Oak Ridge Institute for Science and Education, Integrated Systems Toxicology Division (ISTD), National Health and Environmental Effects Research Laboratory (NHEERL), Office of Research and Development (ORD), U.S. Environmental Protection Agency (EPA), Research Triangle Park, North Carolina, USA.
Research Cores Unit, NHEERL, ORD, U.S. EPA, Research Triangle Park, North Carolina, USA.
Environ Health Perspect. 2020 Apr;128(4):47005. doi: 10.1289/EHP5843. Epub 2020 Apr 9.
Per- and polyfluoroalkyl substances (PFAS) are a diverse class of industrial chemicals with widespread environmental occurrence. Exposure to long-chain PFAS is associated with developmental toxicity, prompting their replacement with short-chain and fluoroether compounds. There is growing public concern over the safety of replacement PFAS.
We aimed to group PFAS based on shared toxicity phenotypes.
Zebrafish were developmentally exposed to 4,8-dioxa-3H-perfluorononanoate (ADONA), perfluoro-2-propoxypropanoic acid (GenX Free Acid), perfluoro-3,6-dioxa-4-methyl-7-octene-1-sulfonic acid (PFESA1), perfluorohexanesulfonic acid (PFHxS), perfluorohexanoic acid (PFHxA), perfluoro--octanoic acid (PFOA), perfluorooctanesulfonic acid (PFOS), or 0.4% dimethyl sulfoxide (DMSO) daily from 0-5 d post fertilization (dpf). At 6 dpf, developmental toxicity and developmental neurotoxicity assays were performed, and targeted analytical chemistry was used to measure media and tissue doses. To test whether aliphatic sulfonic acid PFAS cause the same toxicity phenotypes, perfluorobutanesulfonic acid (PFBS; 4-carbon), perfluoropentanesulfonic acid (PFPeS; 5-carbon), PFHxS (6-carbon), perfluoroheptanesulfonic acid (PFHpS; 7-carbon), and PFOS (8-carbon) were evaluated.
PFHxS or PFOS exposure caused failed swim bladder inflation, abnormal ventroflexion of the tail, and hyperactivity at nonteratogenic concentrations. Exposure to PFHxA resulted in a unique hyperactivity signature. ADONA, PFESA1, or PFOA exposure resulted in detectable levels of parent compound in larval tissue but yielded negative toxicity results. GenX was unstable in DMSO, but stable and negative for toxicity when diluted in deionized water. Exposure to PFPeS, PFHxS, PFHpS, or PFOS resulted in a shared toxicity phenotype characterized by body axis and swim bladder defects and hyperactivity.
All emerging fluoroether PFAS tested were negative for evaluated outcomes. Two unique toxicity signatures were identified arising from structurally dissimilar PFAS. Among sulfonic acid aliphatic PFAS, chemical potencies were correlated with increasing carbon chain length for developmental neurotoxicity, but not developmental toxicity. This study identified relationships between chemical structures and phenotypes that may arise from shared mechanisms of PFAS toxicity. These data suggest that developmental neurotoxicity is an important end point to consider for this class of widely occurring environmental chemicals. https://doi.org/10.1289/EHP5843.
全氟和多氟烷基物质(PFAS)是一类具有广泛环境存在的工业化学物质。长链 PFAS 的暴露与发育毒性有关,促使它们被短链和氟醚化合物取代。公众对替代 PFAS 的安全性越来越关注。
我们旨在根据共同的毒性表型对 PFAS 进行分组。
从受精后 0-5 天(dpf)每天对斑马鱼进行 4,8-二恶烷-3H-全氟壬酸(ADONA)、全氟-2-丙氧基丙酸钠(GenX 游离酸)、全氟-3,6-二恶烷-4-甲基-7-辛烯-1-磺酸(PFESA1)、全氟己烷磺酸(PFHxS)、全氟己酸(PFHxA)、全氟辛酸(PFOA)、全氟辛烷磺酸(PFOS)或 0.4%二甲基亚砜(DMSO)的发育暴露。在 6 dpf 时,进行发育毒性和发育神经毒性测定,并使用靶向分析化学测量介质和组织剂量。为了测试脂肪族磺酸 PFAS 是否引起相同的毒性表型,评估了全氟丁烷磺酸(PFBS;4 碳)、全氟戊烷磺酸(PFPeS;5 碳)、PFHxS(6 碳)、全氟庚烷磺酸(PFHpS;7 碳)和 PFOS(8 碳)。
PFHxS 或 PFOS 暴露在非致畸浓度下导致游泳囊充气失败、尾巴腹侧弯曲异常和过度活跃。PFHxA 暴露导致独特的过度活跃特征。ADONA、PFESA1 或 PFOA 暴露导致幼体组织中存在母体化合物的可检测水平,但毒性结果为阴性。GenX 在 DMSO 中不稳定,但在去离子水中稀释时稳定且无毒性。PFPeS、PFHxS、PFHpS 或 PFOS 暴露导致以身体轴和游泳囊缺陷和过度活跃为特征的共同毒性表型。
所有测试的新兴氟醚 PFAS 对评估结果均为阴性。两种独特的毒性特征是由结构不同的 PFAS 引起的。在磺酸脂肪族 PFAS 中,发育神经毒性的化学效力与碳链长度的增加呈正相关,但发育毒性则不然。本研究确定了化学结构与表型之间的关系,这些表型可能源于 PFAS 毒性的共同机制。这些数据表明,发育神经毒性是这一类广泛存在的环境化学物质的一个重要终点。https://doi.org/10.1289/EHP5843.