Coordenação de Aperfeiçoamento de Pessoal de Nível Superior / Environmental contamination caused by frequent use of herbicides in agriculture has increased in last decades. The quinclorac and clomazone herbicides are widely used in agriculture, which can cause contamination to organisms, such as fish. However, it is necessary studies in order to minimize the toxic effects of these compounds on aquatic ecosystems. Micronutrients such as selenium, which is essential in the nutrition of fish, may have antioxidant functions against oxidative damage caused by herbicides. The objective of this study was to verify whether a diet supplemented with diphenyl diselenide [(PhSe)2], has a protective effect against damage induced by herbicides quinclorac and clomazone in fish species Cyprinus carpio (carp) and Rhamdia sp. (silver catfish). In the first experiment, carp were fed a diet without (PhSe)2 or a diet containing 3.0 mg/Kg of (PhSe)2 for 60 days and after were exposed to 1 mg/L of quinclorac for 192 h. Thiobarbituric acid reactive substances (TBARS), protein carbonyl, non-protein thiols (SHNP), ascorbic acid (AA), and the activity of catalase (CAT), superoxide dismutase (SOD) and glutathione S-transferase (GST) were determined in liver, gills, brain and muscle of carp. The quinclorac increased TBARS levels in liver and gills, decreased NPSH levels in brain and muscle, AA in muscle, inhibited enzymes SOD in liver and GST in liver and brain. The (PhSe)2 reversed these effects by preventing the increase of TBARS in liver and gills and recovering GST activity in liver and NPSH in brain and muscle. In the second experiment, silver catfish were fed a diet without (PhSe)2 or a diet containing 3.0 mg/Kg of (PhSe)2 for 60 days and after were exposed to 1 mg/L of quinclorac for 192 h. We investigated the effect of (PhSe)2 on plasma metabolic changes, enzymes of intermediary metabolism, pro-oxidants parameters and antioxidant defense in the liver of silver catfish. The weight, length and hepatic somatic index (HSI) were also determined. Animals exposed to quinclorac showed a decrease at HSI, an increase lactate levels in plasma and in the enzymes fructose bifosfatase (FBPase), glucose-6-phosphatase (G6Pase), glycogen phosphorylase (GPase) and aspartate aminotransferase (AST) in liver. Furthermore, were observed increased of TBARS, decreased NPSH and AA levels and inhibition of SOD in liver of silver catfish. The (PhSe)2 was effective in protecting the liver of silver catfish by decreased TBARS, increasing NPSH levels, AA and the activity of SOD. However, the (PhSe)2 was not effective in recovery the effects caused by the increase of hepatic enzyme AST. In the third experiment investigated the ability of (PhSe)2 in reducing oxidative damage in the liver, gills and muscle of carp and silver catfish exposed to clomazone. Silver catfish and carp were fed with a diet without (PhSe)2 or a diet containing 3.0 mg/Kg of (PhSe)2 for 60 days and after were exposed to 1 mg/L of clomazone (192 h). At the end of the exposure period, oxidative parameters and antioxidant defenses were determined. Silver catfish exposed to clomazone showed increased TBARS in liver and muscle and protein carbonyl in liver and gills. In addition, decrease in levels of NPSH in liver and gills, AA in the liver and of enzyme glutathione peroxidase (GPx) in liver was observed. The (PhSe)2 reversed some effects caused by clomazone in silver catfish, preventing the increase in TBARS and protein carbonyl and by increasing NPSH and AA levels. Moreover, clomazone no caused apparent situation of oxidative stress in carp and thus cannot assess the role of (PhSe)2 in this species exposed to that herbicide. However, the (PhSe)2 in both species reduced per se the TBARS levels in liver and muscle, increased NPSH and AA levels and the activity of GPx in liver. Considering that exposure to herbicides is more frequent and that is the cause of several changes in fish, the results of these studies are of great importance, since the (PhSe)2 may represent an alternative to prevent or mitigate toxicity caused by herbicides in different fish species of commercial importance. / A contaminação ambiental causada pelo uso frequente de herbicidas na agricultura tem aumentado nas últimas décadas. O quinclorac e o clomazone são herbicidas amplamente utilizados na agricultura, os quais podem causar contaminação a organismos, como os peixes. Entretanto é necessário estudos no sentido de minimizar os efeitos tóxicos desses compostos em ecossistemas aquáticos. Micronutrientes como o selênio, o qual é essencial na nutrição de peixes, podem ter funções antioxidantes contra danos oxidativos causados por herbicidas. Assim, o objetivo deste trabalho foi verificar se uma dieta suplementada com o disseleneto de difenila [(PhSe)2], possui efeito protetor contra danos induzidos pelos herbicidas quinclorac e clomazone em peixes das espécies Cyprinus carpio (carpas) e Rhamdia sp. (jundiás). No primeiro experimento carpas foram alimentadas com uma dieta sem (PhSe)2 ou uma dieta contendo 3.0 mg/Kg de (PhSe)2 por 60 dias e após foram expostas a 1 mg/L do quinclorac por 192 horas. Substâncias reativas ao ácido tiobarbitúrico (TBARS), carbonilação de proteínas, tióis não proteicos (SHNP), ácido ascórbico (AA), bem como a atividade das enzimas catalase (CAT), superóxido dismutase (SOD) e glutationa S-transferase (GST) foram determinados em fígado, brânquias, cérebro e músculo de carpas. O quinclorac aumentou os níveis de TBARS em fígado e brânquias, diminuiu os níveis de SHNP em cérebro e músculo e de AA no músculo e inibiu as enzimas SOD em fígado e GST em fígado e cérebro. O (PhSe)2 reverteu esses efeitos prevenindo o aumento do TBARS em fígado e brânquias e recuperando a atividade da GST em fígado e SHNP em cérebro e músculo. No segundo experimento jundiás foram alimentados com uma dieta sem (PhSe)2 ou uma dieta contendo 3.0 mg/Kg de (PhSe)2 por 60 dias e após expostos a 1 mg/L do quinclorac por 192 horas. Investigou-se o efeito do (PhSe)2 sobre as alterações metabólicas no plasma, enzimas do metabolismo intermediário, bem como parâmetros pró-oxidantes e de defesa antioxidante em fígado dos jundiás. O peso, comprimento e índice hepatossomático (IHS) também foram determinados. Animais expostos ao quinclorac apresentaram diminuição no IHS, aumento nos níveis de lactato em plasma e das enzimas frutose bifosfatase (FBPase), glicose 6-fosfatase (G6Pase), glicogênio fosforilase (GPase) e da asparato aminotransferase (AST) em fígado. Além disso, foram observadas aumento do TBARS, diminuição nos níveis de SHNP e AA e inibição da enzima SOD no fígado dos jundiás. O (PhSe)2 foi efetivo em proteger o tecido hepático dos jundiás por diminuir o TBARS, aumentar os níveis de SHNP, AA, e a atividade da SOD. Porém o (PhSe)2 não foi eficaz na recuperação dos efeitos causados pelo aumento da enzima hepática AST. No terceiro experimento investigou-se a capacidade do (PhSe)2 em reduzir o dano oxidativo em fígado, brânquias e músculo de carpas e jundiás expostos ao clomazone. Jundiás e carpas foram alimentados com uma dieta sem (PhSe)2 ou uma dieta contendo 3.0 mg/Kg de (PhSe)2 por 60 dias e após foram expostos a 1 mg/L do clomazone (192 horas). No final do período de exposição, parâmetros oxidativos e defesas antioxidantes foram determinados. Jundiás expostos ao clomazone apresentaram aumento do TBARS em fígado e músculo e da proteína carbonil em fígado e brânquias. Além da diminuição nos níveis de SHNP em fígado e brânquias, AA em fígado e inibição da enzima glutationa peroxidase (GPx) em fígado. O (PhSe)2 reverteu alguns efeitos causados pelo clomazone em jundiás, prevenindo o aumento do TBARS e da proteína carbonil e aumentando os níveis de SHNP e AA. Por outro lado, o clomazone não causou uma aparente situação de estresse oxidativo em carpa e assim não podemos avaliar o papel do (PhSe)2 nesta espécie exposto a esse herbicida. Porém o (PhSe)2 em ambas as espécies diminuiu per se os níveis de TBARS em fígado e músculo, aumentou os níveis de SHNP e AA e atividade da enzima GPx em fígado. Considerando-se que a exposição aos herbicidas é cada vez mais frequente e que é a causa de diversas alterações em peixes, os resultados desses trabalhos são de grande importância, uma vez que o (PhSe)2 pode representar uma alternativa para prevenir ou atenuar a toxicidade causada por herbicidas em diferentes espécies de peixes de importância comercial.

Coordenação de Aperfeiçoamento de Pessoal de Nível Superior / Treatment with neuroleptic drugs has been associated to side effects like tardive diskynesia and hepatic damage. In spite of the several reports of hepatotoxicity after neuroleptic administration, few data are available in the literature about these effects and the precise mechanisms by which neuroleptics induce hepatotoxicity remain unclear. In the same way, there are few studies about the effects of neuroleptics on kidney. In this way, the first aim of the present work was to assess the effects of chronic exposure to fluphenazine in liver and kidney of rats, as well as the protective effect of diphenyl diselenide on the fluphenazine-induced damage (article 1). Long-term treatment with fluphenazine caused an increase in lipid peroxidation levels in liver and kidney homogenates, a decrease in hepatic SOD activity, and an increase in hepatic CAT activity. Diphenyl diselenide was able to protect liver and kidney from lipid peroxidation, ameliorate SOD activity in liver, and prevent the increase in hepatic CAT activity. Diphenyl diselenide treatment did not affect δ-ALA-D activity, but fluphenazine and/or in combination with diphenyl diselenide showed an inhibitory effect on δ-ALA-D activity in liver and kidney. The second objective of this study was to determine whether the treatment with haloperidol (HP), valerian or both in association impairs liver or kidney functions (article 2). Valerian did not affect oxidative stress parameters in the liver or kidney of rats. HP only increased glutathione (GSH) depletion in liver, but not in kidney. However, when HP was associated with valerian, an increase in lipid peroxidation levels and reactive species production was observed in the hepatic tissue. HP and valerian when administered independently did not affect the activity of hepatic and renal δ-ALA-D, however, these drugs administered concomitantly provoked an inhibition of hepatic δ-ALA-D activity. Serum aspartate aminotransferase (AST) activity was not altered by any treatment. However, serum alanine aminotransferase (ALT) activity was higher in the HP group and HP plus valerian group. Taken together, these results indicate the relationship between the treatment with flufenazine and the oxidative stress, and also point to the protective role of diphenyl diselenide on the oxidative damage induced by fluphenazine in liver. Our data also suggest adverse interactions between haloperidol and valerian treatments causing hepatic damage related to oxidative stress. / O tratamento com drogas neurolépticas tem sido associado a efeitos colaterais como a discinesia tardia (DT) e o dano hepático. Apesar dos inúmeros casos de hepatotoxicidade após a administração de neurolépticos, são escassos os dados na literatura a respeito desses efeitos e o mecanismo exato pelo qual neurolépticos induzem hepatotoxicidade permanece incerto. Da mesma forma, existem poucos estudos relatando os efeitos dos neurolépticos sobre o rim. Dessa forma, o primeiro objetivo deste trabalho foi avaliar os efeitos da exposição crônica à flufenazina em fígado e rim de ratos bem como o efeito protetor do disseleneto de difenila sobre o dano induzido por flufenazina (artigo 1). O tratamento prolongado com flufenazina causou um aumento na peroxidação lipídica no fígado e no rim, uma diminuição na atividade da SOD hepática, e um aumento na atividade da CAT hepática. O disseleneto de difenila foi capaz de proteger o fígado e o rim da peroxidação lipídica, melhorou a atividade da SOD no fígado, e preveniu o aumento na atividade da CAT no fígado. O tratamento com disseleneto de difenila não afetou a atividade da δ-ALA-D, mas a flufenazina e/ou em combinação com disseleneto de difenila demonstrou ter efeito inibitório sobre a atividade da δ-ALA-D no fígado e no rim. O segundo objetivo deste estudo foi determinar se o tratamento com haloperidol (HP), valeriana ou a associação de ambas as drogas pode alterar as funções hepáticas e renais (artigo 2). A valeriana não afetou nenhum parâmetro de estresse oxidativo no fígado e no rim dos ratos. O HP apenas aumentou a depleção de glutationa (GSH) no fígado, mas não no rim. Entretanto, quando o HP foi associado com a valeriana, um aumento na peroxidação lipídica e produção de espécies reativas foram observados no tecido hepático. HP e valeriana quando administrados independentemente não afetaram a atividade da δ-ALA-D hepática e renal, contudo, quando estas drogas foram administradas concomitantemente provocaram uma inibição da atividade da δ-ALA-D hepática. A atividade da aspartato aminotransferase (AST) do soro não foi alterada por nenhum dos tratamentos. No entanto, a atividade da alanina aminotransferase (ALT) do soro estava aumentada nos grupos tratados com HP e HP mais flufenazina. Juntos estes resultados indicam uma relação entre o tratamento com flufenazina e o estresse oxidativo, e também apontam para o papel protetor do disseleneto de difenila no dano oxidativo induzido por flufenazina no fígado. Nossos dados também sugerem interações adversas no tratamento com haloperidol e valeriana, ocasionando dano hepático associado ao estresse oxidativo.

Polybrominated dibenzo-p-dioxins (PBDD) and dibenzofurans (PBDF) are a group of compounds of emerging interest as potential environmental stressors. Their structures as well as toxic responses are similar to the highly characterized toxicants polychlorinated dibenzo-p-dioxins. High levels of PBDDs have been found in algae, shellfish, and fish, also from remote areas in theBaltic Sea. This thesis presents studies on PBDD behavior in fish and offspring, and natural formation of PBDDs from naturally abundant phenolic precursors. The uptake, elimination, and maternal transfer of mono- to tetraBDD/Fs were investigated in an exposure study reported in Paper I. The effects of PBDDs in fish were examined in a dose-response study (Paper II). It was shown that fish can assimilate PBDD/Fs from their feed, although non-laterally substituted congeners were rapidly eliminated. Laterally substituted congeners were retained as was congeners without vicinal hydrogens to some extent. PBDD/Fs were transferred to eggs, and congeners that were rapidly eliminated in fish showed a higher transfer ratio to eggs. Exposure to the laterally substituted 2,3,7,8-TeBDD had significant effects on the health, gene expression and several reproduction end-points of zebrafish, even at the lowest dose applied. The geographical and temporal variations of PBDD in biota samples from the Baltic Seasuggest biogenic rather than anthropogenic origin. In Paper III, bromoperoxidase-mediated coupling of 2,4,6-tribromophenol yielded several PBDD congeners, some formed after rearrangement. The overall yield was low, but significantly higher at low temperature, and the product profile obtained was similar to congener profiles found in biota from the Swedish West Coast. In Paper IV, photo­chemi­cally induced cyclization of hydroxylated polybrominated diphenyl ethers under natural conditions produced PBDDs at percentage yield. Rearranged products were not detected, and some abundant congeners do not seem to be formed this way. However, the product profile obtained was similar to congener profiles found in biota from the Baltic Proper. Since the PBDD congeners found in biota have a high turn-over in fish, the exposure must be high and continuous to yield the PBDD levels measured in wild fish. Thus, PBDDs must presumably be formed by common precursors in general processes, such as via enzymatic oxidations, UV-initiated reactions or a combination of both. The presented pathways for formation of PBDDs are both likely sensitive to changes in climatic conditions.

V oblasti nových nízkomolekulárních organických materiálů patří deriváty difenyldiketopyrrolopyrrolu (DPP), používané dříve jako barviva a pigmenty, k objektům vysokého zájmu pro jejich potencionální aplikace v moderních technologiích. Studium jejich optických vlastností ve vztahu k jejich chemické struktuře umožní využití jejich vysokého potenciálu ve vývoji pokročilých inteligentních materiálů. Přehled chemických a fyzikálních vlastností DPP derivátů a zhodnocení současného stavu řešené problematiky jsou uvedeny v teoretické části této práce. Tři hlavní procesy studované v této práci jsou: klasická absorpce a emise, dvoufotonová absorpce (TPA) a zesílená spontánní emise (ASE). Výsledky budou diskutovány a shrnuty ve dvou částech: první zahrnuje první dvě výše zmíněné oblasti a druhá problematiku zesílené spontánní emise.

No description available.

No description available.

3-Chloro-4,4,5-trimethyl-3,5-diphenyl-4,5-dihydro-3H-pyrazole (3b) and 3-bromo-4,4,5-trimethyl-3,5-diphenyl-4,5-dihydro-3H-pyrazole (3c) were prepared for the thermolysis project. The thermal decompositions of 3b and 3c were monitored using 1H NMR spectroscopy. Plots of ln (% starting material) vs. time (sec) were linear for at least two half lives and the first order rate constants were determined over at least a 30o temperature range. The relative reactivity was found to be 3c > 3b. The activation parameters determined for the thermal decomposition of the pyrazoline at 150oC were found to be: for 3b &#;H‡ = 33 &#;1.0 kcal/mol, &#;S‡ = -2.4 &#; 0.07eu , k150 0 = 7.34 &#; 0.44 x 10 -5 s-1 ; for 3c &#;H‡ = 30&#;0.2 kcal/mol, &#;S‡ = -6.9 &#;0.03 eu, k150o = 42.3&#;0.7 x 10-5 s-1. Thermal decomposition of 3b both neat and in dibromobenzene (DBB) resulted in the formation of an intermediate 2,3-diphenyl-4-methyl-1,3-pentadiene (8) as a major product and minor isomers of 8. These intermediates then thermally decomposed to 1,1,3-trimethyl-2-phenyl-1H-indene (9) via an acid catalyzed process. In order to gain a mechanistic understanding (ionic vs. radical pathways) of the thermal decomposition of 3b, a product study was conducted in protic solvents. In methanol and ethanol, 3b underwent an ionic reaction (SN1-type) with the solvent to produce 3-methoxy/ethoxy-4,4,5-trimethyl-3,5-diphenyl-4,5-dihydro-3H-pyrazole (3/3d) in good yield. The reaction of 3b with refluxing protic solvents led to the development of new method for the synthesis of alkoxy-4,5-dihydro-3H-pyrazoles which is both safe and efficient.

Persistent organic pollutants (POPs) are hydrophobic substances that readily sorb to organic matter in particles and colloids instead of being freely dissolved in the water phase. This sorption affects the bio­availability and environmental transport of the POPs. The major part of this thesis concerns the role of sediments as secondary sources of POPs. As the primary emissions decrease, contaminated sediments where POPs have accumulated can become the main source of contamination. If the contaminated sediment by time becomes covered with cleaner layers, the POPs are buried and no longer in contact with the aquatic environment. Experiments in this thesis showed, however, that new invading species can alter the sediment-water dynamics as a result of their bioturbation, i.e. mixing of sediment particles and pore-water. Marenzelleria spp., invading species in the Baltic Sea that burrow deeper than native species, were found to increase the remobilization of buried contaminants. The sediment-to-water flux was inversely related to the burial depth (2-10 cm) of the POP congeners (polychlorinated biphenyls (PCBs) and polybrominated diphenyl ethers) and also inversely related to the hydrophobicity of the congener. The flux was therefore most pronounced for less hydrophobic contaminants, which was linked to the bioirrigating behaviour of these species. Marenzelleria spp. also accumulated the buried POPs and increased concentrations in surface sedi­ment. Contaminants previously considered buried at a ’safe’ depth can thus be remobilized as a result of the invasion of Marenzelleria spp. in the Baltic Sea. One method to decrease the remobilization of contaminants from sediments is ’capping’, i.e. a layer of clean material is placed as a cap on the sediment. By amending the cap with active materials, which sequester the POPs and decrease their availability, thinner layers can be used (’active capping’ or ’thin-layer capping’). Results from an experiment with thin-layer capping using different active materials (activated carbon (AC) and kraft lignin) showed that both the sediment-to-water flux and the bioaccumulation by benthic species of polychlorinated dibenzo-p-dioxins and dibenzofurans (PCDD/Fs), hexachlorobenzene (HCB) and octachlorostyrene (OCS) decreased with increased thick­ness of the cap layer (0.5-5 cm). Amendments with active materials further increased the cap efficiency. AC was more efficient than kraft lignin, and a 3 cm cap with 3.3% AC reduced the flux and bioaccumulation with ~90%. The reduction of the sediment-to-water flux was inversely related to the hydrophobicity of the POP, and reductions in the flux had similar magnitudes as reductions in the concentration in deep-burrowing polychaetes, demonstrating the importance of bioturbation for sediment-to-water transport. In a one-year study on the levels of PCDD/Fs, PCBs, and HCB in a coastal area of the Baltic Sea, the correlations between the POP levels and the levels of particles and organic carbon in the water were found to differ for POPs of different structure and hydrophobicity. The levels of PCDD/Fs decreased to one third in May, which could be related to the increased sedimentation, i.e. water-to-sediment transport, during spring bloom.

Les ignifuges sont ajoutés à divers produits afin de les rendre conformes aux normes d’inflammabilité. Les plus communs sont les polybromodiphényléthers (PBDE) et les esters d’organophosphorés (OPE), qui sont détectés en forte proportion dans la population générale. Quelques industries, comme celle du recyclage électronique, peuvent exposer les travailleurs à des niveaux élevés de ces ignifuges, dont certains sont soupçonnés d’être des perturbateurs endocriniens. L’objectif de cette thèse était d’évaluer l’exposition à des ignifuges chez les travailleurs et d’étudier les effets endocriniens associés. Trois types de données ont été utilisés. D’abord, deux bases de données populationnelles ont permis de déterminer les valeurs biologiques de base des PBDE chez les travailleurs des populations générales canadienne et états-unienne, et d’identifier les secteurs industriels les plus exposés. Ensuite, une revue systématique de littérature a recensé les niveaux d’exposition professionnelle aux ignifuges dans diverses industries en portant un regard critique sur les méthodes de prélèvement. Finalement, des prélèvements d’air en poste personnel, d’urine et de sang ont été réalisés auprès de 100 travailleurs dans six entreprises de recyclage électronique et une de recyclage commercial. Des modèles Tobit et des régressions de Cox inversées ont identifié les tâches les plus exposantes. L’association entre les mesures biologiques d’exposition et les niveaux d’hormones thyroïdiennes et sexuelles a été explorée avec des modèles Tobit et des régressions sur composantes principales. L’analyse des données populationnelles a révélé que les travailleurs canadiens, tous secteurs confondus, avaient des concentrations sériques de PBDE 10 à 20% plus élevées que celles des non-travailleurs. La revue systématique a identifié les milieux du recyclage électronique, de la fabrication de câbles, du transport aérien et des casernes d’incendie comme étant parmi les plus exposants aux ignifuges, particulièrement au BDE209. Cependant, les méthodes de prélèvement utilisées dans ces études étaient généralement peu appropriées pour les ignifuges. L’analyse des données de l’étude terrain a mis en évidence des concentrations d’ignifuges dans l’air plus élevées dans le recyclage électronique que dans le recyclage commercial, avec une concentration en BDE209 plus élevée que toutes les valeurs publiées à ce jour (moyenne géométrique [MG] : 5100 ng/m³). Les tâches de démantèlement et de compactage étaient respectivement associées à des expositions en moyenne 2,2 et 1,4 fois plus élevées que celle de supervision. Finalement, les concentrations sanguines de BDE209 (MG : 18 ng/g lipides) chez les travailleurs du recyclage électronique étaient plus élevées que dans le recyclage commercial (MG : 1,7 ng/g lipides), mais moins élevées que celles rapportées dans la fabrication de câbles (moyenne : 54 ng/g lipides). On a estimé chez l’homme des diminutions de 18% de la testostérone libre et totale pour un doublement de la concentration de tb-TPhP (métabolite OPE), et une augmentation de 16% de l’estradiol pour un doublement de la concentration de o-iPr-DPhP (métabolite OPE). Cette thèse montre que l’exposition aux ignifuges est très répandue, particulièrement chez les travailleurs de quelques industries. Les concentrations plus élevées de certains ignifuges dans le recyclage électronique par rapport aux autres industries, et l’association entre l’exposition aux OPE et les niveaux d’hormones sexuelles chez l’homme ont été identifiées pour la première fois. Bien que devant être reproduits, ces résultats justifient des efforts préventifs de maîtrise de l’exposition aux ignifuges dans cette industrie. / Flame retardants are added to various products to comply to flammability standards. The most common are polybrominated diphenyl ethers (PBDEs) and organophosphate esters (OPEs), which are detected in high proportion in the general population. A few industries, such as electronic recycling, can expose workers to high levels of flame retardants, some of which are suspected of being endocrine disruptors. The objective of this thesis was to evaluate the exposure to flame retardants in workers and to study the associated endocrine effects. Three types of data were used. First, two population databases were used to determine baseline PBDE levels for workers in the general population in Canada and the United States, and to identify the major industrial sectors that are exposed the most. Then, a systematic literature review identified levels of occupational exposure to flame retardants in various industries while critically examining sampling methods. Finally, personal air, urine and blood samples were collected from 100 workers in six electronic recycling and one commercial recycling companies. Tobit models and reverse Cox regressions identified the most exposing tasks. The association between biological concentrations of flame retardants and thyroid and sex hormone levels was explored with Tobit models and principal component regressions. The analysis of the population data revealed that Canadian workers, taking all sectors into consideration, had serum PBDE levels 10 to 20% higher than those of non-workers. The systematic review identified electronic recycling, cable manufacturing, air transport and fire stations as some of the workplaces where flame retardants were found in the highest concentrations, particularly BDE209. However, the sampling methods used in these studies were generally not optimal for flame retardants. Analysis of the field study data revealed higher air concentrations of flame retardants in electronic recycling than in commercial recycling, with a higher BDE209 concentration than all values published to date (geometric mean [MG]: 5100 ng/m³). Dismantling and bailing tasks were associated with exposures averaging 2.2 and 1.4 times higher than supervisory tasks, respectively. Finally, blood concentrations of BDE209 (MG: 18 ng/g lipid) in electronic recycling workers were higher than in commercial recycling (MG: 1.7 ng/g lipid), but lower than those reported in cable manufacturing (average: 54 ng/g lipid). Decreases of 18% in free and total testosterone were estimated in humans for a doubling of the concentration of tb-TPhP (OPE metabolite), and a 16% increase in estradiol for a doubling of the concentration of o-iPr-DPhP (OPE metabolite). This thesis shows that exposure to flame retardants is widespread, particularly among workers in a few industries. The higher concentrations of some flame retardants in electronic recycling compared with other industries, and the association between exposure to OPEs and sex hormone levels in humans were identified for the first time. Although these results must be reproduced, they justify preventive efforts to control exposure to flame retardants in this industry.

Avec plus de 350 000 produits chimiques utilisés et de nouveaux arrivant sur le marché chaque année, des outils rapides et à coûts réduits sont nécessaires pour l'étude de ces produits. L’évaluation des risques pour ces produits est généralement faite à partir d’études animales, mais celles-ci présentent plusieurs limitations. Par exemple, évaluer le potentiel cancérogène d’une substance prendre jusqu'à trois ans et coûter six millions de dollars. En outre, il a été démontré que les modèles animaux n'ont qu'un faible pouvoir prédictif par rapport aux effets chez l’humain. Pour surmonter ces obstacles, on assiste actuellement à un mouvement mondial en faveur du développement et de l'acceptation de nouvelles approches méthodologiques (NAM) pour la priorisation des produits chimiques et l'évaluation des risques. Notre objectif était d’élaborer et d'évaluer une nouvelle approche d’extrapolation in vitro à in vivo (IVIVE) pour établir des niveaux d'exposition acceptables chez l'homme en combinant des des études in vitro et des outils de modélisation toxicologique. À cette fin, nous avons développé et évalué un outil informatique utilisé dans l'approche IVIVE et mené des études de cas sur deux produits chimiques pour lesquels étaient disponibles des données in vitro, des modèles d'exposition, et des études épidémiologiques associant l’exposition à des effets néfastes chez l’humain. Dans le premier article, nous avons développé et évalué un modèle de bilan de masse dynamique (IV-MBM DP v1.0) pour estimer les concentrations intracellulaires au cours d'expériences in vitro avec administration répétée, incluant une description du transport facilité. Pour évaluer la précision du modèle, nous avons paramétré et appliqué le modèle à des scénarios de dose unique et de doses répétées, et évalué les concentrations estimées aux données empiriques. En outre, nous avons simulé des scénarios de dosage répété pour des produits chimiques organiques représentant une diversité de caractéristiques physico-chimiques, et nous avons comparé leur dispersion dans le système au fil du temps. Dans l'ensemble, pour les scénarios de dosage unique et répété, la concordance entre les données simulées et expérimentales a illustré le pouvoir prédictif du modèle. i Dans les deuxième et troisième articles, nous nous sommes concentrés sur l'utilisation et l'évaluation de notre nouvelle approche IVIVE en faisant deux études de cas impliquant l'exposition placentaire et lactationnelle à des polluants organiques persistants. La première étape de notre méthodologie a été la sélection d'un point de départ à partir d'une étude in vitro utilisant des cellules humaines. Ensuite, nous avons appliqué la modélisation benchmark dose pour obtenir la concentration associée à un changement relatif de 5% de la réponse par rapport au contrôle. Nous avons ensuite appliqué la modélisation de de bilan de masse pour déterminer la concentration cellulaire pour un point de départ conduisant à un changement de réponse de 5%. Un modèle toxicocinétique pour le transfert placentaire et par l’allaitement a ensuite été utilisé pour calculer la dose équivalente administrée et la concentration plasmatique associée, et des facteurs d'incertitude (variabilité interindividuelle (10) et sous-chronique à chronique (10)) ont été appliqués pour calculer les apports quotidiens tolérables et les équivalents de biosurveillance. Les équivalents de biosurveillance ont été comparés aux concentrations dans le sang de la mère et du cordon ombilical mesurées dans les études épidémiologiques. Nos études de cas portaient sur la neurotoxicité développementale du 2,2',4,4'-tétrabromodiphényléther (BDE-47) et sur l'obésogénicité du dichlorodiphényldichloroéthylène (p,p'-DDE). Pour les deux études, les apports quotidiens tolérables calculés en tenant compte des facteurs d’incertitude étaient plus faibles que les valeurs toxicologiques de référence déterminées sur la base d’études animales. En outre, les deux études de cas ont produit des équivalents de biosurveillance se situant dans la gamme des concentrations maternelles et du cordon ombilical mesurées dans les études épidémiologiques. Dans l'ensemble, l'évaluation de notre modèle de bilan de masse, ainsi que les valeurs conservatrices générées par l'approche IVIVE dans nos études de cas, renforcent la confiance dans les NAM, ce qui est essentiel pour leur adoption future par les organismes de réglementation. / With over 350,000 chemicals in use and more entering the market every year, cost-effective and time-efficient tools are necessary for the investigation of these products. Whole animal models are traditionally used and accepted by regulatory agencies; however, animal models carry multiple limitations. Specifically, animal models may take up to three years and six million dollars to investigate the carcinogenicity of a compound. Additionally, animal models have been shown to have poor predictive power for human safety. To overcome these obstacles, a global movement toward the development and acceptance of new alternative methods (NAMs) for chemical prioritization and risk assessment is taking place. Our objective was to develop and evaluate a novel in vitro to in vivo (IVIVE) approach to establish acceptable exposure levels in humans by combining novel in vitro and biological/computational modeling technologies for chemical safety assessment. To this end, we tested and evaluated a computational tool utilized in the IVIVE approach, and conducted proof-of-concept studies on two case chemicals with publicly available in vitro data, exposure models, and epidemiological studies demonstrating adverse health effects. In the first paper, we aimed to develop and evaluate a dynamic partitioning mass-balance model (IV-MBM DP v1.0) to estimate intracellular concentrations during in vitro experiments of repeat dosing, and incorporate facilitated transport into the model. To evaluate the model accuracy, we parametrized and applied the model to single dose and repeat dosing scenarios and assessed the output against empirical data. In addition, we simulated repeat dosing scenarios for organic chemicals with different properties and compared their dispersion within the system over time. Overall, for single and repeat dosing scenarios, concordance between simulated and experimental data illustrated the predictive power of the model. In the second and third papers, we focused on the use and evaluation of our novel IVIVE approach through case studies involving placental and lactational exposure to persistent organic pollutants. The first step of our methodology was the selection of a point of departure from an in vitro study utilizing human cells. Next, we applied benchmark dose modeling to obtain the nominal iv concentration at a 5% relative change in response from control. We subsequently applied mass- balance modeling to determine the cellular concentration for the POD leading to a 5% change in response. A toxicokinetic model for placental transfer and lactation was then used to calculate the administered equivalent dose and associated maternal and cord plasma concentration, and uncertainty factors (interindividual variability (10) and subchronic to chronic (10)) were applied to calculate tolerable daily intakes and biomonitoring equivalents. Biomonitoring equivalents were compared to concentrations in maternal and cord blood measured in epidemiological studies. Our case studies were on 2,2',4,4'-tetrabromodiphenyl ether (BDE-47) developmental neurotoxicity and dichlorodiphenyldichloroethylene (p,p’-DDE) obesogenicity. For both studies, calculated tolerable daily intakes accounting for uncertainty factors were more conservative than the reference doses determined through the use of whole animal models. Moreover, both case studies produced biomonitoring equivalents within the range of maternal and cord levels measured in epidemiological studies. Overall, assessment of our IV-MBM DP v1.0 mass-balance model, as well as the demonstrated protective quality of the IVIVE approach in our case studies, enhances confidence in NAMs, which is essential for their future adoption by regulatory agencies.