Electron current is inherent to microbial metabolism. Microorganisms transfer electrons from an electron donor (lower potential species) to an electron acceptor (higher potential species). If the electron acceptor is an external ion or molecule, the process is called respiration. If the process is internal, electron transfer is called fermentation. The microorganism attempts to maximize their energy gain by selecting the electron acceptor with the highest potential available. In nature, mainly minerals containing iron or manganese oxides are reduced. Often soluble electron acceptors are depleted in the microbial environment. The microorganism can also maximize their energy by selecting a good electron donor that can be easily metabolized. These processes are done by extracellular electron transfer (EET).[5] The theoretical free energy change (ΔG) for microorganisms relates directly to the potential difference between the electron acceptor and the donor. However, inefficiencies like internal resistance will decrease this free energy change.[6] The advantage of these devices is their high selectivity in high speed processes limited by kinetic factors.
On March 25, 2013, scientists at the University of East Anglia were able to transfer electrical charge by allowing bacteria to touch a metal or mineral surface. The research shows that it is possible to 'tether' bacteria directly to electrodes.[10]
History
In 1911 M. Potter described how microbial conversions could create reducing power, and thus electric current. Twenty years later Cohen (1931) investigated the capacity of bacteria to produce an electrical flow and he noted that the main limitation is the small capacity of current generation in microorganisms. Berk and Canfield (1964) didn't build the first microbial fuel cell (MFC) until the 60's.
Currently, the investigation of bioelectrochemical reactors is increasing. These devices have real applications in fields like water treatment,[11] energy production and storage, resources production, recycling and recovery.
Applications
Water Treatment
Bioelectrochemical reactors are finding an application in wastewater treatment settings. Current activated sludge processes are energy- and cost-inefficient due to sludge maintenance, aeration needs, and energy needs. By using a bioelectrochemical reactor that utilizes the concept of trickling filtering, these inefficiencies can be addressed.[12] While processing wastewater using this reactor, nitrification, denitrification, and organic matter removal all take place simultaneously in both aerobic and anaerobic conditions using multiple different microbes located on the anode of the system. Though the processing parameters of the reactor affect the overall composition of each microbe, genus Geobacter and genus Desulfuromonas are frequently found in these applications.[12]
^Krieg T, Sydow A, Schröder U, Schrader J, Holtmann D (December 2014). "Reactor concepts for bioelectrochemical syntheses and energy conversion". Trends in Biotechnology. 32 (12): 645–55. doi:10.1016/j.tibtech.2014.10.004. PMID25457389.
^Rabaey K, Angenent L, Schroder U, Keller J, eds. (2010). Bioelectrochemical systems : from extracellular electron transfer to biotechnological application. London: IWA Publishing. ISBN978-1-84339-233-0.
^Rabaey K, Angenent L, Schroder U, Keller J, eds. (2010). Bioelectrochemical systems : from extracellular electron transfer to biotechnological application. London: IWA Publishing. ISBN978-1-84339-233-0.
^Krieg T, Sydow A, Schröder U, Schrader J, Holtmann D (December 2014). "Reactor concepts for bioelectrochemical syntheses and energy conversion". Trends in Biotechnology. 32 (12): 645–55. doi:10.1016/j.tibtech.2014.10.004. PMID25457389.
^Liang Q, Yamashita T, Koike K, Matsuura N, Honda R, Hara-Yamamura H, et al. (November 2020). "A bioelectrochemical-system-based trickling filter reactor for wastewater treatment". Bioresource Technology. 315: 123798. doi:10.1016/j.biortech.2020.123798. PMID32707501. S2CID225536351.
^Liang Q, Yamashita T, Koike K, Matsuura N, Honda R, Hara-Yamamura H, et al. (November 2020). "A bioelectrochemical-system-based trickling filter reactor for wastewater treatment". Bioresource Technology. 315: 123798. doi:10.1016/j.biortech.2020.123798. PMID32707501. S2CID225536351.
^ abLiang Q, Yamashita T, Koike K, Matsuura N, Honda R, Hara-Yamamura H, et al. (November 2020). "A bioelectrochemical-system-based trickling filter reactor for wastewater treatment". Bioresource Technology. 315: 123798. doi:10.1016/j.biortech.2020.123798. PMID32707501. S2CID225536351.
External links
Sasaki K, Morita M, Sasaki D, Hirano S, Matsumoto N, Ohmura N, Igarashi Y (January 2011). "Methanogenic communities on the electrodes of bioelectrochemical reactors without membranes". Journal of Bioscience and Bioengineering. 111 (1): 47–9. doi:10.1016/j.jbiosc.2010.08.010. PMID20840887.
Ghafari S, Hasan M, Aroua MK (2009). "Nitrate remediation in a novel upflow bio-electrochemical reactor (UBER) using palm shell activated carbon as cathode material". Electrochimica Acta. 54 (17): 4164–71. doi:10.1016/j.electacta.2009.02.062.
Goel RK, Flora JR (2005). "Sequential Nitrification and Denitrification in a Divided Cell Attached Growth Bioelectrochemical Reactor". Environmental Engineering Science. 22 (4): 440–9. doi:10.1089/ees.2005.22.440.
Watanabe T, Jin HW, Cho KJ, Kuroda M (2004). "Application of a bio-electrochemical reactor process to direct treatment of metal pickling wastewater containing heavy metals and high strength nitrate". Water Science and Technology. 50 (8): 111–8. doi:10.2166/wst.2004.0501. PMID15566194.