Bogdanffy M S, Sarangapani R, Plowchalk D R, Jarabek A, Andersen M E
Haskell Laboratory for Toxicology and Industrial Medicine, E.I. du Pont de Nemours and Co., Inc., Newark, Delaware 19714, USA.
Toxicol Sci. 1999 Sep;51(1):19-35. doi: 10.1093/toxsci/51.1.19.
The 1990 Clean Air Act Amendments require that health risk from exposure to vinyl acetate be assessed. Vinyl acetate is a nasal carcinogen in rats, but not mice, and induces olfactory degeneration in both species. A biologically based approach to extrapolating risks of inhalation exposure from rats to humans was developed, which incorporates critical determinants of interspecies dosimetry. A physiologically based pharmacokinetic (PBPK) model describing uptake and metabolism of vinyl acetate in rat nose was validated against nasal deposition data collected at three airflow rates. The model was also validated against observations of metabolically derived acetaldehyde. Modifying the rat nose model to reflect human anatomy created a PBPK model of the human nose. Metabolic constants from both rats and humans specific for vinyl acetate and acetaldehyde metabolism enabled predictions of various olfactory tissue dosimeters related to the mode of action. Model predictions of these dosimeters in rats corresponded well with observations of vinyl acetate toxicity. Intracellular pH (pHi) of olfactory epithelial cells was predicted to drop significantly at airborne exposure concentrations above the NOAEL of 50 ppm. Benchmark dose methods were used to estimate the ED10 and LED10 for olfactory degeneration, the precursor lesion thought to drive cellular proliferation and eventually tumor development at excess cellular acetaldehyde levels. A concentration x time adjustment was applied to the benchmark dose values. Human-equivalent concentrations were calculated by using the human PBPK model to predict concentrations that yield similar cellular levels of acetic acid, acetaldehyde, and pHi. After the application of appropriate uncertainty factors, an ambient air value of 0.4 to 1.0 ppm was derived. The biologically based approach supports a workplace standard of 10 ppm.
1990年《清洁空气法修正案》要求对接触醋酸乙烯酯的健康风险进行评估。醋酸乙烯酯是大鼠而非小鼠的鼻腔致癌物,且在两种物种中均可诱发嗅觉退化。开发了一种基于生物学的方法,用于将大鼠吸入暴露风险外推至人类,该方法纳入了种间剂量测定的关键决定因素。基于生理学的药代动力学(PBPK)模型描述了醋酸乙烯酯在大鼠鼻腔中的摄取和代谢,该模型根据在三种气流速率下收集的鼻腔沉积数据进行了验证。该模型还根据代谢衍生的乙醛的观测结果进行了验证。修改大鼠鼻腔模型以反映人体解剖结构,创建了人类鼻腔的PBPK模型。大鼠和人类针对醋酸乙烯酯和乙醛代谢的代谢常数能够预测与作用模式相关的各种嗅觉组织剂量计。该剂量计在大鼠中的模型预测与醋酸乙烯酯毒性的观测结果吻合良好。预计在空气传播暴露浓度高于无观察到有害作用水平(NOAEL)50 ppm时,嗅觉上皮细胞的细胞内pH(pHi)会显著下降。采用基准剂量法估算嗅觉退化的ED10和LED10,嗅觉退化是一种前驱病变,被认为在细胞乙醛水平过高时会驱动细胞增殖并最终导致肿瘤发展。对基准剂量值应用浓度×时间调整。通过使用人类PBPK模型预测产生相似细胞水平的乙酸、乙醛和pHi的浓度,计算出人类等效浓度。在应用适当的不确定因素后,得出环境空气值为0.4至1.0 ppm。基于生物学的方法支持10 ppm的工作场所标准。