Organic and inorganic carbon can enter inland waters in different ways, and often a considerable amount of this carbon is coming from terrestrial input. Once this terrestrial carbon enters a lake, the carbon may be degraded, mineralized or eventually buried in the sediment. Below the oxic zone of the sediment carbon may be used by archaea to produce methane (CH4). The CH4 can then diffuse up in the sediment and escape to the bottom waters, or the CH4 can be oxidized by bacteria using oxygen as an oxidant. There is also an anoxic process to oxidize CH4 (anaerobic oxidation of methane: AOM), using sulfate (SO4) and by recent findings also ferric iron (Fe(III)) as electron acceptors. In this study the main questions of interest were if CH4 is produced in deep (i.e. old) lake sediments and if CH4 is oxidized anaerobically using Fe(III). Two Swedish boreal forest lakes were studied, sediment profiles of CH4 were conducted in the field (down to 60 cm). Collected sediments were sliced anoxically at different depths and then analyzed for ferrous iron (Fe(II)), Fe(III) and SO4. Sediment from different depths was also incubated anoxic in order to test if CH4 production depends on sediment age. The results show that methanogenic activity occurs by degrading old carbon in deep boreal forest lake sediments, and that a certain part of this might then be oxidized anaerobically. However, all cores exposed a general trend of increasing CH4 concentrations with sediment depth, indicating that CH4 production in old sediment layers is greater than AOM. AOM could therefore only act as a partial sink for CH4 in anoxic deep sediments.

No description available.

京都大学 / 0048 / 新制・課程博士 / 博士(理学) / 甲第20926号 / 理博第4378号 / 新制||理||1629(附属図書館) / 京都大学大学院理学研究科地球惑星科学専攻 / (主査)教授 生形 貴男, 教授 酒井 治孝, 教授 田上 高広 / 学位規則第4条第1項該当 / Doctor of Science / Kyoto University / DFAM

The depth of the sulfate-methane transition (SMT) above gas hydrate systems is a direct proxy to interpret upward methane flux and hydrate saturation. However, two competing reaction pathways can potentially form the SMT. Moreover, the pore water profiles across the SMT in shallow sediment show broad variability leading to different interpretations for how carbon, including CH4, cycles within gas-charged sediment sequences over time. The amount and distribution of marine gas hydrate impacts the chemistry of several other dissolved pore water species such as the dissolved inorganic carbon (DIC). A one-dimensional (1-D) numerical model is developed to account for downhole changes in pore water constituents, and transient and steady-state profiles are generated for three distinct hydrate settings. The model explains how an upward flux of CH4 consumes most SO42- at a shallow SMT implying that anaerobic oxidation of methane (AOM) is the dominant SO42- reduction pathway, and how a large flux of 13C-enriched DIC enters the SMT from depth impacting chemical changes across the SMT. Crucially, neither the concentration nor the d13C of DIC can be used to interpret the chemical reaction causing the SMT. The overall thesis objective is to develop generalized models building on this 1-D framework to understand the primary controls on gas hydrate occurrence. Existing 1-D models can provide first-order insights on hydrate occurrence, but do not capture the complexity and heterogeneity observed in natural gas hydrate systems. In this study, a two-dimensional (2-D) model is developed to simulate multiphase flow through porous media to account for heterogeneous lithologic structures (e.g., fractures, sand layers) and to show how focused fluid flow within these structures governs local hydrate accumulation. These simulations emphasize the importance of local, vertical, fluid flux on local hydrate accumulation and distribution. Through analysis of the fluid fluxes in 2-D systems, it is shown that a local Peclet number characterizes the local hydrate and free gas saturations, just as the Peclet number characterizes hydrate saturations in 1-D, homogeneous systems. Effects of salinity on phase equilibrium and co-existence of hydrate and gas phases can also be investigated using these models. Finally, infinite slope stability analysis assesses the model to identify for potential subsea slope failure and associated risks due to hydrate formation and free gas accumulation. These generalized models can be adapted to specific field examples to evaluate the amount and distribution of hydrate and free gas and to identify conditions favorable for economic gas production.

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