Henry T R, Spitsbergen J M, Hornung M W, Abnet C C, Peterson R E
School of Pharmacy, University of Wisconsin, Madison 53706, USA.
Toxicol Appl Pharmacol. 1997 Jan;142(1):56-68. doi: 10.1006/taap.1996.8024.
Toxicity and histopathology of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in zebrafish (Danio rerio) early life stages was characterized from 12 to 240 hr postfertilization (hpf) following water-borne exposure of newly fertilized eggs. TCDD did not increase egg mortality (0-48 hpf), nor did it affect time to hatching (48-96 hpf). Egg doses of 1.5 ng [3H]TCDD/g or greater elicited toxic responses in zebrafish larvae. Pericardial edema and craniofacial malformations were first observed at 72 hpf, followed by the onset of yolk sac edema (96 hpf) and mortality (132 hpf). At 240 hpf the ED50s for pericardial edema, yolk sac edema, and craniofacial malformations were 2.2, 2.1, and 1.9 ng [3H]TCDD/g egg, respectively. The LD50, determined at 240 hpf, was 2.5 ng [3H]TCDD/g egg. Severe hemodynamic changes, observed as slowed blood flow in vascular beds of the trunk, head, and gills and slowed heart rate, occurred in TCDD-treated zebrafish prior to or coincident with the onset of gross signs of toxicity. Histological examination of TCDD-treated zebrafish revealed a variety of epithelial tissue lesions including arrested gill development and ballooning degeneration and/or necrosis of the renal tubules, hepatocytes, pancreas, and all major brain regions. Mesenchymal tissue lesions included subcutaneous edema in the head, trunk, and yolk sac, edema of the pericardium and skeletal muscle, and underdevelopment of the swim bladder. This demonstration of zebrafish responsiveness to TCDD early life stage toxicity coupled with the considerable information on developmental biology and genetics of zebrafish provides a foundation for future investigations into the mechanism of TCDD developmental toxicity.
在新受精的鱼卵经水体暴露后,对斑马鱼(Danio rerio)幼鱼期(受精后12至240小时)2,3,7,8 - 四氯二苯并 - p - 二恶英(TCDD)的毒性和组织病理学特征进行了研究。TCDD未增加鱼卵死亡率(0至48小时),也未影响孵化时间(48至96小时)。鱼卵剂量为1.5纳克[³H]TCDD/克或更高时,斑马鱼幼鱼会出现毒性反应。心包水肿和颅面畸形在72小时首次观察到,随后出现卵黄囊水肿(96小时)和死亡(132小时)。在240小时时,心包水肿、卵黄囊水肿和颅面畸形的半数效应剂量(ED50)分别为2.2、2.1和1.9纳克[³H]TCDD/克鱼卵。在240小时测定的半数致死剂量(LD50)为2.5纳克[³H]TCDD/克鱼卵。在TCDD处理的斑马鱼出现明显毒性体征之前或同时,观察到严重的血液动力学变化,表现为躯干、头部和鳃血管床的血流减慢以及心率减慢。对TCDD处理的斑马鱼进行组织学检查发现了多种上皮组织病变,包括鳃发育停滞以及肾小管、肝细胞、胰腺和所有主要脑区的气球样变性和/或坏死。间充质组织病变包括头部、躯干和卵黄囊的皮下水肿、心包和骨骼肌水肿以及鳔发育不全。斑马鱼对TCDD幼鱼期毒性的反应证明,再加上关于斑马鱼发育生物学和遗传学的大量信息,为未来研究TCDD发育毒性机制奠定了基础。