A Mathematical Model for the Release, Transport, and Retention of Per‐ and Polyfluoroalkyl Substances (PFAS) in the Vadose Zone
Open accessAbstract
Per‐ and polyfluoroalkyl substances (PFAS) are emerging contaminants of critical concern. As surfactants, PFAS tend to accumulate at air‐water interfaces and may stay in the vadose zone for long times before contaminating groundwater. Yet not well understood, the extent of retention in the vadose zone has critical implications for risk management and remediation strategies. We present the first mathematical model that accounts for surfactant‐induced flow and solid‐phase and air‐water interfacial adsorption. We apply the model to simulate PFOS (a PFAS compound of primary concern) transport in the vadose zone at a model fire‐training area site impacted by aqueous film‐forming foam (AFFF). Air‐water interfacial adsorption is shown to have a significant impact—amplified by the low water content due to gravity drainage—total retardation factors range from 233 to 1,355 for the sand and 146 to 792 for the soil used in the study. The simulations illustrate it can take several decades or longer for PFOS to reach groundwater. Counterintuitively, the lower water content in the sand—due to stronger drainage and weaker capillary retention—leads to retardation factors greater than for the soil. Also, most PFOS is adsorbed at air‐water interfaces with only 1–2% in the aqueous phase. The implications include (1) fine‐texture materials could have lower retardation factors than sand due to higher retained water content, (2) soil PFAS concentrations are likely to be orders of magnitude higher than those in groundwater at source zones. Both implications are consistent with recent field observations at hundreds of AFFF‐impacted sites.
Verified 2026-10-06 · 19 references not checked yet
Integrity signals
Registry
Cites
Statistics
Claims the paper makes
0 of 39 cited sources checked · 0 supported · 0 flagged
- Findingreasoning
The lower water content in the sand, caused by stronger drainage and weaker capillary retention, produced retardation factors greater than those for the soil.
“Counterintuitively, the lower water content in the sand—due to stronger drainage and weaker capillary retention—leads to retardation factors greater than for the soil.”
Quote in the paperSubstantial claim- The authors state this as an assumption: Capillary pressure head scales with surface tension according to Leverett scaling.
- The authors state this as an assumption: The contact angle does not change when PFAS is dissolved.
- The authors state this as an assumption: All precipitation is treated as rainfall, with no distinction between rain and snow.
- The authors state this as an assumption: Evapotranspiration data are approximated as potential evapotranspiration to determine surface evaporation fluxes.
- The authors state this as an assumption: All applied AFFF solution infiltrates into the vadose zone.
- Findingown data
Including interfacial adsorption increased the time for PFOS to reach groundwater by one to two orders of magnitude, from 1-2 years to several decades or longer.
“The overall time scale for PFOS to reach groundwater has increased by one to two orders of magnitude from 1 or 2 years to several decades or longer.”
Quote in the paperSubstantial claim- The authors state this as an assumption: Capillary pressure head scales with surface tension according to Leverett scaling.
- The authors state this as an assumption: The contact angle does not change when PFAS is dissolved.
- The authors state this as an assumption: All precipitation is treated as rainfall, with no distinction between rain and snow.
- The authors state this as an assumption: Evapotranspiration data are approximated as potential evapotranspiration to determine surface evaporation fluxes.
- The authors state this as an assumption: All applied AFFF solution infiltrates into the vadose zone.
- Findingreasoning
Among the four scenarios, PFOS moved slowest with low PFOS concentration under a semi-arid climate, with the front migrating only 2 meters after 40 years.
“Among the four scenarios, PFOS propagates the slowest with the low PFOS concentration under a semi-arid climate—the front has only migrated down 2 meters after 40 years.”
Quote in the paperNot a substantial claim- The authors state this as an assumption: Capillary pressure head scales with surface tension according to Leverett scaling.
- The authors state this as an assumption: The contact angle does not change when PFAS is dissolved.
- The authors state this as an assumption: All precipitation is treated as rainfall, with no distinction between rain and snow.
- The authors state this as an assumption: Evapotranspiration data are approximated as potential evapotranspiration to determine surface evaporation fluxes.
- The authors state this as an assumption: All applied AFFF solution infiltrates into the vadose zone.
- Findingown data
The wetting front reached the groundwater table in about 60 days in the Vinton soil.
“For Vinton, the wetting front propagation is considerably slower—it takes ~ 60 days for the wetting front to reach the groundwater table (Fig. 4(b)).”
Quote in the paperSubstantial claim- The authors state this as an assumption: Capillary pressure head scales with surface tension according to Leverett scaling.
- The authors state this as an assumption: The contact angle does not change when PFAS is dissolved.
- The authors state this as an assumption: All precipitation is treated as rainfall, with no distinction between rain and snow.
- The authors state this as an assumption: Evapotranspiration data are approximated as potential evapotranspiration to determine surface evaporation fluxes.
- The authors state this as an assumption: All applied AFFF solution infiltrates into the vadose zone.
- Findingown data
The wetting front reached the groundwater table in about 5 days in the Accusand.
“The results show that it takes ~ 5 days for the wetting front to reach the groundwater table in the Accusand (Fig. 4(a)).”
Quote in the paperSubstantial claim- The authors state this as an assumption: Capillary pressure head scales with surface tension according to Leverett scaling.
- The authors state this as an assumption: The contact angle does not change when PFAS is dissolved.
- The authors state this as an assumption: All precipitation is treated as rainfall, with no distinction between rain and snow.
- The authors state this as an assumption: Evapotranspiration data are approximated as potential evapotranspiration to determine surface evaporation fluxes.
- The authors state this as an assumption: All applied AFFF solution infiltrates into the vadose zone.
- Findingown data
Total retardation factors ranged from 233 to 1355 for the sand and 146 to 792 for the soil.
“total retardation factors range from 233 to 1355 for the sand and 146 to 792 for the soil used in the study.”
Quote in the paperSubstantial claim- The authors state this as an assumption: Capillary pressure head scales with surface tension according to Leverett scaling.
- The authors state this as an assumption: The contact angle does not change when PFAS is dissolved.
- The authors state this as an assumption: All precipitation is treated as rainfall, with no distinction between rain and snow.
- The authors state this as an assumption: Evapotranspiration data are approximated as potential evapotranspiration to determine surface evaporation fluxes.
- The authors state this as an assumption: All applied AFFF solution infiltrates into the vadose zone.
- Findingreasoning
The extent of PFOS retardation varies with climate and PFOS concentration.
“The extent of retardation varies among different climates and PFOS concentrations.”
Quote in the paperSubstantial claim- The authors state this as an assumption: Capillary pressure head scales with surface tension according to Leverett scaling.
- The authors state this as an assumption: The contact angle does not change when PFAS is dissolved.
- The authors state this as an assumption: All precipitation is treated as rainfall, with no distinction between rain and snow.
- The authors state this as an assumption: Evapotranspiration data are approximated as potential evapotranspiration to determine surface evaporation fluxes.
- The authors state this as an assumption: All applied AFFF solution infiltrates into the vadose zone.
- Findingreasoning
In Vinton soil scenarios without air-water interfacial adsorption, PFOS migration is much slower than in Accusand simulations.
“the scenarios without air-water interfacial adsorption also produce much slower PFOS migration than those in the Accusand simulations.”
Quote in the paperNot a substantial claim - Findingnone given
Surface tension drops from 65.7 mN/m to 52.8 mN/m when aqueous PFOS concentration increases from 2 mg/L to 20 mg/L.
“the surface tension drops from 65.7mN/m to 52.8mN/m when the aqueous concentration increases from 2mg/L to 20mg/L.”
Quote in the paperNot a substantial claim - Findingown data
After PFOS reaches the higher water saturation zone near the groundwater table, saturation and air-water interfacial area become more sensitive to capillary pressure head.
“After PFOS reaches the higher water saturation zone near the groundwater table, saturation and air-water interfacial area become more sensitive to capillary pressure head.”
Quote in the paperSubstantial claim - Findingown data
For all simulated cases, total cumulative PFOS mass increases linearly before PFOS reaches groundwater.
“For all cases, the total cumulative mass of PFOS increases linearly before PFOS reaches groundwater.”
Quote in the paperNot a substantial claim - Findingreasoning
In Vinton soil when air-water interfacial adsorption is turned off, cumulative PFOS in the vadose zone plateaus at a much higher value than in Accusand.
“When air-water interfacial adsorption is turned off, the cumulative PFOS in the vadose zone plateaus at a much higher value than that of the Accusand case.”
Quote in the paperNot a substantial claim - Findingreasoning
Vinton soil has higher relative permeabilities than Accusand because of higher water content.
“though Vinton has higher relative permeabilities because of the higher water content”
Quote in the paperSubstantial claim - Findingown data
In Vinton soil, it takes about 5 years (high PFOS concentration, humid climate) to about 20 years (low PFOS concentration, semi-arid climate) for PFOS to reach groundwater.
“It takes ~ 5 years (high PFOS concentration; humid climate) to ~ 20 years (low PFOS concentration; semi-arid climate) for the PFOS to reach groundwater.”
Quote in the paperSubstantial claim - Findingreasoning
The simulations show counterintuitively that Vinton soil has lower PFOS retardation factors than Accusand.
“Our simulations show rather counterintuitively that the Vinton soil has lower PFOS retardation factors compared to the Accusand.”
Quote in the paperSubstantial claim - Findingown data
In the simulated vadose zone, most PFOS mass is adsorbed at air-water interfaces.
“The majority of the PFOS in the vadose zone is adsorbed at air-water interfaces.”
Quote in the paperSubstantial claim - Findingreasoning
The partitioning of PFOS mass among air-water interfacial adsorption, solid-phase adsorption, and aqueous phase varies over time, primarily due to time-dependent rainfall events.
“The partitioning of mass between air-water interfacial adsorption, solid-phase adsorption, and aqueous phase varies over time, primarily driven by time-dependent rainfall events.”
Quote in the paperSubstantial claim - Findingreasoning
In Vinton soil, the remainder of PFOS mass is adsorbed at air-water interfaces.
“The remainder are adsorbed at the air-water interfaces.”
Quote in the paperSubstantial claim - Findingreasoning
The impact of surfactant-induced flow is slightly greater for Vinton soil than for Accusand.
“the impact is slightly greater for Vinton soil than that for Accusand.”
Quote in the paperNot a substantial claim - Findingreasoning
In Vinton soil simulations, PFOS moves much slower than in Accusand simulations.
“The PFOS moves much slower when compared to the Accusand simulations.”
Quote in the paperSubstantial claim - Findingreasoning
The retardation factors, though varying with PFOS concentrations, climates, and porous media, are always on the order of several hundreds to more than one thousand.
“The retardation factors—though varying with PFOS concentrations, climates, and different types of porous media—are always on the order of several hundreds to more than one thousand.”
Quote in the paperSubstantial claim - Findingnone given
The air-water interfacial adsorption coefficient Kbar_aw decreases by 5 to 10 times from low to high PFOS concentrations.
“A major difference between low and high PFOS concentrations is the value of K¯aw—it decreases by 5 to 10 times from low to high PFOS concentrations”
Quote in the paperSubstantial claim - Findingown data
After PFOS reaches groundwater, cumulative PFOS mass plateaus with slight variations driven by seasonal and interannual rainfall.
“After PFOS reaches groundwater, the cumulative mass plateaus with slight variations driven by seasonal and interannual variations of rainfall.”
Quote in the paperSubstantial claim - Findingown data
Vinton soil has saturated hydraulic conductivity about 18 times smaller than Accusand.
“its saturated hydraulic conductivity is much smaller (~ 18 times smaller; see Table 1).”
Quote in the paperSubstantial claim - Findingown data
Applying the model to simulate PFOS transport in a vadose zone beneath a synthetic FTA site shows that adsorption at air-water interfaces has a significant impact on transport and retention of PFAS.
“By applying the model to simulate PFAS (using PFOS as a representative PFAS) transport in a vadose zone beneath a synthetic FTA site, we show that adsorption at air-water interfaces has a significant impact on the transport and retention of PFAS.”
Quote in the paperSubstantial claim - Findingown data
PFOS-induced flow has a relatively minor impact on PFOS transport and migration in the vadose zone for both Accusand and Vinton soil, especially before PFOS reaches groundwater.
“PFOS-induced flow has a relatively minor impact on PFOS transport and migration in the vadose zone for both Accusand and Vinton soil, especially before PFOS reaches groundwater”
Quote in the paperSubstantial claim - Findingown data
Air-water interfacial adsorption accounts for more than 97% of the retardation.
“R¯ ranges from 233 to 1355, and are mainly contributed by the air-water interfacial adsorption; it accounts for more than 97% of the retardation.”
Quote in the paperSubstantial claim - Findingown data
In Vinton soil, the aqueous phase fraction of PFOS is still very small, one or two percent.
“The fraction of the aqueous phase PFOS is still very small—one or two percent.”
Quote in the paperNot a substantial claim - Findingown data
The mean retardation factor over 40 years ranges from 233 to 1355 across simulations that include air-water interfacial adsorption.
“R¯ ranges from 233 to 1355, and are mainly contributed by the air-water interfacial adsorption; it accounts for more than 97% of the retardation.”
Quote in the paperSubstantial claim - Findingown data
In Vinton soil, PFOS migration is substantially slower when air-water interfacial adsorption is included than when it is turned off.
“PFOS migration is still substantially slower for the scenarios that considered the air-water interfacial adsorption compared to those with air-water interfacial adsorption turned off.”
Quote in the paperSubstantial claim - Findingown data
In the semi-arid case with air-water interfacial adsorption included, more than 93% of PFOS mass remaining in the vadose zone is adsorbed at air-water interfaces.
“For the semi-arid case, more than 93% of the mass in the vadose zone is adsorbed at the air-water interfaces.”
Quote in the paperNot a substantial claim - Findingown data
Vinton soil has solid-phase adsorption much greater than Accusand, with Kf about 9 times larger.
“the solid-phase adsorption in Vinton is much greater (with a Kf that is ~ 9 times larger than Accusand).”
Quote in the paperSubstantial claim - Findingown data
In the plume over 40 years, average water content is as low as 0.037, corresponding to a water saturation of 0.126.
“The water content is down to 0.037 (corresponding to a water saturation of 0.126).”
Quote in the paperSubstantial claim - Findingown data
In Vinton soil simulations, after 40 years PFOS reaches groundwater only for the high PFOS concentration case under a humid climate.
“After 40 years, PFOS reaches groundwater for only the high PFOS concentration case under a humid climate.”
Quote in the paperSubstantial claim - Findingown data
In Vinton soil, the time scale to reach groundwater is only about 5 times greater when air-water interfacial adsorption is included compared to when it is not.
“the time scale to reach groundwater is only ~ 5 times greater when air-water interfacial adsorption is included.”
Quote in the paperNot a substantial claim - Findingown data
Surface evaporation accounts for approximately 44% of total rainfall in Vinton simulations.
“It is larger for Vinton, which accounts for approximately 44% of the total rainfall.”
Quote in the paperNot a substantial claim - Findingown data
The retardation factors vary among scenarios but are always on the order of several hundred to more than one thousand.
“The retardation factors—though vary among the different scenarios—are always on the order of several hundred to more than one thousand.”
Quote in the paperSubstantial claim - Findingown data
For low PFOS concentration scenarios, surface evaporation accounts for approximately 16% of total rainfall in Accusand simulations.
“For the low PFOS concentration scenarios, surface evaporation only accounts for approximately 16% of the total rainfall in the Accusand simulations.”
Quote in the paperNot a substantial claim - Findingreasoning
For the simulated conditions, it takes several decades or longer for PFOS to reach a groundwater table at about 5 m below land surface.
“For the conditions we simulate, it takes several decades or longer to reach a groundwater table at ~ 5m below the land surface.”
Quote in the paperSubstantial claim - Findingown data
The detailed simulations show that adsorption at air-water interfaces has a strong impact on migration and retention of PFOS in the vadose zone.
“The detailed simulations show that adsorption at air-water interfaces has a strong impact on the migration and retention of PFOS in the vadose zone.”
Quote in the paperSubstantial claim - Interpretationreasoning
If AFFF concentrates are 3% or 6%, dilution yields PFOS concentrations from 147 to 684 mg/L.
“Assuming these AFFF concentrates are either 3% or 6%, it leads to a PFOS concentration from 147 mg/L to 684 mg/L after dilution.”
Quote in the paperNot a substantial claim - Premisecitation
Solid-phase and air-water interfacial adsorption are the main processes of concern for PFOS and similar PFAS.
“Here we focus on two processes—solid-phase and air-water interfacial adsorption, that are the primary processes of concern for PFOS and similar PFAS.”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Brusseau, 2018
Not checked in the free run.
- Premisecitation
Earlier modeling studies included solid-phase adsorption but omitted fluid-fluid interfacial adsorption.
“The prior modeling studies incorporated solid-phase adsorption for the transport of surfactants, but not fluid-fluid interfacial adsorption.”
Quote in the paperSubstantial claim0 of 2 sources checked- cites Smith & Gillham, 1994
Not checked in the free run.
- cites Henry and Smith, 2003
Not checked in the free run.
- Premisereasoning
Before this study, the effect of transient variably saturated flow on PFAS transport and retention had not been examined.
“To date, all of these theoretical and experimental studies employed or assumed steady-state flow conditions. The impact of transient variably saturated flow on the transport and retention of PFAS has not been considered.”
Quote in the paperSubstantial claim - Premisecitation
PFOS is the dominant PFAS in AFFF solutions.
“PFOS is used as a representative PFAS because of its dominance in AFFF solutions (Houtz et al., 2013; Høisæter et al., 2019).”
Quote in the paperSubstantial claim0 of 2 sources checked- cites Houtz et al., 2013
Not checked in the free run.
- cites Høisæter et al., 2019
Not checked in the free run.
- Interpretationreasoning
Because solid-phase adsorption is nonlinear with exponent N < 1, the effective linear adsorption coefficient decreases at higher aqueous PFOS concentration.
“Second, the solid-phase adsorption is nonlinear with an exponent N < 1 and thus the effective linear adsorption coefficient will decrease for a higher aqueous concentration.”
Quote in the paperSubstantial claim- The authors state this as an assumption: Capillary pressure head scales with surface tension according to Leverett scaling.
- The authors state this as an assumption: The contact angle does not change when PFAS is dissolved.
- The authors state this as an assumption: All precipitation is treated as rainfall, with no distinction between rain and snow.
- The authors state this as an assumption: Evapotranspiration data are approximated as potential evapotranspiration to determine surface evaporation fluxes.
- The authors state this as an assumption: All applied AFFF solution infiltrates into the vadose zone.
- Premisecitation
PFAS transport and fate in the vadose zone with complex fluid-fluid interfaces are poorly understood.
“The transport and fate processes of PFAS in the vadose zone in the presence of complex fluid-fluid interfaces are not well understood (SERDP, 2017).”
Quote in the paperSubstantial claim0 of 1 sources checked- cites SERDP, 2017
Not checked in the free run.
- Interpretationreasoning
Variably saturated flow, PFAS transport, and PFAS adsorption are fully coupled.
“These interactive processes lead to a system where variably saturated flow and PFAS transport and adsorption are fully coupled.”
Quote in the paperSubstantial claim - Interpretationown data
These water saturation and air-water interfacial area distributions amplify the effect of air-water interfacial adsorption on PFOS retention in the vadose zone.
“These distributions of water saturation (or water content) and air-water interfacial area have strong implications on the transport simulations in the following two sections, namely they amplify the impact of air-water interfacial adsorption on the retention of PFOS in the vadose zone.”
Quote in the paperSubstantial claim- The authors state this as an assumption: Capillary pressure head scales with surface tension according to Leverett scaling.
- The authors state this as an assumption: The contact angle does not change when PFAS is dissolved.
- The authors state this as an assumption: All precipitation is treated as rainfall, with no distinction between rain and snow.
- The authors state this as an assumption: Evapotranspiration data are approximated as potential evapotranspiration to determine surface evaporation fluxes.
- The authors state this as an assumption: All applied AFFF solution infiltrates into the vadose zone.
- Premisecitation
The vadose zone can act as a source zone for PFAS.
“A number of field studies have demonstrated that the vadose zone can serve as a source zone of PFAS (Filipovic et al., 2015; Xiao et al., 2015; Weber et al., 2017; Anderson et al., 2019; Dauchy et al., 2019; Høisæter et al., 2019).”
Quote in the paperSubstantial claim0 of 3 sources checked- cites Filipovic et al., 2015
Not checked in the free run.
- cites Xiao et al., 2015
Not checked in the free run.
- cites Weber et al., 2017
Not checked in the free run.
- Premisereasoning
No PFAS transport model before this work included both transient variably saturated flow and solid-phase and fluid-fluid interfacial adsorption.
“To the best of our knowledge, no models for PFAS transport to date have accounted for both transient variably saturated flow and solid-phase and fluid-fluid interfacial adsorption processes.”
Quote in the paperSubstantial claim - Interpretationreasoning
The air-water interfacial adsorption coefficient rises monotonically as aqueous concentration falls and approaches a maximum asymptotically.
“Eq. (11) shows that Kaw monotonically increases as C decreases and asymptotically approaches a maximum value.”
Quote in the paperSubstantial claim - Premisecitation
PFOS concentrations in AFFF concentrates manufactured between 1984 and 2010 ranged from 4.9 to 11.4 g/L.
“Houtz et al. (2013) analyzed AFFF concentrates manufactured between 1984–2010 from various manufacturers; PFOS concentration was reported to range from 4.9–11.4 g/L.”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Houtz et al., 2013
Not checked in the free run.
- Premisereasoning
Dissolved PFAS can change surface tension and thereby influence flow.
“Conversely—as surfactants—PFAS present in solution can modify surface tension and hence impact flow.”
Quote in the paperSubstantial claim - Interpretationown data
At higher aqueous PFOS concentration, the air-water interfacial adsorption coefficient becomes smaller.
“First, the air-water interfacial adsorption coefficient becomes smaller (see Fig. 3).”
Quote in the paperSubstantial claim- The authors state this as an assumption: Capillary pressure head scales with surface tension according to Leverett scaling.
- The authors state this as an assumption: The contact angle does not change when PFAS is dissolved.
- The authors state this as an assumption: All precipitation is treated as rainfall, with no distinction between rain and snow.
- The authors state this as an assumption: Evapotranspiration data are approximated as potential evapotranspiration to determine surface evaporation fluxes.
- The authors state this as an assumption: All applied AFFF solution infiltrates into the vadose zone.
- Premisecitation
Solid-phase adsorption of PFAS can be represented by a nonlinear Freundlich isotherm.
“The solid-phase adsorption Cs can be modeled by the nonlinear Freundlich isotherm as suggested by prior experimental measurements (Higgins & Luthy, 2006; Wei et al., 2017; Brusseau, Khan, et al., 2019; Brusseau, 2020)”
Quote in the paperSubstantial claim0 of 3 sources checked- cites Higgins & Luthy, 2006
Not checked in the free run.
- cites Wei et al., 2017
Not checked in the free run.
- cites Brusseau, 2020
Not checked in the free run.
- Study design and conductcitation
The surfactant-induced flow model has been validated by application to sand-packed column and flow cell experiments.
“The model for surfactant-induced flow has been validated by application to sand-packed column and flow cell experiments (Smith & Gillham, 1999; Henry & Smith, 2002; Henry et al., 2002; Karagunduz et al., 2015).”
Quote in the paperSubstantial claim0 of 3 sources checked- cites Smith & Gillham, 1999
Not checked in the free run.
- cites Henry & Smith, 2002
Not checked in the free run.
- cites Henry et al., 2002
Not checked in the free run.
- Premisecitation
Good agreement of breakthrough curves between simulation and experiment was reported for those column studies.
“Good agreement of breakthrough curves between simulation and experiment were reported (Brusseau, Yan, et al., 2019; Brusseau, 2020).”
Quote in the paperSubstantial claim0 of 2 sources checked- cites Brusseau, Yan, et al., 2019
Not checked in the free run.
- cites Brusseau, 2020
Not checked in the free run.
- Study design and conductcitation
The computed water content is consistent with measured water content in large lysimeters packed with Vinton soil at the University of Arizona's Karsten Center for Turfgrass Research.
“the computed water content is consistent with measured water content in large lysimeters (4 m deep and 2.5 m in diameter) packed with the Vinton soil at The University of Arizona’s Karsten Center for Turfgrass Research (Young et al., 1996; Carlson et al., 2003).”
Quote in the paperNot a substantial claim0 of 2 sources checked- cites Young et al., 1996
Not checked in the free run.
- cites Carlson et al., 2003
Not checked in the free run.
- Premisecitation
The water content in those lysimeters was observed to reach as low as 0.035.
“The water content in the lysimeters was 528 observed to reach as low as 0.035.”
Quote in the paperSubstantial claim0 of 2 sources checked- cites Young et al., 1996
Not checked in the free run.
- cites Carlson et al., 2003
Not checked in the free run.
- Interpretationreasoning
The large contributions of air-water interfacial adsorption to retardation are caused by low water content and corresponding high air-water interfacial areas.
“The large contributions of air-water interfacial adsorption are caused by the low water content and the corresponding high air-water interfacial areas.”
Quote in the paperSubstantial claim - Study design and conductcitation
The individual components of the formulations have been validated by prior experiments.
“the individual components of the formulations have been validated by prior experiments.”
Quote in the paperSubstantial claim0 of 3 sources checked- cites Smith & Gillham, 1999
Not checked in the free run.
- cites Henry & Smith, 2002
Not checked in the free run.
- cites Henry et al., 2002
Not checked in the free run.
- Premisecitation
The solid-phase and air-water interfacial adsorption formulations have been used to model PFAS transport in soil or sand-packed columns under steady-state unsaturated flow.
“The solid-phase and air-water interfacial adsorption formulations have been used to model PFAS transport in soil/sand-packed columns under steady-state unsaturated flow.”
Quote in the paperSubstantial claim0 of 2 sources checked- cites Brusseau, Yan, et al., 2019
Not checked in the free run.
- cites Brusseau, 2020
Not checked in the free run.
- Interpretationreasoning
The total PFAS concentration in the vadose zone is likely orders of magnitude higher than in groundwater beneath source zones.
“This implies that the total PFAS concentration in the vadose zone is likely orders of magnitude higher than that in groundwater beneath source zones.”
Quote in the paperSubstantial claim- Rests on an assumption: Laboratory-measured parameters used in the simulations are representative of field-scale vadose zone conditions.
- Study design and conductreasoning
The model does not include partitioning to the air phase or organic immiscible liquids.
“We note that other partitioning processes may be relevant for some PFAS such as partitioning to the air phase and organic immiscible liquids (when present) (Brusseau, 2018). Here we focus on two processes—solid-phase and air-water interfacial adsorption”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Brusseau, 2018
Not checked in the free run.
- Interpretationreasoning
The results appear to imply that a fine-texture porous medium that retains more water in the vadose zone, such as silt or clay, could have a lower retardation factor than sand materials.
“our results appear to imply that a fine-texture porous medium that can retain more water in the vadose zone, for example silt or clay, could have a lower retardation factor than sand materials similar to the scenarios of the Vinton soil vs. Accusand in the present work.”
Quote in the paperSubstantial claim- Rests on an assumption: Laboratory-measured parameters used in the simulations are representative of field-scale vadose zone conditions.
- Interpretationown data
In Vinton soil, retardation factors decrease from low to high PFOS concentration scenarios due to reduction in air-water interfacial adsorption coefficients caused by increased aqueous PFOS concentration.
“The retardation factors decrease from low to high PFOS concentration scenarios, similar to Accusand, due to the reduction in the air-water interfacial adsorption coefficients caused by the increase in the aqueous PFOS concentration.”
Quote in the paperSubstantial claim - Interpretationreasoning
Because water content and air-water interfacial areas have a major impact on PFAS retention, other factors that influence them also impact retention.
“Because water content and air-water interfacial areas have a major impact on the retention of PFAS transport in the vadose zone, other factors that can influence water content and the amount of air-water interfacial area will thus also have an impact on the retention.”
Quote in the paperSubstantial claim - Interpretationreasoning
The presence of PFOS surfactant, by modifying capillary pressure head and the soil water characteristic curve, has a more noticeable but still not significant impact on PFOS transport.
“the presence of PFOS surfactant—by modifying the capillary pressure head and the soil water characteristic curve—has a more noticeable impact, though still not significant, on PFOS transport.”
Quote in the paperNot a substantial claim - Premisenone given
To the authors' knowledge, this is the first mathematical model for PFAS transport in the vadose zone that explicitly accounts for solid-phase and air-water interfacial adsorption.
“To the best of our knowledge, this is the first mathematical model for PFAS transport in the vadose zone that explicitly accounts for the solid-phase and air-water interfacial adsorption processes.”
Quote in the paperNot a substantial claim - Interpretationreasoning
The air-water interfacial adsorption fraction is slightly lower in the high PFOS concentration scenario because of a lower Kaw.
“The fraction of the air-water interfacial adsorption is slightly less in the high PFOS concentration scenario because of a lower Kaw.”
Quote in the paperNot a substantial claim - Interpretationreasoning
After PFOS reaches groundwater, the amount of PFOS entering the vadose zone is comparable to the amount discharged to groundwater.
“This implies that the amount of PFOS that goes into the vadose zone is comparable to the amount that is discharged to groundwater after this point.”
Quote in the paperSubstantial claim - Interpretationnone given
Soil PFAS concentrations are likely to be orders of magnitude higher than groundwater concentrations at source zones.
“soil PFAS concentrations are likely to be orders of magnitude higher than those in groundwater at source zones.”
Quote in the paperSubstantial claim- The authors state this as an assumption: Capillary pressure head scales with surface tension according to Leverett scaling.
- The authors state this as an assumption: The contact angle does not change when PFAS is dissolved.
- The authors state this as an assumption: All precipitation is treated as rainfall, with no distinction between rain and snow.
- The authors state this as an assumption: Evapotranspiration data are approximated as potential evapotranspiration to determine surface evaporation fluxes.
- The authors state this as an assumption: All applied AFFF solution infiltrates into the vadose zone.
- Interpretationown data
These mass conservation errors are small enough to have no impact on PFOS transport in the vadose zone.
“These errors are small enough with no impact on PFOS transport in the vadose zone”
Quote in the paperNot a substantial claim - Interpretationreasoning
Fine-texture materials could have lower retardation factors than sand because they retain more water.
“fine-texture materials could have lower retardation factors than sand due to higher retained water content”
Quote in the paperSubstantial claim- The authors state this as an assumption: Capillary pressure head scales with surface tension according to Leverett scaling.
- The authors state this as an assumption: The contact angle does not change when PFAS is dissolved.
- The authors state this as an assumption: All precipitation is treated as rainfall, with no distinction between rain and snow.
- The authors state this as an assumption: Evapotranspiration data are approximated as potential evapotranspiration to determine surface evaporation fluxes.
- The authors state this as an assumption: All applied AFFF solution infiltrates into the vadose zone.
- Interpretationreasoning
Surfactant-induced flow will likely have a greater impact on PFOS transport in fine-texture porous media where water saturation is higher.
“surfactant-induced flow will likely have a greater impact on PFOS transport in fine-texture porous media wherein the water saturation is higher”
Quote in the paperNot a substantial claim - Interpretationown data
Vadose zones with deeper groundwater tables than 4.82 m are expected to have similar or even lower water contents.
“We expect that vadose zones with deeper groundwater 529 tables (4.82m is set in our simulations) will have similar or even lower water contents.”
Quote in the paperSubstantial claim - Premisecitation
Recent field investigations have shown measured PFAS concentrations in soil up to six or seven orders of magnitude higher than in groundwater.
“Recent field investigations have shown that measured PFAS concentrations in the soil were up to six or seven orders of magnitude higher than the concentrations in the groundwater (Anderson et al., 2019; Dauchy et al., 2019).”
Quote in the paperNot a substantial claim0 of 2 sources checked- cites Anderson et al., 2019
Not checked in the free run.
- cites Dauchy et al., 2019
Not checked in the free run.
- Interpretationreasoning
The large retardation factors are mainly caused by low water content resulting from gravity drainage.
“We have demonstrated that such large retardation factors are mainly caused by the low water content resulting from gravity drainage.”
Quote in the paperSubstantial claim - Interpretationnone given
During large infiltration from rainfall, increased water saturation decreases air-water interfacial area.
“When large infiltration occurs due to rainfall events, the water saturation increases leading to a decrease in air-water interfacial area.”
Quote in the paperSubstantial claim - Interpretationown data
Air-water interfacial adsorption is amplified by low water content and hence large air-water interfacial areas in the vadose zone caused by gravity drainage.
“air-water interfacial adsorption is amplified by the low water content (and hence large air-water interfacial areas) in the vadose zone caused by gravity drainage.”
Quote in the paperSubstantial claim - Premisenone given
Field evidence supports decreasing soil to groundwater PFAS concentrations with increasing clay content.
“This is supported by field evidence of decreasing soil to groundwater PFAS concentrations with increasing clay content.”
Quote in the paperNot a substantial claim - Interpretationreasoning
Lower water content caused by greater gravity drainage and weaker capillary retention in sand led to the counterintuitive result that retardation factors for sand (233 to 1355) are larger than those for soil (146 to 792).
“The lower water content caused by greater gravity drainage and weaker capillary retention in the sand has also led to a counterintuitive result that the retardation factors for the sand (233 to 1355) are larger than those for the soil (146 to 792).”
Quote in the paperSubstantial claim - Interpretationreasoning
A direct implication is that fine-texture materials such as silt or clay could have lower PFAS retardation factors compared to sand due to higher retained water content in the vadose zone.
“A direct implication is that fine-texture materials such as silt or clay could have lower PFAS retardation factors compared to sand due to the higher retained water content in the vadose zone.”
Quote in the paperSubstantial claim- Rests on an assumption: Laboratory-measured parameters used in the simulations are representative of field-scale vadose zone conditions.
- Interpretationreasoning
PFAS concentrations in the vadose zone are likely orders of magnitude higher than those in groundwater in source zones.
“This implies that PFAS concentrations in the vadose zone are likely orders of magnitude higher than those in the groundwater in source zones”
Quote in the paperSubstantial claim- Rests on an assumption: Laboratory-measured parameters used in the simulations are representative of field-scale vadose zone conditions.
- Interpretationreasoning
The large retardation factors lead to long time scales for PFOS to reach groundwater.
“The large retardation factors lead to long time scales for PFOS to reach groundwater.”
Quote in the paperSubstantial claim - Interpretationreasoning
Not including groundwater table dynamics will likely overestimate retention of PFAS in the vadose zone.
“not including the groundwater table dynamics will likely overestimate the retention of PFAS in the vadose zone.”
Quote in the paperNot a substantial claim - Interpretationreasoning
For high PFOS concentration scenarios, surface evaporation is slightly lower due to more induced drainage caused by greater reduction in surface tension.
“For the high PFOS concentration scenarios, the surface evaporation is slightly lower due to more induced drainage caused by a greater reduction in surface tension.”
Quote in the paperNot a substantial claim
- May combine two claims. 34
- Classified as probably not a substantial claim. 9
- The quote only partly states this claim. 1
May combine two claims.
Findingown dataFor most of the 5-day Accusand simulation, water saturation stayed below 0.25 and air-water interfacial area stayed above 400 cm2/cm3.
“For the majority of the time during the 5-day simulation, the water saturation stays below 0.25 (corresponding to a water content of 0.074) and the air-water interfacial area stays above 400 cm2/cm3 (Fig. 4(c)) despite the fact that the conditions represent the largest rainfall event.”
Quote in the paperSubstantial claim- The authors state this as an assumption: Capillary pressure head scales with surface tension according to Leverett scaling.
- The authors state this as an assumption: The contact angle does not change when PFAS is dissolved.
- The authors state this as an assumption: All precipitation is treated as rainfall, with no distinction between rain and snow.
- The authors state this as an assumption: Evapotranspiration data are approximated as potential evapotranspiration to determine surface evaporation fluxes.
- The authors state this as an assumption: All applied AFFF solution infiltrates into the vadose zone.
May combine two claims.
Findingown dataFor most of the Vinton simulation, water saturation stayed below 0.35 and air-water interfacial area stayed above 700 cm2/cm3.
“For the majority of the time, the water saturation is below 0.35 (corresponding to a water content of 0.138) and the air-water interfacial area is above 700 cm2/cm3 (Fig. 4(d)).”
Quote in the paperSubstantial claim- The authors state this as an assumption: Capillary pressure head scales with surface tension according to Leverett scaling.
- The authors state this as an assumption: The contact angle does not change when PFAS is dissolved.
- The authors state this as an assumption: All precipitation is treated as rainfall, with no distinction between rain and snow.
- The authors state this as an assumption: Evapotranspiration data are approximated as potential evapotranspiration to determine surface evaporation fluxes.
- The authors state this as an assumption: All applied AFFF solution infiltrates into the vadose zone.
May combine two claims.
Findingnone givenMost PFOS was adsorbed at air-water interfaces, with only 1-2% in the aqueous phase.
“Also, most PFOS is adsorbed at air-water interfaces with only 1–2% in the aqueous phase.”
Quote in the paperSubstantial claim- The authors state this as an assumption: Capillary pressure head scales with surface tension according to Leverett scaling.
- The authors state this as an assumption: The contact angle does not change when PFAS is dissolved.
- The authors state this as an assumption: All precipitation is treated as rainfall, with no distinction between rain and snow.
- The authors state this as an assumption: Evapotranspiration data are approximated as potential evapotranspiration to determine surface evaporation fluxes.
- The authors state this as an assumption: All applied AFFF solution infiltrates into the vadose zone.
May combine two claims.
FindingreasoningHigher PFOS concentration and a more humid climate both speed up PFOS migration.
“A higher PFOS concentration and a more humid climate both accelerate the migration of PFOS.”
Quote in the paperSubstantial claim- The authors state this as an assumption: Capillary pressure head scales with surface tension according to Leverett scaling.
- The authors state this as an assumption: The contact angle does not change when PFAS is dissolved.
- The authors state this as an assumption: All precipitation is treated as rainfall, with no distinction between rain and snow.
- The authors state this as an assumption: Evapotranspiration data are approximated as potential evapotranspiration to determine surface evaporation fluxes.
- The authors state this as an assumption: All applied AFFF solution infiltrates into the vadose zone.
May combine two claims.
Findingown dataIn the semi-arid case with air-water interfacial adsorption included, about 1.5% of PFOS mass remaining in the vadose zone is in the aqueous phase and about 5.5% is in solid-phase adsorption.
“Approximately 1.5% is in the aqueous phase, and the remaining 5.5% is in the solid-phase adsorption.”
Quote in the paperSubstantial claimMay combine two claims.
Findingown dataSimulated water saturation above the groundwater table is generally small, and for Accusand and Vinton soil, saturation and air-water interfacial area are not sensitive to capillary pressure head at low saturations.
“the simulated water saturation above the groundwater table is generally small, and for Accusand and Vinton soil, saturation (and thus air-water interfacial area) is not sensitive to capillary pressure head (or water pressure head) at low saturations”
Quote in the paperSubstantial claimMay combine two claims.
Findingown dataThe majority of PFOS in the vadose zone is retained at air-water interfaces, with only one or two percent in the aqueous phase.
“The other critical finding from our simulations is that the majority of the PFOS in the vadose zone is retained at the air-water interfaces—only one or two percent is in the aqueous phase.”
Quote in the paperSubstantial claimMay combine two claims.
Findingown dataIn Vinton soil when air-water interfacial adsorption is turned off, about 60% of total released PFOS remains in the vadose zone in the semi-arid climate and about 20% in the humid climate, almost 10 times greater than Accusand.
“Approximately 60% and 20% of the total released PFOS remain in the vadose zone for the semi-arid and humid climates respectively, which are almost 10 times greater than those in the Accusand scenarios.”
Quote in the paperSubstantial claimMay combine two claims.
Findingown dataIn the humid-climate case with air-water interfacial adsorption included, about 97% of PFOS mass remaining in the vadose zone is adsorbed at air-water interfaces, about 1% is in the aqueous phase, and about 2% is in solid-phase adsorption.
“For the humid-climate case, approximately 97% is adsorbed at the air-water interfaces, 1% is in the aqueous phase, and 2% is in the solid-phase.”
Quote in the paperSubstantial claimMay combine two claims.
Findingown dataAt the maximum plume concentration, air-water interfacial adsorption accounts for about 99% of total PFOS in the low PFOS concentration scenario and about 95% in the high PFOS concentration scenario.
“at the maximum concentration of the plume, the air-water interfacial adsorption accounts for roughly 99% and 95% of the total PFOS in the low and high PFOS concentration scenarios, respectively.”
Quote in the paperSubstantial claimMay combine two claims.
Findingown dataWhen air-water interfacial adsorption is not considered, about 7% of total released PFOS remains in the vadose zone at 40 years in the semi-arid climate and about 2% in the humid climate.
“When air-water interfacial adsorption is not considered, the total mass left in the vadose zone is substantially lower—approximately 7% and 2% remain in the vadose zone for the semi-arid and humid climates, respectively.”
Quote in the paperSubstantial claimMay combine two claims.
Findingown dataWhen air-water interfacial adsorption is included, about 58% of total released PFOS remains in the vadose zone at 40 years in the semi-arid climate and about 45% in the humid climate.
“When air-water interfacial adsorption is considered, approximately 58% and 45% of the total released PFOS remains in the vadose zone at 40 years, for the semi-arid and humid climates, respectively.”
Quote in the paperSubstantial claimMay combine two claims.
Findingown dataIn Vinton soil, solid-phase adsorption accounts for about 30% of total mass in the vadose zone in the semi-arid climate and about 17% in the humid climate.
“The solid-phase adsorption accounts for about 30% and 17% of the total mass in the vadose zone for the semi-arid and humid climates, respectively (Fig. 10), which are much higher than the corresponding Accusand values.”
Quote in the paperSubstantial claimProbably not a substantial claim: may not pass S3 (load-bearing), S4 (based). May combine two claims.
Findingnone givenA humid climate leads to higher water content and lower air-water interfacial area than a semi-arid climate.
“a humid climate leads to a higher water content and a lower air-water interfacial area than a semi-arid climate.”
Quote in the paperNot a substantial claimProbably not a substantial claim: may not pass S3 (load-bearing), S4 (based). The quote only partly states this claim.
Findingnone givenThe humid climate leads to higher average water content than the semi-arid climate.
“The humid climate leads to higher average water content as expected.”
Quote in the paperNot a substantial claimMay combine two claims.
FindingreasoningIn Vinton soil simulations including air-water interfacial adsorption, average retardation factors are on the order of several hundreds and lower than Accusand retardation factors.
“The retardation factors are on the order of several hundreds—though still very large—they are lower compared to the Accusand retardation factors.”
Quote in the paperNot a substantial claimMay combine two claims.
Findingown dataThe results show that the majority of PFOS in the vadose zone is retained at air-water interfaces (70% or more) and solid surfaces (5% to 30%), leaving only one or two percent in the aqueous phase.
“the results show that the majority of the PFOS in the vadose zone is retained at the air-water interfaces (70% or more) and the solid surfaces (5% to 30%) leaving only one or two percent in the aqueous phase.”
Quote in the paperSubstantial claimMay combine two claims.
PremisecitationCostanza-Robinson and Henry (2017) held adsorption coefficients constant within each simulation, which underestimated nonlinear adsorption responses under transient flow.
“The adsorption coefficients—though varying among simulations—were kept constant during each simulation, and thus have underestimated the nonlinear responses of the adsorption processes under transient flow.”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Costanza-Robinson and Henry (2017)
Not checked in the free run.
May combine two claims.
InterpretationreasoningUnder a more humid climate, PFOS migrates faster because more water flows through the vadose zone with higher pore water velocities and because higher water content reduces air-water interfacial adsorption.
“Under a more humid climate, it is expected that PFOS will migrate faster because: 1) more water is flowing through the vadose zone to groundwater with higher pore water velocities leading to more “leaching”, and 2) the water content is likely higher leading to less air-water interfacial adsorption.”
Quote in the paperSubstantial claim- The authors state this as an assumption: Capillary pressure head scales with surface tension according to Leverett scaling.
- The authors state this as an assumption: The contact angle does not change when PFAS is dissolved.
- The authors state this as an assumption: All precipitation is treated as rainfall, with no distinction between rain and snow.
- The authors state this as an assumption: Evapotranspiration data are approximated as potential evapotranspiration to determine surface evaporation fluxes.
- The authors state this as an assumption: All applied AFFF solution infiltrates into the vadose zone.
May combine two claims.
PremisecitationAir-water interfacial area depends on capillary pressure head, water saturation, and drainage/imbibition history.
“The functional relationship between air-water interfacial area and water saturation will in general depend on the drainage and imbibition history (Hassanizadeh & Gray, 1993; Reeves & Celia, 1996; Schaefer et al., 2000).”
Quote in the paperNot a substantial claim0 of 3 sources checked- cites Hassanizadeh & Gray, 1993
Not checked in the free run.
- cites Reeves & Celia, 1996
Not checked in the free run.
- cites Schaefer et al., 2000
Not checked in the free run.
Probably not a substantial claim: may not pass S3 (load-bearing).
PremisecitationPFAS can be released from fire-training areas, fire response sites, industrial sites, landfills, and wastewater treatment plants.
“PFAS can be released from various types of sources including fire-training area (FTA) sites, fire response sites, industrial sites, landfills, and wastewater treatment plants (ITRC, 2018).”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites ITRC, 2018
Not checked in the free run.
May combine two claims.
PremisecitationA 1:100 dilution of an AFFF concentrate gives a PFOS concentration of 100 mg/L, and PFOS makes up 88.7% of total PFAS.
“Høisæter et al. (2019) reported that 1:100 dilution of an AFFF concentrate leads to a PFOS concentration of 100 mg/L; PFOS is the dominant PFAS accounting for 88.7% of the total PFAS.”
Quote in the paperSubstantial claim0 of 1 sources checked- cites Høisæter et al., 2019
Not checked in the free run.
May combine two claims.
InterpretationreasoningThe lower Vinton retardation factors are counterintuitive because Vinton has larger interfacial areas and stronger solid-phase adsorption than Accusand.
“This is rather counterintuitive because the Vinton soil has larger interfacial areas and also stronger solid-phase adsorption.”
Quote in the paperNot a substantial claimProbably not a substantial claim: may not pass S3 (load-bearing). May combine two claims.
PremisecitationAnderson et al. (2019) showed that the ratio between PFAS concentration in soil and groundwater decreases with increasing clay content, which they hypothesized is due to higher water saturation with higher clay content.
“Anderson et al. (2019) showed that the ratio between the PFAS concentration in the soil and groundwater decreases with increasing clay content, which they hypothesized is due to the higher water saturation in the presence of higher clay content.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Anderson et al., 2019
Not checked in the free run.
May combine two claims.
InterpretationreasoningPFOS adsorbed at air-water interfaces is released to the aqueous phase during large infiltration, and most of it is then adsorbed to solid surfaces.
“The PFOS adsorbed at the air-water interfaces is released to the aqueous phase and the majority of that is then adsorbed to the solid surface.”
Quote in the paperSubstantial claimMay combine two claims.
InterpretationreasoningAverage water content is slightly lower for higher PFOS concentration, possibly because of greater surfactant-induced drainage caused by a greater decrease in surface tension at higher aqueous PFOS concentration.
“It is slightly lower for higher PFOS concentration because of possibly greater surfactant-induced drainage caused by a greater decrease of surface tension at a higher aqueous PFOS concentration.”
Quote in the paperNot a substantial claimMay combine two claims.
PremisecitationAnderson et al. (2019) analyzed 324 Air Force sites across the continental US impacted by AFFF and observed higher soil PFAS concentrations in 87% of the data collected.
“the study by Anderson et al. (2019) was based on an analysis of 324 Air Force sites across the continental US impacted by AFFF, and higher soil PFAS concentrations were observed in the vast majority (87%) of the data collected.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Anderson et al., 2019
Not checked in the free run.
Probably not a substantial claim: may not pass S3 (load-bearing).
Study design and conductnone givenHysteresis effects are not included in the model.
“Hysteresis effects are not considered.”
Quote in the paperNot a substantial claimProbably not a substantial claim: may not pass S3 (load-bearing).
Interpretationnone givenA shallower groundwater table may increase overall water content if the porous medium has a thick capillary transition zone.
“A 530 shallower groundwater table may increase the overall water content if the porous medium 531 has a thick capillary transition zone.”
Quote in the paperNot a substantial claimMay combine two claims.
InterpretationreasoningThe reason Vinton has lower retardation factors is that although it has larger interfacial area than Accusand for the same water saturation, it retains much higher water saturation due to stronger capillary forces.
“The reason is that though the Vinton soil has a larger interfacial area than the Accusand for the same water saturation, it retains much higher water saturation than the Accusand does in the vadose zone due to stronger capillary forces.”
Quote in the paperSubstantial claimMay combine two claims.
Study design and conductnone givenThe model has not been compared directly to experimental data because such data does not yet exist.
“Though we have not compared our model directly to experimental data (such data does not yet exist)”
Quote in the paperSubstantial claimMay combine two claims.
InterpretationreasoningLow water content increases the retardation factor because it is in the denominator of the retardation expression and because it leads to a large interfacial area and thus more interfacial adsorption.
“A low water content increases the retardation factor because: 1) it is in the denominator of the expression for the retardation factor, and 2) it leads to a large interfacial area and thus more interfacial adsorption.”
Quote in the paperSubstantial claimMay combine two claims.
Study design and conductown dataThe numerical implementation was verified against HYDRUS-1D for water infiltration and solute transport, and the two codes agreed excellently.
“To verify our implementation of the Richards’ and advection-dispersion equations, we have compared our code with HYDRUS-1D for a simulation of water infiltration and solute transport (see the supporting information (SI)). Excellent agreement between the results from the two codes is observed (Fig. S1 in the SI).”
Quote in the paperNot a substantial claimMay combine two claims.
Study design and conductown dataFor all simulations, relative global mass conservation error at the end of 40 years is less than 0.1% for water and less than 0.005% for PFOS.
“For all simulations performed in the present work, the relative global mass conservation error (at the end of 40 years) is less than 0.1% for water and less than 0.005% for PFOS, respectively.”
Quote in the paperSubstantial claimMay combine two claims.
InterpretationreasoningAccusand has much lower water content than Vinton soil (more than 3 times lower), which is the main reason for Accusand's greater retardation factors.
“A closer inspection reveals that the Accusand has much lower water content than the Vinton soil (more than 3 times lower), which is the main reason responsible for the Accusand’s greater retardation factors.”
Quote in the paperSubstantial claimMay combine two claims.
Interpretationown dataThe solid-phase adsorption contribution to retardation in Vinton soil is about 4 times that in Accusand because Vinton has almost 9 times greater solid-phase adsorption capacity.
“When looking at the contributions to the retardation factors associated with the solid-phase adsorption alone (f¯spa), they are ~ 4 times that of the Accusand f¯spa values because Vinton has a solid-phase adsorption capacity that is almost 9 times greater.”
Quote in the paperNot a substantial claimProbably not a substantial claim: may not pass S4 (based).
Study design and conductnone givenThe simulations converged with respect to grid size and time step.
“Our simulations have converged for Δx and Δt.”
Quote in the paperNot a substantial claimProbably not a substantial claim: may not pass S3 (load-bearing), S4 (based).
Interpretationnone givenSeasonal and interannual variability of the groundwater table may influence water saturation and air-water interfaces in the vadose zone, especially when the vadose zone is shallow.
“the seasonal and interannual variability of the groundwater table may influence the water saturation in the vadose zone and hence the air-water interfaces, especially when the vadose zone is relatively shallow.”
Quote in the paperNot a substantial claimMay combine two claims.
InterpretationreasoningNot accounting for transpiration fluxes due to plant uptake will likely overestimate water content and underestimate the time-scale of retention in the vadose zone.
“not accounting for transpiration fluxes due to plant uptake will likely overestimate the water content and thus underestimate the time-scale of retention in the vadose zone.”
Quote in the paperNot a substantial claimProbably not a substantial claim: may not pass S3 (load-bearing), S4 (based).
Premisenone givenThis implication is consistent with recently reported data at hundreds of AFFF-impacted FTA sites in the US and elsewhere.
“which is consistent with recently reported data at hundreds of AFFF-impacted FTA sites in the US and elsewhere.”
Quote in the paperNot a substantial claimMay combine two claims.
PremisecitationDauchy et al. (2019) showed that PFAS were detected 15 m below ground despite clay layers, implying that retardation factors in clay may not be as great as usually thought for other contaminants.
“Dauchy et al. (2019) showed that PFAS were detected 15m below ground despite the presence of clay layers implying that the retardation factors in clay may not be as great as what is usually thought for other contaminants.”
Quote in the paperNot a substantial claim0 of 1 sources checked- cites Dauchy et al., 2019
Not checked in the free run.
The authors state this as an assumption.
Capillary pressure head scales with surface tension according to Leverett scaling.
“Here we assume that the capillary pressure head (−h) scales with surface tension σ following Leverett et al. (1941) and Smith and Gillham (1994)”
The authors state this as an assumption.
The contact angle does not change when PFAS is dissolved.
“For simplicity, the contact angle is assumed unchanged with dissolved PFAS.”
The authors state this as an assumption.
All precipitation is treated as rainfall, with no distinction between rain and snow.
“For simplicity, we treat all precipitation as rainfall and do not distinguish between rain and snow in our simulations.”
The authors state this as an assumption.
Evapotranspiration data are approximated as potential evapotranspiration to determine surface evaporation fluxes.
“In addition, we approximate the evapotranspiration data as potential evapotranspiration to determine the surface evaporation fluxes.”
The authors state this as an assumption.
All applied AFFF solution infiltrates into the vadose zone.
“Assuming all of the AFFF solutions infiltrate into the vadose zone, it gives a total infiltration of 0.0458cm per training session.”
The paper relies on this without support.
The time scale over which PFAS may remain in the vadose zone due to fluid-fluid interfacial adsorption and the potential for long-term release to groundwater are unknown.
“In particular, the time scale that PFAS may stay in the vadose zone due to fluid-fluid interfacial adsorption and the potential long-term release to groundwater are unknown.”
The paper relies on this without support.
PFAS behave as surfactants and tend to accumulate at air-water interfaces, potentially remaining in the vadose zone for long periods.
“when released to the environment they tend to accumulate at air-water interfaces and may stay in the vadose zone for long periods of time (Fig. 1(b,c)).”
The paper relies on this without support.
The implications are consistent with recent field observations at hundreds of AFFF-impacted sites.
“Both implications are consistent with recent field observations at hundreds of AFFF-impacted sites.”
The paper relies on this without support.
Laboratory-measured parameters used in the simulations are representative of field-scale vadose zone conditions.
“though our simulations used laboratory measured parameters”
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 AWI sorption capability of the extended LEACHM code has been successfully benchmarked against Guo et al. (2020) and Zeng et al. (2021).
“The AWI sorption capability of the extended LEACHM code has been successfully benchmarked against Guo et al. (2020) and Zeng et al. (2021”
From Model-based identification of vadose zone controls on PFAS mobility under semi-arid climate conditions (2022) · cites this paper as Guo et al. (2020)
Prior field studies and theoretical models suggest that retention of PFAS in the vadose zone due to partitioning at the air-water interface and biotransformation of precursors may sustain long-term downstream contamination of the more mobile perfluoroalkyl sulfonates and perfluoroalkyl carboxylates.
“These studies suggest that retention of PFAS in the vadose zone due to partitioning at the air–water interface and biotransformation of precursors may sustain long-term downstream contamination of the more mobile perfluoroalkyl sulfonates (PFSA) and PFCA.”
From Centurial Persistence of Forever Chemicals at Military Fire Training Sites (2023) · cites this paper as [14]
These results agree with mathematical and experimental evidence showing much larger solids retention of PFAS under unsaturated compared to saturated conditions.
“These results agree with mathematical and experimental evidence showing much larger solids retention of PFAS under unsaturated compared to saturated conditions.14,33”
From Centurial Persistence of Forever Chemicals at Military Fire Training Sites (2023) · cites this paper as [14]
Results from theoretical models and laboratory experiments in prior work suggest that PFAS retention at the air-water interface in the vadose zone is likely to be a rate-limiting step mediating attenuation at AFFF-contaminated sites.
“Results from theoretical models and laboratory experiments in prior work suggest that PFAS retention at the air–water interface in the vadose zone is likely to be a rate-limiting step mediating attenuation at AFFF-contaminated sites.14,49”
From Centurial Persistence of Forever Chemicals at Military Fire Training Sites (2023) · cites this paper as [14]
The simulation code represented transient flow under variably saturated conditions, surfactant effects on flow, and both nonlinear and rate-limited sorption to solids and air-water interfaces.
“The mathematical model that was employed to conduct the numerical simulations accounts for transient variably saturated flow, surfactant-induced flow, nonlinear and rate-limited solid-phase sorption, and nonlinear and rate-limited air-water interfacial adsorption (Guo et al., 2020).”
From PFAS concentrations in soil versus soil porewater: Mass distributions and the impact of adsorption at air-water interfaces (2022) · cites this paper as Guo et al., 2020
Guo et al. (2020) conducted long-term numerical simulations for a model fire-training source area for representative field conditions.
“Guo et al. (2020) conducted long-term numerical simulations for a model fire-training source area for representative field conditions.”
From PFAS concentrations in soil versus soil porewater: Mass distributions and the impact of adsorption at air-water interfaces (2022) · cites this paper as Guo et al. (2020)
These dynamic changes of porewater concentration due to transient water infiltration are consistent with those reported in prior work.
“These dynamic changes of porewater concentration due to transient water infiltration are consistent with those reported in our prior work (Guo et al., 2020; Zeng et al., 2021).”
From PFAS concentrations in soil versus soil porewater: Mass distributions and the impact of adsorption at air-water interfaces (2022) · cites this paper as Guo et al., 2020
Porewater concentrations ranging up to tens of mg/L were obtained for PFOS, for a simulated release concentration of 1,000 mg/L.
“Porewater concentrations ranging up to 10’s of mg/L were obtained for PFOS, for a simulated release concentration of 1,000 mg/L.”
From PFAS concentrations in soil versus soil porewater: Mass distributions and the impact of adsorption at air-water interfaces (2022) · cites this paper as Guo et al. (2020)
PFAS in the unsaturated zone can be sources to underlying groundwater systems for decades.
“PFAS in the unsaturated zone can be sources to underlying groundwater systems for decades,7,14”
From Perfluoroalkyl and Polyfluoroalkyl Substances in Groundwater Used as a Source of Drinking Water in the Eastern United States (2022) · cites this paper as [14]
Initial field and modeling studies reflect these anticipated porewater concentrations.
“The results of initial field and mathematical-modeling studies reflect these anticipated concentrations (Guo et al., 2020; Quinnan et al., 2021; Brusseau and Guo, 2022).”
From Global distributions, source-type dependencies, and concentration ranges of per- and polyfluoroalkyl substances in groundwater (2022) · cites this paper as Guo et al., 2020
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.
First-model claim conflicts with the paper's account of earlier work
MinorThe abstract calls this the first model to include surfactant-induced flow and both adsorption processes. The introduction describes an earlier model that included those same processes, although it treated the adsorption coefficients as constant during each simulation.
“We present the first mathematical model that accounts for surfactant-induced flow and solid-phase and air-water interfacial adsorption.”
“More recently, Costanza-Robinson and Henry (2017) modified HYDRUS-1D (Simunek et al., 2008) to simulate surfactant-induced flow to evaluate the aqueous air-water Interfacial Partitioning Tracer Test (IPTT) method. Both solid-phase and air-water interfacial adsorption were included.”
Cites
A Closed‐form Equation for Predicting the Hydraulic Conductivity of Unsaturated Soils
van Genuchten, M. T. (1980) · Soil Science Society of America Journal · doi:10.2136/sssaj1980.03615995004400050002x · Cited by 27,578 · see citing works
Physical chemistry of surfaces
Adamson, A. W., & Gast, A. P. (1998) · Choice Reviews Online · doi:10.5860/choice.35-4499 · Cited by 11,684 · see citing works
A new model for predicting the hydraulic conductivity of unsaturated porous media
Mualem, Y. (1976) · Water Resources Research · doi:10.1029/wr012i003p00513 · Cited by 8,300 · see citing works
CAPILLARY CONDUCTION OF LIQUIDS THROUGH POROUS MEDIUMS
Richards, L. A. (1931) · Physics · doi:10.1063/1.1745010 · Cited by 6,531 · see citing works
Buck, R. C., Franklin, J., Berger, U., Conder, J. M., Cousins, I. T., de Voogt, P., Jensen, A. A., Kannan, K., Mabury, S. A., & van Leeuwen, S. P. (2011) · Integrated Environmental Assessment and Management · doi:10.1002/ieam.258 · Cited by 4,641 · see citing works
Millington, R. J., & Quirk, J. P. (1961) · Transactions of the Faraday Society · doi:10.1039/tf9615701200 · Cited by 2,273 · see citing works
Capillary Behavior in Porous Solids
Leverett, M. C. (1941) · Transactions of the AIME · doi:10.2118/941152-g · Cited by 2,258 · see citing works
A Never-Ending Story of Per- and Polyfluoroalkyl Substances (PFASs)?
Wang, Z., DeWitt, J. C., Higgins, C. P., & Cousins, I. T. (2017) · Environmental Science & Technology · doi:10.1021/acs.est.6b04806 · Cited by 1,921 · see citing works
A general mass‐conservative numerical solution for the unsaturated flow equation
Celia, M. A., Bouloutas, E. T., & Zarba, R. L. (1990) · Water Resources Research · doi:10.1029/wr026i007p01483 · Cited by 1,816 · see citing works
Sorption of Perfluorinated Surfactants on Sediments
Higgins, C. P., & Luthy, R. G. (2006) · Environmental Science & Technology · doi:10.1021/es061000n · Cited by 1,563 · cited 1× · see citing works
“The solid-phase adsorption C s can be modeled by the nonlinear Freundlich isotherm as suggested by prior experimental measurements (Brusseau et al., 2019; Brusseau, 2020; Higgins & Luthy, 2006; Wei et al., 2017) 10.1029/2019WR026667 where K 𝑓 and N are fitting parameters to experimental data.”
MethodInfluentialOrganofluorine chemistry : principles and commercial applications
Banks, R. E., SMART, B. E., & Tatlow, J. C. (1994) · Springer eBooks · Cited by 1,105 · see citing works
Persistence of Perfluoroalkyl Acid Precursors in AFFF-Impacted Groundwater and Soil
Houtz, E. F., Higgins, C. P., Field, J. A., & Sedlak, D. L. (2013) · Environmental Science & Technology · doi:10.1021/es4018877 · Cited by 849 · see citing works
Chang, C., & Franses, E. I. (1995) · Colloids and Surfaces A Physicochemical and Engineering Aspects · doi:10.1016/0927-7757(94)03061-4 · Cited by 773 · see citing works
Thermodynamic basis of capillary pressure in porous media
Hassanizadeh, S. M., & Gray, W. G. (1993) · Water Resources Research · doi:10.1029/93wr01495 · Cited by 748 · see citing works
Perfluorinated Surfactants and the Environmental Implications of Their Use in Fire-Fighting Foams
Moody, C. A., & Field, J. A. (2000) · Environmental Science & Technology · doi:10.1021/es991359u · Cited by 707 · see citing works
An Introduction to Reservoir Simulation Using MATLAB/GNU Octave
Lie, K. (2019) · Cambridge University Press eBooks · doi:10.1017/9781108591416 · Cited by 487 · see citing works
A compositional simulator for modeling surfactant enhanced aquifer remediation, 1 formulation
Delshad, M., Pope, G. A., & Sepehrnoori, K. (1996) · Journal of Contaminant Hydrology · doi:10.1016/0169-7722(95)00106-9 · Cited by 412 · see citing works
Reeves, P. C., & Celia, M. A. (1996) · Water Resources Research · doi:10.1029/96wr01105 · Cited by 396 · see citing works
Convective‐dispersive solute transport with a combined equilibrium and kinetic adsorption model
Cameron, D. R., & Klute, A. (1977) · Water Resources Research · doi:10.1029/wr013i001p00183 · Cited by 372 · see citing works
Xiao, F., Simcik, M. F., Halbach, T. R., & Gulliver, J. S. (2015) · Water Research · doi:10.1016/j.watres.2014.09.052 · Cited by 359 · see citing works
Pennell, K. D., Abriola, L. M., & Weber, W. J. J. (1993) · Environmental Science & Technology · doi:10.1021/es00048a005 · Cited by 359 · see citing works
Brusseau, M. L. (2018) · Science of The Total Environment · doi:10.1016/j.scitotenv.2017.09.065 · Cited by 306 · see citing works
Self-citationFilipovic, M., Woldegiorgis, A., Norström, K., Bibi, M., Lindberg, M., & Österås, A.-H. (2015) · Chemosphere · doi:10.1016/j.chemosphere.2014.09.005 · Cited by 284 · see citing works
Adsorption of PFOA at the air-water interface during transport in unsaturated porous media
Lyu, Y., Brusseau, M. L., Chen, W., Yan, N., Fu, X., & Lin, X. (2018) · Environmental Science & Technology · doi:10.1021/acs.est.8b02348 · Cited by 259 · see citing works
Self-citationAccumulation of PFOA and PFOS at the Air–Water Interface
Costanza, J., Arshadi, M., Abriola, L. M., & Pennell, K. D. (2019) · Environmental Science & Technology Letters · doi:10.1021/acs.estlett.9b00355 · Cited by 255 · see citing works
Xu, M., & Eckstein, Y. (1995) · Ground Water · doi:10.1111/j.1745-6584.1995.tb00035.x · Cited by 252 · see citing works
Høisæter, Å., Pfaff, A., & Breedveld, G. D. (2019) · Journal of Contaminant Hydrology · doi:10.1016/j.jconhyd.2019.02.010 · Cited by 243 · see citing works
Comprehensive retention model for PFAS transport in subsurface systems
Brusseau, M. L., Yan, N., Van Glubt, S., Wang, Y., Chen, W., Lyu, Y., Dungan, B., Carroll, K. C., & Holguin, F. O. (2019) · Water Research · doi:10.1016/j.watres.2018.10.035 · Cited by 232 · see citing works
Self-citationWeber, A. K., Barber, L. B., LeBlanc, D. R., Sunderland, E. M., & Vecitis, C. D. (2017) · Environmental Science & Technology · doi:10.1021/acs.est.6b05573 · Cited by 227 · see citing works
A Chemical Flooding Compositional Simulator
Pope, G. A., & Nelson, R. C. (1978) · Society of Petroleum Engineers Journal · doi:10.2118/6725-pa · Cited by 226 · see citing works
Shin, H.-M., Vieira, V. M., Ryan, P. B., Detwiler, R., Sanders, B., Steenland, K., & Bartell, S. M. (2011) · Environmental Science & Technology · doi:10.1021/es102769t · Cited by 198 · see citing works
Dauchy, X., Boiteux, V., Colin, A., Hémard, J., Bach, C., Rosin, C., & Munoz, J.-F. (2019) · Chemosphere · doi:10.1016/j.chemosphere.2018.10.003 · Cited by 192 · see citing works
Scott, R. L. (2009) · Agricultural and Forest Meteorology · doi:10.1016/j.agrformet.2009.11.002 · Cited by 183 · see citing works
The influence of surfactant and solution composition on PFAS adsorption at fluid-fluid interfaces
Brusseau, M. L., & Van Glubt, S. (2019) · Water Research · doi:10.1016/j.watres.2019.05.095 · Cited by 180 · see citing works
Self-citationKim, H., Rao, P. S. C., & Annable, M. D. (1997) · Water Resources Research · doi:10.1029/97wr02227 · Cited by 177 · see citing works
The use of surfactants for in situ extraction of organic pollutants from a contaminated aquifer
Fountain, J. C., Klimek, A., Beikirch, M. G., & Middleton, T. M. (1991) · Journal of Hazardous Materials · doi:10.1016/0304-3894(91)87081-c · Cited by 172 · see citing works
Hunter Anderson, R., Adamson, D. T., & Stroo, H. F. (2019) · Journal of Contaminant Hydrology · doi:10.1016/j.jconhyd.2018.11.011 · Cited by 169 · see citing works
Wei, C., Song, X., Wang, Q., & Hu, Z. (2017) · Ecotoxicology and Environmental Safety · doi:10.1016/j.ecoenv.2017.03.040 · Cited by 158 · see citing works
Brusseau, M. L. (2019) · Water Research · doi:10.1016/j.watres.2018.12.057 · Cited by 157 · see citing works
Self-citationCulver, T. B., Hallisey, S. P., Sahoo, D., Deitsch, J. J., & Smith, J. A. (1997) · Environmental Science & Technology · doi:10.1021/es9600946 · Cited by 151 · see citing works
Dynamic interfacial tension of surfactant solutions
Miller, R., Aksenenko, E. V., & Fainerman, V. B. (2016) · Advances in Colloid and Interface Science · doi:10.1016/j.cis.2016.12.007 · Cited by 150 · see citing works
Surfactant-enhanced solubilization of residual dodecane in soil columns. 2. Mathematical modeling
Abriola, L. M., Dekker, T. J., & Pennell, K. D. (1993) · Environmental Science & Technology · doi:10.1021/es00048a006 · Cited by 139 · see citing works
Simulating PFAS transport influenced by rate-limited multi-process retention
Brusseau, M. L. (2019) · Water Research · doi:10.1016/j.watres.2019.115179 · Cited by 128 · see citing works
Self-citationNonideal Transport and Extended Elution Tailing of PFOS in Soil
Brusseau, M. L., Khan, N., Wang, Y., Yan, N., Glubt, S. V., & Carroll, K. C. (2019) · Environmental Science & Technology · doi:10.1021/acs.est.9b02343 · Cited by 128 · see citing works
Self-citationBrusseau, M. L., Peng, S., Schnaar, G., & Murao, A. (2007) · Environmental Science & Technology · doi:10.1021/es061474m · Cited by 125 · see citing works
Self-citationSchaefer, C. E., DiCarlo, D. A., & Blunt, M. J. (2000) · Water Resources Research · doi:10.1029/2000wr900007 · Cited by 109 · see citing works
Silva, J. A. K., Martin, W. A., Johnson, J. L., & McCray, J. E. (2019) · Journal of Contaminant Hydrology · doi:10.1016/j.jconhyd.2019.03.004 · Cited by 108 · see citing works
Brusseau, M. L. (2019) · Environmental Pollution · doi:10.1016/j.envpol.2019.113102 · Cited by 93 · see citing works
Self-citationSolute Transport in Porous Media with Sorption-Site Heterogeneity
Chen, W., & Wagenet, R. J. (1995) · Environmental Science & Technology · doi:10.1021/es00011a005 · Cited by 92 · see citing works
Description of Atrazine Transport in Soil with Heterogeneous Nonequilibrium Sorption
Chen, W., & Wagenet, R. J. (1997) · Soil Science Society of America Journal · doi:10.2136/sssaj1997.03615995006100020003x · Cited by 83 · see citing works
LARGE WEIGHING LYSIMETERS FOR WATER USE AND DEEP PERCOLATION STUDIES
Young, M. H., Wierenga, P. J., & Mancino, C. F. (1996) · Soil Science · doi:10.1097/00010694-199608000-00004 · Cited by 82 · see citing works
Pinder, G. F., & Celia, M. A. (2006) · Wiley eBooks · doi:10.1002/0470044209 · Cited by 79 · see citing works
Smith, J. E., & Gillham, R. W. (1999) · Water Resources Research · doi:10.1029/1998wr900106 · Cited by 77 · see citing works
The effect of nonlinear sorption on transformation of contaminants during transport in porous media
Brusseau, M. L. (1995) · Journal of Contaminant Hydrology · doi:10.1016/0169-7722(94)00041-f · Cited by 65 · see citing works
Self-citationAdsorption of Ionic Surfactants at an Expanding Air−Water Interface
Valkovska, D. S., Shearman, G. C., Bain, C. D., Darton, R. C., & Eastoe, J. (2004) · Langmuir · doi:10.1021/la035739b · Cited by 64 · see citing works
Smith, J. E., & Gillham, R. W. (1994) · Water Resources Research · doi:10.1029/93wr02745 · Cited by 62 · see citing works
Henry, E. J., & Smith, J. E. (2002) · Journal of Contaminant Hydrology · doi:10.1016/s0169-7722(01)00206-6 · Cited by 59 · see citing works
Measurement of Aqueous Diffusivities for Perfluoroalkyl Acids
Schaefer, C. E., Drennan, D. M., Tran, D. N., García, R. A., Christie, E. C., Higgins, C. P., & Field, J. A. (2019) · Journal of Environmental Engineering · doi:10.1061/(asce)ee.1943-7870.0001585 · Cited by 56 · see citing works
Surfactant-Induced Flow Phenomena in the Vadose Zone: A Review of Data and Numerical Modeling
Henry, E. J., & Smith, J. E. (2003) · Vadose Zone Journal · doi:10.2113/2.2.154 · Cited by 45 · see citing works
Li, Z., & Brusseau, M. L. (2000) · Water Resources Research · doi:10.1029/2000wr900089 · Cited by 44 · see citing works
Self-citationJi, W., & Brusseau, M. L. (1998) · Water Resources Research · doi:10.1029/98wr01040 · Cited by 42 · see citing works
Self-citationNovel methods for measuring air–water interfacial area in unsaturated porous media
Brusseau, M. L., Ouni, A. E., Araujo, J. B., & Zhong, H. (2015) · Chemosphere · doi:10.1016/j.chemosphere.2015.01.029 · Cited by 41 · see citing works
Self-citationTwo‐dimensional modeling of flow and transport in the vadose zone with surfactant‐induced flow
Henry, E. J., Smith, J. E., & Warrick, A. W. (2002) · Water Resources Research · doi:10.1029/2001wr000674 · Cited by 37 · see citing works
Influence of surfactants on unsaturated water flow and solute transport
Karagündüz, A., Young, M. H., & Pennell, K. D. (2015) · Water Resources Research · doi:10.1002/2014wr015845 · Cited by 35 · see citing works
Surfactant‐Induced Flow Phenomena in the Vadose Zone: A Review of Data and Numerical Modeling
Henry, E. J., & Smith, J. E. (2003) · Vadose Zone Journal · doi:10.2136/vzj2003.1540 · Cited by 32 · see citing works
AmeriFlux US-Wkg Walnut Gulch Kendall Grasslands
Scott, R. L. (2016) · Figshare · doi:10.17190/amf/1246112 · Cited by 31 · see citing works
Adsorption Kinetics in Binary Surfactant Mixtures Studied with External Reflection FTIR Spectroscopy
Day, J. P. R., Campbell, R. A., Russell, O. P., & Bain, C. D. (2007) · The Journal of Physical Chemistry C · doi:10.1021/jp067051o · Cited by 29 · see citing works
Measuring air–water interfacial area for soils using the mass balance surfactant-tracer method
Araujo, J. B., Mainhagu, J., & Brusseau, M. L. (2015) · Chemosphere · doi:10.1016/j.chemosphere.2015.04.035 · Cited by 28 · see citing works
Self-citationShin, H., Ryan, P. B., Vieira, V. M., & Bartell, S. M. (2012) · Atmospheric Environment · doi:10.1016/j.atmosenv.2012.01.049 · Cited by 23 · see citing works
Adsorption kinetics of ammonium perfluorononanoate at the air–water interface
Sekine, M., Campbell, R. A., Valkovska, D. S., Day, J. P. R., Curwen, T. D., Martin, L. J., Holt, S. A., Eastoe, J., & Bain, C. D. (2004) · Physical Chemistry Chemical Physics · doi:10.1039/b411044g · Cited by 23 · see citing works
Carlson, T. D., Costanza‐Robinson, M. S., Keller, J., Wierenga, P. J., & Brusseau, M. L. (2003) · Soil Science Society of America Journal · doi:10.2136/sssaj2003.4830 · Cited by 15 · see citing works
Self-citationCostanza-Robinson, M. S., & Henry, E. J. (2017) · Chemosphere · doi:10.1016/j.chemosphere.2016.12.072 · Cited by 13 · see citing works
Dynamics of Surfactants and Polymers at Liquid Interfaces
Loppinet, B., & Monteux, C. (2015) · Lecture notes in physics · doi:10.1007/978-3-319-24502-7_5 · Cited by 9 · see citing works
SERDP and ESTCP Workshop on Research and Demonstration Needs for Management of AFFF-Impacted Sites
Stroo, H. F., Leeson, A., Deeb, R. A., Higgins, C. P., Mills, M. A., Patton, C., Porter, R., Sedlak, D. L., Sepúlveda, M., Thompson, T., et al. (2017) · doi:10.13140/rg.2.2.35923.89124 · Cited by 8 · see citing works
Measuring and predicting steady state infiltration rates for Arizona irrigated soils
Bagour, M. H. (2001) · UA Campus Repository (The University of Arizona) · Cited by 2 · see citing works
Flagged first, then by citations
Research works printed but not linked: 2
- 10.1021/es981355 · DOI
- Simunek J., 2008, The HYDRUS‐1D software package for simulating the one‐dimensional movement of water, Heat, and Multiple Solutes in Variably‐Saturated Media, Version, 4, 281
Cited by
Sorted by citations
PFAS concentrations in soils: Background levels versus contaminated sites
Brusseau, M. L., Anderson, R. H., & Guo, B. (2020) · Science of The Total Environment · doi:10.1016/j.scitotenv.2020.140017 · Cited by 817 · see citing works
Self-citationWang, D., Xiao, F., Xiao, F., Chen, J., Park, C. M., Park, C. M., Flury, M., & Flury, M. (2022) · Reviews of Geophysics · doi:10.1029/2021rg000765 · Cited by 274 · see citing works
Sima, M. W., & Jaffé, P. R. (2021) · Science of The Total Environment · doi:10.1016/j.scitotenv.2020.143793 · Cited by 242 · see citing works
McMahon, P. B., Tokranov, A. K., Bexfield, L. M., Lindsey, B. D., Johnson, T. D., Lombard, M. A., & Watson, E. (2022) · Environmental Science & Technology · doi:10.1021/acs.est.1c04795 · Cited by 183 · see citing works
Fate and transport of per- and polyfluoroalkyl substances (PFASs) in the vadose zone
Sharifan, H., Bagheri, M., Wang, D., Burken, J. G., Higgins, C. P., Liang, Y., Liu, J., Schaefer, C. E., & Blotevogel, J. (2021) · Science of The Total Environment · doi:10.1016/j.scitotenv.2021.145427 · Cited by 180 · see citing works
Updated review on emerging technologies for PFAS contaminated water treatment
Yadav, S., Ibrar, I., Al-Juboori, R. A., Singh, L., Ganbat, N., Kazwini, T., Karbassiyazdi, E., Samal, A. K., Subbiah, S., & Altaee, A. (2022) · Process Safety and Environmental Protection · doi:10.1016/j.cherd.2022.04.009 · Cited by 171 · see citing works
Johnson, G. R., Brusseau, M. L., Carroll, K. C., Tick, G. R., & Duncan, C. M. (2022) · Science of The Total Environment · doi:10.1016/j.scitotenv.2022.156602 · Cited by 173 · see citing works
Self-citationGuelfo, J. L., Korzeniowski, S. H., Mills, M. A., Anderson, J. K., Anderson, R. H., Arblaster, J. A., Conder, J., Cousins, I. T., Dasu, K., Henry, B. J., et al. (2021) · Environmental Toxicology and Chemistry · doi:10.1002/etc.5182 · Cited by 151 · see citing works
Centurial Persistence of Forever Chemicals at Military Fire Training Sites
Ruyle, B. J., Thackray, C. P., Butt, C. M., LeBlanc, D. R., Tokranov, A. K., Vecitis, C. D., & Sunderland, E. M. (2023) · Environmental Science & Technology · doi:10.1021/acs.est.3c00675 · Cited by 142 · see citing works
Mass-Based, Field-Scale Demonstration of PFAS Retention within AFFF-Associated Source Areas
Adamson, D. T., Nickerson, A., Kulkarni, P. R., Higgins, C. P., Popovic, J., Field, J., Rodowa, A., Newell, C., DeBlanc, P., & Kornuc, J. J. (2020) · Environmental Science & Technology · doi:10.1021/acs.est.0c04472 · Cited by 141 · see citing works
Groundwater-Surface water interactions research: Past trends and future directions
Irvine, D. J., Singha, K., Kurylyk, B. L., Briggs, M. A., Sebastian, Y., Tait, D. R., & Helton, A. M. (2024) · Journal of Hydrology · doi:10.1016/j.jhydrol.2024.132061 · Cited by 129 · see citing works
Treatment technologies for removal of per- and polyfluoroalkyl substances (PFAS) in biosolids
Garg, A., Shetti, N. P., Basu, S., Nadagouda, M. N., & Aminabhavi, T. M. (2022) · Chemical Engineering Journal · doi:10.1016/j.cej.2022.139964 · Cited by 128 · see citing works
Incidence of Pfas in soil following long-term application of class B biosolids
Pepper, I. L., Brusseau, M. L., Prevatt, F. J., & Escobar, B. A. (2021) · Science of The Total Environment · doi:10.1016/j.scitotenv.2021.148449 · Cited by 125 · see citing works
A modified HYDRUS model for simulating PFAS transport in the vadose zone
Silva, J. A. K., Šimůnek, J., & McCray, J. E. (2020) · Water · doi:10.3390/w12102758 · Cited by 111 · see citing works
Wallis, I., Hutson, J., Davis, G., Kookana, R., Rayner, J., & Prommer, H. (2022) · Water Research · doi:10.1016/j.watres.2022.119096 · Cited by 103 · see citing works
Brusseau, M. L., & Guo, B. (2022) · Chemosphere · doi:10.1016/j.chemosphere.2022.134938 · Cited by 97 · see citing works
Self-citationBrusseau, M. L., & Van Glubt, S. (2021) · Chemosphere · doi:10.1016/j.chemosphere.2021.130829 · Cited by 86 · see citing works
Self-citationKabiri, S., Tucker, W. A., Navarro, D. A., Bräunig, J., Thompson, K., Knight, E. R., Nguyen, T. M. H., Grimison, C. C., Barnes, C. M., Higgins, C. P., et al. (2021) · Environmental Science & Technology · doi:10.1021/acs.est.1c06604 · Cited by 85 · see citing works
Characterization of relevant site-specific PFAS fate and transport processes at multiple AFFF sites
Adamson, D. T., Kulkarni, P. R., Nickerson, A., Higgins, C. P., Field, J., Schwichtenberg, T., Newell, C., & Kornuc, J. J. (2022) · Environmental Advances · doi:10.1016/j.envadv.2022.100167 · Cited by 83 · see citing works
Zeng, J., & Guo, B. (2021) · Advances in Water Resources · doi:10.1016/j.advwatres.2021.104015 · Cited by 77 · see citing works
Self-citationSörengård, M., Bergström, S., McCleaf, P., Wiberg, K., & Ahrens, L. (2022) · Environmental Pollution · doi:10.1016/j.envpol.2022.119981 · Cited by 83 · see citing works
McGarr, J. T., Mbonimpa, E. G., McAvoy, D. C., & Soltanian, M. R. (2023) · Soil Systems · doi:10.3390/soilsystems7020053 · Cited by 75 · see citing works
Ideal versus Nonideal Transport of PFAS in Unsaturated Porous Media
Brusseau, M. L., Guo, B., Huang, D., Yan, N., & Lyu, Y. (2021) · Water Research · doi:10.1016/j.watres.2021.117405 · Cited by 77 · see citing works
Self-citationLi, H., Dong, Q., Zhang, M., Gong, T., Zan, R., & Wang, W. (2023) · Environmental Pollution · doi:10.1016/j.envpol.2023.121579 · Cited by 80 · see citing works
A screening model for quantifying PFAS leaching in the vadose zone and mass discharge to groundwater
Guo, B., Zeng, J., Brusseau, M. L., & Zhang, Y. (2022) · Advances in Water Resources · doi:10.1016/j.advwatres.2021.104102 · Cited by 72 · see citing works
Self-citationModeling PFAS Sorption in Soils Using Machine Learning
Fabregat‐Palau, J., Ershadi, A., Finkel, M., Rigol, A., Vidal, M., & Grathwohl, P. (2025) · Environmental Science & Technology · doi:10.1021/acs.est.4c13284 · Cited by 68 · see citing works
Borthakur, A., Leonard, J., Koutnik, V. S., Ravi, S., & Mohanty, S. K. (2021) · Current Opinion in Environmental Science & Health · doi:10.1016/j.coesh.2021.100309 · Cited by 67 · see citing works
Alam, M. S., Abbasi, A., & Chen, G. (2024) · Journal of Environmental Management · doi:10.1016/j.jenvman.2024.123163 · Cited by 65 · see citing works
Monitored Natural Attenuation to Manage PFAS Impacts to Groundwater: Scientific Basis
Newell, C. J., Adamson, D. T., Kulkarni, P. R., Nzeribe, B. N., Connor, J. A., Popovic, J., & Stroo, H. F. (2021) · Groundwater Monitoring & Remediation · doi:10.1111/gwmr.12486 · Cited by 64 · see citing works
Retention of PFOS and PFOA Mixtures by Trapped Gas Bubbles in Porous Media
Abraham, J. E. F., Mumford, K. G., Patch, D. J., & Weber, K. P. (2022) · Environmental Science & Technology · doi:10.1021/acs.est.2c00882 · Cited by 62 · see citing works
Zeng, J., Brusseau, M. L., & Guo, B. (2021) · Journal of Hydrology · doi:10.1016/j.jhydrol.2021.127172 · Cited by 62 · see citing works
Self-citationLe, S.-T., Kibbey, T. C. G., Weber, K. P., Glamore, W. C., & O’Carroll, D. M. (2020) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2020.142882 · Cited by 62 · see citing works
Høisæter, Å., Arp, H. P. H., Slinde, G. A., Knutsen, H., Hale, S. E., Breedveld, G. D., & Hansen, M. C. (2021) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2021.148763 · Cited by 58 · see citing works
Brusseau, M. L. (2023) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2023.163730 · Cited by 56 · see citing works
Self-citationBrusseau, M. L. (2020) · Water Research · doi:10.1016/j.watres.2020.116778 · Cited by 54 · see citing works
Self-citationGlubt, S. V., & Brusseau, M. L. (2021) · Environmental Science & Technology · doi:10.1021/acs.est.0c07355 · Cited by 54 · see citing works
Self-citationJi, Y., Yan, N., Brusseau, M. L., Guo, B., Zheng, X., Dai, M., Liu, H., & Li, X. (2021) · Environmental Science & Technology · doi:10.1021/acs.est.1c01919 · Cited by 54 · see citing works
Self-citationMobilization of Per- and Polyfluoroalkyl Substances (PFAS) in Soils: A Review
Khalil, C. A., Sarkar, D., Braykaa, P., & Boufadel, M. C. (2022) · Current Pollution Reports · doi:10.1007/s40726-022-00241-8 · Cited by 56 · see citing works
Huang, D., Saleem, H., Guo, B., & Brusseau, M. L. (2021) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2021.150595 · Cited by 54 · see citing works
Self-citationField-Scale Demonstration of PFAS Leachability Following In Situ Soil Stabilization
McDonough, J. T., Anderson, R. H., Lang, J. R., Liles, D. S., Matteson, K., & Olechiw, T. (2021) · ACS Omega · doi:10.1021/acsomega.1c04789 · Cited by 52 · see citing works
Sprocati, R., & Rolle, M. (2021) · Water Resources Research · doi:10.1029/2021wr029959 · Cited by 52 · see citing works
John, J., Coulon, F., & Chellam, P. V. (2021) · Journal of Water Process Engineering · doi:10.1016/j.jwpe.2021.102463 · Cited by 53 · see citing works
Anderson, R. H. (2021) · Environmental Science & Technology · doi:10.1021/acs.est.1c01543 · Cited by 51 · see citing works
Watershed scale PFAS fate and transport model for source identification and management implications
Rafiei, V., & Nejadhashemi, A. P. (2023) · Water Research · doi:10.1016/j.watres.2023.120073 · Cited by 51 · see citing works
Stults, J. F., Choi, Y. J., Schaefer, C. E., Illangasekare, T. H., & Higgins, C. P. (2022) · Environmental Science & Technology · doi:10.1021/acs.est.2c00819 · Cited by 46 · see citing works
Quinnan, J., Rossi, M., Curry, P., Lupo, M., Miller, M., Korb, H., Orth, C., & Hasbrouck, K. (2021) · Remediation Journal · doi:10.1002/rem.21680 · Cited by 46 · see citing works
Steffens, S. D., Cook, E. K., Sedlak, D. L., & Alvarez‐Cohen, L. (2021) · Environmental Science & Technology Letters · doi:10.1021/acs.estlett.1c00762 · Cited by 44 · see citing works
Guo, B., Saleem, H., & Brusseau, M. L. (2023) · Environmental Science & Technology · doi:10.1021/acs.est.2c08601 · Cited by 45 · see citing works
Self-citationCáñez, T. T., Guo, B., McIntosh, J. C., & Brusseau, M. L. (2021) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2021.147906 · Cited by 46 · see citing works
Self-citationAqueous Film-Forming Foams Exhibit Greater Interfacial Activity than PFOA, PFOS, or FOSA
Costanza, J., Abriola, L. M., & Pennell, K. D. (2020) · Environmental Science & Technology · doi:10.1021/acs.est.0c03117 · Cited by 41 · see citing works
Adsorption of PFAAs in the Vadose Zone and Implications for Long-Term Groundwater Contamination
Gnesda, W. R., Draxler, E. F., Tinjum, J. M., & Zahasky, C. (2022) · Environmental Science & Technology · doi:10.1021/acs.est.2c03962 · Cited by 44 · see citing works
Zeng, J., & Guo, B. (2023) · Geophysical Research Letters · doi:10.1029/2022gl102655 · Cited by 40 · see citing works
Self-citationAir-water interfacial areas relevant for transport of per and poly-fluoroalkyl substances
Brusseau, M. L., & Guo, B. (2021) · Water Research · doi:10.1016/j.watres.2021.117785 · Cited by 42 · see citing works
Self-citationChallenges in the PFAS Remediation of Soil and Landfill Leachate: A Review
Travar, I., Uwayezu, J. N., Kumpienė, J., & Yeung, L. W. Y. (2021) · Advances in Environmental and Engineering Research · doi:10.21926/aeer.2102006 · Cited by 39 · see citing works
Stults, J. F., Choi, Y. J., Rockwell, C., Schaefer, C. E., Nguyen, D. D., Knappe, D. R. U., Illangasekare, T. H., & Higgins, C. P. (2023) · Environmental Science & Technology · doi:10.1021/acs.est.2c07316 · Cited by 38 · see citing works
Lari, K. S., Davis, G. B., Kumar, A., Rayner, J. L., Kong, X., & Saar, M. O. (2024) · ACS Omega · doi:10.1021/acsomega.3c09201 · Cited by 39 · see citing works
Holly, M. A., Gunn, K. M., Keymer, D. P., & Sanford, J. R. (2024) · ACS ES&T Water · doi:10.1021/acsestwater.3c00414 · Cited by 39 · see citing works
Rovero, M., Cutt, D., Griffiths, R., Filipowicz, U. I., Mishkin, K. R., White, B., Goodrow, S. M., & Wilkin, R. T. (2021) · Groundwater Monitoring & Remediation · doi:10.1111/gwmr.12485 · Cited by 38 · see citing works
Soil Pollution and Its Interrelation with Interfacial Chemistry
Omo-Okoro, P. N., Ofori, P. A., Amalapridman, V., Dadrasnia, A., Abbey, L., & Emenike, C. U. (2025) · Molecules · doi:10.3390/molecules30122636 · Cited by 39 · see citing works
Lyu, Y., Wang, B., Du, X., Guo, B., & Brusseau, M. L. (2022) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2022.154905 · Cited by 39 · see citing works
Self-citationEnhanced attenuation (EA) to manage PFAS plumes in groundwater
Newell, C. J., Javed, H., Li, Y., Johnson, N. W., Richardson, S. D., Connor, J. A., & Adamson, D. T. (2022) · Remediation Journal · doi:10.1002/rem.21731 · Cited by 37 · see citing works
Bigler, M. C., Brusseau, M. L., Guo, B., Jones, S. L., Pritchard, J. C., Higgins, C. P., & Hatton, J. W. (2024) · Environmental Science & Technology · doi:10.1021/acs.est.4c01615 · Cited by 37 · see citing works
Self-citationGarza‐Rubalcava, U., Klevan, C., Pennell, K. D., & Abriola, L. M. (2024) · Water Research · doi:10.1016/j.watres.2024.122728 · Cited by 35 · see citing works
Dry-wet and freeze-thaw cycles enhance PFOA leaching from subsurface soils
Borthakur, A., Olsen, P., Dooley, G., Cranmer, B. K., Rao, U., Hoek, E. M. V., Blotevogel, J., Mahendra, S., & Mohanty, S. K. (2021) · Journal of Hazardous Materials Letters · doi:10.1016/j.hazl.2021.100029 · Cited by 37 · see citing works
Sherman-Bertinetti, S. L., Kostelnik, E. G., Gruber, K. J., Balgooyen, S., & Remucal, C. K. (2024) · Environmental Science & Technology · doi:10.1021/acs.est.4c02285 · Cited by 35 · see citing works
Li, C., Zhang, C., Gibbes, B. R., Wang, T., & Lockington, D. A. (2022) · Advances in Water Resources · doi:10.1016/j.advwatres.2022.104240 · Cited by 35 · see citing works
Predicting the impact of salt mixtures on the air-water interfacial behavior of PFAS
Le, S.-T., Gao, Y., Kibbey, T. C. G., Glamore, W. C., & O’Carroll, D. M. (2021) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2021.151987 · Cited by 33 · see citing works
Gerardu, T., Dijkstra, J. J., Beeltje, H., van Duivenbode, A. V. R., & Griffioen, J. (2022) · Environmental Advances · doi:10.1016/j.envadv.2022.100332 · Cited by 33 · see citing works
Determining groundwater recharge for quantifying PFAS mass discharge from unsaturated source zones
Newell, C. J., Stockwell, E. B., Alanis, J., Adamson, D. T., Walker, K. L., & Anderson, R. H. (2023) · Vadose Zone Journal · doi:10.1002/vzj2.20262 · Cited by 32 · see citing works
Diffusion of perfluoroalkyl acids through clay-rich soil
Schaefer, C. E., Drennan, D. M., Nickerson, A., Maizel, A. C., & Higgins, C. P. (2021) · Journal of Contaminant Hydrology · doi:10.1016/j.jconhyd.2021.103814 · Cited by 32 · see citing works
Schaefer, C. E., Nguyen, D. N., Christie, E. C., Shea, S., Higgins, C. P., & Field, J. A. (2021) · Journal of Environmental Engineering · doi:10.1061/(asce)ee.1943-7870.0001952 · Cited by 32 · see citing works
Srivastava, A., & Verma, D. (2022) · Environmental Science and Pollution Research · doi:10.1007/s11356-022-22198-3 · Cited by 30 · see citing works
Smith, J., Brusseau, M. L., & Guo, B. (2024) · Water Research · doi:10.1016/j.watres.2024.121236 · Cited by 31 · see citing works
Self-citationMonitored natural attenuation to manage PFAS impacts to groundwater: Potential guidelines
Newell, C. J., Adamson, D. T., Kulkarni, P. R., Nzeribe, B. N., Connor, J. A., Popovic, J., & Stroo, H. F. (2021) · Remediation Journal · doi:10.1002/rem.21697 · Cited by 30 · see citing works
Silva, J. A. K., Šimůnek, J., & McCray, J. E. (2022) · Journal of Contaminant Hydrology · doi:10.1016/j.jconhyd.2022.103984 · Cited by 31 · see citing works
Chen, S., & Guo, B. (2023) · Water Resources Research · doi:10.1029/2023wr034664 · Cited by 28 · see citing works
Self-citationDamião, G., Morgado, P., Silva, P., Martins, L. F. G., McCabe, C., & Filipe, E. J. M. (2023) · Fluid Phase Equilibria · doi:10.1016/j.fluid.2023.113928 · Cited by 29 · see citing works
Revising the EPA dilution-attenuation soil screening model for PFAS
Brusseau, M. L., & Guo, B. (2023) · Journal of Hazardous Materials Letters · doi:10.1016/j.hazl.2023.100077 · Cited by 28 · see citing works
Self-citationIslam, M. A., Parvin, M. I., Nguyen, C., Alam, M. R., Kwong, P. C. W., Zhou, J. L., Hessel, V., & Ahmed, M. B. (2025) · Environmental Pollution · doi:10.1016/j.envpol.2025.127036 · Cited by 30 · see citing works
Delor, L., Louzon, M., Pelosi, C., Michel, E., Maillet, G., & Carronnier, H. (2023) · Environmental Pollution · doi:10.1016/j.envpol.2023.122221 · Cited by 28 · see citing works
Rasmusson, K., & Fagerlund, F. (2024) · Chemosphere · doi:10.1016/j.chemosphere.2024.142663 · Cited by 29 · see citing works
Biesek, B. J., Szymkiewicz, A., Šimůnek, J., Gumuła-Kawęcka, A., & Jaworska-Szulc, B. (2024) · Science of The Total Environment · doi:10.1016/j.scitotenv.2024.173252 · Cited by 26 · see citing works
Arshadi, M., Garza‐Rubalcava, U., Guedes, A., Cápiro, N. L., Pennell, K. D., Christ, J. A., & Abriola, L. M. (2024) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2024.170566 · Cited by 24 · see citing works
Vahedian, F., Silva, J. A., Šimůnek, J., & McCray, J. E. (2024) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2024.177420 · Cited by 24 · see citing works
Zeng, J., Brusseau, M. L., & Guo, B. (2024) · Water Resources Research · doi:10.1029/2024wr037707 · Cited by 24 · see citing works
Self-citationLow-concentration tracer tests to measure air-water interfacial area in porous media
Brusseau, M. L., Lyu, Y., Yan, N., & Guo, B. (2020) · Chemosphere · doi:10.1016/j.chemosphere.2020.126305 · Cited by 22 · see citing works
Self-citationXingchun, J., Zhao, W., Jing, P., Lu, G., Chen, D., Zhaohe, Z., & Yiran, Z. (2023) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2023.165904 · Cited by 22 · see citing works
Kulkarni, P. R., Adamson, D. T., Popovic, J., & Newell, C. J. (2022) · Journal of Contaminant Hydrology · doi:10.1016/j.jconhyd.2022.103986 · Cited by 20 · see citing works
Zhang, W., & Guo, B. (2024) · Water Resources Research · doi:10.1029/2023wr035775 · Cited by 20 · see citing works
Self-citationBigler, M. C., He, X., & Brusseau, M. L. (2024) · Water Research · doi:10.1016/j.watres.2024.121922 · Cited by 19 · see citing works
Self-citationBierbaum, T., Klaas, N., Braun, J., Nürenberg, G., Lange, F. T., & Haslauer, C. (2023) · The Science of The Total Environment · doi:10.1016/j.scitotenv.2023.162588 · Cited by 18 · see citing works
Cogorno, J., & Rolle, M. (2024) · Environmental Science & Technology · doi:10.1021/acs.est.4c02164 · Cited by 17 · see citing works
Ouni, A. E., Guo, B., Zhong, H., & Brusseau, M. L. (2020) · Chemosphere · doi:10.1016/j.chemosphere.2020.128193 · Cited by 18 · see citing works
Self-citationBrusseau, M. L. (2025) · Water Research · doi:10.1016/j.watres.2025.123952 · Cited by 17 · see citing works
Self-citationZeng, J., Liu, K., Weng, C., Yan, C. Y., Wang, X., Lin, X., Liu, N., & Qiu, J. (2025) · Environmental Science & Technology · doi:10.1021/acs.est.5c05607 · Cited by 19 · see citing works
Self-citationToxicity of per- and polyfluoroalkyl substances to microorganisms in confined hydrogel structures
Jeong, Y., Vyas, K., & Irudayaraj, J. (2023) · Journal of Hazardous Materials · doi:10.1016/j.jhazmat.2023.131672 · Cited by 17 · see citing works
Statistical Mapping of PFOA and PFOS in Groundwater throughout the Contiguous United States
Park, B., Kang, H., & Zahasky, C. (2024) · Environmental Science & Technology · doi:10.1021/acs.est.4c05616 · Cited by 17 · see citing works
Costanza, J., Clabaugh, C. D., Leibli, C., Ferreira, J., & Wilkin, R. T. (2025) · Environmental Science & Technology · doi:10.1021/acs.est.4c10246 · Cited by 15 · see citing works
Mosthaf, K., Rosenberg, L., Broholm, M. M., Fjordbøge, A. S., Lilbæk, G., Christensen, A. G., & Bjerg, P. L. (2023) · Journal of Contaminant Hydrology · doi:10.1016/j.jconhyd.2023.104281 · Cited by 15 · see citing works
PFAS fate using lysimeters during degraded soil reclamation using biosolids
Peter, L. G., Gharehveran, M. M., Alvarez‐Campos, O., Evanylo, G. K., & Lee, L. (2024) · Journal of Environmental Quality · doi:10.1002/jeq2.20576 · Cited by 15 · see citing works
- Authors
- Guo, B., Zeng, J., & Brusseau, M. L.
- Affiliations
- University of Arizona (US)
- Corresponding author
- Guo, Bo
- Venue
- Water Resources Research
- Publisher
- American Geophysical Union (AGU)
- Published
- 2020-02
- Volume
- 56
- Issue
- 2
- ISSN
- 0043-1397 (ISSN-L)
- 1944-7973
- PMC
- PMC7673302
- OpenAlex
- W2999663693
- Cited by
- 224
- References
- 74
- Citations by year
- 2026: 45 · 2025: 37 · 2024: 38 · 2023: 27 · 2022: 31 · 2021: 37 · 2020: 9
- FWCI
- 9.64
- Type
- journal article
- Language
- en
- Open access
- green
- europepmc.org
- Locations
- Water Resources Research (publishedVersion)
- PubMed (publishedVersion)
- Europe PMC (PubMed Central) (acceptedVersion)
- PubMed Central (acceptedVersion)
- UA Campus Repository (The University of Arizona) (acceptedVersion)
- Funders
- National Institute of Environmental Health Sciences (P42ES004940)
- Topics
- Physical Sciences › Environmental Science › Environmental Chemistry › Per- and polyfluoroalkyl substances research
- Physical Sciences › Environmental Science › Environmental Engineering › Groundwater flow and contamination studies
- Physical Sciences › Engineering › Civil and Structural Engineering › Soil and Unsaturated Flow
- Keywords
- per- and polyfluoroalkyl substances, PFOS, vadose zone, air-water interface adsorption, solid-phase adsorption, retention factor, groundwater contamination, aqueous film-forming foam, gravity drainage, capillary retention, source zone
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 ›
Are you an author, or do you see a problem with this page? Request a review