The Water Laboratory, 2031 BE Haarlem, the Netherlands; Amsterdam Institute for Life and Environment (A-LIFE), Vrije Universiteit Amsterdam, 1081 HV Amsterdam, the Netherlands.
The Water Laboratory, 2031 BE Haarlem, the Netherlands.
Environ Int. 2023 Nov;181:108256. doi: 10.1016/j.envint.2023.108256. Epub 2023 Oct 10.
Per- and polyfluoroalkyl substances (PFAS) are a group of xenobiotics that are widely distributed throughout the aquatic environment. Many PFAS are possible thyroid hormone (TH) system disrupting compounds, because they have the capacity to -amongst other- inhibit the TH thyroxine (T) from binding to its transport protein transthyretin (TTR). This study investigated the occurrence of TH-displacing activity in the Dutch water cycle, and more specifically, the contribution of PFAS to this effect. Over one year of monitoring data of 29 PFAS (linear and branched) showed the continuous presence of PFAS in drinking waters and their surface water sources. Secondly, the FITC-T and TTR-TRβ-CALUX bioassays were mutually compared using positive (HPLC-grade water spiked with PFOA) and negative control samples (HPLC-grade water), as well as relative potency factors (RPFs) of up to 20 PFAS congeners. Both assays were found to be suitable for measuring TH-displacing activity in water samples. As a third aim, a field study was performed in the Dutch water cycle that was comprised of samples from drinking water, surface water, PFAS contaminated sites, and 2 wastewater treatment plants. All samples were analyzed with 1. chemical analysis for 29 PFAS, 2. the FITC-T bioassay, and 3. the TTR-TRβ-CALUX bioassay. The bioassays mutually showed good correlation (R 0.85). Bioanalytical equivalent concentrations (BEQ) based on chemically-determined concentrations and RPFs (BEQ) revealed that analyzed PFAS only explained ≤4.1 % of their activity in water extracts measured by both bioassays (BEQ). This indicated that as yet unknown compounds contribute to the majority of the measured TH-displacing activity. Moreover, water treatment processes (e.g. DW production from SW) showed a larger contribution of target PFAS to the BEQ. This could be a first lead to identify unknown compounds that contribute to this activity, and as such, enable the assessment of possible risks associated by the occurrence of TH-displacing activity in water.
全氟和多氟烷基物质(PFAS)是一组广泛分布于水生态环境中的外源性化学物质。许多 PFAS 可能是甲状腺激素(TH)系统扰乱化合物,因为它们有能力——除其他外——抑制 TH 甲状腺素(T)与转甲状腺素蛋白(TTR)结合。本研究调查了荷兰水生态系统中 TH 置换活性的发生情况,更具体地说,调查了 PFAS 对此效应的贡献。对 29 种(直链和支链)PFAS 的一年多监测数据显示,PFAS 持续存在于饮用水及其地表水水源中。其次,使用阳性(用 PFOA 加标 HPLC 级水)和阴性对照样品(HPLC 级水)以及多达 20 种 PFAS 同系物的相对效力因子(RPF),相互比较了 FITC-T 和 TTR-TRβ-CALUX 生物测定法。两种测定法均被发现适用于测量水样中的 TH 置换活性。作为第三个目标,在荷兰水生态系统中进行了一项现场研究,该研究包括饮用水、地表水、PFAS 污染场地和 2 个废水处理厂的样本。所有样品均用 1. 化学分析 29 种 PFAS,2. FITC-T 生物测定法和 3. TTR-TRβ-CALUX 生物测定法进行分析。生物测定法相互之间显示出良好的相关性(R 0.85)。基于化学测定浓度和 RPF(BEQ)的生物等效浓度(BEQ)表明,分析的 PFAS 仅解释了生物测定法测量的水样中其活性的≤4.1%(BEQ)。这表明,未知化合物在很大程度上导致了所测量的 TH 置换活性。此外,水处理工艺(例如,从地表水生产饮用水)显示出目标 PFAS 对 BEQ 的贡献更大。这可能是识别对这种活性有贡献的未知化合物的第一个线索,并由此评估 TH 置换活性在水中存在所带来的潜在风险。