Department of Chemistry, University of Toronto , 80 St. George St., Toronto, Ontario, Canada , M5S 3H6.
Environ Sci Technol. 2014;48(1):340-9. doi: 10.1021/es403949z. Epub 2013 Dec 16.
Significant contamination of perfluoroalkyl acids (PFAAs) in wastewater treatment plant (WWTP) sludge implicates the practice of applying treated sludge or biosolids as a potential source of these chemicals onto agricultural farmlands. Recent efforts to characterize the sources of PFAAs in the environment have unveiled a number of fluorotelomer-based materials that are capable of degrading to the perfluoroalkyl carboxylates (PFCAs), such as the polyfluoroalkyl phosphate diesters (diPAPs), which have been detected in WWTP and paper fiber biosolids. Here, a greenhouse microcosm was used to investigate the fate of endogenous diPAPs and PFCAs present in WWTP and paper fiber biosolids upon amendment of these materials with soil that had been sown with Medicago truncatula plants. Biodegradation pathways and plant uptake were further elucidated in a separate greenhouse microcosm supplemented with high concentrations of 6:2 diPAP. Biosolid-amended soil exhibited increased concentrations of diPAPs (4-83 ng/g dry weight (dw)) and PFCAs (0.1-19 ng/g dw), as compared to control soils (nd-1.4 ng/g dw). Both plant uptake and biotransformation contributed to the observed decline in diPAP soil concentrations over time. Biotransformation was further evidenced by the degradation of 6:2 diPAP to its corresponding fluorotelomer intermediates and C4-C7 PFCAs. Substantial plant accumulation of endogenous PFCAs present in the biosolids (0.1-138 ng/g wet weight (ww)) and those produced from 6:2 diPAP degradation (100-58 000 ng/g ww) were observed within 1.5 months of application, with the congener profile dominated by the short-chain PFCAs (C4-C6). This pattern was corroborated by the inverse relationship observed between the plant-soil accumulation factor (PSAF, Cplant/Csoil) and carbon chain length (p < 0.05, r = 0.90-0.97). These results were complemented by a field study in which the fate of diPAPs and PFCAs was investigated upon application of compost and paper fiber biosolids to two farm fields. Together, these studies provide the first evidence of soil biodegradation of diPAPs and the subsequent uptake of these chemicals and their metabolites into plants.
污水处理厂 (WWTP) 污泥中存在大量全氟烷基酸 (PFAAs),这意味着将经过处理的污泥或生物固体作为这些化学物质的潜在来源施用于农田是一种实践。最近,人们努力描述环境中 PFAAs 的来源,发现了一些能够降解为全氟烷基羧酸 (PFCAs) 的含氟端基材料,例如多氟烷基磷酸二酯 (diPAPs),这些物质已在 WWTP 和造纸纤维生物固体中被检测到。在这里,使用温室微宇宙研究了在将这些材料与已播种了紫花苜蓿植物的土壤混合后,WWTP 和造纸纤维生物固体中存在的内源性 diPAPs 和 PFCAs 的命运。在补充高浓度 6:2 diPAP 的另一个温室微宇宙中,进一步阐明了生物降解途径和植物吸收。与对照土壤 (nd-1.4 ng/g dw) 相比,添加生物固体的土壤中 diPAPs(4-83 ng/g 干重 (dw)) 和 PFCAs(0.1-19 ng/g dw) 的浓度增加。随着时间的推移,植物吸收和生物转化都导致 diAP 土壤浓度下降。生物转化进一步证明了 6:2 diPAP 降解为相应的含氟端基中间体和 C4-C7 PFCAs。在应用 1.5 个月内,观察到生物固体中存在的内源性 PFCAs(0.1-138 ng/g 湿重 (ww)) 和由 6:2 diPAP 降解产生的 PFCAs(100-58000 ng/g ww) 的大量植物积累,具有短链 PFCAs (C4-C6) 为主的同系物分布。这一模式得到了观察到的植物-土壤积累因子 (PSAF,Cplant/Csoil) 与碳链长度之间的反比关系的证实 (p < 0.05,r = 0.90-0.97)。这些结果得到了田间研究的补充,该研究调查了在将堆肥和造纸纤维生物固体施用于两个农田后,diPAPs 和 PFCAs 的命运。总的来说,这些研究提供了关于 diPAPs 的土壤生物降解以及随后这些化学物质及其代谢物被植物吸收的第一个证据。