Université de Bordeaux, EPOC, UMR 5805, F-33400 Talence, France.
CNRS, EPOC, UMR 5805, F-33400 Talence, France.
Environ Sci Process Impacts. 2019 Nov 1;21(11):1864-1874. doi: 10.1039/c9em00322c. Epub 2019 Sep 16.
The present work examined the trophic transfer of perfluoroalkyl and polyfluoroalkyl substances (PFASs) in a typical urban river (Orge River, near Paris, France), and aimed to investigate the potential contribution of precursors to the biomagnification of perfluoroalkyl acids (PFAAs). Sixteen PFAAs, twelve of their precursors (pre-PFAAs) and two fluorinated alternatives to long-chain PFASs were analyzed in water, sediments and biota (including biofilm, invertebrates and fish). Twenty two compounds were detected in biological samples (2.0-147 ng g wet weight), perfluorooctane sulfonate (PFOS) and C-C perfluoroalkyl carboxylates (PFCAs) being predominant while ∑pre-PFAAs contributed to 1-18% of ∑PFASs. Trophic magnification factors (TMFs) were >1 (i.e. denoting biomagnification) for C-C PFCAs, C-C perfluoroalkyl sulfonates (PFSAs) and several pre-PFAAs (e.g. 8 : 2 and 10 : 2 fluorotelomer sulfonates). The significant decrease in ∑pre-PFCAs/∑PFCAs concentration ratio with trophic level suggested a likely contribution of selected precursors to the biomagnification of PFCAs through biotransformation, while this was less obvious for PFOS. The total oxidizable precursor assay, applied for the first time to sediment and biota, revealed the presence of substantial proportions of extractable unknown pre-PFAAs in all samples (i.e. 15-80% of ∑PFASs upon oxidation). This proportion significantly decreased from sediments to invertebrates and fish, thereby pointing to the biotransformation of unattributed pre-PFAAs in the trophic web, which likely contributes to the biomagnification of some PFAAs (i.e. C-C PFCAs and C-C PFSAs).
本研究考察了典型城市河流(法国巴黎附近的奥热河)中全氟烷基和多氟烷基物质(PFAS)的营养传递,并旨在研究前体对全氟烷基酸(PFAAs)生物放大的潜在贡献。在水、沉积物和生物群(包括生物膜、无脊椎动物和鱼类)中分析了 16 种 PFAAs、12 种前体(前 PFAS)和两种长链 PFAS 的氟代替代品。在生物样本中检测到 22 种化合物(2.0-147 ng g 湿重),过氧全氟辛烷磺酸(PFOS)和 C-C 全氟烷基羧酸(PFCAs)为主,而∑前 PFASs 占∑PFASs 的 1-18%。营养级放大因子(TMFs)>1(表示生物放大),适用于 C-C PFCAs、C-C 全氟烷基磺酸盐(PFSAs)和几种前 PFASs(例如 8:2 和 10:2 氟调聚磺酸盐)。随着营养级的增加,∑前 PFCAs/∑PFCAs 浓度比显著下降,这表明通过生物转化,某些前体可能对 PFCAs 的生物放大有贡献,而对于 PFOS 则不太明显。总可氧化前体测定法首次应用于沉积物和生物群,表明所有样品中均存在大量可提取的未知前 PFASs(即氧化后占∑PFASs 的 15-80%)。从沉积物到无脊椎动物和鱼类,这一比例显著下降,这表明在营养网络中未归因的前 PFASs 发生了生物转化,这可能有助于某些 PFAAs(即 C-C PFCAs 和 C-C PFSAs)的生物放大。