Perfluoroalkyl acids on suspended particles: Significant transport pathways in surface runoff, surface waters, and subsurface soils
Open accessAbstract
Eroded particles from the source zone could transport a high concentration of perfluoroalkyl acids (PFAAs) to sediments and water bodies. Yet, the contribution of suspended particles has not been systematically reviewed. Analyzing reported studies, we quantitatively demonstrate that suspended particles in surface water can contain significantly higher concentrations of PFAAs than the sediment below, indicating the source of suspended particles are not the sediment but particles eroded and carried from the source zone upstream. The affinity of PFAAs to particles depends on the particle composition, including organic carbon fraction and iron or aluminum oxide content. In soils, most PFAAs are retained within the top 5 m below the ground surface. The distribution of PFAAs in the subsurface varies based on site properties and local weather conditions. The depth corresponding to the maximum concentration of PFAA in soil decreases with an increase in soil organic carbon or rainfall amount received in the catchment areas. We attribute a greater accumulation of PFAAs near the upper layer of the subsurface to an increase in the accumulation of particles eroded from source zones upstream receiving heavy rainfall. Precursor transformation in the aerobic zone is significantly higher than in the anaerobic zone, thereby making the aerobic subsurface zone serve as a long-term source of groundwater pollution. Collectively, these results suggest that suspended particles, often an overlooked vector for PFAAs, can be a dominant pathway for the transport of PFAAs in environments.
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Written from the paper’s full text.
TL;DR
This review synthesizes reported data to argue that suspended particles are an overlooked but potentially dominant transport vector for perfluoroalkyl acids (PFAAs) in surface runoff, surface waters, and subsurface soils. It finds that particle-associated PFAAs can greatly exceed bed-sediment concentrations and that most PFAAs are retained in shallow subsurface, with organic carbon, mineral oxides, rainfall, and aerobic precursor transformation influencing distribution.
Key findings
- Suspended particles in surface waters often contain 1–3 orders of magnitude higher PFAA concentrations than bed sediments, indicating eroded source-zone particles rather than sediment resuspension; PFSAs are enriched more than PFCAs, with Koc values 5.1–5.8 times greater for PFSAs than PFCAs in suspended sediments versus 1.7 times in sediments.
- Most PFAAs are retained within the top 5 m below ground surface; the depth of maximum PFAA concentration decreases with increasing soil organic carbon content or annual precipitation, which the authors attribute to erosion and deposition of impacted particles and to oxic-zone precursor transformation.
- Aerobic precursor biotransformation is an order of magnitude faster than anaerobic transformation (p < 0.02), while no significant difference (p > 0.05) was found among half-lives of non-ionic, anionic, and zwitterionic precursors.
- PFAA sorption to particles and soils is associated with organic carbon, iron oxide, and aluminum oxide content; PFOS adsorption is higher than PFOA adsorption for the same mineralogical properties.
Methods
- Literature search in Web of Science in July 2020 using keyword combinations of “PFAS” with “properties,” “soil,” and “water”; 697 articles were found, 249 were selected after title and abstract screening, and the final synthesis analyzed 35 studies.
- Quantitative comparisons included PFAA concentrations in suspended particles versus bed sediments, normalized vertical subsurface profiles, correlations with soil organic carbon and annual precipitation, and correlations of PFOA/PFOS sorption with soil mineralogy.
- Subsets included 20 studies on PFAA precursor biotransformation, 11 studies on PFOA/PFOS adsorption affinity, 6 studies on mineralogy-related sorption, and 5 studies on vertical PFOA/PFOS distribution within 4 m of the ground surface.
Limitations
- Stated: soil conclusions apply to hotspots because soil PFAA data came from hotspot studies, and background concentrations are not often reported.
- Stated: limited data were available beyond 5 m depth, groundwater table locations were often unreported, hydraulic conductivity data were not provided to confirm the precipitation/erosion hypothesis, and mineral correlations were weak potentially due to interactive effects among minerals.
- Evident: the review relies on heterogeneous published datasets with small subsets for some analyses (e.g., only five studies reported organic carbon content, and six studies were used for mineralogy correlations), which limits causal inference and generalizability; the paper also notes that source apportionment based on particle-associated PFAS requires further environmental forensic work not explored in detail.
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Claims the paper makes
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- Findingown data
Suspended particles in surface water can contain significantly higher concentrations of PFAAs than the sediment below.
“Analyzing reported studies, we quantitatively demonstrate that suspended particles in surface water can contain significantly higher concentrations of PFAAs than the sediment below, indicating the source of suspended particles are not the sediment but particles eroded and carried from the source zone upstream.”
- Also stated in: § 3.1. Surface water · plain
“Our analysis reveals that suspended particles in surface water bodies often contain a disproportionally higher concentration of PFAAs than the sediment below the water columns.”
Quote in the paperSubstantial claim - Also stated in: § 3.1. Surface water · plain
- Findingreasoning
Suspended particles are enriched with perfluoroalkane sulfonic acids (PFSAs) to a greater extent than perfluoroalkyl carboxylic acids (PFCAs).
“The suspended particles are enriched with perfluoroalkane sulfonic acids (PFSAs) to a greater extent than perfluoroalkyl carboxylic acids (PFCAs) (Fig. 2), possibly due to the higher affinity of PFSAs to suspended sediments than that of PFCAs.”
Quote in the paperSubstantial claim - Findingreasoning
The depth corresponding to PFAA concentration maxima decreased with an increase in annual precipitation received at the sites assessed.
“However, our analysis reveals that the depth corresponding to PFAA concentration maxima decreased with an increase in annual precipitation received at the sites assessed (Fig. 5b).”
- Also stated in: § Abstract · plain
“The depth corresponding to the maximum concentration of PFAA in soil decreases with an increase in soil organic carbon or rainfall amount received in the catchment areas.”
Quote in the paperSubstantial claim - Also stated in: § Abstract · plain
- Findingreasoning
PFAAs are accumulated near the surface in areas receiving high annual precipitation.
“In other words, PFAAs are accumulated near the surface in areas receiving high annual precipitation.”
Quote in the paperSubstantial claim - Findingown data
The concentration of most PFAAs decreased steadily with increases in depth surveyed.
“Our analysis reveals that the concentration of most PFAAs decreased steadily with increases in depth surveyed (Fig. 3).”
Quote in the paperSubstantial claim
- Findingown data
Concentration varied widely for all types of PFAAs, except PFOS, within the top 5 m below ground surface at all sites surveyed.
“Most PFAAs are retained within 5 m below ground surface, although concentration varied widely for all types of PFAAs, except PFOS, within the top 5 m below the ground surface at all sites surveyed.”
- Also stated in: § 3.2. Subsurface soil · plain
“Except for PFOS, all other PFAAs showed high variability within the first 5 m below ground surface.”
Quote in the paperSubstantial claim - Also stated in: § 3.2. Subsurface soil · plain
- Findingown data
Most PFAAs are retained within 5 m below ground surface.
“In soils, most PFAAs are retained within the top 5 m below the ground surface.”
- Also stated in: § 3.2. Subsurface soil · plain
“Most PFAAs are retained within 5 m below ground surface, although concentration varied widely for all types of PFAAs, except PFOS, within the top 5 m below the ground surface at all sites surveyed.”
Quote in the paperSubstantial claim - Also stated in: § 3.2. Subsurface soil · plain
- Findingown data
Analyzing the vertical distribution of PFOA and PFOS in subsurface soils within 4 m from ground surface reported in five studies, the depth corresponding to their concentration maxima increases with decreases in the organic carbon content of soil.
“Analyzing the vertical distribution of PFOA and PFOS in subsurface soils within 4 m from ground surface reported in five studies, we found that depth corresponding to their concentration maxima increases with decreases in the organic carbon content of soil (Fig. 5a).”
- Also stated in: § Abstract · plain
“The depth corresponding to the maximum concentration of PFAA in soil decreases with an increase in soil organic carbon or rainfall amount received in the catchment areas.”
Quote in the paperSubstantial claim - Also stated in: § Abstract · plain
- Findingown data
Analyzing 20 studies on biotransformation of PFAA precursors, the PFAA precursor transformation rate by aerobic bacteria is an order of magnitude faster than that of anaerobic bacteria.
“Analyzing 20 studies on the biotransformation of PFAA precursors, we observed that the PFAA precursor transformation rate by aerobic bacteria is an order of magnitude faster than that of anaerobic bacteria (Fig. 4).”
- Also stated in: § Abstract · plain
“Precursor transformation in the aerobic zone is significantly higher than in the anaerobic zone, thereby making the aerobic subsurface zone serve as a long-term source of groundwater pollution.”
Quote in the paperSubstantial claim - Also stated in: § Abstract · plain
- Findingown data
There is no significant difference (p > 0.05) between the half-lives of non-ionic, anionic, and zwitterionic precursors.
“Our analysis shows no significant difference (p > 0.05) between the half-lives of non-ionic, anionic, and zwitterionic precursors.”
Quote in the paperNot a substantial claim - Findingreasoning
Despite relatively high Kd of PFOA and PFHxS, there is significant variability in their concentrations at different depths of the subsurface.
“However, despite relatively high K d of PFOA and PFHxS, there is significant variability in the concentrations at different depths of the subsurface.”
Quote in the paperSubstantial claim - Findingnone given
The subsurface soil depth corresponding to the concentration maxima decreases rapidly with increases in soil organic carbon content.
“The subsurface soil depth corresponding to the concentration maxima decreases rapidly with increases in soil organic carbon content.”
Quote in the paperSubstantial claim - Findingown data
Analyzing 6 studies where sorption of PFAAs to soils and soil properties were reported, the dominant compositional properties affecting PFAA sorption include organic carbon (OC), iron oxide, and aluminum oxides.
“Analyzing 6 studies (Li et al., 2019;Mejia-Avendano et al., 2020;Miao et al., 2017;Milinovic et al., 2015;Nguyen et al., 2020;Wei et al., 2017) where sorption of PFAAs to soils and the soil properties were reported, we found that the dominant compositional properties affecting PFAA sorption include organic carbon (OC), iron oxide, and aluminum oxides (Fig. 6).”
- Also stated in: § Abstract · plain
“The affinity of PFAAs to particles depends on the particle composition, including organic carbon fraction and iron or aluminum oxide content.”
Quote in the paperSubstantial claim - Also stated in: § Abstract · plain
- Findingown data
Analysis of 35 studies reveals a significant role of suspended particles in the transport of PFAAs in surface waters and subsurface soils.
“Analyzing 35 studies, we reveal a significant role of suspended particles on the transport of PFAAs in surface waters and subsurface soils.”
Quote in the paperSubstantial claim - Findingreasoning
The depth corresponding to the concentration maxima is lower in areas receiving higher rainfall intensity.
“Surprisingly, the depth corresponding to the concentration maxima is lower in areas receiving higher rainfall intensity.”
Quote in the paperSubstantial claim - Findingown data
Soil partitioning constant (Kd) of PFOA and PFOS correlates linearly with soil organic carbon, iron oxide content, and aluminum oxide content.
“Correlation of soil partitioning constant (K d ) of PFOA and PFOS with soil properties including (a) organic carbon, (b) iron oxide content, and (c) aluminum oxide content.The dashed lines indicate a linear correlation.”
Quote in the paperSubstantial claim - Findingnone given
In all cases, PFOS adsorption is higher than PFOA adsorption for the same mineralogical properties.
“In all cases, PFOS adsorption is higher than PFOA adsorption for the same mineralogical properties, indicating PFOS are more likely to be transported in association with particles, compared with PFOA.”
Quote in the paperNot a substantial claim - Findingown data
Increase in organic carbon and iron or aluminum oxides content in particles could enhance PFAA adsorption on particles.
“Analyzing the mineralogy of soils in the reported studies, we found that increase in organic carbon and iron or aluminum oxides content in particles could enhance PFAA adsorption on particles”
Quote in the paperSubstantial claim - Findingnone given
Suspended particles in surface waters often contain 1-3 orders of magnitude higher PFAA concentration than bed sediments.
“Suspended particles in surface waters often contain 1-3 orders of magnitude higher PFAA concentration than bed sediments,”
Quote in the paperSubstantial claim - Interpretationown data
The source of suspended particles in surface water is not the sediment but particles eroded and carried from the source zone upstream.
“Analyzing reported studies, we quantitatively demonstrate that suspended particles in surface water can contain significantly higher concentrations of PFAAs than the sediment below, indicating the source of suspended particles are not the sediment but particles eroded and carried from the source zone upstream.”
Quote in the paperSubstantial claim - Interpretationcitation
Suspended particles may be precontaminated by PFAA before being carried by runoff into surface water sources.
“Suspended particles may also be precontaminated by PFAA before being carried by runoff into surface water sources (Chen et al., 2019;Xiao et al., 2012).”
Quote in the paperSubstantial claim0 of 2 sources checked - Premisecitation
In suspended sediments, Koc values of PFSAs are 5.1-5.8 times greater than Koc of PFCAs for the same carbon chain length.
“In suspended sediments, K oc values of PFSAs is 5.1-5.8 times greater than K oc of PFCAs for the same carbon chain length (Ahrens et al., 2010), whereas, in sediments, the K oc values of PFSAs are 1.7 times greater than the K oc values of PFCAs (Higgins and Luthy, 2006).”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Ahrens et al., 2010 source
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- Interpretationcitation
The relative concentration of PFAAs in particles or sediment could depend on their surface chemistry or mineralogy such as the fraction of organic carbon.
“The relative concentration of PFAAs in particles or sediment could depend on their surface chemistry or mineralogy such as the fraction of organic carbon (Higgins and Luthy, 2006;Li et al., 2018Li et al., , 2019)).”
Quote in the paperNot a substantial claim0 of 3 sources checked- cites Higgins and Luthy, 2006 source
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- cites Li et al., 2018
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- cites Li et al., 2019
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- Premisecitation
In sediments, Koc values of PFSAs are 1.7 times greater than Koc values of PFCAs.
“In suspended sediments, K oc values of PFSAs is 5.1-5.8 times greater than K oc of PFCAs for the same carbon chain length (Ahrens et al., 2010), whereas, in sediments, the K oc values of PFSAs are 1.7 times greater than the K oc values of PFCAs (Higgins and Luthy, 2006).”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Higgins and Luthy, 2006 source
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- Interpretationcitation
A higher concentration of PFAAs in suspended particles could be due to their higher specific surface area from small size enhancing adsorption.
“Suspended particles have a higher specific surface area due to their small size which enhances adsorption (Li et al., 2019).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Li et al., 2019
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- Interpretationcitation
Bioaccumulation of PFAAs by algae and other organisms can increase PFAA concentrations in suspended particles.
“In addition, bioaccumulation of PFAAs by algae and other organisms can also increase the PFAA concentrations in suspended particles (Ahrens et al., 2010).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Ahrens et al., 2010 source
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- Interpretationreasoning
The relative contribution of these processes on PFAS retention could vary with soil organic carbon, pore-size distribution, and relative saturation of the soil.
“Thus, the relative contribution of these processes on PFAS retention could vary with several factors: (a) soil organic carbon that affects adsorption on pore walls, (b) the pore-size distribution that affects infiltration rate through the subsurface, and (c) the relative saturation of the soil that affects total air-water interface areas available for PFAA retention.”
Quote in the paperSubstantial claim - Premisecitation
6:2 fluorotelomer thioether propionate has been shown to transform into stable compounds that do not transform to PFAAs under anaerobic conditions.
“For instance, 6:2 fluorotelomer thioether propionate has been shown to transform into stable compounds that do not transform to PFAAs under anaerobic conditions (Yi et al., 2018).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Yi et al., 2018
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- Interpretationcitation
Cationic and zwitterionic precursors are more susceptible to particle-facilitated transport due to their strong affinity to suspended particles that have a net negative surface charge.
“In particular, cationic and zwitterionic precursors are more susceptible to particle-facilitated transport due to their strong affinity to suspended particles that have a net negative surface charge (Ahrens et al., 2010;Chen et al., 2015).”
Quote in the paperNot a substantial claim0 of 2 sources checked - Interpretationcitation
Another cause of inconsistent location for maximum PFAA concentrations within the top 3 m in the subsurface, where conditions are likely more oxic, could be enhanced transformation of polyfluorinated precursors by microbial communities.
“Another cause of an inconsistent location for maximum PFAA concentrations within the top 3 m in the subsurface, where conditions are likely more oxic, could be enhanced transformation of polyfluorinated precursors by microbial communities (Dasu et al., 2013;Hamid et al., 2020;Zhang et al., 2017).”
Quote in the paperSubstantial claim0 of 3 sources checked - Interpretationreasoning
The cause of the trend of shallower PFAA concentration maxima with higher annual precipitation is an increase in erosion in the source zone by high rainfall and a corresponding increase in loading of impacted particles to the area surveyed.
“We attributed the cause of this trend to an increase in erosion in the source zone by high rainfall and a corresponding increase in loading of impacted particles to the area surveyed.”
Quote in the paperSubstantial claim - Premisecitation
Water expansion and contraction during freeze-thaw cycles can release suspended particles from soil.
“Finally, water expansion and contraction during freeze-thaw cycles can release suspended particles from the soil as well (Mohanty et al., 2014).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Mohanty et al., 2014 source
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- Interpretationreasoning
If particles contain sorbed PFAAs, they can transport the PFAAs as well.
“If the particles contain sorbed PFAAs, they can transport the PFAAs as well.”
Quote in the paperSubstantial claim - Premisecitation
The concentration of suspended particles in water above sediments could depend on the rate at which suspended particles agglomerate and deposit on sediments and the rate at which deposited particles are resuspended by fluid turbulence or shear force.
“The concentration of suspended particles in water above sediments could depend on the rate at which the suspended particles can agglomerate and deposit on the sediments and the rate at which the deposited particles are resuspended by fluid turbulence or shear force (Turner and Millward, 2002).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Turner and Millward, 2002
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- Premisecitation
The advancement of air-water interfaces during intermittent rainfall cycles can dislodge particles from the soil trapped at these interfaces.
“Moreover, the advancement of air-water interfaces during intermittent rainfall cycles can also dislodge particles from the soil trapped at these interfaces (Flury and Aramrak, 2017).”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Flury and Aramrak, 2017
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- Premisecitation
Subsurface leaching of PFAS during intermittent infiltration of water was shown to increase with flow rate.
“For instance, subsurface leaching of PFAS during intermittent infiltration of water was shown to increase with flow rate (Gellrich et al., 2012;Hoisaeter et al., 2019).”
Quote in the paperNot a substantial claim0 of 2 sources checked - Interpretationreasoning
Particle association could also reduce the bioavailability of cationic and zwitterionic precursors.
“Particle association could also reduce their bioavailability.”
Quote in the paperSubstantial claim - Interpretationown data
Precursor transformation and thus downward migration of PFASs in the topsoil may proceed at a faster rate.
“The implications are that precursor transformation and thus downward migration of PFASs in the topsoil may proceed at a faster rate.”
Quote in the paperSubstantial claim - Premisecitation
Precursors with an ether group are recalcitrant to microbial cleavage.
“Similarly, precursors with an ether group are recalcitrant to microbial cleavage (Chen et al., 2018).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Chen et al., 2018 source
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- Interpretationreasoning
Once released, suspended particles can move further down into the subsurface.
“Once released, the suspended particles can move further down into subsurface.”
Quote in the paperSubstantial claim - Interpretationreasoning
In addition to desorption, release of suspended particles from surface soil may also contribute to downward migration of PFAA compounds, especially those with high Kd values.
“Therefore, in addition to desorption, the release of suspended particles from the surface soil may also be contributing to the downward migration of PFAA compounds, especially those with high K d values.”
Quote in the paperSubstantial claim - Interpretationreasoning
Biotransformation of cationic and zwitterionic precursors to less sorptive anionic PFAAs may enhance PFAS mobility in the subsurface.
“Biotransformation of cationic and zwitterionic precursors, which strongly bind to negatively charged soil, to less sorptive anionic PFAAs may enhance PFAS mobility in the subsurface.”
Quote in the paperSubstantial claim - Premisecitation
Natural environmental conditions such as dry-wet and freeze-thaw cycles have been shown to accelerate the release of mobile particles in the subsurface.
“In particular, natural environmental conditions such as dry-wet and freeze-thaw cycles have been shown to accelerate the release of mobile particles in the subsurface (Mohanty et al., 2014(Mohanty et al., , 2015)).”
Quote in the paperNot a substantial claim0 of 2 sources checked - Interpretationreasoning
Particles eroded from organic-rich soil could facilitate the transport of PFAAs in water and subsurface, similar to how they enhance the transport of other organic pollutants.
“Thus, particles eroded from organic-rich soil could facilitate the transport of PFAAs in water and subsurface, similar to how they enhance the transport of other organic pollutants (Grolimund et al., 1996).”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Grolimund et al., 1996 source
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- Interpretationown data
Organic carbon is an important factor that can affect peak depth.
“The result indicates that organic carbon is an important factor that can affect peak depth.”
Quote in the paperSubstantial claim - Interpretationreasoning
Resuspension of particles can increase the concentration of PFAS in water.
“The resuspension of particles can increase the concentration of PFAS in the water.”
Quote in the paperSubstantial claim - Premisecitation
Suspended particles can be released from bulk soil by fluctuations in flow rate or pore water chemistry in saturated conditions.
“In saturated conditions, fluctuations in flow rate (Borthakur et al., 2021) or pore water chemistry (Ryan and Gschwend, 1994) can release suspended particles from the bulk soil.”
Quote in the paperSubstantial claim0 of 2 sources checked- cites Borthakur et al., 2021
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- cites Ryan and Gschwend, 1994
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- Premisecitation
In unsaturated conditions, suspended particles adsorbed on air-water interfaces can be released when the interfaces collapse.
“In unsaturated conditions, suspended particles adsorbed on air-water interfaces can be released when the interfaces collapse (Flury and Aramrak, 2017).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Flury and Aramrak, 2017
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- Interpretationreasoning
Suspended particles can be a significant pathway for the transport of PFAAs in the environment.
“Collectively, the results indicate that suspended particles, which are often ignored in previous assessment studies, can be a significant pathway for the transport of PFAAs in the environment.”
Quote in the paperSubstantial claim- Rests on an assumption: Risk assessment studies often overlook the transport of PFAAs in association with suspended particles eroded from source zones.
- Premisecitation
The same processes that release PFAA from air-water interfaces release soil particulates.
“The same processes release soil particulates (Mohanty et al., 2014(Mohanty et al., , 2015)).”
Quote in the paperNot a substantial claim0 of 2 sources checked - Premisecitation
The detection limit and sensitivity of the analytical method used to identify unknown PFAAs and precursors on particles could affect the estimation of particle-associated PFAS.
“The detection limit and sensitivity of the analytical method used to identify unknown PFAAs and precursors on particles could affect the estimation of particle-associated PFAS (Coggan et al., 2019).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Coggan et al., 2019 source
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- Interpretationreasoning
The release of suspended particles by the air-water interface can also enhance the mobility of the associated PFAAs.
“In such cases, the release of suspended particles by the air-water interface can also enhance the mobility of the associated PFAAs.”
Quote in the paperNot a substantial claim - Interpretationreasoning
PFAAs sorbed to colloids can then be transported to the groundwater.
“PFAAs sorbed to the colloids can then be transported to the groundwater.”
Quote in the paperSubstantial claim - Interpretationown data
The transport of PFAA contaminated suspended particles could be responsible for the increase in surface PFAA concentrations with precipitation rate.
“Our analysis showed that this transport of PFAA contaminated suspended particles could be responsible for the increase in surface PFAA concentrations with precipitation rate (Fig. 5b).”
Quote in the paperSubstantial claim - Interpretationreasoning
The source of suspended particles in surface water may not be bed sediments but eroded particles from source zones upstream.
“indicating the source of suspended particles in surface water may not be the sediments but eroded particles from source zones upstream”
Quote in the paperSubstantial claim - Interpretationreasoning
The lower depth of concentration maxima in areas with higher rainfall intensity is attributed to increased erosion of soil from the source zone during high-intensity rainfall, which increases loading of suspended particles and their deposition in the subsurface zone near the ground surface.
“We attribute this result to an increase in erosion of soil from the source zone during high-intensity rainfall, which could increase the loading of suspended particles and their deposition in the subsurface zone near the ground surface.”
Quote in the paperSubstantial claim - Interpretationreasoning
Cationic and zwitterionic PFAS can strongly bind with soil particles compared with PFAAs.
“Thus, these PFAS can strongly bind with soil particles compared with PFAAs.”
Quote in the paperSubstantial claim - Premisecitation
Adsorption of dissolved organic carbon (DOC) on mineral oxides can reduce their affinity to PFAAs.
“Adsorption of dissolved organic carbon (DOC) on these mineral oxides can also reduce their affinity to PFAAs (Wang et al., 2015).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Wang et al., 2015 source
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- Premisecitation
The concentration of PFAA on suspended particles in surface runoff is difficult to quantify because sorbed PFAA resist desorption for analysis.
“High concentrations of PFAA were observed on suspended particles in surface runoff (Xiao et al., 2012), but their concentration is difficult to quantify as the sorbed PFAA resist desorption for analysis (Nguyen et al., 2016).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Nguyen et al., 2016 source
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- Premisecitation
Suspended particles have a high affinity to the air-water interface as well.
“However, the suspended particles have a high affinity to the air-water interface as well (Flury and Aramrak, 2017).”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Flury and Aramrak, 2017
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- Interpretationreasoning
The air-water interface can also retain PFAA which is adsorbed to suspended sediments.
“Therefore, the air-water interface can also retain PFAA which is adsorbed to suspended sediments.”
Quote in the paperSubstantial claim - Premisecitation
The recovery of adsorbed PFAS from solids varies widely based on the solvent type and extraction protocol.
“However, the recovery of adsorbed PFAS from solids varies widely based on the solvent type and extraction protocol (Zhang et al., 2010).”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Zhang et al., 2010 source
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- Premisecitation
Some other iron oxides such as magnetite can be negatively charged in neutral pH conditions.
“It should be noted that some other iron oxides such as magnetite can be negatively charged in neutral pH conditions (Aredes et al., 2013;Carlson and Kawatra, 2013).”
Quote in the paperNot a substantial claim0 of 2 sources checked- cites Aredes et al., 2013 source
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- cites Carlson and Kawatra, 2013
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- Interpretationreasoning
PFOS are more likely to be transported in association with particles compared with PFOA.
“In all cases, PFOS adsorption is higher than PFOA adsorption for the same mineralogical properties, indicating PFOS are more likely to be transported in association with particles, compared with PFOA.”
Quote in the paperSubstantial claim - Premisecitation
Studies using specific soil minerals validated the finding that PFAAs may sorb onto metal oxides such as iron and aluminum oxides including hematite, goethite, and boehmite.
“Nevertheless, studies using specific soil minerals validated our finding.For instance, several studies show that PFAAs may sorb onto metal oxides such as iron and aluminum oxides including hematite, goethite, and boehmite (Gao and Chorover, 2012;Tang et al., 2010;Wang et al., 2012;Zhao et al., 2014) particularly because many iron oxides, may have a net positive surface charge around neutral pH (Hs”
Quote in the paperSubstantial claim0 of 3 sources checked - Premisecitation
Organic carbon can coat iron oxides and block sorption sites.
“For instance, organic carbon can coat iron oxides and block sorption sites (Borggaard et al., 1990).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Borggaard et al., 1990 source
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- Interpretationreasoning
Surface runoff carrying contaminated suspended particles can cause recontamination of sediments in surface water sources, creating secondary hotspots.
“Therefore, surface runoff carrying these contaminated suspended particles can cause recontamination of sediments in surface water sources, creating secondary hotspots in the process.”
Quote in the paperSubstantial claim - Premisecitation
Many iron oxides may have a net positive surface charge around neutral pH.
“particularly because many iron oxides, may have a net positive surface charge around neutral pH (Hsia et al., 1994).”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Hsia et al., 1994 source
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- Interpretationreasoning
Organic-rich suspended sediment could facilitate the transport of PFAAs.
“Thus, organic-rich suspended sediment could facilitate the transport of PFAAs.”
Quote in the paperSubstantial claim - Interpretationreasoning
Enhanced PFAA adsorption on particles increases their ability to serve as a PFAA vector in environments.
“and consequently their ability to serve as a PFAA vector in environments”
Quote in the paperSubstantial claim - Premisecitation
The air-water interface can also leach sorbed PFAAs from the soil when the subsurface is exposed to intermittent rainfall, increasing its mobility through the subsurface to the groundwater.
“On the other hand, the air-water interface can also leach sorbed PFAAs from the soil when the subsurface is exposed to intermittent rainfall, increasing its mobility through the subsurface to the groundwater (Gellrich et al., 2012).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Gellrich et al., 2012 source
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- Interpretationreasoning
Particles could affect the transport of cationic and zwitterionic PFAS to a greater extent than the anionic PFAS.
“Consequently, particles could affect the transport of cationic and zwitterionic PFAS to a greater extent than the anionic PFAS.”
Quote in the paperSubstantial claim - Premisecitation
PFAAs can bind to air-water interfaces, where the hydrophobic tail sticks into the air phase.
“PFAAs can also bind to air-water interfaces (Brusseau, 2019), where the hydrophobic tail sticks into the air phase (Meng et al., 2014).”
Quote in the paperSubstantial claim0 of 2 sources checked - Premisecitation
High concentrations of PFAA were observed on suspended particles in surface runoff.
“High concentrations of PFAA were observed on suspended particles in surface runoff (Xiao et al., 2012), but their concentration is difficult to quantify as the sorbed PFAA resist desorption for analysis (Nguyen et al., 2016).”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Xiao et al., 2012 source
Not checked in the free run.
- Interpretationreasoning
Subsurface soil could serve as a secondary source for long-term release of PFAAs into groundwater.
“indicating subsurface soil could serve as a secondary source for longterm release of PFAAs into groundwater”
- Also stated in: § 5. Conclusions · hedged
“Most PFAS are located near the surface indicating subsurface as a long-term reservoir of PFAS.”
Quote in the paperSubstantial claim - Also stated in: § 5. Conclusions · hedged
- May combine two claims. 26
- Classified as probably not a substantial claim. 12
May combine two claims.
FindingreasoningBiotransformation depends on functional groups on the precursors: hydroxyl groups are highly susceptible to enzymatic transformation whereas the urethane group is least susceptible.
“The analysis also reveals that biotransformation depends on functional groups on the precursors: hydroxyl groups are highly susceptible to enzymatic transformation whereas the urethane group is least susceptible, possibly due to the unavailability of urethane transforming enzymes in most soil microorganisms.”
Quote in the paperNot a substantial claimMay combine two claims.
Findingnone givenPFAA concentration in subsurface soil is typically high within the top 5 m below ground surface and decreases rapidly thereafter.
“The concentration of PFAAs in subsurface soil is typically high within the top 5 m below ground surface, but the concentration decreased thereafter rapidly”
Quote in the paperSubstantial claimMay combine two claims.
FindingreasoningThe correlation between PFAA sorption and the dominant compositional properties is weak, potentially because of the interactive effect between these minerals.
“However, it should be noted that the correlation is weak, potentially because of the interactive effect between these minerals.”
Quote in the paperNot a substantial claimMay combine two claims.
Interpretationown dataSuspended particles could transport a significant amount of PFAAs in surface water and recontaminate sediments.
“Nevertheless, our result indicates that suspended particles could transport a significant amount of PFAAs in surface water and recontaminate sediments.”
Quote in the paperSubstantial claimMay combine two claims.
Study design and conductnone givenLimited data were available beyond 5 m depth, and groundwater table locations in most sites were not reported.
“There was also limited data available beyond 5 m depth, and the groundwater table locations in most sites were not reported.”
Quote in the paperNot a substantial claimMay combine two claims.
PremisecitationAqueous PFAAs in infiltrating water have been shown to adsorb on pore walls, infiltrate into the soil matrix, or accumulate at air-water interfaces.
“Aqueous PFAAs in infiltrating water have been shown to adsorb on pore walls, infiltrate into the soil matrix, or accumulate at air-water interfaces (Brusseau, 2019;Lyu et al., 2018;Meng et al., 2014).”
Quote in the paperSubstantial claim0 of 3 sources checkedMay combine two claims.
PremisecitationVariability in data increases with decrease in Kd of the compound, as desorption of PFAAs increases with decrease in Kd.
“This is supported by the fact that the variability in data increases with the decrease in K d of the compound, as the desorption of PFAAs increase with the decrease in K d of the compound (Milinovic et al., 2015).”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Milinovic et al., 2015 source
Not checked in the free run.
May combine two claims.
InterpretationreasoningPFOS has a high affinity and low desorption coefficient, so its concentration profile in the subsurface exhibited the lowest variability.
“Because PFOS has a high affinity and low desorption coefficient, its concentration profile in the subsurface exhibited the lowest variability.”
Quote in the paperSubstantial claimProbably not a substantial claim: may not pass S3 (load-bearing).
PremisecitationA previous study observed an increase in PFAA sorption onto the soil with an increase in organic carbon content and decreasing clay content.
“A previous study (Anderson et al., 2019) observed an increase in PFAA sorption onto the soil with an increase in organic carbon content and decreasing clay content.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Anderson et al., 2019 source
Not checked in the free run.
May combine two claims.
InterpretationcitationAreas receiving high rainfall amounts can deposit more impacted particles downstream, most of which are filtered out in topsoil.
“Consequently, areas receiving high rainfall amounts can deposit more impacted particles downstream, most of which are filtered out in topsoil (Tondera et al., 2013).”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Tondera et al., 2013
Not checked in the free run.
May combine two claims.
InterpretationreasoningParticle-associated PFAA transport could lower the effectiveness of remediation of impacted sediments and delay cleanup.
“This could lower the effectiveness of remediation of impacted sediments in a surface water body and delay the cleanup effort of sediment.”
Quote in the paperSubstantial claimProbably not a substantial claim: may not pass S3 (load-bearing).
InterpretationcitationOther soil properties such as hydraulic conductivity, soil chemical heterogeneity, air-water interface, and protein, iron oxide, and manganese oxide content may also contribute to variable PFAA transport in subsurface soil.
“It should be noted that other soil properties such as hydraulic conductivity, soil chemical heterogeneity, air-water interface, and protein, iron oxide, and manganese oxide content may also contribute to variable PFAA transport in subsurface soil (Gellrich et al., 2012;Guelfo et al., 2020;Hoisaeter et al., 2019;Longstaffe et al., 2012;Lyu et al., 2018;Ololade et al., 2016).”
Quote in the paperNot a substantial claim0 of 3 sources checkedMay combine two claims.
InterpretationcitationAccumulation of PFAA and PFAA-containing particles in subsurface soil and transformation of PFAA precursors in aerobic conditions could make subsurface soils serve as a secondary source for PFAAs to groundwater.
“However, accumulation of PFAA and PFAAcontaining particles in subsurface soil and transformation of PFAA precursors in aerobic conditions could make subsurface soils serve as a secondary source for PFAAs to groundwater (Weber et al., 2017).”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Weber et al., 2017 source
Not checked in the free run.
Probably not a substantial claim: may not pass S3 (load-bearing).
InterpretationreasoningThese factors are expected to affect the soil depth corresponding to maximum PFAA concentration.
“Thus, these factors are expected to affect the soil depth corresponding to maximum PFAA concentration.”
Quote in the paperNot a substantial claimMay combine two claims.
PremisecitationPFAAs may migrate down the subsurface due to leaching and redistribution, and sorbed PFAS can desorb and leach leading to downward migration.
“First, PFAAs may migrate down the subsurface due to leaching and redistribution of PFAAs in the subsurface.Sorbed PFAS compounds can desorb and leach from the soil, which can lead to their downward migration through the subsurface (Gellrich et al., 2012).”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Gellrich et al., 2012 source
Not checked in the free run.
Probably not a substantial claim: may not pass S3 (load-bearing).
PremisecitationThe same previous study observed an increase in PFAA transport with the degree of flushing.
“Moreover, they also observed an increase in PFAA transport with the degree of flushing.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Anderson et al., 2019 source
Not checked in the free run.
Probably not a substantial claim: may not pass S1 (asserted), S3 (load-bearing), S4 (based).
InterpretationreasoningThe concentration maxima of PFAS compounds should move to deeper layers in subsurface soil with an increased precipitation rate.
“Thus, the concentration maxima of PFAS compounds should move to deeper layers in subsurface soil with an increased precipitation rate.”
Quote in the paperNot a substantial claimProbably not a substantial claim: may not pass S3 (load-bearing). May combine two claims.
PremisecitationAn increase in precipitation in an area could increase the amount of water flushed through subsurface soil, which could increase the desorption of PFAS from subsurface soil to groundwater.
“Generally, it is expected that an increase in precipitation in an area could increase the amount of water flushed through subsurface soil, which could increase the desorption of PFAS from subsurface soil to groundwater (Anderson et al., 2019).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Anderson et al., 2019 source
Not checked in the free run.
May combine two claims.
Premisenone givenThe subsurface can adsorb aqueous PFAAs and filter PFAA-impacted particles from infiltrating water, and the impacted region can subsequently release the PFAAs over longer periods.
“The subsurface can also adsorb aqueous PFAAs and filter PFAAimpacted particles from infiltrating water, and the impacted region can subsequently release the PFAAs over longer periods.”
Quote in the paperSubstantial claimMay combine two claims.
PremisecitationSuspended particles can be removed from pore water by diffusion, straining or sedimentation.
“Suspended particles can be removed from the pore water by diffusion, straining or sedimentation (Bradford et al., 2002;Flury and Qiu, 2008).”
Quote in the paperNot a substantial claim0 of 2 sources checked- cites Bradford et al., 2002
Not checked in the free run.
- cites Flury and Qiu, 2008
Not checked in the free run.
Probably not a substantial claim: may not pass S3 (load-bearing). May combine two claims.
PremisecitationPFAS and their precursors can be removed by adsorption to soil minerals, air-water interfaces, and microbial biomass or roots, translocated into plants, and degraded or transformed by soil microorganisms.
“Briefly, PFAS and their precursors can be removed by adsorption to soil minerals, air-water interfaces, and microbial biomass or roots, translocated into plants, and degraded or transformed by soil microorganisms.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Sharifan et al., 2021 source
Not checked in the free run.
May combine two claims.
InterpretationcitationAdsorption of cationic and zwitterionic precursors to soil minerals could reduce their bioavailability, consequently the likelihood of them being transformed to PFAAs.
“Adsorption of cationic and zwitterionic precursors to soil minerals could reduce their bioavailability, consequently the likelihood of them being transformed to PFAAs (Mejia-Avendano et al., 2020).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Mejia-Avendano et al., 2020
Not checked in the free run.
Probably not a substantial claim: may not pass S1 (asserted), S3 (load-bearing), S4 (based). May combine two claims.
InterpretationreasoningAnother possibility for high accumulation of PFAAs near the surface compared to deeper soil in wet climates is that deeper soils in wetter climates remain submerged most of the time, developing anoxic conditions, while near-surface soil could drain and become oxic.
“Another possibility of the high accumulation of PFAAs near the surface compared to deeper soil in wet climates is that deeper soils in wetter climates remain submerged most of the time, thereby developing anoxic conditions.In contrast, near-surface soil could drain and become oxic.”
Quote in the paperNot a substantial claimProbably not a substantial claim: may not pass S3 (load-bearing).
InterpretationreasoningPerturbation of air-water interfaces during dry-wet and freeze-thaw cycles could release PFAA attached to air-water interfaces.
“Perturbation of air-water interfaces during dry-wet and freeze-thaw cycles could release PFAA attached to air-water interfaces.”
Quote in the paperNot a substantial claimMay combine two claims.
Premisenone givenThe air-water interface is dynamic and collapses during rewetting.
“However, the air-water interface is dynamic and collapses during rewetting.”
Quote in the paperNot a substantial claimMay combine two claims.
PremisecitationSubsurface soils naturally experience dry-wet and freeze-thaw cycles, which can accelerate the mobilization of particles and particle-associated pollutants.
“Subsurface soils naturally experience dry-wet and freeze-thaw cycles, which can accelerate the mobilization of particles and particleassociated pollutants (Mohanty et al., 2014).”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Mohanty et al., 2014
Not checked in the free run.
May combine two claims.
Interpretationnone givenSurface runoff carries PFAAs and eroded particles impacted with PFAAs from source zones to surface waters.
“Surface runoff carries PFAAs and eroded particles impacted with PFAAs from the source zones to surface waters.”
Quote in the paperSubstantial claimProbably not a substantial claim: may not pass S4 (based). May combine two claims.
Premisenone givenCationic and zwitterionic PFAS have positive charges, whereas most natural soil particles have a net negative charge.
“Cationic and zwitterionic PFAS have positive charges, whereas most natural soil particles have a net negative charge.”
Quote in the paperNot a substantial claimMay combine two claims.
Interpretationnone givenImpacted runoff can infiltrate into subsurface soil, where PFAAs can adsorb on soil or impacted particles can be deposited in topsoil, which can serve as a long-term source for groundwater pollution.
“Impacted runoff can infiltrate into the subsurface soil where PFAAs can adsorb on soil or impacted particles can be deposited in topsoil, which can serve as a long-term source for groundwater pollution.”
Quote in the paperSubstantial claimProbably not a substantial claim: may not pass S3 (load-bearing).
Study design and conductnone givenHydraulic conductivity data was not provided in the assessed studies to confirm the hypothesis that soil types determine the amount of runoff that infiltrates into the ground.
“However, hydraulic conductivity data was not provided in the assessed studies to confirm this hypothesis.”
Quote in the paperNot a substantial claimMay combine two claims.
PremisecitationLimited studies have examined the transport of cationic and zwitterionic PFAS, and none of these studies considered particle-mediated transport.
“However, limited studies have examined the transport of cationic and zwitterionic PFAS (Barzen--Hanson et al., 2017;Mejia-Avendano et al., 2020;Nickerson et al., 2021;Xiao et al., 2019), and none of these studies considered particle-mediated transport.”
Quote in the paperSubstantial claim0 of 3 sources checkedClassified as probably not a substantial claim.
InterpretationreasoningThe biotransformation rate of precursors at deeper depths will be lower in wetter climates than drier climates.
“Thus, the biotransformation rate of precursors at the deeper depths will be lower in wetter climates than drier climates.”
Quote in the paperSubstantial claimMay combine two claims.
PremisecitationThe air-water interface can retain significant amounts of PFAAs and has been found to be the major retention mechanism of PFAAs in the subsurface.
“The air-water interface can retain significant amounts of PFAAs and has been found to be the major retention mechanism of PFAAs in the subsurface (Brusseau, 2018).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Brusseau, 2018 source
Not checked in the free run.
May combine two claims.
PremisecitationMost studies filter or centrifuge samples before analysis, and these steps remove particles and could potentially lower the measured PFAA concentration in water samples.
“Most studies filter or centrifuge samples before analysis (Qiu et al., 2010;Zhou et al., 2013).These steps remove particles and could potentially lower the measured PFAA concentration in the water samples.”
Quote in the paperSubstantial claim0 of 2 sources checked- cites Qiu et al., 2010
Not checked in the free run.
- cites Zhou et al., 2013 source
Not checked in the free run.
The authors state this as an assumption.
Advection of dissolved PFAAs is the dominant mechanism of transport in surface waters and subsurface.
“Advection of dissolved PFAAs is currently assumed to be the dominant mechanism of transport in surface waters and subsurface (Dauchy et al., 2019b(Dauchy et al., , 2019a;;Xiao et al., 2012), whereas sorption to soil or sediment is considered the primary retention mechanism.”
The paper relies on this without support.
Sorption to soil or sediment is the primary retention mechanism for PFAAs.
“Advection of dissolved PFAAs is currently assumed to be the dominant mechanism of transport in surface waters and subsurface (Dauchy et al., 2019b(Dauchy et al., , 2019a;;Xiao et al., 2012), whereas sorption to soil or sediment is considered the primary retention mechanism.”
The paper relies on this without support.
The subsurface zone acts as a natural filter to remove particles in surface runoff and adsorb pollutants.
“Impacted surface runoff passes through the subsurface zone before reaching groundwater, so the subsurface zone acts as a natural filter to remove particles in surface runoff and adsorb pollutants.”
The paper relies on this without support.
Soil types, not only precipitation amount, determine the amount of runoff that infiltrates into the ground.
“It should be noted that the soil types, not only the precipitation amount, determine the amount of runoff that infiltrates into the ground.”
The paper relies on this without support.
The role of suspended particles on PFAA transport is relatively unexplored.
“The role of suspended particles on PFAA transport is relatively unexplored, although their role in enhancing the transport of other organic chemicals such as polycyclic aromatic hydrocarbons (Guo et al., 2007), chlorinated solvents (Tanabe and Tatsukawa, 1983), and heavy metals (Zhang, 1999) has been well established.”
The paper relies on this without support.
The relevance of suspended particles on PFAA distribution in the environment has not been critically reviewed.
“However, the relevance of suspended particles on PFAA distribution in the environment has not been critically reviewed, although the fate and transport of aqueous PFAA in the environment have been reviewed extensively (Ahmed et al., 2020;Ahrens and Bundschuh, 2014;Armitage et al., 2009;Banzhaf et al., 2017;Brusseau et al., 2020;Lam et al., 2017;Nadal and Domingo, 2014;Prevedouros et al., 2006;Shar”
The paper relies on this without support.
Risk assessment studies often overlook the transport of PFAAs in association with suspended particles eroded from source zones.
“Risk assessment studies often overlook the transport of PFAAs in association with suspended particles eroded from the source zones.”
“suspended particles, which are often ignored in previous assessment studies”
Claims other papers make about this one
Each is checked against this paper’s own text: does it say what the citing paper says it does?
The fate and transport of sediment-bound PFAS in rivers, lakes, estuaries, and open waters are governed by different hydrological processes, making watershed-level sediment monitoring critical.
“While there are several other studies on PFAS occurrence in sediment, the fate and transport of sedimentbound PFAS in rivers, lakes, estuaries, and open waters are governed by different hydrological processes, 29,30 rendering it critical to perform watershed level sediment monitoring”
From Per- and Polyfluoroalkyl Substances in Surface Water and Fluvial Sediments of a Rural Gulf Coast Watershed: A Year-long Spatiotemporal Assessment (2026) · cites this paper as [30]
The Introduction and §3.1 (page unavailable) describe runoff, flow velocity, deposition, and turbulence as processes affecting particle-bound PFAA transport in surface waters. The paper does not distinguish hydrological processes across rivers, lakes, estuaries, and open waters. The watershed-level monitoring recommendation follows the citations in the citing sentence and appears to be the citing authors’ conclusion, not a separate claim attributed to this source. (LLM, conf=0.82)
Experimental — accuracy not yet measuredBiotransformation of retained PFAS precursors into less sorptive terminal PFASs is an expected phenomenon in soil media.
“Biotransformation of the retained PFAS precursors into less sorptive terminal PFASs (e.g., SC-PFCAs, PFOA, and PFOS), which depends on oxic/anoxic conditions at the accumulation depth, is also an expected phenomenon in soil media.”
From Occurrence, Concentration, and Distribution of 35 PFASs and Their Precursors Retained in 20 Stormwater Biofilters (2024) · cites this paper as [49]
Section 3.2 (Subsurface soil; page unavailable) says that strongly retained cationic and zwitterionic precursors may transform into less sorptive anionic PFAAs, and reports faster precursor transformation under aerobic than anaerobic conditions. It presents the soil-mobility consequence as a possibility, not an expected outcome for retained PFAS precursors generally, and does not identify SC-PFCAs, PFOA, and PFOS as the products of that transformation. (LLM, conf=0.82)
Experimental — accuracy not yet measuredPFSA are reported to adsorb more readily to riverine solids than PFCA.
“Generally, PFSA are reported to adsorb more readily to riverine solids than PFCA (Borthakur et al., 2021; Wang et al., 2023).”
From Occurrence of emerging and persistent organic pollutants in the rivers Cam, Ouse and Thames, UK (2025) · cites this paper as Borthakur et al., 2021
Some studied pollutants, especially PFAS, have high sorptive properties, and thus the extent of water pollution by these substances cannot be inferred from analysis of water samples only.
“Furthermore, some of the studied pollutants, especially PFAS, have been reported to possess high sorptive properties (Borthakur et al., 2021; Wang et al., 2023; Folorunsho et al., 2024), and thus the extent of water pollution by these substances cannot be inferred from the analysis of water samples only.”
From Occurrence of emerging and persistent organic pollutants in the rivers Cam, Ouse and Thames, UK (2025) · cites this paper as Borthakur et al., 2021
PFASs released from source zones during weathering and drainage events are delivered either via suspended solids in runoffs to surface waters or via leaching to groundwater.
“PFASs released from source zones during weathering and drainage events are delivered either via suspended solids in runoffs to surface waters or via leaching to groundwater.11−13”
From Sources and Pathways of PFAS Occurrence in Water Sources: Relative Contribution of Land-Applied Biosolids in an Agricultural Dominated Watershed (2025) · cites this paper as [12]
Site N60 is likely impacted by short-chain PFAAs that leached into tile drains following land application of biosolids in addition to surface runoff of long-chain PFAS sorbed to the soil.
“The site is likely impacted by short-chain PFAAs that leached into tile drains following land application of biosolids in addition to surface runoff of long-chain PFAS sorbed to the soil.12”
From Sources and Pathways of PFAS Occurrence in Water Sources: Relative Contribution of Land-Applied Biosolids in an Agricultural Dominated Watershed (2025) · cites this paper as [12]
Self-check
Percentages, sums and reported differences re-computed from the paper’s own numbers.
Each contradiction between two passages listed here was confirmed by an independent check.
Figure 5b is described as showing a different outcome
MinorSection 4.2 cites Fig. 5b as evidence that surface PFAA concentrations increase with precipitation. The figure caption instead identifies its outcome as the subsurface depth of maximum PFAA concentration, not surface concentration.
“Our analysis showed that this transport of PFAA contaminated suspended particles could be responsible for the increase in surface PFAA concentrations with precipitation rate (Fig. 5b).”
“Fig. 5. Change in the depth of maximum PFAA concentrations in the subsurface with (a) soil organic carbon content (%) and (b) annual precipitation (cm year -1 ).”
Cites
Sunderland, E. M., Hu, X. C., Dassuncao, C., Tokranov, A. K., Wagner, C. C., & Allen, J. G. (2019) · Journal of Exposure Science & Environmental Epidemiology · doi:10.1038/s41370-018-0094-1 · Cited by 2,786 · see citing works
Sources, fate and transport of perfluorocarboxylates
Prevedouros, K., Cousins, I. T., Buck, R. C., & Korzeniowski, S. H. (2006) · Environmental Science & Technology · doi:10.1021/es0512475 · Cited by 2,594 · see citing works
Sorption of Perfluorinated Surfactants on Sediments
Higgins, C. P., & Luthy, R. G. (2006) · Environmental Science & Technology · doi:10.1021/es061000n · Cited by 1,563 · see citing works
Persistence of Perfluoroalkyl Acid Precursors in AFFF-Impacted Groundwater and Soil
Houtz, E. F., Higgins, C. P., Field, J. A., & Sedlak, D. L. (2013) · Environmental Science & Technology · doi:10.1021/es4018877 · Cited by 849 · see citing works
PFAS concentrations in soils: Background levels versus contaminated sites
Brusseau, M. L., Anderson, R. H., & Guo, B. (2020) · Science of The Total Environment · doi:10.1016/j.scitotenv.2020.140017 · Cited by 817 · see citing works
Fate and Effects of Poly- and Perfluoroalkyl Substances in the Aquatic Environment: A Review
Ahrens, L., & Bundschuh, M. (2014) · Environmental Toxicology and Chemistry · doi:10.1002/etc.2663 · Cited by 817 · see citing works
Physical factors affecting the transport and fate of colloids in saturated porous media
BRADFORD, S. A., Yates, S. R., Bettahar, M., & Šimůnek, J. (2002) · Water Resources Research · doi:10.1029/2002wr001340 · Cited by 815 · see citing works
Nguyen, T. M. H., Bräunig, J., Thompson, K., Thompson, J., Kabiri, S., Navarro, D. A., Kookana, R. S., Grimison, C., Barnes, C. M., Higgins, C. P., et al. (2020) · Environmental Science & Technology · doi:10.1021/acs.est.0c05705 · Cited by 523 · see citing works
Suspended Particles: Their Role in Estuarine Biogeochemical Cycles
Turner, A., & Millward, G. E. (2002) · Estuarine Coastal and Shelf Science · doi:10.1006/ecss.2002.1033 · Cited by 464 · see citing works
Guelfo, J. L., & Higgins, C. P. (2013) · Environmental Science & Technology · doi:10.1021/es3048043 · Cited by 436 · see citing works
Ahrens, L., Taniyasu, S., Yeung, L. W. Y., Yamashita, N., Lam, P. K. S., & Ebinghaus, R. (2010) · Chemosphere · doi:10.1016/j.chemosphere.2010.01.045 · Cited by 418 · see citing works
D’Agostino, L. A., & Mabury, S. A. (2014) · Environmental Science & Technology · doi:10.1021/es403729e · Cited by 387 · see citing works
Sorption behaviour of perfluoroalkyl substances in soils
Milinovic, J., Lacorte, S., Vidal, M., & Rigol, A. (2015) · Science of The Total Environment · doi:10.1016/j.scitotenv.2014.12.017 · Cited by 387 · see citing works
Adsorption of perfluoroalkyl substances on microplastics under environmental conditions
Llorca, M., Schirinzi, G. F., Martínez, M., Barceló, D., & Farré, M. (2018) · Environmental Pollution · doi:10.1016/j.envpol.2017.12.075 · Cited by 383 · see citing works
Guo, W., He, M., Yang, Z., Lin, C., Quan, X., & Wang, H. (2007) · Chemosphere · doi:10.1016/j.chemosphere.2006.12.072 · Cited by 347 · see citing works
Self-citationGrolimund, D., Borkovec, M., Barmettler, K., & Sticher, H. (1996) · Environmental Science & Technology · doi:10.1021/es960246x · Cited by 339 · see citing works
Li, Y., Oliver, D. P., & Kookana, R. S. (2018) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2018.01.167 · Cited by 331 · see citing works
Zhou, Z., Liang, Y., Shi, Y., Xu, L., & Cai, Y. (2013) · Environmental Science & Technology · doi:10.1021/es402120y · Cited by 324 · see citing works
Brusseau, M. L. (2018) · Science of The Total Environment · doi:10.1016/j.scitotenv.2017.09.065 · Cited by 306 · see citing works
Hepburn, E., Madden, C., Szabo, D., Coggan, T. L., Clarke, B., & Currell, M. (2019) · Environmental Pollution · doi:10.1016/j.envpol.2019.02.018 · Cited by 289 · see citing works
Influence of organic matter on phosphate adsorption by aluminium and iron oxides in sandy soils
BORGGAARD, O. K., JDRGENSEN, S. S., MOBERG, J. P., & RABEN‐LANGE, B. (1990) · Journal of Soil Science · doi:10.1111/j.1365-2389.1990.tb00078.x · Cited by 285 · see citing works
Filipovic, M., Woldegiorgis, A., Norström, K., Bibi, M., Lindberg, M., & Österås, A.-H. (2015) · Chemosphere · doi:10.1016/j.chemosphere.2014.09.005 · Cited by 284 · see citing works
Effect of solution chemistry on the adsorption of perfluorooctane sulfonate onto mineral surfaces
Tang, C. Y., Shiang Fu, Q., Gao, D., Criddle, C. S., & Leckie, J. O. (2010) · Water Research · doi:10.1016/j.watres.2010.01.038 · Cited by 284 · see citing works
Adsorption behavior of perfluorooctanesulfonate (PFOS) and perfluorooctanoate (PFOA) on boehmite
Wang, F., Liu, C., & Shih, K. (2012) · Chemosphere · doi:10.1016/j.chemosphere.2012.06.071 · Cited by 260 · see citing works
Li, F., Fang, X., Zhou, Z., Liao, X., Zou, J., Yuan, B., & Sun, W. (2018) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2018.08.209 · Cited by 259 · see citing works
Adsorption of PFOA at the air-water interface during transport in unsaturated porous media
Lyu, Y., Brusseau, M. L., Chen, W., Yan, N., Fu, X., & Lin, X. (2018) · Environmental Science & Technology · doi:10.1021/acs.est.8b02348 · Cited by 259 · see citing works
Per- and Polyfluoroalkyl Substances in Landfill Leachate: Patterns, Time Trends, and Sources
Benskin, J. P., Li, B., Ikonomou, M. G., Grace, J. R., & Li, L. Y. (2012) · Environmental Science & Technology · doi:10.1021/es302471n · Cited by 258 · see citing works
Armitage, J. M., MacLeod, M., & Cousins, I. T. (2009) · Environmental Science & Technology · doi:10.1021/es900753y · Cited by 257 · see citing works
Gao, X., & Chorover, J. (2012) · Environmental Chemistry · doi:10.1071/en11119 · Cited by 251 · see citing works
Zhao, L., Bian, J., Zhang, Y., Zhu, L., & Liu, Z. (2014) · Chemosphere · doi:10.1016/j.chemosphere.2014.03.098 · Cited by 247 · see citing works
Banzhaf, S., Filipovic, M., Lewis, J., Sparrenbom, C. J., & Barthel, R. (2017) · Ambio · doi:10.1007/s13280-016-0848-8 · Cited by 245 · see citing works
Høisæter, Å., Pfaff, A., & Breedveld, G. D. (2019) · Journal of Contaminant Hydrology · doi:10.1016/j.jconhyd.2019.02.010 · Cited by 243 · see citing works
Colloid Movement in Unsaturated Porous Media: Recent Advances and Future Directions
DeNovio, N. M., Saiers, J. E., & Ryan, J. N. (2004) · Vadose Zone Journal · doi:10.2113/3.2.338 · Cited by 240 · see citing works
Ryan, J. N., & Gschwend, P. M. (1994) · Journal of Colloid and Interface Science · doi:10.1006/jcis.1994.1139 · Cited by 231 · see citing works
Spatial Trends of Anionic, Zwitterionic, and Cationic PFASs at an AFFF-Impacted Site
Nickerson, A., Rodowa, A. E., Adamson, D. T., Field, J. A., Kulkarni, P. R., Kornuc, J. J., & Higgins, C. P. (2021) · Environmental Science & Technology · doi:10.1021/acs.est.0c04473 · Cited by 228 · see citing works
Self-citationWeber, A. K., Barber, L. B., LeBlanc, D. R., Sunderland, E. M., & Vecitis, C. D. (2017) · Environmental Science & Technology · doi:10.1021/acs.est.6b05573 · Cited by 227 · see citing works
The removal of arsenic from water using natural iron oxide minerals
Aredes, S., Klein, B., & Pawlik, M. (2012) · Journal of Cleaner Production · doi:10.1016/j.jclepro.2012.01.029 · Cited by 222 · see citing works
Guelfo, J. L., & Adamson, D. T. (2018) · Environmental Pollution · doi:10.1016/j.envpol.2018.01.066 · Cited by 216 · see citing works
Self-citationEnhanced Extraction of AFFF-Associated PFASs from Source Zone Soils
Nickerson, A., Maizel, A. C., Kulkarni, P. R., Adamson, D. T., Kornuc, J. J., & Higgins, C. P. (2020) · Environmental Science & Technology · doi:10.1021/acs.est.0c00792 · Cited by 214 · see citing works
Self-citationDauchy, X., Boiteux, V., Bach, C., Rosin, C., & Munoz, J.-F. (2017) · Chemosphere · doi:10.1016/j.chemosphere.2017.05.056 · Cited by 198 · see citing works
de Solla, S. R., De Silva, A. O., & Letcher, R. J. (2012) · Environment International · doi:10.1016/j.envint.2011.09.011 · Cited by 198 · see citing works
Managed aquifer recharge implementation criteria to achieve water sustainability
Alam, S., Borthakur, A., Ravi, S., Gebremichael, M., & Mohanty, S. K. (2021) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2021.144992 · Cited by 197 · see citing works
Self-citationXiao, F., Jin, B., Golovko, S. A., Golovko, M. Y., & Xing, B. (2019) · Environmental Science & Technology · doi:10.1021/acs.est.9b05379 · Cited by 197 · see citing works
Behavior of perfluorinated compounds in soils during leaching experiments
Gellrich, V., Stahl, T., & Knepper, T. P. (2012) · Chemosphere · doi:10.1016/j.chemosphere.2012.02.011 · Cited by 195 · see citing works
Characterization of arsenate adsorption on hydrous iron oxide using chemical and physical methods
Hsia, T.-H., Lo, S.-L., Lin, C.-F., & Lee, D.-Y. (1994) · Colloids and Surfaces A Physicochemical and Engineering Aspects · doi:10.1016/0927-7757(94)02752-8 · Cited by 192 · see citing works
Dauchy, X., Boiteux, V., Colin, A., Hémard, J., Bach, C., Rosin, C., & Munoz, J.-F. (2019) · Chemosphere · doi:10.1016/j.chemosphere.2018.10.003 · Cited by 192 · see citing works
Liu, Y., Zhang, Y., Li, J., Wu, N., Li, W., & Niu, Z. (2019) · Environmental Pollution · doi:10.1016/j.envpol.2018.11.113 · Cited by 191 · see citing works
Colloid Movement in Unsaturated Porous Media: Recent Advances and Future Directions
DeNovio, N. M., Saiers, J. E., & Ryan, J. N. (2004) · Vadose Zone Journal · doi:10.2136/vzj2004.0338 · Cited by 190 · see citing works
Lam, N. H., Cho, C.-R., Kannan, K., & Cho, H.-S. (2017) · Journal of Hazardous Materials · doi:10.1016/j.jhazmat.2016.04.010 · Cited by 188 · see citing works
Mejia-Avendaño, S., Zhi, Y., Yan, B., & Liu, J. (2020) · Environmental Science & Technology · doi:10.1021/acs.est.9b04989 · Cited by 185 · see citing works
Fate and transport of per- and polyfluoroalkyl substances (PFASs) in the vadose zone
Sharifan, H., Bagheri, M., Wang, D., Burken, J. G., Higgins, C. P., Liang, Y., Liu, J., Schaefer, C. E., & Blotevogel, J. (2021) · Science of The Total Environment · doi:10.1016/j.scitotenv.2021.145427 · Cited by 180 · see citing works
Self-citationAhmed, M. B., Johir, M. A. H., McLaughlan, R., Nguyen, L. N., Xu, B., & Nghiem, L. D. (2020) · Science of The Total Environment · doi:10.1016/j.scitotenv.2020.141251 · Cited by 177 · see citing works
Hunter Anderson, R., Adamson, D. T., & Stroo, H. F. (2019) · Journal of Contaminant Hydrology · doi:10.1016/j.jconhyd.2018.11.011 · Cited by 169 · see citing works
Self-citationChen, X., Zhu, L., Pan, X., Fang, S., Zhang, Y., & Yang, L. (2015) · Water Research · doi:10.1016/j.watres.2015.04.032 · Cited by 163 · see citing works
Wang, P., Lü, Y., Wang, T., Meng, J., Li, Q., Zhu, Z., Sun, Y., Wang, R., & Giesy, J. P. (2016) · Journal of Hazardous Materials · doi:10.1016/j.jhazmat.2015.12.059 · Cited by 162 · see citing works
Wei, C., Song, X., Wang, Q., & Hu, Z. (2017) · Ecotoxicology and Environmental Safety · doi:10.1016/j.ecoenv.2017.03.040 · Cited by 158 · see citing works
Barzen-Hanson, K. A., Davis, S. E., Kleber, M., & Field, J. A. (2017) · Environmental Science & Technology · doi:10.1021/acs.est.7b03452 · Cited by 158 · see citing works
Mejia-Avendaño, S., Munoz, G., Vo Duy, S., Desrosiers, M., Benoı̂t, P., Sauvé, S., & Liu, J. (2017) · Environmental Science & Technology · doi:10.1021/acs.est.7b02028 · Cited by 147 · see citing works
Baduel, C., Paxman, C. J., & Mueller, J. F. (2015) · Journal of Hazardous Materials · doi:10.1016/j.jhazmat.2015.03.007 · Cited by 141 · see citing works
Zhang, J. (1999) · Continental Shelf Research · doi:10.1016/s0278-4343(99)00029-1 · Cited by 139 · see citing works
Role of air‐water interfaces in colloid transport in porous media: A review
Flury, M., & Aramrak, S. (2017) · Water Resources Research · doi:10.1002/2017wr020597 · Cited by 134 · see citing works
Factors Affecting Zeta Potential of Iron Oxides
Carlson, J. J., & Kawatra, S. K. (2013) · Mineral Processing and Extractive Metallurgy Review · doi:10.1080/08827508.2011.604697 · Cited by 134 · see citing works
Perfluoroalkyl acids in urban stormwater runoff: Influence of land use
Xiao, F., Simcik, M. F., & Gulliver, J. S. (2012) · Water Research · doi:10.1016/j.watres.2011.11.029 · Cited by 131 · see citing works
The removal of arsenic from water using natural iron oxide minerals
Aredes, S., Klein, B., & Pawlik, M. (2013) · Journal of Cleaner Production · doi:10.1016/j.jclepro.2012.10.035 · Cited by 128 · see citing works
Coggan, T. L., Anumol, T., Pyke, J., Shimeta, J., & Clarke, B. O. (2019) · Analytical and Bioanalytical Chemistry · doi:10.1007/s00216-019-01829-8 · Cited by 124 · see citing works
Hatfield, R. G., & Maher, B. A. (2009) · Earth Surface Processes and Landforms · doi:10.1002/esp.1824 · Cited by 122 · see citing works
Chen, H., Reinhard, M., Yin, T., Nguyen, T. V., Tran, N. H., & Yew-Hoong Gin, K. (2019) · Water Research · doi:10.1016/j.watres.2019.02.009 · Cited by 122 · see citing works
Colloid-facilitated mobilization of metals by freeze–thaw cycles
Mohanty, S. K., Saiers, J. E., & Ryan, J. N. (2014) · Environmental Science & Technology · doi:10.1021/es403698u · Cited by 118 · see citing works
Self-citationSilva, J. A. K., Martin, W. A., Johnson, J. L., & McCray, J. E. (2019) · Journal of Contaminant Hydrology · doi:10.1016/j.jconhyd.2019.03.004 · Cited by 108 · see citing works
Wang, P., Wang, T., Giesy, J. P., & Lü, Y. (2013) · Chemosphere · doi:10.1016/j.chemosphere.2013.02.017 · Cited by 106 · see citing works
Robey, N. M., da Silva, B. F., Annable, M. D., Townsend, T. G., & Bowden, J. A. (2020) · Environmental Science & Technology · doi:10.1021/acs.est.0c01266 · Cited by 104 · see citing works
Meng, P., Deng, S., Lu, X., Du, Z., Wang, B., Huang, J., Wang, Y., Yu, G., & Xing, B. (2014) · Environmental Science & Technology · doi:10.1021/es504108u · Cited by 103 · see citing works
Modeling Colloid‐Facilitated Contaminant Transport in the Vadose Zone
Markus Flury, A., & Qiu, H. (2008) · Vadose Zone Journal · doi:10.2136/vzj2007.0066 · Cited by 103 · see citing works
Wang, F., Shih, K., & Leckie, J. O. (2015) · Chemosphere · doi:10.1016/j.chemosphere.2014.08.080 · Cited by 102 · see citing works
Effects of wave-induced seabed liquefaction on sediment re-suspension in the Yellow River Delta
Jia, Y., Zhang, L., Zheng, J., Liu, X., Jeng, D., & Shan, H. (2014) · Ocean Engineering · doi:10.1016/j.oceaneng.2014.08.004 · Cited by 102 · see citing works
Chanson, H., Reungoat, D., Simon, B., & Lubin, P. (2011) · Estuarine Coastal and Shelf Science · doi:10.1016/j.ecss.2011.09.012 · Cited by 101 · see citing works
Subsurface transport potential of perfluoroalkyl acids (PFAAs): Column experiments and modeling
Guelfo, J. L., Wunsch, A., McCray, J. E., Stults, J. F., & Higgins, C. P. (2020) · Journal of Contaminant Hydrology · doi:10.1016/j.jconhyd.2020.103661 · Cited by 98 · see citing works
Brusseau, M. L. (2019) · Environmental Pollution · doi:10.1016/j.envpol.2019.113102 · Cited by 93 · see citing works
Hamid, H., Li, L. Y., & Grace, J. R. (2020) · Environmental Pollution · doi:10.1016/j.envpol.2019.113835 · Cited by 92 · see citing works
Mohanty, S. K., Saiers, J. E., & Ryan, J. N. (2015) · Environmental Science & Technology · doi:10.1021/acs.est.5b00889 · Cited by 90 · see citing works
Self-citationAssociation of perfluoroalkyl substances exposure with impaired lung function in children
Qin, X.-D., Qian, Z. (., Dharmage, S. C., Perret, J., Geiger, S. D., Rigdon, S. E., Howard, S., Zeng, X.-W., Hu, L.-W., Yang, B.-Y., et al. (2017) · Environmental Research · doi:10.1016/j.envres.2017.01.025 · Cited by 90 · see citing works
Vertical transport and residence time of chlorinated hydrocarbons in the open ocean water column
Tanabe, S., & Tatsukawa, R. (1983) · Journal of Oceanography · doi:10.1007/bf02210759 · Cited by 89 · see citing works
Knutsen, H., Mæhlum, T., Haarstad, K., Slinde, G. A., & Arp, H. P. H. (2019) · Environmental Science Processes & Impacts · doi:10.1039/c9em00170k · Cited by 86 · see citing works
Pitter, G., Jeddi, M. Z., Barbieri, G., Gion, M., Fabricio, A. S. C., Daprà, F., Russo, F., Fletcher, T., & Canova, C. (2020) · Environmental Health · doi:10.1186/s12940-020-00656-0 · Cited by 83 · see citing works
Yi, S., Harding-Marjanovic, K. C., Houtz, E. F., Gao, Y., Lawrence, J. E., Nichiporuk, R. V., Iavarone, A. T., Zhuang, W., Hansen, M. A., Field, J. A., et al. (2018) · Environmental Science & Technology Letters · doi:10.1021/acs.estlett.8b00148 · Cited by 79 · see citing works
Rates and equilibria of perfluorooctanoate (PFOA) sorption on soils from different regions of China
Miao, Y., Guo, X., Peng, D., Fan, T., & Yang, C. (2017) · Ecotoxicology and Environmental Safety · doi:10.1016/j.ecoenv.2017.01.022 · Cited by 78 · see citing works
Zhang, L., Lee, L. S., Niu, J., & Liu, J. (2017) · Environmental Pollution · doi:10.1016/j.envpol.2017.05.074 · Cited by 69 · see citing works
Dauchy, X., Boiteux, V., Colin, A., Bach, C., Rosin, C., & Munoz, J.-F. (2019) · Archives of Environmental Contamination and Toxicology · doi:10.1007/s00244-018-0585-z · Cited by 69 · see citing works
Chen, H., Choi, Y. J., & Lee, L. S. (2018) · Environmental Science & Technology · doi:10.1021/acs.est.8b02913 · Cited by 66 · see citing works
Milley, S. A., Koch, I., Fortin, P., Archer, J., Reynolds, D., & Weber, K. (2018) · Journal of Environmental Management · doi:10.1016/j.jenvman.2018.05.028 · Cited by 62 · see citing works
Zhang, T., Sun, H., Gerecke, A. C., Kannan, K., Müller, C. E., & Alder, A. C. (2010) · Journal of Chromatography A · doi:10.1016/j.chroma.2010.05.061 · Cited by 60 · see citing works
PFOA and Cancer in a Highly Exposed Community: New Findings from the C8 Science Panel
Nicole, W. (2013) · Environmental Health Perspectives · doi:10.1289/ehp.121-a340 · Cited by 57 · see citing works
Nguyen, T. V., Reinhard, M., Chen, H., & Gin, K. Y.-H. (2016) · Environmental Science and Pollution Research · doi:10.1007/s11356-016-6788-9 · Cited by 54 · see citing works
Borthakur, A., Cranmer, B. K., Dooley, G. P., Blotevogel, J., Mahendra, S., & Mohanty, S. K. (2021) · Environmental Pollution · doi:10.1016/j.envpol.2021.117297 · Cited by 53 · see citing works
Self-citationLiu, Y., Qi, F., Fang, C., Naidu, R., Duan, L., Dharmarajan, R., & Annamalai, P. (2020) · Environmental Technology & Innovation · doi:10.1016/j.eti.2020.100965 · Cited by 50 · see citing works
Ambient levels of PFOS and PFOA in multiple environmental media
Vedagiri, U., Anderson, R. H., Loso, H. M., & Schwach, C. M. (2018) · Remediation Journal · doi:10.1002/rem.21548 · Cited by 47 · see citing works
Tondera, K., Koenen, S., & Pinnekamp, J. (2013) · Water Science & Technology · doi:10.2166/wst.2013.340 · Cited by 43 · see citing works
Dasu, K., Lee, L. S., Turco, R. F., & Nies, L. F. (2013) · Chemosphere · doi:10.1016/j.chemosphere.2012.11.076 · Cited by 42 · see citing works
Rokoff, L. B., Rifas-Shiman, S., Coull, B., Cardenas, A., Calafat, A., Ye, X.-Y., Gryparis, A., Schwartz, J., Sagiv, S., Gold, D., et al. (2018) · Environmental Health · doi:10.1186/s12940-018-0363-4 · Cited by 41 · see citing works
Influence of oxic/anoxic condition on sorption behavior of PFOS in sediment
Ololade, I. A., Zhou, Q., & Pan, G. (2015) · Chemosphere · doi:10.1016/j.chemosphere.2015.08.068 · Cited by 33 · see citing works
In-Situ Molecular-Level Elucidation of Organofluorine Binding Sites in a Whole Peat Soil
Longstaffe, J. G., Courtier‐Murias, D., Soong, R., Simpson, M. J., Maas, W. E., Fey, M., Hutchins, H., Krishnamurthy, S., Struppe, J. O., Alaee, M., et al. (2012) · Environmental Science & Technology · doi:10.1021/es3026769 · Cited by 29 · see citing works
Nadal, M., & Domingo, J. L. (2014) · Current Organic Chemistry · doi:10.2174/1385272819666140804230713 · Cited by 26 · see citing works
Qiu, Y., He, J., & Shi, H. (2010) · 中国环境科学与工程前沿:英文版 · doi:10.1007/s11783-010-0236-8 · Cited by 22 · see citing works
Yang, B., Li, R., Liu, P. N., Geng, X. H., Mooney, B., Chen, C., Cheng, J. J., Fritsche, K. L., Beversdorf, D. Q., Lee, J. C., et al. (2020) · Journal of Proteome Research · doi:10.1021/acs.jproteome.9b00792 · Cited by 17 · see citing works
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- Borthakur, 2021, Dataset for the review: Perfluoroalkyl acids on suspended particles: Significant transport pathways in surface runoff, surface waters, and subsurface soils., figshare. Collection.
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O’Connor, J., Bolan, N. S., Kumar, M., Nitai, A. S., Ahmed, M. B., Bolan, S. S., Vithanage, M., Rinklebe, J., Mukhopadhyay, R., Srivastava, P., et al. (2022) · Process Safety and Environmental Protection · doi:10.1016/j.psep.2022.06.002 · Cited by 183 · see citing works
Treatment technologies for removal of per- and polyfluoroalkyl substances (PFAS) in biosolids
Garg, A., Shetti, N. P., Basu, S., Nadagouda, M. N., & Aminabhavi, T. M. (2022) · Chemical Engineering Journal · doi:10.1016/j.cej.2022.139964 · Cited by 128 · see citing works
Pozzebon, E. A., & Seifert, L. (2023) · Environmental Health · doi:10.1186/s12940-023-01008-4 · Cited by 129 · see citing works
Niu, S., Cao, Y., Chen, R., Bedi, M., Sanders, A. P., DUCATMAN, A. M., & Ng, C. A. (2023) · Environmental Health Perspectives · doi:10.1289/ehp11885 · Cited by 116 · see citing works
Wang, Z., Alinezhad, A., Nason, S. L., Xiao, F., & Pignatello, J. J. (2022) · Water Research · doi:10.1016/j.watres.2022.119467 · Cited by 89 · see citing works
Zhang, K., Qadeer, A., Chang, S., Tu, X., Shang, H., Khan, M. A., Zhu, Y., Fu, Q., Yu, Y., & Feng, Y. (2025) · Environment International · doi:10.1016/j.envint.2025.109602 · Cited by 78 · see citing works
Microplastics retained in stormwater control measures: Where do they come from and where do they go?
Koutnik, V. S., Leonard, J., Glasman, J. B., Brar, J., Koydemir, H. C., Novoselov, A., Bertel, R., Tseng, D. K., Özcan, A., Ravi, S., et al. (2021) · Water Research · doi:10.1016/j.watres.2021.118008 · Cited by 74 · see citing works
Self-citationBorthakur, A., Leonard, J., Koutnik, V. S., Ravi, S., & Mohanty, S. K. (2021) · Current Opinion in Environmental Science & Health · doi:10.1016/j.coesh.2021.100309 · Cited by 68 · see citing works
Self-citationKalra, S. S., Cranmer, B. K., Dooley, G., Hanson, A. J., Maraviov, S., Mohanty, S. K., Blotevogel, J., & Mahendra, S. (2021) · Chemical Engineering Journal · doi:10.1016/j.cej.2021.131778 · Cited by 65 · see citing works
Self-citationGe, F., Zhou, B., Yuan, R., Luo, S., Gai, N., & Chen, H. (2024) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2024.171785 · Cited by 65 · see citing works
Zhou, J., Zhao, G., Li, M., Li, J., Liang, X., Yang, X., Guo, J., Wang, T., & Zhu, L. Y. (2021) · Environment International · doi:10.1016/j.envint.2021.107007 · Cited by 54 · see citing works
Ohoro, C. R., Amaku, J. F., Conradie, J., Olisah, C., Akpomie, K., Malloum, A., Akpotu, S. O., Adegoke, K. A., Okeke, E., & Omotola, E. (2024) · Marine Pollution Bulletin · doi:10.1016/j.marpolbul.2024.117040 · Cited by 52 · see citing works
Richardson, M. J., Kabiri, S., Grimison, C., Bowles, K., Corish, S., Chapman, M., & McLaughlin, M. J. (2022) · Environmental Science & Technology · doi:10.1021/acs.est.2c05377 · Cited by 52 · see citing works
Understanding PFAS Adsorption: How Molecular Structure Affects Sustainable Water Treatment
Hamza, M., Ayinla, R. T., Elsayed, I., & Hassan, E. B. (2025) · Environments · doi:10.3390/environments12090330 · Cited by 43 · see citing works
Li, J., Duan, W., Jiang, Z., Jiang, Z., Li, L., Guo, M., Tan, Z., Zeng, X., Liu, X., Liu, Y., et al. (2024) · Journal of Hazardous Materials · doi:10.1016/j.jhazmat.2024.135795 · Cited by 43 · see citing works
Peter, L. G., & Lee, L. S. (2025) · Environmental Science & Technology · doi:10.1021/acs.est.4c09490 · Cited by 40 · see citing works
Li, J., Peng, G., Xu, X., Liang, E., Sun, W., Chen, Q., & Yao, L. (2022) · Chemosphere · doi:10.1016/j.chemosphere.2022.134873 · Cited by 40 · see citing works
Cui, Q., Liu, J., Tang, Y., Ma, Y., Gong, L., Wang, R., Zhang, W., Zuo, Q., Zhao, X., & Wu, F. (2023) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2023.164242 · Cited by 37 · see citing works
Bayode, A. A., Emmanuel, S. S., Akinyemi, A. O., Ore, O. T., Akpotu, S. O., Koko, D. T., Momodu, D. E., & López‐Maldonado, E. A. (2024) · Environmental Research · doi:10.1016/j.envres.2024.119719 · Cited by 36 · see citing works
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Wu, J.-Y., Ding, F.-G., Shen, Z.-W., Hua, Z., & Gu, L. (2022) · Chemosphere · doi:10.1016/j.chemosphere.2022.135403 · Cited by 33 · see citing works
Interactions between MPs and PFASs in aquatic environments: A dual-character situation
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Shen, L., Zhou, J., Liang, X., Qin, L., Wang, T., & Zhu, L. Y. (2023) · Environmental Science & Technology · doi:10.1021/acs.est.2c07500 · Cited by 32 · see citing works
Ren, J., Yu, M., Chen, F., Cui, L. R., Zhang, Y., Li, J., Chen, M., Wang, X., & Fu, J. (2022) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2022.159026 · Cited by 30 · see citing works
Islam, M. A., Parvin, M. I., Nguyen, C., Alam, M. R., Kwong, P. C. W., Zhou, J. L., Hessel, V., & Ahmed, M. B. (2025) · Environmental Pollution · doi:10.1016/j.envpol.2025.127036 · Cited by 30 · see citing works
Bhagat, C., Kumar, M., Mahlknecht, J., Hdeib, R., & Mohapatra, P. K. (2022) · Environmental Pollution · doi:10.1016/j.envpol.2022.119771 · Cited by 29 · see citing works
Adeogun, A. O., Chukwuka, A. V., Ibor, O. R., Asimakopoulos, A. G., Zhang, J., & Arukwe, A. (2024) · Environmental Pollution · doi:10.1016/j.envpol.2024.123575 · Cited by 29 · see citing works
Niu, L., Gärtner, A., König, M., Krauss, M. K. V., Spahr, S., & Escher, B. I. (2025) · Environmental Science & Technology · doi:10.1021/acs.est.4c13378 · Cited by 25 · see citing works
Reif, D., Zoboli, O., Wolfram, G., Amann, A., Saračević, E., Riedler, P., Hainz, R., Hintermaier, S., Krampe, J., & Zessner, M. (2022) · Journal of Environmental Management · doi:10.1016/j.jenvman.2022.115871 · Cited by 26 · see citing works
Shang, M., Dong, J., Xie, H., Wang, Y., & Du, Y. (2023) · Water Research · doi:10.1016/j.watres.2023.120384 · Cited by 26 · see citing works
Chang, N. Y., Eichler, C. M. A., Amparo, D. E., Zhou, J., Baumann, K., Cohen Hubal, E. A., Surratt, J. D., Morrison, G. C., & Turpin, B. J. (2025) · Environmental Science: Processes & Impacts · doi:10.1039/d4em00359d · Cited by 24 · see citing works
Bhagat, C., Mohapatra, P. K., & Kumar, M. (2021) · Marine Pollution Bulletin · doi:10.1016/j.marpolbul.2021.112773 · Cited by 23 · see citing works
Beryani, A., Furén, R., Österlund, H., Tirpak, A., Smith, J., Dorsey, J., Winston, R. J., Viklander, M., & Blecken, G.-T. (2024) · Environmental Science & Technology · doi:10.1021/acs.est.4c05170 · Cited by 22 · see citing works
Byns, C., Groffen, T., & Bervoets, L. (2024) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2024.170611 · Cited by 21 · see citing works
Borthakur, A., Das, T. K., Zhang, Y., Libbert, S., Prehn, S., Ramos, P., Dooley, G., Blotevogel, J., Mahendra, S., & Mohanty, S. K. (2022) · Journal of Cleaner Production · doi:10.1016/j.jclepro.2022.134244 · Cited by 20 · see citing works
Self-citationLiu, N., & Li, M. (2024) · Environmental Science and Pollution Research · doi:10.1007/s11356-024-35725-1 · Cited by 19 · see citing works
Soltaninia, S., Taghavi, L., Hosseini, S. A., Motamedvaziri, B., & Eslamian, S. (2022) · Journal of Water Reuse and Desalination · doi:10.2166/wrd.2022.046 · Cited by 19 · see citing works
Lv, L., Liu, B., Zhang, B., Yu, Y., Gao, L., & Ding, L. (2023) · Environmental Research · doi:10.1016/j.envres.2023.116156 · Cited by 19 · see citing works
Walker, T., & Milligan, D. K. (2025) · Frontiers in Environmental Chemistry · doi:10.3389/fenvc.2025.1591290 · Cited by 18 · see citing works
Raschke, A., Nejadhashemi, A. P., Rafiei, V., Fernandez, N., Shabani, A., & Li, S. (2022) · Journal of Environmental Engineering · doi:10.1061/(asce)ee.1943-7870.0002034 · Cited by 17 · see citing works
Groffen, T., Keirsebelik, H., Dendievel, H., Falcou-Préfol, M., Bervoets, L., & Schoelynck, J. (2023) · Journal of Hazardous Materials · doi:10.1016/j.jhazmat.2023.133024 · Cited by 16 · see citing works
Liu, C., Ma, X.-X., Wang, S.-Q., Li, Q., Cheng, P., Hou, W., Li, Y.-Y., Li, W.-L., & Wang, X.-H. (2024) · Science of The Total Environment · doi:10.1016/j.scitotenv.2024.177646 · Cited by 16 · see citing works
Dong, J., Feng, R., Yao, Z., Wang, J., Wang, Y., Wang, H., Yan, D., Cui, Y., Xie, H., Du, Y., et al. (2024) · Journal of Hazardous Materials · doi:10.1016/j.jhazmat.2024.134675 · Cited by 15 · see citing works
Wen, W., Gao, L., Cheng, H., Xiao, L., Zhang, S., Li, S., Jiang, X., & Xia, X. (2024) · Water Research · doi:10.1016/j.watres.2024.122095 · Cited by 16 · see citing works
Hitzelberger, M., Khan, N., Mohamed, R., Brusseau, M., & Carroll, K. (2022) · Environmental Science and Technology · doi:10.1021/acs.est.2c02193 · Cited by 12 · see citing works
Chen, J., Liu, Y., Chao, L., Hou, L., Wang, Y., Chu, J., & Sun, J. (2024) · Environmental Research · doi:10.1016/j.envres.2024.119746 · Cited by 14 · see citing works
Hua, Z., Wang, Y., Zhang, J., Li, X., & Yu, L. H. (2022) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2022.155295 · Cited by 13 · see citing works
Liu, X., Yu, L., Zhang, Y., Hua, Z., Li, X., Xue, H., & Chu, K. (2024) · Water Research · doi:10.1016/j.watres.2024.121947 · Cited by 12 · see citing works
Turbulence‐Driven Clogging of Hyporheic Zones by Fine Particle Filtration
Cifuentes, E. S., Teitelbaum, Y., Arnon, S., Dallmann, J., Phillips, C. B., & Packman, A. I. (2023) · Geophysical Research Letters · doi:10.1029/2023gl105002 · Cited by 10 · see citing works
Raoelison, O. D., Das, T. K., Visweswaran, A., Guyett, K., Spallone, S., Ramos, R., Merrifield, R., Dittrich, T. M., & Mohanty, S. K. (2023) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2023.166635 · Cited by 10 · see citing works
Self-citationWang, S., Liu, T., Qian, X., Wang, H., Wang, X., Wei, S., & Chen, H. (2023) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2023.164775 · Cited by 9 · see citing works
Co-transport of PFCs in the environment- An interactive story
Khurana, P., Hasaneen, N., Pulicharla, R., Kaur, G., & Brar, S. K. (2022) · Current Research in Green and Sustainable Chemistry · doi:10.1016/j.crgsc.2022.100302 · Cited by 9 · see citing works
Occurrence of emerging and persistent organic pollutants in the rivers Cam, Ouse and Thames, UK
Folorunsho, O., Bogush, A., & Kourtchev, I. (2025) · Science of The Total Environment · doi:10.1016/j.scitotenv.2025.178436 · Cited by 8 · see citing works
Understanding the scale and potential contributions of background PFAS in the environment
Adamson, D. T., Gamlin, J. D., Jin, Y., Casteel, W., Schaefer, C. E., & Higgins, C. P. (2026) · Journal of Hazardous Materials · doi:10.1016/j.jhazmat.2026.141121 · Cited by 8 · see citing works
Self-citationDong, J., Gu, S., Shang, M., Cui, Y., Song, X. S., Wang, H., Xie, H., Feng, R., Yan, D., Du, Y., et al. (2024) · Journal of Cleaner Production · doi:10.1016/j.jclepro.2024.142837 · Cited by 7 · see citing works
Study on interaction, feedback, and response between perfluorinated compounds and soil environments
Song, J., Song, J., Zhang, R., Che, C., Yuan, Y., Tan, W., Xi, B., Hui, K., & Zhang, J. (2024) · Emerging contaminants · doi:10.1016/j.emcon.2024.100428 · Cited by 6 · see citing works
Overview of Modeling, Applications, and Knowledge Gaps for Integrated Large-Scale PFAS Modeling
Raschke, A., Nejadhashemi, A. P., & Rafiei, V. (2022) · Journal of Environmental Engineering · doi:10.1061/(asce)ee.1943-7870.0002033 · Cited by 6 · see citing works
The fundamental role of healthy soil in maintaining water quality
Kah, M., Wilson, S. C., & Carter, L. (2025) · Nature Water · doi:10.1038/s44221-025-00553-1 · Cited by 5 · see citing works
Han, X., Pan, B., Pan, Z., Xu, N., Wu, J., Sun, W., Hou, B., & Dong, Y. (2025) · Water Research · doi:10.1016/j.watres.2025.123461 · Cited by 5 · see citing works
Cui, F., Wang, H., Shen, Z., Li, Y., Li, S., & Tian, X. (2023) · Sustainability · doi:10.3390/su15086888 · Cited by 5 · see citing works
Raoelison, O. D., Das, T. K., Guyett, K., Merrifield, R., Visweswaran, A., Indiresan, S., Yang, K. L., Pierce, G., & Mohanty, S. K. (2023) · Journal of Hazardous Materials · doi:10.1016/j.jhazmat.2023.132989 · Cited by 5 · see citing works
Self-citationLü, Y., Chu, K., Hua, Z., Gao, C., & Liu, Y. (2025) · Water Research · doi:10.1016/j.watres.2025.123260 · Cited by 4 · see citing works
Bai, W., Xu, J., Hu, Z., Tang, R., & Zhan, X. (2025) · Water Research · doi:10.1016/j.watres.2025.124133 · Cited by 4 · see citing works
PFAS Dynamics in a Macrotidal Estuary: Insights from Fractionated Particle Components
Liu, C., Li, Q., Ma, X., Wang, S., Cheng, P., Li, Y., Chen, Y., & Wang, X. (2025) · Environmental Science & Technology · doi:10.1021/acs.est.5c07778 · Cited by 4 · see citing works
Byns, C., Newell, K., AbdElgawad, H., Beemster, G. T. S., Bervoets, L., & Groffen, T. (2025) · Environmental Pollution · doi:10.1016/j.envpol.2025.127067 · Cited by 3 · see citing works
Li, X., Zhao, Z.-X., Zi, J.-X., Huang, Y., Liu, S., & Chen, C.-E. (2025) · Exposure and Health · doi:10.1007/s12403-025-00711-6 · Cited by 2 · see citing works
Lee, C., Yu, J.-Y., & Chang, Y.-T. (2025) · ACS ES&T Water · doi:10.1021/acsestwater.5c00822 · Cited by 2 · see citing works
Recent trends in hyporheic zone research
Wang, H., Zhang, Z., Zheng, T., Chen, M., & Fang, Y. (2025) · Environmental Earth Sciences · doi:10.1007/s12665-025-12708-0 · Cited by 2 · see citing works
Dunn, M., Juriasingani, P., Arnseth, R., Shabani, A., & Salk, K. R. (2025) · ACS ES&T Water · doi:10.1021/acsestwater.5c00931 · Cited by 2 · see citing works
Colloid-facilitated release of PFAS from polluted-soil monoliths
Fries, E., Courtier‐Murias, D., Labadie, P., Bechet, B., Peyneau, P., Caurel, C., Dubois, Q., Pardon, P. R., Budzinski, H., & Michel, E. (2026) · Journal of Hazardous Materials · doi:10.1016/j.jhazmat.2026.142279 · Cited by 2 · see citing works
Hui, K., Song, J., Xi, B., Yuan, Y., & Tan, W. (2025) · Journal of Hazardous Materials · doi:10.1016/j.jhazmat.2025.140638 · Cited by 1 · see citing works
Liu, T., Zhang, Y., Chen, F., Han, M., Zhao, M., & Chen, X. (2026) · Journal of Hazardous Materials Advances · doi:10.1016/j.hazadv.2026.101207 · Cited by 1 · see citing works
Zhang, M., Xie, M., & Jin, Z. (2026) · Langmuir · doi:10.1021/acs.langmuir.5c05640 · Cited by 1 · see citing works
Saheed, M., Salma, M., Usman, R. A., Abubakar, H. L., Muhammad, L. A., Oladejo, T. J., Abdulkareem, A. S., Mohammed, N. M., Obayomi, K. S., Díaz‐Sainz, G., et al. (2026) · Colloids and Surfaces C Environmental Aspects · doi:10.1016/j.colsuc.2026.100098 · Cited by 1 · see citing works
Rodriguez, C. A., Schramm, M., Postma, S., McDonald, T. J., Brinkmeyer-Langford, C., & Ma, X. (2026) · ACS ES&T Water · doi:10.1021/acsestwater.6c00886
Fate and distribution of per and poly fluoroalkyl Substances (PFASs) in the urban environment
Nanjappa, V. (2024) · Queensland University of Technology · doi:10.5204/thesis.eprints.247479
Ranjan, A., Saxena, P., Rajput, V. D., Prazdnova, E. V., Rath, P., Arora, J., Pahariya, R., Chauhan, A. P. S., Jindal, T., Sushkova, S. N., et al. (2024) · Elsevier eBooks · doi:10.1016/b978-0-443-18985-2.00003-1 · Cited by 1 · see citing works
Price, D., Trites, A. W., Raverty, S., Cottrell, P. E., Cottrell, B., Zysk, I., & Alava, J. J. (2025) · Environmental Toxicology and Chemistry · doi:10.1093/etojnl/vgaf226
Duncan, C. M., Ghezelsofla, F., Nyoni, H. H., Escobar, J., & Mina, O. (2026) · Toxics · doi:10.3390/toxics14030245
Yan, D., Dong, J., Qiao, R.-X., Zhang, X., Chen, Q.-W., Feng, T., & Yan, X.-C. (2026) · Water Research · doi:10.1016/j.watres.2026.126049
Peter, L. G., Lee, L., Burbage, C., Richardson, A., Hoffman, K., & Holloway, D. (2026) · ACS ES&T Water · doi:10.1021/acsestwater.6c00339
Yang, H., Jiang, H., Xing, H., Chen, Z. F., Zhang, Q., & Yan, Z. (2026) · Journal of Environmental Sciences · doi:10.1016/j.jes.2026.105633 · Cited by 1 · see citing works
Wang, L., Liu, Y., Chen, Y., Tan, J., Bian, X., Liu, S., Guo, H., & Liu, W. (2026) · Water Research · doi:10.1016/j.watres.2026.126946
Ren, S., Yao, J., Wang, Y., Gao, M., Li, M., Gong, L., Cao, Y., Zhang, W., & Wu, F. (2026) · Journal of Hazardous Materials · doi:10.1016/j.jhazmat.2026.143713
Tan, C., Ji, Y., Chapman, M., Fincher, K., Huang, Q., & Xu, X. (2026) · ACS ES&T Water · doi:10.1021/acsestwater.6c00736
- Authors
- Borthakur, A., Wang, M., He, M., Ascencio, K., Blotevogel, J., Adamson, D. T., Mahendra, S., & Mohanty, S. K.
- Affiliations
- University of California, Los Angeles (US)
- University of Pittsburgh (US)
- Colorado State University (US)
- GSI Environmental (United States) (US)
- Corresponding author
- Mohanty, Sanjay K.
- Venue
- Journal of Hazardous Materials
- Publisher
- Elsevier BV
- Published
- 2021-09
- Volume
- 417
- Pages
- 126159
- ISSN
- 0304-3894 (ISSN-L)
- OpenAlex
- W3162149283
- Cited by
- 87
- References
- 103
- Citations by year
- 2026: 13 · 2025: 20 · 2024: 18 · 2023: 14 · 2022: 16 · 2021: 6
- FWCI
- 1.00
- Type
- journal article
- Language
- en
- Open access
- hybrid
- doi.org
- Licence
- Locations
- Journal of Hazardous Materials (publishedVersion, cc-by)
- PubMed (publishedVersion)
- Topics
- Physical Sciences › Environmental Science › Environmental Chemistry › Per- and polyfluoroalkyl substances research
- Physical Sciences › Environmental Science › Pollution › Pharmaceutical and Antibiotic Environmental Impacts
- Physical Sciences › Environmental Science › Pollution › Pesticide and Herbicide Environmental Studies
- Keywords
- perfluoroalkyl acids, suspended particulate matter, surface runoff, surface water contamination, soil organic carbon, iron and aluminum oxides, particle erosion, source zone, groundwater contamination, precursor transformation, rainfall effects
- MeSH terms
- Carbon, Environmental Monitoring, Fluorocarbons, Soil, Water Pollutants, Chemical, Groundwater
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