Source apportionment of perfluoroalkyl substances in surface sediments from lakes in Jiangsu Province, China: Comparison of three receptor models
Graphical abstract
Introduction
The mass production and widespread usage of perfluoroalkyl substances (PFASs) have begun since the late 1940s (Kim et al., 2012). PFASs are ubiquitous in various environmental media, such as water, soils, sediments, sewage sludge, biota and human bodies (Wang et al., 2015, Zhao et al., 2012). It was inferred that a large proportion of PFASs would be released to the surface waters, and sediments, as the natural environment of benthic organisms, are considered as one of the most important environmental sinks of PFASs (Prevedouros et al., 2006). PFASs have been found in sediments from several countries and regions, and PFAS concentrations have reached up to 800 ng/g dry weight (dw) (Ahrens et al., 2015, Campo et al., 2015, Zhou et al., 2013). Source apportionment of PFASs in sediments is of great significance for pollution control and ecological protection of aquatic environments.
Qualitative and semiquantitative methods have been widely employed to identify PFAS sources. Xiao et al. (2012) adopted cluster analysis, correlation analysis, ANOVA and per capita discharge to distinguish different PFAS patterns in influent samples from thirty-seven wastewater treatment plants in a multi-city survey. Murakami et al. (2009) used ratio methods to evaluate PFAS contributions from street runoff and wastewater to the aquatic environments. A few methods, e.g., principal component analysis (PCA), multiple linear regression model (MLR), positive matrix factorization (PMF) and Unmix models, have been applied to quantitative source apportionment of PFASs. However, only one or two of these models are usually applied to source apportionment of PFASs, and it is not enough to provide comprehensive information for PFAS sources (Kuroda et al., 2014, Qi et al., 2016).
Jiangsu Province, located in the lower reaches of the Yangtze River and Huaihe River, is traversed by the Beijing-Hangzhou Grand Canal from north to south. It forms part of the Yangtze River Delta urban agglomeration, which is one of the six world-class city clusters. As one of the most intensively industrialized provinces in China, Jiangsu Province contributed the largest portion of perfluorooctane sulfonic acid (PFOS) emissions in China (Xie et al., 2013). PFOS concentrations in Taihu Lake in Jiangsu Province even exceeded US EPA standards of 0.2 μg/L for PFOS in drinking water (US EPA, 2009, Yang et al., 2011). Our published work showed that lake sediments from Jiangsu Province have also suffered the heaviest PFAS pollution (mean 1.76 ng/g dw) among all provinces studied (Qi et al., 2016). In this study, PCA-MLR, PMF and Unmix models were applied to identify source categories and quantitatively calculate source contributions of PFASs in lake sediments from Jiangsu Province. Results from three models were evaluated and compared in order to improve source apportionment of PFASs. Comparative statistics could enhance the persuasiveness of the conclusions and offer us a better knowledge of PFAS sources in lake sediments.
Section snippets
Standards and reagents
Seventeen PFASs including C4–C14-perfluoroalkyl carboxylic acids (PFCAs) and C4, C6, C8 and C10-perfluoroalkane sulfonic acids were targeted. A mixture of seventeen native PFASs and nine stable isotope-labeled surrogate internal standards in 2 μg/mL solution mixtures were both purchased from Wellington Laboratories (Guelph, ON, Canada). Perfluoro-1-[1,2,3,4,5,6,7,8-13C8]octanesulfonate and perfluoro-n-[1,2,3,4,5,6,7,8-13C8]octanoic acid (50 μg/mL, 99%) were purchased from Cambridge Isotope
PFAS concentrations in sediments
PFASs were detected in all sediment samples. The ∑12PFASs concentrations ranged from 0.264 to 4.44 ng/g dw, with an average of 1.76 ng/g dw. 87%–100% of sediment samples had concentrations higher than LODs for twelve individual PFAS species. PFOS was the predominant compound, with an average of 0.384 ng/g dw, followed by perfluoroundecanoic acid (PFUnDA) and perfluorooctanoate acid (PFOA) with averages of 0.337 and 0.320 ng/g dw, respectively. Average concentrations of the long-chained PFCAs (C9–C14
Conclusions
In this study, sixty sediment samples were collected from fourteen lakes in Jiangsu Province of China. Concentrations of the ∑12PFASs ranged from 0.264 to 4.44 ng/g dw, with an average of 1.76 ng/g dw. All targeted PFASs were quantifiable and PFOS was the most abundant compound. Source apportionment of PFASs in sediments was conducted by three multivariate factor analysis receptor models: PCA-MLR, PMF and Unmix. Four sources were identified consistently by three models: textile treatments,
Acknowledgments
This work was supported by the Mega-projects of Science Research for Water Environmental Improvement (No. 2012ZX07101-002) and the National Natural Science Foundation of China (No. 41521003).
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