Landfill leachate contains valuable, recoverable organics, water, and nutrients. This project investigated leachate treatment and resource recovery from landfill leachates by innovative methods such as forward osmosis (FO), bioelectrochemical systems (BES), and advanced oxidation. In this study, a microbial fuel cell (MFC) removed 50-75% of the ammonia from a leachate through the electricity driven movement of ammonium to the cathode chamber followed by air stripping at high pH (> 9). During this process, the MFC system removed 53-64% of the COD, producing a net energy of 0.123 kWh m-3. Similarly, an integrated microbial desalination cell (MDC) in an FO system recovered 11-64% of the ammonia from a leachate; this was affected by current generation and hydraulic retention time in the desalination chamber. The MDC-FO system recovered 51.5% of the water from a raw leachate. This increased to 83.5% when the FO concentrate was desalinated in the MDC and then recirculated through the FO unit. In addition, the project investigated humic acid (HA) recovery from leachate during the synergistic incorporation of FO, HA recovery, and Fenton's oxidation to enhance leachate treatment and to reduce Fenton's reagent requirements. This led to the investigation of harmful disinfection byproducts (DBPs) formation during Fenton's oxidation of landfill leachate. The removal of leachate UV-quenching substances (humic, fulvic, and hydrophilic acids) using an MFC and a chemical oxidant (i.e., sodium percarbonate) with a focus on energy production and cost efficiency were also studied. BES treatment can reduce leachate organics concentrations; lower UV absorbance; recover ammonia; and, in combination with FO, recover water. Although BES is promising, significant work is needed before its use in landfill leachate becomes practical. FO application to leachate treatment must consider the choice of an appropriate draw solute, which should require minimal effort for regeneration. Resources like HA in leachate deserve more attention. Further efforts can focus on purification and application of the recovered products. The emerging issue of DBP formation in leachate treatment also requires attention due to the potential environmental and human health effects. The broader impact of this study is the societal benefit from more sustainable and cost-efficient leachate treatment. / Doctor of Philosophy / On average, each of us produces 3 – 4 pounds of solid waste every day. In the U.S., the yearly generation of solid waste is 250 million tons, while the global generation is 1.1 billion tons. The global management cost of solid waste is around 200 billion dollars. About half of U.S. municipal solid waste ends up in landfills, in China, this number is 80%. Among the different municipal solid waste (MSW) management approaches, landfilling is the most common because of its low cost and relatively low maintenance requirements. In a landfill, the combination of precipitation and solid waste degradation produce leachate, a complex wastewater. A ton of municipal solid waste can generate 0.05–0.2 tons of leachate in its lifetime during the process of landfilling. Leachate contains a vast array of pollutants, which can result in major environmental impact and adverse human health risk if not contained and treated appropriately. At present, leachate is mostly treated biologically, without any resource recovery. Among the myriad recoverable resources in landfill leachates, water and ammonia are the most abundant. We applied innovative approaches such as, bioelectrochemical systems, forward osmosis, advanced oxidation to recover resources and remove contaminants from leachate simultaneously. We also incorporated these novel technologies to help each other. For instance, we recovered humic fertilizer from leachate prior to advanced oxidation (i.e., Fenton’s oxidation) that helped the reduction of Fenton’s reagent requirements. The next step of our study could be the pilot scale application of the proposed techniques so that it can be applied in field. The broader impacts of this study include improvements in sustainability and cost efficiency of leachate treatment that can benefit the society.

La récupération d'énergie ambiante est une solution efficace et respectueuse de l'écosystème pour alimenter de manière autonome des nœuds de capteurs. La pile microbienne benthique (BMFC) est un système récupérant l'énergie de la biomasse sédimentaire à l'aide du métabolisme électro-actif des bactéries présentes naturellement dans le milieu. Bien que prometteuse comme source d'énergie long terme pour des capteurs marins, ses niveaux de puissance (autour de 100 µW) et de tension (0,6 V en circuit ouvert) nous engage à mener une réflexion sur la conception de son interface électronique de récupération. La première partie de cette thèse détaille la conception de BMFCs de taille centimétrique faites en laboratoire en maintenant des conditions proches du milieu naturel. Une seconde partie s’intéresse à caractériser et modéliser le comportement électrique des BMFCs dans le domaine statique puis dynamique, en vue de concevoir le circuit de récupération de manière appropriée. A l’aide du modèle électrique statique, une interface de récupération est définie et optimisée de manière à extraire le maximum de puissance et maximiser le rendement de conversion. Le choix se porte sur le convertisseur flyback en mode de conduction discontinue. A l’aide d’un modèle prédisant les pertes du flyback validé expérimentalement, une étude portée sur la fréquence de découpage, le rapport cyclique et le choix des inductances couplées a permis d’atteindre un rendement de 82% et 64% pour une BMFC délivrant respectivement 90 µW et 30 µW. Une dernière partie s’intéresse à optimiser l’interface de récupération en prenant en compte les différentes variabilités de la BMFC. Notamment, l’intérêt du suivi du MPP est discuté et l’influence du comportement commuté du flyback sur les pertes dynamiques supplémentaires au sein de la BMFC est analysée grâce au modèle électrique dynamique de la BMFC déduit au second chapitre. / Harvesting energy in the surrounding environment is an advantageous alternative to conventional batteries for powering autonomously remote sensors in addition to processing in an eco-friendly way. Many researches currently focus on harvesting energy from solar, thermal and vibrational sources scavenged in environments near the sensor. Less analyzed in the literature, the benthic microbial fuel cell (BMFC) is an emerging harvesting technology that exploits the waste materials in the seafloors. The catalysis properties of bacteria into a couple of redox reactions convert chemical energy from the sediment into electrical energy. Although promising as a long-term energy source for marine sensors, its power levels (around 100 μW) and voltage (0.6 V in open circuit) commit us to reflect on the design of its electronic harvesting interface. The first chapter of this thesis details the design of lab-made cm2-BMFC while maintaining conditions close to the natural environment. A second chapter focuses on characterizing and modeling the electrical behavior of BMFCs in the static and dynamic domains. Thanks to the static electric model, a harvesting electrical interface is defined and optimized to extract the maximum power and maximize the conversion efficiency. The flyback converter in discontinuous conduction mode is chosen. By using a model predicting the losses of the experimentally validated flyback, we studied the choice of the switching frequency, the duty cycle and the coupled inductances. We reached an efficiency of 82% and 64% for a BMFC delivering respectively 90 μW and 30 μW. A final chapter focuses on optimizing the harvesting interface by taking into account the different variabilities of the BMFC. In particular, the interest of the MPP monitoring is discussed and the influence of the flyback switched behavior on the additional dynamic losses within the BMFC is analyzed thanks to the dynamic electrical model of the BMFC deduced in the second chapter.

No description available.