DeCaprio A P, McMartin D N, O'Keefe P W, Rej R, Silkworth J B, Kaminsky L S
Fundam Appl Toxicol. 1986 Apr;6(3):454-63. doi: 10.1016/0272-0590(86)90219-8.
In contrast to the well-characterized acute toxicity of the environmental contaminant 2,3,7,8-tetrachlorodibenzo-p-dioxin (2,3,7,8-TCDD) in the guinea pig, the effects of prolonged po exposure in this species are unknown. The present report describes the results of administration to guinea pigs of 2,3,7,8-TCDD in the feed at levels of 0, 2, 10, 76, or 430 ppt for up to 90 days. Additional aims were to examine recovery following prolonged 2,3,7,8-TCDD exposure in the guinea pig and to generate data to facilitate comparison of the previously reported toxicity of a transformer fluid pyrolysate with that of pure 2,3,7,8-TCDD. Animals receiving 430 ppt 2,3,7,8-TCDD exhibited body weight loss, thymic atrophy, liver enlargement, and 60% mortality by Day 46 (males) and by Day 60 (females), when surviving animals in this group were sacrificed. Total 2,3,7,8-TCDD consumption was approximately 1.3 and 1.9 micrograms/kg, respectively. Animals receiving 76 ppt 2,3,7,8-TCDD for 90 days (total 0.44 microgram/kg) exhibited a decreased rate of body weight gain and increased relative (to body) liver weights. Male animals also displayed a reduction in relative thymus weights and elevated serum triglycerides, while females exhibited hepatocellular cytoplasmic inclusion bodies and lowered serum alanine aminotransferase activities. Toxic effects were generally similar to those observed after acute 2,3,7,8-TCDD administration. No dose-related alterations were seen in animals receiving either 10 ppt (total 0.06 micrograms/kg) or 2 ppt (total 0.01 micrograms/kg) for 90 days, establishing a no-observed-effect level of approximately 0.65 ng 2,3,7,8-TCDD/kg/day. In the recovery study, groups of guinea pigs were administered 430 ppt 2,3,7,8-TCDD for 11, 21, or 35 days and then allowed to recover for an additional 79, 69, or 55 days, respectively. Treatment-related mortality in each group was 0, 10, and 70%, respectively, by Day 90. An effective LD50 of 0.8 microgram 2,3,7,8-TCDD/kg for prolonged exposure was calculated on the basis of these results, a value lower than those previously reported from this laboratory for acute exposure. The results also suggested a possible lowering of the body weight "set point" following 2,3,7,8-TCDD exposure. Comparison of the present findings with those previously reported for a transformer fluid pyrolysate containing a mixture of polychlorinated aromatic species indicated both a greater variety of toxic effects and flatter dose-response relationships for the pyrolysate in the guinea pig.
与环境污染物2,3,7,8 - 四氯二苯并 - p - 二恶英(2,3,7,8 - TCDD)在豚鼠中已得到充分表征的急性毒性相反,该物质在豚鼠中长期经口暴露的影响尚不清楚。本报告描述了以0、2、10、76或430 ppt的水平在饲料中给豚鼠投喂2,3,7,8 - TCDD长达90天的结果。其他目的是研究豚鼠在长期暴露于2,3,7,8 - TCDD后的恢复情况,并生成数据以便于比较先前报道的变压器油热解产物与纯2,3,7,8 - TCDD的毒性。接受430 ppt 2,3,7,8 - TCDD的动物出现体重减轻、胸腺萎缩、肝脏肿大,到第46天(雄性)和第60天(雌性)时死亡率达60%,此时该组存活的动物被处死。2,3,7,8 - TCDD的总摄入量分别约为1.3和1.9微克/千克。接受76 ppt 2,3,7,8 - TCDD处理90天(总摄入量0.44微克/千克)的动物体重增加速率降低,相对(相对于体重)肝脏重量增加。雄性动物还表现出相对胸腺重量降低和血清甘油三酯升高,而雌性动物出现肝细胞胞质内包涵体且血清丙氨酸转氨酶活性降低。毒性作用总体上与急性给予2,3,7,8 - TCDD后观察到的相似。接受10 ppt(总摄入量0.06微克/千克)或2 ppt(总摄入量0.01微克/千克)处理90天的动物未观察到剂量相关的变化,确定未观察到效应水平约为0.65纳克2,3,7,8 - TCDD/千克/天。在恢复研究中,将豚鼠分组给予430 ppt 2,3,7,8 - TCDD 11、21或35天,然后分别再恢复79、69或55天。到第90天,每组与处理相关的死亡率分别为0、10%和70%。根据这些结果计算出长期暴露的2,3,7,8 - TCDD的有效半数致死剂量为0.8微克/千克,该值低于本实验室先前报道的急性暴露值。结果还表明,2,3,7,8 - TCDD暴露后可能会降低体重“设定点”。将本研究结果与先前报道的含有多氯代芳烃混合物的变压器油热解产物的结果进行比较,表明热解产物在豚鼠中产生的毒性作用种类更多,剂量 - 反应关系更平缓。