Office of Research and Development, Oak Ridge Institute for Science and Education Fellow at the United States Environmental Protection Agency, Research Triangle Park, North Carolina 27711, USA.
Office of Research and Development, United States Environmental Protection Agency, Research Triangle Park, North Carolina 27711, USA.
Toxicol Sci. 2023 Dec 21;197(1):95-103. doi: 10.1093/toxsci/kfad098.
Per- and polyfluoroalkyl substances (PFAS) are regularly found in soils and dusts, both of which can be consumed by children at relatively high amounts. However, there is little data available to model the bioaccessibility of PFAS in soils and dusts when consumed or to describe how the physiochemical properties of PFAS and soils/dusts might affect bioaccessibility of these chemicals. Because bioaccessibility is an important consideration in estimating absorbed dose for exposure and risk assessments, in the current study, in vitro assays were used to determine bioaccessibility of 14 PFAS in 33 sets of soils and dusts. Bioaccessibility assays were conducted with and without a sink, which was used to account for the removal of PFAS due to their movement across the human intestine. Multiple linear regression with backward elimination showed that a segmented model using PFAS chain length, number of branches, and percent total organic carbon explained 78.0%-88.9% of the variability in PFAS bioaccessibility. In general, PFAS had significantly greater bioaccessibility in soils relative to dusts and the addition of a sink increased bioaccessibility in the test system by as much as 10.8% for soils and 20.3% for dusts. The results from this study indicate that PFAS bioaccessibility in soils and dusts can be predicted using a limited set of physical chemical characteristics and could be used to inform risk assessment models.
全氟和多氟烷基物质(PFAS)经常存在于土壤和尘埃中,儿童可能会以相对较高的量摄入这些物质。然而,目前可用的数据很少能够模拟摄入土壤和尘埃中的 PFAS 的生物可及性,也无法描述 PFAS 和土壤/尘埃的物理化学特性如何影响这些化学物质的生物可及性。由于生物可及性是估计暴露和风险评估中吸收剂量的一个重要考虑因素,因此在当前研究中,使用体外测定法来确定 33 组土壤和尘埃中 14 种 PFAS 的生物可及性。生物可及性测定法在有和没有吸收池的情况下进行,吸收池用于解释由于 PFAS 在人体肠道中的迁移而导致的 PFAS 去除。使用向后消除的多元线性回归表明,使用 PFAS 链长、分支数和总有机碳百分比分段模型可以解释 PFAS 生物可及性变化的 78.0%-88.9%。一般来说,PFAS 在土壤中的生物可及性明显高于尘埃,并且吸收池的添加使测试系统中的生物可及性增加了高达 10.8%(土壤)和 20.3%(尘埃)。本研究的结果表明,可以使用有限的物理化学特性来预测土壤和尘埃中的 PFAS 生物可及性,并可用于为风险评估模型提供信息。