Evidence map›Paper›PMID 34779453›Full record

ArticleEnvironmental science. Processes & impacts2021

Surface-water/groundwater boundaries affect seasonal PFAS concentrations and PFAA precursor transformations.

Andrea K Tokranov, Denis R LeBlanc, Heidi M Pickard, Bridger J Ruyle, Larry B Barber, Robert B Hull, Elsie M Sunderland, Chad D Vecitis

Abstract read
In one paragraph

Article in Environmental science. Processes & impacts, 2021. The graph could read no effect estimate from its abstract, so it casts no vote on the map. Cited by 22 papers.

0numbers the graph read from it
0cells of the map it votes in
22citing papers in PubMed
–field-weighted citation impact
1 · What the graph read from it

What it found

Each row is one number read from the abstract, on the scale the paper reported it, with its interval. Left of the dashed line favours the treatment, right favours the comparator. Under each row is the sentence it came from. New to these charts? A ten-minute tutorial.

The abstract states no effect estimate the extractor could read, or names no intervention and outcome on the map, so this paper lights no cell and moves no belief. It is still indexed, cited and linked below.

2 · The registry

The trial behind it

Trials whose registry record cites this paper, or whose number appears in the abstract. A trial that started after this paper was published is citing it as background, not reporting it.

Neither the registry nor the abstract names a trial number. If this is a trial report, that itself is worth knowing.

3 · Its place in the literature

Who cites it

22 citing papers in PubMed.

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  17. Bioaccumulation of Perfluoroalkyl Sulfonamides (FASA).Environmental science & technology letters · 2024
    Article
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  19. Article
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4 · The record

Corrections and comments

PubMed lists nothing against this paper. Absence here is not a guarantee, only a check that was made.

5 · Who and what money

Authors and funding

8 authors.

Andrea K TokranovHarvard John A. Paulson School of Engineering and Applied Sciences, Cambridge, MA 02138, USA. vecitis@seas.harvard.edu.ORCID http://orcid.org/0000-0003-4811-8641
Denis R LeBlancU.S. Geological Survey, Northborough, MA 01532, USA.
Heidi M PickardHarvard John A. Paulson School of Engineering and Applied Sciences, Cambridge, MA 02138, USA. vecitis@seas.harvard.edu.ORCID http://orcid.org/0000-0001-8312-7522
Bridger J RuyleHarvard John A. Paulson School of Engineering and Applied Sciences, Cambridge, MA 02138, USA. vecitis@seas.harvard.edu.ORCID http://orcid.org/0000-0003-1941-4732
Larry B BarberU.S. Geological Survey, Boulder, CO 80303, USA.
Robert B HullU.S. Geological Survey, Northborough, MA 01532, USA.
Elsie M SunderlandHarvard John A. Paulson School of Engineering and Applied Sciences, Cambridge, MA 02138, USA. vecitis@seas.harvard.edu.ORCID http://orcid.org/0000-0003-0386-9548
Chad D VecitisHarvard John A. Paulson School of Engineering and Applied Sciences, Cambridge, MA 02138, USA. vecitis@seas.harvard.edu.ORCID http://orcid.org/0000-0001-8813-4967

Funding

Sources, Transport, Exposure & Effects of PFAS (STEEP) Center - RENEWALP42ES027706 · NIEHS · UNIVERSITY OF RHODE ISLAND · PI Angela L Slitt · 2017 to 2026
$18.9M
NIEHS NIH HHS P42 ES027706
6 · The paper itself

Abstract

Elevated concentrations of per- and polyfluoroalkyl substances (PFAS) in drinking-water supplies are a major concern for human health. It is therefore essential to understand factors that affect PFAS concentrations in surface water and groundwater and the transformation of perfluoroalkyl acid (PFAA) precursors that degrade into terminal compounds. Surface-water/groundwater exchange can occur along the flow path downgradient from PFAS point sources and biogeochemical conditions can change rapidly at these exchange boundaries. Here, we investigate the influence of surface-water/groundwater boundaries on PFAS transport and transformation. To do this, we conducted an extensive field-based analysis of PFAS concentrations in water and sediment from a flow-through lake fed by contaminated groundwater and its downgradient surface-water/groundwater boundary (defined as ≤100 cm below the lake bottom). PFAA precursors comprised 45 ± 4.6% of PFAS (PFAA precursors + 18 targeted PFAA) in the predominantly oxic lake impacted by a former fire-training area and historical wastewater discharges. In shallow porewater downgradient from the lake, this percentage decreased significantly to 25 ± 11%. PFAA precursor concentrations decreased by 85% between the lake and 84-100 cm below the lake bottom. PFAA concentrations increased significantly within the surface-water/groundwater boundary and in downgradient groundwater during the winter months despite lower stable concentrations in the lake water source. These results suggest that natural biogeochemical fluctuations associated with surface-water/groundwater boundaries may lead to PFAA precursor loss and seasonal variations in PFAA concentrations. Results of this work highlight the importance of dynamic biogeochemical conditions along the hydrological flow path from PFAS point sources to potentially affected drinking water supplies.

Indexed as

FluorocarbonsGroundwaterWater Pollutants, ChemicalHumansLakesSeasonsFluorocarbonsWater Pollutants, Chemical

Identifiers

PMID34779453
PMCPMC8673475

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Registered trials

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Read under generation 80e0d062 · epoch 390. Bibliography from PubMed, PubMed Central and OpenAlex; grants from NIH RePORTER; trial links from ClinicalTrials.gov; estimates, votes and beliefs from the OpenQuestion graph.