미생물 연료전지(MFC)는 미생물의 촉매 반응을 이용하여 폐수 등 환경 오염물질을 처리함과 동시에 전기에너지를 생성하는 생물전기화학 장치다. 미생물 연료전지의 주요 성분 중 하나인 양이온 교환막(PEM)은 미생물 연료 전지의 성능에 결정적인 영향을 미치며, 현재 가장 많이 사용되고 있는 양성자교환막은 Nafion이다. Nafion은 우수한 성능을 가지고 있지만, 단가가 높고, 생물오염에 취약하며, 생분해가 불가능하다는 단점이 있다. 따라서 Nafion을 대체하기 위한 새로운 복합막 을 개발하고자 하는 시도가 꾸준히 이루어졌다. 본 총설에서는 미생물 연료전지 분야에서 최근 개발된 복합막의 특징과 성능을 고찰하며, 특히 양성자교환막을 중점적으로 다룬다.

재생 불가능한 에너지 자원이 수년에 걸쳐 고갈됨에 따라, 재생 에너지 생산을 위한 보다 효과적인 방법에 대한 연구가 증가되었다. 연로전지 개발의 한 분야인 미생물 연료전지(MFC)는 이중 성능의 잠재력 덕분에 발전하였다. MFC는 박테리아와 같은 전극 감소 생물에서 전력을 모아서 전기 에너지를 생산한다. MFC는 폐수를 연료로 사용하여 에너지를 생산하고 폐수를 정화한다. 양성자 교환막(PEM)은 양극과 음극 챔버의 분리막으로, 양성자만 효과적으로 통과할 수 있게 하는 중요한 역할을 한다. Nafion은 MFC에 상업적으로 사용되는 PEM이지만 비용, 생산 시간, 양성자 전도성 차원에서 보완할 점들이 많다. 본 리뷰 논문에는 Nafion을 대체할 수 있는 새로 개발된 PEM 몇 가지를 논의하였다. 또한, PEM, 혼합 PEM 및 복합 PEM에 기반한 MFC를 요약하고자 한다.

미생물 연료전지는 신재생에너지로서 미생물이 유기물을 분해하는 신진대사 과정을 통해서 전기에너지를 생성한다. 각종 유기물이 풍부한 폐수를 이용하여 전력을 생산할 뿐 아니라, 슬러지 발생량도 감축할 수 있는 미래 전도유망한 친환경에너지이다. 하지만 이를 상용화하기 위해서는 전지 내부에서 발생하는 모든 저항요소들을 감소시켜 더 높은 전력밀도를 생산해야 될 필요가 있다. 예를 들어 신진대사가 활발한 미생물의 종류, 미생물과 전극의 효과적인 전자전달 과정, 전극의 재료 및 형태 등의 개선을 통하여 전력밀도를 높일 수 있다. 특히, 고분자 전해질 분리막의 성능개선은 산화, 환원전극조를 완벽히 분리할 뿐만 아니라, 환원전극으로의 수소이온 전도도를 높여 내부저항을 줄일 수 있는 핵심 요소이다.

Livestock wastewater has high potential as one of energy resources because this wastewater is including high organic matter. Therefore the studies attempting to bio-gasification and bio-electricity generation using livestock wastewater is being tried. The pre-treatment system used in this study was the purpose to control the ammonia nitrogen in conjunction with the system and the microbial fuel cell. Because ammonia nitrogen is to inhibit the electricity generation efficiency of microbial fuel cell. These studies were to ascertain the effect of oxidants on the nitrogen removal in the pre-treatment system using catalyst and microbubbles to treat the ammonia nitrogen. The three kinds of oxidant such as air, oxygen (O2), and hydrogen peroxide (H2O2) were used to know the ammonia and nitrate nitrogen removal. This system was operated with four kinds of conditions. First method is O2 gas with 100 mL/min with 1ml of 30% H2O2 was supplied to the wastewater. A second method, the O2, with 400 and 1,000 mL/min was supplied through the flow meter before livestock wastewater was flow in the reactor. The last method, air was supplied 800 mL/min. The nitrate removal had no significant difference all conditions except the air supply. On the other hand, the ammonia and nitrate nitrogen removal when oxygen was supplied with 1000 mL O2/min was higher than that of the other conditions. The removal rate when air was supplied 800 mL/min was similar to the value in the supplied with 400 ml O2/min. This result showed that oxidant was important factor to improve the ammonia nitrogen removal rate.

The purpose of this study was to evaluate the applicability of the microbial fuel cell for the combined treatment of food waste water and landfill leachate. Contents of the study was to develop a carbon-containing electrode material radially to maximize microbial attachment. Also to evaluate the electric energy production efficiency by combining the electrode surface coating technology. By using a microbial fuel cell organic matter and nitrogen removal efficiency is evaluated for the food waste water and landfill leachate. BET to evaluate the surface characteristics of the developing electrode (Brunauer Emmett Teller) To evaluate the coating adhesion through measurement and to evaluate the adhesion characteristics micro-organism Weighing. Excellent electrical conductivity in the development electrode platinum, cobalt, by coating a catalyst such as palladium and to evaluate the electric energy generation efficiency. Lab. scale reactor capacity is a 5 L, and to configure the cross-section and the oxidizing electrode as cathode sequentially added.

Livestock Wastewater shall cause a high concentration of organic matter and nutrients such as rivers because of the lake and groundwater contamination, such as the accumulation of nutrients in the soil contained in the manure, livestock wastewater containing large amounts of organic matter that will flow to the river or appeal If eutrophication, and comfortable living environment to cause harm, such as odor and pest damage and can. Organic waste and organic waste, such as the world has a direct interest in acquiring the available resources and the development of clean energy from waste is a growing desire, is expected to contribute to the environment from waste materials industry growth by developing innovative technologies such as direct electrical energy production. In the case of livestock waste water and high concentration of organic material in addition to containing ammonia nitrogen, nitrate nitrogen for nitrification is created due to the electron acceptor is used as the fuel cell according to this has been reported to decrease the efficiency of electricity production. Therefore, to derive the electricity production efficiency due to organic concentration and ammonia nitrogen concentration in order to apply a microbial fuel cell (MFC) livestock wastewater treatment process in this study, and to derive the energy production potential with livestock waste water through the study. Lab. scale Reactor fabrication and operation to try to derive the reaction factor of the optimum operating conditions in accordance with the livestock wastewater applied through the evaluation of trends and removal efficiency of organic matter and nutrients in the microbial fuel cell. In addition, from the final research results, I try to present the direction of future research for the improvement of application possibilities and microbial fuel cell power generation efficiency of microbial fuel cell in the livestock wastewater treatment facilities.

Sediment microbial fuel cell (SMFC), equipped with Zn, Al, Cu, Fe or graphite felt (GF) anode and marine sediment, was performed. Graphite felt was used as a common cathode. SMFC was single chambered and did not use any redox mediator. The aim of this work was to find efficient anodic material. Oxidation reduction potential (ORP), cell voltage, current density, power density, pH and chemical oxygen demand (COD) were measured for SMFC’s performance.. The order of maximum power density was 913 mWm-2 for Zn, 646 mWm-2 for Fe, 387.8 mWm-2 for Cu, 266 mWm-2 for Al, and 127 mWm-2 for graphite felt (GF). The current density over voltage was found to be strongly correlated with metal electrodes, but the graphite felt electrode, in which relatively weaker electricity was observed because of its bio-oriented mechanism. Metal corrosion reactions and/or a complicated microbial electron transfer mechanism acting around the anodic compartment may facilitate to generate electricity. We presume that more sophisticated selection of anodic material can lead to better performance in SMFC.

This study was attempted to evaluate the change of microbial community in inoculums, lag, and stationary phase using the community level physiological profiles (CLPP) base on C-substrate utilization. It was to ascertain the characterizing microbial community over time in the enrichment step of microbial fuel cells. Microbial fuel cell is a device that converts chemical energy to electricity with aid of the catalytic reaction of microorganisms using C-substrate included wastewater. Microbial fuel cells enriched by a mixture of anaerobic digestive sludge of the sewage treatment plant and livestock wastewater were used. The current after enrichment was generated about 0.84 ± 0.06 mA. Microbial community in inoculums, lag and stationary phase used amine group, phosphorylated chemical group, and carboxylic acid group (some exclusion). However, phenolic compound did not use by microorganisms in lag and stationary phase. It means that there are not the microorganisms capable of decompose the phenol in microbial fuel cell enriched by livestock wastewater. In case of substrates of amino acid and carbohydrates group, these C-substrates were only used by microorganisms in the stationary phase. It may be that electrochemically active microorganisms (EAM) which we want to know should utilize the better these C-substrates than that of lag phase. This study showed that the electrochemically active bacteria that can be distinguished by electron changes of C-substrate utilization over time could be separated.

Sediment works as a resource for electric cells. This paper was designed in order to verify how sediment cells work with anodic material such as metal and carbon fiber. As known quite well, sediment under sea, rivers or streams provides a furbished environment for generating electrons via some electron transfer mechanism within specific microbial population or corrosive oxidation on the metal surfaces in the presence of oxygen or water molecules. We experimented with one type of sediment cell using different anodic material so as to attain prolonged, maximum electric power. Iron, Zinc, aluminum, copper, zinc/copper, and graphite felt were tested for anodes. Also, combined type of anodes-metal embedded in the graphite fiber matrix-was experimented for better performances. The results show that the combined type of anodes exhibited sustainable electricity production for ca. 600 h with max. 0.57 W/㎡ Al/Graphite. Meanwhile, graphite-only electrodes produced max. 0.11 W/㎡ along with quite stationary electric output, and for a zinc electrode, in which the electricity generated was not stable with time, therefore resulting in relatively sharp drop in that after 100 h or so, the maximum power density was 0.64 W/㎡. It was observed that the corrosive reaction rates in the metal electrodes might be varied, so that strength and stability in the electric performances(voltage and current density) could be affected by them. In addition to that, COD(chemical oxygen demand) of the sediment of the cell system was reduced by 17.5∼36.7% in 600 h, which implied that the organic matter in the sediment would be partially converted into non-COD substances, that is, would suggest a way for decontamination of the aged, anaerobic sediment as well. The pH reduction for all electrodes could be a sign of organic acid production due to complicated chemical changes in the sediment.