京都大学 / 0048 / 新制・課程博士 / 博士(地球環境学) / 甲第18628号 / 地環博第123号 / 新制||地環||25(附属図書館) / 31528 / 京都大学大学院地球環境学舎環境マネジメント専攻 / (主査)教授 藤井 滋穂, 教授 梶井 克純, 准教授 田中 周平 / 学位規則第4条第1項該当 / Doctor of Global Environmental Studies / Kyoto University / DFAM

Objectives: This study aimed to examine the association of Per and Polyfluoroalkyl substances (PFAS) and markers of chronic inflammation and oxidative stress. Methods: Using data (n = 6652) from the National Health and Nutrition Examination Survey (NHANES) 2005–2012, generalized linear models were used to examine the association between PFAS and inflammatory (ferritin, alkaline phosphatase, C-reactive protein, absolute neutrophil count and lymphocyte count) and oxidative stress (serum bilirubin, albumin and iron) per unit exposure to PFAS while adjusting for covariates. Study participants were those ≥20 years of age. Outcome variables were markers of chronic inflammation and oxidative stress and exposure variables were PFAS. Resullts: Percentage change in Perfluorohexane sulfonic acid (PFHxS), Perfluorononanoic acid (PFNA), Perfluorooctanoic acid (PFOA), Perfluorooctane sulfonic acid (PFOS), and Perfluorodecanoic acid (PFDA) were all significantly associated with percentage increases in lymphocyte counts, beta (95% confidence interval); 0.04(0.02,0.05), 0.04(0.02,0.05), 0.05(0.03, 0.07), 0.04(0.03,0.05), 0.03(0.13,1.23) and with percentage increases in serum iron 0.07(0.05,0.09), 0.04(0.02,0.07), 0.10(0.07,0.12), 0.05(0.03,0.07), 0.04(0.02,0.06) and increased serum albumin 0.02(0.02,0.02), 0.02(0.02,0.03), 0.03(0.03,0.04), 0.02(0.017, 0.025), 0.01 (0.01, 0.05). Only PFHxS, PFNA, PFOA and PFOS were associated with percentage increases in serum total bilirubin 0.04(0.03,0.05), 0.02(0.00,0.03), 0.06(0.04,0.08), 0.03(0.02,0.05). Similar results were obtained for categorical quintile analysis with PFOA showing a significant trend (P < 0.001) with lymphocyte count, serum iron, serum total bilirubin and serum albumin. Trend for neutrophil count was not significant (p = 0.183). Conclusion: Per and Polyfluoroalkyl substances are associated with markers of chronic inflammation and oxidative stress. Increased exposure leads to increase in serum concentration of these markers meaning these chemicals are associated with both chronic inflammation and oxidative stress.

Today there are many uncertainties in the form of a lack of knowledge about perfluorinated and polyfluorinated substances (PFAS) regarding long-term risks to health and the environment, there is no efficacy data for many environments. The fluorocarbon bond is the strongest chemical bond, which means that PFAS can be transported long distances, for example through water streams and into the atmosphere. If surface water and groundwater are contaminated by PFAS, people are at risk of exposure to PFAS through the drinking water. It is therefore important to investigate and identify what difficulties and opportunities the municipalities see in their work to influence and reduce the occurrence of PFAS in drinking water with PFAS in water revenues and drinking water. The purpose of the study is to map what Halmstad, Linköping and Uppsala municipality see for difficulties and opportunities in their work on influencing and reducing the occurrence of PFAS in drinking water and how the result relates to scientific research about national environmental management. We have chosen to do a qualitative interview with an analysis of the interview using previous research on national environmental management about actions, cooperation and policy, directives, guidelines, and legislation. Some of the conclusions the study came to where that the municipalities see similar difficulties and opportunities in working with PFAS and have similar ways of working with PFAS. But there are still some differences and similarities in what they see for difficulties and opportunities in their work with PFAS. Difficulties that have been identified are inadequate or unclear guidelines, directives, legislation and insufficient limit values. It is also a difficulty that the municipalities do not know where all sources of PFAS pollution come from. Opportunities that have been identified are collaborations, knowing where certain parts of PFAS's pollution come from. One possibility that exists is to influence certain polluting activities by means of distribution routes, to submit activities to improve purification methods and to set requirements for sampling and remediation. / Det finns idag många osäkerheter i form av bristande kunskap om perfluorerade och polyfluorerade ämnen (PFAS) när det gäller långsiktiga risker mot hälsa och miljö, det saknas effektdata för många miljöer. Fluor-kol-bindningen är den starkaste kemiska bindningen vilket leder till att PFAS kan transporteras långa vägar, genom till exempel vattenströmmar och i atmosfären. Om ytvatten och grundvatten blir förorenat av PFAS så riskerar människor att exponeras för PFAS genom dricksvattnet. Det är därför av vikt att undersöka och identifiera vad för svårigheter och möjligheter kommunerna ser med sitt arbete med att påverka och minska förekomsten av PFAS i dricksvatten med PFAS i vattentäkter och dricksvatten. Syftet med studien är att kartlägga vad Halmstad, Linköping och Uppsala kommun, ser för svårigheter och möjligheter i sitt arbete med att påverka och minska förekomsten av PFAS i dricksvatten och hur resultatet förhåller sig till vetenskaplig forskning om nationell miljömanagement. Vi har valt att göra en kvalitativ intervju med en analys av intervjun med hjälp av tidigare forskning om nationell miljömanagement med avseende på åtgärder, samarbete och direktiv, riktlinjer och lagstiftning. Några av slutsatserna studien kom fram till var att kommunerna ser liknande svårigheter och möjligheter i arbetet med PFAS och har liknande sätt att arbeta med PFAS på. Men det finns ändå en del skillnader och likheter i vad de ser för svårigheter och möjligheter i deras arbete med PFAS. Svårigheter som har identifierats är otillräckliga eller otydliga riktlinjer, direktiv, lagstiftning och otillräckliga gränsvärden. Det är även en svårighet att kommunerna inte vet vart alla källor av PFAS-föroreningar kommer från. Möjligheter som har identifierats är samarbeten, att veta vart vissa delar av PFAS föroreningar kommer från. En möjlighet som finns är att påverka vissa förorenande verksamheter genom spridningsvägar, förelägga verksamheter att förbättra reningsmetoder och sätta krav på provtagning och sanering.

The overall goal of this research is to synthesize two different monomers for proton exchange membrane (PEM) Fuel Cells. Such monomers are proposed to be polymerized to improve the efficiency and compatibility of electrodes and electrolytes in PEM fuel cells. The first target is to synthesize 4-diazonium-3-fluoro PFSI zwitterionic monomer. Three steps were carried out in the lab. First one was the ammonolysis of 3-fluoro-4-nitrobenzenesulfonyl chloride. Second reaction was the bromination of Nafion monomer. The next coupling reaction, between brominated Nafion monomer and the 3-fluoro-4-nitrobenzenesulfonamide, was failed. The obstacles involve the harsh reaction condition and troublesome purification procedure. The second target is to synthesize 5-nitro-1, 3-benzenedisulfonamide. According to the literature, this synthesis was also designed as three steps: 1)nitration of sodium 1, 3-benzenedisulfonate salt; 2)chlorination of sodium 5-nitro-1, 3-benzenedisulfonate salt; and 3)ammonolysis of 5- nitro-1, 3- benzenedisulfonyl chloride. This monomer is expected to be copolymerized for membrane electrolyte in PEM fuel cells.

Perfluoroalkyl substances (PFASs) are contaminants of emerging concern, and have been detected in drinking water, wildlife, humans, and the environment. Cyclodextrins (CDs), cyclic sugars composed of glucose monomers, are proposed as a potential remediation strategy. CDs can form host-guest complexes with hydrophobic molecules; this complexation could be capitalized on for PFAS removal and sequestration. These dissertation projects aim to study the fundamental host-guest interactions between a variety of PFASs and CDs for eventual applications in environmental and biological remediation. 1D and 2D Nuclear magnetic resonance (NMR) spectroscopic methods were employed to determine the strength, dynamics, and structure of the CD:PFAS host-guest complexes. Legacy and emerging PFASs were studied with the three native CDs (α-, β-, and γ-CDs) as well as β-CD derivatives. β-CD and its derivatives exhibit the strongest complexation with all studied PFASs, with association constants of 102-105 M-1, depending on PFAS chain length, functional groups, and branching. The host-guest complex was not significantly disturbed under different environmental conditions, such as changing pH, ionic strength, and in the presence of humic acid. A competition study between perfluorooctanoic acid (PFOA), β-CD, and human serum albumin (HSA), the most abundant protein in blood serum, was then conducted using NMR, circular dichroism, and fluorescence spectroscopies. Excess β-CD was able to totally reverse all PFOA binding to HSA. Finally, the host-guest complex was studied within a biological organism to test its viability as a remediation strategy. The attenuation of the toxicity of PFOA in zebrafish embryos, a model organism for toxicology studies, was tested with β-CD. Excess β-CD increased the LC50 (lethal concentration for 50 % of the population) of PFOA compared to PFOA in the absence of β-CD (p < 0.0001). These dissertation projects suggest that the encapsulation of PFASs by CDs has potential in PFAS remediation strategies.

Les substances poly- et per-fluorées (PFAS), exclusivement d’origine anthropique, sont de nos jours largement utilisées dans diverses applications industrielles et domestiques. La synthèse des PFAS engendre leurs rejets dans l’environnement, où ces composés se retrouvent aussi bien dans l’atmosphère que dans les milieux terrestres et aquatiques. Les études de distribution environnementale, relativement récentes, ont montré la bioaccumulation de certains PFAS chez les vertébrés aquatiques. La toxicocinétique (TK) des PFAS est particulière en raison de leurs propriétés physico-chimiques. Même si les études de TK de ces composés sont de plus en plus nombreuses, quelques verrous mécanistiques restent encore à lever chez les vertébrés aquatiques, notamment concernant les processus d’absorption, de distribution et d’élimination. Dans l’optique d’améliorer ces connaissances, un modèle toxicocinétique à base physiologique (PBTK) a été développé pour décrire le devenir de trois PFAS appartenant à la famille des perfluoroalkyles : le perfluorooctane sulfonate (PFOS), le perfluorohexane sulfonate (PFHxS) et l’acide perfluorononanoïque (PFNA). Ce modèle PBTK s’appuie sur les paramètres physiologiques de la truite arc-en-ciel (Oncorhynchus mykiss) et a permis de tester plusieurs hypothèses mécanistiques de la bioaccumulation des PFAS, utile à l’évaluation du risque engendré par l’exposition à ces substances. La croissance et la température de l’eau, facteurs clés dans la TK des poïkilothermes, ont également été intégrées dans le modèle. Les trois expériences d’exposition aux PFOS, PFHxS et PFNA par voie alimentaire à différentes températures (7°C, 11°C et 19°C) réalisées au cours de cette thèse ont permis (i) de mesurer les concentrations dans les organes d’intérêt et (ii) de calibrer et évaluer les prédictions du modèle / Poly- and per-fluorinated substances (PFAS), exclusively derived from anthropogenic activity, are nowadays widely used for industrial and domestic purposes. During their synthesis, PFAS are released in the atmosphere as well as in aquatic and terrestrial compartments. Environmental distribution studies are relatively recent and have shown the bioaccumulation of some PFAS in aquatic vertebrates. Physico-chemical properties of PFAS lead to a specific toxicokinetic (TK) profile. Although TK studies on these compounds are becoming more and more abundant, some mechanistic challenges still need to be solved for aquatic vertebrates, particularly for absorption, distribution and elimination processes. In order to improve this knowledge, a physiologically based toxicokinetic (PBTK) model has been developed to describe the fate of three PFAS belonging to the perfluoroalkyl family: perfluorooctane sulfonate (PFOS), perfluorohexane sulfonate (PFHxS) and perfluoronanoic acid (PFNA). This PBTK model was parametrized with rainbow trout (Oncorhynchus mykiss) physiological parameters. Next, it was used to test several mechanistic hypotheses about PFAS bioaccumulation, useful for improving the risk assessment of these chemicals. Fish growth and water temperature are key factors in the TK for poikilotherms. So, they have been integrated in the model. Three experiments of dietary exposure to PFOS, PFHxS and PFNA at different temperatures (7°C, 11°C and 19°C) have been performed. They allowed (i) to measure concentrations in organs of interest and (ii) to calibrate and evaluate the model predictions

Nous avons étudié la stabilisation de microbulles d’air par les tensioactifs semi-fluorés CF3(CF2)n-1(CH2)mOP(O)(OH)2 (FnHmPhos, où n = 8, 10, m = 2) et des nanoparticules magnétiques d’oxyde de fer et de ferrite de cobalt. Ces nouveaux objets combinant propriétés acoustiques et magnétiques pourraient servir d’agent de contraste à la fois en échographie et en imagerie IRM. Nous avons étudié des propriétés physico-chimiques des tensioactifs en solution et à l’interface aireau. Nous avons montré par tensiométrie dynamique et par des études de films de Langmuir que les tensioactifs F8H2Phos et F10H2Phos forment des monocouches dont le module élastique est très élevé, ce qui favorise la stabilisation de bulles de petite taille ainsi que de bulles non-sphériques. Nous avons proposé une approche de dégonflement/gonflement contrôlé en faisant varier la pression dans la bulle par la température et nous avons étudié le froissement de la paroi des bulles pendant le dégonflement. Des microbulles portant des nanoparticules ont été obtenues dans une suspension des nanoparticules d’oxyde de fer ou de ferrite de cobalt en présence de F8H2Phos ou F10H2Phos, en déstabilisant la suspension par NaCl, ce qui permet de diminuer la barrière électrostatique entre les nanoparticules et la surface des bulles et de favoriser l’adsorption. Les microbulles obtenues sont stables pendant plus d’une semaine grâce à la paroi rigide des nanoparticules. / The stabilization of air microbubbles by semi-fluorinated surfactants CF3(CF2)n-1(CH2)mOP(O)(OH)2 (FnHmPhos, where n = 8, 10, m = 2) and iron oxide nanoparticles was studied in order to design novel microbubbles that possess both acoustical and magnetic properties. Such microbubbles have potential applications as dual constrast agents by enhancing the signals from both ultrasonography and MRI imaging. We have studied physic-chemical properties of the surfactants in solution and at water-air interface. We have demonstrated by dynamic tensiometry and studies of Langmuir monolayers that F8H2Phos and F10H2Phos form highly elastic interfacial films that are favorable for long-term stabilization of small bubbles and bubbles of non-spherical shape. We designed an approach of temperature-controlled pumping/shrinking of the microbubbles and demonstrated the correlation of the collapse structures of the bubble shell with microbubble stability. The stabilization of microbubbles by iron oxide or cobalt ferrite nanoparticles was achieved by destabilizing the nanoparticle suspension in the presence of F8H2Phos or F10H2Phos. Under these conditions the nanoparticles were adsorbed onto the surface of the microbubbles forming a rigid shell which enhanced their stability and lengthened their lifetime to greater than one week.

No description available.

Ion exchange chromatography (IC) is an analytical technique used to separate charged molecules including ions, proteins, small nucleotides, and amino acids. It can function in anion or cation mode. In this dissertation, anion exchange chromatography was used, and column materials were made in our lab with resorcinarene-based compounds called cavitands. Cavitands create cavities to bind to molecules because of their three-dimensional structure. Two new gradient IC methods were established to identify and quantify perrhenate and perfluoroalkyl substances (PFAS) by customized resorcinarene-based column, zinc cyclen resoecinarene (ZCR) and arginine methyl ester (RUE) columns. The ZCR column accomplished outstanding separation of perrhenate from other anions such as chloride and sulfate by using a gradient elution of 2-60 mM NaOH. There was a logarithmic relationship between the perrhenate concentration and its retention time. In addition to separating anions, the ZCR column was able to preconcentrate perrhenate with over 90% recovery in different conditions. RUE was successfully synthesized and attached to polystyrene resin and used in IC to separate the PFAS, perfluorobutanoic acid (PFBA), perfluoropentanoic acid (PFPeA), perfluorobutanesulfonic acid (PFBS), perfluorohexanoic acid (PFHxA), perfluorohexanesulphonic acid (PFHxS), and perfluorooctanoic acid (PFOA). The sample preparation for the PFAS was simple and only needed filtration. A gradient method starting with 70 mM NaOH and going to pure water was necessary to separate the PFAS. There was no detectable PFAS in Provo tap water and Utah Lake water by our method. Although the LOD and LOQ of PFAS were not as low as the existing methods, the IC method does not require complicated sample preparation steps to separate and quantify PFAS. Binding studies of RUE and RUA were done with organic acids, including citric, malic, and succinic acid, and PFAS including PFBA, and PFHxA. The strongest binding was for L-malic acid followed by succinic acid, D-malic acid, pentanoic acid, citric acid, and dimethyl L-malate. RUE displayed some chiral recognition between L-malic acid and D-malic acid. Unfortunately, it did not show significant differences in binding between the different PFAS even though RUE had been able to separate them by IC.

Poly- and perfluoroalkyl substances (PFAS) are ubiquitous contaminants across the globe, can bioaccumulate in aquatic taxa, and potentially biomagnify in food webs. Consequently, research examining the influence of PFAS on wildlife is warranted. Amphibians are sensitive to contaminants such as PFAS because of their porous skin and associations with aquatic habitats where contaminants accumulate. Because PFAS tend to bioaccumulate and can adversely affect the endocrine system, there is a need to examine uptake rates to inform ecotoxicology studies, as well as a need to examine sublethal effects. To address these knowledge gaps I conducted two experiments. First, I exposed larval northern leopard frogs (<i>Rana pipiens</i>), American toads (<i>Anaxyrus americanus</i>), and eastern tiger salamanders (<i>Ambystoma tigrinum</i>) to PFAS chemicals perfluorooctanoic acid (PFOA) or perfluorooctane sulfonate (PFOS) at concentrations of 10 or 1000 ppb for 10 days and sampled them every 48 hours during the exposure period. In the next experiment, I examined the effects of PFAS exposure via contaminated substrate on the survival and growth of post metamorphic amphibians of the same species. I found that, for all species, body burdens often reached steady state within 48 to 96 h of exposure. Steady-state body burdens of PFOA ranged from 3,819–16,481 ng/g dry weight among treatments and species (corresponding BCFs of 0.5 to 2.5), while PFOS body burdens ranged from 6,955–489,958 ng/g dry weight (corresponding BCFs of 47–259) among treatments and species. These data suggest that steady state is rapidly reached in larval amphibians exposed to PFAS, particularly regarding PFOS. This reflects a high potential for trophic transfer of PFAS within food webs because amphibians are often low in trophic position and are important prey for many aquatic and terrestrial species. In post-metamorphic amphibians, there was no influence of PFAS on survival or mass. However, significant effects on snout-vent length were observed in all species, and body condition differences were observed for two of my species. I found that all leopard frogs increased in scaled mass index (SMI) when exposed to a PFAS treatment, indicating an increased body condition. Toads exhibited a more variable SMI pattern across treatments, with no outstanding trends, and tiger salamanders did not differ significantly across treatments. These data suggest that sublethal effects vary greatly depending on the species, possibly due to life history traits. Future research examining biomagnification potential is warranted to determine the influence of PFAS on food webs. Additionally, there is a need to determine the physiological mechanisms underlying the observed effects of PFAS exposure.<br>