AN ABSTRACT OF THE DISSERTATION OF Shoutao Xu for the degree of Doctor of Philosophy in Biological and Ecological Engineering presented on June 15, 2012. Title: Bacterial Community Analysis, New Exoelectrogen Isolation and Enhanced Performance of Microbial Electrochemical Systems Using Nano-Decorated Anodes Abstract approved: Hong Liu Frank W.R. Chaplen Microbial electrochemical systems (MESs) have attracted much research attention in recent years due to their promising applications in renewable energy generation, bioremediation, and wastewater treatment. In a MES, microorganisms interact with electrodes via electrons, catalyzing oxidation and reduction reactions at the anode and the cathode. The bacterial community of a high power mixed consortium MESs (maximum power density is 6.5W/m2) was analyzed by using denature gradient gel electrophoresis (DGGE) and 16S DNA clone library methods. The bacterial DGGE profiles were relatively complex (more than 10 bands) but only three brightly dominant bands in DGGE results. These results indicated there are three dominant bacterial species in mixed consortium MFCs. The 16S DNA clone library method results revealed that the predominant bacterial species in mixed culture is Geobacter sp (66%), Arcobacter sp and Citrobacter sp. These three bacterial species reached to 88% of total bacterial species. This result is consistent with the DGGE result which showed that three bright bands represented three dominant bacterial species. Exoelectrogenic bacterial strain SX-1 was isolated from a mediator-less microbial fuel cell by conventional plating techniques with ferric citrate as electron acceptor under anaerobic conditions. Phylogenetic analysis of the 16S rDNA sequence revealed that it was related to the members of Citrobacter genus with Citrobacter sp. sdy-48 being the most closely related species. The bacterial strain SX-1 produced electricity from citrate, acetate, glucose, sucrose, glycerol, and lactose in MFCs with the highest current density of 205 mA/m2 generated from citrate. Cyclic voltammetry analysis indicated that membrane associated proteins may play an important role in facilitating electron transfer from the bacteria to the electrode. This is the first study that demonstrates that Citrobacter species can transfer electrons to extracellular electron acceptors. Citrobacter strain SX-1 is capable of generating electricity from a wide range of substrates in MFCs. This finding increases the known diversity of power generating exoelectrogens and provids a new strain to explore the mechanisms of extracellular electron transfer from bacteria to electrode. The wide range of substrate utilization by SX-1 increases the application potential of MFCs in renewable energy generation and waste treatment. Anode properties are critical for the performance of microbial electrolysis cells (MECs). Inexpensive Fe nanoparticle modified graphite disks were used as anodes to preliminarily investigate the effects of nanoparticles on the performance of Shewanella oneidensis MR-1 in MECs. Results demonstrated that average current densities produced with Fe nanoparticle decorated anodes were up to 5.9-fold higher than plain graphite anodes. Whole genome microarray analysis of the gene expression showed that genes encoding biofilm formation were significantly up-regulated as a response to nanoparticle decorated anodes. Increased expression of genes related to nanowires, flavins and c-type cytochromes indicate that enhanced mechanisms of electron transfer to the anode may also have contributed to the observed increases in current density. The majority of the remaining differentially expressed genes were associated with electron transport and anaerobic metabolism demonstrating a systemic response to increased power loads. The carbon nanotube (CNT) is another form of nano materials. Carbon nanotube (CNT) modified graphite disks were used as anodes to investigate the effects of nanostructures on the performance S. oneidensis MR-1 in microbial electrolysis cells (MECs). The current densities produced with CNT decorated anodes were up to 5.6-fold higher than plain graphite anodes. Global transcriptome analysis showed that cytochrome c genes associated with extracellular electron transfer are up-expressed by CNT decorated anodes, which is the leading factor to contribute current increase in CNT decorated anode MECs. The up regulated genes encoded to flavin also contribute to current enhancement in CNT decorated anode MECs. ©Copyright by Shoutao Xu June 15, 2012 All Rights Reserved Bacterial Community Analysis, New Exoelectrogen Isolation and Enhanced Performance of Microbial Electrochemical Systems Using Nano-Decorated Anodes by Shoutao Xu A DISSERTATION Submitted to Oregon State University in partial fulfillment of the requirements for the degree of Doctor of Philosophy Presented June 15, 2012 Commencement June 2013 Doctor of Philosophy dissertation of Shoutao Xu presented on June 15, 2012. APPROVED: Co-Major Professor, representing Biological and Ecological Engineering Co-Major Professor, representing Biological and Ecological Engineering Head of the Department of Biological and Ecological Engineering Dean of the Graduate School I understand that my dissertation will become part of the permanent collection of Oregon State University libraries. My signature below authorizes release of my dissertation to any reader upon request. Shoutao Xu, Author ACKNOWLEDGEMENTS I would like to thank all people who have helped and inspired me during my doctoral study. Foremost, I would like to express my sincere gratitude to my advisors Dr. Hong Liu and Dr. Frank Chaplen for their continuous support of my Ph.D. study and the research of Microbial Fuel Cells at Oregon State University. Hong inspired me to devote myself to the field of Bio-energy with her great patience and enthusiasm towards scientific educations. Frank was always available and willing to help me with my study especially during the period of Hong’s sabbatical leave. Thanks to his kindness and assistance, my study at OSU became smooth and rewarding. Besides my advisors, I would like to thank everyone in my dissertation committee: Dr. Martin Schuster, Dr. Clare Reimers, and Dr. Mark Dolan. Due to their encouragement and insightful comments on my research, I could always have the courage and knowledge to overcome difficulties in my research. I benefited greatly from Martin’s valuable suggestions on my writing skills and his generous help regarding microarray data analysis. Clare’s advice helped me build a solid foundation of Electrochemistry. Also, it was a great honor to have Mark as my committee member. His teaching gave me an insight into the world of environmental engineering and enhanced the depth and width of my research. I thanked Dr. Yanzhen Fan for always giving me guidance about the designs of the reactors in my experiments. It was also important for me to say thanks to my current and previous lab-mates: Keaton Lesnik, Kuhuan Chien, Cheng Li, Corale Abourached, Anthony Janicek, Hongqiang Hu, Jeremy Chignell, Yudith Nieto, and Wengguo Wu. I had a wonderful time enjoying doing research with them. Their friendship and help made me confident of my ability to do research as a scientist. In addition, I cherished and appreciated the friendly environment in our BEE department. Faculty members, especially Dr. John Bolte, Dr. John Selker, Dr. Roger Ely, Dr. Ganti Murthy, and Desiree Tullos made BEE an excellent department for our students. My deepest gratitude went to my father, Fuqin Wang, and my mother, Jinzhi Wang for their endless care, love and support throughout my life. Also I would like to say thanks to my best-loved wife, Songhua Zhu. She always supported me and never complained that I could spend so little time accompanying with her. This dissertation was also for my lovely son Gabriel Hong-Yi Xu. TABLE OF CONTENTS Page 1 General Introduction……………………………………………………….. 1 2 Bacterial Community Analysis of Mixed Consortium in Microbial Electrochemical Systems…………............................................................... 13 3 New Exoelectrogen Citrobacter sp. SX-1 Isolation and Characterization……………………………………………………………. 27 4 Enhanced Performance and Mechanism Study of Microbial Electrolysis Cells using Fe Nanoparticles Decorated Anodes…………………………... 45 5 Global Transcriptome Analysis of Response of Shewanella oneidensis MR-1 to CNT Nanostructure Decorated Anodes in Microbial Electrochemical System................................................................................ 66 6 Summary…………………………………………………………………… 80 7 Bibliography ………………………………………………………………. 82 8 Appendices ………………………………………………………………… 93 LIST OF FIGURES Page Figure 1-1 Generalized schematics: (a) Microbial fuel cell (MFCs)(b) Microbial electrolysis cell (MECs) …………...……………… …………................ 2 1-2 Mechanisms for extracellular electron transport in a MFCs anode.......... 7 2-1 Polarization curves of high power mixed culture MFCs……………….. 20 2-2 DGGE result of high power generation mixed culture MFCs....………... 21 2-3 Bacterial species and percentage of bacterial community of mixed culture MFCs ………….…………………………………………........... 22 2-4 Phylogenetic trees of bacterial species from mixed culture MFCs........... 22 2-5 Dominant bacterial species identification in DGGE……………………. 23 2-6 Current density generated by different dominant isolates………………. 24 3-1 Phylogenetic tree of strain SX-1 and closely related species based on 16S rDNA sequences…………………………………………………… 35 3-2 SEM image of planktonic cells of Citrobacter sp. SX-1..……………… 35 3-3 Electricity generation by Citrobacter sp. SX-1 in a single chamber MFCs with sodium citrate ……………………………….……………... 36 Electricity generation of Citrobacter sp. SX-1 using different substrates in single chamber air-cathode MFCs at 1 KΩ………............ 37 Power and voltage generation by Citrobacter sp. SX-1 as a function of current density …………………………………………………..…... 38 3-6 Four current generating stages for CV analysis. …………………...…... 39 3-7 Cyclic Voltammetry analysis of of Citrobacter sp. SX-1 biofilms ……. 41 4-1 SEM images of Fe NPs decorated anodes…………………………….... 50 4-2 Effects of Fe-NP decorated anodes on the current density in MECs …… 51 4-3 Differentially expressed genes grouped by functional classification in Fe NP decorated anodes………………... ……………………………… 53 5-1 SEM images of CNT decorated anodes……………………………….... 70 5-2 Effects of CNT decorated anodes on the current density in MECs……... 73 5-3 Differentially expressed genes grouped by functional classification in CNT decorated anodes ………………………………………………….. 74 3-4 3-5 LIST OF TABLES Table 1-1 Taxa of bacteria, current density generated and reactor configuration used in microbial electrochemical cell experiments..…………................. Page 4 4-1 Expression levels of genes related to biofilm formation……..……….. 55 4-2 Genes related to anaerobic growth and electron transfer with significantly change expression level…………………………………..... 56 4-3 Expression level of flavin and cytochrome genes....…………………….. 58 4-4 Other genes with significantly changed expression level........................... 59 5-1 Expression level of cytochrome c as response to CNT decorated anodes.. 76 5-2. Expression level of genes related to flavin synthesis as response to CNT decorated anode in CNT decorated anodes……......................................... 78 1 1 Bacterial Community Analysis, New Exoelectrogen Isolation and Enhanced Performance of Microbial Electrochemical Systems Using Nano-Decorated Anodes Chapter 1 General Introduction 1.1 Microbial Fuel Cells and Microbial Electrolysis Cells Microbial electrochemical systems (MESs) have drawn the attention of researchers in recent years due to their promising applications in a variety of scientific fields, such as renewable energy generation, bioremediation, and wastewater treatment. In a MES, microorganisms interact with electrodes, catalyzing oxidation and reduction reactions at the anode and the cathode. The most-described type of MESs is the microbial fuel cells (MFCs), in which useful power is generated directly using the catalytic action of active microorganisms (Kim, 2002; Cheng and Logan, 2007; Cheng et al., 2006). In a typical two-chamber MFCs (Figure 1a), organic matter is oxidized by electrochemically active microorganisms in the anode chamber to release protons and electrons. Protons diffuse into the cathode chamber through a proton exchange membrane. Meanwhile, electrons are transferred to the anode through various mechanisms (Logan et al., 2006; Lovley 2 2006; Rabaey et al., 2003) and then travel to the cathode, where normally they combine with oxygen and protons to form water. Another common used type of MES is the microbial electrolysis cell (MECs), in which hydrogen is produced instead of electricity by applying a circuit voltage to the MFCs system and maintaining anaerobic conditions in the cathode chamber (Liu et al. 2005; Logan et al. 2008; Rozendal et al. 2006; Schaller et al. 2009) (Figure 1b). A cathode potential of at least - 410 mV (vs standard hydrogen electrode at pH 7.0) is required to produce hydrogen at the cathode. Therefore, a theoretical potential of 110 mV (i.e., 410-300 mV) is needed, but voltages of >0.2 V are normally applied due to various overpotentials. a e- e- R b e- e- PS H2O Cathode H+ PEM Bacteria Anode Cathode PEM Bacteria Anode H+ H2 Fig 1-1. Generalized schematics: (a) Microbial fuel cells (MFCs), where electricity is captured through the resistance R; (b) Microbial electrolysis cells (MECs), where hydrogen gas is produced in the cathode chamber. R for resistor, PS for power supply and PEM for proton exchange membrane The fundamental feature shared by microbial electrochemical systems (MESs) (MECs and MFCs) is the microbe-catalyzed electron transfer from organic matter to electrodes (anodes) (Rebaey et al., 2004). Therefore, different types of MESs can be 3 utilized to investigate the phenomena and mechanisms of interactions between microbes and electrodes. 1.2 Bacteria and Electron Transfer Mechanisms in MESs The electrochemically active bacteria in MFCs are thought to be iron-reducing bacteria such as Shewanella and Geobacter species (Gorby et al., 2006). They have great importance in the natural environment, principally in metal oxidation and reduction. However, recent studies have shown that the diversity of bacterial communities is much greater than these model iron reducers on MFCs anodes (Reimers et al. 2001; Liu et al. 2004b; Kim et al. 2005). Over 20 electrochemically active bacterial species, those can transfer electrons exocellularly to electrodes, have been reported in the past 10 years (Logan 2009; Liu et al. 2010). These bacteria have been categorized into diverse genetic groups so far, including alphaproteobacteria (Rhodopseudomonas, Ochrobactrum and Acidiphilium) (Malki et al. 2008; Xing et al. 2008; Zuo et al. 2008) betaproteobacteria (Rhodoferax) (Chaudhuri et al. 2003), gammaproteobacteria (Shewanella, Pseudomonas, Klebsiella, Enterobacter and Aeronomas) (Kim et al. 2002; Pham et al. 2003; Rabaey et al. 2005; Bretschger et al. 2007; Zhang et al. 2008; Chung et al. 2009; Rezaei et al. 2009), deltaproteobacteria (Geobacter, Geopsychrobacter, Desulfuromonas, and Desulfobulbus) (Bond et al. 2002; Bond and Lovley 2003; Holmes et al. 2004a,b; 2006), Epsilonproteobacteria (Arcobacter) (Fedorovich et al. 2009) Firmicutes (Clostridium and Thermincola) (Park et al. 2001; Wrighton et al. 2008), Acidobacteria (Geothrix) (Bond and Lovley 2005), and actinobacteria (Propionibacterium) (Wang et al., 2008). A wider range of electrochemically active bacteria are expected to be discovered. 4 Table 1. Taxa of bacteria, current density generated and reactor configuration used in microbial electrochemical cell experiments. (Liu et al. 2010) Taxon Microorganisms α-proteobacteria β-proteobacteria γ-proteobacteria δ-proteobacteria Firmicutes Acidobacteria Actinobacteria 2 Current Density (A/m ) Rhodopseudomonas palustris DX-1 0.03 Ochrobactrum anthropi YZ-1 0.71 Acidiphilium sp. 3.2sup5 3.00 Rhodoferax ferrireducens 0.031 Shewanella putrefaciens IR-1 0.016 Shewanella oneidensis DSP10 0.013 Shewanella oneidensis MR-1 0.018 Pseudomonas aeruginosa KRA3 0.017 Escherichia coli K12 HB101 1.00 Klebsiella pneumoniae L17 1.20 Enterobacter cloacae 0.13 Aeromonas hydrophila PA3 0.30 Geobacter metallireducens 0.65 Geobacter sulfurreducens 8.00 Desulfuromonas acetoxidans Geopsychrobacter Electrodiphilus strain A2 0.005 0.066 Desulfobulbus propionicus 0.03 Lactococcus lactis 0.03 Thermincola sp. strain Jr 0.20 Clostridium butyricum EG3 0.22 Thermincola ferriacetica Z-0001 0.40 Brevibacillus spp. PTH1 0.009 Desulfitobacterium hafniense DCB2 1.10 Geothrix fermentans Propionibacterium freudenreichiiET-3 0.097 1.20 The electrochemically active bacterial species that possess the ability to transfer electrons outside of the cell are called exoelectrogens in the MESs research field. The different exoelectrogens have demonstrated a wide-ranging power generation ability in MFCs. For example, Shewanella oneidensis MR-1 has demonstrated the ability to 2 generate 0.018 A/m current density in single chamber MFCs; while the Geobacter 5 2 sulfurreducens species has generated current densities as high as 8.0 A/m , which is 400 times higher than the one generated by Shewanella oneidensis MR-1. However, mixedculture communities have generated much higher power densities than their pure-culture counterparts in MFCs, perhaps due to synergistic interactions within the anode bacterial communities and the participation of currently unknown bacteria species and mechanisms (Jung and Regan 2007). The dominant bacteria species vary in mixed cultures bacteria communities in MFCs due to the enrichment of different substrates. Traditional methods of extroelectrogen study depend on cultivation hampered novel exoelectrogens discovery because the inadequacy of defined media underestimates the actual microbial diversity in MFCs; Slow growth rate and unknown growth requirements of anaerobic microorganisms make some anaerobic extroelectrogens cultivation difficult. However, these limitations have been overcome by using molecular biological methods based on DNA/RNA analysis. Molecular biological techniques are now widely applied to assess the diversity of microbial communities by analyzing the 16S rDNA sequence. The most commonly used molecular biological techniques for bacterial community analysis include denaturing gradient gel electrophoresis (DGGE), restriction fragment length polymorphism (RFLP) and 16S rDNA sequencing. These methods are much less time consuming than traditional isolation and cultivation methods. Isolated exoelectrogens were utilized to explore the mechanism of electron transfer to the anode. However, the mechanisms of electron transfer to extracellular electron acceptors are not well understood. Three mechanisms have been proposed for exocellular transport of electrons by exoelectrogens to anodes in MFCs so far. Some exoelectrogenic bacteria can transfer electrons to electrodes through soluble redox compounds (Bond and 6 Lovley 2005). These compounds include artificial mediators and mediators secreted by exoelectrogenic bacteria. A variety of chemicals have been used to facilitate the shuttling of electrons from inside of cell to electrodes outside the cell. These exogenous mediators include, neutral red (Park et al. 1999), anthraquinone-2-6, disulfonate (AQDS), thionin, potassium ferricyanide (Bond et al. 2002), methyl viologen, and others (Logan 2004; Rabaey and Verstraete 2005). Some bacteria can secrete their own chemical mediator, for example, Pseudomonas aeruginosa secretes pyocyanin and phenazine-1-carboxamide to transfer electrons toward the MFCs anode (Rabaey et al. 2005). Another evidence for mediator production by bacteria is Geothrix fermentans. When the medium was replaced in a MFCs that had stable power generation with this bacteria, power dropped by 50% and required 10 days to resume the original level. Some bacteria can directly transfer electrons to anodes via outer cell membrane proteins (Myers and Myers 1992). The outer cell membrane protein cytochrome c is thought to play a critical role in to transferring electrons to anodes. Ly et al (2011) isolated the haem protein cytochrome c, and demonstrated that electric field effects may be functional for the natural redox processes of cytochrome c in the respiratory chain. Shewanella oneidensis is the example of a bacterium that is capable of transfer electron to anode via outer cell membrane proteins. When Shewanella oneidensis adhered to an iron surface, the greater force has showed benefits to grow cells because closer contact required for electron transfer from cell bound cytochromes (Lower et al. 2001). 7 Fig.1-2. Mechanisms for extracellular electron transport in an MFCs anode (1) direct contact (top in green); (2) by nanowires (middle in purple); and (3) self-produced mediators (bottom in blue). (Logan, 2009) More and more evidence supports the involvement of bacterial nanowires in extracellular electron transport (Reguera et al. 2005; 2006; Gorby et al. 2006). Nanowires are conductive appendages produced by both Geobacter and Shewanella species (Gorby and Beveridge 2005). The conductivity of the appendages was examined and confirmed by using conductive scanning tunneling microscopy (STM) (Gorby et al. 2006). Nanowires can carry electrons from the cell to the anode surface of MFCs. The solid component of the extracellular biofilm matrix has high efficiency on extracellular electron transfer compared with other extracellular electron transfer 8 mechanisms and recently, Torres et al. (2010) hypothesized that the solid component of the extracellular biofilm matrix formed by exoelectogens is another way bacteria transfer electrons to electrodes. This hypothesis was based on kinetic analysis of each EET mechanism reported in available literature (Torres et al. 2010). 1.3 Anode electrodes In MFCs/MECs anode electrodes are a critical component because exoelectrogens adhere to the surface of anodes to transfer electrons to the electrode. The characteristics of anodes have significant effects on electron transfer rate from bacteria to anode electrodes in MFCs. The requirements of an anode material are: it should be highly conductive, non-corrosive, have a high specific surface area (area per volume), high porosity, be non-fouling, inexpensive, and easily scaled to larger sizes. Of these properties, the most important one that is different from other biofilm reactors is that the material must be electrically conductive. Normally they are made of various carbon materials, including carbon fiber, carbon clothe, and carbon paper due to their stability, high conductivity and high specific surface-area. Nevertheless, they have little electrocatalytic activity for the anode microbial reactions and thus a modification of the carbon materials is the main approach for improving their performance. Consequently, there is a great need to develop a new type of anode material for MFCs/MECs. It is a great challenge to develop a new anode material to further increase the power density of a MFCs. The nature of the catalytic mechanism of a MFC’s anode involves not only a biological but also an electrocatalytic process. An optimal nanostructure with a high specific surface area favorable for both catalytic processes could play a critical role in improving the power density of the MFCs, such a structure needs to host the bacteria 9 with high bioactivity while enhancing the electron-transfer rate. Schröder et al (2008). employed PANI to modify a platinum anode for MFCs and achieved a current density 1 order of magnitude higher than the previously reported value. PANI/inorganic composites are also reported to have better conductivity. Qiao, et al also applied a new mesoporous TiO2 electrode material with uniform nanopore distribution and a high specific surface area to anode, in comparison to previously reported work with E. coli MFCs, the composite anode delivers 2-fold higher power density (Qiao et al., 2008). Thus, it has great potential for use as the anode in a high-power MFCs and may be a new approach for improving performance of MFCs. 1.4 Other parts of MESs 1.4.1 Membranes and ion transport The ion exchange membrane is another one of the critical components in twochamber MESs systems. It separates anode and cathode chambers and at the same time maintains the electron neutrality of the system, i.e., transport of electrons to the cathode needs to be compensated by transport of an equal amount of positive charge to the cathode chamber. A proton exchange membrane (PEM), such as Nafion, a per-fluorinated sulphonic acid membrane (PFSAs) consisting of a hydrophobic fluorocarbon backbone to which hydrophilic sulfonate groups (-SO3-) are attached, is commonly used in chemical fuel cell systems. For MFCs systems, however, mainly cation species like Na+ and K+ other than proton are often responsible for the dominant transport of positive charge through the cation exchange membrane (CEM) to maintain electroneutrality due to the low proton concentration in any aqueous medium with near neutral pH (Rozendal et al., 2006). Consequently, the pH increases in the cathode chamber due to the consumption of 10 protons and decreases in the anode chamber because of the accumulation of protons (Rozendal et al. 2007). This pH change in two-chamber systems results in a decrease of the cathode potential and performance. The application of anion exchange membrane (AEM) has also been explored in MFCs systems (Cheng and Logan, 2007, Kim and Logan, 2007), where it has been proposed that protons are transferred via pH buffers, like phosphate anions. 1.4.2 Cathodes and Catalysts The cathode is another challenge for making MFCs commercially available technology because the chemical reaction that occurs at the cathode is difficult to engineer as the electrons, protons and oxygen must all meet at a catalyst in a tri-phase reaction (solid catalyst, air, and water). The catalyst must be on a conductive surface and must be exposed to both water and air so that protons and electrons in these different phases can reach the same point. The most commonly used material for a cathode is commercially available carbon paper pre-loaded with a Pt catalyst on one side. When it is used in a MFC, the side that contains the catalyst faces the water and the uncoated side faces air. To reduce the high cathode cost associated with platinum catalyst, other preciousmetal-free cathodes such as (NiMo and NiW) were developed by electrodepositing on a carbon fiber. They have achieved comparable performance with Pt catalyst with same loading at a much lower cathode fabrication cost (Hu, 2010). The requirements of cathode for MECs are quite similar to the requirements of cathode for MFCs but easier than cathode for MFCs for the manufacturing process, because the cathode in MECs is not necessarily to exposed to air. Therefore, it can be made of the exact same materials of cathode in MFCs except a waterproof layer. 11 Recently, some researchers have attempted to apply microorganisms as a biocatalyst to precede the combination of electron with oxygen in the cathodes. 1.5 Dissertation overview Low power densities in MESs limit practical applications. The improvement of MESs performance requires a detailed understanding of the physiology and ecology of microorganisms in MESs, including the mechanism of electron transfer to the anode from the microorganism. This dissertation focuses on the problem of the low power density of MESs. The bacterial community structure of a high power generated mixed culture communities in MFCs will be identified firstly, and then one of major exoelectrogens will be isolated and characterized. This information will be helpful to understand the physiology and ecology of exoelectrogens in MESs. Consequently, they will be beneficial to improve power density of MFCs. Lastly, the nanostructure decorated anodes in MECs will be utilized to improve the power density. The power enhancement mechanism will be explored by using a whole genome microarray. They are presented here as four papers. In the first paper, the cultivation independent molecular biological techniques, denaturing gradient gel electrophoresis (DGGE) and 16S rDNA clone library, are utilized to analyze the bacterial community structure of a higher power mixed culture MFCs. The analyzed results provide fundamental information for isolating the dominant bacteria in mixed culture MFCs. Two of dominant bacterial species has been isolated and used aone to test power generation in MFCs. The possible interaction among different bacterial species in mixed culture is discussed. 12 In the second paper, one isolated exoelectrogenic bacterial strain SX-1 is characterized. It is identified as a member of the Citrobacter genus and power generation is tested ultilizing a wide range of different substrates. The electron transfer mechanism is explored using Cyclic Voltammetry (CV). This study increases the known diversity of power generating exoelectrogens and provides a new strain to explore the mechanisms of extracellular electron transfer from bacteria to electrodes. The third paper shows effects on MESs performance by Fe nanoparticle decorated anodes in the MESs. The average current density produced with Fe nanoparticle decorated anodes increased up to 5.9-fold higher than plain graphite anodes. A whole genome microarray is utilized to analyze the possible mechanism of enhanced current density as responded to nanoparticle decorated anodes. The fourth paper describes the effects of carbon nanotube (CNT) modified anode on the performance S. oneidensis MR-1 in MESs. Results demonstrate that current densities produced with CNT decorated anodes are up to 5.6-fold higher than plain graphite anodes. The possible mechanisms of enhanced current density by CNT decorated are explored. 13 Chapter 2 Bacterial community analysis of mixed consortium in higher power density MESs Shoutao Xu and Hong Liu 1 Introduction: The improvement in the performance of mixed culture MFCs requires an understanding of the ecology in microbial communities of MFCs. Many researchers have attempted to characterize microbial populations and activities to elucidate the behaviors and ecology of microorganisms in MFCs (Wrighton et al. 2008; Fedorovich et al. 2009). In order to study the microbial ecology of the mixed culture in a MFC and select the appropriate isolation medium for dominant bacterial species in the mixed culture, the fundamental steps are to analyze the bacterial diversity in the mixed culture of MFCs and identity the dominant bacterial species in bacteria communities in MFCs. 14 As for the identification of bacterial communities, typically, there are two general methods. The first method for identification of bacterial community is the traditional cultivation processes using selective nutrients to promote the growth of different types of bacteria within the samples (Amman et al. 2000). The community structure can then be assessed by identifying the isolates from the dominant colonies that were cultured. This can often be costly and laborious as each isolate has to be further studied by examining its physiology, taxonomy and reactivity to stains (Adwards et al. 1989). The second method relies on utilizing molecular techniques to analyze bacterial community DNA. Several molecular methods involving the extraction and analysis of DNA from entire bacterial communities are used to identify genetic fingerprints of bacteria. These methods, including the cloning and sequencing of 16S rDNA, automated ribosomal intergenic spacer analysis (ARISA), terminal restriction fragment length polymorphism (T-RFLP), and denaturing gradient gel electrophoresis (DGGE), generate profiles of bacterial community structures. They can rapidly assess complex communities from various environments (Amman et al. 2000). Due to the conservative characteristic of 16S rDNA in bacteria during the process of evolution, 16S rDNA sequencing can be used to identify different species of bacteria. Therefore, the molecular techniques of denaturing gradient gel electrophoresis (DGGE) with PCR and 16S rDNA clone library are used for analysis of the microbial diversity. These methods are more convenient and save time compared to traditional isolation/cultivation methods for microorganism analysis. In this work, a biofilm bacterial community from an anode of a MFCs wase studied by using denaturing gradient gel electrophoresis (DGGE) of PCR-amplified partial 16S 15 rRNA genes followed by cloning and sequencing of 16S rDNA. The results provided essential information for dominant bacterial isolation in mixed culture MFCs. 2 Materials and methods 2.1 High power generation of mixed culture MFCs Mixed cultures were originally inoculated from domestic wastewater (Corvallis Wastewater Treatment Plant, Corvallis, OR) to MFCs after operating for 2 years using a defined medium solution (Lovely, 2002) with sodium acetate as the carbon source. A new MFCs was inoculated from the operating MFCs. The polarization curves were performed to measure the power generation when maximal stable power were established (normally 3-5 batches post-inoculation); and the genomic DNA from the microbial biofilm on the anode was extracted under the sterile conditions for further bacterial community analysis. 2.2 Denaturing gradient gel electrophoresis (DGGE). DGGE with PCR is a method of analysis of bacterial community composition based on different GC percentage of 16s rDNA in different bacterial species. PCR-DGGE comprises three steps: (i) extraction of total community DNA from the sample; (ii) PCRcontrolled amplification using specific oligonucleotide primers; and (iii) separation of the amplicons using DGGE. For this purpose, a reproducible and efficient method for total DNA extraction is indispensable and needs to be evaluated and optimized depending on the nature of the sample. In the subsequent PCR step, multiple PCR primer sets with different resolution can be used. In most PCR-DGGE applications on bacteria, universal or specific primers are targeting the 16S rRNA gene. Upon electrophoresis of the PCR 16 amplicons and gel staining (using ethidium bromide, silver staining or SYBR green), DGGE gels are digitally captured and further analyzed using computer software packages. The richness of DNA fragment bands in DGGE indicates the bacterial diversity of the sample. The detailed steps are as followed. Biofilms were scratched from the anodes of high power generated MFCs fed with sodium acetate. Bacterial genomic DNA was extracted from the biofilm samples using the DNeasy blood and tissue kit (Qiagen) according to the manufacturer’s instructions. The universal primer set was used to amplify the 16S rDNA from the extracted genomic DNA, then the V3 region of bacterial 16S ribosomal DNA (rDNA) was amplified with GC-clamp primer (Muyzer et al. 1993) for DGGE. PCR amplification was performed in a thermocycler. DGGE of the PCR products was carried out in a DcodeTM Universal Mutation Detection System). The 8% (w/v) polyacrylamide gels contains from 30% to 55% denaturing gradients. Electrophoresis was conducted using a 1×TAE (Tris-Acetate-EDTA) buffer at 130V and 60°C for 5 hours. After electrophoresis, the gel was stained with ethidium bromide in 1×TAE buffer for 15 minutes and washed in 1×TAE buffer for 10 minutes. The fragments were visualized under a UV transilluminator. The richness of single band in DGGE gel picture preliminarily showed that the bacterial diversity in mixed culture since the single band in gel represents one bacterial species. 2.3 16S rDNA clone library construction method 16S rDNA-DGGE fingerprinting has proven to be particularly useful as an initial investigation into bacterial communities and is suitable for identifying the predominant bacteria that comprise 1% or more of cells within a given sample. In the 16s rDNA clone 17 library construction process, the first step is the extratction of the total genomic DNA, then the genomic DNA of the mixed culture biofilm was used as template for PCR amplification of approximately 1500 bp of 16S rDNA with universal primers. The PCR products of 16S rDNA were purified and inverted into pGEM-T Easy vector system before they were transformed into competent E. coli. The transformed cells were spread on Luria-Bertani (LB) plates containing the selective antibiotic ampicillin and X-Gal and incubated overnight at 37 OC. after the more than 80 inverted 16s DNA fragment E. coli colonies were picked up and inoculated in the 1-3 ml liquid LB medium and left to grow for 16 hours, The plasmid DNA were extracted and sequenced. The sequences were compared directly to all known sequences deposited in GenBank databases using the basic local alignment search tool (BLAST). 2.4 Bioinformatics Analysis 16S rDNA sequencing results of more than 80 colones were queried against the GenBank and Ribosomal Database Project (RDP) databases using BLAST and SEQUATCH algorithms (Cole, et al. 2007; Wang et al. 2007; Cole, et al. 2009). The neighbor-joining trees were constructed with the Molecular Evolutionary Genetics Analysis package (MEGA, Version 4) based on 1000 bootstrap analysis (Tamura et al. 2007). 2.5 Dominant bacterial species band in DGGE identification The DGGE results gave the information of dominant bacterial richness of bacterial species in mixed culture based on the theory that single band represents one bacterial species, which showed the diversity of bacterial community in the mixed culture of a MFC. 16S rDNA clone library results provided the whole picture of bacterial community, 18 including the bacterial species name and bacterial species percentage in the mixed culture. The known pure bacterial species which have been sequenced can be used as markers to identify dominant bacterial species in DGGE. The whole experimental procedure is similar to the procedure of the mixed culture DGGE steps. The first step is to extract the collect the mixed culture biofilm genomic DNA and pure bacterial species marker genomic DNA. Then, the universal primer set was used to amplify the 16S rDNA from the extracted genomic DNA. After that, the V3 region of bacterial 16S ribosomal DNA (rDNA) was amplified with GC-clamp primer (Muyzer et al. 1993) for DGGE. The subsequent steps were similar to the mixed culture DGGE experimental procedure. The dominant bacterial bands in DGGE were determined by comparisons of the single band position in the mixed culture DGGE with single pure bacterial species location in DGGE. 2.6 Dominant bacterial species isolation and power generation The bacterial community of mixed culture in MFCs were predominantly composed of Geobacter sp, Arcobacter sp , and Citrobacter sp. Two dominant bacterial species have been isolated. Citrobacter sp SX-1 was isolated from the anode biofilm by using a solid agar medium containing NH4Cl, 6mM; KCl, 2mM; CH3COONa (electron donor), 30 mM; FeC6H5O7 (electron acceptor), 20mM; minerals and vitamins (Lovley and Phillips 1988). Single colonies were picked up after culturing on the plate for 36 hours at 30 °C, and transferred two times on the agar plate for purification. Then the isolates grew in a liquid medium solution in anaerobic tubes, containing the same constituents as the solid medium. All isolation process was operated in a glove box anaerobic chamber (Coy Laboratory Products, Grass Lake, MI). 19 Arcobacter sp SX-2 was isolated from the anode biofilm of a MFC fed with sodium acetate by using the same method of isolation of pure bacterial species Citrobacter XS-1 except using Trypticase Soy Agar with 5% Sheep Blood solid (from American type culture collection (ATCC)) agar medium instead of Citrobacter sp medium. Single colonies were picked up after culturing on the plate for 36 hours at 30 °C, and transferred twice on the agar plate for purification. Then the isolates grew in a liquid medium solution microaerobically. Geobacter sp have been trying to isolate by using three different methods. They are the colony pickup after different condition enrichment; Goebacter medium isolation and dilution to extinction by multiple channel mini MFCs isolation, however, the Geobacter sp. has not been isolated yet due to some limits so far. But they provide valuable information for further isolation of Geobacter sp. Single chamber MFCs were used to evaluate power generation by different isolates. The MFCs were constructed as described previously (Liu and Logan, 2004) and modified with 3 cm2 carbon cloth anodes and 7 cm2 carbon cloth/Pt cathodes. The total liquid volume of each MFCs was about 15 ml with electrode spacing about 1.7 cm. All MFCs were operated in an autoclaved closed plastic box and sterile cotton was attached to the outer surface of the air cathodes to prevent contamination. A MFCs without bacterial culture was used as control. MFCs were inoculated with 3 ml late exponential phase cultures of SX-1 in the medium solution reported previously (Liu and Logan 2004). 3 Results and discussion 3.1 Power production by mixed culture MFCs. 20 A polarization curve was used to characterize current as a function of voltage in the MFCs. The polarization curves are performed by varying a series of external resistances. The results are shown in Figure 2.1. With MFCs acclimated to 25 Ω external resistance, the maximum power density was achieved at 6.5W/m2 based on the polarization data. At this point, the current density is 2.1mA/cm2. The power density was three times higher than previous report (2.0 W/m2) using phosphate buffer (Fan et al. 2007). Power density was also 2 times higher than (2.8 m W/m2) using a bicarbonate buffer ( Fan et al. 2007). 7 power density 6.5w/m2 at current density2.08 mA/cm 2 Power Voltage 0.60 0.50 5 0.40 4 0.30 3 Voltage (V) Power density (W/m2) 6 0.70 0.20 2 0.10 0.4 0.5 0.5 0.6 0.7 0.8 1.0 1.1 1.3 1.5 2.1 2.2 2.3 2.4 Current density (mA/cm2) Figure 2-1: Polarization curves of high power mixed culture MFCs. 3.2 Bacterial community structure assessed by PCR-DGGE Bacterial DGGE profiles for higher power generating MFCs mixed culture setups were relatively complex (more than 10 bands). However, there are three brightly stained bands and other less intense bands (Fig. 2-2). These results indicated there were probably three dominant bacterial species in mixed culture MFCs. 21 1 2 Figure 2.2 DGGE result of high power generation mixed culture MFC (1 mixed culture; 2. pure culture control). 3.3 16S rDNA clone library results A total of 83 colonies were sequenced for 16S rDNA clone library construction. They represented the bacterial community structure in mixed culture in MFCs. The results revealed that the predominant bacterial species in mixed culture are Geobacter sp (66% of the mixed culture) Arcobacter sp (12% of the mixed culture) and Citrobacter sp (11% of the mixed culture). Those three genuses comprised 88% of the total bacterial species (Fig. 2.3). This result is consistent with the DGGE result which showed that three bright bands in the DGGE gel represented three dominant bacterial species in the mixed culture. The phylogenetic analysis of the colonies (83 colony sequences) is shown in Figure 2.4. 22 Anaerovorax 2% Pseudomonas 1% others 6% Geobacter Arcobacter Clostridium 2% Citrobacter Clostridium Citrobacter 11% Anaerovorax Pseudomonas others Arcobacter 12% Geobacter 66% Figure 2.3 Bacterial species and percentage of bacterial community of mixed culture MFC '< 1% Alcaligens>' 100 '<1% Commamonas>' 100 '<1% Pseudomonas aeruginosa> ' '<1 % Klebsiella>' 85 82 100 '<11% Citrobacter>' '<1% Wolinella>' 100 100 99 '<12% Arobacter>' '<2% Anaeroborax>' '<2 % Clostridium >' 87 '<1% unclear bacteria>' '<66%Geobacter>' 0.02 Figure 2.4 Phylogenetic trees of bacterial species from mixed culture MFC 3.4 Dominant bacterial band in DGGE identification 23 The dominant bacterial species, including Goebacter sp, Citrobacter sp and Arcobacter sp in the mixed culture, are shown in Figure 2.5. The upper band is Arcobacter sp; and Citrobacter sp is located in the bottom band of DGGE. Geobacter sp is the middle one. The analysis of the bacterial community using denaturing gradient gel electrophoresis (DGGE) of PCR-amplified 16S rRNA gene fragments and 16S rDNA clone library construction method showed great phylogenetic diversity of mixed culture in MFCs, with the identification of sequences derived from bacteria of the taxa deltaproteobacteria (Geobacter sp), gammaproteobacteria (Citrobacter sp) , and epsilonproteobacteria (Arcobacter sp). The result is consistent with the conclusion that among the isolated exoelectrogens, gammaproteobacteria and deltaprotebactia appear to be dominant among others (Parot et al. 2009; Liu et al. 2010). A B C D A: Citrobacter sp. B: Geobacter sp. C: Arobacter butzmeri D: mixed culture control Figure 2.5 Dominant bacterial species identification in DGGE 3.5 The dominant bacterial species isolation and power generation 24 Two dominant bacterial species Citrobacter sp XS-1 and Arcobacter sp XS-2 have been isolated and tested for power generation. The power densities generated by the two isolates are shown in the Fig 2.6. Current densities generated by isolate Citrobacter sp and Arcobacter sp were 98 mA/m2 and 20 mA/m2, respectively, which were much less than that (2.1A/m2) generated by the mixed culture from which they were isolated. 2500 Current density (mA/m2) 2000 1500 1000 500 0 Mixed culture Citrobacter sp Arcobacter Sp Figure 2.6 Current density generated by different dominant isolates The maximum current density generated by mixed culture is much higher than the one produced by pure bacterial species Citrobacter sp XS-1 and Arcobacter sp XS-2 in the same structure MFCs. Although the Geobacter sp in our mixed culture has not been isolated, a previous study showed that maximum current density generated by Geobacter sp was 0.80 A/m2 (Bond and Lovley 2003). The current density results seem partially supporting the conclusion that mixed-culture generated higher power densities than their pure-culture counterparts in MFCs (Jung and Regan 2007). This result suggests there may be synergistic interactions within the anode bacterial communities. 25 Geobacter sp are strictly anaerobic bacteria which were enriched in most of the anode biofilms (George 2005); Citrobacter species are facultative anaerobic bacteria (George 2005) which can be found in a wide variety of habitats, including in soil, water and wastewater; Arcobacter sp are micro-aerobic bacteria, including both environmental nonpathogens and opportunistic human pathogens. They are able to grow in aerobic conditions but in the optimal growth under micro-aerobic conditions (George 2005). Arcobacter sp has been discovered in the MFCs by Fedorovich (Fedorovich et al. 2009). It is interesting that the mixed culture bacterial community composed of primarily these three bacterial species has demonstrated to generate high power at non-strictly anaerobic condition, while leading dominant bacterial species Geobacter sp (66%) is strict anaerobic bacteria and generated powder in the MFCs only under strict anaerobic condition (George 2005). Therefore, it is possible that microaerobic bacteria such as Arcobacter sp and facultative anaerobic bacteria Citrobacter sp can facilitate to create anaerobic condition for Geobacter sp when they utilized oxygen for growing in the mixed culture. Syntrophic communities study have showed that anaerobic bacteria and methanogenic archaea form compact microbial structures that operate like an organ rather than a set of microorganisms functioning independently (Stams and Plugge, 2009). Some substrates have been degradeted within these communities while they are not able to be fermented by individual species alone. interspecies electron transfer also have been presented in these communities (Stams and Plugge, 2009). Summers et al (2010) also discovered that direct exchange of electrons happened within coculture of Geobacter metallireducens and Geobacter sulfurreducens. Therefore, we believe that there are 26 more complex synergistic interactions between different bacteria species in mixed culture in the MFCs. Acknowledgements The authors acknowledge support from the U.S. National Science Foundation (CBET 0955124). We also thank Keaton Lesnik for the review of this manuscript. 27 Chapter 3 New Exoelectrogen Citrobacter sp. SX-1 Isolated from a Microbial Fuel Cell Shoutao Xu and Hong Liu Published in Journal of Applied Microbiology, 111(5):1108-1115 (2011) ABSTRACT Exoelectrogenic bacterial strain SX-1 was isolated from a mediator-less microbial fuel cell by conventional plating techniques with ferric citrate as electron acceptor under anaerobic condition. Phylogenetic analysis of the 16S rDNA sequence revealed that it 28 was related to the members of Citrobacter genus with Citrobacter sp. sdy-48 being the most closely related species. The bacterial strain SX-1 produced electricity from citrate, acetate, glucose, sucrose, glycerol, and lactose in MFCs with the highest current density of 205 mA m-2 generated from citrate. Cyclic voltammetry analysis indicated that membrane associated proteins may play an important role in facilitating the electrons transferring from bacteria to electrode. This is the first study that demonstrates that Citrobacter species can transfer electrons to extracellular electron acceptors. Citrobacter strain SX-1 is capable of generating electricity from a wide range of substrates in MFCs. This finding increases the known diversity of power generating exoelectrogens and provided a new strain to explore the mechanisms of extracellular electron transfer from bacteria to electrode. The wide range of substrate utilization by SX-1 increases the application potential of MFCs in renewable energy generation and waste treatment. Keywords: Microbial fuel cell; Exoelectrogen; Citrobacter sp. SX-1; Extracellular electron transfer 29 Introduction Microbial Fuel Cells (MFCs) technology has become an active research area recently as a promising approach for renewable energy generation, wastewater treatment, and bioremediation (Rabaey and Verstraete 2005; Lovley 2006; Fan et al. 2008; Logan 2009; Liu et al. 2010). The key feature of MFCs system is the microbe-catalyzed electron transfer from organic matter to anodes. Many studies have shown the presence of diverse bacterial communities on MFCs anodes (Reimers et al. 2001; Liu et al. 2004b; Kim et al. 2005). Over 20 exoelectrogens, i.e. microbes that can transfer electrons exocellularly to electrodes have been reported in the past 10 years (Logan 2009; Liu et al. 2010). The exoelectrogens so far belong to diverse genetic groups, including alphaproteobacteria (Rhodopseudomonas, Ochrobactrum and Acidiphilium) (Malki et al. 2008; Xing et al. 2008; Zuo et al. 2008) betaproteobacteria (Rhodoferax) (Chaudhuri et al. 2003), gammaproteobacteria (Shewanella, Pseudomonas, Klebsiella, Enterobacter and Aeronomas) (Kim et al. 2002; Pham et al. 2003; Rabaey et al. 2005; Bretschger et al. 2007; Zhang et al. 2008; Chung et al. 2009; Rezaei et al. 2009), deltaproteobacteria (Geobacter, Geopsychrobacter, Desulfuromonas, and Desulfobulbus) (Bond et al. 2002; Bond and Lovley 2003; Holmes et al. 2004a,b; 2006), Epsilonproteobacteria (Arcobacter) (Fedorovich et al. 2009) Firmicutes (Clostridium and Thermincola) (Park et al. 2001; Wrighton et al. 2008), Acidobacteria (Geothrix) (Bond and Lovley 2005), and actinobacteria (Propionibacterium) (Wang et al., 2008). A wider range of exoelectrogenic species are expected to be discovered. Three mechanisms have been proposed for exocellular transport of electrons by exoelectrogens without artificial mediators. Some exoelectrogenic bacteria can transfer 30 electrons to electrodes through soluble redox compounds excreted by microorganisms (Bond and Lovley 2005; Rabaey et al. 2005) and others can directly transfer electrons to anodes via outer cell membrane proteins (Myers and Myers 1992). Recently, more and more evidence supports the involvement of bacterial nanowires in extracellular electron transport (Reguera et al. 2005; 2006; Gorby et al. 2006). In spite of the discovery of many bacterial species that can transfer the electrons to electrode without the need of artificial mediators, the investigation of extracellular electron transfer mechanisms was mainly focused on a few species, such as those from Geobacter and Shewanella genera (Kim et al. 1999; 2002; Reguera et al. 2005; 2006; Gorby et al. 2006). The electron transfer mechanisms for many of the isolated exoelectrogens species are still not well studied. In the present study, we isolated a new exoelectrogen strain SX-1 from a MFC, a strain phylogenetically related to Citrobacter sp. Power generation from various carbon sources by this strain was evaluated using single chamber MFCs. Plausible extracellular electron transfer mechanisms were also discussed based on the characterization of anodic biofilms by cyclic voltammetry (CV). Materials and methods Bacterial strain SX-1 isolation Bacterial strain SX-1 was isolated from the anode biofilm of a MFC fed with sodium acetate operated in fed-batch mode over a period of six months. The original source of the inoculum is wastewater from a local waste water treatment plant. Bacterial cells were released from the carbon cloth anode by shaking the cloth in a sterile flask with 15 mL sterile 1% NaCl solution and glass beads (2 mm diameter). The suspension was then 31 serially diluted from 10 times to 105 times and plated on a petri dish with a solid agar medium containing NH4Cl, 6mM; KCl, 2mM; CH3COONa (electron donor), 30 mM; FeC6H5O7 (electron acceptor), 20mM; minerals and vitamins (Lovley and Phillips 1988). Single colony was randomly selected after culturing on the plate for 36 hours at 30 °C, and purified on a new agar plate following a procedure reported previously (Chung and Okabe, 2009). Then the isolate was picked up and grew in a liquid medium solution in anaerobic tubes containing the same constituents as the solid medium for further analysis. All isolation process was operated in a glove box anaerobic chamber (Coy Laboratory Products, Grass Lake, MI). 16S rDNA sequencing and phylogenetic analysis Bacterial genomic DNA was extracted from the isolated strain SX-1 using the DNeasy tissue Kits (Qiagen, Valencia, CA) according to the manufacturer’s instructions. The 16S rDNA was amplified by PCR using a pair of universal primers: 27F (5’AGAGTTTGATCMTGGCTCAG-3’) and 1492R (5’-GGTTACCTTTGTTACGACTT3’) (Park et al. 2001). The conditions used for PCR were described previously (Ferna´ndez et al. 1999). PCR products were purified, ligated and cloned according to a procedure described in a previous report (Xing et al. 2008). Plasmids were isolated from randomly selected clone colonies with a QIAprep Spin Miniprep kit (Qiagen, Valencia, CA), and three plasmid inserts were then sequenced in both directions using an ABI 3730 DNA sequencer (Applied Biosystems, Carlsbad, CA)United States). Due to the identical 16S rDNA sequence of the three colones, only one was queried against the GenBank and Ribosomal Database Project (RDP) databases using BLAST and SEQUATCH algorithms (Cole, et al. 2007; Wang et al. 2007; Cole, et al. 2009). The 16S rDNA sequence of 32 strain SX-1 and closely related type strains were aligned using CLUSTALX software (Thompson et al. 1997). The neighbor-joining trees were constructed with the Molecular Evolutionary Genetics Analysis package (MEGA, Version 4) based on 1000 bootstrap analysis (Tamura et al. 2007). SEM The morphologies of SX-1 cells growing overnight in anaerobic tubes were examined with a scanning electron microscope (FEI Quanta 600 FEG, FEI Company, Hillsboro, OR). The suspended cells were fixed in a 2.5% glutaraldehyde and 0.1M phosphate buffer solution and dehydrated with a graded ethanol series from 30% to 100%. After dehydration, the samples were dried in a critical point dryer and then sputter-coated with Au/Pd for SEM examination (Liu and Logan. 2004). Evaluation of power generation by SX-1 in MFCs Single chamber MFCs were used to evaluate power generation by SX-1 using various substrates. The MFCs were constructed as described previously (Liu and Logan 2004) and modified with 3 cm2 carbon cloth anodes and 7cm2 carbon cloth/Pt cathodes. The total liquid volume of each MFCs was about 15 ml with electrode spacing about 1.7 cm. All MFCs were operated in an autoclaved closed plastic box and sterile cotton was attached to the outer surface of the air cathodes to prevent contamination. A MFC without bacterial culture was used as control. MFCs were inoculated with 3 ml late exponential phase cultures of SX-1 in the medium solution reported previously (Liu and Logan 2004). Seven substrates, including citrate, acetate, glucose, sucrose, glycerol, and lactose were evaluated individually for power generation in a fed-batch mode in a temperature control chamber (30 ±2°C). For each substrate, at least 8 batches were run to 33 investigate the effect of biofilm formation on current output at fixed external resistance of 1kΩ and the same initial substrate concentration of 30 mM. Phosphate buffer (100mM) was used to maintain the solution pH and conductivity. The MFCs with sodium citrate as electron donors were also examined for maximum power output by varying the external resistance from 20 kΩ to 4 kΩ. A data acquisition system was used to record voltage data during the MFCs operation (Keithley 2700, Keithley Instruments Inc., Cleveland, OH). It took about 15 to 30 minutes for the MFCs to stabilize depending on the external resistance. At each resistance, we collected at least five data at the steady condition to make the polarization curves. Averaged voltages were used to calculate the power density (mW m-2) according to P=IV/A, where I was the current, V was voltage, and A was crosssectional area of the anode. CV analysis CV was used to characterize the oxidation and reduction reactions on the anodic surface of the MFCs fed with citrate and operated at 7 KΩ. This external resistance was selected because the maximum power density was obtained at this resistance based on the polarization experiment. We assumed the biofilm on the anode of MFCs were welldeveloped when stable power output was obtained after 3 batches of operation. The MFCs were then used directly for CV analysis at four current generating stages of the fourth batch: (1) initial exponential current increasing stage (middle point of stage about 4 h after media change); (2) current plateau stage (middle point of stage about 8 h after media change); and (3) current decreasing stage (middle point of stage about 16h after media change); (4) right after the complete replacement of medium solution (Figure 6). The anode was used as working electrode, the cathode as counter electrode, and an 34 Ag/AgCl electrode was selected as the reference. The CV curves were scanned from 200 to -600 mV at a rate of 5 mV s-1 using a potentiostat (G300, Gamry Instrument Inc.,Warminster, PA). Control experiment was also conducted using new anode (without biofilm) and new medium solution. Nucleotide sequence accession number The 16S r DNA sequence determined in this study has been deposited in the GenBank database under accession number HQ845373. Results Identification of the strain SX-1 An almost-complete 16S rDNA sequence (1,475 bp) of strain SX-1 was obtained and subjected to comparative analysis with the 16S rDNA of closely related reference strains. A phylogenetic analysis revealed that strain SX-1 should be assigned to the genus Citrobacter and was most closely related to Citrobacter sp. sdy-48 EJ463782 (99.0% sequence similarity) and Citrobacter sp. yy-21 FJ463779 (97.5% sequence similarity). These three strains formed a distinct sub cluster in the neighbor-joining, in which the new isolate and Citrobacter sp. sdy-48 EJ463782 formed a distinct subline (Figure 3.1). The SEM image illustrated that the strain SX-1 is a rod-shaped bacterium 0.3-0.6 µm wide and 1.2-1.7 µm long (Figure 3.2). Strain SX-1 colonies on nutrient agar appeared 23 mm in diameter, smooth moist opaque with a shiny surface after 5 days incubation under anaerobic condition. The fact that strain SX-1 grew both aerobically and anaerobically using FeC6H5O7 as electron acceptor suggests that the strain is facultatively anaerobic. Strain SX-1 showed robust growthD on citrate as a carbon source. These 35 properties were similar to those of genus Citrobacter described in Bergey’s Manual of Systematic Bacteriology (George 2005). 53 Strain SX-1 36 Citrobacter sp. sdy-48 (FJ463782) Citrobacter sp. yy-21 (FJ463779) 92 Citrobacter koseri E639 (ATCC 25408) Citrobater koseri CDC 3613-63(AF025372) 44 76 Citrobacter koseri CDC 8132-86(AF025366) 100 Salmonella enterica SL483 (CP001138) Salmonella enterica AKU12601(AY696668) Shigella sonnei Ss046(CP000038) 100 88 E. coli C2 (AF403733) E. coli E24377A(CP000800) 0.001 Figure 3.1: phylogenetic tree of strain SX-1 and closely related species based on 16S rDNA sequences. The tree was constructed using the neighbor-joining method. 1 µm Figure 3.2: SEM image of planktonic cells of Citrobacter sp. SX-1 36 Electricity production by strain SX-1 in MFCs The isolated strain SX-1 was first tested for its ability to generate current from sodium citrate at 1kΩ. Current gradually increased to a maximum 50 mA m-2 after cell inoculation and then decreased (Figure 3.3). After the MFCs was refilled with new substrate solution, the current recovered rapidly and reached a higher level than the first batch. After 4 batches operation, the maximum current output of each batch became stable. The highest current density achieved in the MFCs with Citrobacter sp. SX-1 at 1 KΩ was 98 mA m-2 (Figure 3.3). Current density (mA m-2) 120 100 80 60 40 20 0 0 50 100 150 200 Time (h) Figure 3.3: Electricity generation by Citrobacter sp. SX-1 in a single chamber MFCs with sodium citrate (30 mM) as substrate at 1 KΩ. 37 Current generation by SX-1 from other substrates, including glucose, lactose, sodium acetate, glycerol, and sucrose, were also assessed at an external resistance of 1KΩ (Figure 3.4). When repeatable cycles of current output were obtained for these substrates, glycerol generated the highest maximum current density of 58 mA m-2, followed by lactose and sucrose with 29 mA m-2 and 27 mA m-2, respectively. Glucose and acetate produced the lowest maximum current density of 9.6 and 4.3 mA m-2, respectively. These results indicated that strain SX-1 can utilize a wide range of substrates for electricity generation in MFCs, but with different power generation potentials. 70 Current density (mA m-2) 60 50 40 30 20 10 0 Glucose Lactose Glycerol Acetate Sucrose Figure 3.4: Electricity generation of Citrobacter sp. SX-1 using different substrates in single chamber air-cathode MFCs at 1 KΩ. (The error bars stand for the standard deviation of 3 replicates) 38 Polarization experiment was further conducted to determine the maximum power density generated by strain SX-1 in the single chamber MFCs with citrate as substrate. A maximum power density of 88.1 mW m-2 was obtained at current density of 205 mA m-2 at an external resistance of 7 KΩ (Figure 3.5). 0.7 100 Voltage 80 Voltage (V) 0.5 70 0.4 60 50 0.3 40 0.2 Power density (mW m-2) 90 Power 0.6 30 0.1 20 80 110 140 170 200 230 Current density (mA m-2) Figure 3.5: Power and voltage generation by Citrobacter sp. SX-1 as a function of current density using sodium citrate (30 mM) as substrate. The error bars stand for the standard deviation of the 3 voltage/power outputs obtained in three MFCs 39 Current density (mA m-2) 250 Stage 2 200 Stage 3 A 150 Stage 4 Stage 1 100 A 50 0 50 55 60 65 70 75 80 85 Time (h) Figure 3.6: Four current generating stages for CV analysis: current increasing stage (stage 1); current plateau stage (stage 2); current decreasing stage (stage 3); and: right after the replacement of medium solution (stage 4). The MFCs was operated at 7 KΩ with sodium citrate (30 mM) as substrate. Cyclic Voltammetry To determine the presence of redox active compounds produced by SX-1 and the location of these compounds, CV scan of the anodic biofilms at four current output stages and the supernatant of MFCs medium solution at the end of the batch experiment were performed. Reduction peaks at range of -310 – -350 mV and oxidation peaks at range 100 – -150 mV were observed at all current generating stages (Figure 3.6, Figure 3.7A), suggesting the presence of redox active compounds may involve in extracellular electron transfer by Citrobacter sp. SX-1. The amplitude of the peaks increased according to the growth stage of the batch and the highest peaks were present after the current plateau stage, which indicated the redox active compounds mainly were secreted in the current plateau stage. While the current density at stage 3 (deceasing stage) was lower than that at stage 2 (current plateau stage), the redox peak at stage 3 was higher than that in stage 2. 40 A plausible explanation for this pattern was that redox active compounds were continuously being secreted and accumulated after the current peak was reached, resulting in more redox compounds present after the plateau stage. But, since most of the carbon source had already been being used up, many of the redox compounds at this stage had not been as active as those at current plateau stage due to much less electrons were available to be transferred. The bigger peak amplitude in stage 4 than in stage 1 indicates that the redox active compounds were continuously being secreted and accumulated in the biofilm even after stable power was generated at 7 kΩ. The slightly change of the peak locations at different stages was possible due to the solution chemistry change during the current generation process or the slightly location change of reference electrode during the measurement (Figure 3.7B). When the medium solution in the MFCs was replaced by fresh medium at the end of the batch, the oxidization and reduction peaks were still presented in the CV (Figure 3.7B), but no peaks were observed when the supernatant and fresh mediums were tested in a MFCs with no biofilm (Figure 3.7C). These results suggest the compounds involved in the electron transfer were located not in the supernatant (solution) but in the biofilm. 41 3.0E-04 A 2.0E-04 Current (A) 1.0E-04 0.0E+00 -1.0E-04 Current plateau stage -2.0E-04 Current increasing stage -3.0E-04 Current decreasing stage -4.0E-04 -0.60 -0.50 -0.40 -0.30 -0.20 -0.10 0.00 0.10 0.20 Potential (V) vs Ag/AgCl 3.0E-04 2.0E-04 B Current (A) 1.0E-04 0.0E+00 -1.0E-04 -2.0E-04 Current decreasing stage -3.0E-04 Biofilm with fresh medium -4.0E-04 -0.60 -0.50 -0.40 -0.30 -0.20 -0.10 0.00 0.10 0.20 Potential (V) vs Ag/AgCl 0.0E+00 -5.0E-05 C Current(A) -1.0E-04 -1.5E-04 -2.0E-04 -2.5E-04 -3.0E-04 Supernatant -3.5E-04 Fresh medium -4.0E-04 -0.60 -0.50 -0.40 -0.30 -0.20 -0.10 0.00 0.10 0.20 Potential (V) vs Ag/AgCl Figure 3.7: Cyclic Voltammetry analysis of Citrobacter sp. SX-1 biofilms at: (A) current increasing stage, current plateau stage and decreasing stage (end of the batch); (B) end of the batch and replaced with fresh medium and (C) controls. 42 Discussion Citrobacter species, belonging to Gammaproteobacteria, Enterobacteriales, Enterobacteriaceae are facultative anaerobic bacteria (George 2005). They can grow with oxygen as an electron acceptor but also with a variety of electron accepters such as Fe (III) in the absence of oxygen (George 2005). Citrobacter species can be found in a wide variety of habitats, including in soil, water and wastewater. Several Citrobacter species have been studied as important bioremediation bacterium for heavy metal removals, sulfate reduction, phenol degradation and chlorophenol degradation (Macaskie et al. 1995; Narde et al. 2004; Qiu et al. 2009). Citrobacter species have also been found on the anodic biofilm of a diesel-degrading MFCs (Morris et al. 2009). However, there was no study reported that Citrobacter species can transfer electrons to extracellular electron acceptors. This finding that Citrobacter strain SX-1 can generate electricity in MFCs increased the diversity of power generating exoelectrogens and provided a new strain to explore the mechanisms of extracellular electron transfer from bacteria to electrode. Among the isolated exoelectrogens, gammaproteobacteria and deltaprotebactia appear to be dominant among others (Parot et al. 2009; Liu et al. 2010). The isolated strain Citrobacter sp SX-1 phylogenetically belongs to gammaproteobacteria, which provides another evidence to support this observation. Most exoelectrogens utilize a limited range of substrates for power generation. For example, Shewanella oniedensis MR-1 can oxidize lactate under anaerobic condition but cannot utilize acetate for electricity generation (Kim et al. 2002); Geobacter sulfurreducens can completely oxidize acetate for power generation, but it cannot utilize simple sugars (Bond and Lovley 2003; Caccavo et al. 1994)). In comparison, strain SX-1 43 not only can oxidize citrate for power generation, but also utilize a wide range of substrates for power generation, including glycerol, glucose, lactose, sucrose and acetate. Interestingly, the higher current density generated by strain SX-1 from glycerol, a main by-product of biodiesel production process, suggests that strain SX-1 may be potentially used for harvesting energy from biodiesel wastes using MFCs. However, the current density generated by strain SX-1 (205 mA m-2) is lower than that (805 mA m-2 at 1 kΩ) generated by the mixed culture from which the SX-1 was isolated, indicating the existence of other higher power generating bacteria and/or complex ecology in the mixed culture community. Understanding mechanisms of microbial extracellular electron transfer is critical for enhancing the electron transfer rate from bacteria to electrode through metabolic or genetic engineering of exoelectrogens. Since the spent supernatant solution of MFCs run with SX-1 showed no redox properties, the redox compounds produced by SX-1 may have been retained in the biofilm. Alternatively, SX-1 may utilize one or both of the other two known extracellular electron transfer mechanisms. For example, it is possible that strain SX-1 transfers electrons to the anode via cell-bound outer membrane proteins. The two distinct oxidation and reduction peaks observed at -100mv- -150 mV and -310-350 mV of the SX-1 biofilm have a midpoint potential range from -205mV to -250mV, which is close to the redox potential of some c-type cytochromes (Field et al. 2000; Meitl et al. 2009), which are well-known to play an important role in extracellular electron trasnfer (Eggleston et al. 2008; Field et al. 2000; Meitl et al. 2009). Field et al. (2000) reported that the c-type cytochromes CymA had the midpoint potentials of -229 mV. Meitl et al. (2009) and Eggleston et al. (2008) reported that the c- type cytochromes 44 OmcA in Shewanella oneidensis MR-1 had the midpoint potentials of -201 mV and -208 mV. While it’s possible that SX-1 may also have conductive appendages to enhance the extracellular transfer electron, similar to the nanowires discovered in some Geobacter and Shewanella species (Reguera et al. 2005; 2006; Gorby et al. 2006), further investigation on the presence of these appendages on the cell surface of SX-1 is needed. Acknowledgements The authors acknowledge support from the U.S. National Science Foundation (CBET 0955124). We also thank Teresa Sawyer for her helps with the SEM analysis and Jeremy Chignell and Yanzhen Fan for their review of this manuscript. 45 Chapter 4 Enhanced Performance and Mechanism Study of Microbial Electrolysis Cells Using Fe Nanoparticles Decorated Anodes Shoutao Xu, Hong Liu,Yanzhen Fan, Rebecca Schaller, Jun Jiao, Frank Chaplen Published in Applied Microbiology and biotechnology 93(2):871-880 (2012) 46 ABSTRACT Anode properties are critical for performance of microbial electrolysis cells (MECs). In the present study, Fe nanoparticle modified graphite disks were used as anodes to investigate the effects of nanoparticles on the performance of Shewanella oneidensis MR1 in MECs. Results demonstrated that average current densities produced with Fe nanoparticle decorated anodes were up to 5.6-fold higher than plain graphite anodes. Whole genome microarray analysis of the gene expression showed that genes encoding biofilm formation were significantly up-regulated as response to nanoparticle decorated anodes. Increased expression of genes related to nanowires, flavins and c-type cytochromes indicate that enhanced mechanisms of electron transfer to the anode may also have contributed to the observed increases in current density. The majority of the remaining differentially expressed genes were associated with electron transport and anaerobic metabolism demonstrating a systemic response to increased power loads. Keywords: Microbial electrochemical system, microbial fuel cell, microbial electrolysis cell, nanotechnology, differential gene expression, DNA microarray 47 Introduction Microbial electrochemical systems (MESs) have been intensively studied since Lewis achieved practical advances in this field (Logan 2007), however they attracted much research attention in recent years due to their promising applications in renewable energy generation, bioremediation, and wastewater treatment. In a MES, microorganisms interact with electrodes via electrons, catalyzing oxidation and reduction reactions at the anode and the cathode. The most-described type of MESs is microbial fuel cells (MFCs), in which useful power is generated from electron donors, typically biodegradable organic materials (Logan et al. 2006). Various novel MESs have recently been developed to produce hydrogen (microbial electrolysis cells (MECs)) (Liu et al. 2005; Logan et al. 2008; Rozendal et al. 2006; Schaller et al. 2009), to power an autonomous sensor or sensor network (Ringeisen et al., 2006), to reduce bioremediation targets (Lovley 2006; Shea et al. 2008); Sukkasem et al. 2008), and to desalinate water (Cao et al. 2009). The key feature shared by these systems is the microbe-catalyzed electron transfer from organic matter to electrodes (anodes) (Rabaey et al 2004). Enhancing the anodic current output, which highly depends on the performance of the electrodes, is critical for the successful application of all these processes (Logan et al. 2007; Park and Zeilus 2002; 2003). Nanomaterials have received much attention from researchers in the context of microbiology due to their unique physical, electrical, and chemical properties, which facilitate the study of interactions between bacteria and surfaces (Liu 2006). Previous studies have demonstrated that electrodes decorated with different nanostructures such as carbon nanotubes , nanostructured polyaniline/titanium dioxide composite and titania 48 nanotubes have the potential to enhance power generation in MFCs (Morozan et al. 2007; Qiao et al. 2008; Quan et al. 2005). Furthermore, our recent study shows nanoparticle (NP) decorated anodes greatly increased the electrochemical electron transfer rate in MFCs (Fan et al. 2011). However, Fe NPs, as an ideal candidate for decorating electrodes because of respectively low price and high conductivity compared to other materials has not been focused to study in MECs. S. oneidensis MR-1, an important electrochemically active bacterial strain, has been exploited for the electricity generation in MFCs (Logan et al. 2007; Logan 2009; Park and Zeikus 2002). The availability of genome sequence for this strain makes it possible to use transcriptome assays to globally measure the responses to different growth conditions and environmental stresses (Murray et al. 2001). S. oneidensis MR-1 gene expression response to heat shock, cold shock, Cr (VI) and U (VI) reduction, chromate stress, and iron and acid tolerance have been studied in the past several years (Bencheikh-Latmani et al. 2005; Brown et al. 2006; Gao et al.2006; Gao et al. 2004; Yang et al. 2008). However, no studies have been focused on the Shewanella gene expression response to NPs in MESs. The mechanism of increased electron transfer rate exhibited by nanoparticle decorated electrodes is not well understood yet. In the present study, graphite disks decorated with Fe NPs were used as anodes to explore the effects of nanostructures on current generation in a multi-anode MECs. DNA microarrays were utilized to investigate differences in the global gene expression profile of S. oneidensis MR-1 grown on plain versus Fe NPs decorated anodes. Materials and methods 49 Bacterial cultures S. oneidensis MR-1 was purchased from American Type Culture collection (ATCC 700550) and stored as freezer stocks at -80°C. Stock cells of S. oneidensis MR-1 was grown aerobically using a medium containing 30 g/L Trypticase Soy Broth (BD 211825, Becton, Dickinson Company Franklin lakes, NJ.) at 30°C. Cells in early stationary growth phase (optical density of 1.5-1.6 at 600nm; (Spectrophotometer UV-1700, Shimadzu, Columbia, MD) were washed two times then injected into the chamber of the MECs for current production. Trypticase Soy Broth medium with 30 mM sodium lactate as electron donor was used in MECs. Phosphate buffer (100mM) was used to maintain the solution pH 7 and solution conductivity at 15 mS/cm. Characterization of nanostructured anodes Superfine isomolded graphite disks (1.6 cm x 0.5 cm, GraphiteStore.com, Inc.) were polished with ultrafine sand paper (2000 grit, 3M Company) as the base for the NP decorated and control anodes. Fe NPs decorated anodes were fabricated by thermal annealing of metal thin film coated graphite disks. Thin films of Fe were firstly deposited on the polished graphite disk by using sputter coating for 9.5 min, and the samples then were annealed in the Chemical vapor deposition (CVD) at 750°C for 20 min to form Fe NPs. Fe-NPs were produced with a diameter of 200±100 nm and a density range (distance between NPs) of 200±100 nm with a coating time of 9.5 min. SEM images of Fe NPs decorated anode and control surfaces were shown in the Figure 4.1. 50 B A 500 nm 500 nm Figure 4.1, SEM images of Fe NPs decorated anodes. (A) Graphite disk control; (B) Fe Nanoparticle decorated. Multiple channel MECs construction and operation A MECs with removable multiple anodes with each effective anode area 0.7 cm2 was constructed and used to evaluate the effects of nanostructure on current density of according to a previous report (Fan et al. 2011). The cathode was made of wet-proof (30%) carbon cloth (type B, E-TEK Division, Inc., USA) coated with Pt/C (20%, E-TEK Division, Inc., USA) following a previously reported procedure (Liu et al. 2005). The final platinum loading was 0.5 mg/cm2 per projected cathode area. The size of cathode (150 cm2) was 25 times larger than the total effective area of the 8 graphite disk anodes (5.6 cm2) to prevent cathode limitations on the performance of the MECs system. All MECs with Fe-NP decorated anodes and control anodes were tested for current generation for 24 h with medium (without bacteria) before injecting the bacterial cells in order to determine whether the Fe-NP decorated anodes demonstrate chemical current generation compared to control anodes. All the testing anodes were set up in the MECs 51 at once so that the S. oneidensis MR-1 culture was applied to all of them simultaneously. Short electrode spacing (1.7 cm) was used in the MECs design to reduce the internal resistance. A voltage of 0.6 V was applied the MECs for current generation after the cells of S. oneidensis MR-1 were inoculated into MECs at early stationary phase. A multimeter with a data acquisition system (2700, Keithly, USA) was used to monitor the current change by measuring the voltage (every 300 seconds) drop through a resistor at 300 ohm. Fig 4. 2 Effects of Fe-NP decorated anodes on the current density in MECs. Control is plain graphite disk anode; Fe-NP is the anode with Fe-NP decoration. Microarray analysis Biofilms for whole gene microarray analysis were aseptically removed from the plain and Fe-NP decorated anodes of MECs after 110 hours further incubation at 30oC when current density obviously started to decease. Total RNA was extracted using Trizol (Ambion inc., Austin,TX) following the manufacturer’s instructions. Integrity of the 52 RNA samples was confirmed using the Agilent 2100 Bioanalyzer (Agilent Technology Inc., Palo Alto, CA). The same amount of RNA (200 ng) from each sample was used for further analysis after amplification by using the MessageAmpTM II-Bacteria Prokaryotic RNA Amplification kit (Ambion, Austin,TX) according to the manufacturer’s instructions. All of the 4295 genes (resource from NCBI) represented on the S. oneidensis MR-1 whole-gene microarrays were ordered from Roche NimbleGen Inc. (Madison, WI). Biological triplicates of biofilms on the Fe-NP decorated anodes and control were analyzed, respectively. cDNA synthesis, labeling and hybridization were carried out by the CGRB Core Laboratories at Oregon State University. DNASTAR ArrayStar TM 3 software was used to identify genes that were up- or down-regulated more than 2-fold when grown on the nanoparticle modified anodes using the unpaired two sample t-test with a cutoff p-value of 0.05. The complete microarray data set generated in this study is deposited for public access in the Gene Expression Omnibus (http://www.ncbi.nlm.nih.gov/geo/) under accession number GSE31535. Results Enhancement of current generation by using NP decorated anodes in MECs The current density generated by Fe-NP decorated anode MECs with S. onidensis MR-1 increased to approximately 43 µA/cm2 20 h following inoculation and then slowly decreased. Figure 4.2 shows that the maximum current density achieved by NP decorated anodes was 8.3 times higher than that (5.1 µA/cm2) generated by the control (plain graphite disk). The average current density improvement of 110 hours was 5.9 times of that generated by the control. The current densities generated in MECs in the 53 absence of bacteria were negligible (0.3 µA/cm2), which demonstrated that the current enhancement observed with the Fe-NP decorated anodes was biologically-derived. Global transcriptome analysis Whole-genome DNA microarrays were used to attain a comprehensive, general overview of the transcriptional response to Fe-NP decorated anodes by S. oneidensis MR-1 in MEC. Of a total 4,295 genes assayed, 392 (188 induced and 204 repressed) exhibited significant (P < 0.05) differential expression at a 2-fold (log (expression ratio 1) level in 3 replicates in response to Fe-NPs. These total gene numbers present 9% of the 4,295 open reading frames (ORFs) presented on the array. 125 Up-Regulated 100 Number of Genes 75 50 25 0 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 -25 -50 -75 Down-Regulated Fig 4.3 Differentially expressed genes grouped by functional classification according to the TIGR S. oneidensis genome database (www.tigr.org). Columns: 1, amino acid biosynthesis; 2, biosynthesis of cofactors, prosthetic groups, and carriers; 3, cell envelope; 4, cellular processes; 5, central intermediary metabolism; 6, DNA metabolism; 7, energy metabolism; 8, fatty acid and phospholipid metabolism; 9, other categories; 10, protein fate; 11, protein synthesis; 12, purines, pyrimidines, nucleosides, and nucleotides; 13, regulatory functions; 14, signal transduction; 15, transcription; 16, transport and binding proteins; 17, unknown function; 18, hypothetical proteins. 54 Figure 4.3 summarizes the overall genomic response of S. oneidensis MR-1 to Fe-NP decorated anodes by grouping the differentially expressed genes into their functional role categories, based on The Institute for Genomic Research’s annotation (Version 8) of the MR-1 genome sequence. The wide distribution of putative functional roles attributed to the differentially expressed genes indicated the extent of the molecular response of S.oniedenis MR-1 to the NP decorated anodes. Among genes with defined function, a large number of up-regulated genes were associated with cellular processes (group 4), energy metabolism (group 7), other categories (group 9) and hypothetical proteins (group 18). While those genes encoding proteins involved in amino acid biosynthesis (group 1), cellular processes (group 4), substrate transport (group 16), and hypothetical proteins (group 18) were among the most down-regulated genes. Two groups of genes that were the most noticeable among the functional gene groups: genes related to energy metabolism (group 7) and genes related to amino acid biosynthesis (group 1). The ratios of up-regulated genes to down-regulated genes in these functional groupings were much higher than other functional gene groupings: there were 21 up-regulated genes, and 7 down-regulated genes in energy metabolism gene group, and 2 up-regulated and 22 down regulated genes in the amino acid biosynthesis group. Genes related to biofilm formation In order to determine whether there was a correlation between the observed biofilm enhancements by NP decorated anodes and the genes related to biofilm formation, the significant modified genes related to biofilm formation were examined and summarized in the Table 4.1. These included SO_3223 and SO_3228 genes encoding the flagellum proteins (Thormann et al. 2004), which has critical impacts on initial attachment to the 55 surface as swimming motility functions, were up-regulated over 1.0 and 0.9 fold, respectively. The gene clusters SO_4178-SO_4180, which are thought to be essential for formation of a three-dimensional biofilm, were up-regulated from 1.2 to 1.3 fold (Thormann et al. 2004). In addition, the genes SO_4105 encoding IV pilus, which is known to represent a critical factor for biofilm formation on a biotic surfaces (Thormann et al. 2004), were also induced 0.8 fold (Table 4.1). The genes related to flagellum motility (SO_4286, SO_1529, and SO_1530) were also induced slightly (Thormann et al. 2004). Table 4.1 Locus Tag Expression levels of genes related to biofilm formation Gene product descriptions Fold change SO_3228 flagellar basal-body MS-ring and collar protein, FliF 1.0 SO_3223 flagellar hook-length control protein FliK 0.9 SO_4103 MshA minor pilin protein, MshD 0.5 SO_4105 MSHA major pilin protein MshA 0.8 SO_4178 expressed protein of unknown function, MxdC 1.2 SO_4179 inner membrane family 2 glycosyltransferase, MxdB 1.3 SO_4180 diguanylate cyclase-like protein, MxdA 1.0 a: fold changes were presented after log2 b: positive number represented up-regulated and negative represented down-regulated Genes related to energy metabolism A closer consideration of energy metabolism genes was undertaken as anaerobic metabolism for electron generation and electron transport functions may play critical roles in enhanced current density generation in MECs. Genes associated with energy 56 metabolism and with significantly modified gene expression levels are summarized in the Table 4.2. Several of the up-regulated genes were related to formate dehydrogenase proteins. Most notably, four genes related to formate dehydrogenase were up-regulated more than 2-fold: SO_0102, SO_0103, SO_0104 and SO_0107. The other genes expression related to formate dehydrogenase proteins SO_4513, SO_4514, SO_4515 also significantly increased. Another interesting gene is that encoding the cytochrome c oxidase protein, gene SO_4609, which was up-regulated 1.1 fold, while the gene SO_0479 related periplasmic octaheme cytochrome c, MccA was down-regulated. However, SO_1519, the gene encoding lactate dehydrogenase was down-regulated 1.2 fold, despite lactate being the primary carbon source in the media. Table 4. 2 Genes related to anaerobic growth and electron transfer with significantly change expression level Locus Tag Gene product descriptions Fold change SO_0101 nitrate-inducible formate dehydrogenase, molybdopterin-binding 1.8 subunit, FdnG SO_0102 formate dehydrogenase, nitrate-inducible, iron-sulfur subunit 2.1 SO_0103 formate dehydrogenase, nitrate-inducible, cytochrome b556 subunit 2.4 SO_0104 formate dehydrogenase accessory protein, FdhE 2.2 SO_0107 formate dehydrogenase accessory protein fdhD 2.4 SO_0397 quinol:fumarate reductase, menaquinol-oxidizing subunit, FrdC_2 1.2 SO_0452 thioredoxin 2 1.5 SO_0903 Na-translocating NADH-quinone reductase subunit B, NqrB_1 1.2 SO_1012 NADH-ubiquinone oxidoreductase subunit K, NuoK 1.2 SO_1013 NADH-ubiquinone oxidoreductase subunit J, NuoJ 1.2 SO_1363 hydroxylamine reductase 1.3 57 SO_2417 ferredoxin, cofactor maintenance protein, YfaE 1.0 SO_3922 formate dehydrogenase, cytochrome b, Fdh -1.2 SO_4513 formate dehydrogenase, molybdopterin-binding subunit, _2 1.5 SO_4514 formate dehydrogenase, FeS subunit, FdhB_2 1.2 SO_4515 formate dehydrogenase, cytochrome b subunit, FdhC_2 1.4 SO_4609 aa3 type cytochrome c oxidase, subunit III, CoxC 1.1 SO_0479 periplasmic octaheme cytochrome c, MccA -1.2 SO_0847 periplasmic nitrate reductase, ferredoxin component, NapG -1.5 SO_1519 L-lactate dehydrogenase, iron-sulfur cluster-binding protein, LldF -1.0 SO_1251 ferredoxin, 4Fe-4S -1.1 SO_3741.1 hypothetical inner membrane protein -1.1 a: fold changes were presented after log2 b: positive number represented up-regulated and negative represented down-regulated Flavin and cytochrome related genes Flavins can be secreted by Shewanella species as electron shuttle to facilitate extracellular electron transfer (Cansterin et al. 2008). C-type cytochromes play the important roles on the process of extracellular electron transfer (Shi et al. 2007). The genes related to flavins synthesis and the genes encoding the cytochromes electron transport proteins were shown in the table 4.3, the genes SO_1414, and SO_3058 related to flavins synthesis was up-regulated to 0.3 and 0.1 folds respectively. The genes related to s C-type cytochromes SO_0135, SO_4105, SO_0169, SO_1778, are increased to 1.0, 0.8, 0.5, 0.4, 0.1 folds respectively. However, most of genes have shown no significant changes (less one-fold change) as response to nano particle decorated anode in MECs. 58 Table 4.3 Expression level of flavin and cytochrome genes Locus Tag Gene product descriptions Fold change SO_1414 flavocytochrome c flavin subunit, putative 0.3 SO_3468 riboflavin synthase subunit alpha -0.2 SO_3058 flavocytochrome c, flavin subunit 0.1 SO_4105 MSHA pilin protein MshA 0.8 SO_0169 general secretion pathway protein, GspG 0.5 SO_1778 outer membrane decaheme cytochrome c lipoprotein, MtrC 0.4 SO_1779 outer membrane decaheme cytochrome c, OmcA 0.1 SO_0135 lipoprotein of unknown function DUF333 1.0 SO_0136 conserved hypothetical inner membrane protein 0.1 a: fold changes were presented after log2 b: positive number represented up-regulated and negative represented down-regulated Other genes with significantly modified expression levels These genes over 1.5 fold change and possibly related to current enhancements were shown in Table 4.4. SO_3104 (expressed inner membrane protein) was over expressed and the gene SO_2194, which encodes outer membrane protein (OmpA family protein) was repressed as response to nanoparticle decorated anode, however it is unclear the relationships of this modified membrane protein genes with the current enhancement. Another interesting phenomenon was possible co-regulation of several gene clusters indicating possible operon associations. This includes three sets of genes that were induced more than 1.5 fold: SO_0108/SO_0109 and SO_1042/SO_1043/SO_1044. The 59 consistency of expression of these genes under the NP conditions provides basic evidence to support operon structure. However, the correlation of these significant changed gene with current density enhance are unclear, which showed there are unknown multiple and complex responses of S. oneidensis MR-1 to nanoparticle anode of MECs. Table 4.4 Other genes with significantly changed expression levels Locus Tag SO_0101 Gene product descriptions nitrate-inducible formate dehydrogenase, molybdopterin-binding Fold change 1.8 subunit, FdnG SO_0108 integral membrane protein of unknown function DUF39, YedE 1.7 SO_0109 SirA family protein, YedF 1.7 SO_0275 N-acetyl-gamma-glutamyl-phosphate reductase -3.1 SO_0277 ornithine carbamoyltransferase -2.1 SO_0279 argininosuccinate lyase -2.4 SO_0404 zinc dependent metalloprotease domain lipoprotein 2.1 SO_0956 alkyl hydroperoxide reductase, F subunit -2.0 SO_1042 amino acid ABC transporter, ATP-binding protein -1.8 SO_1043 amino acid ABC transporter, permease protein -2.7 SO_1044 amino acid ABC transporter, periplasmic amino acid-binding protein -2.7 SO_1072 chitin-binding protein, putative 2.1 SO_1405 transglutaminase family protein 2.0 SO_1822 TonB-dependent receptor, putative -2.2 1-(5-phosphoribosyl)-5-[(5-phosphoribosylamino) SO_2069 -1.9 methylideneamino] imidazole-4-carboxamide isomerase SO_2070 amidotransferase HisH -2.6 SO_2071 imidazole glycerol-phosphate dehydratase/histidinol phosphatase -2.7 60 SO_2072 histidinol-phosphate aminotransferase -2.8 SO_2073 histidinol dehydrogenase -3.0 SO_2194 OmpA family protein -3.6 SO_2195 inter-alpha-trypsin inhibitor domain protein -2.7 SO_2767 asparagine synthetase B -2.6 SO_2945 prophage LambdaSo tail fiber protein 2.0 SO_2963 prophage LambdaSo, major capsid protein, HK97 family 2.0 SO_2987 prophage LambdaSo hypothetical protein 1.9 SO_2988 prophage LambdaSo expressed protein of unknown function 1.8 SO_3104 expressed inner membrane protein 1.31 SO_3408 conserved hypothetical inner membrane protein -1.8 SO_3585 azoreductase, putative -1.8 SO_3586 glyoxalase family protein -1.7 SO_3687 curli production assembly/transport component CsgE, putative -1.8 SO_3819.1 hypothetical ammonia permease -1.9 SO_4014 AcrB/AcrD/AcrF family protein 1.8 SO_4015.1 type I secretion system, membrane fusion protein, RND family 1.8 SO_4054 5,10-methylenetetrahydrofolate reductase 1.8 SO_4245 N-acetylglutamate synthase -2.2 SO_4525.1 hypothetical transcriptional regulator, LysR family -1.7 SO_4527 integral membrane domain protein -1.9 SO_4705 transcriptional regulator, putative -1.9 a: fold changes were presented after log2 b: positive number represented up-regulated and negative represented down-regulated Discussion 61 The addition of NP to anodes significantly impacts current densities with the elemental composition being a critical factor. The chemical composition of NPs significantly affects the current enhancement in MECs (Fan et al. 2011), because the chemical composition of NP properties is a critical factor in determining the conductivity, which significantly affects the efficiency of electron transfer from bacteria to electrode. Fe is an ideal candidate for NP formation for current enhancement in MESs because of high conductivity and low price compared to gold and other conductive materials. Gold NPs has also been studies for enhancement of electricity conductivity (Bao et al. 2008). However, the disadvantages of the high price of gold limit their practical application in MECs (Fan et al. 2011). The different size and density of the same composition of NP also has essential effects on the current density enhancement (Fan et al. 2011). In this study, the results showed the current density enhancement with Fe-NP size range of 200±100 nm and density range of 200±100 nm is considerable enhancement consequence. There are a number of reports of studies of current density enhancement in MFCs by nanostructured anodes (Fan et al. 2011; Qiao et al. 2008; Sharma et al. 2008; Tsai et al. 2009). Based on bacterial behavior on nanostructured anode surface, Qiao et al. (2008) believes that Escherichia coli cells on the nanostructured electrode surface produce hairlike structures, similar to pili that could facilitate the electron transfer between the cells and electrode. The production of hair-like structures is believed to be stimulated by nanostructures and could play the key role on current density enhancement in piliproducing bacteria in MFCs (Qiao et al. 2008). S. oneidensis can produce electrically conductive bacterial nanowires, which have similar structure to the hair-like structures in E.coli (Gorby et al. 2006; Reguera et al. 2005). A number of possible genes related 62 nanowires of S. oneidensis have been identified, including mshA (SO_4105), and gspG (SO_0169) (Konstantinidis et al. 2009), They are up-regulated 0.8 and 0.5 fold in the current study respectively, even though they are not significant induced. This result supported the increased nanowire genes had contributions to enhance current density in MFCs by NPs decorated anodes. Based on the previous research on electron transfer mechanisms for S. oneidensis, it is known that self-produced mediators (flavins) and multihaem c-type cytochromes (c-Cyts) may play critical roles in the electron transfer of S. oneidensis to extracellular insoluble electrode (Canstein et al. 2008; Myers and Myers 1992; Scott and Nealson 1994; Shi et al. 2007). The flavins secreted by S. oneidensis can facilitate to transfer electrons from bacteria to solid anode electrodes by acting as extracellular electron shuttles (Canstein et al. 2008). In this study, the genes encoding flavins (SO_1414, SO_3468, and SO_3058) had no significant increase (less than 1 fold change) as a response to nanoparticle decorated anode in MECs, which suggests that increased flavin gene expression does not significantly contribute to the current density enhancements in nano-particle decorated anode. The genes encoding cytochromes electron transport proteins (SO_4104, SO_0417, SO_1778/79, SO_0135/36) had no significant increase (less than 1-fold change). However, those genes were up-regulated slightly. These results suggest the increased expression flavin and c type cytochromes genes had partial contributions even not significantly to enhance current density in MFCs by NPs decorated anodes. The thickness of bacterial biofilm on the anode can affect the power generation in MFCs (Biffinger et al. 2007; Heydorn et al. 2000), since increased biofilm thickness on the anode represents more active bacteria involving in the process of electron generation 63 and transfer in MFCs. Biofilm formation related genes included flagellar genes IV, pilus genes and other genes. The flagellar related genes SO_3228, SO_3229 (fliB and fliK) and IV pilus genes SO_4105 (mshA) were induced from 1.9 to 0.9 fold; the genes (SO_4178 -4180) related to formation of a three-dimensional biofilm were up-regulated from 1.0 to 1.3 folds, even though the genes related bacterial motility protein (SO_ 4286, SO_4287, SO_1529 and SO_1530) are induced slightly (less than 0. 5 fold). However, the motility genes most probably play a role for initial biofilm attachment on the anode surfaces (Thormann et al. 2004; Thormann et al. 2006), with the rest of biofilm genes being more essential for biofilm maintenance in mature cultures as were presented at harvest in this study. This enhancement of biofilm density under conditions of increase current density has been observed for gold NP decorated anodes using confocal light microscopy (data not shown) but has not yet been confirmed for Fe NP decorated anodes. In any event, an increase in the expression level of genes related biofilm formation therefore also supported the possibility of enhanced biofilm formation on NPs decorated anodes, thus facilitating electron transfer from bacteria to anodes. Beliaev et al. described a model of the Fe reduction pathway in S oneidensis MR-1 using solid substrates as the electron acceptor (Beliaev et al. 2001). This model proposes that electrons are generated and released in cytoplasm then transferred to the quinone pool, e.g., menaquinone in the cytoplasmic membrane. The reduced menaquinone in turn reduces CymA, and from there electrons are then transferred to a periplasmic shuttle (e.g. CctA) and then to MtrA, a periplasmic soluble decaheme cytochrome c located in associated with the outer membrane via interaction with MtrB. Finally, surface displayed outer membrane proteins decaheme cytochromes (OmcA, MtrC, or MtrF) can transfer 64 electron to Fe or other solid substrates (Beliaev et al. 2001)). Bencheikh-Latmani et al., demonstrated that the same electron transport pathway may be used for more than one electron acceptor through studies of the response of S. oneidensis MR-1 to U(VI) and Cr(VI) under anaerobic conditions, particularly focused on the critical genes (SO_1777:mtrA, SO_1776:mtrB, SO_1778:mtrC) (Bencheikh-Latmani et al. 2005). However, our studies showed that these genes had no significant expression changes in response to nanostructured anodes. Contrastingly, one of expressed inner membrane protein genes SO_3104 and one of cytochromes genes SO_4609 encoding cytochrome c oxidase subunit III demonstrated a 1.3-fold and 1.1-fold up-regulation respectively in this study, while the gene SO_2194 which encodes outer membrane protein (OmpA family protein) was down regulated 3.6 fold. Our results therefore suggest that S. oneidensis MR-1 does not utilize the same set of core critical genes (SO_1777: mtrA, SO_1776: mtrB, SO_1778: mtrC) products to transfer electrons in all instances. This is the similar result with the study of Bretschger et al. (2007), which indicated that the electron transport system in S. oneidensis MR-1 is complex, with several different proteins able to participate in electron transfer to the anode of MECs. It should also be mentioned that the gene (SO_1519) encoding lactate dehydrogenase repressed (-1.2 fold) here suggesting that lactate was depleted at the time of cell harvest from the MECs and that other pathways of anaerobiosis had been activated including those associated with amino acid uptake and consumption; the growth media was a complex mixture including yeast extract. In particular, the catabolic pathway for histidine of S. oneidensis MR-1, a pathway that may formate as an intermediate, is upregulated, with the genes for histidine ammonia lyase, SO_0098, SO_3057 and SO_4374 65 up-regulated 1.3, 1.1, and 1.1-fold, respectively. The possible production of formate during histidine degradation may in turn explain the high levels of formate dehydrogenates as evidenced by upregulation of SO_0102, SO_0103, SO_0104 and SO_0107, annotated as formate dehydrogenase proteins. These genes had the highest levels of up-regulated expression as response to Fe NP decorated anodes (greater than 2fold). Acknowledgements This research was partially supported by the U.S. National Science Foundation CBET 0828544 and the funds from ONAMI/DOD (ARL-DOD Cooperative Agreement# W911NF-07-2-0083). We thank Barbara Gvakharia and Caprice Rosato for helpful suggestions. We also thank Margaret Romine of Pacific Northwest Laboratories for valuable comments on manuscripts. We also thank anonymous reviewers for significant suggested improvements imparted as part of prior review of this manuscript. 66 Chapter 5 Global Transcriptome Analysis of the Response of Shewanella oneidensis MR-1 to Carbon Nanotube Decorated Anodes in Microbial Electrochemical Systems Shoutao Xu, Yanzhen Fan, Rebecca Schaller, Frank Chaplen, Jun Jiao, Hong Liu* 67 Abstract: Shewanella oneidensis MR-1 is an important model microorganism for metabolic studies on the effects of different environmental factors because of its diverse respiratory capabilities. Carbon nanotube (CNT) modified graphite disks were used as anodes to investigate the effects of nanomatrials on the performance of S. oneidensis MR-1 in microbial electrolysis cells (MECs). The current densities produced with CNT decorated anodes were on average 5.6-fold higher than plain graphite anodes. Whole genome microarray analysis of gene expression showed that up-regulation of cytochromes c genes associated with extracellular electron transfer are strongly correlated to current increases in CNT decorated anodes. Genes involved in flavin biosynthesis also contribute to current increase in CNT decorated anode MECs. Keywords: Microbial electrochemical system; microbial fuel cell; microbial electrolysis cell; carbon nanotube, gene expression; DNA microarray. 68 Introduction: Shewanella oneidensis MR-1 is an important model microorganism for metabolic studies of the effects of different environmental factors because of its diverse respiratory capabilities. It has been used for transcriptome analysis to investigate the responses to different growth conditions and environmental stresses (Murray et al., 2001). Gene expression patterns under different conditions such as heat shock, cold shock, Cr (VI), U (VI) reduction, chromate stress, iron and acid tolerance have been studied previously (Bencheikh-Latmani et al. 2005; Brown et al. 2006; Gao et al.2006; Gao et al. 2004; Yang et al. 2008). More recently, it has been exploited as a model species for power generation in microbial electrochemical systems (MESs),which have potential applications in renewable energy generation, bioremediation, and wastewater treatment (Logan et al. 2007; Logan 2009; Park and Zeikus 2002; Fan et al 2011; Xu et al 2012). In a MES, electrochemically active microorganisms oxidize organic matter in the an ode chamber to release electrons. Electrons are then transferred to the anode electrode thr ough various mechanisms (Logan et al., 2006; Lovley 2006; Rabaey et al., 2003) and fina lly travel to the cathode electrode and combine with the terminal electron acceptor. The key feature of MESs is the microbe-catalyzed electron transfer from the organic matter to the anode (Rabaey et al 2004). Enhancing the current output, which highly depends on the performance of the anode electrode, is critical for the successful application of MESs (Logan et al. 2007; Park and Zeilus 2002; 2003). Several nanomaterials including TiO2, gold (Au) and palladium (Pd) nanoparticles have been utilized to decorate electrodes to enhance power density in MESs (Qiao et al. 2008; Quan et al. 2005; Fan et al. 2011). The possible mechanisms for increased current densities have been studied by using Fe 69 nanoparticle-decorated anodes (Xu et al 2012). Carbon nanotubes (CNT) are cylindrically shaped nanomaterials with extremely high surface area, excellent electrical conductivity and chemical inertness (He et al. 2005a; Serp et al. 2003). These unique properties make CNT a promising electrode material (Liang et al. 2008). The biocompatibility of microorganisms and carbon nanostructures has been evaluated (Morozan et al. 2007). The effects of CNT on anodic biofilms have been tested in MFCs (Liang et al. 2011). However, no studies have been re ported on global transcriptome analysis for the response of S. oneidensis MR-1 to CNT decorated anode in MECs. In the present study, the graphite disks decorated with CNT were used as anodes to investigate the effects of nanomaterials on current generation in multi-anode MECs. DNA microarrays were used to analyze differences in the global gene expression profile of S. oneidensis MR-1 grown on plain versus CNT decorated anodes. Materials and methods Bacterial cultures: S. oneidensis MR-1 was purchased from American Type Culture collection (ATCC 700550) and stored as freezer stocks at -80°C. Stock S. oneidensis MR-1 cells were grown aerobically using M1 medium at 30°C. Cells in early stationary growth phase (optical density of 1.5-1.6 at 600nm; (Spectrophotometer UV-1700, Shimadzu, Columbia, MD) were injected into the chamber of the MECs for current production. Sodium lactate (final concentration 30mM) was added as the additional electron donor. Fabrication and characterization of nanostructured anodes: Superfine isomolded graphite disks (1.6 cm x 0.5 cm, GraphiteStore.com, Inc.) were polished with ultrafine 70 sand paper (2000 grit, 3M Company) as the base for the CNT decorated and control anodes. Aligned multi-walled carbon nanotube samples were synthesized via plasma enhanced chemical vapor deposition (PECVD). Samples, superfine isomolded graphite pillars with a 1.6 cm diameter and 0.5 cm thickness, were sputtered with a thin film of Ni in a CRC 300 magnetron sputter coater for 1 to 2 min. They were then placed in the PECVD reactor where the Ni was annealed into small catalyst islands, C2H2 was bled into the chamber for growth, and an NH3 plasma was used to vertically align the growth of the multi-walled carbon nanotubes (MWCNTs). The temperature and time were varied between 725°C and 775oC and 15 to 60 min to control the length of the tubes and density of samples. Samples were then analyzed in a FEI Sirion field emission scanning electron microscope (FESEM). SEM images of CNT decorated anode and control surfaces were shown in the Figure 5.1. A B Figure 5.1, SEM images of CNT decorated anodes. (A) Graphite disk control; (B) CNT decorated anode. Multiple channel MECs construction and operation: A MECs with multiple removable anodes each with an effective anode area of 0.7 cm2 was constructed and used to evaluate the effects of nanostructures on the current density of according to a previous 71 study (Fan et al, 2011). The cathode was made of wet-proof (30%) carbon cloth (type B, E-TEK Division, Inc., USA) coated with Pt/C (20%, E-TEK Division, Inc., USA) following a previously reported procedure (Liu et al. 2005). The final platinum loading was 0.5 mg/cm2 per projected cathode area. The size of the cathode (150 cm2) was 25 times larger than the total effective area of the 8 graphite disk anodes (5.6 cm2) to prevent cathode limitations on the performance of the MECs system. All MECs with CNT decorated anodes and control anodes were tested for current generation for 24 h with sterile a medium (without bacteria) before injecting the bacterial cells in order to determine whether the CNT decorated anodes demonstrate chemical current generation compared to control anodes. All the testing anodes were set up in the MECs simultaneously so that the S. oneidensis MR-1 culture was applied to all of them simultaneously. Short electrode spacing (1.7 cm) was used in the MECs design to reduce the internal resistance. A voltage of 0.6 V was applied the MECs for current generation after the cells of S. oneidensis MR-1 were inoculated into the MECs in the early stationary phase. A multimeter with a data acquisition system (2700, Keithly, USA) was used to monitor the current change by measuring the voltage drop through a resistor. Microarray analysis: Biofilms for whole gene microarray analysis were aseptically removed from the plain and CNT decorated anodes of MECs after 80 hours further incubation at 30oC when current density obviously reached to a stable phase. Total RNA was extracted using Trizol (Ambion inc., Austin,TX) following the manufacturer’s instructions. Integrity of the RNA samples was confirmed using the Agilent 2100 Bioanalyzer (Agilent Technology Inc., Palo Alto, CA). Total RNA (200 ng) from each sample was amplified using the MessageAmpTM II-Bacteria Prokaryotic RNA A 72 Amplification kit (Ambion, Austin,TX) according to the manufacturer’s instructions. The S. oneidensis MR-1 whole-gene microarrays representing all of the 4295 genes (resource from NCBI) were ordered from Roche NimbleGen Inc. (Madison, WI). Biological triplicates of biofilms on the CNT decorated anodes and control were analyzed. cDNA synthesis, labeling and hybridization were carried out by the CGRB Core Laboratories at Oregon State University. DNASTAR ArrayStarTM 3 software was used to identify genes that were up- or down-regulated more than 2-fold when grown on the nanoparticle modified anodes using the unpaired two sample t-test with a cutoff p-value of 0.05 with bonferroni correction . Results and discussion: Enhancement of current generation using CNT decorated anodes in MECs: The current density generated by CNT decorated anode MECs with S. onidensis MR-1 increased to 36 µA/cm2 10 hours post-inoculation and reached a maximum of 40 µA/cm2 at 29 hours inoculation, then gradually decreased. The current density stabilized at 30µA/cm2 after 78 h operation. Figure 5.2 shows that the current density curve generated by CNT decorated anode in MECs. The average current density generated by CNT decorated anodes was 5.6 times that of the control. The current density generated in the MECs without bacteria was negligible (data not shown). This result demonstrates that the current enhancement observed with the CNT decorated anodes was biologically-derived. 73 48 Control Current density (µA/cm2) 41 CNT 34 27 20 13 6 -1 0 10 20 30 40 50 Time (Hours) 60 70 80 Figure 5.2 Effects of CNT decorated anodes on the current density in MECs (3 replicates) . Control is plain graphite disk anode; CNT is the anode with CNT decoration. (Error bars represent standard deviation) It has been reported that nanostructured decorated anodes have significant impacts on current densities (Fan et al. 2011; Qiao et al. 2006; Sharma 2008; Tsai et al. 2009). The CNT decorated anodes had significantly enhanced current densities in MECs in this study. This result is consistent with previous studies. Interestingly, the current density curve generated by CNT decorated anode MECs is quite different from the current density curve generated by Au NP and Pd NP decorated anodes using same bacterial species (Fan et al., 2011). In the Au and Pd NP decorated anode MECs, the current density curve was not significantly increased in the beginning compared with the control but gradually increased after the inoculation; the current density reached the maximum current density more than 50 hours after the inoculation. However, the current density generated by CNT decorated anode MECs started to increase significantly immediately after the inoculation. It reached a maximum current density 29 hours post-inoculation. 74 These results indicate that there might be different current density enhancement mechanisms between CNT with other metal NP decorated anodes in MECs. Global transcriptome analysis: Whole-genome DNA microarrays were used to attain a comprehensive, general overview of the transcriptional response of S. oneidensis MR-1 of S. oneidensis MR-1 to CNT decorated anodes in MECs. In a total of 4,295 genes analyzed, 457 genes (250 genes up-regulated and 207 genes down-regulated) exhibited significantly (P < 0.05) changed expression at a 2-fold level in at least 3 replicates in the response to CNT. The total number of the regulated genes present 11% of the 4,295 open reading frames (ORFs) presented on the microarray. The total number of genes at significant expression levels in response to CNT decorated anodes is close to that to Fe NP decorated anodes in MECs (392, 9%) ( Xu et al. 2012). 100 80 Up-regulated Number of Genes 60 40 20 0 -20 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 -40 -60 Down-regulated -80 Fig 5.3 Differentially expressed genes grouped by functional classification according to the TIGR S. oneidensis genome database (www.tigr.org). Columns: 1, amino acid biosynthesis; 2, biosynthesis of cofactors, prosthetic groups, and carriers; 3, cell envelope; 4, cellular processes; 5, central intermediary metabolism; 6, DNA metabolism; 7, energy metabolism; 8, fatty acid and phospholipid metabolism; 9, other categories; 10, protein fate; 11, protein synthesis; 12, purines, pyrimidines, nucleosides, and nucleotides; 75 13, regulatory functions; 14, signal transduction; 15, transcription; 16, transport and binding proteins; 17, unknown function; 18, hypothetical proteins. The overall transcript genomic response of S. oneidensis MR-1 to CNT decorated anodes was summarized in Figure 5.3 by grouping the differentially expressed genes into their functional role categories, based on The Institute for Genomic Research’s annotation (Version 8) of the MR-1 genome sequence. The wide distribution of putative functional roles attributed to the differentially expressed genes indicated the extent of the molecular response of S.oniedenis MR-1 to the CNT decorated anodes. A large number of upregulated genes were presented in genes associated with biosynthesis of cofactors, prosthetic groups, and carriers (group 2), cell envelope (group 3), protein fate (group 10), protein synthesis (group 11), and purines, pyrimidines, nucleosides, and nucleotides (group 12) in this study. The number of up-regulated genes was two times more than that of down-regulated genes in each functional group. Contrastingly, in the genomic response S. oneidensis MR-1 to Fe NP decorated anodes (chapter 4), most of up-regulated genes were associated with cellular processes (group 4), energy metabolism (group 7), other categories (group 9) and hypothetical proteins (group 18). The down-regulated genes presented in the amino acid biosynthesis (group 1), cellular processes (group 4), substrate transport (group 16), and hypothetical proteins (group 18). While those genes encoding proteins involved in amino acid biosynthesis (group 1), central intermediary metabolism ( group 5), DNA metabolism( group 6), fatty acid and phospholipid metabolism (group 8), and other categories (group 9) were among the most down-regulated genes in this study. However, the two groups of genes that were the most noticeable between the genomic response S. oneidensis MR-1 to CNT and Fe NP decorated anodes, which they are the genes related to energy metabolism (group 7), and hypothetical proteins (group 76 18). These results indicated there are different and common genomic responses to S. oneidensis MR-1 on CNT and Fe NP decorated anodes in MECs. Electron transfer related genes: Based on previous electron transfer mechanism studies on Shewanella, a serial of group proteins collectively described as the Mtr pathway play the role to transfer electron rom the inner bacterial body to the outer membrane (Beliaev et al. 2001, Shi et al. 2007, Brutinel and Gralnick, 2012). In the Mtr pathway, firstly electrons generated by bacteria received by CymA, a tetraheme c-type cytochrome anchored in the inner membrane, then electrons were transferred to MtrA, a periplasmic decaheme c-type cytochrome. After that, electrons were transferred from MtrA to MtrC, an outer-membrane decaheme c-type cytochrome is facilitated by MtrB, a non-heme containing integral outer-membrane protein.Outer-membrane decaheme c-type cytochrome MtrC and OmcA are in change of electron transfer to exreacellular electron acceptor (Shi et al. 2007, Brutinel and Gralnick, 2012 ). These genes encoding electron transport proteins are shown in the table 5.1. The critical genes SO_1777: mtrA, SO_1776: mtrB, SO_1778: mtrC are unregulated 4.1 to 8.0 fold in response to CNT decorated anodes, other cytochrome c genes related to electron transfer in MtrA pathway also are significantly increased in response to CNT decorated anodes. These genes encoding outer membrane proteins have different level increases, supporting that the increase of cytochrome c gene expression contributes to the current enhancements of MECs as response to CNT decorated anodes. 77 Table 5.1 Expression level of cytochrome c as response to CNT decorated anodes Locus Tag Gene product descriptions Fold change CNT SO_0165 general secretion pathway protein, GspC 3.1 SO_0167 general secretion pathway protein, GspE 4.5 SO_1776 outer membrane protein precursor MtrB 4.1 SO_1777 outer membrane decaheme cytochrome c 8.0 lipoprotein, MtrA SO_1778 outer membrane decaheme cytochrome c 4.3 lipoprotein, MtrC SO_1779 outer membrane decaheme cytochrome c, 6.3 OmcA SO_0135 lipoprotein of unknown function DUF333 2.2 SO_0136 conserved hypothetical inner membrane protein 2.4 Flavin related genes: It is known that self-produced mediators play critical roles in the electron transfer of S. oneidensis to extracellular insoluble electrode (Canstein von et al. 2 008; Myers et al. 1992; Scott et al. 1994; Shi et al. 2007). It has been proved that the flavins secreted by S. oneidensis can facilitate electron transfer from bacteria to solid anode electrodes by acting as extracellular electron shuttles (Cansterin von et al. 2008). T wo critical genes (SO_1414, and SO_3468) related to flavin synthesis were shown increa sed significantly (more than 2 folds) increase in this study (Table 5.2). This result support s the hypothesis that flavin production increases as the response to CNT decorated anodes in MECs, have significant contribution to the current density enhancements. 78 Table 5.2 Expression levels of genes related to flavin synthesis as response to CNT decorated anode Locus Tag Gene product descriptions Fold change CNT SO_1414 flavocytochrome c flavin subunit, putative 2.2 SO_3468 riboflavin synthase subunit alpha 2.0 The amount of bacterial biofilm biomass on the anode can affect the power generation in MFCs (Biffinger et al. 2007; Heydorn et al. 2000). Biofilm formation related genes include flagellar gene IV, pilus genes and other genes; the flagellar related genes (fliB and fliK) and IV pilus genes (mshA) were induced only from 1.05 to 1.34 fold as response of S. oneidensis MR-1 to CNT decorated anodes in this study. No biofilm-associated genes presented significant changes in expression levels in this study, indicating there is no direct connections between biofilm enhancements to CNT decorated anodes in this study. This result is consistent with the Liang et al (2011) conclusion that using CNT enhanced the electrochemical activity of anodic biofilms but did not result in a significant increase of biomass in the anodic biofilms. Our microarray results showed two significantly up-regulated gene groups: the genes encoding proteins localized on the outer membrane and the genes involved in flavin biosynthesis contributed to current density enhancement by CNT decorated anodes. Among 457 significantly changed genes to CNT in this study, there are also a relatively large number of genes encoding proteins with unknown functions, which are either up- or down-regulated in the response to CNT decorated anodes, which indicated more 79 complicated responses of S. oneidensis MR-1 to CNT decorated anodes in MECs and further study is needed . 80 Chapter 6 Summary Microbial electrochemical systems (MESs) with a mixed culture initially inoculated from Corvallis wastewater treatment plant have been studied for more than 6 years for varying purposes, including power generation, hydrogen production, heavy metal removal and wastewater treatment. Experiment results have shown that the mixed culture is quite stable with excellent performance in MESs. Our community analysis using denaturing gradient gel electrophoresis (DGGE) and 16S rDNA clone library construction suggests that the mixed culture is composed predominantly of Geobacter sp (66%), Arcobacter sp (12%) and Citrobacter sp (11%). These results not only improved our understanding of the mixed culture community, but also guided our studies on the cultivation and isolation of the different bacterial species. Exoelectrogenic Citrobacter sp SX-1 was first isolated and characterized from a MFC operated with the mixed culture. Citrobacter sp SX-1 has been demonstrated to produce electricity from wide range of different substrates, including citrate, acetate, glucose, sucrose, glycerol, and lactosein MFCs. Cyclic voltammetry analysis indicated that membrane associated proteins may play an important role in facilitating the electrons transferring from bacteria to electrode. The strain SX-1 increased the known diversity of power generating exoelectrogens and provided a unique bacterial species for study in renewable energy generation and waste treatment 81 To enhance the electron transfer from bacteria to anode, nano decorated anodes including Fe NP and CNT were developed and characterized and evaluated in MECs using Shewanella oneidensis MR-1 as a model species. Both nanostructures have significantly increased current density compared with the control. Whole genome microarray analysis elucidated the possible mechanisms of power enhancement in response to these nano-decorated anodes. These results benefit to understanding of physiology and ecology of mixed cultures in MFCs and improve the efficiency of current generation in MESs, which will facilitate the viability of niche applications for MESs in near future. 82 Bibliography 1. Amman R., Ludwig W. (2000) Ribosomal RNA-targeted nucleic acid probes for studies in microbial ecology. FEMS Microbiol. Ecol., 24: 555–565. 1. Bao SJ., Li CM., Zang JF., Cui XQ., Qiao Y., Guo J. (2008) Novel Nanoporous TiO2 Electrode for Directly Electrochemistry of glucose oxidase. Adv Funct Mater 18(4): 591-599. 2. Beliaev AS., Saffarini DA, McLaughlin JL., Hunnicutt D. (2001) MtrC, an outer membrane decahaem c cytochrome required for metal reduction in Shewanella putrefaciens MR-1. Mol Microbiol 39:722-30. 3. Bencheikh-Latmani R., Williams SM., Haucke L., Criddle CS., Wu L., Criddle CS., Zhou J., Tebo BM. (2005) Global transcriptional profiling of Shewanella oneidensis MR-1 during Cr(VI) and U(VI) reduction. Appl Environ Microbiol 71: 7453–7460. 4. Biffinger JC., Pietron J., Ray R., Little B. and Ringeisen BR. (2007) A biofilm enhanced miniature microbial fuel cell using Shewanella oneidensis DSP10 and oxygen reduction cathodes. Biosens Bioelectron 22:1672–1679. 5. Bodelier PLE., Roslev P., Henckel T., FenzelP. (2000) Stimulation by ammonium based fertilizers of methane oxidation in soil around rice root. Nature 40: 421–424. 6. Bond DR., Holmes DE., Tender LM., Lovley DR. (2002) Electrode-reducing microorganisms that harvest energy from marine sediments. Science 295: 483-485. 7. Bond DR., Lovley DR. (2003) Electricity production by Geobacter sulfurreducens attached to electrodes. Appl Environ Microbiol 69: 1548-1555. 8. Bond DR., Lovley DR. (2005) Evidence for involvement of an electron shuttle in electricity generation by Geothrix fermentans. Appl Environ Microbiol 71: 21862189. 9. Bretschger O., Obraztsova A., Sturm CA., Chang IS., Gorby YA., Reed SB., Culley, DE., Reardon CL., Barua S., Romine MF., Zhou J., Beliaev AS., Bouhenni R., Saffarini D., Mansfeld F., Kim BH., Fredrickson JK., Nealson KH. (2007) Current production and metal oxide reduction by Shewanella oneidensis MR-1 wildtype and mutants. Appl Environ Microbiol 73: 7003–7012. 10. Brown SD., Thompson MR., Verberkmoes NC., Chourey K., Shah M., Zhou J., Hettich RL., and Thompson DK. (2006) Molecular dynamics of the Shewanella oneidensis response to chromate stress. Mol Cell Proteomics 5:1054-1071. 11. Brutinel ED., Gralnick JA. (2012) Shuttling happens: soluble flavin mediators of extracellular electron transfer in Shewanella. Appl. Microbiol Biotechnol. 93(1): 41-8. 12. Butler JE., Kaufmann F., Coppi MV., Núñez C., Lovley DR. (2004) MacA, a diheme c-type cytochrome involved in Fe(III) reduction by Geobacter sulfurreducens. J. Bacteriol. 186(12): 4042–4045. 83 13. Caccavo F., Lonergan DJ., Lovley DR., Davis M., Stolz JF., McInerney MJ. (1994) Geobacter sulfurreducens sp. nov., a hydrogen- and acetate oxidizing dissimilatory metal-reducing microorganism. Appl Environ Microbiol 60: 3752–3759. 14. Canstein von H., Ogawa J., Shimizu S., Lloyd JR. (2008) Secretion of flavins by Shewanella species and their role in extracellular electron transfer. Appl Environ Microbiol 74: 615–623. 15. Cao X., Huang X., Liang P., Xiao K., Zhou Y., Zhang X., Logan BE. (2009) A New Method for Water Desalination Using Microbial Desalination Cells. Environ Sci Technol 43(18):7148-7152. 16. Chaudhuri SK., Lovley DR. (2003) Electricity generation by direct oxidation of glucose in mediatorless microbial fuel cells. Nat Biotechnol 21: 1229-1232. 17. Cheng S., Liu H., Logan B. E. (2006) Increased power generation in a continuous flow MFC with advective flow through the porous anode and reduced electrode spacing. Environ. Sci. Technol. 40:2426-2432. 18. Cheng S., Logan B. E. (2007) Sustainable and efficient biohydrogen production via electrohydrogenesis. PNAS. 104: 18871-18873. 19. Chignell J., (2010) Energy Recovery from Biodiesel Waste: Performance of Microbial Electrochemical Systems on Glycerol. Thesis. 20. Chung K., Okabe S. (2009) Characterization of electrochemical activity of a strain ISO2-3 phylogenetically related to Aeromonas sp. isolated from a glucose-fed microbial fuel cell. Biotechnol Bioeng 104(5): 901-910. 21. Cole J.R., Chai B., Farris R.J., Wang Q., Kulam-Syed-Mohideen A.S., McGarrell D.M., Bandela A.M., Cardenas E., Garrity G.M., Tiedje J.M. (2007) The ribosomal database project (RDP-II): introducing myRDP space and quality controlled public data. Nucleic Acids Res 35 (Database issue): D169-D172; doi: 10.1093/nar/gkl889. 22. Cole J.R., Wang Q., Cardena E., Fish J., Chai B., Farris R.J., Kulam-Syed-Mohideen A.S., McGarrell D.M., Marsh T., Garrity G.M., Tiedje J.M. (2009) The Ribosomal Database Project: improved alignments and new tools for rRNA analysis. Nucleic Acids Res 37 (Database issue): D141-D145; doi: 10.1093/nar/gkn879. 23. Dey A., De S., De A., De SK. (2004) Characterization and dielectric properties of polyaniline-TiO2 nanocomposites. Nanotechnol 15: 1277-1283. 24. Edwards U., Rogall T., Blöcker H., Emde M., Böttger EC. (1989) Isolation and direct complete nucleotide determination of entire genes—characterization of a gene coding for 16S-ribosomal RNA. Nucleic.Acids. Res. 17: 7843–7853. 25. Eggleston C.M., Vörös J., Shi L., Lower B.H., Droubay T.C., Colberg P.J.S. (2008) Binding and direct electrochemistry of OmcA, an outer-membrane cytochrome from an iron reducing bacterium, with oxide electrodes: a candidate biofuel cell system. Inorg Chim Acta 361:769–777. 26. Fan Y., Sharbrough E., Liu H. (2008) Quantification of the Internal Resistance Distribution of Microbial Fuel Cells. Environ Sci Technol 42: 8101–8107. 84 27. Fan Y., Xu S., Schaller R., Jiao J., Chaplen F., Liu H. (2011) Nanoparticle decorated anodes for enhanced current generation in microbial electrochemical cells. Biosensors and Bioelectronics, 26 (5):1908–1912. 28. Fan Y., Hu H., Liu H. (2007)Sustainable power generation in microbial fuel cells using bicarbonate buffer and proton transfer mechanisms. Environ Sci Technol. 41(23): 8154-8. 29. Fedorovich V., Knighton M.C., Pagaling E., Ward F.B., Free A., Goryanin I. (2009) Novel electrochemically active bacterium phylogenetically related to Arcobacter butzleri, isolated from a microbial fuel cell. Appl Environ Microbiol 75(23): 73267334. 30. Ferna´ndez A., Huang S., Seston S., Xing J., Hickey R., Criddle C., Tiedje J. (1999) How stable is stable? Function versus community composition. Appl Environ Microbiol 65: 3697–3704. 31. Field S.J., Dobbin P.S., Cheesman M.R., Watmough N.J., Thomson A.J., Richardson D.J. (2000) Purification and magneto-optical spectroscopic characterization of cytoplasmic membrane and outer membrane multiheme c-type cytochromes from Shewanella frigidimarina NCIMB400. J Biol Chem 275: 8515–8522. 32. Freguia S., Masuda M., Tsujimura S., Kano K. (2009) Lactococcus lactis catalyses electricity generation at microbial fuel cell anodes via excretion of a soluble quinone. Bioelectrochemistry 76:14–18. 33. Fricke K., Harnisch F. and Schröder U. (2008) On the use of cyclic voltammetry for the study of the anodic electron transfer in microbial fuel cells. Energy Environ Sci 1: 144–147. 34. Gao H., Wang Y., Liu X., Yan T., Wu L., Alm E., Arkin A., Thompson DK. and Zhou J. (2004) Global transcriptome analysis of the heat shock response of Shewanella oneidensis. J Bacteriol 186:7796-7803 35. Gao H., Yang ZK., Wu L., Thompson DK., Zhou J. (2006) Global transcriptome analysis of the cold shock response of Shewanella oneidensis MR-1 and mutational analysis of its classical cold shock proteins. J Bacteriol 188:4560-4569. 36. George M.G. (2005) Bergey’s Manual of Systematic Bacteriology Volume Two The Proteobacteria Part B The Gammaproteobacteria. Second Edition. New York: Springer. 651p 37. González-Toril E., Llobet-Brossa E., Casamayor EO., Amann R., Amils R. (2003) Microbial ecology of an extreme acidic environment, the Tinto river. Appl Environ Microbiol 69(8): 4853–4865. 38. Gorby Y.A., Yanina S., Mclean J.S., Rosso K.M., Moyles D., Dohnalkova A., Beveridge T.J., Chang I.S., Kim B.H., Kim K.S., Culley D.E., Reed S.B., Romine M. F., Saffarini D.A., Hill E.A., Shi L., Elias D.A., Kennedy D.W., Pinchuk G., Watanabe K., Ishii S., Logan B., Nealson K.H., Fredrickson J.K. (2006) Electrically conductive bacterial nanowires produced by Shewanella oneidensis strain MR-1 and other microorganisms. Proc Natl Acad Sci USA. 103:11358-11363. 85 39. He Z., Wagner N., Minteer SD., Angenent LT. (2006) An upflow microbial fuel cell with an interior cathodes: assessment of the internal resistance by impedance spectroscopy:. Environ. Sci. Technol. 40: 5212-5217. 40. Heydorn A., Nielsen AT., Hentzer M., Sternberg C., Givskov M., Ersbøll BK., Molin S. (2000) Quantification of biofilm structures by the novel computer program COMSTAT. Microbiol 146:2395-2407. 41. Holmes D.E., Bond D.R., Lovley D.R. (2004a) Electron transfer by Desulfobulbus propionicus to Fe(III) and graphite electrodes. Appl Environ Microbiol 70:1234– 1237. 42. Holmes D.E., Chaudhuri S.K., Nevin K.P., Mehta T., Methe B.A., Liu A., Ward J.E., Woodard T.L., Webster J., Lovley D.R. (2006) Microarray and genetic analysis of electron transfer to electrodes in Geobacter sulfurreducens. Environ Microbiol 8:1805-1815. 43. Holmes D.E., Nicoll J.S., Bond D.R., Lovley D.R. (2004b) Potential role of a novel psychrotolerant member of the family Geobacteraceae, Geopsychrobacter electrodiphilus gen. nov., sp. nov., in electricity production by a marine sediment fuel cell. Appl Environ Microbiol 70: 6023–6030. 44. Holmes DE., Chaudhuri SK., Nevin KP., Mehta T., MethéBA., Liu A., Ward JE., Woodard TL., Webster J., Lovley DR. (2006) microarray and genetic analysis of electron transfer to electrodes in Geobacter sulfurreducens. Environ. Microbial. 8(10):1805-1815. 45. Hu H, (2009). Enhancing Hydrogen Production in Microbial Electrolysis Cells through Development of Platinum-free Cathode and Improvement of Reactor. Dissertation. 46. Ince B.K., Ayman O N., Turker G., Çelikkol S., Ince O. (2010) Microbial ecology of anaerobic reactors for treatment of alcohol industry wastewaters: a review . Current research, technology and education topics in applied microbiology and microbial ecology. 988-999. 47. Jung S., Regan J.R. (2007) Comparison of anode bacterial communities and performance in microbial fuel cells with different electron donors Appl. Microbiol. Biotechnol. 77:393– 402. 48. Kim B.H., Kim H.J., Hyun M.S., Park D.H. (1999) Direct electrode reaction of Fe(III) reducing bacterium Shwwanella putrefaciens. J Microbial Biotechnol 9:127-131. 49. Kim GT., Hyun MS., Chang IS., Kim HJ., Park HS., Kim BH., Kim SD., Wimpenny JW., Weightman AJ. (2005) Dissimilatory Fe(III) reduction by an electrochemically active lactic acid bacterium phylogenetically related to Enterococcus gallinarum isolated from submerged soil. J .Appl. Microbiol. 99(4): 978–987. 50. Kim GT., Webster G., Wimpenny JW., Kim BH., Kim HJ., Weightman AJ. (2006) Bacterial community structure, compartmentalization and activity in a microbial fuel cell. J Appl. Microbiol. 101(3): 698–710. 86 51. Kim H.J., Park H.S., Hyun M.S., Chang I.S., Kim M., Kim B.H. (2002) A mediatorless microbial fuel cell using a metal reducing bacterium, Shewanella putrefaciens. Enzyme Microb Technol 30: 145-152. 52. Kim J.R., Min B., Logan B.E. (2005) Evaluation of procedures to acclimate a microbial fuel cell for electricity production. Appl Microbiol Biotechnol 68(1):23-30. 53. Kim JR., Cheng S., Oh SE., Logan BE. (2007) Power generation using different cation, anion, and ultrafiltration membranes in microbial fuel cells. Environ. Sci. Technol. 41: 1004-1009. 54. Konstantinidis KT., Serres MH., Romine MF., Rodrigues JL., Auchtung J., McCue LA., Lipton MS., Obraztsova A., Giometti CS., Nealson KH., Fredrickson JK., Tiedje JM. (2009) Comparative systems biology across an evolutionary gradient within the Shewanella genus. Proc Natl Acad Sci U S A 106(37):15909-15914. 55. Lee J., Phung NT., Chang IS., Kim BH., Sung HC. (2003) Use of acetate for enrichment of electrochemically active microorganisms and their 16S rDNA analyses. FEMS Microbiol. Lett. 223:185–191. 56. Liang P, Wang H, Xia X, Huang X, Mo Y, Cao X, Fan M.(2011)Carbon nanotube powders as electrode modifier to enhance the activity of anodic biofilm in microbial fuel cells. Biosens Bioelectron. 26(6):3000-4. 57. Lies DP., Hernandez ME., Kappler A., Mielke RE., Gralnick JA., Newman DK. (2005) Shewanaella oneidensis MR-1 uses overlapping pathways for iron reduction at a distance and by direct contact under conditions relevant for biofilms. Appl. Environ. Microbiol. 71: 4414-4426. 58. Liu H., and Logan B. E. (2004) Electricity generation using an air-cathode single chamber microbial fuel cell in the presence and absence of a proton exchange membrane. Environ. Sci. Technol. 38: 4040-4046. 59. Liu H., Grot S., Logan B.E. (2005) Electrochemically assisted microbial production of hydrogen from acetate. Environ. Sci. Technol. 39: 4317 – 320. 60. Liu H., Hu H., Chignell J., Fan, Y. (2010) Microbial Electrolysis: Novel Technology for Hydrogen Production from Biomass. Biofuels 1(1): 129–142. 61. Liu H., Ramnarayanan R., Logan B.E. (2004) Production of electricity during wastewater treatment using a single chamber microbial fuel cell. Environ Sci Technol 38:2281-2285. 62. Liu WT., Marsh TL., Cheng H., Forney LJ. (1997) Characterization of microbial diversity by determining terminal restriction fragment length polymorphisms of gene encoding 16S rRNA. Appl. Environ. Microbiol. 63: 4516–4522. 63. Logan B E., Hamelers B., Rozendal R., Schroder U., Keller J., Freguia S., Aelterman P., Verstraete W., Rabaey K. (2006) Microbial fuel cells: methodology and technology. Environ Sci Technol 40 (17): 5181-5192. 64. Logan B. E. and Regan J.M. (2006) Electricity-producing bacterial communities in microbial fuel cells. Trends. Microbiol. 14:512–518. 87 65. Logan B., Cheng S., Watson V., Estadt G. (2007) Graphite fiber brush anodes for increased power production in air-cathode microbial fuel cells. Environ Sci Technol 41(9):3341-3346. 66. Logan B.E. (2009) Exoelectrogenic bacteria that power microbial fuel cells. Nat Rev Microbiol 5: 375-381. 67. Logan B.E., Call D., Cheng S., Hamelers HV., Sleutels TH., Jeremiasse AW., Rozendal RA. (2008) Microbial electrolysis cells for high yield hydrogen gas production from organic matter. Environ Sci Technol 42: 8630-8640. 68. Logan B.E., Hamelers B., Rozendal R., Schroder U., Keller J., Freguia S., Aelterman P., Verstraete W., Rabaey K. (2006) Microbial fuel cells: methodology and technology. Environ. Sci.Technol. 40: 5181-5192. 69. Lovely D.R. (2006) Bug juice: harvesting electricity with microorganisms. Nature Review| Microbiology. 4: 497-508. 70. Lovley D.R., Phillips E.J. (1988) Novel Mode of Microbial Energy Metabolism: Organic Carbon Oxidation Coupled to Dissimilatory Reduction of Iron or Manganese. Appl Environ Microbiol 54(6): 1472-1480. 71. Ly HK., Sezer M., Wisitruangsakul N., Feng JJ., Kranich A., Millo D., Weidinger IM., Zebger I., Murgida DH., Hildebrandt P. (2011) Surface-enhanced vibrational spectroscopy for probing transient interactions of proteins with biomimetic interfaces: electric field effects on structure, dynamics and function of cytochrome c. FEBS J. 278(9):1382-90. 72. Macaskie L.E., Hewitt C.J., Shearer J.A., Kent C.A. (1995) Biomass production for the removal of heavy metals from aqueous solutions at low pH using growthdecoupled cells of a Citrobacter sp. Int Biodeter Biodegr 35:73–92. 73. Malki M., De Lacey A.L., Rodriguez N., Amils R., Fernandez V.M. (2008) Preferential use of an anode as an electron acceptor by an acidophilic bacterium in the presence of oxygen. Appl Environ Microbiol 74: 4472–4476. 74. Meitl L.A., Eggleston C.M., Colberg PJS., Khare N., Reardon C.L., Shi L. (2009) Electrochemical interaction of Shewanella oneidensis MR-1 and its outer membrane cytochromes OmcA and MtrC with hematite electrodes. Geochim Cosmochim Ac 73(18): 5292-5307. 75. Morozan A., Stamatin L. and Nastase F. (2007) The biocompatibility microorganisms-carbon nanostructures for applications in microbial fuel cells. Phys Stat Sol 6: 1797-1803. 76. Morris J.M., Jin S., Crimi B., Pruden A. (2009) Microbial fuel cell in enhancing anaerobic biodegradation of diesel. Chem Eng J 146: 161–167. 77. Murray AE., Lies D., Li G., Nealson K., Zhou J., Tiedje JM. (2001) DNA/DNA hybridization to microarrays reveals gene-specific differences between closely related microbial genomes. Proc Natl Acad Sci U S A 98: 9853-9858. 78. Muyzer G., de Waal EC., Uitterlinden AG. (1993) Profiling of complex microbial communities by denaturing gradient gel electrophoresis analysis of polymerase chain 88 reaction amplified genes coding for 16S rRNA. Appl. Environ. Microbiol. 59: 695– 700. 79. Myers C.R., Myers J.M. (1992) Localization of cytochromes to the outer membrane of anaerobically grown Shewanella putrefacians MR-1. J Bacteriol 174: 3429–3438. 80. Narde G.K., Kapley A., Purohit H.J. (2004) Isolation and characterization of Citrobacter strain HPC255 for broad-range substrate specificity for chlorophenols. Curr Microbiol 48(6): 419-423. 81. Okabe S., Ito T., Sugita K., Satoh H. (2005) Succession of internal sulfur cycles and sulfur-oxidizing bacterial communities in microaerophilic wastewater biofilms. Appl Environ Microbiol 71(5): 2520-2529. 82. Park D.H., and Zeikus J.G. (2000) Electricity generation in microbial fuel cells using neutral red as an electronophore. Appl Environ Microbial 66: 292-1297. 83. Park D.H., and Zeikus J.G. (2002) Impact of electrode composition on electricity generation in a single-compartment fuel cell using Shewanella putrefaciens. Appl Microbiol Biotechnol 59:58–56. 84. Park D.H., and Zeikus J.G. (2003) Improved fuel cell and electrode designs for producing electricity from microbial degradation. Biotechnol Bioeng 81: 348–355. 85. Park H.S., Kim B.H., Kim H.S., Kim H.J., Kim G.T., Kim M., Chang I.S., Park Y. K., Chang H.I. (2001) A novel electrochemically active and Fe(III)-reducing bacterium phylogenetically related to Clostridium butyricum isolated from a microbial fuel cell. Anaerobe 7: 297-306. 86. Parot S., Nercessian O., Delia M.L., Achouak W., Bergel A. (2009) Electrochemical checking of aerobic isolates from electrochemically active biofilms formed in compost. J Appl Microbiol 106(4): 1350-1359. 87. Pham C.A., Jung S.J., Phung N.T., Lee J., Chang I.S., Kim B.H., Yi H., Chun J. (2003) A novel electrochemically active and Fe(III)-reducing bacterium phylogenetically related to Aeromonas hydrophila, isolated from a microbial fuel cell. FEMS Microbiol Lett 223: 129-134. 88. Qiao Y., Bao SJ., Li CM., Cui XQ., Lu ZS., Guo J. (2008) Nanostructured polyaniline/titanium dioxide composite anode for microbial fuel cells. ACS Nano 2: 113-119. 89. Qiu R., Zhao B., Liu J., Huang X., Li Q., Brewer E., Wang S., Shi N. (2009) Sulfate reduction and copper precipitation by a Citrobacter sp. isolated from a mining area. J Hazard Mater 164:1310-1315. 90. Quan X., Yang SG., Ruan X.L. and Zhao H.M. (2005) Preparation of titania nanotubes and their environmental applications as electrode. Environ Sci Technol 39: 3770–3775 91. Rabaey K., Boon N., Hofte M., Verstraete W. (2005) Microbial phenazine production enhances electron transfer in biofuel cells. Environ Sci Technol 39:3401– 3408. 89 92. Rabaey K., Boon N., Siciliano S D., Verhaege M., Verstraete W. (2004) Biofuel cells select for microbial consortia that self-mediate electron transfer. Appl Environ Microbiol 70(9): 5373–5382. 93. Rabaey K., Lissens G., Siciliano S. D., Verstraete W. (2003) Amicrobial fuel cell capable of converting glucose to electricity at high rate and efficiency. Biotechnol. Lett. 25: 1531-15. 94. Rabaey K., Verstraete W. (2005). Microbial fuel cells: novel biotechnology for energy generation. Trends Biotechnol 23(6): 291-298. 95. Reguera G., McCarthy K.D., Mehta T., Nicoll J.S., Tuominen M.T., Lovley D.R. (2005) Extracellular electron transfer via microbial nanowires. Nature 435: 10981101. 96. Reguera G., Nevin K.P., Nicoll J.S., Covalla S.F., Woodard T.L., Lovley D.R. (2006) Biofilm and nanowire production leads to increased current in Geobacter sulfurreducens fuel cells. Appl Environ Microbiol 72: 7345-7348. 97. Reimers C.E., Tender L.M., Fertig S., Wang W. (2001) Harvesting energy from the marine sediment-water interface. Environ Sci Technol 35:192-195. 98. Rezaei F., Xing D., Wagner R., Regan J.M., Richard T.M., Logan B.E. (2009) Simultaneous cellulose degradation and electricity production by Enterobacter cloacae in a microbial fuel cell. Appl Microbiol Biotechnol 75: 3673–3678. 99. Richter H., Nevin K.P., Jia H., Lowy D.A.., Lovley D.R., Tender L.M. (2009) Cyclic voltammetry of biofilms of wild type and mutant Geobacter sulfurreducens on fuel cell anodes indicates possible roles of OmcB, OmcZ, type IV pili, and protons in extracellular electron transfer. Energy Environ Sci 2: 506–516. 100.Riesenfeld S.C., Schloss D.P., Handelsman J.(2004) Metagenomics: Genomic Analysis of Microbial Communities. Annual Review Genetics. 38:525-552. 101.Rozendal RA., Hamelers HV., Buisman CJ.. (2006) Effects of membrane cation transport on pH and microbial fuel cell performance. Environ. Sci. Technol. 40: 5206-5211. 102.Rozendal RA., Hamelers HVM., Euverink GJW., Metz SJ., Buisman CJN. (2006) Principle and perspectives of hydrogen production through biocatalyzed electrolysis. Int J Hydrogen Energ 31:1632-1640. 103.Rozendal RA., Hamelers HV., Molenkamp RJ., Buisman CJ. (2007) Performance of single chamber biocatalyzed electrolysis with different types of ion exchange membrances. Water Res. 41: 1984-1994. 104.Schlüter A., Bekel T., Diaz NN., Dondrup M., Eichenlaub R., Gartemann KH., Krahn I., Krause L., Krömeke H., Kruse O., Mussgnug JH., Neuweger H., Niehaus K., Pühler A., Runte KJ., Szczepanowski R., Tauch A., Tilker A., Viehöver P., Goesmann A. (2008) The metagenome of a biogas-producing microbial community of a production-scale biogas plant fermenter analyzed by the 454-pyrosequencing technology. J Biotechnol.136: 77-90. 90 105.Scott J. H., and Nealson K.H. (1994) A biochemical study of the intermediary carbon metabolism of Shewanella putrefaciens. J Bacteriol 176(11): 3408–3411. 106.Sekiguchi H., Tomioka H., Nakahara T., and Uchiyama H. (2001) A single band does not always represent single bacterial strains in denaturing gradient gel electrophoresis analysis. Biotechnology Letters.23: 1205–1208. 107.Sharma T., Leela M., Reddy A., Chandra TS., Ramaprabhu S. (2008) Development of carbon nanotubes and nanofluids based microbial fuel cell. Int J Hydrogen Energ 33:6749–6754. 108.Shea C., Clauwaert P., Verstraete W., Nerenberg R. (2008) Adapting a denitrifying biocathode for perchlorate reduction. Water Sci Technol 58 (10): 1941-1946. 109.Shi L., Squier TC., Zachara JM., Fredrickson JK. (2007) Respiration of metal (hydr) oxides by Shewanella and Geobacter: a key role for multihaem c-type cytochromes. Mol Microbiol 65:12-20. 110. Stams AJ. and Plugge CM.(2009)Electron transfer in syntrophic communities of anaerobic bacteria and archaea. Nat Rev Microbiol.7(8):568-77. 111.Sukkasem C., Xu S., Park S., Boonsawang P., Liu H. (2008) Effect of Nitrate on the Performance of Single Chamber Air Cathode Microbial Fuel Cells. Water Res 42(19): 4743-4750. 112.Summers ZM., Fogarty HE., Leang C., Franks AE., Malvankar NS., Lovley DR. ( 2010 ) Direct exchange of electrons within aggregates of an evolved syntrophic coculture of anaerobic bacteria. Science. 330 (6009):1413-5. 113.Szczepanowski R., Bekel T., Goesmann A., Krause L., Krömeke H., Kaiser O., Eichler W., Pühler A., Schlüter A. (2008) Insight into the plasmid metagenome of wastewater treatment plant bacteria showing reduced susceptibility to antimicrobial drugs analysed by the 454-pyrosequencing technology, J Biotechnol. 136: 54-64. 114.Tamura K., Dudley J., Nei M., Kumar S. (2007) MEGA4: Molecular Evolutionary Genetics Analysis (MEGA) software version 4.0. MolBiol Evol 24(8): 1596-1599. 115.Thompson J.D., Gibson T.J., Plewniak F., Jeanmougin F., Higgins D.G. (1997) The CLUSTAL_X windows interface: flexible strategies for multiple sequence alignment aided by quality analysis tools. Nucleic Acids Res 25: 4876-4882. 116.Thormann KM., Duttler S., Saville RM., Hyodo M., Shukla S., Hayakawa Y., Spormann AM. (2006) Control of formation and cellular detachment from Shewanella oneidensis MR-1 biofilms by cyclic di-GMP. J Bacteriol 188:2681-2691. 117. Thormann KM., Saville RM., Shukla S., Pelletier DA., Spormann AM. (2004) Initial Phases of biofilm formation in Shewanella oneidensis MR-1. J Bacteriol 186(23): 8096-104. 118.Torres CI., Kato Marcus A., Rittmann BE. (2008b) Proton transport inside the biofilm limits electrical current generation by anode-respiring bacteria. Biotechnol Bioeng 100: 872–881. 91 119.Torres CI., Marcus AK., Lee HS., Parameswaran P., Krajmalnik-Brown R., Rittmann BE. (2010) A kinetic perspective on extracellular electron transfer by anoderespiring bacteria. FEMS Microbiol Rev. 234(1):3-17. 120.Torres CI., Marcus AK., Parameswaran P., Rittmann BE. (2008a) Kinetic experiments for evaluating the Nernst–Monod model for anode-respiring bacteria (ARB) in a biofilm anode. Environ Sci Technol 42: 6593–6597. 121.Tsai HY., Wu Ch-Ch., Lee Ch-Y., Shih EP. (2009) Microbial fuel cell performance of multiwall carbon nanotubes on carbon cloth as electrodes. J Power Sources 194:199-205. 122.Tyson GW., Chapman J., Hugenholtz P., Allen EE., Ram RJ., Richardson PM., Solovyev VV., Rubin EM., Rokhsar DS., Banfield JF.(2004) Community structure and metabolism through reconstruction of microbial genomes from the environment. Nature.428:37-43. 123.Venkateswaran K., Moser DP., Dollhopf ME., Lies DP., Saffarini D A., MacGregor BJ., Ringelberg DB., White DC., Nishijima M., Sano H., Burghardt J., Stackebrandt E., Nealson KH. (1999) Polyphasic taxonomy of the genus Shewanella and description of Shewanella oneidensis sp. Int J Syst Bacteriol 49:705-724. 124.von Canstein H., Ogawa J., Shimizu S., Lloyd JR. (2008) secretion of Flavins by Shewanella Species and Their Role in Extracellular Electron Transfer. Appl. Environ. Microbiol. 74: 3615-623. 125.Wang A., Liu W., Cheng Sh., Xing D., Zhou J. Logan BE. (2009) Source of methane and methods to control its formation in single chamber microbial electrolysis cells. Int J Hydrogen Energ 34: 3653-3658 126.Wang J., Ma T., Zhao L., Lv J., Li G., Liang F., Liu R. (2008) PCR–DGGE method for analyzing the bacterial community in a high temperature petroleum reservoir. World J Microbiol Biotechnol 2: 9694-9702. 127.Wang Q., Garrity G.M., Tiedje J.M., Cole J.R. (2007) Naïve Bayesian Classifier for Rapid Assignment of rRNA Sequences into the New Bacterial Taxonomy. Appl Environ Microbiol 73(16): 5261-5267. 128.Wang Y.F., Masuda M., Tsulimura S., Kano K. (2008) Electrochemical regulation of the end-product profile in Propionibacterium freudenreichii ET-3 with an endogenous mediator. Biotechnol Bioeng 101(3): 579–586. 129.Wrighton K.C., Agbo P., Warnecke F., Weber K.A., Brodie E.L., DeSantis T.Z., Hugenholtz P., Andersen G.L., Coates J.D. (2008) A novel ecological role of the Firmicutes identified in thermophilic microbial fuel cells. ISME J 2: 1146–1156. 130.Xing D., Zuo Y., Cheng S., Regan J.M., Logan B.E. (2008) Electricity generation by Rhodopseudomonas palustris DX-1. Environ Sci Technol 42: 4146-4151. 131.Xu S, Liu H, Fan Y, Schaller R, Jiao J, Chaplen F. (2012) Enhanced performance and mechanism study of microbial electrolysis cells using Fenanoparticle-decorated anodes. Appl Microbiol Biotechnol. 93(2):871-880. 92 132.Yang Y., Harris DP., Luo F., Wu L., Parsons AB., Palumbo AV., Zhou J. (2008) Characterization of the Shewanella oneidensis Fur gene: roles in iron and acid tolerance response. BMC Genomics 9 Suppl 1:S11. 133.Zhang L., Zhou S., Zhuang L., Li W., Zhang J., Lu N., Deng L. (2008) Microbial fuel cell based on Klebsiella pneumoniae biofilm. Electrochem Commun10: 1641– 1643. 134.Zuo Y., Xing D.F., Regan J.M., Logan B.E. (2008) Isolation of the exoelectrogenic bacterium Ochrobactrum anthropi YZ-1 by using a U-tube microbial fuel cell. Appl Environ Microbiol 74: 3130-3137 93 APPENDICES List of published papers during PhD study 1. Shoutao Xu, Hong Liu, Yanzhen Fan, Rebecca Schaller, Jun Jiao and Frank Chaplen. (2012) Enhanced performance and mechanism study of microbial electrolysis cells using Fe nanoparticle-decorated anodes. Applied Microbiology and Biotechnology, 93(2):871-880. 2. Shoutao Xu, Hong Liu. (2011) New exoelectrogen Citrobacter sp. SX-1 isolated from a microbial fuel cell. Journal of Applied Microbiology,111(5):1108-1115. 3. Yanzhen Fan, Shoutao Xu, Rebecca Schaller, Jun Jiao, Frank Chaplen, Hong Liu (2011) Nanoparticle decorated anodes for enhanced current generation in microbial electrochemical cells. Biosensors and Bioelectronics, 26(5): 1908-1912. 4. Tunc Catal, Shoutao Xu, Kaichang Li, Hakan Bermek, Hong Liu. (2008) Electricity generation from polyalcohols in single-chamber microbial fuel cells. Biosensors and Bioelectronics, 24(4):849-854. 5. Chontisa Sukkasema, Shoutao Xu, Sunhwa Park, Piyarat Boonsawang, Hong Liu (2008). Effect of nitrate on the performance of single chamber air cathode microbial fuel cells. Water research, 42:4743-4750. 6. Rebecca Schaller, Yanzhen. Fan, Shoutao Xu, Alan Fern, Frank. Chaplen, Hong Liu, and Jun Jiao. (2009) Vertically Aligned Multi-walled Carbon Nanotube Decorated Anodes for Microbial Fuel Cells. Proceedings of Materials Research Society 2009, 1170: R05-13.