Geomicrobiology: Difference between revisions
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[http://www.sciencedirect.com/science?_ob=ArticleURL&_udi=B6VBT-49R0V00-7&_user=10&_rdoc=1&_fmt=&_orig=search&_sort=d&view=c&_acct=C000050221&_version=1&_urlVersion=0&_userid=10&md5=b2b8c13eb5098d4cc425947335b64b09] | [http://www.sciencedirect.com/science?_ob=ArticleURL&_udi=B6VBT-49R0V00-7&_user=10&_rdoc=1&_fmt=&_orig=search&_sort=d&view=c&_acct=C000050221&_version=1&_urlVersion=0&_userid=10&md5=b2b8c13eb5098d4cc425947335b64b09] | ||
Gonzalez-Toril, E., Gomez, F.,Rodriquez, N., Fernandez, D., Zuluaga, J., Marin, I., and Amils, R. "Geomicrobiology of the Tinto River, a model of interest for biohydrometallurgy". ''Hydrometalluragy''. 71:301-309. | Gonzalez-Toril, E., Gomez, F.,Rodriquez, N., Fernandez, D., Zuluaga, J., Marin, I., and Amils, R. "Geomicrobiology of the Tinto River, a model of interest for biohydrometallurgy". ''Hydrometalluragy''. 71:301-309. | ||
Delgado, G. Delgado, R., Parraga, J., Rivadeneyra, M. A., Aranda, V. 2008. Precipitation of Carbonates and Phosphates by Bacteria in Extract Solutions from a Semi-arid Saline Soil. Influence of Ca2+ and Mg2+ Concentrat ions and Mg2+/Ca2+ Molar Ratio in Biomineralization. Geomicro. J. 25:1–13. | |||
Herrera, A., Cockell, C. S., Self, S., Blaxter, M., Reitner, J., Arp, G., Drose, W., Thorsteinsson, T. , Tindle, A. G.2008. Bacterial Colonization and Weathering of Terrestrial Obsidian in Iceland. Geomicro. J. 25: 25-37. | |||
Engelen, B., Ziegelmuller, K., Wolf, L., Kopke, B., Gittel, A., Cypionka, H., Treude, T., Nakagawa, S., Inahaki, F., Lever, M. A., Steinsbu, B. O. 2008. Fluids from the Oceanic Crust Support Microbial Activities within the Deep Biosphere. Geomicro. J. 25:56-66. | |||
Fomina, M., Podgorsky, V. S., Olishevska, V., Kadoshnikov, V. M., Pisanska, I. R., Hillier, S., Gadd, G. M. 2007. Fungal Deterioration of Barrier Concrete used in Nuclear Waste Disposal. Geomicro. J. 24:643-653. | |||
Edited by student of [mailto:kmscow@ucdavis.edu Kate Scow] | Edited by student of [mailto:kmscow@ucdavis.edu Kate Scow] |
Revision as of 02:56, 10 March 2008
Introduction
Welcome to the world of GEOMICROBIOLOGY!
In a nutshell, geomicrobiology includes microbes that "eat rocks". A more precise definition is "a subset of the scientific discipline microbiology. The field of geomicrobiology concerns the role of microbe and microbial processes in geological and geochemical processes. The field is especially important when dealing with microorganisms in aquifers and public drinking water supplies." (Wikipedia, 2008.)
This page will discuss a broad introduction to what geomicrobiological processes are all about, key microorganisms found in geomicrobiology, examples of such microbes, and current research in this field.
Enjoy your visit!
Process - key points
Geomicrobiological processes are relevant in many natural environments including aquifers, geological and geochemical processes, extreme environments (acidic, extreme temperatures and saline conditions) and metal ion reduction. Some of the most important processes include: 1- Weathering 2- Precipitation of carbonates and phosphates 3- Ocean crust support 4- Nuclear waste disposal 5- Hot springs
Weathering
Weathering plays an important role on Earth ecosystems and is important for the release of nutrients into the biosphere as a result of rock dissolution or the regulation of long-term climate by the consumption of atmospheric carbon dioxide from silicate alterations. Weathering has been considered a strictly physical and chemical process. Nonetheless, many weathering processes can be affected by the presence of microbial communities. All types of rocks are susceptible to microbial weathering, including siliceous and calcareous rocks. In general microbial weathering is due to the formation of organic acids or the production of metal-chelating siderophores on the surface of rock or minerals. Other processes include oxidative or reductive conditions of metals on rocks or minerals (Herrera et al., 2008). Additional information can be found in the following link: [1]
Precipitation of carbonates and phosphates
The influence of Bacteria in mineral precipitation has been described in different natural habitats including aquatic environments and geological systems. Carbonate precipitation is controlled by bacteria processes and one of the mechanisms proposed is the production of ammonium by metabolizing nitrogen base organic compounds which increases environment pH. Other authors report that the matrix of extracellular polymeric secretions (EPS) affects mineral precipitation Simultaneous precipitation of struvite (MgNH4PO4•6H2O) associated with bacterial activity has been described in vitro carbonate precipitation experiments as well as carbonate and phosphate precipitation by bacteria from saline soils (Delgado et al., 2008). Additional information can be found in the following link: [2]
Ocean crust support
Microbiological studies on sediment cores collected by the Deep Sea Drilling Program (DSDP) and the Ocean Drilling Program (ODP) have demonstrated the presence of microbial communities in deeply buried marine sediments. Prokaryotes in the marine sub-seafloor biosphere have been estimated to comprise one-tenth to one-third of the world’s living biomass and therefore probably play an important role in global biogeochemical processes. Microbial populations in these regions vary considerably as a result of sediment type and age, organic matter availability, temperature and sedimentation rate. An example of the processes involved in this type of ecosystems was proposed for the Juan de Fuca Ridge in the northeast pacific and can be found below (Engelen et al., 2008). Additional information can be found in the following link: [3]
Nuclear waste disposal
Fungi can be very radiation-resistant and can survive and colonize concrete barriers under severe radioactive contamination. After then years of the catastrophe of Chernobyl in 1986 extensive fungal growth was observed on the walls and other building structures constructed in the inner part of the “Shelter” built over the fourth Unit of the Chernobyl nuclear power plant. Safe long-term storage of both existing and future nuclear wastes is of vital importance in protecting the environment, therefore the study of these fungi has been key for future construction of nuclear waste repositories. The deterioration of concrete by fungi is performed by common mechanisms used by fungi for rock and mineral weathering. Some of the microorganisms isolated from these extreme environments include modified strains from the genera Alternaria, Cladosporium, and Aureobasidium (Fomina et al., 2007). Additional information can be found in the following link:[4]
Geobiology habitats
Geomicrobes can be found in the most extreme environments, examples of which are, the deep sea, and hydrothermal vents. The conditions under which these microbes can live is very diverse, ranging from high and low temperature and high to low pH.
Microbial Energetics
The Big Picture: a nice summary of microbial metabolism can be found at: [5].
An important part of microbial metabolism is microbial energenetics. Microbial energenetics are driven by Gibbs free-energy yield derived from ATP. ATP is heterotrophically generated by fermentation or respiration. The latter requires terminal electron acceptors (e.g. molecular oxygen, nitrate, sulphate, ferric iron, carbon dioxide, or molecular hydrogen), and produces greater amounts of ATP per unit substrate. Fermentation is less feasible in the presence of either highly oxidised or highly reduced substrate, and may rise toxic products (simple organic acids) that can eventually impede the process. The energy in soil is preserved in both organic and inorganic components enabling the microbial communities to sustain catabolic and anabolic processes.
Geobiology method
We need to measure redox potential, PH, temperature and available electron donor and acceptor. Microbe foam a consortium so we need pure isolate method. Phase contrast, DIC, Epiflorsentce FISH MPN
Key Microorganisms within Geomicrobiology
Geomicrobiology included organisms that are concidered extremophiles. Extremophiles are microorganisms that live in areas considered too hostile for most. An example of an extremophile is anerobic sulfate reducing bacteria, which are know to live in hyper-saline lagoons in Brazil and Australia. It is believed these bacteria may be responsible for the formation of dolmite
Examples of Microorganisms
An example of extemophile organism is: anaerobic sulfate-reducing bacteria
Sulfate-reducing bacteria (SRB) comprise of several groups of bacteria that use sulfate as an oxidizing agent, reducing it to sulfide. Most sulfate-reducing bacteria can also use other oxidized sulfur compounds such as sulfite and thiosulfate, or elemental sulfur. This type of metabolism is called dissimilatory, since sulfur is not incorporated - assimilated - into any organic compounds. Sulfate-reducing bacteria have been considered as a possible way to deal with acid mine waters that are produced by other bacteria.
Another interested description of SRB is found at: [6].
Acidithiobacillus is a genus of proteobacteria. The members of this genus used to belong to Thiobacillus, before they were reclassified in the year 2000. Members of this genus can be fined in pyrite deposits, metabolizing iron and sulfur and producing sulfuric acid.
Example: Acidithiobacillus thiooxidans consumes sulfur and produces sulfuric acid. This bacterium in conjunction with others of the same genus is currently used in a mining technique called bioleaching whereby metals are extracted from their ores through oxidation. The bacteria are used as catalysts.
Hydrogenophilaceae also belongs to the Proteobacteria, and it is believed to be made of two genera. They are thermophilic bacterium growing in temperatures close to 50 °C. They obtain their energy from hydrogen oxidation. Example: Thiobacillus genus; includes only species from beta proteobacteria. This bacterium is used as a pest control in potato fields to control scabs.
Bacillus sp. strain SG-1 and Pseudomonas putida are common soil and freshwater Mn(II)-oxidizing bacterium. Mn(II)-oxidizing bacteria are a diverse group found in almost all environments. These bacteria are up to 5 orders of magnitude faster than abiotic reactions in the production of Mn oxides which have an amorphous structure with a high surface area. Mn(II) oxides are the only known oxidants of Cr(III) in the environment. The mechanism of Mn(II) oxidation by these bacteria is not clear, although recent outcomes from studies with Bacillus sp. strain SG-1 have shown that a Mn(III) is an intermediate in the final oxidation of Mn(II) through enzymatic activity. For more information on this group of bacterium look at the reference from Karen et al., 2007
The Epsilon-proteobacteria have recently been recognized as globally ubiquitous in marine and terrestrial ecosystems. They play a major role in biogeochemical and geological processes and have been isolated from sulfur rich terrestrial and marine environments, some of which are considered extreme habitats. Most representatives are only known through the 16S rRNA gene sequence despite current effort to develop culture techniques. For more information of this bacterium look at the reference from Campbell et al., 2006.
Current Research and Links
There is a very intresting site hosted by the Geomicrobiology & Environmental Microbiology Studies at Louisiana State University [7] This site is filled with current research photos and informative discussions concerning the topic.
Geomicrobiology of the Tinto River, a model of interest for biohydrometallurgy Researchers have been using molecular and non molecular techniques to study the microbial ecology in the Tinto river (Southwestern Spain). The acidic conditions of the river (average pH 2.3) make it an example of an extreme environment. Researchers have found while sulfur does play a role in the rivers acidity Iron is the key element. Within the river Iron acts both as an substrate for oxidizing bacteria and as an electron acceptor in the anoxic areas of the river. Isotopic dating has concluded the rivers conditions have evolved from natural phenomena and are not the results of manmade pollutants. [8]
References
Murray, K. J., Tebo, B. M. 2007. Cr(III) Is Indirectly Oxidized by the Mn(II)-Oxidizing Bacterium Bacillus sp. Strain SG-1 Environ. Science Technology. 41: 528-533.
Campbell, B.J., Engel, A.S., Porter, M.L., and Takai, K. (2006) The versatile Epsilonproteobacteria: Key players in sulphidic habitats. Nature Reviews Microbiology. 4: 458-468.
Gonzalez-Toril, E., Gomez, F.,Rodriquez, N., Fernandez, D., Zuluaga, J., Marin, I., and Amils, R. "Geomicrobiology of the Tinto River, a model of interest for biohydrometallurgy". Hydrometalluragy. 71:301-309.
Delgado, G. Delgado, R., Parraga, J., Rivadeneyra, M. A., Aranda, V. 2008. Precipitation of Carbonates and Phosphates by Bacteria in Extract Solutions from a Semi-arid Saline Soil. Influence of Ca2+ and Mg2+ Concentrat ions and Mg2+/Ca2+ Molar Ratio in Biomineralization. Geomicro. J. 25:1–13.
Herrera, A., Cockell, C. S., Self, S., Blaxter, M., Reitner, J., Arp, G., Drose, W., Thorsteinsson, T. , Tindle, A. G.2008. Bacterial Colonization and Weathering of Terrestrial Obsidian in Iceland. Geomicro. J. 25: 25-37.
Engelen, B., Ziegelmuller, K., Wolf, L., Kopke, B., Gittel, A., Cypionka, H., Treude, T., Nakagawa, S., Inahaki, F., Lever, M. A., Steinsbu, B. O. 2008. Fluids from the Oceanic Crust Support Microbial Activities within the Deep Biosphere. Geomicro. J. 25:56-66.
Fomina, M., Podgorsky, V. S., Olishevska, V., Kadoshnikov, V. M., Pisanska, I. R., Hillier, S., Gadd, G. M. 2007. Fungal Deterioration of Barrier Concrete used in Nuclear Waste Disposal. Geomicro. J. 24:643-653.
Edited by student of Kate Scow