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Applications
editGeobacter's ability to consume oil-based pollutants and radioactive material with carbon dioxide as waste byproduct has been used in environmental clean-up for underground petroleum spills and for the precipitation of uranium out of groundwater. Geobacter metabolize the material by creating electrically conductive pili between itself and the food material.
Multiple Geobacter species cooperate in metabolizing a mixture of chemicals that neither could process alone. Provided with ethanol and sodium fumarate, G. metallireducens broke down the ethanol, generating an excess of electrons that were passed to G. sulfurreducens via "nanowires" grown between them, enabling G. sulfurreducens to break down the fumarate ions. The nanowires are made of proteins with metal-like conductivity.
Microgravity
editGeobacter has been tested in microgravity and this does not make a substantial difference.
Biodegradation and bioremediation
editMicrobial biodegradation of recalcitrant organic pollutants is of great environmental significance and involves intriguing novel biochemical reactions. In particular, hydrocarbons and halogenated compounds have long been doubted to be anaerobically degradable, but the isolation of hitherto unknown anaerobic hydrocarbon-degrading and reductively dehalogenating bacteria documented these processes in nature. Novel biochemical reactions were discovered, enabling the respective metabolic pathways, but progress in the molecular understanding of these bacteria was slowed by the absence of genetic systems for most of them. However, several complete genome sequences later became available for such bacteria. The genome of the hydrocarbon degrading and iron-reducing species G. metallireducens (accession nr. NC_007517) was determined in 2008. The genome revealed the presence of genes for reductive dehalogenases, suggesting a wide dehalogenating spectrum. Moreover, genome sequences provided insights into the evolution of reductive dehalogenation and differing strategies for niche adaptation.
Geobacter species are often the predominant organisms when extracellular electron transfer is an important bioremediation process in subsurface environments. Therefore, a systems biology approach to understanding and optimizing bioremediation with Geobacter species has been initiated with the ultimate goal of developing in silico models that can predict the growth and metabolism of Geobacter species under a diversity of subsurface conditions. The genomes of multiple Geobacter species have been sequenced. Detailed functional genomic/physiological studies on one species, G. sulfurreducens was conducted. Genome-based models of several Geobacter species that are able to predict physiological responses under different environmental conditions are available. Quantitative analysis of gene transcript levels during in situ uranium bioremediation demonstrated that it is possible to track in situ rates of metabolism and the in situ metabolic state of Geobacter in the subsurface.
Applications
editGeobacter's ability to consume oil-based pollutants and radioactive material with carbon dioxide as waste byproduct has been used in environmental clean-up for underground petroleum spills and for the precipitation of uranium out of groundwater. Geobacter metabolize the material by creating electrically conductive pili between itself and the food material.
Multiple Geobacter species cooperate in metabolizing a mixture of chemicals that neither could process alone. Provided with ethanol and sodium fumarate, G. metallireducens broke down the ethanol, generating an excess of electrons that were passed to G. sulfurreducens via "nanowires" grown between them, enabling G. sulfurreducens to break down the fumarate ions. The nanowires are made of proteins with metal-like conductivity.
Biofilm Conductivity
editMany Geobacter species, such as G. sulfureducens, are capable of creating thick networks of biofilms on microbial fuel cell anodes for extracellular electron transfer. Cytochromes within the biofilm accept electrons from the microorganisms as well as from other reduced cytochromes present in the biofilm. Electric currents are produced when the transfer of these electrons to anodes is coupled to the oxidation of intracellular organic wastes.[1] Previous research has proposed that the high conductivity of Geobacter biofilms can be used to power microbial fuel cells and to generate electricity from organic waste products.[2] In particular, G. sulfureducens holds one of the highest records for microbial fuel cell current density that researchers have ever been able to measure in vitro.[3]
Many researchers are currently studying how we can utilize biofilm conductivity to our advantage to produce even higher current densities. Low pH environments change redox potentials, thus inhibiting electron transfer from microorganisms to cytochromes.[1] However, the presence of pili or flagella on Geobacter increases electric current generation by enabling electron transfer to be more efficient.[4] These different factors can be tweaked to produce maximum electricity and to optimize bioremediation.
Biodegradation and bioremediation
editMicrobial biodegradation of recalcitrant organic pollutants is of great environmental significance and involves intriguing novel biochemical reactions. In particular, hydrocarbons and halogenated compounds have long been doubted to be anaerobically degradable, but the isolation of hitherto unknown anaerobic hydrocarbon-degrading and reductively dehalogenating bacteria documented these processes in nature. Novel biochemical reactions were discovered, enabling the respective metabolic pathways, but progress in the molecular understanding of these bacteria was slowed by the absence of genetic systems for most of them. However, several complete genome sequences later became available for such bacteria. The genome of the hydrocarbon degrading and iron-reducing species G. metallireducens (accession nr. NC_007517) was determined in 2008. The genome revealed the presence of genes for reductive dehalogenases, suggesting a wide dehalogenating spectrum. Moreover, genome sequences provided insights into the evolution of reductive dehalogenation and differing strategies for niche adaptation.
Geobacter species are often the predominant organisms when extracellular electron transfer is an important bioremediation process in subsurface environments. Therefore, a systems biology approach to understanding and optimizing bioremediation with Geobacter species has been initiated with the ultimate goal of developing in silico models that can predict the growth and metabolism of Geobacter species under a diversity of subsurface conditions. The genomes of multiple Geobacter species have been sequenced. Detailed functional genomic/physiological studies on one species, G. sulfurreducens was conducted. Genome-based models of several Geobacter species that are able to predict physiological responses under different environmental conditions are available. Quantitative analysis of gene transcript levels during in situ uranium bioremediation demonstrated that it is possible to track in situ rates of metabolism and the in situ metabolic state of Geobacter in the subsurface.
Applications
editGeobacter's ability to consume oil-based pollutants and radioactive material with carbon dioxide as waste byproduct has been used in environmental clean-up for underground petroleum spills and for the precipitation of uranium out of groundwater. Geobacter metabolize the material by creating electrically conductive pili between itself and the food material.
Multiple Geobacter species cooperate in metabolizing a mixture of chemicals that neither could process alone. Provided with ethanol and sodium fumarate, G. metallireducens broke down the ethanol, generating an excess of electrons that were passed to G. sulfurreducens via "nanowires" grown between them, enabling G. sulfurreducens to break down the fumarate ions. The nanowires are made of proteins with metal-like conductivity.
Biodegradation and Bioremediation
editMicrobial biodegradation of recalcitrant organic pollutants is of great environmental significance and involves intriguing novel biochemical reactions. In particular, hydrocarbons and halogenated compounds have long been doubted to be anaerobically degradable, but the isolation of hitherto unknown anaerobic hydrocarbon-degrading and reductively dehalogenating bacteria documented these processes in nature. Novel biochemical reactions were discovered, enabling the respective metabolic pathways, but progress in the molecular understanding of these bacteria was slowed by the absence of genetic systems for most of them. However, several complete genome sequences later became available for such bacteria. The genome of the hydrocarbon degrading and iron-reducing species G. metallireducens (accession nr. NC_007517) was determined in 2008. The genome revealed the presence of genes for reductive dehalogenases, suggesting a wide dehalogenating spectrum. Moreover, genome sequences provided insights into the evolution of reductive dehalogenation and differing strategies for niche adaptation.
Geobacter species are often the predominant organisms when extracellular electron transfer is an important bioremediation process in subsurface environments. Therefore, a systems biology approach to understanding and optimizing bioremediation with Geobacter species has been initiated with the ultimate goal of developing in silico models that can predict the growth and metabolism of Geobacter species under a diversity of subsurface conditions. The genomes of multiple Geobacter species have been sequenced. Detailed functional genomic/physiological studies on one species, G. sulfurreducens was conducted. Genome-based models of several Geobacter species that are able to predict physiological responses under different environmental conditions are available. Quantitative analysis of gene transcript levels during in situ uranium bioremediation demonstrated that it is possible to track in situ rates of metabolism and the in situ metabolic state of Geobacter in the subsurface.
Biofilm Conductivity
editMany Geobacter species, such as G. sulfureducens, are capable of creating thick networks of biofilms on microbial fuel cell anodes for extracellular electron transfer.[5] Cytochromes within the biofilm associate with pili to form extracellular structures called nanowires, which facilitate extracellular electron transfer throughout the biofilm.[1] These cytochromes accept electrons from the microorganisms as well as from other reduced cytochromes present in the biofilm.[1]
Electric currents are produced when the transfer of these electrons to anodes is coupled to the oxidation of intracellular organic wastes.[1] Previous research has proposed that the high conductivity of Geobacter biofilms can be used to power microbial fuel cells and to generate electricity from organic waste products.[2][3] In particular, G. sulfureducens holds one of the highest records for microbial fuel cell current density that researchers have ever been able to measure in vitro.[3] This ability can be attributed to biofilm conductivity, as highly conductive biofilms have been found to be positively correlated with high current densities in microbial fuel cells.[2]
At the moment, the development of microbial fuel cells for power generation purposes is partly restricted by its inefficiency compared to other sources of power and an insufficient understanding of extracellular electron transfer.[6] As such, many researchers are currently studying how we can utilize biofilm conductivity to our advantage to produce even higher current densities. Low pH environments have been found to change redox potentials, thus inhibiting electron transfer from microorganisms to cytochromes.[1] In addition, biofilms have been found to become less conductive with decreasing temperature, although raising the temperature back up again can restore biofilm conductivity without any adverse effects.[7] The presence of pili or flagella on Geobacter species has been found to increase electric current generation by enabling more efficient electron transfer.[4] These different factors can be tweaked to produce maximum electricity and to optimize bioremediation in the future.[6]
Veenalin (talk) 01:58, 20 November 2017 (UTC)
- ^ a b c d e f Bond, Daniel R.; Strycharz-Glaven, Sarah M.; Tender, Leonard M.; Torres, César I. (21 May 2012). "On Electron Transport through Geobacter Biofilms". ChemSusChem. 5 (6). doi:10.1002/cssc.201100748.
- ^ a b c Malvankar, Nikhil S.; Tuominen, Mark T.; Lovley, Derek R. (25 January 2012). "Biofilm conductivity is a decisive variable for high-current-density Geobacter sulfurreducens microbial fuel cells". Energy & Environmental Science. 5 (2). doi:10.1039/C2EE03388G. ISSN 1754-5706.
- ^ a b c Yi, Hana; Nevin, Kelly P.; Kim, Byoung-Chan; Franks, Ashely E.; Klimes, Anna; Tender, Leonard M.; Lovley, Derek R. (15 August 2009). "Selection of a variant of Geobacter sulfurreducens with enhanced capacity for current production in microbial fuel cells". Biosensors & Bioelectronics. 24 (12). doi:10.1016/j.bios.2009.05.004. ISSN 1873-4235.
- ^ a b Reguera, Gemma; Nevin, Kelly P.; Nicoll, Julie S.; Covalla, Sean F.; Woodard, Trevor L.; Lovley, Derek R. (1 November 2006). "Biofilm and Nanowire Production Leads to Increased Current in Geobacter sulfurreducens Fuel Cells". Applied and Environmental Microbiology. 72 (11). doi:10.1128/AEM.01444-06. ISSN 0099-2240.
- ^ Yates, Matthew D.; Strycharz-Glaven, Sarah M.; Golden, Joel P.; Roy, Jared; Tsoi, Stanislav; Erickson, Jeffrey S.; El-Naggar, Mohamed Y.; Barton, Scott Calabrese; Tender, Leonard M. (2016-11-08). "Measuring conductivity of living Geobacter sulfurreducens biofilms". Nature Nanotechnology. 11 (11): 910–913. doi:10.1038/nnano.2016.186. ISSN 1748-3395.
- ^ a b Logan, Bruce E. (2009-03-30). "Exoelectrogenic bacteria that power microbial fuel cells". Nature Reviews Microbiology. 7 (5): 375–381. doi:10.1038/nrmicro2113. ISSN 1740-1534.
- ^ Yates, Matthew D.; Golden, Joel P.; Roy, Jared; Strycharz-Glaven, Sarah M.; Tsoi, Stanislav; Erickson, Jeffrey S.; El-Naggar, Mohamed Y.; Barton, Scott Calabrese; Tender, Leonard M. (2015-12-02). "Thermally activated long range electron transport in living biofilms". Physical Chemistry Chemical Physics. 17 (48): 32564–32570. doi:10.1039/c5cp05152e. ISSN 1463-9084.