beta-naphthoflavone (betaNF), and 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and then investigated TCDD modulation of aflatoxin B1 (AFB1) metabolism and hepatic AFB1-DNA adduction. Aroclor 1254 fed at 500 ppm for 1 to 9 days or intraperitoneal (ip) injection of 75-200 mg Aroclor 1254/kg body weight failed to induce CYP1A protein or associated 7-ethoxyresorufin-O-deethylase (EROD) activity. By contrast, dietary betaNF at 500 ppm for 3 or 7 days induced CYP1A protein and EROD activity approximately threefold above controls. A single ip injection of 150 mg/kg betaNF showed maximal induction of CYP1A protein and EROD activity near 24 hr, both of which decreased to control levels during the next 6 days. Single ip administration of 25, 50, 100, or 150 mg betaNF/kg body weight provided dose-responsive increases in CYP1A and EROD activity. Dietary exposure to 0.75 ppm TCDD for 3 days also significantly induced CYP1A and EROD. The effect of TCDD on the metabolism of [3H]AFB1 in zebrafish was then investigated. The major [3H]AFB1 metabolites excreted in water over 24 hr in the control group were aflatoxicol, aflatoxicol-glucuronide, and parent AFB1. By contrast, the predominant metabolites in the TCDD-pretreated group were aflatoxicol-M1-glucuronide, aflatoxicol, aflatoxin M1 plus aflatoxicol-M1 (unresolved), aflatoxicol-glucuronide, and parent AFB1. Surprisingly, hepatic AFB1-DNA adduction was approximately fourfold higher in the TCDD treated group than in controls. This significant difference could not be explained by increased capacity for bioactivation of AFB1 as measured by an in vitro AFB1-exo-8, 9-epoxide trapping assay. However, it was demonstrated that both control and induced zebrafish have high capacity to bioactivate aflatoxin M1 to a reactive intermediate, such that secondary bioactivation of this genotoxic intermediate may be responsible for the increased DNA binding.
本研究调查了斑马鱼(Danio rerio)暴露于多氯联苯混合物1254(Aroclor 1254)、β-萘黄酮(βNF)和2,3,7,8-四氯二苯并对二恶英(TCDD)后细胞色素P4501A(CYP1A)的诱导反应,然后研究了TCDD对黄曲霉毒素B1(AFB1)代谢和肝脏AFB1-DNA加合物的调节作用。以500 ppm的剂量喂食Aroclor 1254 1至9天,或腹腔注射75 - 200 mg Aroclor 1254/kg体重,均未能诱导CYP1A蛋白或相关的7-乙氧基异吩恶唑酮-O-脱乙基酶(EROD)活性。相比之下,以500 ppm的剂量喂食βNF 3或7天,诱导的CYP1A蛋白和EROD活性比对照组高约三倍。单次腹腔注射150 mg/kg βNF在24小时左右显示出CYP1A蛋白和EROD活性的最大诱导,在接下来的6天内两者均降至对照水平。单次腹腔注射25、50、100或150 mg βNF/kg体重可使CYP1A和EROD活性呈剂量依赖性增加。以0.75 ppm的剂量喂食TCDD 3天也显著诱导了CYP1A和EROD。然后研究了TCDD对斑马鱼中[3H]AFB1代谢的影响。对照组在24小时内排泄到水中的主要[3H]AFB1代谢产物是黄曲霉毒素醇、黄曲霉毒素醇-葡萄糖醛酸苷和母体AFB1。相比之下,TCDD预处理组中的主要代谢产物是黄曲霉毒素醇-M1-葡萄糖醛酸苷、黄曲霉毒素醇、黄曲霉毒素M1加黄曲霉毒素醇-M1(未分离)、黄曲霉毒素醇-葡萄糖醛酸苷和母体AFB1。令人惊讶的是,TCDD处理组中的肝脏AFB1-DNA加合物比对照组高约四倍。通过体外AFB1-外-8,9-环氧化物捕获试验测量的AFB1生物活化能力增加无法解释这种显著差异。然而,已证明对照和诱导的斑马鱼都有很高的能力将黄曲霉毒素M1生物活化为反应性中间体,因此这种遗传毒性中间体的二次生物活化可能是DNA结合增加的原因。