L'oxydation anaérobie du méthane (AOM) couplé à la réduction du sulfate (AOM-SR) est un processus biologique médié par méthanotrophes anaérobie (ANME) et de bactéries sulfato-réductrices. La communauté scientifique s'inquiète de AOM, en raison de sa pertinence dans la régulation du cycle global du carbone et de la potentielle application biotechnologique pour le traitement de sulfate riches eaux usées.Pour améliorer les connaissances récentes sur les conditions de distribution et d'enrichissement ANME, cette recherche a étudié AOM-SR avec les objectifs suivants: (i) caractériser les communautés microbiennes responsables de AOM dans les sédiments marins, (ii) de les enrichir dans les bioréacteurs avec différentes configurations, à savoir bioréacteur à membrane (MBR), filtre biotrickling (BTF) et bioréacteur à haute pression (HPB), et (iii) d'évaluer l'activité de l'ANME et le processus AOM dans différentes conditions de pression et de température.Les microbes habitant peu profonde dans les sédiments de Marine lac Grevelingen (Pays-Bas) ont été caractérisés et leur capacité de faire AOM-SR a été évaluée. Un test d'activité a été réalisée en discontinu pour 250 jours, AOM-SR est mise en évidence par la production de sulfure et de la prise concomitante de sulfate et de méthane dans des rapports équimolaires et il a été atteint 5 µmoles par gramme de poids par jour de taux de réduction du sulfate. L'analyse des séquences de gènes 16SrRNA a montré la présence de méthanotrophes anaérobie ANME-3 dans les sédiments marins du lac Grevelingen.Deux configurations de bioréacteurs, à savoir MBR et BTF ont été opérés dans des conditions ambiantes pendant 726 jours et 380 jours, respectivement, pour enrichir les micro-organismes de Ginsburg Mud Volcano performantes AOM. Les réacteurs sont exploités en mode fed-batch pour la phase liquide avec un apport continu de méthane. Dans le MBR, une membrane d'ultrafiltration externe a été utilisée pour retenir la biomasse, alors que, dans la BTF, la rétention de biomasse a été accomplie par la fixation de la biomasse sur le matériau d'emballage. AOM-SR a été enregistrée seulement après ~ 200 jours dans les deux configurations de bioréacteurs. L'opération du BTF a montré l'enrichissement de l'ANME dans le biofilm par la méthode Illumina Miseq, en particulier ANME-1 (40%) et ANME-2 (10%). Dans le MBR, les agrégats d'ANME-2 et Desulfosarcina ont été visualisées par CARD-FISH. La production d'acétate a été observée dans le MBR, ce qui indique que l'acétate était un possible intermédiaire d'AOM. Bien que les deux configurations de bioréacteurs ont montré de bonnes performances, le taux de réduction du sulfate était légèrement plus élevée et plus rapide dans la BTF (1,3 mM par jour âpres 280 jours) que le MBR (0,5 mM par jour jour âpres 380 jours).Afin de simuler les conditions de suintement froid et de différencier l'impact des conditions environnementales sur AOM, les sédiments fortement enrichi avec le clade ANME-2a ont été incubées dans HPB à différentes températures (4, 15 et 25 °C à 100 bars) et pressions (20, 100, 200 et 300 bar à 15 °C). L'incubation à une pression de 100 bar et 15 ° C a été observé comme la condition la plus appropriée pour la phylotype ANME-2a, qui est similaire aux conditions in situ (Capitaine Aryutinov Mud Volcano, Golfe de Cadix). L'incubation de ce sédiment aux conditions in situ pourrait être une option privilégiée pour obtenir une activité AOM-SR plus élevée.Dans cette thèse, il a été démontré expérimentalement que la rétention de la biomasse et l'approvisionnement continu de méthane peuvent favoriser la croissance de la lente communauté microbienne qui oxyde le méthane en anaérobiose dans des bioréacteurs, même dans des conditions ambiantes. Par conséquent, la localisation des habitats de ANME dans des environnements peu profonds et l'enrichissant dans des conditions ambiantes peut être avantageuse pour les futures applications de la biotechnologie environnementale / Anaerobic oxidation of methane (AOM) coupled to sulfate reduction (AOM-SR) is a biological process mediated by anaerobic methanotrophs (ANME) and sulfate reducing bacteria. Due to its relevance in regulating the global carbon cycle and potential biotechnological application for treating sulfate-rich wastewater, AOM-SR has drawn attention from the scientific community. However, the detailed knowledge on ANME community, its physiology and metabolic pathway are scarcely available, presumably due to the lack of either pure cultures or the difficulty to enrich the biomass. To enhance the recent knowledge on ANME distribution and enrichment conditions, this research investigated AOM-SR with the following objectives: (i) characterize the microbial communities responsible for AOM in marine sediment, (ii) enrich ANME in different bioreactor configurations, i.e. membrane bioreactor (MBR), biotrickling filter (BTF) and high pressure bioreactor (HPB), and (iii) assess the AOM-SR activity under different pressure and temperature conditions.The microbes inhabiting coastal sediments from Marine Lake Grevelingen (the Netherlands) was characterized and the ability of the microorganisms to carry out AOM-SR was assessed. By performing batch activity tests for over 250 days, AOM-SR was evidenced by sulfide production and the concomitant consumption of sulfate and methane at approximately equimolar ratios and a sulfate reduction rate of 5 µmol sulfate per gram dry weight per day was attained. Sequence analysis of 16S rRNA genes showed the presence of ANME-3 in the Marine Lake Grevelingen sediment.Two bioreactor configurations, i.e. MBR and BTF were operated under ambient conditions for 726 days and 380 days, respectively, to enrich the microorganisms from Ginsburg Mud Volcano performing AOM. The reactors were operated in fed-batch mode for the liquid phase with a continuous supply of gaseous methane. In the MBR, an external ultra-filtration membrane was used to retain the biomass, whereas, in the BTF, biomass retention was achieved via biomass attachment to the packing material. AOM-SR was recorded only after ~ 200 days in both bioreactor configurations. The BTF operation showed the enrichment of ANME in the biofilm by Illumina Miseq method, especially ANME-1 (40%) and ANME-2 (10%). Interestingly, in the MBR, aggregates of ANME-2 and Desulfosarcina were visualized by CARD-FISH. Acetate production was observed in the MBR, indicating that acetate was a possible intermediate of AOM. Although both bioreactor configurations showed good performance and resilience capacities for AOM enrichment, the sulfate reduction rate was slightly higher and faster in the BTF (1.3 mM day-1 at day 280) than the MBR (0.5 mM day-1 at day 380).In order to simulate cold seep conditions and differentiate the impact of environmental conditions on AOM activities, sediment highly enriched with the ANME-2a clade was incubated in HPB at different temperature (4, 15 and 25 oC at 100 bar) and pressure (20, 100, 200 and 300 bar at 15 oC) conditions. The incubation at 100 bar pressure and 15 oC was observed to be the most suitable condition for the ANME-2a phylotype, which is similar to in-situ conditions where the biomass was sampled, i.e. Captain Aryutinov Mud Volcano, Gulf of Cadiz. The incubations at 200 and 300 bar pressures showed the depletion in activities after 30 days of incubation. Incubation of AOM hosting sediment at in-situ condition could be a preferred option for achieving high AOM activities and sulfate reduction rates.In this thesis, it has been experimentally demonstrated that biomass retention and the continuous supply of methane can favor the growth of the slow growing anaerobic methane oxidizing community in bioreactors even under ambient conditions. Therefore, locating ANME habitats in shallow environments and enriching them at ambient conditions can be advantageous for future environmental biotechnology applications

Methyl-coenzyme M reductase (MCR) is the key enzyme involved in the production of methane by methanogenic archaea and its consumption by anaerobic methanotrophs (ANME). MCR is a multimeric complex composed of six different subunits arranged in a 2α, 2β, 2γ configuration that requires two molecules of its nickel-containing tetrapyrrole prosthetic group, coenzyme F430. Additionally, the α subunits of MCR house a variety of different post-translational modifications across both methanogens and ANME. In methanogens, MCR is encoded in a conserved mcrBDCGA gene cluster, which encodes accessory proteins McrD and McrC. These are believed to be involved in the assembly and activation of MCR, respectively. However, one or both accessory proteins are often omitted from the operon in other MCR-containing archaea as is the case in ANME. MCR knowledge is mostly limited to methanogens due to difficulties associated with large-scale cultivation of ANME and other MCR-containing archaea. Due to the complexity of MCR, studies on this enzyme are also largely limited to native enzymes. Developing methods for the detailed biochemical characterization ANME MCRs would be highly desirable since these enzymes are proposed to be optimized for methane oxidation and thus have immense potential for bioenergy and greenhouse gas mitigation applications. In addition to containing the necessary machinery for the production of an assembled and active MCR, model methanogens are easier to culture and have established genetic manipulation techniques, making them ideal candidates for the development of heterologous expression systems. Thus, here we sought to generate such a system for the study of various ANME MCRs in the methanogen, Methanococcus maripaludis. We report the successful expression and purification of an ANME-2d MCR, marking a significant step toward the development of a heterologous MCR expression system. Additionally, our attempts to purify various recombinant MCRs revealed the importance of including accessory proteins, particularly McrD, within expression constructs. Therefore, we also sought to functionally characterize McrD, which we show is likely an MCR chaperone that plays a key role in MCR maturation. Taken together, our work has provided key insights into MCR assembly as well as provided a foundation for the eventual development of MCR based biocatalytic systems to be used for methane mitigation strategies and bioenergy platforms. / Doctor of Philosophy / Life is divided into three domains known as Bacteria, Eukarya, and Archaea. Methanogens are anerobic microbes belonging to the domain Archaea, which can be found across a wide variety of oxygen deprived environments. These organisms can turn different carbon-containing compounds into energy and methane gas in a process known as methanogenesis. This results in roughly 90 billion tons of biologically produced methane, making methanogenesis a key point of interest for potential greenhouse gas mitigation. The methane-generating step of methanogenesis is performed by methyl-coenzyme M reductase (MCR), a large enzyme composed of two α subunits, two β subunits, and two γ subunits. Additionally, this enzyme harbors a nickel-containing cofactor which is responsible for catalyzing the difficult methane formation reaction. In addition to the MCR-encoding genes, MCR gene clusters contain two extra genes that encode accessory proteins, named McrC and McrD, which are believed to play an important role in the activation and the assembly of the enzyme, respectively. Relatives of methanogens known as Anerobic Methanotrophs (ANME) are a different type of archaea which consume methane by reversing methanogenesis in a process known as anerobic methane oxidation. Because of their ability to consume methane, there is a large interest in studying MCR from these organisms to potentially use it for methane mitigation strategies and for bioenergy applications to convert methane to more usable liquid fuels. However, due to the high difficulty of growing ANME in a lab setting, studying any biochemical processes from ANME is a difficult task. Luckily, genetic manipulation techniques are available for many methanogens, making them ideal candidates to study MCR from ANME organisms. In this work, we sought to develop a system to express and purify MCR from different methanogens and ANME in a methanogenic host, Methanococcus maripaludis. We also sought to understand the role and importance of accessory protein McrD, especially with respect to developing a proper expression system for MCRs. We were able to successfully express a ANME MCR in M. maripaludis and found that McrD is an important aspect to consider when expressing MCRs in a methanogen, although it is not essential for this protein to exist within the MCR gene cluster. This work sets the stage for the future biotechnological use of MCR for methane mitigation and bioenergy applications.

Au niveau des marges continentales, et plus particulièrement dans des zones dites d'émissions de fluides froids, des communautés microbiennes et animales complexes se développent localement à la surface des sédiments. Ces communautés utilisent pour leur croissance des composés chimiques réduits (H2S, Méthane, CO2 ...), contenus dans un fluide à basse température, percolant à travers les sédiments et issus de phénomènes géologiques et de divers processus microbiens. Afin d'étudier la diversité des communautés microbiennes associées à ces écosystèmes ainsi que leur rôle dans l'environnement, et d'appréhender les paramètres environnementaux influençant la distribution et l'écophysiologie de ces communautés, des sédiments de surface (0-20 cm) mais également plus profonds (<9 mbsf) ont été prélevés au niveau de la Marge de Sonora. Les communautés microbiennes présentes ont été étudiées par diverses approches de biologie moléculaire, de mise en culture et de microscopie. Ce travail de recherche a permis : i) de déterminer la structure et la diversité des communautés microbiennes métaboliquement actives dans ces sédiments, ii) de mettre en évidence des écophysiologies différentes entre les acteurs du cycle du méthane (méthanogènes, ANMEs, SRB), prépondérant dans cet écosystème et iii) de découvrir la présence de nouvelles lignées et fonctions microbiennes dans les sédiments de zones d'émission de fluides froids des marges continentales. / At continental margins, and more particularly in cold seep areas, microbial and animal communities were locally detected at the surface of the sediments. These communities grow using reduced chemical compounds (H2S, Methane, COZ ...) contained in the percolated cold fluids and produced by both geological and microbial processes. ln order to study microbial community diversity in these ecosystems and their role in the environment as well as to understand the environmental factors influencing the distribution and ecophysiology of these communities, surface (0-20 cmbsf) but also deeper (<9 mbsf) sediments were collected at the Sonora Margin. Microbial communities have been studied using various molecular, cultural and microscopy approaches. This research allowed: i) to determine the structure and diversity of metabolically active microbial communities in sediments, ii) to highlight different ecophysiologies for methane cycling microorganisms (methanogens, ANME, SRB) and iii) to discover the presence of new microbial lineages and functions in the cold seeps sediments of the continental margins.