Per- and polyfluorinated alkyl substances (PFASs) belong to a large group of man-made chemicals that pollute the environment. Perfluorooctane sulfonic acid (PFOS) and perfluorooctanoic acid (PFOA) are the most commonly found PFASs. The pollution of PFASs can be caused among others by using of aqueous fire-fighting foams (AFFFs). PFASs are persistent compounds; that can travel long distances and bioaccumulate in biota. There are several exposure routes for PFASs, but the most common are via food and drinking water. A possible way for PFASs to enter the food chain is by adsorption to microbes. In this project, binding of PFASs to three gram-negative bacteria, Eschericha coli, Acidovorax delafieldii and Pseudomonas nitroreducens, was assessed. Microbes were exposed for fluorinated compounds in environmental water samples and a PFAS-11 solution with 11 PFAS substances prepared in the laboratory. The binding seems to be preferential to the most abundant compounds, PFOS, since the second most abundant compound in the samples was PFHxS with concentrations at one third of the PFOS concentration but nonetheless PFHxS was not detected in any of the samples. The binding of mainly one PFAS was identified; PFOS was bound at highest concentrations in E. coli treated with both environmental water sample and a PFAS-11 solution. Low concentrations of FOSA and PFDoDS were identified in E. coli and PFNA in A. delafieldii. Only PFOS was detected in P. nitroreducens. The concentrations of other PFASs were below their respective method detection limits.

Per- and polyfluoroalkyl substances (PFASs) are a group of man-made organic chemicals that have been commercially used since the 1950s in many consumer products, including impregnated textiles, impregnated paper, nonstick products (e.g., Teflon), cleaning agents, and in firefighting foams. However, PFASs have in recent years received increasing public attention due to their persistence, bioaccumulative potential, and potentially toxic effects on humans and animals. Firefighting training sites have been identified as one of the most important sources for the spread of PFASs in the environment, due to the use of PFAS-containing firefighting foam of type AFFFs (aqueous film forming foams). This has resulted in contamination of both drinking water and groundwater in several municipalities in Sweden. At the former fire station in Åkersberga, AFFFs were handled and used during the fire-training exercises. WSP Environmental Sweden has performed a preliminary investigation on site and elevated levels of PFASs in both soil and groundwater were observed. Since the property is located next to a railroad track, there is a concern that PFASs will spread through the railroad track towards the nearby Åkers canal. The aim of this master’s thesis has therefore been to map the transport of PFASs in groundwater from this former fire station. A groundwater flow model was first constructed in the software program Visual MODFLOW. The groundwater model was then used as a basis for the construction of a transport model with MODPATH and MT3DMS. The transport of four PFAS homologues was modeled; perfluorooctane sulfonic acid (PFOS), perfluorooctanoic acid (PFOA), 6:2 Fluorotelomer sulfonate (6:2 FTS), and perfluoropentanoic acid (PFPeA). The result of the groundwater modelling showed that groundwater from the property flows towards the southwest and then further towards Åkers canal. The approximated velocity of a water molecule varied between 270 m/year and 400 m/year. The transport modelling showed that all four PFAS homologues traveled towards Åkers canal via the railroad track and that the short-chain PFAS homologues (6:2 FTS and PFPeA) traveled longer and faster than the long-chain PFAS homologues (PFOS and PFOA). The approximated velocity of the contaminant plume for the concentration 4.5 ·10−5 mg/L was 0.6 m/year for PFOS, 3 m/year for PFOA, 8 m/year for 6:2 FTS, and 16 m/year for PFPeA. / Per- och polyfluorerade alkylsubstanser (PFAS) är en grupp av konstgjorda organiska kemikalier som sedan 1950-talet har kommersiellt använts i många konsumentprodukter, inklusive impregnerade textilier, impregnerat papper, nonstick-produkter (t.ex. Teflon), rengöringsmedel och brandsläckningsskum. PFAS har dock under senare år fått ökad allmän uppmärksamhet på grund av deras persistens, bioackumuleringspotential och potentiella toxiska effekter på människor och djur. Brandövningsplatser har identifierats som en av de största källorna för spridningen av PFAS i miljön, på grund av användningen av PFAS-innehållande brandsläckningsskum av typen AFFF (aqueous film forming foams). Detta har resulterat i förorening av både dricksvatten och grundvatten i flera kommuner i Sverige. På den tidigare brandstationen i Åkersberga har hantering och användning av AFFF ägt rum under släckningsövningarna. WSP Environmental Sverige har utfört förundersökning på plats och förhöjda halter PFAS i både jord och grundvatten observerades. Då fastigheten gränsar mot en banvall, finns det en oro att PFAS ska sprida via banvallen mot den närliggande Åkers kanalen. Syftet med detta examensarbete har därför varit att kartlägga transporten av PFAS i grundvatten från denna tidigare brandstation. En grundvattenflödesmodell konstruerades först i programvaran Visual MODFLOW. Grundvattenmodellen användes sedan som grund för konstruktionen av en transportmodell med MODPATH och MT3DMS. Transporten av fyra PFAS-homologer modellerades; perfluoroktansulfonat (PFOS), perfluorooktansyra (PFOA), 6:2 fluortelomersulfonat (6: 2 FTS) och perfluorpentansyra (PFPeA). Resultatet av grundvattenmodelleringen visade att grundvatten från fastigheten strömmar mot sydväst och sedan vidare mot Åkers kanal. Den approximerade hastigheten hos en vattenmolekyl varierade mellan 270 m/år och 400 m/år. Transportmodelleringen visade att alla fyra PFAS-homologerna spred mot Åkers kanal via banvallen och att de kortkedjiga PFAS-homologerna (6:2 FTS och PFPeA) spred längre och snabbare än de långkedjiga PFAS-homologerna (PFOS och PFOA). Ungefärlig hastighet av föroreningsplymen för koncentration 4.5 ·10−5 mg/L var 0,6 m/år för PFOS, 3 m/år för PFOA, 8 m/år för 6: 2 FTS och 16 m/år för PFPeA.

Per- and polyfluoroalkyl substances (PFASs) are synthetic chemicals which are used in a wide range of applications such as aqueous film forming foam (AFFF) for firefighting, paint, coating and cosmetics. For almost a decade, PFASs have received worldwide attention because of the ubiquitous detection of PFAS in the environment and their bioaccumulative, persistent and give toxic effects on animals and humans. A number of study have shown many unknown organofluorine present in environmental samples. The total oxidizable precursor (TOP) method is an oxidation method to convert any precursor compounds of PFASs into measurable perfluorinated carboxylic acids (PFCAs) or sulfonic acids (PFSAs). The aims of this project are to evaluate if the use of total oxidizable precursor (TOP) assay may help improve the mass balance analysis between the quantifiable PFASs and extractable organofluorine in samples. In this study, three water samples: landfill leachate water, contaminated groundwater and adiluted Sthamex AFFF with tap water were undergone TOP assay to reveal the present of any unidentified precursor compounds. To obtain the extractable organofluorine and quantifiable PFAS levels in the samples, combustion ion chromatography (CIC) and liquid chromatography – tandem mass spectrometry (LC-MS/MS) were used, respectively. Results suggested the presence of unidentified precursor compounds in the samples with the aid of TOP assay reaction. Although after the oxidative conversion, a large portion of unidentified PFASs compounds were still present in the samples. The quantifiable PFASs in the samples were up to 7 % of the EOF; in other word, there were still around 93 % of unidentified compounds present in the samples. Further development of analytical method for characterization or identification of these unknown PFAS compounds is needed.