<p>Waste-derived organic products are nutrient-rich materials often applied to agricultural land as a fertilizer to enhance agricultural production and soil quality. Commercially available biosolid-based products, which are sold and distributed in bags or bulk, are rapidly gaining popularity for urban and suburban use. Although biosolid-derived products have many benefits, they may contain trace organic contaminants such as per- and polyfluoroalkyl acids (PFAAs) and pharmaceutical and personal care products (PPCPs), in varying levels, depending on waste source composition. These organic compounds have been used in a variety of consumer and industrial products and are known to accumulate in biosolids due to their recalcitrance in conventional wastewater treatment processes. Thus, the application of commercially available biosolids-based products on urban and suburban gardens may lead to transfer and accumulation of organic contaminants into food crops, raising food safety concerns. Most studies to date have focused on municipal biosolids application on agricultural lands with very few studies focused on commercial products available for home and urban gardens. For the latter, the evaluations of bioavailability and subsequent plant uptake of organic contaminants from biosolids have also often been conducted by adding organic contaminants to the growing media (e.g., soil or hydroponic) at a concentration that greatly exceed environmentally relevant concentrations. Moreover, there are currently no studies evaluating leaching and plant uptake potential of contaminants from commercially available (e.g., local stores) biosolids. The research described in this dissertation 1) assessed the occurrence of PFAAs and representative PPCPs in commercially available biosolid-based products and their porewater concentrations in saturated media as a measure of bioavailability and leachability; 2) investigated how heat-treatment, composting, blending and thermal hydrolysis processes on biosolids to convert them to commercial biosolid-based products affect PFAA concentrations in the production of commercial biosolid-based product; and 3) assessed the bioavailability and plant uptake of PFAAs and targeted PPCPs by kale and turnips grown in soil-less potting media amended with Milorganite (a commercially available biosolids-based fertilizer product) at the recommended rate and four times the recommended rate.</p><p>The biosolid-based products displayed varying levels of organic contaminants. Higher PFAA concentrations were detected in biosolid-based products compared to nonbiosolid-based products. The common treatment processes used in taking biosolids to commercially available products were ineffective in reducing PFAA levels in the products except for blending with other essentially PFAA-free materials, thus served as a simple dilution. Porewater concentrations of PFAAs and PPCPs as an indicator of leachability and bioavailability were higher for the less hydrophobic compounds (e.g., short-chain PFAAs and diphenhydramine and carbamazepine with lower octanol-water partition coefficient). Leachability alone did not explain the observed plant uptake potential of PFAAs and PPCPs. With similar leachability and molecular weight/size between diphenhydramine and carbamazepine, higher uptake was observed with a positively charged compound (diphenhydramine compared to a neutral compound (carbamazepine). However, not all positively charged compounds were taken up by the plant. Azithromycin, a positively charged compound, had lower uptake than other contaminants which may be due to its large molecular size compared to diphenhydramine. Higher concentrations of miconazole, triclosan, and triclocarban were found in the biosolids-fertilizer; however, these compounds had low leachabilities and limited uptake by plants. Also, for PPCPs, the application rates of biosolid-based products did not necessarily correlate with the higher uptake and translocation of contaminants to the above-ground portion of plants. </p><p>This study provides an evaluation of commercially available waste-derived organic products under condition comparable to home and urban garden setting. Although biosolids-based products can serve as alternatives to synthetic fertilizers, they contain higher levels of trace organic contaminants than nonbiosolid-organic products. Common biosolids treatment processes are ineffective for reducing the levels of trace organic contaminants in biosolids, particularly for PFAAs. Thus, it is critical to control the sources contributing to the higher level of these contaminants in biosolids-based products. Also, regulations (e.g., triclosan and triclocarban) and replacements (e.g., longer-chain PFAAs to short-chain PFAAs) of persistent trace organic chemicals have led to a reduction in their levels in biosolids-based products. Although longer chain PFAAs are more likely to bioaccumulate and persistent than the replacement short-chain alternatives, the current study has shown that the short-chain PFAAs are more readily taken up to edible parts of plants than longer-chain PFAAs even when applying at the recommended fertilizer rate. Thus, the current movement to replace longer chain PFAAs with short chains has the potential to result in higher total PFAA concentrations being bioavailable for plant uptake, thus increasing the risk of food contamination by PFAAs. </p>

<div> <p>In recent years, the presence of per- and polyfluoroalkyl substances (PFAS) in aquatic systems has led to research on their fate, effects and treatability. PFAS have been found in various environmental matrices including wastewater effluents, surface, ground, and drinking water. Perfluoroalkyl acids (PFAAs) are the class of PFAS most commonly tested due to their ability to migrate rapidly through groundwater and include perfluoroalkyl sulfonic acids (PFSAs) and perfluoroalkyl carboxylic acids (PFCAs). Of the globally distributed and persistent PFAAs, PFSAs are the most resistant to biological and oxidative chemical attack. This doctoral study focused on a reductive treatment approach with zero valent metals/bimetals nanoparticles (NPs) synthesized onto a carbon material to reduce NP aggregation. Initial work focused on exploring reactivity of different combinations of nano (n) Ni, nFe⁰ and activated carbon (AC) at 22 ^oC to 60 ^oC for transforming perfluorooctanesulfonate (PFOS) from which nNiFe⁰-AC at 60 ^oC led to transformation of both linear (L-) and branched (Br-) PFOS isomers. The remaining research focused on work with nNiFe⁰-AC at 60 ^oC in batch reactors including optimizing nNiFe⁰-AC preparation, quantifying PFOS transformation kinetics and evaluating the effects of PFAA chain length (C4, C6 and C8) and polar head group (PFSA versus PFCA) as well a groundwater matrix on transformation magnitude. Optimization of analytical methods to provide multiple lines of evidence of transformation including fluoride, sulfite and organic product generation was an ongoing throughout the research.</p> <p>nNiFe⁰-AC prepared with a 3-h synthesis stirring time led to the highest PFOS transformation of 51.1 ± 2.1% with generation of ~ 1 mole of sulfite (measured as sulfate) and 12 moles of fluoride. Several poly/per-fluorinated intermediates with single and double bonds were identified using quadrupole time-of-flight mass spectrometry (QToF-MS) in negative electrospray ionization (ESI-) mode with MS/MS fragmentation confirmation as well as one and later two desulfonated products with QToF negative atmospheric pressure chemical ionization (APCI-). All organic transformation products were found in only particle extracts as well as most of the sulfite generated. PFOS transformation kinetics showed that generated fluoride concentrations increased for the first day whereas sulfate concentrations continued to increase during the 5-d reaction. The transformation products identified showed defluorination of single- and double-bond structures, formation of C8 to C4 PFCAs and paraffins from cleavage of the C-S bond.</p> <p>The length of the perfluoroalkyl chain affected the length of time to achieve peak removal, but overall magnitude of transformation when reactions appeared complete were similar for both PFSAs and PFCAs. Like PFOS, PFOA transformation maxed in 1 d whereas shorter chains required more time to reach their peak removal, which is hypothesized to be due to lower sorption of the shorter chain PFAAs to the reactive surfaces. Measured F mass balance was higher for PFOS and PFOA (>90% F) compared to shorter chain PFAAs (~50-70% F). The Perfluorohexanesulfonate (PFHxS) and perfluorobutanesulfonate (PFBS) degradation products include single bond polyfluoroalkyl sulfonates and shorter-chain perfluoroalkyl carboxylates. For example, PFHxS transformation resulted in perfluorohexane carboxylic acid (PFHxA) and perfluorobutane carboxylic acid (PFBA). PFCA transformation products included per- & polyfluoroalkyl carboxylates with single bonds and alcohols with single and double bonds. The effect of inorganic matrix on transformation with nNiFe⁰-AC at 60 ^oC was explored using a contaminated groundwater collected at a former fire-training area in Massachusetts. Transformation appeared ‘generally’ lower than in the single-solute clean water systems, which may have been due to the presence of PFAS precursors that degraded to PFAAs and competitive adsorption between anionic PFAAs and inorganic ions onto the NP surface.</p><p>The research presented here demonstrates that nNiFe⁰-AC at 60 ^oC can mineralize PFAAs even in a typical groundwater matrix. Additional lab and pilot scale studies are needed to clarify the mechanisms leading to transformation as well as why transformation reactions plateau prior to all the parent compounds being transformed. The latter may be due to a poisoning phenomenon that can occur in closed systems, which may not occur in a flowing system more characteristic of an environmental scenario, as well as surface area and reactive site constraints or particle passivation.</p></div>

The occurrence of chemical contaminants in the environment is one of the key issues the world isfacing today. Special effort has been put on the screening of endocrine disrupting compounds(EDCs), substances that have been shown to have adverse effects on the endocrine system. EDCs are mainly found in pharmaceuticals and personal care products (PPCPs), but also other products covering almost all categories of our daily life. EDCs can be both organic, such as the persistent organic pollutants (POPs), and inorganic, e.g. heavy metals. Today, all kinds of EDCs are currently being investigated on a large scale. Two EDC sub-categories that have gained increased public attention during the last years are organic flame retardants (FRs) and per- and polyfluoroalkylated substances (PFASs). Both categories have shown to be bioaccumulating, persistent and toxic, which has led to banning of several substances in both categories. However, as both FRs and PFASs are considered to be emerging POPs, their fate and behaviour in the environment are still in great need of research. FRs and PFASs often end up in surface waters due to their disinclination of getting removed in waste water treatment plants (WWTPs) and their persistence. Thus, the objective of this project was to provide a snapshot of the current situation of FRs and PFASs in Swedish rivers, including both smaller streams and bigger rivers. Grab water samples were taken at 25 sites for FRs and 44 for PFASs in rivers all over Sweden. The results showed that sparsely populated areas such as the northern part of Sweden generally showed lower concentrations of PFASs in the water than the southern part did. The summarised concentrations of FRs ranged from 37 ng L-1 to 4.6 μg L-1, and from 0.59 ng L-1 to 59 ng L-1 for the detected PFASs, which was in good comparison to previous studies carried out on surface water in Europe. The percentile composition, the so-called fingerprint, showed significant differences between the southern part and the northern part for both FRs and PFASs, but also great similarities between some of the rivers with the highest measured PFASs concentrations. The highest loads of both FRs and PFASs were detected in Delångersån, which is one of the smaller rivers screened and likely to be affected by a nearby industrial point source. The European environmental quality standard of 0.65 ng L-1 of perfluorooctane sulfonic acid (PFOS) was exceeded in 12 of all 44 sampled rivers.

Perfluoroalkylated substances (PFASs) are a group of synthetic compounds that have gained growing attention due to their environmental persistence, toxicity and their potential to bioaccumulate. Even though PFASs are not occurring naturally in our environment, they are globally distributed and can be found ubiquitously in air, water, soil, wildlife as well as in humans. PFASs have primarily been used, due to their unique properties of being both hydrophilic and hydrophobic, as surfactants in numerous products such as firefighting foams, paint, leather and textile coating. The occurrence of PFASs in drinking water as well as in wastewater makes it important to develop effective techniques to remove these compounds from drinking water sources and wastewater. To be able to effectively remove PFASs from drinking water and wastewater it is important to understand which treatment process is most efficient and how the removal efficiency is affected by the physicochemical properties of PFASs and characteristics of water. In this study, the removal efficiency of PFASs was investigated using six different water types with varying dissolved organic carbon (DOC) character. Four different treatment techniques were evaluated including anion exchange using MIEX® resins, coagulation with iron (III) chloride (FeCl3), adsorption using powdered activated carbon (PAC) and nanofiltration (NF) membrane. The batch experiments were performed in laboratory-scale for 14 individual PFASs including C3-11, C13 perfluoroalkyl carboxylic acids (PFCAs), C4, C6, C8 perfluoroalkyl sulfonic acids (PFSAs) and perfluorooctane sulfonamide (FOSA). The results showed that the removal efficiency of PFASs was dependent on both perfluorocarbon chain length as well as functional group, with an increase in removal efficiency with increased perfluorocarbon chain length. Short-chained PFASs (C!6) were removed in less extent than the long chained PFASs for all treatment techniques. Amongst the four treatment techniques investigated, NF membrane exhibited the best removal efficiency for both short- and long chained PFASs (on average, 51%). Lower removal efficiencies for PFASs were observed for MIEX (33%) &lt; FeCl3 (16%) &lt; PAC (14%). However, all tested treatment techniques used in this study exhibited generally low removal efficiency (&lt; 78%), in particular for the short-chained PFASs (C!6, &lt; 41%) Results using three different doses of PAC (i.e. 20, 50, 100 mg L-1) showed an increase in removal (i.e. 2.2-41%, 8.0-78% and 12-92% respectively) with increasing dose. No significant trends were found between PFAS removal and DOC removal for any of the treatments (p&lt;0.05, student t-test). However, the removal efficiency was different of the six different water types, which indicates that the DOC characteristics (i.e. Freshness, humification index, pH and absorbance) have an influence on the removal efficiency of PFASs in water. / Perfluoroalkylerade ämnen (PFASer) är en grupp syntetiska ämnen som har fått allt större uppmärksamhet den senaste tiden då de har visat sig vara persistenta, toxiska och bioackumulerande. Även om PFASer inte förekommer naturligt i vår miljö är de globalt fördelade och kan återfinnas i luft, vatten, mark, djur och hos människor. PFASer har främst använts, på grund av sina unika egenskaper att vara både hydrofila och hydrofoba, som tensider i många produkter såsom brandsläckningsskum, färg, läder och textil. Förekomsten av PFASer i dricksvattentäkter och i många reningsverk gör det viktigt att utveckla effektiva metoder för att ta bort dessa föreningar i vattenreningsverk. För att effektivt kunna avlägsna PFASer från dricks- och avloppsvatten är det viktigt att ha kunskap om vilken behandlingsmetod som är effektivast och hur reningseffektiviteten påverkas av ämnenas fysikalisk-kemiska egenskaper och vattnets karaktär.   Syftet med denna studie var att undersökta reningseffektiviteten för PFASer i sex olika vatten innehållande olika typer av löst organiskt kol (DOC). Detta undersöktes för fyra olika behandlingsteknikert; jonbyte med MIEX®, koagulering med järnklorid (FeCl3), adsorption med hjälp av pulveriserat aktivt kol (PAC) och nanofiltrering. Försöken gjordes små skaligt i laboratorie och 14 olika PFASer undersöktes; C3-11,13  perfluoralkyl karboxylsyror (PFCAer), C4, C6, C8, perfluoralkyl sulfonsyror (PFSAer) och perfluoroktan sulfonamid (FOSA). Resultaten visar att reningseffektiviteten för PFASer var beroende av både den perfluorerade kolkedjans längd och funktionell grupp, med en ökning av reningseffektivitet med längre perfluorerad kolkedja. PFASer med kort perfluorerad kolkedja (C≤6) renades i mindre utsträckning än PFASer med lång perfluorerad kolkedjade; detta gällde för alla behandlingstekniker. Bland de fyra behandlingstekniker som undersöktes uppvisade nanofiltreringen den bästa reningseffektiviteten för PFASer med både korta och långa kolkedjor (i genomsnitt, 51%.). Lägre reningseffektivitet för PFASer observerades för MIEX®(33%), &lt; FeCl3(16%) &lt; PAC (14%). Totalt sett erhölls en relativt låg reningseffektivitet (&lt;78%) för samtliga reningstekniker, speciellt för de kortkedjade PFASer (C£6, &lt; 41%). Resultat från försök med tre olika doser PAC (e.g. 20, 50, 100 mg L-1) visade på en ökad reningseffektivitet (2,2-41%, 8,0-78% och 12-92%) med ökad dos PAC. Inga signifikanta trender kunde urskiljas vad gäller reningseffektivitet av PFASer och rening av DOC (p&lt;0.05, student t-test), detta gällde för samtliga behandlingstekniker. Det fanns dock tydliga skillnader i reningseffektivitet mellan de sex olika vattentyperna vilket indikerar på att DOC egenskaperna (Freshnessindex, humifieringsindex, pH, absorbans) har en påverkan på reningseffektiviteten för PFASer i vatten.

Landfills are potential sources for PFASs and treatment techniques for landfill leachate are urgently needed. Foam fractionation is an aeration technique which utilizes the tendency of PFASs to escape the liquid phase and build foam. The foam is harvested and with it the contamination. Landfill leachate from Hovgården, Uppsala Sweden contained PFASs of higher concentration than desired and investigations into whether foam fractionation could reduce PFASs amounts were initiated. Landfill leachate containing sum PFASs of 5500 ng/L on average were aerated in two different aeration foam collection pilot set-ups for the research. The pilot set-ups were divided into two models: a batch pilot and a continuous pilot. The batch pilot was run for 60 minutes testing parameters such as column volume, air flow rate, dilution and using additives as NaCl, FeCl3 and dish soap. The continuous pilot used contact times of 5, 10 and 20 minutes with constant air flow rate and column volume and no additives. All batch experiments showed reduced concentrations of PFASs, from 62 up to 91%, with an average sum PFASs removal efficiency of 77%. Air flow rates of 4 and 6 L/min were more effective than 2 L/min to reduce the amount of PFASs. Smaller volumes got higher removal efficiency. The dilution experiments showed mixed and somewhat contradictory results, where the nondiluted experiment had removal efficiency of sum PFASs of average 77% while the 50% diluted had an average sum PFASs removal efficiency of 84%. The experiment with the greatest dilution (75%) had the lowest average sum PFASs removal efficiency as suspected, at 68%. Regarding additives, the experiments with added 0.155 and 0.313% NaCl in the leachate were most effective at removing PFASs. The dish soap and FeCl3 additives also contributed to higher PFASs reduction. The experiment with the addition of dish soap had an average sum PFASs removal efficiency of 88% compared to 77% without additives, and the highest concentration of FeCl3 (0,09% of the leachate) had an average sum PFASs removal efficiency of 85%. All continuous experiments showed reduced reduced PFASs concentrations with sum PFASs removal efficiencies ranging from 72 up to 94%, with an average of 86%. The majority of the PFASs were reduced within the first time steps for all experiments, but for the last amount to be removed the contact time needed to be longer. The column contact time of 20 min had the highest average sum PFASs removal efficiency. The conclusion is that PFASs are reduced during the treatment in the pilots and that the reduction is dependent on the chain length and functional groups of the substances, and increased with additives and increased air flow rate. The volume treated and the concentration of raw water also influenced the removal efficiency.

Per- and polyfluoroalkyl substances (PFAS) are synthetic compounds that have beenaround since 1940. They can be used in a variety of products such as fire-fighting foam, food packaging and cosmetic products. Many PFAS have potential toxic effects on both humans and animals which poses a problem due to their wide distribution and persistency. Another problem concerns the remediation of PFAS, where the substances ends up circulating between the different disposal types (landfills, wastewater treatment and incineration). Active methods are therefore needed to remove or retain the contaminants. Some examples of these remediation technologies can be biomaterials, organoclays and more advanced methods such as activated carbon and ion exchange. The more advanced being suited for remediation of drinking water. In this study, the sorption efficiency of two pine bark fractions has been studied and also compared to the efficiency of activated carbon. The evaluation was done for both target analysis (PFAS-11) and non-specific analysis of extractable organofluorine (EOF) compounds in contaminated water from a hazardous waste management facility. The two pine bark fractions indicated similar sorption efficiencies, for both the PFAS-11 and the EOF compounds. The sorption efficiency ranged from 10% up to 75% for perfluorinated sulfonic acids (PFSA) and from below zero up to 40% for perfluorinated carboxylic acids (PFCA). A general pattern can be seen, the sorption efficiency increases with increasing length of the PFAS chain. The activated carbon had a higher sorption efficiency, where the majority of PFAS had an average sorption of 100%. In comparison, the PFAS-11 and total EOF analysis displayed high concentrations of unidentified EOF compounds. These compounds indicated a negative sorption, which might imply that non-targeted PFAS or other fluorinated organic compounds desorb from the bark. Therefore, the pine bark might be suitable as a rough remediation of long-chain PFAS (≥8C), but further studies on the sorption of unidentified fluorinated organic compounds are of interest.

Machine learning and artificial intelligence are increasingly becoming mainstream in our daily lives, from smart algorithms that recognize us online to cars that can drive themselves. In this defense, the intersection of machine learning and computational chemistry are applied to the generation of new PFAS molecules that are less toxic than those currently used today without sacrificing the unique properties that make them desirable for industrial use. Additionally, machine learning is used to complete the SAMPL6 logP challenge and to correlate molecules to best DFT functionals for enthalpies of formation.

A relatively unexplored source of pollution is fire stations and their usage of aqueous film forming foam (AFFF) containing per- and polyfluorinated substances (PFAS). It is well documented that these were used at fire drill sites that contaminated surrounding surface water, sediments and groundwater. The aim of this study was to assess whether fire stations could be a source of pollution and spread of PFAS and if the industry should be given priority for further investigations. Four fire stations were selected for the assessment, which were carried out by using part one of the Method of Surveying Contaminated Sites (Acronym in Swedish: MIFO). This included studies of maps, archives and field visits where fire fighters were interviewed to gather information about activities that had taken place historically on the specific sites. All of the fire stations were classified as level 2, meaning they pose a high risk for the enviroment and human health accordning to MIFO. In conjunction to the assessment, existing testing results of PFAS in soil and water from other fire stations in Sweden are submitted in purpose of showing the general situation of pollution linked with the results of this evaluation. The conclusion of this study was that various activities at fire stations possibly have polluted ground -and surface waters and that the industry should be given priority for further investigations.

<div> <div> <div> <p>Water is a critical resource for life, and communities are dependent upon reliable access to clean </p> <p>water to maintain stable quality of life. Issues of water contamination threaten this stability, creating uncertainty, threatening public health, and necessitating community response. One emerging water contamination issue involves a family of industrial chemicals called Per- and Polyfluoroalkyl Substances (PFAS). This study uses an integrated multi-theory approach to examine the processes of Resilience and Collective Action within a community experiencing issues of PFAS contamination. Results indicate that the community was generally successful in enacting resilience, however some challenges were encountered in the form of high levels of uncertainty, inaccessibility of technical information, challenges foregrounding productive action, and challenges maximizing transformative potential. Results also indicated the community was general successful with collective action in the immediate aftermath of the issue. The community struggled to maintain collective action over a long period and to transition to high level advocacy. Results demonstrated that existing theoretical frames are limited in their ability to predict effective resilience and collective action in events of long-term water contamination. These limitations are described in detail and the potential for expansion of these theories is discussed. Suggestions to improve future responses to issues of PFAS contamination, as well as suggestions for intervention into the community of focus are offered. </p> </div> </div> </div>

Leachate from landfills is contaminated in many ways and per- and polyfluoroalkyl substances (PFAS)-contamination is one of them. Recent studies have demonstrated the environmental and human concerns of PFAS. Therefore, the treatment of leachate is important. One technique to reduce the PFAS concentration is by using aeration and foam fractionation. Hovgården is a landfill northeast of Uppsala, where previous measurements have shown high levels of PFAS in the leachate. Earlier small-scale experiments using aeration foam fractionation as a treatment technique for PFAS removal have been done successfully, but with upcoming requirements of PFAS concentrations there is a need to investigate whether an upscaling is possible or not. In this study, this has been investigated by pumping PFAS contaminated leachate from the landfill in to a 0.046 square metre plastic cylinder and aerated the leachate with an airflow of ten L min-1. A total of six experiments were conducted were the contact time and fraction of extracted foam was parameters that was varying. Four experiments were done with a contact time of ten min and foam fraction of five, ten, twenty and thirty percent and two experiments were made with a foam fraction of five percent and a contact time of twenty respectively thirty min. The average ΣPFAS removal, i.e., the percentage difference in ΣPFAS concentrations between the influent and effluent water in the different runs varied between 31 % and 66 %. The removal of long chained PFAS (≥C6) was higher than the removal of short chained PFAS(≤C5) even if all experiments did reduce the PFAS concentration. Carbon chains with a functional group containing a carboxylic acid is called perfluorocarboxylic acids (PFCA) and with a functional group containing a sulfonic acid is called perfluoroalkane sulfonic acids (PFSA). Precursors are PFAS that after a reaction degrades into PFCA and PFSA. The average removal efficiency of PFCA were 48 %, of PFSA 59 % and of precursors 78 %. The highest removal efficiency was discovered in the experiment with a 30-min contact time and five percent foam fraction with an average ΣPFAS removal of 58 % and an average Σlong chained PFAS removal of 92 %. The lowest removal efficiency was discovered in the experiment with a 10-min contact time and 20 percent foam fraction with an average ΣPFAS removal of 41 % and an average Σlong chained PFAS removal of 67 %. In conclusion a connection between increased contact time and increased removal efficiency was discovered but no clear connections between foam fraction and removal efficiency were found. However, it cannot be stated beyond reasonable doubt that the contact time is the decisive factor. Another conclusion is that the enrichment of short chained PFAS are higher in the water and a higher enrichment of long chained PFAS in the foam. In general, a higher inlet concentration of PFAS in the influent water resulted in a higher removal efficiency.