Liu Chen, Liu Jinxia
Department of Civil Engineering, McGill University, Montreal, Quebec, H3A 0C3, Canada.
Department of Civil Engineering, McGill University, Montreal, Quebec, H3A 0C3, Canada.
Environ Pollut. 2016 May;212:230-237. doi: 10.1016/j.envpol.2016.01.069. Epub 2016 Feb 2.
Microbial transformation of polyfluoroalkyl phosphate esters (PAPs) into perfluorocarboxylic acids (PFCAs) has recently been confirmed to occur in activated sludge and soil. However, there lacks quantitative information about the half-lives of the PAPs and their significance as the precursors to PFCAs. In the present study, the biotransformation of 6:2 and 8:2 diPAP in aerobic soil was investigated in semi-dynamics reactors using improved sample preparation methods. To develop an efficient extraction method for PAPs, six different extraction solvents were compared, and the phenomenon of solvent-enhanced hydrolysis was investigated. It was found that adding acetic acid could enhance the recoveries of the diPAPs and inhibit undesirable hydrolysis during solvent extraction of soil. However 6:2 and 8:2 monoPAPs, which are the first breakdown products from diPAPs, were found to be unstable in the six solvents tested and quickly hydrolyzed to form fluorotelomer alcohols. Therefore reliable measurement of the monoPAPs from a live soil was not achievable. The apparent DT50 values of 6:2 diPAP and 8:2 diPAP biotransformation were estimated to be 12 and > 1000 days, respectively, using a double first-order in parallel model. At the end of incubation of day 112, the major degradation products of 6:2 diPAP were 5:3 fluorotelomer carboxylic acid (5:3 acid, 9.3% by mole), perfluoropentanoic acid (PFPeA, 6.4%) and perfluorohexanoic acid (PFHxA, 6.0%). The primary product of 8:2 diPAP was perfluorooctanoic acid (PFOA, 2.1%). The approximately linear relationship between the half-lives of eleven polyfluoroalkyl and perfluoroalkyl substances (PFASs, including 6:2 and 8:2 diPAPs) that biotransform in aerobic soils and their molecular weights suggested that the molecular weight is a good indicator of the general stability of low-molecular-weight PFAS-based compounds in aerobic soils.
最近已证实,多氟烷基磷酸酯(PAPs)在活性污泥和土壤中会微生物转化为全氟羧酸(PFCAs)。然而,关于PAPs的半衰期及其作为PFCAs前体的重要性,缺乏定量信息。在本研究中,使用改进的样品制备方法,在半动态反应器中研究了6:2和8:2二PAP在好氧土壤中的生物转化。为开发一种高效的PAPs提取方法,比较了六种不同的提取溶剂,并研究了溶剂增强水解现象。研究发现,添加乙酸可以提高二PAPs的回收率,并抑制土壤溶剂萃取过程中不必要的水解。然而,发现作为二PAPs的首批分解产物的6:2和8:2单PAPs在测试的六种溶剂中不稳定,并迅速水解形成氟调聚物醇。因此,无法可靠地测量来自活土壤中的单PAPs。使用双一级平行模型估计,6:2二PAP和8:2二PAP生物转化的表观DT50值分别为12天和>1000天。在第112天培养结束时,6:2二PAP的主要降解产物为5:3氟调聚物羧酸(5:3酸,摩尔分数9.3%)、全氟戊酸(PFPeA,6.4%)和全氟己酸(PFHxA,6.0%)。8:2二PAP的主要产物是全氟辛酸(PFOA,2.1%)。在好氧土壤中发生生物转化的11种多氟烷基和全氟烷基物质(PFASs,包括6:2和8:2二PAPs)的半衰期与其分子量之间的近似线性关系表明,分子量是低分子量PFAS基化合物在好氧土壤中总体稳定性的良好指标。