Department of Animal Science, Michigan State University, East Lansing, MI, USA.
Environ Toxicol Chem. 2012 Nov;31(11):2545-56. doi: 10.1002/etc.1975. Epub 2012 Aug 31.
This study assessed the effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), 2,3,4,7,8-pentachlorodibenzofuran (PeCDF), and 2,3,7,8 tetrachlorodibenzofuran (TCDF) on the incidence of jaw lesions and on hepatic cytochrome P4501A (CYP1A) endpoints in mink (Mustela vison). Adult female mink were assigned randomly to one of 13 dietary treatments (control and four increasing doses of TCDD, PeCDF, or TCDF) and provided spiked feed for approximately 150 d (60 d prior to breeding through weaning of offspring at 42 d post-parturition). Offspring were maintained on their respective diets for an additional 150 d. Activity of hepatic CYP1A enzymes in adult and juvenile mink exposed to TCDD, PeCDF, or TCDD was generally greater compared with controls, but changes in other CYP1A endpoints were less consistent. Histopathology of the mandible and maxilla of juvenile mink suggested a dose-related increase in the incidence of jaw lesions. The dietary effective doses (ED) for jaw lesions in 50% of the population (ED50) were estimated to be 6.6, 14, and 149 ng/kg body weight (bw)/d for TCDD, PeCDF, and TCDF, respectively. The relative potencies of PeCDF and TCDF compared with TCDD based on ED10, ED20, and ED50 values ranged from 0.5 to 1.9 and 0.04 to 0.09, respectively. These values are within an order of magnitude of the World Health Organization toxic equivalency factor (TEF(WHO)) values of 0.3 and 0.1 for PeCDF and TCDF, respectively.
本研究评估了 2,3,7,8-四氯二苯并对二恶英(TCDD)、2,3,4,7,8-五氯二苯并呋喃(PeCDF)和 2,3,7,8-四氯二苯并呋喃(TCDF)对水貂(Mustela vison)颚病变发生率和肝细胞色素 P4501A(CYP1A)终点的影响。成年雌性水貂被随机分配到 13 种饮食处理中的一种(对照和四种递增剂量的 TCDD、PeCDF 或 TCDF),并提供添加了这些物质的饲料,大约 150 天(从繁殖前 60 天到分娩后 42 天断奶)。后代在各自的饮食中再维持 150 天。与对照组相比,暴露于 TCDD、PeCDF 或 TCDF 的成年和幼年水貂的肝 CYP1A 酶活性通常更高,但其他 CYP1A 终点的变化则不太一致。幼年水貂的下颌骨和上颌骨组织病理学显示,颚病变的发生率与剂量有关。在 50%人群中引起颚病变的饮食有效剂量(ED)的 50%(ED50)分别估计为 TCDD、PeCDF 和 TCDF 的 6.6、14 和 149ng/kg 体重/天。基于 ED10、ED20 和 ED50 值,PeCDF 和 TCDF 与 TCDD 的相对效力范围为 0.5 至 1.9 和 0.04 至 0.09,分别。这些值与世界卫生组织(WHO)毒性等效因子(TEF(WHO))值的数量级一致,分别为 PeCDF 和 TCDF 的 0.3 和 0.1。