TY - BOOK
T1 - Screening of PFASs in groundwater and surface water
AU - Ahrens, Lutz
AU - Hedlund, Johanna
AU - Tröger, Rikard
AU - Wiberg, Karin
AU - Dürig, Wiebke
PY - 2016
Y1 - 2016
N2 - Per- and polyfluoroalkyl substances (PFASs) are emerging organic pollutants characterized by their persistency, and bioaccumulation and toxicity potential. In this study, 26 PFASs were screened in 502 water samples originating from Swedish groundwater, surface water, sewage treatment plant (STP) effluents and landfill leachates. The objectives were to establish baseline concentrations of PFASs in the aquatic environment, to screen for potential sources, and to compare PFAS concentrations with guideline values for estimation of potential effects on the ecosystem and human health. In drinking water source areas, the average ∑26PFAS concentration was 8.4 ng L-1 with a median value of 0.6 ng L-1 (n = 172). The drinking water guideline value of 90 ng L-1 for ∑7PFASs (PFPeA, PFHxA, PFHpA, PFOA, PFBS, PFHxS, PFOS) established by the Swedish National Food Agency was exceeded in 4 samples (2% of the total number of samples in this category). In water not used for drinking water, ∑26PFASs concentrations were on average 142 ng L-1 (median 5.4 ng L-1). The high average PFAS concentrations can be explained by the fact that some samples showed extremely high PFAS concentrations with a maximum ∑26PFASs value of 12 900 ng L-1. In surface water, PFOS concentrations exceeded the annual average Environmental Quality Standard (AA-EQS) of the EU Water Framework Directive (WFD) in 42% of the samples. Among the different water categories, the landfill leachates had the highest average concentration of ∑26PFAS with 487 ng L-1 (median 435 ng L-1, n = 10), followed by surface water (average 112 ng L-1, median 4.1 ng L-1, n = 285), groundwater (average 49 ng L-1, median 0.4 ng L-1, n = 164), STP effluents (average 35 ng L-1, median 26 ng L-1; n = 13) and background screening lakes (remote lakes; average 3.4 ng L-1, median 1.4 ng L-1, n = 10). The composition profile of the PFASs differed between the types of waters showing an even distribution of ∑PFCAs, ∑PFSAs and ∑PFAS precursors in groundwater, whereas in all other water categories (surface water, background lakes, STP effluents and landfill leachates), ∑PFCAs were dominant. As FOSA, PFNA, PFDA, and 6:2 FTSA were frequently detected in drinking water source areas (constituted 20%, 7.3%, 5.9%, and 4.4% of the ∑26PFASs, respectively), it is reasonable to consider the inclusion of these in the Swedish drinking water guideline.
AB - Per- and polyfluoroalkyl substances (PFASs) are emerging organic pollutants characterized by their persistency, and bioaccumulation and toxicity potential. In this study, 26 PFASs were screened in 502 water samples originating from Swedish groundwater, surface water, sewage treatment plant (STP) effluents and landfill leachates. The objectives were to establish baseline concentrations of PFASs in the aquatic environment, to screen for potential sources, and to compare PFAS concentrations with guideline values for estimation of potential effects on the ecosystem and human health. In drinking water source areas, the average ∑26PFAS concentration was 8.4 ng L-1 with a median value of 0.6 ng L-1 (n = 172). The drinking water guideline value of 90 ng L-1 for ∑7PFASs (PFPeA, PFHxA, PFHpA, PFOA, PFBS, PFHxS, PFOS) established by the Swedish National Food Agency was exceeded in 4 samples (2% of the total number of samples in this category). In water not used for drinking water, ∑26PFASs concentrations were on average 142 ng L-1 (median 5.4 ng L-1). The high average PFAS concentrations can be explained by the fact that some samples showed extremely high PFAS concentrations with a maximum ∑26PFASs value of 12 900 ng L-1. In surface water, PFOS concentrations exceeded the annual average Environmental Quality Standard (AA-EQS) of the EU Water Framework Directive (WFD) in 42% of the samples. Among the different water categories, the landfill leachates had the highest average concentration of ∑26PFAS with 487 ng L-1 (median 435 ng L-1, n = 10), followed by surface water (average 112 ng L-1, median 4.1 ng L-1, n = 285), groundwater (average 49 ng L-1, median 0.4 ng L-1, n = 164), STP effluents (average 35 ng L-1, median 26 ng L-1; n = 13) and background screening lakes (remote lakes; average 3.4 ng L-1, median 1.4 ng L-1, n = 10). The composition profile of the PFASs differed between the types of waters showing an even distribution of ∑PFCAs, ∑PFSAs and ∑PFAS precursors in groundwater, whereas in all other water categories (surface water, background lakes, STP effluents and landfill leachates), ∑PFCAs were dominant. As FOSA, PFNA, PFDA, and 6:2 FTSA were frequently detected in drinking water source areas (constituted 20%, 7.3%, 5.9%, and 4.4% of the ∑26PFASs, respectively), it is reasonable to consider the inclusion of these in the Swedish drinking water guideline.
KW - PFASs
KW - PFOS
KW - groundwater
KW - landfill leachates
KW - national screening
KW - per- and polyfluoroalkyl substances
KW - sewage treatment plant (STP) effluents
KW - surface water
KW - trend lakes
KW - PFASs
KW - PFOS
KW - groundwater
KW - landfill leachates
KW - national screening
KW - per- and polyfluoroalkyl substances
KW - sewage treatment plant (STP) effluents
KW - surface water
KW - trend lakes
UR - https://res.slu.se/id/publ/71156
M3 - Report
SN - 978-91-576-9386-0
T3 - Rapport / Sveriges lantbruksuniversitet, Institutionen för vatten och miljö
BT - Screening of PFASs in groundwater and surface water
PB - Department of Aquatic Sciences and Assessment, Swedish University of Agricultural Sciences
ER -