De Vito M J, Maier W E, Diliberto J J, Birnbaum L S
Center for Environmental Medicine, University of North Carolina, Chapel Hill 27599.
Fundam Appl Toxicol. 1993 Jan;20(1):125-30.
Toxic equivalency factors (TEFs) have been proposed for dibenzo-p-dioxins, dibenzofurans, and polyhalogenated biphenyls. The proposed toxic equivalency factors (TEFs), which are presently being evaluated in our laboratory, are currently used to estimate the potential health risk associated with exposure to complex mixtures containing these chemicals. In preliminary studies, equally potent doses, based on the published TEFs and relative enzyme-inducing potency, of 2,3,7,8-tetrachloro-dibenzo-p-dioxin (TCDD), 2,3,7,8-tetrachlorodibenzofuran, 1,2,3,7,8-pentachlorodibenzofuran, 1,2,3,4,6,7,8,9-octachloro-dibenzofuran, 3,4,3',4'-tetrachlorobiphenyl, 2,3,4,3',4'-pentachlorobiphenyl, 3,4,5,3',4'-pentachlorobiphenyl, 2,3,4,3',4',5'-hexachlorobiphenyl, 2,3,4,5,3',4'-hexachlorobiphenyl, and 3,4,5,3',4',5'-hexachlorobiphenyl were administered to female B6C3F1 mice 5 days a week over a 4-week period. Hepatic, skin, and lung cytochrome P450 1A1 and hepatic 1A2 activities were determined for all chemicals tested and compared to those from TCDD-treated mice. These initial studies indicate that the present TEFs do not reliably predict induction potency for many of the chemicals. Furthermore, our data suggest that the relative inductive potency of these chemicals may be tissue specific and that estimates of TEFs based on hepatic ethoxyresorufin O-de-ethylase activity may not accurately reflect the potency of these chemicals in nonhepatic tissue. The TEFs proposed for the "dioxin-like" polychlorinated biphenyls (PCBs) overestimate the potency of these compounds by factors of 10-1000. The present study indicates that more experimental data are required before TEFs for PCBs should be used in regulatory decision making.
已针对二苯并 - 对 - 二恶英、二苯并呋喃和多卤代联苯提出了毒性当量因子(TEFs)。目前正在我们实验室进行评估的拟议毒性当量因子,目前用于估计与接触含有这些化学物质的复杂混合物相关的潜在健康风险。在初步研究中,根据已发表的TEFs和相对酶诱导能力,给予雌性B6C3F1小鼠等量的2,3,7,8 - 四氯二苯并 - 对 - 二恶英(TCDD)、2,3,7,8 - 四氯二苯并呋喃、1,2,3,7,8 - 五氯二苯并呋喃、1,2,3,4,6,7,8,9 - 八氯二苯并呋喃、3,4,3',4' - 四氯联苯、2,3,4,3',4' - 五氯联苯、3,4,5,3',4' - 五氯联苯、2,3,4,3',4',5' - 六氯联苯、2,3,4,5,3',4' - 六氯联苯和3,4,5,3',4',5' - 六氯联苯,每周5天,持续4周。对所有测试的化学物质测定肝脏、皮肤和肺中的细胞色素P450 1A1以及肝脏中的1A2活性,并与TCDD处理小鼠的活性进行比较。这些初步研究表明,目前的TEFs不能可靠地预测许多化学物质的诱导能力。此外,我们的数据表明,这些化学物质的相对诱导能力可能具有组织特异性,并且基于肝脏乙氧基异吩恶唑酮O - 脱乙基酶活性的TEFs估计可能无法准确反映这些化学物质在非肝脏组织中的能力。为“类二恶英”多氯联苯(PCBs)提出的TEFs将这些化合物的能力高估了10 - 1000倍。本研究表明,在将PCBs的TEFs用于监管决策之前,需要更多的实验数据。