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C1 至 C8 全氟烷基羧酸和磺酸的同系物特异性有机碳归一化土壤和沉积物-水分配系数。

Congener-specific organic carbon-normalized soil and sediment-water partitioning coefficients for the C1 through C8 perfluoroalkyl carboxylic and sulfonic acids.

机构信息

Department of Chemistry, University of Winnipeg, Winnipeg, Manitoba, Canada.

出版信息

J Environ Sci Health A Tox Hazard Subst Environ Eng. 2009 Nov;44(13):1374-87. doi: 10.1080/10934520903217229.

Abstract

Organic carbon-normalized soil and sediment-water partitioning coefficients (K(oc)) were estimated for all C(1) through C(8) perfluoroalkyl carboxylic (PFCA) and sulfonic (PFSA) acid congeners. The limited experimental K(oc) data set for the straight chain C(7) through C(10) PFCAs and C(8) and C(10) PFSAs was correlated to SPARC and ALOGPS computationally estimated octanol-water partitioning/distribution constants and used to predict K(oc) values for both branched and linear C(1) through C(8) isomers. Branched and linear congeners in this homologue range are generally expected to have K(oc) values > 1, leading to their accumulation in organic matter on sediments and soils, retardation during ground and pore water flow, and the preferential association with dissolved organic matter in aquatic systems. Both increasing perfluoroalkyl chain length and linearity increase K(oc) values with substantial intra- and inter-homologue variation and interhomologue mixing. Variability in K(oc) values among the PFCA and PFSA congeners will likely lead to an enrichment of more linear and longer-chain isomers in organic matter fractions, resulting in aqueous phases fractionated towards shorter-chain branched congeners. The expected magnitude of fractionation will require inclusion in source apportionment models and risk assessments. A comparison of representative established quantitative structure property relationships for estimating K(oc) values from octanol-water partitioning constants suggests that these equilibrium partitioning frameworks may be applicable towards modeling PFCA and PFSA environmental fate processes.

摘要

对所有 C(1) 到 C(8) 全氟烷基羧酸 (PFCA) 和磺酸 (PFSA) 酸同系物进行了归一化有机碳的土壤和水分配系数 (K(oc)) 的估算。对于直链 C(7) 到 C(10) PFCAs 和 C(8) 和 C(10) PFSA 的有限实验 K(oc) 数据集,与 SPARC 和 ALOGPS 计算估计的辛醇-水分配/分布常数相关联,并用于预测支链和线性 C(1) 的 K(oc) 值通过 C(8) 异构体。在该同系物范围内的支链和线性同系物通常预计具有 K(oc) 值>1,导致它们在沉积物和土壤中的有机质中积累,在地面和孔隙水中的迁移率降低,以及在水生系统中优先与溶解有机质结合。随着全氟烷基链长度和线性度的增加,K(oc) 值会显著增加,具有较大的同系物内和同系物间变化以及同系物混合。PFCA 和 PFSA 同系物之间 K(oc) 值的可变性可能导致更多线性和长链异构体在有机质中富集,导致分相朝向较短链支链同系物。分馏的预期幅度需要包括在源分配模型和风险评估中。对从辛醇-水分配常数估算 K(oc) 值的代表性定量构效关系的比较表明,这些平衡分配框架可能适用于模拟 PFCA 和 PFSA 环境归宿过程。

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