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美国纽约州哈德逊河上游鱼类中的膳食暴露对水貂(Mustela vison)的器官质量和病理学的影响。

Dietary exposure of mink (Mustela vison) to fish from the upper Hudson River, New York, USA: effects on organ mass and pathology.

机构信息

Department of Animal Science, Michigan State University, East Lansing, Michigan, USA.

出版信息

Environ Toxicol Chem. 2013 Apr;32(4):794-801. doi: 10.1002/etc.2114. Epub 2013 Feb 19.

DOI:10.1002/etc.2114
PMID:23293106
Abstract

The authors evaluated effects of feeding ranch mink (Mustela vison) diets containing polychlorinated biphenyl (PCB)-contaminated fish from the upper Hudson River (New York, USA) on adult and offspring organ mass and pathology. Diets contained 2.5 to 20% Hudson River fish, providing 0.72 to 6.1 µg ΣPCBs/g feed (4.8-38 pg toxic equivalents [TEQWHO 2005 ]/g feed). Absolute thyroid and adrenal gland masses were increased in adult females and 31-week-old juveniles, respectively, and absolute liver and heart masses were decreased in six-week-old kits exposed to dietary PCBs. Dietary concentrations of 0.72 µg ΣPCBs/g feed (4.8 pg TEQWHO 2005 /g feed) and greater induced mandibular and maxillary squamous epithelial proliferation in adult animals. The dietary concentration of ΣPCBs predicted to result in 20% incidence of the jaw lesion (EC20) was 2.3 µg ΣPCBs/g feed (15 pg TEQWHO 2005 /g feed), and the hepatic concentration was 2.8 µg ΣPCBs/g liver (89 pg TEQWHO 2005 /g liver). The EC20 values were greater than the dietary and hepatic concentrations predicted to result in a 20% increase in kit mortality (LC20) at six weeks of age (0.34 µg ΣPCBs/g feed or 2.6 pg TEQWHO 2005 /g feed and 0.80 µg ΣPCBs/g liver or 13 pg TEQWHO 2005 /g liver). However, the EC20 values reflect exposure of adults to PCBs for approximately six months, and the LC20 values reflect exposure of offspring from conception onward.

摘要

作者评估了喂食含有多氯联苯(PCB)污染哈德逊河(美国纽约州)鱼的牧场貂(Mustela vison)饮食对成年和后代器官质量和病理学的影响。饮食中含有 2.5%至 20%的哈德逊河鱼,提供 0.72 至 6.1µgΣPCBs/g 饲料(4.8-38pg 总毒性当量[2005 年 WHO] /g 饲料)。成年雌性和 31 周龄幼崽的甲状腺和肾上腺质量分别增加,暴露于饮食 PCB 的六周龄幼崽的肝脏和心脏质量减少。饮食中 0.72µgΣPCBs/g 饲料(4.8pg 总毒性当量[2005 年 WHO] /g 饲料)及更高浓度的 PCB 会导致成年动物下颌和上颌鳞状上皮增生。导致 20%下颌病变发生率(EC20)的ΣPCBs 饮食浓度为 2.3µgΣPCBs/g 饲料(15pg 总毒性当量[2005 年 WHO] /g 饲料),肝脏浓度为 2.8µgΣPCBs/g 肝脏(89pg 总毒性当量[2005 年 WHO] /g 肝脏)。EC20 值大于预测会导致六周龄幼崽死亡率增加 20%(LC20)的饮食和肝脏浓度,即 0.34µgΣPCBs/g 饲料或 2.6pg 总毒性当量[2005 年 WHO] /g 饲料和 0.80µgΣPCBs/g 肝脏或 13pg 总毒性当量[2005 年 WHO] /g 肝脏)。然而,EC20 值反映了成年动物暴露于 PCB 的时间约为六个月,而 LC20 值反映了从受孕开始暴露于后代的情况。

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