The aim of this study was to develop an analytical method for fluorinated silanes. Furthermore, as a secondary aim, to explore if there would be possible to detect 1H,1H,2H,2H-perfluorooctyl triethoxysilane (6:2 PTrEtSi) and 1H,1H,2H,2H-perfluorodecyl triethoxysilane (8:2 PTrEtSi) in two different matrices, sludge and cosmetic extract. The method development included experiments using LC-MS, LC-MS/MS, UPC2, GC-MS and APGC-MS/MS and was carried out using standards containing 6:2 PTrEtSi and 8:2 PTrEtSi. The analytical method that worked best for the compounds was GC-MS/MS and an analytical method using APGC-MS/MS was developed for fluorinated silanes. The IDL for 6:2 PTrEtSi was 0.0012 μg/mL and 1.32 μg/mL for 8:2 PTrEtSi. This makes the developed method suitable for high contaminated samples, such as extracts from cosmetic products. It was concluded that a method using LC as the analytical instrument would not work for the two target compounds since they were too reactive with the mobile phase. However, LC could be a good choice for siloxanes, compounds that are formed from hydrolysis and condensation of fluorinated silanes. The samples analyzed in this study were three sludge extracts and one extract from a cosmetic product. 6:2 PTrEtSi was expected to be detected in the cosmetic sample since the compound was stated on the table of contents of the cosmetic product. No detection of 6:2 TrEtSi or 8:2 TrEtSi could be made in either of the samples. The reason for this was suspected to be transformation or degradation of the compounds into other compounds. Therefore, a full scan of the cosmetic sample using LC-MS/MS was included in the experiment as an addition to verify the suspicions that compounds such as siloxanes could have been formed. An interesting peak was discovered with m/z 947 which could be a disiloxane of 6:2 PTrEtSi.

No description available.

<p> Per- and polyfluoroalkyl substances (PFAS) are a class of persistent environmental contaminants that have become ubiquitous, resulting in widespread exposure among humans and wildlife. Amphibians are regularly exposed in the field, making them susceptible to sublethal effects of PFAS exposure. In amphibians exposed to PFAS, deleterious effects have been observed, including reduction in body condition measured using the scaled mass index (SMI) and degraded hepatic condition, among others. PFAS may dysregulate lipid metabolism by altering signaling cascades regulated by peroxisome proliferator activated receptors (PPAR), but whether changes in energy stores can explain changes in amphibian SMI and/or hepatic condition remain underexplored. Since lipids are a critical energy reserve for anurans, understanding whether lipid metabolism is being perturbed is critical. The central objective of this thesis was to investigate the effect of PFAS on lipid homeostasis in <em>Xenopus laevis </em>tadpoles within the context of a PPAR mechanism of action (MOA), considering apical, molecular, and lipidomic endpoints. I conducted three studies: (a) a study to characterize SMI and the relative expression of the hepatic xPPARα/β/γ during metamorphosis, (b) a pharmaceutical exposure to assess the <em>in vivo</em> effects of xPPARα/β/γ agonism on hepatic gene expression for select downstream targets (<em>apoa5, fabp1, acox1,​ pck1</em>), and (c) a chronic PFAS exposure to investigate the effects of environmentally relevant concentrations (PFOS, PFHxS, PFOA, PFHxA at 0.5 ppb; binary mixture of PFOS:PFHxS at 1 ppb) on lipid homeostasis through apical endpoints (mass, snout vent length, SMI, hepatic condition), relative hepatic gene expression, and Multiple Reaction Monitoring (MRM) profiling of the hepatic lipidome for changes in relative class abundance. In study (a), I identified SMI and hepatic expression of <em>xPPARα/β/γ</em> is dynamic during late metamorphosis, indicating the potential for heightened susceptibility. However, in study (b), pharmaceutical agonists had no effect on <em>X. laevis</em> at high doses. For study (c), I did not observe effects on a majority of apical endpoints, including SMI, but detected a significant sex-specific reduction in hepatic condition for male<em> X. laevis</em> tadpoles exposed to single-chemical perfluorosulfonic acid (PFSA) treatments. For gene expression, I observed a transient downregulation for apolipoprotein-V (<em>apoa5</em>) at Nieuwkoop and Faber (NF) stage 62 for <em>X. laevis</em> tadpoles exposed to single-chemical perfluorocarboxylic acid (PFCA) treatments. Lipid profiling detected transient dysregulation of predominantly membrane lipids in-response to short-chain PFAS treatments at NF 58. Overall, our findings indicate PFAS may exert toxicity during anuran metamorphosis through multiple mechanisms of action (MOA) with sex-specific and developmental-stage specific outcomes.</p>

Spridning av läkemedelsrester och andra prioriterade mikroföroreningar i miljön har uppmärksammats och stor oro väckts kring problematiken. Bland observationer som forskare har noterat till följd av antibiotika, hormoner och läkemedel i vattenmiljöer är bland annat bakteriell resistens, könsbyte och sterilitet hos fisk och groddjur. Persistenta föroreningar som per- och polyfluor alkalysyror (PFAS) bryts inte heller ner i naturen och mikroskräppartiklar kan anrikas i vattendrag och orsaka negativa effekter på vattenlevande organismer. Gemensamt för mikroföroreningar är att dessa förekommer oftast i små halter och kan härstamma från olika mänskliga aktiviteter. Avloppsreningsverk (ARV) är inte primärt anpassade för att avskilja mikroföroreningar utan främst för att avlägsna kväve, fosfor och organiskt material. Uppströmsarbete är inte heller tillräckligt effektivt för att avlasta reningsprocessen vilket medför att mängden mikroföroreningar ökar i vattenmiljöer och sätter ytterligare påtryckningar på ARV. Utmaningar som ARV står inför idag med nya mikroföroreningar och förekomsten av dessa i miljön har väckt frågor både nationellt och internationellt. Stockholm Vatten och Avfalls (SVOA) beslut att implementera membranbioreaktor (MBR) på Henriksdals reningsverk av porstorleken 0,04 μm är en åtgärd för att rusta upp inför framtida hydrauliska volymer men även potentiella striktare reningskrav. Fördelen med MBR-processen är att den förhindrar föroreningar som förekommer partikulärt att passera membranen och på så sätt hindras skadliga ämnen att passera reningsprocessen. I dagsläge saknas krav på ARV att rena avloppsvatten från de flesta mikroföroreningar. Det förväntas dock att kommande lagstiftning omfattar läkemedel och andra organiska föroreningar. I detta projekt undersöktes mikroföroreningar i form av läkemedelsrester, antibiotika, hormoner, PFAS och mikroskärp i en MBR-process samt förekomsten av adsorberbara och extraherbara organiska halogener (AOX, EOX) som potentiellt bildas under rengöring av membranen till följd av reningsprocessen. Resultat från detta projekt med MBR-processen visade en generell högre reduktion av prioriterade mikroföroreningar i avloppsvatten än tidigare undersökningar på konventionella ARV, med undantag för några substanser som visade på en liknande sämre reduktion. Läkemedlen diklofenak, oxazepam, citalopram med flera visade på en sämre reduktion och lika så för antibiotikumen clindamycin, claritomycin och erytromycin där reduktionen var negativ och visade på en återkommande trend. Östrogena hormoner reducerades i reningsprocessen och likaså för mikroskräp där 60 partiklar/m3 mikroplast av porstorleken större än 300 μm passerade membranen. Mikroplast av en porstorlek i intervallet mindre än 300 men större än 50 μm passerade 140 partiklar/m3 membranen. För AOX och EOX var halten i MBR-processen typiska och i nivå med tidigare undersökningar genomförda på konventionella ARV. Eftersom membranen inte kan avskilja partiklar på molekylnivå visades sig även att det passerade fortfarande mikroföroreningar som undersöktes. En slutsats från detta projekt är att endast ett få tal ämnen reducerades helt medan majoriteten av de prioriterade mikroföroreningarna reducerades delvis i avloppsvatten. För att kunna reducera dessa prioriterade mikroföroreningar i reningsprocessen ytterligare om striktare reningskrav skulle bli aktuella krävs vidare efterbehandling efter MBR-processen. / Release of pharmaceutical residues and other emerging substances in the environment has been highlighted and raised a great concern regarding the issue. Among observations that scientists have noted as a result of antibiotics, hormones and pharmaceutical residues in the aquatic environment are bacterial resistance, sex change and sterility in fish and batrachians. Persistent pollutants such as perfluorinated-alkylated substances (PFAS) are also not degraded in nature, and microscopic debris particles can be enriched in aquatic systems and cause adverse effects on aquatic organisms. The common aspect with these substances is that they usually occur in small quantities and can derive from different human activities. Wastewater treatment plants (WWTP) are not primarily designed to separate emerging substances of concern (ESOC), but primarily to remove nitrogen, phosphorus and particulate organic matter. Upstream work is also not sufficiently effective to relieve the purification process, which means that the amount of pollutants increases in aquatic environments and puts additional pressure on the WWTP. The challenges facing WWTP today with ESOC and their presence in the environment has raised issues both nationally and internationally. Stockholm Vatten och Avfall (SVOA) decision to implement a membrane bioreactor (MBR) with poresize of 0,04 μm at Henriksdal WWTP is a step to prepare for future hydraulic volumes, but also potentially stricter treatments requirements regarding ESOC. The advantage of the MBR process is that it prevents contaminants that appear to be particulate to pass the membranes and end up in the receiving waters. Today, WWTP are not required to treat wastewater in order to remove pharmaceutical residues, antibiotics, hormones, PFAS or microscopic debris particles. However, it is expected that future legislations will include pharmaceuticals and other organic pollutants. In this project, ESOC such as pharmaceutical residues, antibiotics, hormones, PFAS and microscopic debris in the MBR-process are studied as well as the presence of adsorbable and extractable organic halogens (AOX, EOX) that are possibly formed during the cleaning or maintains of the membranes. Results from this study showed a higher general reduction of the studied ESOCs in wastewater with the MBR-process than previous studies in conventional WWTP, except of some substances that showed a poor reduction. Pharmaceuticals such as diclofenac, oxazepam and citalopram showed a weak reduction as well as the antibiotics clindamycin, clarithromycin and erythromycin where they showed a higher outcome levels than the incoming to the treatment process. Estrogenic hormones were reduced in the purification process as well as microplastics where only 60 particles/m3 of pore size higher than 300 μm passed the membranes. Microplastics of the pore size smaller than 300 and larger than 50 μm were detected to 140 particle/m3 in the effluent water. For AOX and EOX, the level of MBR process showed typical values and were in line with previous studies on conventional ARV. However, since the membranes cannot treat contaminants at molecular level, it was also shown that some ESOC that were studied bypassed the treatment process. A conclusion from this project is that only a few numbers of substances were fully reduced while the majority of ESOCs were partially reduced in wastewater. In order to reduce further ESOCs and in case of stricter treatment were to be applied, additional post-treatment is also needed for the MBR process.

The theoretical part of this diploma thesis consists of current matters regarding the presence of perfluorinated organic compounds in living environment elements. The attention has been focused on perfluoroktanoic acid (PFOA), (PFOS), and (FOSA). Physical-chemical characteristics of these organic pollutants and their toxicological and environmental aspects have been described. Possible ways of the pollutants analytical determination have been specified. The experimental part has explored effects of extraction techniques (sonication, pressurized solvent extraction, solid-phase extraction) used for PFAS separation from seats of fire soil sample. Identification of the analytes have been achieved by liquid chromatography/mass spektrometry.

Im ersten Teil wurde Probenvorbereitungs-Methoden und instrumentelle Methoden zur Organofluor-Bestimmung verglichen, um Vor- und Nachteile bei der Summenparameter-Analytik von per- und polyfluorierten Alkylverbindungen (PFAS) zu identifizieren. Daher wurden Oberflächenwasserproben aus der Spree in Berlin und Industrieabwasserproben mit zwei PFAS-Summenparametern analysiert – dem extrahierbaren (EOF) und dem adsorbierbaren organisch gebundenen Fluor (AOF). Beide PFAS-Summenparameter wurden mit zwei fluorsensitiven Detektionssystemen analysiert – Hochauflösender Kontinuumstrahler-Graphitofen Molekülabsorptionsspektrometrie (HR-CS-GFMAS) und combustion Ionenchromatographie (CIC). HR-CS-GFMAS erwies sich im Vergleich zu CIC als der empfindlichere und schnellere Ansatz mit höherer Präzision. Im zweiten Teil wurde eine neue Methode zur PFAS-Summenparameteranalyse und EOF-Bestimmung in Bodenproben auf Basis von HR-CS-GFMAS entwickelt und optimiert. EOF-Massenanteile wurden bei mehrfacher Extraktion und Nutzung der Festphasenextraktion (SPE) zur Entfernung anorganischen Fluors untersucht. Bei einem Vergleich der optimierten Methode mit und ohne SPE zeigte sich eine drastische Diskriminierung von Organofluor-Verbindungen mittels SPE. Im dritten Teil wurden Organofluor-Massenbilanzen in aquatischen Systemen anhand von Oberflächenwasser- und Schwebstoffproben (SPM) untersucht. SPM-Proben wurden mit vier komplementären Analysemethoden analysiert – target und non-target, direct total oxidizable precursor assay (dTOPA) und EOF. Daher wurden drei Organofluor-Massenbilanzansätze für die räumlich und zeitaufgelöste SPM-Probenanalyse verwendet: (I) Identifizierung von oxidierbaren PFAS-Vorläufer, (II) Identifizierung des Anteils der identifizierten und nicht identifiziertes EOF und (III) PFAS-target, PFAS dTOPA, non-target-Screening und EOF-Analyse, um das nicht identifizierte EOF aus Ansatz (II) weiter zu entschlüsseln. / In the first part, a comparison of sample preparation and instrumental methods for organofluorine determination was used to identify advantages and disadvantages in sum parameter analysis of per- and polyfluoroalkyl substances (PFASs). Therefore, surface water samples from the Spree River in Berlin, Germany and industrial effluent samples were analyzed using two PFAS sum parameters – the extractable (EOF) and adsorbable organically bound fluorine (AOF). Both PFAS sum parameters were analyzed using two fluorine sensitive detection systems – high-resolution-continuum source-graphite furnace molecular absorption spectrometry (HR-CS-GFMAS) and combustion ion chromatography (CIC). HR-CS-GFMAS turned out to be the more sensitive and faster approach accompanied with higher precision compared to CIC. In the second part, a new method for PFAS sum parameter analysis and EOF determination in soil samples based on HR-CS-GFMAS was developed and optimized. EOF mass fractions were investigated upon multiple extraction and utilization of solid phase extraction (SPE) for inorganic fluorine removal. In a comparison of the optimized method with and without SPE, a highly biased discrimination of organofluorines using SPE was shown. In the third part, organofluorine mass balances were investigated in aquatic systems using surface water and suspended particulate matter (SPM) samples. SPM samples were analyzed using 4 complementary analytical methods – target and non-target HRMS, direct total oxidizable precursor assay (dTOPA) and EOF. Therefore, 3 organofluorine mass balance approaches were used for SPM sample analysis in spatial and time resolved manner: (I) Identification of oxidizable PFAS precursors, (II) Identification of the proportion of identified and unidentified EOF and (III) PFAS target, PFAS dTOPA, non-target screening and EOF analysis to further unravel the unidentified EOF from approach (II).

Les estuaires sont des écosystèmes aquatiques particulièrement soumis au changement global et notamment à la pollution par de nombreux xénobiotiques pouvant présenter un risque écotoxicologique et sanitaire. En toxicologie environnementale et en évaluation des risques la bioaccumulation est un processus fondamental car elle contrôle les doses internes de toxiques potentiels. Or les flux de contamination et de décontamination des organismes dépendent de processus internes (e.g. nutrition, croissance) eux-mêmes dépendant des conditions environnementales (e.g. température, nourriture) qui peuvent être affectées par le changement global.Dans ce contexte, cette thèse se propose de décrire, dans un cadre de modélisation mécaniste, les processus de bioaccumulation de deux familles de polluants organiques persistants (POP) halogénés potentiellement toxiques et bioaccumulables, aux propriétés physico-chimiques contrastées : les polychlorobiphényles (PCB, composés historiques fortement lipophiles) et les substances perfluorées (PFAS, composés émergents amphiphiles). Ce travail se focalise sur l’estuaire de la Gironde dont la fonction de nourricerie est fondamentale pour de nombreuses espèces de poissons marins dont la sole commune (Solea solea), souvent utilisée comme indicatrice de la qualité des nourriceries côtières et estuariennes.Pour permettre de tenir compte des fluctuations des conditions environnementales sur la bioaccumulation, dans la première partie de ce travail, j’ai développé un modèle de toxicocinétique(TK) couplé avec un modèle mécaniste bioénergétique basé sur la théorie DEB (Dynamic Energy Budget). Ce modèle DEB a été paramétré pour la sole commune et calibré pour chaque sexe (package DEB tool). Il permet de prédire les principales évolutions des fonctions physiologiques d’intérêt en bioaccumulation (ingestion, croissance, reproduction...), tout au long du cycle de vie d’un individu, en fonction de conditions environnementales dynamiques. Le modèle TK développé a été complexifié par l’ajout d’un flux d’élimination de contaminants, non considéré dans les précédents modèles DEB-TK.La calibration des paramètres toxicocinétiques (TK) du modèle, pour 4 congénères de PCB, est basée sur une méthode innovante de prise en compte de la variabilité individuelle d’ingestion, appliquée à une expérimentation de contamination de juvéniles de sole via leur nourriture. Ce travail a montré que même en tenant compte de l’ingestion de chaque poisson, l’assimilation efficace de contaminant était très variable et corrélée aux taux de lipides des individus. Dans une seconde partie, ce modèle a été appliqué aux conditions in situ de l’estuaire de la Gironde. Il a permis de mettre en évidence la forte influence de la composition du régime alimentaire sur la variabilité de l’âge à la maturité sexuelle et de la contamination des soles pour les deux familles de contaminant étudiées. La confrontation des prédictions du modèle aux mesures de contaminants dans les juvéniles de sole de l’estuaire a permis de calibrer les paramètres TK du composé majeur de chaque famille dans l’environnement (CB153 et PFOS). Cette calibration a conduit à deux constats dans le cadre de l’évaluation du risque : (1) un manque de connaissances pour extrapoler les calibrations de paramètres TK en conditions contrôlées vers les conditions naturelles ; (2) la différence d’erreur d’évaluation du risque liée à l’utilisation des mêmes paramètres TK «les plus pessimistes » quels que soient les composés. Enfin, des scenarios prospectifs simples ont été développés pour illustrer ces résultats et les possibles applications du modèle développé.In fine, ces prédictions de la contamination, de la croissance et du développement des soles pourront être reliées, lors de travaux ultérieurs, à des effets potentiels sur les fonctions physiologiques de la sole (modèles DEBtox), et aux conséquences sur la dynamique des populations de soles (e.g.modèles matriciels de population). / Estuarine ecosystems are particularly impacted by global change and, specifically, bychemical pollution from numerous xenobiotics that may be associated to ecotoxicological and health risks. In environmental toxicology and risk assessment, bioaccumulation is a fundamental process as it controls the internal doses of potential toxicants in organisms. However, the contamination and decontamination flows depend on internal processes thatare themselves dependent on environmental conditions (e.g. temperature, food) and thus on the other variables of global change.In this context, this manuscript aims at describing, within a mechanistic modelling framework, the bioaccumulation processes of two families of potentially toxic and bioaccumulable halogenated persistent organic pollutants (POPs) with contrasting physicochemical properties: the polychlorinated biphenyls (PCBs, highly lipophilic historical compounds) and the perfluorinated substances (PFAS, amphiphilic emerging compounds).This work focuses on the Gironde estuary whose nursery function is fundamental for many species of marine fish including the common sole (Solea solea), often used as an indicator of the quality of coastal and estuarine bursary grounds. In order to account for the influence of environmental conditions on bioaccumulation, the first part of this work consisted in developing a toxicokinetic model (TK) coupled with a mechanistic bioenergetic model based on the theory DEB (Dynamic Energy Budget). This DEBmodel has been parameterized for common sole and calibrated for each sex (packageDEBtool). It allows predicting the main evolution of the physiological functions of interest forbioaccumulation (ingestion, growth, reproduction...) throughout the life cycle of an individualaccounting for dynamic environmental conditions. The developed TK model was first calibrated for some PCBs, under controlled conditions, using an innovative method to take into account individual ingestion variability. This work showed that even if the individual ingestion of each fish is accounted for, the effective assimilation of contaminant is very variable and correlated with the lipid levels of the individuals. The application of the model tothe in situ conditions of the Gironde estuary led to identify that, whatever the contaminant family, the composition of the soles diet had a strong influence on the variability of soles contamination and age at sexual maturity. The comparison of model predictions with measurements made in juveniles of the estuary allowed calibrating the TK parameters values for the major compound of each family in the environment (CB153 and PFOS). This calibration led to two observations in the context of a risk assessment: (1) a lack of knowledge to extrapolate calibrations of TK parameters under controlled conditions to natural conditions;(2) the difference in risk assessment error related to the use of the same "worst case" TK parameters regardless of the compounds. Lastly, simple prospective scenarios have beendeveloped to illustrate these results and the possible applications of the model developed.Ultimately, these predictions of soles contamination, growth and development may be related in future work to potential effects on the physiological functions of sole (DEBtox models), and to consequences on soles population dynamics (e.g. matrix population models).

Perfluoroalkyl substances (PFASs) are global environmental contaminants and a need for monitoring levels has arisen due to their persistency and their ability to bioaccumulate. One relatively novel method of monitoring for both long and short time intervals and generating time-weighted average (TWA) concentrations is passive sampling for which no power, maintenance and supervision is required. The polar organic compound integrative sampler (POCIS) with a weak anion exchange (WAX) sorbent and the POCIS with a hydrophilic-lipophilic balance (HLB) adsorbent were calibrated for PFASs in a laboratory uptake experiment, and applied at a drinking water treatment plant (DWTP) in Stockholm, Sweden.   In the calibration study, all of the 14 studied PFASs were taken up by both passive samplers. Two and three out of the 14 studied PFASs had reached equilibrium after 28 days using POCIS WAX (PFBA and PFTeDA) and POCIS HLB (PFBA, PFPeA and PFTeDA), respectively. The sampling rate (Rs), which is the extracted water in liters per day, ranged between 0.003 and 0.10 L day-1 for the POCIS WAX and between 0.00052 and 0.13 L day-1 for the POCIS HLB. In general, Rs increased with increasing perfluorocarbon chain-length (C4 to C8) and for a perfluorocarbon chain-length longer than C8, Rs decreased with increasing perfluorocarbon chain-length (C8 to C13) for both passive samplers. FOSA had the highest Rs-value (0.10 and 0.13 L day-1) for both POCIS WAX and POCIS HLB, respectively. The POCIS WAX had a higher uptake for the short-chained PFASs PFBA (134 ng after 28 days), PFPeA (410 ng) and PFHxA (834 ng), compared to the POCIS HLB (0.5 ng, 58 ng, and 373 ng, respectively). For all other compounds, the accumulated amounts in the POCIS HLB were in the same range as in the POCIS WAX.   The application of the passive samplers at the DWTP showed that both passive samplers could detect ultra-trace (pg to ng L-1) levels of PFASs. A comparison of the TWA concentration showed that the two passive samplers had a good linear correlation (R2 = 0.63), but the TWA concentrations derived by POCIS WAX was approximately 40% higher compared to POCIS HLB. A comparison between the passive samplers and the grab samples did not show a correlation (R2 = 0.24 for POCIS WAX and R2 = 0.10 for POCIS HLB). The application also included a comparison of the removal efficiency in the conventional DWTP and a pilot plant with additional treatments steps of granulated activated carbon (GAC) and nanofiltration (NF). For the full-scale DWTP the average removal efficiency was 32% and high removal efficiency was observed for PFBA (81%). For the pilot plant, the removal efficiency was 100% for all the detected PFASs in the raw water. / Perfluoroalkylsubstanser (PFAS) har blivit uppmärksammade som globala miljöföroreningar, och ett behov av att övervaka dessa ämnens förekomst i miljön har uppkommit på grund av hög persistens i kombination med hög förmåga att bioackumulera. En relativt ny metod för tidsintegrerad provtagning är så kallad passiv provtagning. En adsorbent placeras i fält och ackumulerar PFAS från vattnet. Tillgång till elektricitet behövs inte, och behov av övervakning och underhåll är minimalt. I denna studie kalibrerades en så kallad ’polar organic compound integrative sampler’ (POCIS) för mätning av PFAS genom upptagsexperiment med två olika adsorbenter: en svag anjons adsorbent (WAX) och en hydrofil-lipofil balanserad adsorbent (HLB). Metodiken tillämpades sedan på vatten från ett dricksvattenverk i Stockholm, Sverige.   Upptagsexperimenten utfördes med 14 PFAS och samtliga togs upp av båda adsorbenterna. Två respektive tre av de studerade PFAS uppnådde jämvikt efter 28 dagar för WAX (PFBS och PFTeDA) samt HLB (PFBA, PFPeA och PFTeDA). Upptagshastigheten (Rs), det vill säga den volym som extraheras per dag, varierade mellan 0,003 och 0,1 L dag-1 för WAX och mellan 0,00052 och 0,13 L dag-1 för HLB. Generellt ökade Rs med en ökande längd på kedjan av perfluorerade kol upp till C8, för att sedan avta med ökande kedjelängd. FOSA hade det högsta Rs-värdet (0,10 och 0,13 L dag-1) för både WAX och HLB. WAX hade ett högre upptag (upp till 134, 410 och 834 ng) för PFAS med kort perfluorerad kolkedja (PFBA, PFPeA respektive PFHxA) jämfört med HLB (upp till 0,5, 58, och 373 ng). Den ackumulerade mängden för alla andra PFAS överensstämde väl mellan de båda provtagarna.   Mätning av PFAS halter i dricksvattenverket med hjälp av POCIS WAX och POCIS HLB visade att även PFAS kunde detekteras även vid miljörelevanta halter. En jämförelse mellan de båda passiva provtagarna visade på ett linjärt samband (R2 = 0,63), men där POCIS WAX hade en tendens att överskatta koncentrationen med ca 40%. En jämförelse mellan de passiva provtagarna och traditionell uppsamlingsprovtagning visade på låg överrensstämmelse (R2 = 0.24 för POCIS WAX och 0.10 för POCIS HLB). Vid tillämpningen gjordes även en beräkning för reningseffektiviteten av PFAS i dricksvattenverket och i en pilotanläggning där ytterligare rening med granulerat aktivt kol (GAC) och nanofiltration (NF) används. I dricksvattenverket var den genomsnittliga reningen 32%, med den högsta reningseffektiviteten för PFBA (81%). I pilotanläggningen var reningen 100% för alla upptäckta PFAS i råvattnet.

The Methodology for inventory of contaminated sites (MIFO) is a method designed by the Swedish Environmental Protection Agency with an aim to facilitate agents and consultants during inventory of contaminated areas. It is structured into two stages, the first phase comprises oriented studies of the area while the second one consists of conceptual studies, such as field testing and analysis. After each phase the object is assigned a risk class that describes the degree of contamination and the risk associated with it. At Sundsvall-Timrå airport, the soil, surface- and groundwater at two fire drilling sites are contaminated with the anthropogenic substance PFOS, a former supplement in extinguishing foam. As a result of this, a number of environmental investigations have occurred over the past seven years which has led to a substantial amount of data in regards to the degree and dispersion of the contamination. However, prior to this date no risk classification according to MIFO phase 2 has been done. In order to appropriately remediate the site, it is essential that this step of the process is completed. Thus the County Administrative Board of Västernorrland in Sweden commissioned this thesis for the purpose of risk classifying Sundsvall-Timrå Airport. This was done by analysing the results from previous environmental investigations made by WSP Environmental and comparing them to the Swedish Geological Institute’s preliminary benchmark value for PFOS. The fact that Sundsvall-Timrå airport is situated in close approximation to a nature reserve and due to the high degree of contamination together with the substance distribution capabilities and high toxicity, the study resulted in the object being assigned risk class 1, very high risk. / Syftet med detta självständiga arbete var att på uppdrag av Länsstyrelsen i Västernorrland göra en MIFO fas 2 riskklassning av ett förorenat område vid Sundsvall-Timrå flygplats. MIFO (Metodik för inventering av förorenade områden) är en metodik framtagen av Naturvårdsverket med ändamålet att vägleda ombud och konsulter vid inventeringar av förorenade områden. Metoden är uppdelad i två steg, fas 1 och fas 2. Den första fasen involverar orienterade studier av området och den andra består av översiktliga studier, som till exempel fältundersökningar och analyser. Efter var fas tilldelas objektet en riskklass utifrån hur allvarlig föroreningssituationen bedöms vara. På Sundsvall-Timrå flygplats är marken, yt- och grundvattnet vid två brandövningsplatser förorenat med det antropogena ämnet PFOS som brukade ingå i släckskum. Som följd till detta har ett flertal miljötekniska mark- och grundvattenundersökningar gjorts i området under de senaste sju åren. Detta har lett till ett betydande underlag av data beträffande halt och spridning av föroreningen men fram tills nu har ingen fas 2 riskklassning av brandövningsplatserna med avseende på PFOS gjorts. Avsikten med arbetet var således att med hjälp av resultaten från tidigare miljötekniska undersökningar och SGIs preliminära riktvärden för PFOS, tilldela objektet en riskklass. Då Sundsvall-Timrå flygplats ligger intill Indalsälvens naturreservat, föroreningsnivån vid brandövningsplatserna anses vara mycket stor samt det faktum att PFOS har höga spridningsförutsättningar och toxicitet, resulterade studien i att området tilldelades riskklass 1, vilket innebär mycket stor risk.

Per- and polyfluorinated substances (PFAS) are compounds that consist of a carbon chainbackbone that is partially or entirely fluorinated, with an addition of a functional group. SomePFAS are known as persistent organic pollutants (POPs) and have therefore been drawing a lot ofattention as well as increased concerns. PFAS have been detected in humans, wildlife and theenvironment and some have exhibited toxic effects such as hepatotoxicity, immunotoxicity,reproductive toxicity and endocrine disruption as well as being persistent and bioaccumulative.Serum, plasma and whole blood have been used as biomonitoring matrices in many studies toevaluate human exposure to PFAS. Restrictions have been applied to some PFAS, but thesecompounds are still ubiquitous. This study will investigate the performance (recovery, matrixeffect (ME) in terms of intra-/inter-day repeatability) of ion-pair extraction (IPE) and solid phaseextraction with weak anion exchange (SPE-WAX). The extraction methods were adapted fromliterature and 13 PFAS were selected for this work based on prior biomonitoring studies. Thetarget PFAS content was analyzed with liquid chromatography coupled with tandem massspectrometry (LC-MS/MS). The extraction methods were also compared for extractableorganofluorine (EOF) extraction in terms of blank levels as well as the amount extracted withdifferent methods; the EOF content was measured with combustion ion chromatography (CIC).The EOF levels were used to estimate the amount of unidentified organofluorine (UOF), to avoidunderestimating potential health hazards. Samples extracted using IPE had an average ionizationenhancement of 9%, while SPE-WAX showed an average ionization suppression of -1%. SPEWAXshowed higher average recoveries for procedural blanks (78%), horse serum (96%) andhuman serum (95%) in comparison to IPE (69%, 36%, 88%, respectively). The CIC analysis forEOF content was observed to be below MDL (&lt;50 ng/mL F) with some contaminations observedin the procedural blanks.