Hébert C D, Harris M W, Elwell M R, Birnbaum L S
Experimental Toxicology Branch, National Institute of Environmental Health Sciences, Research Triangle Park, North Carolina 27709.
Toxicol Appl Pharmacol. 1990 Feb;102(2):362-77. doi: 10.1016/0041-008x(90)90033-q.
2,3,7,8-Tetrachlorodibenzo-p-dixoin 2,3,4,7,8-pentachlorodibenzofuran (PCDF), and 1,2,3,4,7,8-hexachlorodibenzofuran (HCDF) are highly toxic members of a class of environmental contaminants, the polychlorinated aromatic hydrocarbons (PCAH), which exhibit a similar and highly characteristic spectrum of toxic effects. For purposes of risk assessment, it is important to be able to make accurate estimates of the relative potency of these and related compounds. Previous investigations have indicated that, in acute exposure or in vitro studies, PCDF is approximately 0.1 times as toxic and HCDF is approximately 0.01 times as toxic as TCDD. In this study, we compared the relative toxicity and tumor-promoting abilities of TCDD, PCDF, and HCDF in hairless mouse skin. Female hairless mice (HRS/J hr/hr) were treated dermally with the initiator MNNG, then dosed twice weekly for 20 weeks with acetone, TCDD (2.5-10 ng/mouse/dose), PCDF (25-100 ng/mouse/dose), or HCDF (250-1000 ng/mouse/dose) as promoter. TCDD, PCDF, and HCDF were all potent promoters for the induction of squamous cell papillomas. There was, however, no difference in the incidence or multiplicity of papilloma formation between groups. The same doses of the three PCAH, in the absence of initiator, induced no skin papillomas. TCDD produced a significant increase in liver:body weight ratio (p less than 0.001) at all doses and a decrease in thymus:body weight ratio at a dose of 10 ng (p less than 0.001). Mice treated with PCDF and HCDF had marked thymic and splenic involution, liver hypertrophy, mucous cell hyperplasia in the fundic portion of the glandular stomach, and loss of body weight. PCDF and HCDF produced a greater incidence and severity of dermatotoxic effects than TCDD. Based on data for dermal toxicity and changes in body weight and organ weights, PCDF is estimated to be 0.2 to 0.4 times, and HCDF 0.08 to 0.16 times, as toxic as TCDD following repeated dermal exposure. Therefore, toxic equivalence factors generated using data from acute and/or in vitro studies may underestimate the risk from repeated low-dose exposures to these compounds.
2,3,7,8 - 四氯二苯并 - 对 - 二噁英、2,3,4,7,8 - 五氯二苯并呋喃(PCDF)和1,2,3,4,7,8 - 六氯二苯并呋喃(HCDF)是一类环境污染物——多氯代芳烃(PCAH)中剧毒的成员,它们表现出相似且极具特征的毒性效应谱。为了进行风险评估,能够准确估计这些及相关化合物的相对毒性强度非常重要。先前的研究表明,在急性暴露或体外研究中,PCDF的毒性约为TCDD的0.1倍,HCDF的毒性约为TCDD的0.01倍。在本研究中,我们比较了TCDD、PCDF和HCDF在无毛小鼠皮肤中的相对毒性和促肿瘤能力。雌性无毛小鼠(HRS/J hr/hr)经皮给予引发剂MNNG,然后每周两次,持续20周给予丙酮、TCDD(2.5 - 10 ng/小鼠/剂量)、PCDF(25 - 100 ng/小鼠/剂量)或HCDF(250 - 1000 ng/小鼠/剂量)作为促癌剂。TCDD、PCDF和HCDF都是诱导鳞状细胞乳头状瘤的强效促癌剂。然而,各组之间乳头状瘤形成的发生率或多发性没有差异。在没有引发剂的情况下,相同剂量的这三种PCAH不会诱发皮肤乳头状瘤。TCDD在所有剂量下均使肝体重比显著增加(p小于0.001),在剂量为10 ng时使胸腺体重比降低(p小于0.001)。用PCDF和HCDF处理的小鼠出现明显的胸腺和脾脏萎缩、肝脏肥大、腺胃底部黏液细胞增生以及体重减轻。PCDF和HCDF产生的皮肤毒性效应比TCDD更严重,发生率更高。根据皮肤毒性以及体重和器官重量变化的数据,重复经皮暴露后,估计PCDF的毒性是TCDD的0.2至0.4倍,HCDF的毒性是TCDD的0.08至0.16倍。因此,使用急性和/或体外研究数据生成的毒性当量因子可能低估了这些化合物重复低剂量暴露带来的风险。