College of Environmental Science and Engineering, Dalian Maritime University, Linghai Road 1, Dalian 116026, PR China.
College of Environmental Science and Engineering, Dalian Maritime University, Linghai Road 1, Dalian 116026, PR China.
Chemosphere. 2018 Jun;200:116-123. doi: 10.1016/j.chemosphere.2018.02.093. Epub 2018 Feb 16.
In the present study, the contamination level and spatial distribution of PFASs in the water dissolved phase and suspended particulate matter (SPM) phase of the Dalian Bay, and the SPM-water partition behavior were investigated. The total concentrations of PFASs (∑PFASs) in the water dissolved phase ranged from 6.9 to 17.1 ng L, with perfluorooctanoic acid (PFOA), perfluorobutanoic acid, and perfluorobutane sulfonate (PFBS) as the predominant PFASs, while ∑PFASs in SPM ranged from 1.7 to 27.5 ng g dw with higher contributions from PFBS, perfluorooctane sulfonic acid and PFOA. As for the pollution distribution, the concentrations of PFASs inside the Dalian Bay were higher than those outside the bay. For perfluoroalkyl carboxylic acid (PFCAs) and perfluoroalkane sulfonic acids (PFSAs), the suspended particulate matter-water partition coefficient (log K) values ranged from 2.62 to 3.76, and from 3.39 to 3.56, respectively. The log K values of PFASs generally increased with the increasing perfluorinated carbon chain length. Short-chain PFCAs were mostly detected in the water dissolved phase, while long-chain PFCAs and PFSAs appeared to bind more strongly to SPM phase. The contamination level of long-chain PFCAs and PFSAs could be underestimated if only the water dissolved phase were measured. Therefore, further investigations should consider the role of SPM on the environmental behavior and fate of PFASs in the aquatic environment.
本研究调查了大连湾水中溶解相和悬浮颗粒物(SPM)相中全氟化合物(PFASs)的污染水平和空间分布,以及 SPM 与水的分配行为。水中溶解相中 PFASs 的总浓度(∑PFASs)范围为 6.9 至 17.1ng/L,以全氟辛酸(PFOA)、全氟丁酸和全氟丁烷磺酸(PFBS)为主要 PFASs,而 SPM 中的∑PFASs 范围为 1.7 至 27.5ng/g dw,其中 PFBS、全氟辛烷磺酸和 PFOA 的贡献较高。就污染分布而言,大连湾内的 PFASs 浓度高于湾外。对于全氟烷基羧酸(PFCAs)和全氟烷磺酸(PFSAs),悬浮颗粒物-水分配系数(log K)值分别为 2.62 至 3.76 和 3.39 至 3.56。PFASs 的 log K 值通常随全氟化碳链长的增加而增加。短链 PFCAs 主要存在于水中溶解相,而长链 PFCAs 和 PFSAs 似乎与 SPM 相结合更强。如果仅测量水溶解相,可能会低估长链 PFCAs 和 PFSAs 的污染水平。因此,进一步的研究应考虑 SPM 在水生环境中 PFASs 的环境行为和归宿中的作用。