Per‐ and polyfluoroalkyl substances in aquatic sediments: Global distribution, partitioning behavior, and ecological consequences
Open accessAbstract
Per‐ and polyfluoroalkyl substances (PFAS) are persistent organic pollutants that accumulate across aquatic compartments, which include sediments, pore water, surface water (including microlayers), suspended particulate matter (SPM), fish, and other biota, causing long‐term ecological impacts. This review analyzes the global distribution of PFAS in aquatic sediments, partitioning behavior across aquatic compartments, and ecological consequences of PFAS on sediment‐dwelling organisms. PFAS in sediments are widespread globally, with the highest mean concentration (274.1 ng/g) found in the African continent, in addition to localized hotspots showing increased average levels in other continents. SPM consistently retains higher PFAS levels than sediments, while porewater concentrations exceed those of surface water (SPM > sediment, porewater > surface water), revealing overlooked exposure pathways. Sediment‐bound PFAS exposes benthic organisms through dermal contact, ingestion, and trophic transfer, with bioaccumulation influenced by organism traits, sediment properties, and environmental factors. Although ecological risk quotient (RQ) values are generally low (RQ < 0.1), localized hotspots and species‐specific sensitivities highlight the need for site‐specific monitoring. Regulatory frameworks in the EU and United States remain focused on drinking and surface waters, lacking sediment‐specific standards and leaving a critical policy gap. Thus, this review suggests sediments as an important yet underexplored reservoir of PFAS, indicating the importance of incorporating sediment compartments into monitoring, ecological risk assessment, and regulatory frameworks.
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- Findingcitation
PFAS concentrations in porewater exceed those in surface water.
“porewater concentrations exceed those of surface water”
- Also stated in: § 3.2 Distribution of PFAS between porewater and surface water · boosted
“Across aquatic systems, PFAS concentrations in porewater consistently exceed those in surface water”
Quote in the paperSubstantial claim - Also stated in: § 3.2 Distribution of PFAS between porewater and surface water · boosted
- Findingcitation
PFAS contamination in aquatic sediments is globally widespread.
“PFAS in sediments are widespread globally, with the highest mean concentration (274.1 ng/g) found in the African continent, in addition to localized hotspots showing increased average levels in other continents.”
- Also stated in: § INTRODUCTION · plain
“PFAS are frequently identified in sediments across diverse aquatic systems, from the Great Lakes to the Red Sea, usually at ng/g levels”
Quote in the paperSubstantial claim - Also stated in: § INTRODUCTION · plain
- Findingnone given
Ecological risk quotient values for PFAS in sediments are generally low, below 0.1.
“Although ecological risk quotient (RQ) values are generally low (RQ < 0.1)”
Quote in the paperSubstantial claim - Findingown data
The number of PFAS targeted and detected in sediment studies varies from 1 to 93 compounds.
“Among these studies, the total number of PFAS targeted and detected varied considerably, ranging from 1 to 93 compounds.”
Quote in the paperNot a substantial claim - Findingnone given
The Roodeplaat and Hartbeespoort Dams in South Africa show the highest average PFAS concentration of 274.1 ng/g.
“with the Roodeplaat and Hartbeespoort Dams in South Africa showing the highest average of 274.1 ng/g.”
Quote in the paperNot a substantial claim
- Findingnone given
Suspended particulate matter retains higher PFAS levels than sediments.
“SPM consistently retains higher PFAS levels than sediments”
Quote in the paperSubstantial claim - Findingown data
The African continent has the highest concentration range of PFAS in sediments among all continents.
“The African continent reveals the highest concentration range of PFAS in sediments among all continents”
Quote in the paperNot a substantial claim - Findingnone given
Information on PFAS in sediments from South America and Australia remains very limited.
“However, information on the South American and Australian continents remains very limited.”
Quote in the paperNot a substantial claim - Findingown data
Among continents, Africa has the highest mean PFAS concentration in sediments, at 274.1 ng/g.
“PFAS in sediments are widespread globally, with the highest mean concentration (274.1 ng/g) found in the African continent, in addition to localized hotspots showing increased average levels in other continents.”
- Also stated in: § 2.2 Global distribution · plain
“The African continent reveals the highest concentration range of PFAS in sediments among all continents, with the Roodeplaat and Hartbeespoort Dams in South Africa showing the highest average of 274.1 ng/g.”
Quote in the paperNot a substantial claim - Also stated in: § 2.2 Global distribution · plain
- Findingnone given
Localized hotspots with elevated average PFAS levels occur in continents other than Africa.
“in addition to localized hotspots showing increased average levels in other continents.”
Quote in the paperNot a substantial claim - Findingcitation
Across aquatic systems, PFAS concentrations in porewater consistently exceed those in surface water.
“Across aquatic systems, PFAS concentrations in porewater consistently exceed those in surface water”
Quote in the paperNot a substantial claim - Findingcitation
Elevated PFAS concentrations in porewater indicate that sediment-porewater partition coefficients (log Kd) are lower than in sediment-surface water systems.
“Elevated PFAS concentrations in porewater indicate that sediment-porewater partition coefficients (log K d ) are lower than in sediment-surface water systems”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Feng et al., 2020
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- Findingcitation
In Changshu, Jiangsu, average PFAS concentrations were 24,000 ng/L in porewater compared to 18,000 ng/L in surface water.
“In the Industrialized region Changshu, Jiangsu, average PFAS concentrations were significantly higher, with porewater reaching 24,000 ng/L compared to 18,000 ng/L in surface water”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites X.Liu et al., 2021
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- Findingcitation
On the coast of Jiangsu Province, mean PFAS was 890 ng/L in high-DOM porewaters compared to 55 ng/L in surface waters.
“on the coast of Jiangsu Province, Feng et al. (2020) reported a mean PFAS of 890 ng/L in high-DOM porewaters, compared to a mean PFAS of 55 ng/L in surface waters.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Feng et al., 2020
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- Findingcitation
Sediment spiking under laboratory conditions confirmed that porewater PFAS concentrations exceed surface water concentrations.
“Sediment spiking under laboratory conditions confirmed this pattern.”
Quote in the paperNot a substantial claim - Findingown data
The extent of localized PFAS contamination varies significantly across global sites.
“In addition to the mean concentration across continents, the extent of localized PFAS contamination varied significantly across global sites.”
Quote in the paperNot a substantial claim - Findingnone given
The relationship between total organic carbon and PFAS sorption remains inconclusive.
“However, the relationship between TOC and PFAS sorption remains inconclusive.”
Quote in the paperNot a substantial claim - Findingreasoning
Long-chain, sulfonated, and emerging PFAS show greater sediment affinity.
“Long-chain, sulfonated, and emerging PFAS show greater sediment affinity”
Quote in the paperNot a substantial claim - Findingnone given
Across 17 studies in the United States, mean PFAS concentration in sediments ranged between 0.067 and 29.45 ng/g.
“Across 17 studies in the United States, mean concentration ranged between 0.067 and 29.45 ng/g”
Quote in the paperNot a substantial claim - Findingreasoning
The extent and level of PFAS concentrations in sediments worldwide, including China, confirms widespread contamination.
“The extent and level of concentration of PFAS in sediments found worldwide including China confirms the widespread contamination.”
Quote in the paperSubstantial claim - Findingreasoning
Aside from Nevada and the Great Lakes region, PFAS concentrations in most US sediments remain below 10 ng/g.
“Aside from Nevada and the Great Lakes region, PFAS concentrations in most US sediments remain below 10 ng/g”
Quote in the paperNot a substantial claim - Findingcitation
In Austria's Wulka River, total porewater PFAS concentrations (30.6 ng/L) were triple those of corresponding surface water.
“Even in less contaminated regions such as Austria's Wulka River, total porewater PFAS concentrations (30.6 ng/L) were triple that of corresponding surface water concentrations”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Reif et al., 2022
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- Findingcitation
In Asia, several rivers in South Korea reported the highest concentration range, from not detected to 337 ng/g.
“in Asia, several rivers in South Korea (Han, Geum, Yeongsan, Seomjin, and Nakdong) reported the highest concentration range (not detected: 337 ng/g)”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Choi et al., 2025
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- Findingcitation
In Europe, Lake Tyrifjorden in Norway recorded the highest sediment PFAS level at 606 ng/g.
“in Europe, Lake Tyrifjorden in Norway recorded the highest sediment levels at 606 ng/g”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Langberg et al., 2020
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- Findingnone given
For treating PFAS in sediments, activated carbon is the sole in situ sorbent that is fully commercialized.
“AC is the only fully commercialized in situ sorbent but carries ecological trade-offs.”
Quote in the paperNot a substantial claim - Findingnone given
Ecological risks from PFAS in sediments are generally low on average in China.
“Ecological risks, though generally low on average in China mainly, reveal significant site-specific vulnerabilities.”
Quote in the paperSubstantial claim - Findingreasoning
The length of the carbon chain and the type of functional group are major determinants of how PFAS partition in sediments.
“This review shows that chain length and functional groups strongly shape partitioning: long-chain and sulfonated PFAS preferentially bind to sediments, while short-chain analogues persist in dissolved phases.”
Quote in the paperSubstantial claim - Findingreasoning
There are significant site-specific vulnerabilities in ecological risks from PFAS in sediments.
“Ecological risks, though generally low on average in China mainly, reveal significant site-specific vulnerabilities.”
Quote in the paperSubstantial claim - Findingreasoning
Sediment remediation for PFAS remains largely experimental.
“Sediment remediation remains largely experimental.”
Quote in the paperSubstantial claim - Findingreasoning
PFAS with long chains or sulfonate groups tend to associate with sediment particles.
“This review shows that chain length and functional groups strongly shape partitioning: long-chain and sulfonated PFAS preferentially bind to sediments, while short-chain analogues persist in dissolved phases.”
Quote in the paperSubstantial claim - Findingown data
Data on PFAS levels in sediments are scarce or absent for South America, Australia, and some regions of Asia and Europe.
“Nevertheless, very limited or no information on PFAS sediment distribution was found in the continents of South America and Australia, as well as in certain parts of Asia and Europe.”
Quote in the paperSubstantial claim- Rests on an assumption: The peer-reviewed literature synthesized is representative of global PFAS sediment distribution.
- Findingnone given
The African continent is more contaminated with PFAS in sediments than other continents.
“A synthesis of peer-reviewed literature revealed that PFAS contamination in sediments is widespread across the globe, with the African continent found to be more contaminated.”
Quote in the paperSubstantial claim- Rests on an assumption: The peer-reviewed literature synthesized is representative of global PFAS sediment distribution.
- Findingown data
Sediment contamination by PFAS is globally widespread.
“A synthesis of peer-reviewed literature revealed that PFAS contamination in sediments is widespread across the globe, with the African continent found to be more contaminated.”
Quote in the paperSubstantial claim- Rests on an assumption: The peer-reviewed literature synthesized is representative of global PFAS sediment distribution.
- Findingreasoning
Short-chain PFAS analogues remain in dissolved phases.
“This review shows that chain length and functional groups strongly shape partitioning: long-chain and sulfonated PFAS preferentially bind to sediments, while short-chain analogues persist in dissolved phases.”
Quote in the paperSubstantial claim - Premisecitation
Polluted sediments act as additional PFAS sources, releasing into overlying water.
“Furthermore, polluted sediments act as additional PFAS sources, releasing into overlying water and generating concerns about ecosystem health and human exposure through water reuse and ingestion”
Quote in the paperSubstantial claim0 of 2 sources checked- cites Da Silva et al., 2022
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- cites Sunderland et al., 2019
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- Premisecitation
Once mobilized, PFAS reaches aquatic and marine systems and accumulates in sediments by deposition, particle sorption, and settling.
“Once mobilized, PFAS reaches aquatic and marine systems and accumulates in sediments by deposition, particle sorption, and settling”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Lin et al., 2020
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- Premisecitation
PFAS tend to bind to suspended particles and accumulate in sediments because of their amphiphilic and resistant character.
“Due to their amphiphilic and resistant character, PFAS tend to bind to suspended particles and accumulate in sediments”
Quote in the paperSubstantial claim0 of 2 sources checked- cites Munoz, Budzinski, & Labadie, 2017
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- cites Sherman-Bertinetti et al., 2024
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- Interpretationnone given
Sediment-bound PFAS exposes benthic organisms through dermal contact, ingestion, and trophic transfer.
“Sediment-bound PFAS exposes benthic organisms through dermal contact, ingestion, and trophic transfer”
Quote in the paperNot a substantial claim - Premisereasoning
Comprehensive insight into sediment-specific PFAS dynamics and global distribution remains scarce.
“comprehensive insight into sediment-specific PFAS dynamics and global distribution remains scarce to the best of my knowledge”
Quote in the paperSubstantial claim0 of 2 sources checked- cites Ahmed et al., 2020
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- cites Tulcan et al., 2025
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- Rests on an assumption: A comprehensive synthesis of sediment-specific PFAS dynamics and global distribution is lacking.
- Premisecitation
Groundwater-surface water exchange is a route for PFAS transfer into aquatic ecosystems.
“Moreover, groundwater-surface water exchange works as another route for PFAS transfer into aquatic ecosystems”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Rey et al., 2025
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- Interpretationnone given
Bioaccumulation of PFAS in benthic organisms is influenced by organism traits, sediment properties, and environmental factors.
“with bioaccumulation influenced by organism traits, sediment properties, and environmental factors.”
Quote in the paperSubstantial claim - Premisecitation
Sediment parameters including grain size, mineral composition, organic carbon content, ionic strength, and pH control PFAS sorption-desorption and bioavailability.
“These dynamics, which are influenced by sediment parameters that include grain size, mineral composition, organic carbon content, ionic strength, and pH of the solution, control the sorption-desorption and bioavailability of PFAS”
Quote in the paperSubstantial claim0 of 3 sources checked- cites Fagbayigbo et al., 2022
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- cites Higgins & Luthy, 2006
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- cites Umeh et al., 2023
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- Premisecitation
Bonso et al. found 10 total PFAS in the Scheldt Estuary, Netherlands-Belgium, varying between 48.6 and 110.3 ng/g.
“Bonso et al. (2026) found significant levels of 10 total PFAS in the Scheldt Estuary, the Netherlands-Belgium, varying between 48.6 and 110.3 ng/g.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Bonso et al., 2026
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- Premisecitation
Seasonal shifts in hydrology and salinity can alter log Kd by up to two log units.
“Seasonal shifts in hydrology and salinity can alter log K d by up to two log units”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites S.Wang et al., 2020
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- Premisecitation
Sediment porosity and permeability critically govern PFAS migration within heterogeneous riparian sediments during surface water-groundwater interactions.
“According to Li et al. (2024), sediment porosity and permeability critically govern PFAS migration within heterogeneous riparian sediments during surface water-groundwater interactions.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Li et al., 2024
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- Interpretationreasoning
Hydrological fluctuations and concentration gradients can remobilize PFOS and PFOA from sediments, increasing the risk of secondary contamination in surrounding water.
“However, hydrological fluctuations and concentration gradients can remobilize PFOS and PFOA from these sediments, increasing the risk of secondary contamination in the surrounding water.”
Quote in the paperSubstantial claim - Premisecitation
Sediment affinity of PFAS depends mainly on molecular structure, chain length, functional group, and substitutions such as halogenation or ether linkages.
“Sediment affinity of PFAS depends mainly on molecular structure, chain length, functional group (sulfonate vs. carboxylate), and substitutions such as halogenation or ether linkages”
Quote in the paperSubstantial claim0 of 3 sources checked- cites An et al., 2023
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- cites Bian et al., 2025
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- cites H. Chen et al., 2024
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- Premisecitation
Partitioning between water, sediments, and suspended particulate matter determines PFAS transport, bioavailability, and persistence.
“Partitioning between water, sediments, and SPM determines PFAS transport, bioavailability, and persistence”
Quote in the paperSubstantial claim0 of 1 sources checked- cites H.Chen et al., 2022
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- Premisecitation
Environmental conditions including sediment composition, pH, ionic strength, microbial activity, hydraulic disturbances, salinity, and total organic carbon may influence in situ log Kd.
“environmental conditions including sediment composition, pH, ionic strength, microbial activity, hydraulic disturbances, salinity, and total organic carbon (TOC) may influence in situ log (K d )'s”
Quote in the paperNot a substantial claim0 of 3 sources checked- cites Dong et al., 2020
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- cites Higgins & Luthy, 2006
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- cites Y. Li et al., 2020
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- Premisecitation
Sediments in the five Great Lakes in the United States are estimated to contain approximately 245 ± 24 tonnes of PFAS.
“Sediments in the five Great Lakes in the United States alone are estimated to contain ∼245 ± 24 tonnes of PFAS”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Christensen et al., 2019
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- Premisecitation
The Bohai, Yellow, East China, and South China Seas receive approximately 87.3 tonnes of PFAS annually via riverine inputs.
“In this coastal area, the Bohai, Yellow, East China, and South China Seas receive ∼87.3 tonnes of PFAS annually via riverine inputs”
Quote in the paperNot a substantial claim0 of 2 sources checked- cites Chen, Han, et al., 2017
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- cites Chen, Wang, et al., 2017
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- Interpretationown data
The comparable mean PFAS concentration ranges indicate a comparable level of contamination between Asia and Europe.
“indicating a comparable level of contamination between the two regions”
Quote in the paperNot a substantial claim - Premisecitation
Munoz et al. found a total PFAS concentration range of 0.057-160 ng/g at St. Lawrence River, Quebec, Canada.
“Munoz et al. (2025) found a total concentration range of 0.057-160 ng/g at St. Lawrence River, Quebec, Canada.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Munoz et al., 2025
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- Interpretationreasoning
PFAS contamination in US sediments is due to historical exposure to aqueous film-forming foams and industrial and wastewater discharges.
“The contamination is due to historical exposure to AFFF, and industrial and wastewater discharges.”
Quote in the paperNot a substantial claim - Interpretationnone given
Sediment-water partitioning of PFAS is predominantly governed by molecular structure, especially carbon chain length and functional group chemistry, as well as local environmental conditions.
“In summary, sediment-water partitioning of PFAS is predominantly governed by molecular structure, especially carbon chain length and functional group chemistry, as well as local environmental conditions.”
Quote in the paperSubstantial claim - Interpretationcitation
Preferential sorption of PFAS to SPM is attributed to fine particle size and high surface area-to-volume ratio, which enhance pollutant binding.
“This preferential sorption to SPM is attributed to its fine particle size and high surface area-to-volume ratio, which enhance pollutant binding (W.Li et al., 2022;Y. Liu et al., 2019).”
Quote in the paperNot a substantial claim0 of 2 sources checked- cites W.Li et al., 2022
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- cites Y. Liu et al., 2019
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- Premisecitation
Sediment-to-dissolved phase log Koc values for PFOS, PFOA, PFNA, and PFDA were more than one order of magnitude lower than SPM-to-dissolved phase log Koc values.
“Ahrens et al. (2010) reported that the sediment to dissolved phase log K oc values for PFOS, PFOA, PFNA, and perfluorodecanoic acid (PFDA) were more than one order of magnitude lower than the SPM to dissolved phase log K OC values.”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Ahrens et al. (2010)
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- Premisecitation
Chain length, functional group type, and acid moiety structure critically shape PFAS interfacial behavior.
“Chain length, functional group type (ester oxygen, chlorine, and hydrogen substitutions), and acid moiety structure critically shape interfacial behavior”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Bai & Son, 2021
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- Interpretationreasoning
Structural characteristics influence interfacial behavior by changing hydrophobicity, sorption affinity, and electrostatic interactions, which collectively determine PFAS partitioning among sediments, porewater, and surface water.
“These structural characteristics influence interfacial behavior by changing hydrophobicity, sorption affinity, and electrostatic interactions, which collectively determine PFAS partitioning among sediments, porewater, and surface water.”
Quote in the paperSubstantial claim - Premisecitation
In surface waters, short-chain PFAS such as PFBA and PFBS comprise the majority of dissolved PFAS.
“In surface waters, short chain PFAS (e.g., PFBA, perfluorobutane sulfonic acid [PFBS]) comprise the majority of dissolved PFAS in surface waters (Ding et al., 2018;W. Li et al., 2023).”
Quote in the paperNot a substantial claim0 of 2 sources checked- cites Ding et al., 2018
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- cites W. Li et al., 2023
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- Premisecitation
Sorption may be stronger at mildly acidic to neutral pH (4-7.5), where protonated sediment surfaces enhance electrostatic attraction with PFAS anions.
“Sorption may be stronger at mildly acidic to neutral pH (4-7.5),where protonated sediment surfaces enhance electrostatic attraction with PFAS anions (Fagbayigbo et al., 2022).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Fagbayigbo et al., 2022
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- Premisecitation
PFAS often display sorption hysteresis, with adsorption and desorption following different pathways, producing partial irreversibility and extended retention, as documented for PFOS, PFOA, and PFHxS.
“PFAS often display sorption hysteresis, where adsorption and desorption follow different pathways, producing partial irreversibility and extended retention, as documented for PFOS, PFOA, and perfluorohexane sulfonic acid (PFHxS) (Navarro et al., 2022).”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Navarro et al., 2022
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- Premisecitation
Sediment typically contains lower PFAS concentrations (0.05-25 ng/g dw) than SPM.
“Sediment, while serving as a long-term sink, typically contains lower PFAS (0.05-25 ng/g dw) than SPM (Table 3) (Ahrens et al., 2010;Ding et al., 2018;L. Li, Han, et al., 2024);”
Quote in the paperNot a substantial claim0 of 3 sources checked- cites Ahrens et al., 2010
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- cites Ding et al., 2018
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- cites L. Li, Han, et al., 2024
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- Interpretationreasoning
PFAS partitioning among water, SPM, and sediment reflects complex interactions of chemical properties, environmental variables, and phase-specific affinities.
“PFAS partitioning behavior among water, SPM, and sediment demonstrates a complex interaction of chemical properties, environmental variables, and phase-specific affinities (Figure 2).”
Quote in the paperSubstantial claim - Interpretationreasoning
Sediments act as dynamic reservoirs capable of both storing and gradually releasing PFAS under fluctuating environmental conditions.
“These findings suggest that sediments act as dynamic reservoirs capable of both storing and gradually releasing PFAS under fluctuating environmental conditions.”
Quote in the paperSubstantial claim - Premisereasoning
SPM consistently shows higher total PFAS concentrations (0.98 to 527 ng/g) than both surface water and sediment.
“SPM consistently shows increased total PFAS concentrations (ranging from 0.98 to 527 ng/g) compared to both surface water and sediment (Table 3).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Table 3
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- Premisecitation
Long-chain PFAS with CF2 ≥ 8 mobility is influenced by organic matter and air-water interfacial area.
“while long-chain PFAS (CF 2 ≥ 8) mobility is influenced by organic matter and air-water interfacial area.”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Evich et al. (2025)
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- Interpretationcitation
SPM is a dynamic interface that facilitates PFAS transport between dissolved and sediment-bound phases under varying flow and sedimentation conditions.
“Furthermore, SPM represents a dynamic interface that facilitates PFAS transport between dissolved and sediment-bound phases under varying flow and sedimentation conditions (Ahrens et al., 2010;Higgins & Luthy, 2006;L. Li, Han, et al., 2024).”
Quote in the paperNot a substantial claim0 of 3 sources checked- cites Ahrens et al., 2010
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- cites Higgins & Luthy, 2006
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- cites L. Li, Han, et al., 2024
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- Interpretationcitation
Sediment remains a critical reservoir for hydrophobic and persistent PFAS, including legacy compounds and precursors such as perfluorooctane sulfonamidoacetic acid and perfluoroethylcyclohexane sulfonic acid.
“Therefore, it remains a critical reservoir for more hydrophobic and persistent PFAS, including legacy compounds and their precursors such as perfluorooctane sulfonamidoacetic acid and perfluoroethylcyclohexane sulfonic acid (H.Chen et al., 2024;Y. Liu et al., 2019).”
Quote in the paperSubstantial claim0 of 2 sources checked- cites H.Chen et al., 2024
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- cites Y. Liu et al., 2019
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- Premisecitation
Higher confluence ratios intensified flow turbulence and Reynolds stress, facilitating PFAS transfer from sediments into overlying water and the particulate phase.
“They observed that higher confluence ratios intensified flow turbulence and Reynolds stress, facilitating the transfer of PFAS from sediments into the overlying water and particulate phase.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites X. Liu et al. (2021)
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- Premisecitation
Average total PFAS was significantly elevated in condensed foam (46,470 ng/L) relative to the SML (80 ng/L) and underlying bulk water (35 ng/L), demonstrating substantial enrichment at the air-water interface.
“The average concentration of total PFAS was significantly elevated in condensed foam (46,470 ng/L) relative to the SML (80 ng/L) and the underlying bulk water (35 ng/L), demonstrating substantial enrichment of PFAS at the air-water interface (Sherman-Bertinetti et al., 2024).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Sherman-Bertinetti et al., 2024
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- Interpretationreasoning
Because bed sediment has much greater volume and mass, it likely retains a much greater share of the total PFAS burden in aquatic systems than SPM.
“however, due to its significantly greater volume and mass, bed sediment is likely to retain a much greater share of the total PFAS burden within aquatic systems.”
Quote in the paperSubstantial claim - Interpretationreasoning
Traditional sediment-porewater partitioning models based only on organic carbon (Kd, Koc) might understate PFAS retention in mineral-dominated sediments.
“The findings suggest that traditional sediment-porewater partitioning models based only on organic carbon (e.g., K d , K oc ) might understate PFAS retention in mineral-dominated sediments.”
Quote in the paperSubstantial claim - Interpretationcitation
PFAS partitioning among sediment, porewater, and surface water is controlled by molecular structure and environmental conditions.
“The partition of PFAS between sediment, porewater, and surface water is dictated by molecular structure and environmental conditions.”
Quote in the paperSubstantial claim - Premisecitation
Short-chain PFAS with C ≤ 7 typically remain dissolved in porewater because of high mobility and low sorption.
“short-chain PFAS (C ≤ 7) typically remain dissolved in porewater due to high mobility and low sorption”
Quote in the paperSubstantial claim0 of 3 sources checked- cites Ahrens et al., 2010
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- cites Y. Liu et al., 2019
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- cites N. Shen et al., 2024
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- Premisecitation
Short-chain PFAS with CF2 ≤ 7 are influenced by aluminum-oxide mineral electrostatic sorption.
“They found that short-chain PFAS (CF 2 ≤ 7) are influenced by aluminum-oxide mineral electrostatic sorption”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Evich et al. (2025)
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- Premisecitation
Replacement PFAS compounds such as 6:2 and 8:2 Cl-PFESAs and HFPO-TA display high SPM affinity (log Kd 2.94-3.30).
“Replacement PFAS compounds, such as 6:2 and 8:2 Cl-PFESAs, as well as HFPO-TA, display high SPM affinity (log K d 2.94-3.30)(Y.Li, Zhao, et al., 2024;Y. Liu et al., 2019).”
Quote in the paperNot a substantial claim0 of 2 sources checked- cites Y.Li, Zhao, et al., 2024
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- cites Y. Liu et al., 2019
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- Premisecitation
Using a conservative Kd of 10, a sediment quality guideline of 60 μg/kg for 1% organic carbon was proposed.
“Using a conservative K d of 10, a sediment quality guideline of 60 μg/kg (for 1% organic carbon) was proposed.”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Simpson et al., 2021
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- Premisecitation
In a 28-day microcosm study, Lumbriculus variegatus accumulated significantly more PFAS than Physella acuta and Elliptio complanata due to its deposit-feeding behavior.
“In a 28-day microcosm study, Lumbriculus variegatus (sediment-ingesting worm) accumulated significantly more PFAS than Physella acuta (snail) and Elliptio complanata (bivalve), due to its deposit-feeding behavior (Lewis et al., 2023;Yun et al., 2023).”
Quote in the paperNot a substantial claim0 of 2 sources checked- cites Lewis et al., 2023
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- cites Yun et al., 2023
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- Premisecitation
An et al. (2023) found PFOS and PFOA posed high risks (RQ > 1) to several aquatic species, including Danio rerio, Chironomus riparius, and Ctenopharyngodon idella.
“For example, An et al. (2023) applied toxicity-based RQ analysis and found PFOS and PFOA posed high risks (RQ > 1) to several aquatic species, including Danio rerio, Chironomus riparius, and Ctenopharyngodon idella.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites An et al. (2023)
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- Premisecitation
Increasing sediment organic carbon from 2% to 8% reduced PFAS uptake, likely due to decreased bioavailability.
“while increasing sediment organic carbon (from 2% to 8%) reduced PFAS uptake, likely due to decreased bioavailability.”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Yun et al., 2023
Not checked in the free run.
- Premisecitation
Moderate risks (0.1 < RQ < 1) were reported for Daphnia carinata, Chironomus tentans, Anguilla anguilla, and Perna viridis.
“Moderate risks (0.1 < RQ < 1) were reported for Daphnia carinata, Chironomus tentans, Anguilla anguilla, and Perna viridis, illustrating speciesspecific sensitivity even where average RQs remain within regulatory limits.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites An et al. (2023)
Not checked in the free run.
- Premisecitation
Elevated divalent cation concentrations (Mg2+, Ca2+ at 7.5 mM) enhanced BAF of long-chain PFAS (≥C8).
“PFAS bioaccumulation was influenced by sediment composition: elevated divalent cation concentrations (Mg 2+ , Ca 2+ at 7.5 mM) enhanced BAF of long-chain PFAS (≥C8), while increasing sediment organic carbon (from 2% to 8%) reduced PFAS uptake, likely due to decreased bioavailability.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Lewis et al., 2023
Not checked in the free run.
- Premisecitation
PFOS and PFDA adsorption was enhanced in the presence of Cu(II) and Cd(II), likely due to formation of ternary surface complexes.
“For instance, PFOS and PFDA adsorption was enhanced in the presence of Cu(II) and Cd(II), likely due to the formation of ternary surface complexes.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Chaudhary et al. (2024)
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- Premisecitation
Sediment cores from the Pearl River Estuary and North South China Sea revealed long-term ecological concerns, particularly for PFOS and 6:2 Cl-PFESA.
“Sediment cores from the Pearl River Estuary and North South China Sea revealed long-term ecological concerns, particularly for PFOS and 6:2 Cl-PFESA.”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Q.Wang, Ruan, et al., 2025
Not checked in the free run.
- Premisecitation
Sediment in Lake Tyrifjorden showed extensive contamination with SAmPAP (max 1872 ng/g), a known PFOS precursor.
“Sediment showed extensive contamination, particularly with SAmPAP (sulfonamido-alcoholbased polyfluoroalkyl phosphate diester) (max 1872 ng/g), a known PFOS precursor.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Langberg et al., 2020
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- Interpretationreasoning
Trophic magnification factors (3.7-9.3) reinforced sediment as a key vector for PFAS transfer to higher trophic levels.
“Trophic magnification factors (3.7-9.3)further reinforced sediment as a key vector for PFAS transfer to higher trophic levels.”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Langberg et al., 2020
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- Premisecitation
Structural changes such as longer perfluorocarbon chains or chlorine substitutions (e.g., Cl-PFESA) increase sorption via hydrophobicity and reduced solubility.
“Structural changes such as longer perfluorocarbon chains or chlorine substitutions (e.g., Cl-PFESA) further increase sorption via hydrophobicity and reduced solubility (Yin et al., 2022).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Yin et al., 2022
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- Premisecitation
PFOA and GenX showed marginal reductions in adsorption under similar conditions.
“In contrast, PFOA and GenX showed marginal reductions in adsorption under similar conditions.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Chaudhary et al. (2024)
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- Premisecitation
Across China, analysis of effluents from 296 municipal WWTPs reported RQ < 0.1 for 14 PFAS, indicating low risk from treated discharges.
“Across China, Mu et al. (2022) analyzed effluents from 296 municipal WWTPs, reporting RQ < 0.1 for 14 PFAS, including short-and long-chain PFCAs, PFSAs, and replacements (perfluorooctane sulfonamide [PFOSA], 6:2 FTS, and 6:2 Cl-PFESA), indicating low risk from treated discharges.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Mu et al. (2022)
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- Premisecitation
Hua et al. (2021) used EPM to derive sediment PNECs using water-phase benchmarks of 610 ng/L for PFOS and 100 ng/L for PFOA.
“Hua et al. (2021) used EPM to derive sediment PNECs, using water-phase benchmarks of 610 ng/L for PFOS and 100 ng/L for PFOA.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Hua et al. (2021)
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- Premisecitation
Divalent metal cations can alter PFAS adsorption in goethite (α-FeOOH), with the extent depending on the specific PFAS compound, pH, and metal ion.
“Chaudhary et al. (2024) demonstrated that divalent metal cations can alter PFAS adsorption in goethite (α-FeOOH), a common iron oxide found in soils and sediments.The extent of this influence depends on the specific PFAS compound, pH, and the type of metal ion present.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Chaudhary et al. (2024)
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- Interpretationnone given
Sediment near industrial or ecologically sensitive areas may present greater risks.
“However, sediment near industrial or ecologically sensitive areas may present greater risks.”
Quote in the paperNot a substantial claim - Premisecitation
PFHxA exposure altered microbial community composition and nutrient cycling, especially archaeal nitrogen and bacterial phosphorus pathways.
“PFAS also disrupt sediment microbes: PFHxA exposure altered community composition and nutrient cycling, especially archaeal nitrogen and bacterial phosphorus pathways (J.Wu, Gu, et al., 2021).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites J.Wu, Gu, et al., 2021
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- Premisecitation
Higher TOC increases PFAS retention, particularly for PFOS and PFOA.
“Higher TOC increases retention, particularly for PFOS and PFOA (Ahrens et al., 2010;Higgins & Luthy, 2006;Navarro et al., 2022).”
Quote in the paperSubstantial claim0 of 3 sources checked- cites Ahrens et al., 2010
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- cites Higgins & Luthy, 2006
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- cites Navarro et al., 2022
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- Premisereasoning
PFAS sorption is improved by increasing ionic strength, which reduces electrostatic repulsion.
“PFAS sorption is improved by increasing ionic strength, which reduces electrostatic repulsion.”
Quote in the paperNot a substantial claim - Interpretationreasoning
Context-dependent dynamics of PFAS in sediments complicate risk assessments.
“These context-dependent dynamics complicate risk assessments and demand site-specific evaluations.”
Quote in the paperSubstantial claim - Premisecitation
Activated carbon is the only fully commercialized sorbent for in situ sediment remediation.
“Currently, activated carbon (AC) is the only fully commercialized sorbent for in situ sediment remediation.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Abrams et al., 2022
Not checked in the free run.
- Interpretationreasoning
The absence of sediment thresholds limits the effectiveness of current regulatory frameworks given PFAS persistence and gradual release from sediments into surrounding waters and organisms.
“Given PFAS persistence and gradual release from sediments into surrounding waters and organisms, the absence of sediment thresholds limits the effectiveness of current regulatory frameworks.”
Quote in the paperSubstantial claim - Premisereasoning
PFAS regulations in the EU and United States focus largely on drinking water, surface water, and biota, while sediments remain largely overlooked.
“PFAS regulations in the EU and United States focus largely on drinking water, surface water, and biota, while sediments, despite acting as long-term PFAS reservoirs, remain largely overlooked.”
Quote in the paperSubstantial claim - Premisecitation
The US regulation introduced a cumulative hazard index to assess combined risks of PFHxS, PFNA, GenX, and PFBS.
“Notably, the regulation also introduced a cumulative hazard index to assess combined risks of PFHxS, PFNA, GenX, and PFBS, reflecting a more holistic approach to PFAS risk management (USEPA, 2024).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites USEPA, 2024
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- Interpretationnone given
Bioturbation, microbial transformation, and local geochemistry affect how sediment-dwelling organisms are exposed to PFAS.
“Sediment-dwelling organisms face heightened exposure through bioavailability, bioaccumulation, and trophic transfer, influenced by bioturbation, microbial transformations, and local geochemical factors.”
Quote in the paperSubstantial claim - Interpretationreasoning
This regulatory gap undermines comprehensive risk mitigation given PFAS persistence and bioaccumulation in benthic ecosystems.
“This gap undermines comprehensive risk mitigation given PFAS persistence and bioaccumulation in benthic ecosystems.”
Quote in the paperSubstantial claim - Interpretationreasoning
The movement and fate of PFAS in water bodies depend on their molecular structure, environmental conditions, and regional pollution histories.
“PFAS showed complex environmental behaviors, with their fate and transport in aquatic systems governed by molecular structure, environmental parameters, and regional pollution histories.”
Quote in the paperSubstantial claim - Premisenone given
No national sediment-specific PFAS standard exists in the United States.
“However, no national sediment-specific PFAS standard exists in the United States.”
Quote in the paperNot a substantial claim - Interpretationreasoning
Sediments act as long-term reservoirs for PFAS.
“Sediments function as long-term PFAS reservoirs, whereas SPM acts as a more dynamic carrier, concentrating pollutants and medi-ating redistribution, underscoring the need to integrate SPM into monitoring and remediation frameworks.”
Quote in the paperSubstantial claim - Interpretationreasoning
The presence of ether bonds and replacement of atoms by Cl or H strongly affects how sediments adsorb PFAS.
“This indicates that the presence of ether linkages and the substitution of Cl or H atoms substantially influence the adsorption of PFAS by sediments.”
Quote in the paperSubstantial claim - Interpretationcitation
Given sediments' function as both PFAS sink and secondary source, the lack of sediment regulation represents a critical regulatory shortcoming that hinders long-term protection of aquatic ecosystems and human health.
“Given the function of sediments as both PFAS sink and secondary source, this represents a critical regulatory shortcoming that hinders the long-term protection of aquatic ecosystems and human health (EEA, 2024;Reinikainen et al., 2024).”
Quote in the paperSubstantial claim0 of 2 sources checked- cites EEA, 2024
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- cites Reinikainen et al., 2024
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- Premisecitation
PFOA and PFOS were designated hazardous substances under CERCLA, enabling federal intervention for cleanup, liability enforcement, and reporting.
“Additionally, PFOA and PFOS were also designated hazardous substances under the Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA), enabling federal intervention for cleanup, liability enforcement, and reporting (EPA, 2024).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites EPA, 2024
Not checked in the free run.
- Premisecitation
PFOS has a higher log Kd (0.73 L/kg) than PFOA (-0.02 L/kg).
“For instance, perfluorooctanesulfonic acid (PFOS) (perfluoroalkyl sulfonic acid [PFSA]) displayed a higher log K d (0.73 L/kg) than PFOA (perfluoroalkyl carboxylic acid [PFCA], -0.02 L/kg) (N.Shen et al., 2024).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites N.Shen et al., 2024
Not checked in the free run.
- Premisecitation
No Canadian Federal Environmental Quality Guideline exists for PFAS in sediments.
“No Canadian Federal Environmental Quality Guideline exists for PFAS in sediments (Munoz et al., 2025),”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Munoz et al., 2025
Not checked in the free run.
- Interpretationreasoning
Suspended particulate matter (SPM) acts as a dynamic carrier that concentrates PFAS and mediates their redistribution.
“Sediments function as long-term PFAS reservoirs, whereas SPM acts as a more dynamic carrier, concentrating pollutants and medi-ating redistribution, underscoring the need to integrate SPM into monitoring and remediation frameworks.”
- Also stated in: § R E F E R E N C E S · plain
“SPM acts as a dynamic carrier, concentrating PFAS and mediating redistribution between phases.”
Quote in the paperSubstantial claim - Also stated in: § R E F E R E N C E S · plain
- Premisecitation
Most emerging PFAS, apart from 6:2 FTCA and OBS, have higher log KOC than legacy PFAS with the same number of fluorinated carbons.
“Tang et al. (2022) found that the log K OC values for the majority of emerging PFAS, except for 6:2 FTCA and OBS (sodium p-perfluorous nonenoxybenzene sulfonate), were typically greater than those of legacy PFAS containing an equivalent number of fluorinated carbons.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Tang et al., 2022
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- May combine two claims. 102
- Classified as probably not a substantial claim. 12
- The quote only partly states this claim. 1
May combine two claims.
FindingcitationAmong 12 African studies, the Volta River in Ghana, Nairobi River in Kenya, and Apies River in South Africa reported the highest mean concentrations of 101, 40.48, and 31.35 ng/g, respectively.
“Among 12 studies found on this continent, the Volta River in Ghana, the Nairobi River in Kenya, and the Apies River in South Africa reported the highest mean concentrations of 101, 40.48, and 31.35ng/g, respectively”
Quote in the paperNot a substantial claim0 of 3 sources checked- cites Chirikona et al., 2022
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- cites Okwuosa, Nomngongo, Petrik, et al., 2025
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- cites L. Zhao et al., 2025
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Probably not a substantial claim: may not pass S4 (based). May combine two claims.
Findingnone givenRegulatory frameworks in the EU and United States focus on drinking and surface waters and lack sediment-specific standards.
“Regulatory frameworks in the EU and United States remain focused on drinking and surface waters, lacking sediment-specific standards and leaving a critical policy gap.”
Quote in the paperNot a substantial claimMay combine two claims.
FindingreasoningLocalized hotspots and species-specific sensitivities exist for PFAS ecological risk.
“localized hotspots and species-specific sensitivities highlight the need for site-specific monitoring.”
Quote in the paperSubstantial claimMay combine two claims.
FindingcitationIn the Bohai and Yellow Seas, porewater PFAS ranged from 150.23 to 1838.48 ng/L (mean 636.8 ng/L), far above surface saltwater.
“In the Bohai and Yellow Seas, porewater ranged from 150.23-1838.48ng/L (mean 636.8 ng/L), far above surface saltwater”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites N.Shen et al., 2024
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FindingcitationNevada's Las Vegas Wash shows the highest PFAS concentration in US sediments, likely due to urban runoff and treated wastewater.
“with Nevada's Las Vegas Wash showing the highest concentration, likely due to urban runoff and treated wastewater”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Bai & Son, 2021
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FindingcitationZ. Wu, Li, et al. introduced PFOS into uncontaminated sediments (600 ng/g dw) and equilibrated them with overlying aerated water for two weeks, detecting porewater PFAS at 32,600 ng/L compared to surface water at 21,400 ng/L.
“Z. Wu, Li, et al. (2021) introduced PFOS into uncontaminated sediments (600 ng/g dw) and equilibrated them with overlying aerated water (1:3 sediment-to-water ratio) for two weeks, detecting elevated PFAS concentrations in porewater (32,600 ng/L) compared to surface water (21,400 ng/L).”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Z.Wu, Li, et al., 2021
Not checked in the free run.
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Findingnone givenExcept for the Chinese coastal area, other regions of Asia remain underexplored and indicate lower levels of PFAS contamination in certain areas.
“Except for the Chinese coastal area, other regions of Asia remain underexplored as well as indicate lower levels of PFAS contamination in certain areas.”
Quote in the paperNot a substantial claimMay combine two claims.
FindingcitationShi et al. introduced a mixture of PFAS (100 μg/kg dw) into homogenized river sediments and observed porewater concentrations (1,397,080 ng/L) exceeding surface water (566,290 ng/L).
“Shi et al. (2024) introduced a mixture of PFAS (100 μg/kg dw) into homogenized river sediments and observed porewater concentrations (1,397,080 ng/L) that exceeded those in surface water (566,290 ng/L).”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Shi et al., 2024
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Findingnone givenIn Asia and Europe, mean PFAS concentrations in sediments ranged from 0.14 to 75 ng/g and 0.083 to 75.9 ng/g, respectively.
“In Asia and Europe, the mean PFAS concentration ranged from 0.14 to 75 and 0.083 to 75.9 ng/g, respectively”
Quote in the paperNot a substantial claimMay combine two claims.
Findingnone givenTotal sediment PFAS concentrations in four rivers in the Pearl River Delta, Qiantang River-Hangzhou Bay, and Kaohsiung Harbor ranged from 0.025 to 150, 31 to 215, and 0.155 to 125 ng/g, respectively.
“Total sediment PFAS concentrations in four rivers in the Pearl River Delta, Qiantang River-Hangzhou Bay in China, and Kaohsiung Harbor, Taiwan, ranged from 0.025 to 150, 31 to 215, and 0.155 to 125 ng/g, respectively.”
Quote in the paperNot a substantial claimMay combine two claims.
Findingnone givenHigher mean PFAS concentrations in Norway, the Netherlands, Spain, and France indicate extensive contamination in the EU, while other parts of Europe such as Russia remain underexplored.
“A higher mean concentration was found in Norway, the Netherlands, Spain, and France in the EU, indicating extensive contamination, while other parts of Europe such as Russia remain underexplored.”
Quote in the paperNot a substantial claimMay combine two claims.
FindingcitationShort-chain PFAS (C ≤ 7) predominate in porewater, while long-chain PFAS (C ≥ 8) sorb more strongly to sediments.
“shortchain PFAS (C ≤ 7)-including PFCAs, PFSAs, hexafluoropropylene oxide dimer acid (HFPO-DA) (C6), and Hsubstituted FTCAs-predominate in porewater, while longchain PFAS (C ≥ 8) such as PFOS, perfluorononanoic acid (PFNA), hexafluoropropylene oxide trimer acid (HFPO-TA) (C9), and 6:2 Cl-PFESA sorb more strongly to sediments”
Quote in the paperSubstantial claim0 of 2 sources checked- cites Feng et al., 2020
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- cites Lyu et al., 2022
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Findingnone givenIon-exchange resins, thermal treatment, and advanced oxidation are promising for PFAS sediment cleanup, but they still need validation and cheaper operation.
“Other technologies such as ion-exchange resins, thermal treatments, and advanced oxidation showed promise but required further validation and cost optimization.”
Quote in the paperSubstantial claimMay combine two claims.
Findingnone givenThe EU and the United States have made regulatory advances for PFAS in drinking water and biota.
“Policy progress has been achieved in drinking water and biota standards in the EU and United States; however, both jurisdictions lack sediment-specific EQS, leaving a critical regulatory gap that weakens long-term PFAS management.”
Quote in the paperSubstantial claimMay combine two claims.
Findingnone givenThe EU and United States lack sediment-specific environmental quality standards (EQS) for PFAS.
“Policy progress has been achieved in drinking water and biota standards in the EU and United States; however, both jurisdictions lack sediment-specific EQS, leaving a critical regulatory gap that weakens long-term PFAS management.”
Quote in the paperSubstantial claimClassified as probably not a substantial claim.
Findingnone givenActivated carbon use in sediment remediation carries ecological trade-offs.
“AC is the only fully commercialized in situ sorbent but carries ecological trade-offs.”
Quote in the paperSubstantial claimMay combine two claims.
PremisecitationGriffin et al. targeted the highest number of PFAS (93) in Florida, and Munoz et al. detected the highest number (45) in Québec, Canada.
“Griffin et al. (2023) targeted the highest number of PFAS (93) in Florida, while Munoz et al. (2025) detected the highest 45 compounds in Québec, Canada.”
Quote in the paperNot a substantial claim0 of 2 sources checked- cites Griffin et al., 2023
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- cites Munoz et al., 2025
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PremisecitationPFAS uptake by macroinvertebrates can occur through sediment ingestion, consumption of contaminated prey or organic matter, and dissolved uptake through respiratory routes, resulting in bioaccumulation and trophic transfer.
“PFAS uptake can occur through sediment ingestion during feeding, consumption of contaminated prey or organic matter, and dissolved uptake through respiratory routes (Lewis et al., 2023;Maruya et al., 2012;Prosser et al., 2016;Simpson et al., 2021), resulting in bioaccumulation and trophic transfer”
Quote in the paperSubstantial claim0 of 3 sources checked- cites Lewis et al., 2023
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- cites Maruya et al., 2012
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- cites Prosser et al., 2016
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InterpretationreasoningSediments are an important yet underexplored reservoir of PFAS.
“this review suggests sediments as an important yet underexplored reservoir of PFAS”
Quote in the paperNot a substantial claimProbably not a substantial claim: may not pass S3 (load-bearing).
PremisecitationBuck et al. identified 256 PFAS as commercially important worldwide.
“Buck et al. (2021) identified 256 PFAS as commercially important worldwide.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Buck et al., 2021
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PremisecitationCombined sewer overflows can have total PFAS concentrations up to 320 ng/L, with a substantial fraction from precursor compounds and limited removal after chlorination.
“These sewer overflows can have total PFAS concentrations of up to 320 ng/L, with a substantial fraction originating from precursor compounds and limited removal efficiency after chlorination treatment”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Butzlaff et al., 2025
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PremisecitationOnce deposited, PFAS can disrupt microbial activity, affect the carbon cycle, and provide long-term exposure to benthic and pelagic creatures via resuspension or pore water.
“Once deposited, they can have an impact on aquatic ecosystems by disrupting microbial activity (Bezabhe et al., 2025;Qiao et al., 2018), affecting carbon cycle (Mah-moudnia, 2023), and providing long-term exposure to benthic and pelagic creatures via resuspension or pore water”
Quote in the paperSubstantial claim0 of 3 sources checked- cites Bezabhe et al., 2025
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- cites Qiao et al., 2018
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- cites Mah-moudnia, 2023
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Probably not a substantial claim: may not pass S3 (load-bearing).
PremisecitationCumulative emissions of perfluoroalkyl acids reach at least 46,000 tonnes.
“This production contributes to cumulative emissions of perfluoroalkyl acids reaching at least 46,000 tonnes (Evich et al., 2022).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Evich et al., 2022
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May combine two claims.
InterpretationreasoningThe patterns of higher PFAS in suspended particulate matter than sediment and in porewater than surface water reveal overlooked exposure pathways.
“revealing overlooked exposure pathways”
Quote in the paperSubstantial claimMay combine two claims.
PremisecitationPFAS enter aquatic systems through point sources such as industrial discharges, aqueous film-forming foams, and wastewater treatment plant effluents, and through nonpoint sources such as land-applied biosolids, landfill and incinerator runoff, leaching from consumer products, atmospheric deposition, and precipitation.
“PFAS enter aquatic systems through point sources, such as industrial discharges, aqueous film-forming foams (AFFF), and wastewater treatment plant (WWTP) effluents, as well as nonpoint sources such as land-applied biosolids, landfill and incinerator runoff, leaching from consumer products, atmospheric deposition, and precipitation”
Quote in the paperNot a substantial claim0 of 3 sources checked- cites Hunter Anderson et al., 2019
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- cites P. Li, McGarr, et al., 2024
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- cites Pfotenhauer et al., 2022
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PremisecitationA significant portion of PFAS pollutants enters aquatic systems through atmospheric deposition, wastewater effluents, industrial discharge, and surface runoff, and subsequently accumulates in sediments.
“A significant portion of these pollutants enter aquatic systems through atmospheric deposition, wastewater effluents come from industrial and household sources, industrial discharge, surface runoff, and subsequently accumulate in sediments”
Quote in the paperNot a substantial claim0 of 3 sources checked- cites Galloway et al., 2020
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- cites X. Hu et al., 2016
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- cites Pétré et al., 2022
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PremisecitationPFAS exposure in benthic organisms is associated with reproductive and developmental toxicity, immunological suppression, increased disease susceptibility, and mortality.
“The reported impacts have been observed across a wide range of benthic organisms, including worms, amphipods, insect larvae, snails, bivalves and bottom-feeding fish and include reproductive and developmental toxicity, immunological suppression, increased disease susceptibility, and mortality”
Quote in the paperSubstantial claim0 of 3 sources checked- cites Jacobson et al., 2010
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- cites Langberg et al., 2020
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- cites Yun et al., 2023
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PremisecitationIn some systems, no significant correlation between total organic carbon and PFAS sorption was observed, possibly due to low organic carbon content (e.g., fOC ∼0.47%), which may limit sorptive capacity.
“In some systems, no significant correlation was observed, possibly due to low organic carbon content (e.g., f OC ∼ 0.47%), which may limit sorptive capacity”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites S.Wang et al., 2020
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PremisecitationOver 300 US military sites have been identified as PFAS hotspots due to decades of aqueous film-forming foam use, which also affects nearby groundwater and surface waters.
“Notably, over 300 US military sites have been identified as PFAS hotspots due to decades of AFFF use, which also affects nearby groundwater and surface waters”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Ruyle et al., 2023
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The quote only partly states this claim.
PremisecitationIn estuarine and marine settings, salinity strengthens PFAS sorption via salting-out and cation bridging, especially through Ca2+ and Mg2+.
“In estuarine and marine settings, salinity strengthens sorption via”
Quote in the paperNot a substantial claim0 of 3 sources checked- cites Y.Chen et al., 2023
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- cites Meng et al., 2021
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- cites You et al., 2010
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PremisecitationHighly aromatic, humiclike, and low molecular weight DOM fractions predominate in water and likely facilitate PFAS migration into the aqueous phase via electrostatic and hydrogen-bond interactions.
“They discovered that highly aromatic, humiclike, and low molecular weight DOM fractions predominated in water, likely facilitating the migration of PFAS into the aqueous phase via electrostatic and hydrogen-bond interactions.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Xie et al., 2026
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PremisecitationSediment porewater, enriched in dissolved organic matter, functions as both a reservoir for pollutants and a primary exposure route for benthic organisms.
“Sediment porewater, enriched in dissolved organic matter (DOM), functions as both a reservoir for pollutants and a primary exposure route for benthic organisms”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Mao et al., 2018
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PremisecitationIndustrial and wastewater discharge, mining activities, agricultural runoff, and electronic waste processing are potential contributors to PFAS in African sediments.
“Industrial and wastewater discharge, mining activities, agricultural runoff, and electronic waste processing were identified as potential contributors”
Quote in the paperNot a substantial claim0 of 2 sources checked- cites Chirikona et al., 2022
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- cites L. Zhao et al., 2025
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PremisecitationCoastal China is a global PFAS hotspot due to rapid industrialization and insufficient emission controls.
“Coastal China is a global PFAS hotspot due to rapid industrialization and insufficient emission controls”
Quote in the paperNot a substantial claim0 of 2 sources checked- cites Meng et al., 2021
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- cites Zhong et al., 2021
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InterpretationcitationSediment acts as both a sink within the water column and a secondary source, gradually releasing PFAS into porewater.
“These findings support the concept that sediment acts as both a sink within the water column and a secondary source, gradually releasing PFAS into porewater.”
Quote in the paperSubstantial claimMay combine two claims.
PremisecitationOrganic matter origin might influence PFAS sorption, with allochthonous and autochthonous inputs boosting binding capacity and limiting desorption.
“Organic matter origin might influence sorption, with both allochthonous (plant detritus, soil erosion) and autochthonous (algae, microbial production) inputs boosting binding capacity and limiting desorption”
Quote in the paperNot a substantial claim0 of 3 sources checked- cites Canuel & Hardison, 2016
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- cites Navarro et al., 2022
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- cites Oliver et al., 2020
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PremisecitationDaily tidal fluctuations in estuaries can cause four- to sevenfold variations in ∑PFAS concentrations, which decrease with rising tide height.
“Daily tidal fluctuations in estuaries can also cause four-to sevenfold variations in ∑PFAS concentrations, which decrease with rising tide height”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Singh et al., 2025
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PremisecitationCoarse, highly permeable sediments facilitate PFAS transport, whereas fine-grained, low-permeability sediments promote PFAS retention.
“Coarse, highly permeable sediments (e.g., sand) facilitate transport, whereas fine-grained, low-permeability sediments (e.g., silt and clay), which have a larger surface area to volume ratio, promote PFAS retention.”
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PremisecitationRelocation of fluorochemical industries has intensified sediment accumulation in China, elevating PFAS levels linked to urban and industrial discharges.
“Relocation of fluorochemical industries has intensified sediment accumulation in China, elevating PFAS levels linked to urban and industrial discharges”
Quote in the paperNot a substantial claim0 of 2 sources checked- cites Q.Wang et al., 2019
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- cites Zhong et al., 2021
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InterpretationreasoningElevated porewater PFAS across field and lab studies underscores its role as a key benthic exposure pathway and vector for contaminant flux back into surface waters.
“Overall, elevated porewater PFAS across field and lab studies underscores its role as a key benthic exposure pathway and vector for contaminant flux back into surface waters.”
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InterpretationreasoningSPM acts as a critical intermediary by concentrating long-chain and emerging PFAS, redistributing them between water and sediment, and sustaining exposure across the system.
“Together, these findings highlight SPM as a critical intermediary: concentrating long-chain and emerging PFAS, redistributing them between water and sediment, and sustaining exposure across the system.”
Quote in the paperSubstantial claimMay combine two claims.
InterpretationreasoningSorption and desorption influence PFAS mobility, persistence, and ecological risk in sediments, shaped by PFAS physicochemical properties, sediment composition, and environmental conditions.
“Sorption and desorption influence PFAS mobility, persistence, and ecological risk in sediments, shaped by PFAS physicochemical properties, sediment composition, and environmental conditions.”
Quote in the paperSubstantial claimMay combine two claims.
PremisecitationHFPO-DA and 6:2 Cl-PFESA exhibited higher log Kd values (1.30 and 1.44 L/kg) than PFOA (-0.02 L/kg) and PFOS (0.73 L/kg), indicating that functional group identity affects partitioning.
“For example, HFPO-DA (1.30 L/kg) and 6:2 Cl-PFESA (1.44 L/kg) exhibited higher log K d than PFOA (-0.02 L/kg) and PFOS (0.73 L/kg), underscoring the role of functional group identity (Feng et al., 2020).”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Feng et al., 2020
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PremisecitationIn the Yangtze River Estuary, average total PFAS in sea surface water was 11 ± 4 ng/L, largely from short-chain PFCAs and PFSAs.
“For example, in the Yangtze River Estuary, the average concentration of total PFAS in sea surface water was 11 ± 4 ng/L, largely from short-chain PFCAs and PFSAs (L.Li, Han, et al., 2024).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites L.Li, Han, et al., 2024
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InterpretationcitationThese interactions drive reversible and irreversible sorption, directly influencing PFAS fate.
“These interactions drive reversible and irreversible sorption, directly influencing PFAS fate (Lyu et al., 2022).”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Lyu et al., 2022
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PremisecitationUnder those conditions, suspended particle-water partitioning increased from 2.14 to 2.26, likely due to resuspension and adsorption onto particulate matter.
“Interestingly, suspended particle-water partitioning increased under these conditions (from 2.14 to 2.26), likely due to resuspension and adsorption onto particulate matter.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites X. Liu et al. (2021)
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PremisecitationIonizable functional groups contribute hydrophilicity and determine PFAS charge characteristics, enabling interactions with organic and mineral phases.
“The ionizable functional groups contribute hydrophilicity and determine the charge characteristics of PFAS, enabling interactions with both organic and mineral phases (Lyu et al., 2022).”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Lyu et al., 2022
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PremisecitationLog Koc values in SPM to water reach as high as 5.4 for PFUnDA, indicating strong hydrophobic interactions especially for long-chain PFAS.
“Also, log K oc values in SPM to water reach as high as 5.4 for PFUnDA, indicative of strong hydrophobic interactions, especially for long-chain PFAS (Munoz et al., 2019).”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Munoz et al., 2019
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PremisecitationShort-chain PFAS have lower log Kow values and increased hydrophilicity, showing enhanced solubility and mobility in porewater, while longer chains show stronger hydrophobic interactions and a larger affinity for sediment organic matter and mineral surfaces.
“Short-chain PFAS, characterized by lower log K ow values and increased hydrophilicity, show enhanced solubility and mobility in porewater, while longer chains show stronger hydrophobic interactions and a larger affinity for sediment organic matter and mineral surfaces”
Quote in the paperSubstantial claim0 of 2 sources checked- cites Bai & Son, 2021
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- cites K. Zhang, Qadeer, et al., 2025
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PremisecitationTurbulence and water confluence enhanced PFAS mobilization from sediments into overlying water, lowering sediment-porewater log Kd from 0.97 to 0.86.
“X. Liu et al. (2021) found turbulence and water confluence enhanced PFAS mobilization from sediments into overlying water, lowering sedimentporewater log K d (from 0.97 to 0.86).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites X. Liu et al. (2021)
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PremisecitationReported sediment-porewater partition fractions for PFPeA, perfluoroheptanoic acid, PFHxA, and PFOA were 33.68%, 50.99%, 64.61%, and 49.1%, respectively.
“N. Shen et al. (2024) reported φ sedi-pw values of 33.68% for PFPeA, 50.99% for perfluoroheptanoic acid, 64.61% for perfluorohexanoic acid (PFHxA) and 49.1% for PFOA”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites N. Shen et al. (2024)
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PremisecitationSediments with high PFAA loads can act as secondary sources as aqueous concentrations decline, while burial under cleaner sediment layers reduces desorption potential.
“Sediments with high PFAA loads can act as secondary sources as aqueous concentrations decline, while burial under cleaner sediment layers reduces desorption potential (Bai & Son, 2021).”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Bai & Son, 2021
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InterpretationcitationSediment exhibits lower Kd values (typically 0.72-2.95) than SPM, reflecting differences in particle size, surface reactivity, and organic matter characteristics.
“Compared to SPM, sediment exhibits lower K d values (typically 0.72-2.95),reflecting differences in particle size, surface reactivity, and organic matter characteristics (W.Li et al., 2022;Y. Liu et al., 2019).”
Quote in the paperSubstantial claim0 of 2 sources checked- cites W.Li et al., 2022
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- cites Y. Liu et al., 2019
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PremisecitationReported SPM concentrations range from 1.7 to 127.72 ng/g dw and are often enriched in long-chain PFAS such as PFOS, PFNA, PFUnDA, and 6:2 FTS.
“Reported concentrations range from 1.7 to 127.72 ng/g dw (Ding et al., 2018;L. Li, Han, et al., 2024) and are often enriched in long-chain PFAS such as PFOS, PFNA, perfluoroundecanoic acid (PFUnDA), and 6:2 fluorotelomer sulfonic acid (FTS) (H.Chen et al., 2024;Ding et al., 2018;Göckener et al., 2022).”
Quote in the paperNot a substantial claim0 of 3 sources checked- cites Ding et al., 2018
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- cites L. Li, Han, et al., 2024
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- cites H.Chen et al., 2024
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PremisecitationLong-chain PFAS with C ≥ 8 and functionally diverse PFAS preferentially associate with sediment.
“whereas long-chain (C ≥ 8) and functionally diverse PFAS preferentially associate with sediment.”
Quote in the paperSubstantial claim0 of 3 sources checked- cites Ahrens et al., 2010
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- cites Y. Liu et al., 2019
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- cites N. Shen et al., 2024
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PremisecitationReported sediment-porewater partition fractions for PFBA, midchain PFCAs C9-C11, PFSAs C6-C8, HFPO-DA, and 6:2 Cl-PFESA ranged from 64.61% to 97.87%, indicating greater retention in the solid phase than in the liquid phase.
“while 64.61%-97.87% reported for perfluorobutanoic acid (PFBA), midchain PFCAs (C9-C11), PFSAs (C6-C8), HFPO-DA, and 6:2 Cl-PFESA, showing higher retention in the solid phase than in the liquid phase.”
Quote in the paperSubstantial claim0 of 1 sources checked- cites N. Shen et al. (2024)
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PremisecitationOrganic-rich sediments retain PFAS more strongly, while low organic carbon in sediments enhances mobility of dissolved PFAS in overlying water.
“Generally, organicrich sediments retain PFAS more strongly, while low organic carbon in sediments enhances the mobility of dissolved PFAS in overlaying water (Bai & Son, 2021;Navarro et al., 2022;Oliver et al., 2020).”
Quote in the paperSubstantial claim0 of 3 sources checked- cites Bai & Son, 2021
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- cites Navarro et al., 2022
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- cites Oliver et al., 2020
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InterpretationcitationGenerally lower concentrations of many short-chain PFAS in sediment and SPM indicate weak partitioning to solids and reinforce their persistence in the aqueous phase.
“Generally lower concentrations of many short-chain PFAS in sediment and SPM underscore their weak partitioning to solids and reinforce their persistence in the aqueous phase (Ahrens et al., 2010;Göckener et al., 2022).”
Quote in the paperNot a substantial claim0 of 2 sources checked- cites Ahrens et al., 2010
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- cites Göckener et al., 2022
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PremisecitationIn water-SPM systems, log Kd values generally range from 2.0 to 3.8 for medium-to-long chain PFCAs and from 1.9 to 3.4 for C6-C8 PFSAs, with sorption capacity increasing with chain length.
“In water-SPM systems, log K d values generally range between 2.0 and 3.8 for medium-to-long chain PFCAs and 1.9-3.4 for C6-C8 PFSAs (Y.Liu et al., 2019;Munoz et al., 2019), with sorption capacity increasing with chain length (Y.Li, Zhao, et al., 2024).”
Quote in the paperNot a substantial claim0 of 3 sources checked- cites Y.Liu et al., 2019
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- cites Munoz et al., 2019
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- cites Y.Li, Zhao, et al., 2024
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InterpretationreasoningWhile acute toxicity appears limited, sediments function as long-term PFAS reservoirs, driving chronic benthic exposure through direct uptake, trophic transfer, and precursor biotransformation.
“Thus, while acute toxicity appears limited, sediments function as long-term PFAS reservoirs, driving chronic benthic exposure through direct uptake, trophic transfer, and precursor biotransformation.”
Quote in the paperSubstantial claimMay combine two claims.
PremisecitationL. variegatus converted N-EtFOSAA into PFOS, acting as a secondary PFOS source.
“L. variegatus also converted N-EtFOSAA into PFOS, acting as a secondary PFOS source (Higgins et al., 2007).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Higgins et al., 2007
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PremisecitationMonoporeia affinis exposed to PFOS (50-5000 ng/L) showed reduced survival, impaired development, and higher microsporidian parasite infection.
“Monoporeia affinis (amphipod) exposed to PFOS (50-5000 ng/L) showed reduced survival, impaired development, and higher microsporidian parasite infection, indicating direct toxicity and immune suppression (Jacobson et al., 2010).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Jacobson et al., 2010
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PremisecitationDesorption is often inhibited under high-salinity conditions, particularly for long-chain PFAS, although the effect is less pronounced in organic-rich sediments where TOC provides a dominant control on retention.
“Additionally, desorption is often inhibited under high-salinity conditions, particularly for long-chain PFAS, although the effect is less pronounced in organicrich sediments where TOC provides a dominant control on retention (Navarro et al., 2022).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Navarro et al., 2022
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InterpretationcitationSimulated dredging tests using spiked sediment elutriates showed no acute toxicity in pelagic organisms, suggesting PFAS remobilization from sediments may not present immediate risks under typical environmental conditions.
“Furthermore, simulated dredging tests using spiked sediment elutriates showed no acute toxicity in pelagic organisms (Cyprinodon variegatus, Pimephales promelas, Ceriodaphnia dubia, Americamysis bahia), suggesting that PFAS remobilization from sediments may not present immediate risks under typical environmental conditions (Krupa et al., 2025).”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Krupa et al., 2025
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PremisereasoningLonger chain and more hydrophobic PFAS generally exhibit stronger sediment affinity and lower desorption rates.
“Longer chain and more hydrophobic PFAS generally exhibit stronger sediment affinity and lower desorption rates.”
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PremisecitationMost field sediment concentrations fall below this threshold, with no acute toxicity in algae, copepods, or amphipods.
“Most field sediment concentrations fall below this threshold, with no acute toxicity in algae, copepods, or amphipods (Simpson et al., 2021).”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Simpson et al., 2021
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PremisereasoningNatural organic matter and elevated pH inhibit PFAS adsorption through electrostatic repulsion.
“Conversely, NOM and elevated pH inhibit adsorption through electrostatic repulsion, respectively.”
Quote in the paperNot a substantial claimMay combine two claims.
PremisecitationTheir sediment RQ calculations ranged from 1.4 × 10^-4 to 8.9 × 10^-1 for PFOS and from 5.0 × 10^-5 to 5.6 × 10^-2 for PFOA, indicating minimal ecological risk under typical conditions.
“Their sediment RQ calculations ranged from 1.4 × 10 -4 to 8.9 × 10 -1 for PFOS and from 5.0 × 10 -5 to 5.6 × 10 -2 for PFOA, indicating minimal ecological risk under typical conditions.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Hua et al. (2021)
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InterpretationcitationSediments act as persistent, bioavailable PFAS reservoirs that disproportionately affect benthic ecosystems.
“Sediments act as persistent, bioavailable PFAS reservoirs, disproportionately affecting benthic ecosystems (Table 4).”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Table 4
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Premisecitation6:2 Cl-PFESA has maintained persistently high risk (RQ > 1) since the 1970s, with moderate risks (RQ = 0.16-0.38) persisting in recent decades.
“In contrast, 6:2 Cl-PFESA has maintained persistently high risk (RQ > 1) since the 1970s, with moderate risks (RQ = 0.16-0.38)persisting in recent decades (Q.Wang, Ruan, et al., 2025).”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Q.Wang, Ruan, et al., 2025
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PremisecitationMicroplastics, particularly secondary microplastics, have the potential to adsorb PFAS from aquatic environments and serve as transport channels.
“Another research by Salawu et al. (2024) has demonstrated that MPs, particularly secondary MPs, have the potential to adsorb PFAS from aquatic environments, thus serving as potential transport channels.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Salawu et al. (2024)
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PremisecitationSpecies-specific differences in precursor metabolism were observed among Cyprinus carpio, Misgurnus anguillicaudatus, and L. hoffmeisteri, with loach showing higher biotransformation efficiency while worms accumulated more precursors.
“Species-specific differences in precursor metabolism were observed among Cyprinus carpio (carp), Misgurnus anguillicaudatus (loach), and L. hoffmeisteri, with loach showing higher biotransformation efficiency, while worms accumulated more precursors (M.Chen et al., 2019).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites M.Chen et al., 2019
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Premisenone givenAdsorption equilibrium is attained within hours, indicating rapid PFAS-microplastic interaction.
“Adsorption equilibrium is attained within hours, signifying rapid PFAS-MP interaction.”
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InterpretationreasoningBioturbation, sediment composition, and microbial activity modulate PFAS risk in sediments.
“Bioturbation, sediment composition, and microbial activity modulate this risk, underscoring the need for sediment-focused ecological assessments.”
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PremisecitationPFOA showed medium risk at 41% of sites and low risk at 54% in the East China Sea and Yellow Sea.
“PFOA showed medium risk at 41% of sites and low risk at 54%.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Zhong et al. (2021)
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PremisecitationFe(II) markedly increased PFAS sorption under anoxic conditions, surpassing the adsorption enhancement observed with Cu(II) and Cd(II).
“Notably, Fe(II) was found to markedly increase PFAS sorption under anoxic conditions, surpassing the adsorption enhancement observed with Cu(II) and Cd(II).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Chaudhary et al. (2024)
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PremisecitationBiota-sediment accumulation factors reached 22-559, and δ13C analysis linked elevated fish PFAS burdens to benthic diets.
“Biota-sediment accumulation factors reached 22-559, and δ 13 C analysis linked elevated fish PFAS burdens to benthic diets.”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Langberg et al., 2020
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Premisenone givenPrecursors such as 8:2 polyfluoroalkylphosphate diester and N-EtFOSAA are bioavailable and metabolically active.
“Precursors such as 8:2 polyfluoroalkylphosphate diester and N-ethyl perfluorooc-tane sulfonamidoacetic acid (N-EtFOSAA) are bioavailable and metabolically active.”
Quote in the paperSubstantial claimMay combine two claims.
PremisecitationIn Lake Tyrifjorden, despite low water-phase linear PFOS (max 0.18 ng/L), perch livers averaged 149 ng/g, with BAF up to 5.14 × 10^6.
“Field data from Lake Tyrifjorden highlight this instances: despite low water-phase linear perfluorooctanesulfonic acid (max 0.18 ng/L), perch livers averaged 149 ng/g, with bioaccumulation factors (BAF) up to 5.14 × 10 6 (Langberg et al., 2020).”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Langberg et al., 2020
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PremisecitationPFOA consistently posed low risk (RQ < 0.1), while PFOS showed RQ > 1 from the 1960s to 2010s, declining only after regulatory controls.
“PFOA consistently posed low risk (RQ < 0.1), while PFOS showed RQ > 1 from the 1960s to 2010s, declining only after regulatory controls (Q.Wang, Ruan, et al., 2025).”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Q.Wang, Ruan, et al., 2025
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PremisecitationReported 24-h desorption rates range from 9% to 69% for PFOS, 33% to 91% for PFOA, and 43% to 116% for PFHxS, consistent with median Kd values of 30.4 L/kg for PFOS, 3.3 L/kg for PFOA, and 2.8 L/kg for PFHxS.
“For example, reported 24-h desorption rates range from 9% to 69% for PFOS, 33% to 91% for PFOA, and 43% to 116% for PFHxS (Oliver et al., 2020), consistent with median K d values of 30.4 L/kg for PFOS, 3.3 L/kg for PFOA, and 2.8 L/kg for PFHxS.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Oliver et al., 2020
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PremisecitationL. variegatus bioturbation reduced PFAS accumulation in Myriophyllum spicatum but facilitated greater root uptake of degradable PFAS precursors.
“Similarly, L. variegatus bioturbation reduced PFAS accumulation in Myriophyllum spicatum (aquatic plant) but facilitated greater root uptake of degradable PFAS precursors, indicating reciprocal interactions between biotic activity and contaminant mobility (Gkika et al., 2024).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Gkika et al., 2024
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PremisecitationBioturbation by Hyalella azteca and Limnodrilus hoffmeisteri enhanced PFOS release into suspended particulates, lowering pore/overlying water PFAS but increasing exposure for cohabiting species; Chironomus kiiensis suffered 100% mortality under these conditions.
“Hyalella azteca and Limnodrilus hoffmeisteri activity enhanced PFOS release into suspended particulates, lowering pore/overlying water PFAS but increasing exposure for cohabiting species; Chironomus kiiensis suffered 100% mortality under these conditions (Z.Wu, Li, et al., 2021).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Z.Wu, Li, et al., 2021
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PremisecitationPFAS uptake by benthic organisms occurs via dermal contact, sediment ingestion, and trophic transfer.
“Uptake occurs via dermal contact, sediment ingestion, and trophic transfer (Abercrombie et al., 2020;Simpson et al., 2021).”
Quote in the paperSubstantial claim0 of 2 sources checked- cites Abercrombie et al., 2020
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- cites Simpson et al., 2021
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PremisecitationIn the East China Sea and Yellow Sea, 71% of sampling sites showed medium ecological risk for PFOS (RQ = 0.1-1), while high risk (RQ > 1) was recorded in four hotspots.
“For PFOS, 71% of sampling sites showed medium ecological risk (RQ = 0.1-1), while high risk (RQ > 1) was recorded in four hotspots.”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Zhong et al. (2021)
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PremisecitationSimpson et al. (2021) reported lowest observed effect concentrations for PFOS at 0.28 mg/L for bivalve growth, 0.49 mg/L for amphipod survival, and 1.2 mg/L for amphipod reproduction.
“Simpson et al. (2021) reported lowest observed effect concentrations for PFOS at 0.28 mg/L (bivalve growth), 0.49 mg/L (amphipod survival), and 1.2 mg/L (amphipod reproduction).”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Simpson et al. (2021)
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PremisecitationIn the United States, the EPA finalized enforceable maximum contaminant levels in 2024 for drinking water, with compliance due by 2031: 4 ng/L for PFOA and PFOS; 10 ng/L for PFNA, PFHxS, and HFPO-DA; and 2000 ng/L for PFBS.
“In the United States, the EPA finalized enforceable maximum contaminant levels in 2024 for drinking water, with compliance due by 2031: 4 ng/L for PFOA and PFOS; 10 ng/L for PFNA, PFHxS, and HFPO-DA (GenX); and 2000 ng/L for PFBS.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites USEPA, 2024
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PremisecitationYu et al. (2024) showed AC amendments lowered PFAA release by 45.5%-99.2% under low disturbance and by 61.0%-98.8% under high disturbance.
“Yu et al. (2024) showed AC amendments lowered PFAA release by 45.5%-99.2%under low disturbance and by 61.0%-98.8%under high disturbance.”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Yu et al. (2024)
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PremisecitationPFAS with longer chains or sulfonate groups are more hydrophobic and have a stronger affinity for sediment.
“This trend mirrors log K ow : longer chain and sulfonated PFAS show greater hydrophobicity and sediment affinity (Y.Chen et al., 2023; Meng et al., 2021; S. Xiao et al., 2021).”
Quote in the paperSubstantial claim0 of 3 sources checked- cites Y.Chen et al., 2023
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- cites Meng et al., 2021
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- cites S. Xiao et al., 2021
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Premisenone givenEmerging PFAS and replacements often have higher sediment-water partitioning coefficients.
“Emerging PFAS and replacements, often with higher sediment-water partitioning coefficients, require systematic inclusion in monitoring and risk frameworks.”
Quote in the paperNot a substantial claimProbably not a substantial claim: may not pass S4 (based).
Premisenone givenRemediation approaches remain largely experimental or cost-prohibitive.
“Remediation approaches remain largely experimental or cost-prohibitive;”
Quote in the paperNot a substantial claimMay combine two claims.
PremisecitationDestructive techniques such as sonolysis and smoldering combustion are actively investigated but not field ready, while separation methods demonstrate feasibility yet face deployment barriers.
“Destructive techniques, such as sonolysis and smoldering combustion, are actively investigated but not field ready, while separation methods (foam fractionation, thermal desorption, and soil washing) demon-strate feasibility yet face deployment barriers (Abrams et al., 2022).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Abrams et al., 2022
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PremisecitationThe emerging compounds 6:2 and 8:2 Cl-PFESAs have high log Kow values (5.24-7.03) and high log Kd.
“Emerging compounds such as 6:2 and 8:2 chlorinated polyfluoroalkyl ether sulfonic acids (Cl-PFESAs) also exhibit high log K ow (5.24-7.03)and log K d (H.Chen et al., 2024;Higgins & Luthy, 2006;Tang et al., 2022).”
Quote in the paperNot a substantial claim0 of 3 sources checked- cites H.Chen et al., 2024
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- cites Higgins & Luthy, 2006
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- cites Tang et al., 2022
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InterpretationreasoningOrganisms living in sediments are exposed to higher PFAS levels via uptake, accumulation in tissues, and transfer through food webs.
“Sediment-dwelling organisms face heightened exposure through bioavailability, bioaccumulation, and trophic transfer, influenced by bioturbation, microbial transformations, and local geochemical factors.”
Quote in the paperSubstantial claimProbably not a substantial claim: may not pass S3 (load-bearing), S4 (based). May combine two claims.
Premisenone givenProposed EU thresholds include a stricter biota limit of 0.0077 ng/g ww and a surface water standard of 4.4 ng/L, shifting emphasis from fish consumption toward drinking-water exposure.
“Proposed thresholds include a stricter biota limit (0.0077 ng/g ww) and a surface water standard of 4.4 ng/L, shifting emphasis from fish consumption toward drinking-water exposure.”
Quote in the paperNot a substantial claimMay combine two claims.
InterpretationreasoningOverall average sediment RQs remained low, but hotspots and interspecies variability demand site-specific, long-term assessments, particularly in historically contaminated or industrial regions.
“Overall, average sediment RQs remained low, but hotspots and interspecies variability demand sitespecific, long-term assessments, particularly in historically contaminated or industrial regions.”
Quote in the paperSubstantial claimMay combine two claims.
InterpretationreasoningSediment is addressed only indirectly through CERCLA-driven cleanups and discharge regulations, offering reactive rather than preventive control.
“Sediment is only addressed indirectly through CERCLA-driven cleanups and discharge regulations, offering reactive rather than preventive control.”
Quote in the paperSubstantial claimMay combine two claims.
InterpretationreasoningSorbent amendments are cost-effective and minimally invasive, immobilizing PFAS by reducing mobility and bioavailability and supporting natural recovery.
“Among in situ methods, sorbent amendments are costeffective and minimally invasive.These materials, when integrated into the sediment matrix, immobilize PFAS by reducing their mobility and bioavailability, supporting natural recovery processes.”
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Interpretationnone givenBecause the EU and the United States have no sediment-specific EQS, a regulatory gap exists that undermines long-term PFAS management.
“Policy progress has been achieved in drinking water and biota standards in the EU and United States; however, both jurisdictions lack sediment-specific EQS, leaving a critical regulatory gap that weakens long-term PFAS management.”
Quote in the paperNot a substantial claimProbably not a substantial claim: may not pass S4 (based).
Interpretationnone givenPFAS partitioning among sediment, SPM, and porewater is controlled by complex geochemical interactions such as organic matter, mineralogy, and electrostatics that remain poorly quantified.
“PFAS partitioning among sediment, SPM, and porewater is controlled by complex geochemical interactions such as organic matter, mineralogy, and electrostatics that remain poorly quantified.”
Quote in the paperNot a substantial claimProbably not a substantial claim: may not pass S3 (load-bearing).
Premisenone givenIn 2022, a revised EQS proposal extended coverage to 24 PFAS based on EFSA's 2020 Tolerable Weekly Intake.
“In 2022, a revised EQS proposal extended coverage to 24 PFAS, based on European Food Safety Authority's 2020 Tolerable Weekly Intake.”
Quote in the paperNot a substantial claimProbably not a substantial claim: may not pass S3 (load-bearing), S4 (based). May combine two claims.
Premisenone givenThe 2020 Drinking Water Directive (effective 2023) added combined limits of 100 ng/L for 20 PFAS and 500 ng/L for total PFAS in public water supplies.
“The 2020 Drinking Water Directive (effective 2023) added combined limits of 100 ng/L for 20 PFAS and 500 ng/L for total PFAS in public water supplies.”
Quote in the paperNot a substantial claimMay combine two claims.
PremisecitationHigh doses of AC can alter microbial community structures and negatively impact benthic organisms, particularly deposit-feeding species.
“High doses of AC can alter the structures of microbial communities and negatively impact benthic organisms, particularly depositfeeding species (Jonker et al., 2009;Kupryianchyk et al., 2011).”
Quote in the paperSubstantial claim0 of 2 sources checked- cites Jonker et al., 2009
Not checked in the free run.
- cites Kupryianchyk et al., 2011
Not checked in the free run.
May combine two claims.
PremisecitationThe log Koc of perfluoroalkyl acids rises with carbon chain length, from 2.84 for PFOA to 4.63 for PFTrDA, an increase of roughly 0.22-0.24 log units per CF2 group.
“with log K oc from 2.84 (perfluorooctanoic acid [PFOA]) to 4.63 (PFTrDA), rising ∼0.22-0.24log units per CF 2 group (Tulcan et al., 2025).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Tulcan et al., 2025
Not checked in the free run.
May combine two claims.
PremisecitationField-scale data on sediment remediation remain sparse, with most technologies still in development or pilot testing.
“However, field-scale data on sediment remediation remain sparse, with most technologies still in development or pilot testing.”
Quote in the paperNot a substantial claimMay combine two claims.
PremisecitationPhysical removal by dredging or excavation followed by off-site incineration or advanced oxidation can fully destroy PFAS, but these methods are energy-intensive and expensive, limiting application to high-priority or localized sites.
“Physical removal by dredging or excavation, followed by off-site incineration or advanced oxidation processes, can fully destroy PFAS.However, these methods are energy-intensive and expensive, limiting their application to high-priority or localized contamination sites (Lampert, 2018).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Lampert, 2018
Not checked in the free run.
Probably not a substantial claim: may not pass S3 (load-bearing).
PremisecitationHealth Canada set a drinking water target of 30 ng/L for 25 PFAS compounds.
“but Health Canada collaborated with provinces, territories, and other federal agencies to set a drinking water target of 30 ng/L for 25 PFAS compounds (Health Canada, 2024).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Health Canada, 2024
Not checked in the free run.
May combine two claims.
PremisecitationOther sorbent-based methods including biochar, ion exchange resins, and carbon nanotubes show promise but remain at pilot scale.
“Other sorbent-based methods, including biochar, ion exchange resins, and carbon nanotubes, show promise but remain at pilot scale.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Abrams et al., 2022
Not checked in the free run.
May combine two claims.
PremisecitationLong-term AC applications improved sediment resilience with limited ecological disruption.
“Long-term AC applications improved sediment resilience with limited ecological disruption.”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Yu et al. (2024)
Not checked in the free run.
May combine two claims.
Premisenone givenIn the EU, PFAS are primarily regulated under the Water Framework Directive, which sets EQS for PFOS at 0.65 ng/L in inland waters, 0.13 ng/L in coastal waters, and 9.1 ng/g ww in fish.
“In the EU, PFAS are primarily regulated under the Water Framework Directive, which sets environmental quality standards (EQS) for compounds such as PFOS: 0.65 ng/L (inland waters), 0.13 ng/L (coastal waters), and 9.1 ng/g ww in fish.”
Quote in the paperNot a substantial claimProbably not a substantial claim: may not pass S4 (based). May combine two claims.
Premisenone givenCurrent risk assessments are geographically biased, with most work focused on Chinese coastal systems; comparable data from inland waters, polar regions, and developing countries are sparse.
“Current risk assessments are geographically biased, with most work focused on Chinese coastal systems; comparable data from inland waters, polar regions, and developing countries are sparse, limiting global-scale evaluations.”
Quote in the paperNot a substantial claim
The paper relies on this without support.
The set of 88 studies is representative enough of global aquatic sediments to support continent-level comparisons.
“A total of 88 studies (2015-present) have assessed the distribution of PFAS in aquatic sediment worldwide, which include lakes, rivers, estuaries, and marine environments.”
The paper relies on this without support.
Summing concentrations of individual PFAS compounds across studies with different target lists yields comparable total PFAS concentrations.
“The mean concentration values were derived by summing the concentrations of all individual PFAS compounds at each sampling point and then averaging these totals across the entire site.”
The paper relies on this without support.
A comprehensive synthesis of sediment-specific PFAS dynamics and global distribution is lacking.
“comprehensive insight into sediment-specific PFAS dynamics and global distribution remains scarce to the best of my knowledge”
The paper relies on this without support.
The upper 0-10 cm sediment layer is the appropriate compartment for assessing PFAS as a long-term reservoir.
“the term”
The paper relies on this without support.
PFAS are anthropogenic chemicals that persist in the environment and can impact aquatic life.
“PFAS, a group of manmade chemicals released and dispersed into the ecosystems, remain a persistent global environmental concern that can impact aquatic life.”
The paper relies on this without support.
The peer-reviewed literature synthesized is representative of global PFAS sediment distribution.
“A synthesis of peer-reviewed literature revealed that PFAS contamination in sediments is widespread across the globe, with the African continent found to be more contaminated.”
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 [29]
Section 3.2 says hydrological fluctuations can remobilize PFAS from sediments, and the Conclusion recommends including sediments in PFAS monitoring. The paper does not establish that distinct hydrological processes govern sediment-bound PFAS across rivers, lakes, estuaries, and open waters, or specifically call for watershed-level monitoring on that basis. No page numbers were available for these passages. (LLM, conf=0.83)
Experimental — accuracy not yet measuredShort-chain PFAS (PFBS, PFBA, PFMeS) were predominantly detected in the dissolved phase, reflecting their higher aqueous solubility and lower sorption coefficients.
“In contrast, short-chain PFAS (PFBS, PFBA, PFMeS) were predominantly detected in the dissolved phase, reflecting their higher aqueous solubility and lower sorption coefficients.”
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 [29]
Section 3.3 (page unavailable) says short-chain PFAS predominate in porewater because of greater solubility and mobility, and lower sorption; Section 3.4 names PFBA and PFBS among dissolved PFAS in surface water. The copy does not establish the claim specifically for PFMeS, so the three-compound list is not fully supported. (LLM, conf=0.88)
Experimental — accuracy not yet measured
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.
South African dam mean falls below its reported range
MajorThe reported mean of 274.1 ng/g is below the reported minimum of 400.5 ng/g for the same site. This affects the site identified as having Africa's highest average.
“Roodeplaat, Hartbeespoort Dams, South Africa 20 10 400.5-591.4274.1 HPLC-MS/MS (Batayi et al., 2020)”
“The mean concentration values were derived by summing the concentrations of all individual PFAS compounds at each sampling point and then averaging these totals across the entire site.”
Apies River mean falls below its reported range
MajorTable 1 gives a mean of 31.35 ng/g, although its reported concentrations range from 300 to 350 ng/g. A mean of values in that range cannot be 31.35 ng/g.
“Apies River, South Africa 18 18 300-350 31.35HPLC-MS/MS (Okwuosa, Nomngongo, Olatunji, et al., 2025)”
“The mean concentration values were derived by summing the concentrations of all individual PFAS compounds at each sampling point and then averaging these totals across the entire site.”
Florida study has conflicting targeted-compound counts
MinorThe narrative says Griffin et al. targeted 93 PFAS, whereas its Table 1 row lists 92.
“Griffin et al. (2023) targeted the highest number of PFAS (93) in Florida”
“Florida, USA 92 14 0.1-8.40.43 UHPLC-MS/MS (Griffin et al., 2023)”
Michigan mean exceeds its reported maximum
MinorThe Michigan row reports a mean of 7.32 ng/g but a maximum of 3.25 ng/g. The mean cannot exceed the maximum of the values averaged.
“Michigan, USA 10 10 ND-3.25 7.32 LC-MS/MS (Balgooyen & Remucal, 2022)”
“The mean concentration values were derived by summing the concentrations of all individual PFAS compounds at each sampling point and then averaging these totals across the entire site.”
Gironde row detects more compounds than it targets
MinorTable 3 lists 26 targeted PFAS and 27 detected PFAS for the same Gironde Estuary study. The detected count cannot exceed the targeted count under the table's stated headings.
“Gironde Estuary, France 26 27 0.077-8.30.11-3.30.98-10 -PFBA-2.5 PFBS-1.3PFOA-3.1 PFHxS-2.2 (Munoz et al., 2017)”
“Location Total PFAS targeted Total PFAS detected Surface water (ng/L) Sediment (ng/g) SPM (ng/g)”
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Cited by
Sorted by citations
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
- Authors
- Ehsan, M. N.
- Affiliations
- Southeast University (BD)
- Corresponding author
- Ehsan, Mohammad Nazmul
- Venue
- Journal of Environmental Quality
- Publisher
- Wiley
- Published
- 2026-01
- Volume
- 55
- Issue
- 1
- Pages
- e70148-e70148
- ISSN
- 0047-2425 (ISSN-L)
- 1537-2537
- OpenAlex
- W7126240361
- Cited by
- 2
- References
- 26
- Citations by year
- 2026: 2
- FWCI
- 1.13
- Type
- journal article
- Language
- en
- Open access
- bronze
- doi.org
- Licence
- Locations
- Journal of Environmental Quality (publishedVersion)
- PubMed (publishedVersion)
- Topics
- Physical Sciences › Environmental Science › Environmental Chemistry › Per- and polyfluoroalkyl substances research
- Physical Sciences › Environmental Science › Health, Toxicology and Mutagenesis › Toxic Organic Pollutants Impact
- Physical Sciences › Environmental Science › Health, Toxicology and Mutagenesis › Environmental Toxicology and Ecotoxicology
- Keywords
- per- and polyfluoroalkyl substances, PFAS, aquatic sediments, global distribution, suspended particulate matter, benthic organisms, bioaccumulation, trophic transfer, environmental risk assessment, persistent organic pollutants
- MeSH terms
- Animals, Environmental Monitoring, Fluorocarbons, Water Pollutants, Chemical, Geologic Sediments
About these checks
Registry, retraction, Cites and statistics results are computed, not judged, with one exception: a printed reference that no index lists is read once by a model before it counts as a citation error. Claims are extracted by a model and kept only when their quote appears verbatim in the text; each cited source is then checked, with a model’s help, for whether it says what the claim relies on. Those verdicts can be wrong — read the claim’s quote and the cited source before relying on one.
Claims read by deepseek-v4.1-flash under definition version 3 (extract-v3) on 2026-10-06.
Classified by jev-1.13-20260917 (gold-guideline-v0.2) on 2026-10-06.
Statistics and arithmetic are recomputed, not judged.
Confidence bands are shown only for fields calibrated on our annotated test set. None is calibrated yet, so no band is shown.
What counts as a claim ›How we measure confidence ›How we check this ›
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