Office of Environmental Health Hazard Assessment, California Environmental Protection Agency, Oakland, CA 94612, USA.
Regul Toxicol Pharmacol. 2010 Mar;56(2):225-36. doi: 10.1016/j.yrtph.2009.12.008. Epub 2010 Jan 1.
Polychlorinated biphenyls (PCBs) are ubiquitous toxic contaminants. Health risk assessment for this class of chemicals is complex: the current toxic equivalency factor (TEF) method covers dioxin-like (DL-) PCBs, dibenzofurans, and dioxins, but excludes non-DL-PCBs. To address this deficiency, we evaluated published data for several PCB congeners to determine common biomarkers of effect. We found that the most sensitive biomarkers for DL-non-ortho-PCB 77 and PCB 126 are liver enzyme (e.g., ethoxyresorufin-O-deethylase, EROD) induction, circulating thyroxine (T4) decrease, and brain dopamine (DA) elevation. For DL-ortho-PCB 118 and non-DL-ortho-PCB 28 and PCB 153, the most sensitive biomarkers are brain DA decrease and circulating T4 decrease. The only consistent biomarker for both DL- and non-DL-PCBs is circulating T4 decrease. The calculated TEF-(TH), based on the effective dose to decrease T4 by 30% (ED(30)) with reference to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), is identical to both TEF-(WHO98) and TEF-(WHO05) for TCDD and DL-PCBs (correlation coefficients are r=1.00, P<0.001; and r=0.99, P<0.001, respectively). We conclude that T4 decrease is a prospective biomarker for generating a new TEF scheme which includes some non-DL-congeners. The new TEF-(TH) parallels the TEF-(WHO) for DL-PCBs and, most importantly, is useful for non-DL-PCBs in risk assessment to address thyroid endocrine disruption and potentially the neurotoxic effects of PCBs.
多氯联苯 (PCBs) 是无处不在的有毒污染物。此类化学物质的健康风险评估较为复杂:目前的毒性等效因子 (TEF) 方法涵盖了类似二噁英 (DL-) 的 PCBs、二苯并呋喃和二噁英,但不包括非 DL-PCBs。为了解决这一不足,我们评估了几种 PCB 同系物的已发表数据,以确定常见的效应生物标志物。我们发现,DL-非邻位-PCB77 和 PCB126 的最敏感生物标志物是肝脏酶(如乙氧基Resorufin-O-去乙基酶,EROD)诱导、循环甲状腺素 (T4) 减少和大脑多巴胺 (DA) 升高。对于 DL-邻位-PCB118 和非 DL-邻位-PCB28 和 PCB153,最敏感的生物标志物是大脑 DA 减少和循环 T4 减少。DL-和非 DL-PCBs 的唯一一致的生物标志物是循环 T4 减少。基于与 2,3,7,8-四氯二苯并-p-二噁英 (TCDD) 相比,降低 T4 30%的有效剂量 (ED30) 计算出的 TEF-(TH),与 TCDD 和 DL-PCBs 的 TEF-(WHO98) 和 TEF-(WHO05) 相同(相关系数分别为 r=1.00,P<0.001 和 r=0.99,P<0.001)。我们得出结论,T4 减少是生成新 TEF 方案的潜在生物标志物,该方案包括一些非 DL-同系物。新的 TEF-(TH) 与 DL-PCBs 的 TEF-(WHO) 平行,最重要的是,它可用于非 DL-PCBs 的风险评估,以解决甲状腺内分泌紊乱和 PCBs 的潜在神经毒性影响。