Os estuários são o receptáculo final de muitos contaminantes antrópicos, como os hidrocarbonetos policíclicos aromáticos (HPAs), que podem ser tóxicos aos organismos. A biodisponibilidade dos HPAs pode ser avaliada através de biomarcadores de exposição, como os metabólitos biliares. Este trabalho teve como objetivo avaliar a biodisponibilidade do HPAs em peixes da espécie Mugil curema do Estuário de Santos e de Cananéia, através da análise de metabólitos de HPAs em bile de peixes. As coletas no Estuário de Cananéia foram realizadas nos meses de junho e novembro de 2008 e as coletas no Estuário de Santos foram realizadas entre os meses de março e maio de 2009. Os metabólitos foram analisados através de cromatografia líquida com detector de fluorescência (HPLC/F). A concentração de metabólitos biliares totais para o Estuário de Cananéia variou entre 0,91 a 89,97 ?g g-1 de bile, e para o Estuário de Santos variou de 4,68 a 528,43 ?g g-1 de bile. Houve diferença significativa entre os locais estudados. Observou-se também que não houve diferença significativa entre as amostras de machos e de fêmeas. A biodisponibilidade de HPAs foi considerada como baixa para o Estuário de Cananéia e alta para o Estuário de Santos. Valores de referência foram propostos para analise ambiental de metabólitos biliares de HPAs, sendo estipulada uma concentração de 2,22 ?g g-1 de bile para locais não contaminados. / Estuaries are the final receptacle to many anthropic contaminants, such as polycyclic aromatic hydrocarbons (PAHs), who can be toxic to organisms. The PAH bioavailability can be evaluated through biomarkers, such as biliary metabolites. This work had as objective evaluate the PAHs bioavailability in fishes of Mugil curema from Santos and Cananéia Estuaries, through the analysis of PAHs metabolites in fish bile. The Cananéia Estuary sampling was made in June and November from 2008 and the Santos Estuary sampling was made between the months of March and May from 2009. The metabolites were analyzed through a high performance liquid chromatograph with fluorescence detector (HPLC/F). The biliary metabolites concentrations from the Cananéia Estuary varied between 0,91 a 89,97 ?g g-1 of bile, and from Santos Estuary varied between 4,68 a 528,43 ?g g-1 of bile. There were significant differences between the sampling sites. There were no significant differences between the male and female samples. The PAHs bioavailability was considered low to Cananéia Estuary and high to Santos Estuary. Reference values were proposed to PAHs biliary metabolites environmental analysis, been stipulated a concentration of 2,22 ?g g-1 of bile to uncontaminated sites.

by Ho, Kai-Man. / Thesis submitted in: December 2004. / Thesis (M.Phil.)--Chinese University of Hong Kong, 2005. / Includes bibliographical references (leaves 158-179). / Abstracts in English and Chinese. / Acknowledgements --- p.i / Abstracts --- p.ii / Contents --- p.vii / List of figures --- p.xiv / List of tables --- p.xvii / Abbreviations --- p.xx / Chapter 1. --- Introduction --- p.1 / Chapter 1.1 --- Poly cyclic Aromatic Hydrocarbons (PAHs) / Chapter 1.1.1 --- Characteristics of PAHs --- p.1 / Chapter 1.1.2 --- Sources of PAHs --- p.3 / Chapter 1.1.3 --- Environmental fates of PAHs --- p.5 / Chapter 1.1.4 --- Effects of PAHs on living organisms --- p.7 / Chapter 1.1.5 --- Summary --- p.10 / Chapter 1.2 --- Target PAH: Benzo[a]pyrene (BaP) --- p.10 / Chapter 1.3 --- PAH contamination in Hong Kong --- p.14 / Chapter 1.4 --- Remediation for PAHs contaminated soils --- p.15 / Chapter 1.4.1 --- Chemical/ Physical methods --- p.15 / Chapter 1.4.2 --- Bioremediation --- p.16 / Chapter 1.5 --- Biodegradation of PAHs by bacteria and fungi --- p.18 / Chapter 1.5.1 --- Tolerance and degradation --- p.18 / Chapter 1.5.2 --- Biodegradation of PAHs by microorganisms --- p.20 / Chapter 1.5.2.1 --- Bacteria --- p.22 / Chapter 1.5.2.2 --- Fungi --- p.23 / Chapter 1.6 --- Environmental standards --- p.26 / Chapter 1.7 --- Strategies of soil sampling and microbial isolation --- p.26 / Chapter 1.7.1 --- Contaminated soil vs. uncontaminated soil --- p.26 / Chapter 1.7.2 --- Native species vs. foreign species --- p.29 / Chapter 1.7.3 --- Background of the sampling areas --- p.30 / Chapter 1.7.3.1 --- North Tsing Yi shipyard --- p.30 / Chapter 1.7.3.2 --- "Tsam Chuk Wan, Sai Kung" --- p.33 / Chapter 1.8 --- Objectives of this study --- p.33 / Chapter 2. --- Materials and Methods --- p.35 / Chapter 2.1 --- Soil Collection --- p.35 / Chapter 2.1.1 --- Abandoned shipyard soil and its sediment soil --- p.35 / Chapter 2.1.2 --- "Tsam Chuk Wan, Sai Kung" --- p.35 / Chapter 2.2 --- Characterization of soils --- p.35 / Chapter 2.2.1 --- Sample preparation --- p.36 / Chapter 2.2.2 --- Soil pH --- p.36 / Chapter 2.2.3 --- Electrical conductivity --- p.36 / Chapter 2.2.4 --- Salinity --- p.36 / Chapter 2.2.5 --- Total organic carbon contents --- p.38 / Chapter 2.2.6 --- Metal analys --- p.is / Chapter 2.2.7. --- Oil and grease content --- p.38 / Chapter 2.2.8 --- Soil texture --- p.39 / Chapter 2.2.9 --- Available ammoniacal nitrogen and oxidized nitrogen --- p.39 / Chapter 2.2.10 --- Available Phosporus --- p.40 / Chapter 2.2.11 --- Total Nitrogen and total Phosporus --- p.40 / Chapter 2.2.12 --- Moisture / Chapter 2.2.13 --- DTPA-extractable metals --- p.41 / Chapter 2.2.14 --- Extraction of PAHs and organic pollutants --- p.41 / Chapter 2.2.14.1 --- Extraction procedures --- p.41 / Chapter 2.2.14.2 --- GC-MSD conditions --- p.41 / Chapter 2.2.14.3 --- Extraction efficiency --- p.43 / Chapter 2.2.15 --- Soil colour --- p.43 / Chapter 2.3 --- Screening and selection of microorganismms --- p.43 / Chapter 2.3.1 --- Isolation of potential BaP-degrading microorganisms --- p.44 / Chapter 2.3.1.1 --- Isolation of bacteria --- p.44 / Chapter 2.3.1.2 --- Isolation of fungi --- p.44 / Chapter 2.3.2 --- Cultures preserving microorganisms --- p.46 / Chapter 2.3.3 --- Screening and selection of microbes --- p.46 / Chapter 2.3.3.1 --- Bacteria --- p.46 / Chapter 2.3.3.2 --- Fungi --- p.46 / Chapter 2.3.4 --- Survival test --- p.47 / Chapter 2.3.5 --- Removal efficiency (RE) towards BaP by the microorganisms --- p.47 / Chapter 2.3.5.1 --- Bacteria --- p.47 / Chapter 2.3.5.2 --- Fungi --- p.48 / Chapter 2.3.6 --- Removal efficiency (RE) --- p.48 / Chapter 2.3.7 --- Relationship of absorbance of bacterial culture and bacterial biomass --- p.49 / Chapter 2.4 --- Identification of selected microorganisms --- p.49 / Chapter 2.4.1 --- Identification of bacterium --- p.49 / Chapter 2.4.1.1 --- 16S rDNA sequencing --- p.49 / Chapter 2.4.1.1.1 --- Primers --- p.49 / Chapter 2.4.1.1.2 --- DNA extraction --- p.51 / Chapter 2.4.1.1.3 --- Specific PCR --- p.51 / Chapter 2.4.1.1.4 --- Gel electrophoresis --- p.51 / Chapter 2.4.1.1.5 --- Purification of PCR products --- p.52 / Chapter 2.4.1.1.6 --- DNA sequencing --- p.52 / Chapter 2.4.1.2 --- Midi Sherlock® Microbial Identification System (MIDI) --- p.53 / Chapter 2.4.1.3 --- Biolog MicroLog´ёØ system (Biolog) --- p.55 / Chapter 2.4.2 --- Identification of fungi --- p.56 / Chapter 2.4.2.1 --- ITS DNA sequencing --- p.56 / Chapter 2.4.2.2 --- Observation under electronic microscope --- p.58 / Chapter 2.5 --- Growth curve of the microorganism --- p.58 / Chapter 2.5.1 --- Bacterium --- p.58 / Chapter 2.5.2 --- Fungi --- p.58 / Chapter 2.6 --- Preparation of Benzo[a]pyrene (BaP) stock solution --- p.58 / Chapter 2.7 --- Comparison of isolated bacterium and fungi --- p.60 / Chapter 2.8 --- Optimization of BaP degradation by selected fungus --- p.60 / Chapter 2.8.1 --- Preparation of straw compost inoculated with selected fungus --- p.60 / Chapter 2.8.2 --- Effect of incubation time --- p.61 / Chapter 2.8.3 --- Effect of initial BaP concentration --- p.61 / Chapter 2.8.4 --- Effect of inoculum size / Chapter 2.8.5 --- Effect of temperature --- p.61 / Chapter 2.8.6 --- Effect of soil pH --- p.62 / Chapter 2.8.7 --- Study of BaP degradation pathway by the microorganisms using GC-MSD --- p.62 / Chapter 2.9 --- Chitin Assay --- p.62 / Chapter 2.10 --- Enzyme assay --- p.63 / Chapter 2.10.1 --- Laccase assay --- p.63 / Chapter 2.10.2 --- Manganese peroxidase assay --- p.63 / Chapter 2.10.3 --- Lignin peroxidase assay --- p.64 / Chapter 2.11 --- Toxicity of treated soil --- p.64 / Chapter 2.12 --- Statistical analysis --- p.65 / Chapter 3. --- Results --- p.66 / Chapter 3.1 --- Soil Collection --- p.66 / Chapter 3.1.1 --- North Tsing Yi shipyard --- p.66 / Chapter 3.1.2 --- "Tsam Chuk Wan, Sai Kung" --- p.66 / Chapter 3.2 --- Characterization of soil samples --- p.71 / Chapter 3.3 --- Extraction efficiency of Benzo[a]pyrene --- p.79 / Chapter 3.4 --- Screening and selection of microorganisms --- p.79 / Chapter 3.4.1 --- Isolation ofpotential BaP-degrading microorganisms --- p.79 / Chapter 3.4.2 --- Screening and selection of microbes --- p.87 / Chapter 3.4.2.1 --- Bacteria --- p.87 / Chapter 3.4.2.2 --- Fungi --- p.93 / Chapter 3.4.3 --- Growth curve of the microorganisms --- p.95 / Chapter 3.4.3.1 --- Bacterium --- p.95 / Chapter 3.4.3.2 --- Fungi --- p.99 / Chapter 3.5 --- Comparison of isolated bacterium and fungi --- p.99 / Chapter 3.6 --- Identification of selected microorganisms --- p.102 / Chapter 3.6.1 --- Identification of bacterium --- p.103 / Chapter 3.6.1.1 --- 16S rDNA sequencing --- p.103 / Chapter 3.6.1.2 --- Midi Sherlock® Microbial Identification System (MIDI) --- p.103 / Chapter 3.6.1.3 --- Biolog MicroLog´ёØ system (Biolog) --- p.107 / Chapter 3.6.2 --- Identification of fungi --- p.107 / Chapter 3.6.2.1 --- ITS DNA sequencing --- p.107 / Chapter 3.6.2.2 --- Observation under electronic microscope --- p.113 / Chapter 3.7 --- Optimization of BaP degradation by the selected fungus: Trichoderma asperellum --- p.107 / Chapter 3.7.1 --- Effect of incubation time --- p.107 / Chapter 3.7.2 --- Effect of inoculum size --- p.113 / Chapter 3.7.3 --- Effect of initial BaP concentration --- p.113 / Chapter 3.7.4 --- Effect of soil pH --- p.113 / Chapter 3.7.5 --- Effect of temperature --- p.117 / Chapter 3.8 --- Determination of breakdown products of BaP by BaP-degrading microorganisms --- p.117 / Chapter 3.9 --- Enzyme assay --- p.117 / Chapter 3.10 --- Evaluation of toxicity by using indigenous bacteria --- p.121 / Chapter 4. --- Discussion --- p.128 / Chapter 4.1 --- Physico-chemical properties of soil samples --- p.128 / Chapter 4.2 --- Determination of BaP and other organic compounds --- p.131 / Chapter 4.3 --- Identification of the microorganisms --- p.132 / Chapter 4.3.1 --- Bacteria --- p.132 / Chapter 4.3.2 --- Fungi --- p.134 / Chapter 4.4 --- Biodegradation by BaP-degrading microorganisms --- p.135 / Chapter 4.4.1 --- Isolation and screening of BaP-degrading microorganisms --- p.135 / Chapter 4.4.2 --- Biodegradation of BaP --- p.137 / Chapter 4.4.2.1 --- Bacteria --- p.137 / Chapter 4.4.2.2 --- Fungi --- p.138 / Chapter 4.4.3 --- BaP degradation pathway --- p.140 / Chapter 4.4.3.1 --- Bacteria --- p.140 / Chapter 4.4.3.2 --- Fungi --- p.140 / Chapter 4.5 --- Optimization of PAH degradation by T. asperellum --- p.143 / Chapter 4.5.1 --- Effect of incubation time --- p.143 / Chapter 4.5.2 --- Effect of initial BaP concentration --- p.144 / Chapter 4.5.3 --- Effect of inoculum size fungus --- p.144 / Chapter 4.5.4 --- Effect of soil pH --- p.145 / Chapter 4.5.5 --- Effect of temperature --- p.146 / Chapter 4.6 --- Comparison the selected bacterium and fungi --- p.146 / Chapter 4.7 --- Evaluation of toxicity by using in indigenous bacteria --- p.148 / Chapter 4.8 --- Post treatment by crude enzyme of Pleurotus pulmonarius --- p.149 / Chapter 4.9 --- Limiting factors for BaP degradation --- p.150 / Chapter 4.10 --- Further Investigations --- p.152 / Chapter 5. --- Conclusion --- p.155 / Chapter 6. --- References --- p.158

Les Hydrocarbures Aromatiques Polycycliques (HAP) représentent une famille de polluants atmosphériques issus de la combustion incomplète de la matière organique. Ils sont ainsi présents dans l'atmosphère polluée des villes, la fumée de cigarette et certaines industries. Une exposition aux HAP peut être à l'origine de cancers du poumon, de la peau et de la vessie. A ce titre, certains HAP sont suspectés ou reconnus cancérigènes pour l'Homme, comme le Benzo[a]pyrène (B[a]P), par leur capacité à induire des dommages à l'ADN après métabolisation. Malgré une émission systématique des HAPs en mélanges, la majorité des études s'est intéressée à l'effet génotoxique des HAP purs et principalement au B[a]P. Afin de fournir des données mécanistiques sur la génotoxicité et le mode d'action des mélanges de HAP, nous avons réalisé une étude in vitro dans des lignées cellulaires de poumons (A549), de vessie (T24) et de foie (HepG2). Les dommages à l'ADN ont été suivis par la mesure des adduits par HPLC-MS/MS et des dommages oxydatifs par la méthode des comètes, ainsi que le métabolisme par l'induction des gènes par RT-qPCR et les activités enzymatiques des CYP540 de phase I (EROD) et de phase II (GST). Dans un premier temps, l'utilisation du B[a]P, comme composé modèle a montré une absence quasi-totale de métabolisation et de génotoxicité pour T24. Par contre, la formation d'adduits et l'induction de la métabolisation a été mise en évidence pour A549, avec des effets notamment de dose-réponse « en cloche » similaires à ceux observés dans d'autres modèles de poumons. Nous avons ensuite étendu cette démarche à 12 HAP prioritaires et étudié leur métabolisation et la formation d'éventuels adduits en se focalisant sur la lignée pulmonaire A549. La combinaison de ces HAP au B[a]P dans des mélanges binaires ou dans des mélanges plus complexes mimant des mélanges environnementaux entraine une forte inhibition de la formation des adduits issus du B[a]P sans apparition d'adduits d'autres HAP. Par ailleurs, nous avons observé dans le cas des mélanges complexes une bonne corrélation entre l'activité EROD et la formation des adduits à l'ADN, alors que les gènes de phase sont eux surexprimés par l'exposition au mélange par rapport au B[a]P pur. Les mécanismes par lesquels s'exerce cette inhibition des adduits restent encore à élucider mais la métabolisation des HAPs constitue une étape clé dans la génotoxicité des mélanges à travers des phénomènes d'inhibition ou de compétition au niveau des CYP entrainant une inhibition de l'activité EROD. Il est donc clair que l'étude des HAP de façon individuelle n'est pas suffisante pour appréhender la génotoxicité des mélanges complexes. L'approche FET, couramment utilisée pour évaluer le risque lié à l'exposition aux mélanges de HAP, repose sur l'additivité des effets toxiques et néglige les interactions métaboliques entre les différents HAP. L'amélioration de cet outil de prédiction est nécessaire et passe obligatoirement par l'étude des mécanismes sous-jacents qui relient la composition des mélanges, leur métabolisation et leur génotoxicité. / Polycyclic Aromatic Hydrocarbons (PAH) represent a family of ubiquitous atmospheric pollutants produced upon incomplete combustion and thus present in polluted atmosphere of the cities, in cigarette smoke and in certain industries. Exposure to HAP can cause lung, skin and bladder cancers. For this reason, some PAHs are suspected or recognized carcinogenic to humans, especially Benzo[a]pyrene (B[a]P), through their ability at inducing the formation of DNA damage after metabolization. In spite of the systematic emission of PAHs in mixtures, the majority of the studies was interested in the genotoxic effect of pure PAH and mainly B[a]P. In order to provide mechanistic data on the genotoxicity and the mode of action of PAH mixtures, we designed an in vitro study using cell lines representative of lungs (A549), bladder (T24) and liver (HepG2). DNA damage was investigated through the quantification of adducts by HPLC-MS/MS and of oxidative damage by the Comet assay. In addition, the metabolism was studied by analyzing genes induction by RT-qPCR and enzymatic activities of phase I CYP540 (EROD) and phase II (GST). First, the use of B[a] P, as a reference compound showed a quasi-total absence of metabolization and genotoxicity for T24. In contrast, the formation of DNA adducts formation and the induction of metabolization was highlighted for A549, with a bell-shaped dose-response curve similar to those observed in other lungs models. Then we extended this approach to 12 priority PAH and analyzed their metabolization and the possible formation of adducts focusing on the pulmonary cell line A549. The combination of these HAP to B[a]P in binary mixtures or in complex mixtures representative to environmental exposures led to a strong inhibition in adducts formation induced by B[a]P without outbreak of adducts from other PAH. In addition, we observed, in the case of complex mixtures, a good correlation between the EROD activity and the formation of adducts in DNA, while phase I genes were always overexpressed after exposure to mixtures when compared to pure B[a]P. The mechanisms involved in the inhibition of DNA adducts remain to be elucidated but PAHs metabolization represents a key step in the mixtures genotoxicity through inhibition or competition of CYP resulting in an inhibition of EROD activity. It is thus clear that the study of the HAP in an individual way is not sufficient to understand the genotoxicity of complex mixtures. The TEF Approach, usually used to asses the risk related to PAH mixtures exposure, relies on toxic effects additivity and ignores metabolic interactions between the various PAH. The improvement of this prediction tool is essential and involves necessarily the study of the underlying mechanisms which connect mixtures composition, their metabolization and their genotoxicity.

Coordenação de Aperfeiçoamento de Pessoal de Nível Superior / As concentrações na exaustão e os fatores de emissão dos hidrocarbonetos policíclicos aromáticos (HPA) prioritários de um veículo a diesel e as suas respectivas concentrações no diesel usado durante os ensaios de emissão veicular foram determinados com a finalidade de estimar a contribuição dos HPA provenientes do combustível nas emissões. Os produtos da combustão foram coletados diretamente nas emissões brutas do escapamento, utilizando um sistema de amostragem a volume constante sem diluição dos gases da exaustão. Os HPA associados ao MP foram amostrados de forma estratificada, utilizando um impactador em cascata MOUDI e filtros de fibra de vidro como substratos, e os HPA em fase gasosa foram amostrados usando cartuchos de amberlite XAD-2. A concentração dos HPA no óleo lubrificante do motor também foi monitorada ao longo do tempo até a sua troca após 12.000 km de uso. Após a extração e tratamento das amostras, a identificação e quantificação dos HPA foram realizadas, utilizando cromatografia de fase gasosa acoplada à espectrometria de massas (CG-EM) com injetor de grande volume de vaporização com a temperatura programável (PTV-LVI). Cinco variáveis do PTV-LVI foram otimizadas, utilizando planejamento de experimentos, o que permitiu obter limites de detecção menores do que 2,0 g L-1. Somente 7 dos 16 HPA prioritários foram identificados na exaustão: NAP, ACY, ACE, FLU, FEN, FLT e PYR. Os ensaios de emissão veicular foram realizados com o veículo em modo estacionário, sem aplicação de carga e com baixa velocidade de rotação do motor (1500 rpm), utilizando um diesel com menor teor de enxofre (10 mg kg-1) e com 5% v/v de biodiesel. Esses fatores possivelmente contribuíram para reduzir as emissões dos outros 9 HPA a valores abaixo dos limites de detecção do método desenvolvido. Aproximadamente 80% da massa dos HPA totais associados ao MP estavam presentes em partículas com tamanho entre 1,0 m e 56 nm, e aproximadamente 4,5% estavam presentes em partículas menores do que 56 nm. Partículas menores que 2,5 m são facilmente inaladas e depositadas no trato respiratório e na região alveolar, justificando a preocupação com relação às emissões de HPA associados a partículas provenientes da exaustão veicular de motores a diesel. Somente 5 dos 7 HPA identificados na exaustão foram detectados no diesel: NAP, ACY, FLU, FEN e PYR. A razão entre os fatores de emissão (g L-1diesel) dos HPA na exaustão e suas respectivas concentrações do diesel (g L-1) variaram de 0,01 0,02 a 0,05 0,029, dependendo do HPA. Esses valores indicam que pelo menos 95 a 99% dos HPA identificados no diesel foram destruídos e/ou transformados em outros compostos durante a combustão, e/ou foram retidos no reservatório do óleo lubrificante. Por outro lado, os HPA que tiveram maiores concentrações no diesel também apresentaram maiores fatores de emissão, o que sugere que os HPA provenientes do diesel possuem uma contribuição significativa para as emissões dos HPA totais. O perfil dos HPA prioritários no óleo lubrificante mostrou-se semelhante ao perfil dos HPA no diesel e nas emissões totais, onde o NAP, FEN e PYR foram os HPA majoritários / A diesel vehicle exhaust concentrations and emission factors of priorities polycyclic aromatic hydrocarbons (PAHs) and their respective concentrations in the diesel fuel used during the vehicle emissions testing were determined in order to estimate the fuel PAHs contribution to vehicle emissions. Combustion products are collected directly from the raw vehicle exhaust using a constant volume sampling system that does not employ exhaust products dilution. The particle-phase PAHs were sampled in stratified way using a Micro-orifice Uniforme Deposite Impactor (MOUDI) and glass fiber filter as substrates and the gas-phase PAHs were sampled using Amberlite XAD-2 cartridge. The PAHs concentrations in the engine lubricant oil were also monitored over time until its change after 12,000 km of use. After sample extractions and treatments, the PAHs identification and quantification were performed using gas chromatography coupled with mass spectrometry (GC-MS) and programmable temperature vaporization large volume injection (PTV-LVI). Five PTV parameters were optimized using statistical design experiments, which allowed to be obtained detection limits below 2.0 g L-1. Only 7 of 16 priority PAH were identified in exhaustion: NAP, ACY, ACE, FLU, FEN, FLT and PYR. The vehicle emission tests were carried out with the vehicle in stationary mode, without load, low engine speed (1500 rpm), using diesel fuel with lower sulfur (10 mg kg-1) and 5% v/v biodiesel. These factors may have contributed to reduce the other 9 PAH emissions to values below the detection limits of the method developed. Approximately 80% of the PAHs total mass associated with the particulate matter were present in particle size between 1.0 m and 56 nm and approximately 4.5% were present in particles smaller than 56 nm. Particles smaller than 2.5 m are easily inhaled and deposited in the respiratory tract and in the alveolar region, justifying the concern about PAHs emissions associated with particles from vehicle exhaust diesel engine. Only 5 of the 7 PAHs identified in exhaust were detected in diesel fuel: NAP, ACY, FLU, PHE and PYR. The ratio between the PAHs emission factors in exhaust (g L-1 diesel) and their respective concentrations in diesel fuel (g L-1) ranged from 0.01 0.02 a 0.05 0.029, depending on the PAH. These values indicate that al least 95 to 99% of the PAH identified in diesel fuel were destroyed and/or converted into other compounds during the combustion, and/or been retained in lubricant oil reservoir. On the other hand, PAHs that had higher concentration in diesel also had higher exhaust emission factors, which suggests that the PAH from diesel have a mean contribution to total PAHs emissions. The PAH priority profile in lubricant oil was similar to PAH profile in diesel and in vehicle exhaust, where the NAP, FEN and PYR were the majorities PAHs

Made available in DSpace on 2014-12-17T15:41:49Z (GMT). No. of bitstreams: 1 JulianaPSDP_DISSERT.pdf: 1777680 bytes, checksum: 11814e53360b103c7198cf617f2a583c (MD5) Previous issue date: 2010-07-06 / The aim of this work is the treatment of produced water from oil by using electrochemical technology. Produced water is a major waste generated during the process of exploration and production in the oil industry. Several approaches are being studied aiming at the treatment of this effluent; among them can be cited the biological process and chemical treatments such as advanced oxidation process and electrochemical treatments (electrooxidation, electroflotation, electrocoagulation, electrocoagulation). This work studies the application of electrochemical technology in the treatment of the synthetic produced water effluent through the action of the electron, in order to remove or transform the toxic and harmful substances from the environment by redox reactions in less toxic substances. For this reason, we used a synthetic wastewater, containing a mixture H2SO4 0,5M and 16 HPAs, which are: naphthalene, acenaphthylene, acenaphthene, fluorene, phenanthrene, anthracene, fluoranthene, pyrene, benzo (a) anthracene, chrysene, benzo(b)fluoranthene, benzo(k) fluoranthene, benzo(a)pyrene, indeno(1,2,3-cd)pyrene, dibenzo(a, h)anthracene, benzo(g, h, i)perylene. Bulk electrochemical oxidation experiments were performed using a batch electrochemical reactor containing a pair of parallel electrodes, coupled with a power supply using a magnetic stirrer for favoring the transfer mass control. As anodic material was used, a Dimensionally Stable Anode (DSA) of Ti/Pt, while as cathode was used a Ti electrode. Several samples were collected at specific times and after that, the analysis of these samples were carried out by using Gas Chromatography Coupled to Mass Spectrometry (GC - MS) in order to determine the percentage of removal. The results showed that it was possible to achieve the removal of HPAs about 80% (in some cases, more than 80%). In addition, as an indicator of the economic feasibility of electrochemical treatment the energy consumption was analyzed for each hour of electrolysis, and based on the value kWh charged by ANEEL, the costs were estimated. Thus, the treatment costs of this research were quite attractive / O presente trabalho ? dirigido ao tratamento de ?gua produzida de petr?leo usando uma tecnologia eletroqu?mica. A ?gua produzida ? um dos principais res?duos gerados durante o processo de explora??o e produ??o na ind?stria petrol?fera, onde corresponde a 98 % de todos os efluentes gerados. V?rias metodologias est?o sendo estudadas visando o tratamento desse efluente, dentre elas est?o os processos biol?gicos, os processos de oxida??o avan?ados (POAs), tratamentos eletroqu?micos como eletrooxida??o, eletrocoagula??o, eletroflota??o e eletroredu??o. Esse trabalho mostra a aplica??o da tecnologia de eletrooxida??o no tratamento da ?gua produzida, pois se trata de uma t?cnica com alta compatibilidade ambiental, onde atrav?s da a??o do pr?prio el?tron, as subst?ncias t?xicas e nocivas ao meio ambiente podem ser removidas ou transformadas atrav?s de rea??es de ?xido-redu??o em subst?ncias menos t?xicas. Para isso, foi utilizado efluente sint?tico contendo uma mistura de H2SO4 0,5M e de 16 hidrocarbonetos polic?clicos arom?ticos (HPAs), que s?o: naftaleno, acenaftileno, acenafteno, fluoreno, fenantreno, antraceno, fluoranteno, pireno, benzo(a)antraceno, criseno, benzo(b)fluoranteno, benzo(k)fluoranteno, benzo(a)pireno, indeno(1,2,3-cd)pireno, dibenzo(a,h)antraceno, benzo(g,h,i)perileno. Utilizou-se o processo de oxida??o eletroqu?mica com um reator eletroqu?mico em batelada contendo um par de eletrodos paralelos, acoplados a uma fonte de corrente cont?nua e usando um agitador magn?tico para favorecer o transporte de massa na solu??o sint?tica. Como material an?dico utilizou-se um eletrodo de ?nodo dimensionalmente est?vel (DSA), constitu?do de Ti/Pt, enquanto o material cat?dico foi o Ti. Para detec??o e quantifica??o dos HPAs utilizou ? t?cnica de cromatografia gasosa acoplada a espectrometria de massa (CG - EM), onde o efluente foi analisado antes e ap?s o tratamento eletroqu?mico. Os resultados se mostraram eficazes, obtendo-se remo??es significativas dos HPAs superiores a 80%. Como indicador da viabilidade econ?mica do tratamento eletroqu?mico foram analisados os consumos energ?ticos do processo para cada hora do tratamento eletroqu?mico com base no valor kWh cobrado pela ANEEL. Os custos dos tratamentos desta pesquisa foram bastantes atrativos

Le sol est une ressource rare remplissant de nombreuses fonctions nécessaires au bon fonctionnement des écosystèmes et de nos sociétés. Malgré tout, il subit des pressions anthropiques à l’origine de sa déterioration. Ainsi en Europe, 16% du territoire est sujet à des degradations des sols. Une des menaces affectant l’homeostasie des sols est la contamination chimique issue des sites à activités industrielles. Ces sites contaminés, estimés au nombre 2,5 millions en Europe sont à l’origine d’un risque pour la santé humaine et environnementale. Malheureusement, à l’heure actuelle, il n’existe pas de cadre réglementaire européen commun concernant la gestion de ces sites, dont les diagnostics sont réalisés uniquement sur des listes restreintes de molécules et les polluants prioritaires. Cependant, la contamination des sols est généralement issue de mélanges complexes dont la toxicité est due à un ensemble de contaminants. L’objectif de cette thèse concerne l’identification de composés à l’origine de la toxicité des sols pollués en appliquant une analyse dirigée par l’effet (EDA), une technique qui combine des analyses biologiques et chimiques à un fractionnement physico-chimique. Après le développement de l’EDA pour les matrices solides, cette approche a été utilisée sur site afin d’identifier des composés liant le recepteur des hydrocarbures aromatiques (AhR). Ceci à permis de mettre au jour des contaminants à activité biologique non pris en compte dans les diagnostics des sols pollués tels que des hydrocarbures aromatiques polycycliques non prioritaires selon l’US-EPA, leurs produits d’oxydation ainsi que des composés contenant des N-,S-,O-Heterocyles. / The soil is a scarce resource fulfilling many functions necessary for the proper functioning of ecosystems and societies. Nevertheless, it suffers human pressures causing its deterioration. In Europe, 16% of the territory is subject to soil degradations. One of the threats to the soil homeostasis is the chemical contamination from industrial activity sites. These contaminated sites, estimated to number of 2.5 million in Europe are causing a risk to human and environmental health. Unfortunately, at present there is no common European regulatory framework for the management of these sites, whose diagnoses are made only on short lists of molecules and priority pollutants. However, soil contamination generally comes from complex mixtures whose toxicity is due to a combination of contaminants. The aim of this work concerns the identification of compounds responsible for the toxicity of the contaminated soil by applying an effect-directed analysis (EDA), a technique which combines biological and chemical analyzes to a physico-chemical fractionation. After the development of EDA on the solid matrices, this approach has been used on polluted sites to identify the compounds binding to the aryl hydrocabon receptor (AhR). This allowed to highlight contaminants with a biological activity not included in the diagnoses of polluted soils such as polycyclic aromatic hydrocarbons non-priority according to US-EPA, their oxidation products and compounds containing N -, S-, O-heterocycles.

<p>Wood combustion is mainly used in cold regions as a primary or supplemental space heating source in residential areas. In several industrialized countries, there is a renewed interest in residential wood combustion (RWC) as an alternative to fossil fuel and nuclear power consumption. The main objective of this thesis was to investigate the impact of RWC on the air quality in urban areas. To this end, a field campaign was conducted in Northern Sweden during wintertime to characterize atmospheric aerosol particles and polycyclic aromatic hydrocarbons (PAH) and to determine their source apportionment.</p><p>A large day-to-day and hour-to-hour variability in aerosol concentrations was observed during the intensive field campaign. On average, total carbon contributed a substantial fraction of PM10 mass concentrations (46%) and aerosol particles were mostly in the fine fraction (PM1 accounted for 76% of PM10). Evening aerosol concentrations were significantly higher on weekends than on weekdays which could be associated to the use of wood burning for recreational purposes or higher space heat demand when inhabitants spend longer time at home. It has been shown that continuous aerosol particle number size distribution measurements successfully provided source apportionment of atmospheric aerosol with high temporal resolution. The first compound-specific radiocarbon analysis (CSRA) of atmospheric PAH demonstrated its potential to provide quantitative information on the RWC contribution to individual PAH. RWC accounted for a large fraction of particle number concentrations in the size range 25-606 nm (44-57%), PM10 (36-82%), PM1 (31-83%), light-absorbing carbon (40-76%) and individual PAH (71-87%) mass concentrations.</p><p>These studies have demonstrated that the impact of RWC on air quality in an urban location can be very important and largely exceed the contribution of vehicle emissions during winter, particularly under very stable atmospheric conditions.</p>

<p>Biomass is considered to be a sustainable energy source with significant potentials for replacing electricity and fossil fuels, not at least in the residential sector. However, present wood combustion is a major source of ambient concentrations of hydrocarbons (e.g. VOC and PAH) and particulate matter (PM) and exposure to these pollutants have been associated with adverse health effects. Increased focus on combustion related particulate emissions has been seen concerning the formation, characteristics and implications to human health. Upgraded biomass fuels (e.g. pellets) provide possibilities of more controlled and optimized combustion with less emission of products of incomplete combustion (PIC´s). For air quality and health impact assessments, regulatory standards and evaluations concerning residential biomass combustion, there is still a need for detailed emission characterization and quantification when using different fuels and combustion techniques.</p><p>This thesis summarizes the results from seven different papers. The overall objective was to carefully and systematically study the emissions from residential biomass combustion with respect to: i) experimental characterization and quantification, ii) influences of fuel, appliance and operational variables and iii) aspects of ash and trace element transformations and aerosol formation. Special concern in the work was on sampling, quantification and characterization of particulate emissions using different appliances, fuels and operating procedures.</p><p>An initial review of health effects showed epidemiological evidence of potential adverse effect from wood smoke exposure. A robust whole flow dilution sampling set-up for residential biomass appliances was then designed, constructed and evaluated, and subsequently used in the following emission studies. Extensive quantifications and characterizations of particulate and gases emissions were performed for residential wood and pellet appliances. Emission factor ranges for different stoves were determined with variations in fuel, appliance and operational properties. The emissions of PIC´s as well as PM_tot from wood combustion were in general shown to be considerably higher compared to pellets combustion. PAH_tot emissions were determined in the range of 1300-220000 µg/MJ for wood stoves and 2-300 µg/MJ for pellet stoves with phenantrene, fluoranthene and pyrene generally found as major PAH´s. The PM emissions from present residential appliances was found to consist of significant but varying fractions of PIC´s, with emissions in the range 35-350 mg/MJ for wood stoves compared to 15-45 mg/MJ for pellet stoves. Accordingly, the use of up-graded biomass fuels, combusted under continuous and controlled conditions give advantageous combustion conditions compared to traditional batch wise firing of wood logs. The importance of high temperature in well mixed isothermal conditions was further illustrated during pellets combustion to obtain complete combustion with almost a total depletion of PIC´s. Fine (100-300 nm) particles dominated in all studied cases the PM with 80-95% as PM1. Beside varying fractions of carbonaceous material, the fine PM consisted of inorganic volatilized ash elements, mainly found as KCl, K₃Na(SO₄)₂ and K₂SO₄ with mass concentrations at 15-20 mg/MJ during complete combustion. The importance of the behavior of alkali elements for the ash transformation and fine particle formation processes was further shown, since the stability, distributions and compositions also directly control the degree of volatilization. In addition to the alkali metals, zinc was found as an important element in fine particles from residential biomass combustion. Finally, the behaviour of volatile trace elements, e.g. Zn and Cd, during pellets production and combustion were studied. A significant enrichment in the pellet fuel during the drying process was determined. The magnitude and importance of the enrichment was, however, relative small and some alternative measures for prevention were also suggested.</p>

Die Toxizität und Kanzerogenität von rein aromatischen polyzyklischen aromatischen Kohlenwasserstoffen (PAK) ist seit Jahrzehnten bekannt und umfassend erforscht. Die alkylierten PAK (alkPAK) besitzen jedoch aufgrund ihrer Alkylgruppe eine weitere Möglichkeit zur Bioaktivierung und müssen daher gesondert betrachtet werden. Die Alkylgruppe wird zunächst hydroxyliert, anschließend zur Säure oxidiert oder direkt konjugiert. Entstehen hierbei instabile benzylische Sulfokonjugate, so können diese DNA-Addukte bilden und zu Mutationen führen. In Hinblick auf die Bioaktivierung von alkPAK galt es daher zu klären welchen Einfluss die Struktur auf die benzylische Hydroxylierung hat und welche humanen Formen der löslichen Sulfotransferasen besonders an der Umsetzung der alkPAK-Derivate beteiligt sind. Die Untersuchung der Albuminbindung von Schwefelsäureestern sowie ihre Aufnahme in Nierenzellen sollten Aufschluss hinsichtlich möglicher Transportvorgänge geben. Für die in-vivo-Situation wurde weiterhin die Modulation des Metabolismus ausgewählter benzylischer Alkohole durch verschiedene Nahrungsmittelbestandteile, Arzneimittel und Fremdstoffe an Ratten untersucht. Als Biomarker wurden benzylische Carbonsäuren im Urin und die entsprechenden Mercaptursäuren in Urin und Fäzes betrachtet. Zunächst wurde anhand von Inkubationen mit Rattenlebermikrosomen festgestellt, dass insbesondere größere Ringsystemen wie etwa alkylierte Benzo[a]pyrene im Gegensatz zu Methylpyrenen in wesentlich geringerem Umfang zum benzylischen Alkohol umgesetzt werden. Dies wurde auch in Untersuchungen mit humanen Lebermikrosomen bestätigt. Untersuchungen an einzelnen humanen Cytochromen P450 zeigten, dass insbesondere die durch PAK induzierbaren Formen hCYP1A1 und 1B1 hohe Umsatzraten aufwiesen. Die hepatisch exprimierten Formen hCYP1A2 und 3A4 waren jedoch auch zur Bildung der benzylischen Alkohole in der Lage. Für die anschließende Sulfonierung der benzylischen Alkohole wurden besonders hohe Aktivitäten mit den humanen Sulfotransferasen hSULT1A1, 1A2, 1C2 und 1E1 festgestellt. Aufgrund der Enzymexpression und der guten Durchblutung, die eine gute Substratversorgung ermöglicht, ist die Leber als Hauptort der benzylischen Hydroxylierung und Sulfonierung anzusehen. Ergebnisse unserer Arbeitsgruppe zeigen jedoch, dass nach 1-Hydroxymethylpyren-Applikation bei Ratten die Niere die höchste Zahl an DNA-Addukten aufweist. Wegen der Fokussierung der Sulfonierung auf die Leber ist die systemische Verteilung der Schwefelsäureester die einzig plausible Erklärung. So wurde im Rahmen dieser Arbeit eine hochaffine Bindungsstelle für 2-Sulfoxymethylpyren an Albumin beschrieben und die Aufnahme von benzylischen Sulfaten durch die humanen organischen Anionentransporter hOAT1, 3 und 4 in Nierenzellen in vitro gezeigt. Für die in-vivo-Situation wurde der Einfluss von Ethanol, 4-Methylpyrazol, Pentachlorphenol, Quercetin und Disulfiram untersucht. Neben der durch die Detoxifizierung mittels Alkoholdehydrogenase und Aldehyddehydrogenase entstandenen benzylischen Carbonsäure kann als Biomarker die entsprechende Mercaptursäure herangezogen werden. Sie ist ein indirekter Nachweis für die reaktiven und toxischen benzylischen Sulfate der alkPAK. Für die beiden im Tierversuch eingesetzten benzylischen Alkohole (1-Hydroxymethylpyren und 1-Hydroxymethyl-8-methylpyren) konnte sie in Urin und Fäzes nachgewiesen werden. Es wurde jedoch ein deutlicher Unterschied in der gebildeten Menge sowie der Verteilung zwischen Urin und Fäzes für die beiden Mercaptursäuren festgestellt. Hierfür sind wahrscheinlich Unterschiede im Transport der benzylischen Schwefelsäureester sowie der Spezifität der an der Mercaptursäurebildung beteiligten Enzyme verantwortlich. In diesem Zusammenhang konnte gezeigt werden, dass der humane organische Anionentransporter hOAT1 1,8-Dimethylpyrenmercaptursäure nicht und der hOAT3 nur mit niedrigen Umsatzraten transportiert. Bei den Modulatoren zeigte die Gabe der kompetitiven Alkoholdehydrogenase-Hemmstoffe Ethanol und 4-Methylpyrazol die Bedeutung der Alkoholdehydrogenasen für die Entgiftung der benzylischen Alkohole: Die Oxidation zur entsprechenden Carbonsäure war reduziert und die Bildung der Mercaptursäure erhöht. Eine Hemmung der Toxifizierung vermittelt durch Sulfotransferase-Inhibitoren konnte nur für Pentachlorphenol beim Metabolismus des 1-Hydroxymethylpyrens beobachtet werden. Gleichzeitig erwies sich Pentachlorphenol als kompetitiver Alkoholdehydrogenase-Inhibitor, da eine signifikant geminderte Carbonsäureausscheidung zu beobachten war. Bei 1-Hydroxymethyl-8-methylpyren traten diese Effekte nicht auf. Die unterschiedlichen bzw. unterschiedlich starken Effekte der Modulatoren beim Metabolismus der verschiedenen benzylischen Alkohole bestätigen die Beobachtungen aus den in-vitro-Untersuchungen, dass unterschiedliche Enzym- und Transporteraffinitäten und –aktivitäten vorliegen. / The toxicity and carcinogenicity of purely aromatic polycyclic aromatic hydrocarbons (PAH) is known since decades and has been thoroughly investigated. Compared to the purely aromatic PAH the alcylated PAH (alcPAH) can additionally be biologically activated because of their alcyl group. The alcyl group is hydroxylated and subsequently oxidised to the corresponding acid or conjugated. If unstable benzylic sulfoconjugates arrise from this bioactivation DNA adducts may be formed and could induce mutations. Concering the bioactivation of alcPAH this work should help to get to know which influence the structure has on the benzylic hydroxylation and it should be clarified which forms of human soluble sulfotransferases catalyse the sulfonation of benzylic alcohols. Furthermore the albumin binding of sulfuric acid esters and the uptake into kidney cells by human organic anion transporters in vitro have been analysed to get inside into transport processes. For the in vivo situation the modulation of enzyme activities by food compounds, pharmaceuticals and xenobiotics is of interest. As biomarkers the respective benzylic carboxylic acid and mercapturic acid were measured in urine only and feces. By the use of incubations with rat liver microsomes it turned out that larger ring systems were benzylically hydroxylated to a remarkable less extent then alcyl pyrenes. This observation was also made for human liver microsomes. In vitro experiments addressing the activity of single human cytochromes P450 revealed that PAH inducable forms hCYP1A1 and 1B1 had highest hydroxylation rates, but also the hepatically expressed forms hCYP3A4 and CYP1A2 catalysed the benzylic hydroxylation. The subsequently following sulfonation of the benzylic alcohols was found to be catalysed with high formation rates by human sulfotransferase hSULT1A1, 1A2, 1C2 and 1E1. Due to the enzyme expression and the high blood circluation ensuring the substrate supply it can be assumed that liver is the main organ for benzylic hydroxylation and sulfonation. Nevertheless results from our group showed that after 1-hydroxy methyl pyrene exposure, rats had higher levels of DNA adducts in kidneys than in liver. Thus, it has to be assumed that the sulfuric acid esters are systemically distributed. In the course of this work a high affinity albumin binding site for 2-sulfoxy methyl pyrene was identified and the uptake of sulfuric acid esters mediated by human organic anion tranporter 1, 3 and 4 to kidneys cells in vitro was shown. For the further estimation of the in vivo bioactivation of alcPAH the modulation of enzyme activities by ethanol, 4-methylpyrazole, quercetin, pentachlorophenol and disulfiram was explored. The carboxylic acids formed via alcohol dehydrogenase and aldehyde dehydrogenase were used as biomarkers as well as the respective mercapturic acids. The occurence of the mercapturic acids is an indirect proof for the reactive and toxic benzylic sulfo conjugates. In the urine and fecal samples of rats treated with either 1-hydroxymethyl pyrene or 1-hydroxymethyl 8-methyl pyrene the corresponding mercapturic acids of the sulfuric acid esters were found. Even though the absolute amount excreted and the distribution in urine and fecal samples were quite different. This observation may be explained by differences in transport of the sulfuric acid esters as well as by different specificities of the enzymes responsable for mercapturic acid formation. Additionally it was shown that the human organic anion transporter 1 does not transport 1,8-dimethyl pyrenyl mercapturic acid and the human organic anion transporter 3 only with very little turnover. Whereas 1-methyl pyrenyl mercapturic acid was well transported by both of these proteins. With regard to the modulation the concurrent application of ethanol or 4-methyl pyrazole to rats revealed the important role of alcohol dehydrogenase for the detoxification of benzylic alcohols: The oxidation leading to the corresponding carboxylic acid was remarkably reduced and the excretion of the mercapturic acid via urine and feces was enhanced. In order to observe an inhibition of sulfotransferases pentachlorophenol and quercetine were concurrently applied to rats. An inhibitory effect by the means of an reduced excretion of mercapturic acid was only observed for pentachlorophenol in animals treated with 1-hydroxymethyl pyrene. In addition it turned out, that pentachlorophenol was a potent competitive alcohol dehydrogenase inhibitor as the renal excretion of the corresponding carboxylic acid was remarkably reduced. For 1-hydroxymethyl 8-methyl pyrene this modulation was not observed. These differences in effects and strenght of effects may be ascribed to different enzymatic and transport affinities and activities which have already been observed in in vitro experiments.

Alkylierte polyzyklische aromatische Kohlenwasserstoffe werden in vielen Matrizes wie Fahrzeugabgasen und Tabakrauch und auch als Kontaminanten in Nahrungsmitteln neben rein aromatischen Kongeneren gefunden. Alkylierte PAK können über die Alkylseitenkette über benzylische Hydroxylierung und nachfolgende Sulfonierung katalysiert über Sulfotransferasen (SULT) zu reaktiven Schwefelsäureestern umgesetzt werden. Die SULT-vermittelte Bioaktivierung zu einem genotoxischen Schwefelsäureester wurde für den benzylischen Alkohol 1-Hydroxymethylpyren des Hepatokanzerogens 1-Methylpyren in früheren Arbeiten gezeigt. In der vorliegenden Arbeit wurde überprüft, ob die benzylischen Alkohole weiterer alkylierter PAK über Sulfonierung zu genotoxischen Schwefelsäureestern umgesetzt werden. Hierzu wurde eine Gruppe von 17 Modellsubstanzen ausgewählt, um die Ableitung von Struktur-Aktivitäts-Beziehungen zu ermöglichen. Das genotoxische Potenzial authentischer benzylischer Schwefelsäureester der Modellsubstanzen wurde zunächst in vitro über DNA-Adduktbildung im zellfreien System und Mutagenität im Salmonella-Rückmutationstest untersucht. Die Sulfate zeigten große Reaktivitätsunterschiede in Abhängigkeit von der Struktur des aromatischen Systems und der Position der Alkylseitenkette, wobei die Endpunkte DNA-Adduktbildung und Mutagenität gut korrelierten. Des Weiteren wurde der Salmonella-Mutagenitätstest mit den benzylischen Alkoholen der untersuchten alkylierten PAK und gentechnisch veränderten S. typhimurium-Stämmen, die SULT-Formen des Menschen heterolog exprimieren, durchgeführt. Bis auf die Alkohole 2- und 4-HMP zeigten alle untersuchten benzylischen Alkohole deutliche mutagene Effekte in einem oder mehreren humane SULT exprimierenden Stämmen. Die durchgeführten in vitro-Versuche zeigten das Potenzial der benzylischen Metabolite alkylierter PAK für genotoxische Wirkungen. Nachfolgend musste geklärt werden, welche Relevanz die beobachteten Effekte für die komplexere in vivo-Situation haben. Nach Verabreichung verschiedener benzylischer Schwefelsäureester und Alkohole an männliche Ratten konnten DNA-Addukte in den untersuchten Organen detektiert werden, was im Fall der Schwefelsäureester deren systemische Bioverfügbarkeit und im Fall der benzylischen Alkohole deren Umsatz durch SULT der männlichen Ratte zeigte. Da im Gegensatz zum Menschen die SULT-Expression in der Ratte auf die Leber fokussiert ist, musste ein Großteil des Umsatzes zu genotoxischen Sulfaten in der Leber stattgefunden haben. DNA-Addukte wurden jedoch auch in extrahepatischen Organen gefunden, was über einen hepatischen Export der gebildeten reaktiven Sulfate und deren Transport über den Blutkreislauf zu diesen Geweben erklärt werden kann. Für die weiterführenden in vivo-Studien wurden die benzylischen Alkohole 1-HMP und 1-HM-8-MP ausgewählt, die trotz großer struktureller Ähnlichkeit toxikodynamische Unterschiede zeigten. Zur Untersuchung der Bedeutung des SULT-vermittelten Toxifizierungsweges als auch konkurrierender detoxifizierender oxidativer Stoffwechselprozesse, wurden für 1-HMP und 1-HM-8-MP in vivo-Inhibitionsstudien mit SULT-Inhibitoren und für 1-HM-8-MP auch mit ADH/ALDH-Inhibitoren durchgeführt. Eine Vorbehandlung mit dem SULT-Hemmstoff Pentachlorphenol führte zu einer Reduktion der DNA-Adduktniveaus in Organen 1-HMP- und 1-HM-8-MP-behandelter Tiere. Die Verabreichung von Quercetin hatte keine Auswirkung auf die DNA-Adduktniveaus. Die Hemmung der DNA-Adduktbildung bei Verabreichung von Pentachlorphenol verdeutlichte jedoch, dass benzylische Alkohole alkylierter PAK in vivo über Sulfonierung bioaktiviert werden. Eine Vorbehandlung mit dem ADH-Inhibitor 4-Methylpyrazol und dem ADH-Substrat Ethanol führte zu erhöhten DNA-Adduktniveaus in Organen 1-HM-8-MP-behandelter Tiere. Den gleichen Effekt, jedoch in geringerem Ausmaß, hatte auch die Vorbehandlung mit dem ALDH-Inhibitor Disulfiram. Dies deutet darauf hin, dass oxidative Modifikationen an der Seitenkette des 1-HM-8-MP einen Detoxifizierungsmechanismus darstellen. Nach Verabreichung benzylischer Metabolite alkylierter PAK wurden oftmals hohe Adduktniveaus in der Niere detektiert. Als mögliche Ursache hierfür wurde eine Transporter-vermittelte renale Sekretion reaktiver Sulfate postuliert, die über Vorbehandlung mit Probenecid vor Verabreichung von 1-HMP und 1-HM-8-MP überprüft wurde. Der Haupteffekt der Probenecid-Behandlung wurde jedoch nicht in der Niere, sondern in der Leber beobachtet, die stark erhöhte Adduktniveaus zeigte. Eine mögliche Erklärung hierfür ist die Hemmung des Exportes in der Leber gebildeter reaktiver Sulfate über Inhibition hepatischer organischer Anionentransporter. / Alkylated polycyclic aromatic hydrocarbons are found besides purely aromatic congeners in numerous matrices like car engine exhausts and tobacco smoke and as contaminants in foods. Alkylated PAH can be converted at the alkyl side chain to reactive sulfuric acid esters via benzylic hydroxylation and subsequent sulfonation catalysed by sulfotransferases (SULT). The SULT-mediated bioactivation to a genotoxic sulfuric acid ester was shown for the benzylic alcohol 1-hydroxymethylpyrene of the hepatocarcinogen 1-methylpyrene in previous studies. In the thesis at hand it was studied if the benzylic alcohols of further alkylated PAH are converted to genotoxic sulfuric acid esters via sulfonation. For this purpose a group of 17 model substances was chosen to allow for deduction of structure activity relationships. The genotoxic potential of authentic benzylic sulfuric acid esters of the model substances was initially investigated in vitro via DNA adduct formation in a cell free system and mutagenicity in the Salmonella reverse mutation test. The sulfates showed large differences in reactivity depending on the structure of the aromatic system and the position of the alkyl side chain whereupon the endpoints DNA adduct formation and mutagenicity correlated well. Furthermore, the Salmonella mutagenicity test was carried out with the benzylic alcohols of the alkylated PAH studied and S. typhimurium strains genetically engineered for the heterologous expression of human SULT forms. Except for the alcohols 2- and 4-HMP all benzylic alcohols studied showed clear mutagenic effects in one or more SULT-expressing strains. The studies performed in vitro demonstrated the potential of benzylic metabolites of alkylated PAH for genotoxic effects. Consecutively, the relevance of the observed effects for the more complex in vivo situation had to be clarified. After administration of different benzylic sulfuric acid esters and alcohols to male rats DNA adducts were detected in the organs studied, in case of the sulfuric acid esters showing their systemic bioavailability and in case of the benzylic alcohols demonstrating their conversion to the corresponding reactive benzylic sulfuric acid esters by SULT of the male rat. Since in contrast to man SULT expression in the rat is focused on the liver, a large part of the conversion to genotoxic sulfates must have been taken place in the liver. However, DNA adducts were also found in extrahepatic tissues which can be attributed to a hepatic export of the reactive sulfates formed and their transport to these tissues via circulation. For the continuative in vivo studies the benzylic alcohols 1-HMP and 1-HM-8-MP were chosen that demonstrated toxicodynamic differences in spite of their great structural resemblance. To investigate the importance of the SULT-mediated toxification pathway as well as competing detoxifying oxidative metabolic pathways, in vivo inhibition studies with SULT inhibitors were performed for 1-HMP and 1-HM-8-MP and with ADH/ALDH inhibitors also for 1-HM-8-MP. A pretreatment with the SULT inhibitor pentachlorophenol led to a reduction of DNA adduct levels in organs of animals treated with 1-HMP and 1-HM-8-MP. Administration of quercetin had no impact on the DNA adduct levels. However, inhibition of DNA adduct formation at administration of pentachlorophenol demonstrated that benzylic alcohols of alkylated PAH are bioactivated via sulfonation in vivo. A pretreatment with the ADH inhibitor 4-methylpyrazole and the ADH substrate ethanol led to increased DNA adduct levels in organs of animals treated with 1-HM-8-MP. The same effect but to a lesser extent was caused by a pretreatment with the ALDH inhibitor disulfiram. This indicates that oxidative modifications at the side chain of 1-HM-8-MP represent a detoxification mechanism. After administration of benzylic metabolites of alkylated PAH often high DNA adduct levels were detected in kidney. A transporter-mediated renal secretion was postulated as possible cause which was investigated using a pretreatment with probenecid before administration of 1-HMP and 1-HM-8-MP. However, the main effect of the treatment with probenecid was not observed in kidney but in liver that showed strongly increased adduct levels. A possible explanation for this effect is the inhibition of the export of reactive sulfates formed in liver via inhibition of hepatic organic anion transporters.