Les poissons sont parmi les modèles aquatiques les plus utilisés pour l’évaluationdes dangers des substances chimiques avant leur mise sur le marché européen(REACh (Registration, Evaluation, Autorisation and Restriction of CHemicals)).Actuellement, cette réglementation ainsi que la directive européenne sur la protectiondes animaux utilisés à des fins scientifiques (2010/63/UE) promeuvent la mise enplace de méthodes alternatives en expérimentation animale. Ces méthodes ont pourbut de remplacer les modèles animaux chaque fois que cela est possible, de réduirele nombre d’animaux utilisés en expérimentation et d’optimiser la méthodologieappliquée aux animaux. Cette thèse vise à comparer la sensibilité de deux de cesoutils alternatifs, les lignées cellulaires et les tests embryo-larvaires poissons, enutilisant des toxiques modèles puis mettre en oeuvre ces outils pour évaluer la toxicitéde mélanges environnementaux de polluants : microplastiques et hydrocarbures(pétrole Arabian Light). Les composés modèles (B(a)P, Cd, MMS, PCB126) ont permisde valider trois biomarqueurs : la production d’espèces réactives de l’oxygène surlignées cellulaires de poissons, le test micronoyaux par cytométrie en flux et lechallenge infectieux sur larves de Médaka. Ces biomarqueurs associés à des analyseschimiques, biochimiques et physiologiques ont permis d’évaluer la toxicité demélanges environnementaux d’hydrocarbures (extrait aqueux de pétrole Arabian =WAF) et de microplastiques. Les WAF présentent une toxicité sur les lignéescellulaires de poissons (induction de l’activité EROD, génotoxicité) ainsi que surembryons et larves de Médaka (comportement, biométrie, EROD, génotoxicité). Lespoissons comme les cellules sont particulièrement sensibles au WAF de l’ArabianLight. La contamination aux microplastiques (MP) environnementaux a révélé unetoxicité des contaminants associés au MP sur les lignées cellulaires et les larves depoisson. L’ingestion de particules de plastiques par les larves a induit des effets létauxet sublétaux (biométrie, comportement et EROD). L’ingestion des particules plastiquespar les larves a été confirmée par microscopie biphotonique. Cette étude a permisd’évaluer la sensibilité et la complémentarité de ces outils in vitro pour l’évaluation desdangers et des risques associés aux substances chimiques. / Fish are among the most widely used aquatic model for assessing the chemicalthreat before they are placed on the European market (REACh (Registration,Evaluation, Authorization and Restriction of CHemicals)). Currently, this regulation aswell as the European directive on the protection of animals used for scientific purposes(2010/63/EU) promote the establishment of alternative methods in animal testing.These methods are intended to replace animal models whenever possible, to reducethe number of animals used in experiments and to optimize the methodology appliedto animals. This thesis aims to compare the sensitivity of two of these alternative tools,cell lines and fish embryo-larval tests, using model toxicants. Then, these tools wereused to evaluate the toxicity of environmental mixtures of pollutants: microplastics andhydrocarbons (Arabian Light oil). The model compounds (B(a)P, Cd, MMS, PCB126)valid three biomarkers: reactive oxygen species (ROS) production on fish cell lines,micronucleus assay by flow cytometry and infectious challenge on Medaka larvae andjuveniles. These biomarkers combined with chemical, biochemical and physiologicalanalyzes have assessed toxicity of environmental mixtures of hydrocarbons (aqueousextract of Arabian oil = WAF) and microplastics. WAF are toxic to fish cell lines (ERODactivity induction and genotoxicity) as well as to Medaka embryos and larvae (behavior,biometrics, EROD, genotoxicity). Fish like cells seem to be particularly susceptible toArabian Light WAF. Contamination with environmental microplastics (MP) hasrevealed a toxicity of MP-associated contaminants on cell lines and fish larvae. Theingestion of plastic particles by the larvae induced lethal and sublethal effects(biometrics, behavior and EROD). The ingestion of the plastic particles by the larvaewas confirmed by two-photon microscopy. This study assessed the sensitivity andcomplementarity of these in vitro tools for assessing hazards and risks associated withchemicals.

La perte de biodiversité induite par les humains touche plus particulièrement les espèces de grande taille corporelle et génère des pressions de sélection contre les grands individus. Un nombre croissant d’études montrent que la diminution des abondances de ces espèces s’accompagne d’une évolution rapide vers des tailles corporelles réduites. La problématique générale de la thèse était d’étudier expérimentalement, de manière intégrée, « des gènes à l’écosystème », les implications évolutives et écologiques de la perte rapide de biodiversité.À l’aide d’une expérience de sélection artificielle sur la taille corporelle de médaka (Oryzias latipes) pendant 6 générations, j’ai montré que (1) un ensemble de traits d’histoire de vie corrélé génétiquement à la taille (e.g. croissance somatique, âge et taille à maturité sexuelle, fécondité) pouvaient évoluer rapidement, (2) la réponse des traits des médakas dépend de la direction de sélection, et que (3) les changements phénotypiques peuvent être reliés à des changements d’expressions d’hormones hypophysaires impliqués dans la régulation de la croissance (i.e. hormone de croissance) et la reproduction (i.e. hormone de croissance et gonadotropines). Ces résultats suggèrent que les mécanismes d’adaptations des populations aux pressions anthropiques pourraient fortement modifier des traits clés pour leur maintien dans les écosystèmes. Par ailleurs, dans une autre expérience, j’ai montré que les variations phénotypiques (taille et de forme d’un médaka), peuvent avoir autant d’importance sur l’intensité de la cascade trophique qu’elles génèrent, que les variations démographiques (présence-absence du médaka). Ce résultat révèle l’importance des traits des organismes dans l’écosystème et suggère que des changements micro-évolutifs pourraient se répercuter dans les réseaux d’interactions biotiques. Cette thèse souligne la nécessité de mieux comprendre les mécanismes adaptatifs afin d’appréhender au mieux les conséquences écologiques des pressions de sélection d’origine anthropique qui s’exercent sur les populations naturelles. Elle ouvre des perspectives sur la compréhension jointe des mécanismes évolutifs et écologiques qui peuvent agir en retour l’un sur l’autre dans des boucles de rétrocontrôle éco-évolutives. / Biodiversity loss induced by humans particularly affects species which large body size and generates selection pressures against large individuals. A growing number of studies show that the decline in abundance of these species is accompanied by a rapid shift towards smaller body sizes. The aim of the thesis was to study experimentally, in an integrative approach, "from genes to ecosystem," the evolutionary and ecological implications of the rapid loss of biodiversity. I applied an artificial selection on body size of medaka (Oryzias latipes) during 6 generations, and I showed that (1) a set of life history traits genetically correlated to the size (e.g. somatic growth, age and size at sexual maturity, fecundity) could evolve rapidly, (2) the response of medaka traits depend on the selection direction, and (3) the phenotypic changes can be related to changes of pituitary hormones expressions involved in the regulation of growth (i.e. growth hormone) and reproduction (i.e. growth hormone and gonadotropins). These results suggest that the adaptation mechanisms of populations to anthropogenic pressures could significantly alter key features for keeping them in ecosystems. Furthermore, in another experiment, I showed that phenotypic variations (size and shape of a medaka), may have as much importance on the intensity of the trophic cascade they generate, as demographic variations (presence-absence of medaka). This result shows the importance of the traits of organisms

Recent empirical studies have demonstrated inter-generational morphological and life-history changes in fish stocks that have been impacted by size-selective harvest. Evolutionary processes in biological populations occur through differential survival and reproductive success based, in part, upon individual phenotypic variability. Fishing is a source of directional selection resulting in the directed removal of some phenotypes; however, many aspects of the evolutionary effects of fishing remain have yet to be described. In order to better understand the life-history and morphological changes that occur as a result of size-selective fishing, and their effect on fishery dynamics, I first determined the suitability of Japanese medaka (Oryzias latipes) for selection experiments. I performed selection experiments using Japanese medaka and report how morphology and life-history characteristics changed over multiple generations of selection. I then used these patterns of change in life-history and morphology to validate individual-based simulation candidate models to test general mechanisms of life-history relationships. Finally, I applied the individual-based simulation modeling approach in order to describe how biological and fishery characteristics change in a large, age-structured population exposed to size-selective fishing over multiple generations. I found that the Japanese medaka has attractive characteristics for biological investigation. The selection experiments indicated large changes in the age-atmaturity, including a nearly 50% decrease over four generations in the most intense sizeselective removal regimes. However, I did not observe significant changes in length-at-age or weight-at-age over the course of the experiment. Candidate simulation models were poor at predicting some aspects of the life-history characteristics of Japanese medaka. The simulation model to determine fishery characteristics predicted large decreases in yield and egg production as a result of decreases in length-at-age. Understanding the relationships of life-history characteristics and their role in determining population resilience is a step toward understanding the importance of evolutionary processes in fishery management. / Ph. D.

Comment la taille d'un organisme est-elle régulée au cours du développement embryonnaire ? Quels sont les mécanismes génétiques à l'origine de l'arrêt de la prolifération pendant la croissance d'un organisme pluricellulaire ? Afin d'identifier des acteurs de la sortie du cycle cellulaire au cours du développement, mon travail s’est orienté sur l’étude de gènes suppresseurs de tumeurs pendant la croissance du toit optique (TO) du médaka Oryzias latipes. Le TO, structure dorsale du cerveau moyen des Vertébrés, est un modèle particulièrement adapté à l’étude de la régulation de la prolifération. Trois zones de la marge vers le centre du TO sont discernables : une zone périphérique de prolifération, une zone intermédiaire de cellules sortant du cycle cellulaire et une zone centrale de cellules différenciées. Un crible d'expression par hybridation In Situ a été réalisé et a permis d'identifier 28 gènes exprimés dans le TO, suggérant leur implication dans le contrôle de la sortie du cycle cellulaire au cours du développement. Dans le but de caractériser in vivo la fonction de gènes issus de ce crible, le gène BTG1 (B-cell Translocation Gene 1) et les membres de sa famille, ont été étudiés au cours du développement du médaka. J’ai mené des expériences fonctionnelles sur BTG1, permettant de mettre en évidence son rôle central pour la morphogenèse du système nerveux central. De plus, une autre partie de mon travail s’est penchée sur l’étude de l’expression des membres de la voie de signalisation Hippo, bien connue et caractérisée chez la drosophile et les Mammifères pour son rôle dans le contrôle de la taille des organes via une régulation de l’arrêt de la prolifération. A l’issu de notre travail, une fonction de la voie de signalisation Hippo dans la formation du TO et des somites a pu être mise en évidence au cours du développement du médaka. / How is an organisms’ size regulated during embryonic development? What are the genetic mechanisms that control the proliferation arrest during multicellular organisms growth? In order to identify a cell cycle exit developmental actor genes, I have analysed the role of tumor suppressor genes (TSGs) in the optic tectum (OT) of the medaka Oryzias latipes. This structure is particularly suited for this kind of studies because, during its morphogenesis, there is a strict correlation between the position of a cell and its degree of differentiation. 3 zones can be easily distinguished from the border to the center: a marginal zone made of proliferative cells, an intermediate zone in which cells exit the cycle, and a central zone made of postmitotic cells. Using this criterium, I have performed an in situ hybridization expression screen on 150 TSGs on medaka embryos. The expression patterns of 28 TSGs in the OT suggest their implication in the OT proliferation arrest mechanisms. I focused my study on the BTG1 gene, implicated in many cancers, and for which few developmental data are available. A functional analysis on developing medaka embryos has been performed and permitted to highlight the essential role of BTG1 in central nervous system morphogenesis. Furthermore, I performed an expression study on Hippo signalling pathway components. Hippo pathway is well caracterised for its organ size control function in drosophila and Mammals. Our results show that this pathway could act in OT formation and somitogenesis in medaka fish.

Depuis le début des années 1990, de nombreuses équipes de recherche ont consacré leurs travaux à étudier les effets des perturbateurs endocriniens (PEs) sur l'homme et les espèces animales. Plusieurs polluants libérés dans l’environnement tels que les pesticides, les herbicides, les plastifiants industriels ou les résidus de médicaments ont ainsi le potentiel de perturber les équilibres hormonaux des organismes, induisant ainsi de graves conséquences sur leur développement et leur reproduction. Pour lutter contre ces dommages, diverses réglementations spécifiques et des systèmes de criblages se mettent en place pour détecter ces molécules. Ces systèmes doivent être rapides et fiables et les poissons téléostéens comme le medaka ou le poisson zèbre constituent d'excellents modèles pour détecter la présence de ces molécules et étudier leurs effets in vivo. Durant cette thèse nous avons étudié l’impact de certains PEs sur le développement embryonnaire en utilisant le poisson zèbre et le médaka comme modèle. Nous avons pu caractériser l'action du Bisphenol A sur la formation des otholites de l’oreille interne du poisson zèbre. En alliant des approches pharmacologiques et génétiques, nous avons identifié le récepteur nucléaire orphelin ERR comme une nouvelle cible in vivo de cette molécule. En parallèle, nous avons développé des lignées transgéniques rapportrices de médaka permettant de détecter la présence de polluants à activités androgénique ou anti-androgénique ce qui accroît ainsi la gamme des outils disponibles pour évaluer la présence des PEs dans les effluents liquides. / Since the early 1990s, many research teams have devoted their work to study the effects of endocrine disruptors (EDCs) in humans and animal species. Many pollutants released into the environment such as pesticides, herbicides, industrial plasticizers or drug residues have the potential to disrupt bodies’ hormonal balances, thus inducing a severe impact on their development and reproduction. To fight against these damages, various specific regulations and screening systems are setting up to detect these molecules. These systems must be fast, reliable. Teleost fish such as medaka and zebrafish are excellent models to detect the presence of these molecules and study their effects in vivo. In this thesis, we studied the impact of certain EDCs on the embryonic development using zebrafish and medaka as models. We characterized the action of Bisphenol A on the otoliths formation in the inner ear of zebrafish. By combining genetic and pharmacological approaches, we identified the orphan nuclear receptor ERRγas a new target of this molecule in vivo. In parallel, we have developed reporter transgenic lines of medaka to detect the presence of pollutants containing androgenic or anti-androgenic activities and thereby increasing the range of tools available to assess the presence of EDCs in liquid effluents.

La majorité des polluants organiques persistants, tels que les hydrocarbures aromatiques polycycliques (HAP), sont hydrophobes et de ce fait s’accumulent au cours du temps dans les sédiments aquatiques. Dans ce contexte, des tests ont été mis en œuvre sur embryons et pro-larves de truite arc-en-ciel Oncorhynchus mykiss et de médaka japonais Oryzias latipes pour étudier la toxicité de ces contaminants. Un sédiment artificiel et de nouveaux critères d’effets sur l’intégrité de l’ADN et l’activité natatoire ont été développés pour améliorer la reproductibilité et la sensibilité des tests. Ces bioessais ont été appliqués à la comparaison de la toxicité de trois mélanges de HAP : un extrait pyrolytique et deux extraits issus d’un pétrole léger Arabian Light et lourd de type Erika. Les trois mélanges de HAP ont été enrobés sur un sédiment artificiel ou sur des graviers à des concentrations comparables à celles retrouvées dans l’environnement. L’exposition des embryons à ces matrices contaminées a provoqué des perturbations de l’expression de gènes impliqués dans le fonctionnement mitochondrial, le métabolisme de la vitamine A, la formation de dommages à l’ADN ainsi que la synthèse d’hormones. Parallèlement ces mélanges ont induit des effets tératogènes, des perturbations de l’activité natatoire et des effets génotoxiques. Le degré de toxicité et le spectre d’effets induits étaient différents selon la composition des mélanges testés. Les mélanges pétrogéniques présentant une forte proportion en HAP de faibles poids moléculaires et HAP alkylés, se sont avérés plus toxiques envers les jeunes stades de développement de poissons que le mélange pyrolytique, composé en majorité de HAP à hauts poids moléculaires non substitués. Des résultats comparables ont été obtenus avec les modèles médaka japonais et truite arc-en-ciel. / Most persistent organic pollutants, such as polycyclic aromatic hydrocarbons (PAHs), are hydrophobic and therefore accumulate over time in aquatic sediments. In this context, tests were performed on rainbow trout Oncorhynchus mykiss and Japanese medaka Oryzias latipes embryos and prolarvae to study the toxicity of these contaminants. Artificial sediment and new integrative endpoints including DNA integrity and swimming activity were developed to improve reproducibility and sensitivity of the tests. These bioassays were applied to the toxicity assessment of three PAH mixtures: a pyrolytic extract and two petrogenic extracts from Arabian Light and Erika oils. The three PAH mixtures were spiked onto sediment or gravel at environmental relevant concentrations. Embryonic exposure to these contaminated matrices induced alteration of gene expressions involved in mitochondrial functions, vitamin A metabolism, DNA damages and hormone synthesis. In parallel, these mixtures induced teratogenicity, alteration of swimming activity and genotoxicity. The toxicity potency and spectrum of effects differed according to PAH mixture composition. The petrogenic mixtures, with high proportions of low molecular weight PAHs and alkylated PAHs, were more toxic to fish early life stages than the pyrolytic mixture, mainly composed of high molecular weight PAHs non substituted. Comparable results were obtained with Japanese medaka and rainbow trout early life stages.

In cultured medaka testis fragments, cells remained viable for the entire culture period (17h), and spermatids that developed from spermatocytes were viable and motile. Primary cultures were characterized over a period of two days with respect to cell viability and the distribution of adherent and suspended cells. These two cell populations were maintained in dynamic equilibrium in vitro for several days. Proliferating cells were predominant among clusters of suspended cells, as determined by BrdU labeling, and CFSE and propidium iodide PI labeling. Based on cytological criteria, the proliferating cells were mostly spermatogonia and possibly also preleptotene spermatocytes. Differentiation of spermatocytes into spermatids or spermatozoa was also observed, mainly among the suspended cells. These results suggest that the organ and primary culture systems are suitable systems for studying the effects of substances that interfere with spermatogenesis in the medaka, a model vertebrate. The organ and primary culture systems were used to analyze the effects of a synthetic estrogen, EE2, on cell proliferation in medaka testis. Both organ and primary culture were suitable for this purpose consistently small concentrations (0.01 and 1 nM) of EE2 stimulated cell proliferation slightly, while higher concentrations (100 nM) had an inhibitory effect. To investigate the effect of phytoestrogens on cell proliferation in spermatogenesis, selected flavonoids [genistein (1, 10, 100 µg/ml), quercetin (0.01, 1, 100 µM), and 8-prenylnarigenin (0.001, 0.1, 1, 10 µM)] were added to medaka testis primary cultures. Genistein and quercetin inhibited cell proliferation in the cultures while 8-prenylnarigenin had no effect. In a second series of experiments the addition of genistein (10 µg/ml) to primary cultures significantly inhibited both cell proliferation and cell differentiation as determined by flow cytometry using CFSE/PI labeling.

In cultured medaka testis fragments, cells remained viable for the entire culture period (17h), and spermatids that developed from spermatocytes were viable and motile. Primary cultures were characterized over a period of two days with respect to cell viability and the distribution of adherent and suspended cells. These two cell populations were maintained in dynamic equilibrium in vitro for several days. Proliferating cells were predominant among clusters of suspended cells, as determined by BrdU labeling, and CFSE and propidium iodide PI labeling. Based on cytological criteria, the proliferating cells were mostly spermatogonia and possibly also preleptotene spermatocytes. Differentiation of spermatocytes into spermatids or spermatozoa was also observed, mainly among the suspended cells. These results suggest that the organ and primary culture systems are suitable systems for studying the effects of substances that interfere with spermatogenesis in the medaka, a model vertebrate. The organ and primary culture systems were used to analyze the effects of a synthetic estrogen, EE2, on cell proliferation in medaka testis. Both organ and primary culture were suitable for this purpose consistently small concentrations (0.01 and 1 nM) of EE2 stimulated cell proliferation slightly, while higher concentrations (100 nM) had an inhibitory effect. To investigate the effect of phytoestrogens on cell proliferation in spermatogenesis, selected flavonoids [genistein (1, 10, 100 µg/ml), quercetin (0.01, 1, 100 µM), and 8-prenylnarigenin (0.001, 0.1, 1, 10 µM)] were added to medaka testis primary cultures. Genistein and quercetin inhibited cell proliferation in the cultures while 8-prenylnarigenin had no effect. In a second series of experiments the addition of genistein (10 µg/ml) to primary cultures significantly inhibited both cell proliferation and cell differentiation as determined by flow cytometry using CFSE/PI labeling.

<div>Following the 2010 Deepwater Horizon oil spill, extensive research has been conducted on the toxicity of oil and polycyclic aromatic hydrocarbons (PAHs) in the aquatic environment. The location and timing of the Deepwater Horizon surface slick coincided with the spawning seasons of many important pelagic and estuarine fish species. As such, there has been particular emphasis placed on the effects of PAHs on sensitive life history stages in fish, such as the embryonic and larval periods. Additionally, the spill occurred throughout the spring and summer months which, in estuaries, are marked by regular fluctuations in abiotic environmental factors such as dissolved oxygen, salinity, and temperature. Until recently, there has been little work done to elucidate the combined effects that PAHs from oil spills and adverse environmental conditions (hypoxia, increased salinity, and elevated temperatures).</div><div>Work presented in this dissertation uses next generation sequencing technology (RNA Seq) to determine differential gene expression in larval estuarine teleosts following exposure to adverse environmental conditions and PAHs. Downstream canonical pathway and toxicological function analysis were then applied to the identified differentially expressed genes (DEGs) to predict cardiotoxic responses at the organismal level. To verify the predicted responses, a phenotypic anchoring study was conducted and identified a cardiotoxic phenotype (pericardial edema) and reduced cardiac output in embryos exposed to oil. Finally, the mechano-genetic interplay governing the morphological development of the teleost heart was investigated and correlations between developmental gene expression and blood flow forces within the cardiovascular system were identified.</div>