The Carbon Cycle affects all life on Earth. Elemental carbon is neither created or destroyed, so the recycling of carbon-containing compounds in the environment is essential to the continuation of life. Recently there has been increased interest in the Carbon Cycle becuase of our awareness of how atmospheric levels of CO2 affect global climate change. Microbes play important roles in all aspects of the Carbon Cycle, and are a very important consideration when analyzing climate change. Many produce CO2 through respiration,and some fix atmospheric carbon, sequestering it in the soil. Some produce methane and nitrous oxide, which are potent greenhouse gasses, while others degrade toxic and environmentally harmful compounds.
The Carbon Cycle
An important step of the carbon cycle is the fixation of atmospheric CO2 and its subsequent assimilation into organic molecules. Organisms that can convert CO2 into organic molecules are called autotrophs, and include plants, algae, some bacteria, and some archaea. Some bacteria specifically involved in carbon fixation are Cyanobacteria (such as Chroococcus, Nostoc, and Spirulina) and some species of Aquifex,such as Aquifex aeolicus. Cyanobacteria are also important Nitrogen fixers in the Nitrogen cycle including GHG
Decomposition of Organic Matter and the Microbes Involved
The major function of microbes in the Carbon Cycle is as decomposers-- degraders of complex organic molecules that would otherwise permanently sequester carbon. These decomposers also release CO2, contributing to the rising concentration in the atmosphere. Each organic compound is utilized in a slightly differently manner, and each yields different products when degraded.
Sugars and Proteins
Plant debris supplies most of the simple sugars and proteins in the soil. All heterotrophic microbes can easily utilize these compounds for both energy metabolism and as carbon sources. Plants link glucose molecules (and other sugar monomers) into long chains to produce polymers such as cellulose and starch, which require more specialized organisms to degrade. For example: alternating alpha 1,4 and beta 1,4 bonds in glucose polysaccarides determine which organisims can break the bonds and utilize the energy in the glucose. Bacteria can frequently be found in mutualistic relationships with detritivores: the bacteria degrades the cellulose to the point that the animal is able to digest it.
Cellulose is a structural polysaccharide that contains glucose. In order to access this glucose for catabolism, the cellulose must be cleaved by extracellular enzymes. These pieces are then transported into the cell for energy generation (catabolism) or production of biomass (anabolism). Fungi such as Penicillium and Aspergillus and bacteria such as Streptomyces and Pseudomonas are important participants in the extracellular cleavage of cellulose.
Hemicellulose is the next most common carbohydrate source in plants. The decomposition of hemicellulose is similar to that of cellulose in that the initial depolymerization step takes place outside of the cell, and the sugars produced are then transported into the cell for catabolism or anabolism. Hemicellulose decomposition is much quicker than cellulose decomposition. In the presence of simple sugars, cells will utilize the sugars as substrates as opposed to hemicellulose.
Chitin is a special compound which can be found in the integument of arthropods and cell wall of fungi. The polymer is not easily degraded,and requires a variety of enzymes to do so. The dominant chitin degraders are the actinomycetes Streptomyces and Nocardia, and (less importantly) fungi such as Trichoderma and Verticillium.
Lignin is the main component of wood in trees. Lignin has a varied, unique, and complicated chemical structure which contain many aromatics. These aromatics can be released from the lignin sturucture by fungal enzymes peroxidase and oxidase. The enzymes utilize H2O2 and OH radicals to break the bonds in the lignin. Common types of fungi which degrade lignin are White rot (Phanerochaete chrysosporium), brown rot, and soft rot. Once the aromatics are released from the original lignin structure they are incorporated in to the metabolic pathway as pyruvate, acetyl CoA, and into the TCA cycle.
The modification and breakdown of lignin by fungi and bacterial enzymes help contribute to the formation of humus.
Aromatics, Aliphatics, and Lipids
Aromatics are compounds released when bonds in lignin are broken by fungal enzymes. The aromatics enter or are incorperated as pyruvate, acetyl CoA, and processed in the TCA cycle,. Aliphatics are non-aromatic organic compounds and are incorporated into the TCA cycle after being converted into acetyl CoA.
Soil Organic Matter
The soil organic matter(SOM)is a complex combination of living organisms, fresh organic residues, actively decomposing material, and stabilized organic matter (otherwise known as humus). Generally, samples contain 50% ore more of carbon are refered as soil organic carbon (SOC).
Where is SOM come from
SOM comes either from plant and crop residues, such as stems, leaves or shoots, or indirectly from animals' manure and sewage.
The "living" part of SOM includes bacteria, fugi and insects; the "nonliving" part of SOM comes from recently dead plant, animal matter, and excreta from soil organisms.
What does Oranic Matter do in the soil
1. Increase soil stablity.
2. Increase soil water reserves.
3. Darken soil color, which help to absorb more heat from the sun.
4. Increase Cation Exchange Capacity (CEC).
5. Increase nutrient supply, especially in N, P, and S.
6. Prevent losing nutrients.
Humus is a combination of many compounds, and is critical in defining many properties of a soil. It increases water and nutrient retention, encourages aggregate formation, and inhibits impaction and caking. Humus is composed mainly of humin, humic acid, and fulvic acid. Two major methods of humus formation are by minor modifications of lignin and by the degradation and reassembly of plant residues (lignin, cellulose, hemicellulose) by fungal extracellular enzymes. Humus is a very stable, long-lived pool of organic matter in the soil (with a turnover rate of 100-500 years), which makes it an effective way to sequester excess carbon.
Benefit of humus in the soil
1. Increase the ability of soil to store water 2. Absorb and deactivate numbers of chemicals such as herbicides added to the soil. 3. Increase the resistant from attacking by microorganisms. 4. Make the soil rich in nutrient. Soil rich in humus are darker in color.
Atmospheric Changes Relating to the Carbon Cycle
Global warming is a result of a greenhouse effect caused by the accumulation of greenhouse gases in the atmosphere. The earth is heated by solar radiation that penetrates the atmosphere and is absorbed by the earth. Some of the enegy is reflected back into the atmosphere. Greenhouse gases prevent the escape of this solar energy, causing increased heating of the earth, a phenomenon known as global warming. The major greenhouse gases are water vapour, nitrous oxide (N2O), carbon dioxide (CO2), methane (CH4), and ozone. Soil microorganisms play a role in the generation of each of these gases.
Water vapor is a naturally occurring greenhouse gas and accounts for the largest percentage of the greenhouse effect, between 36% and 66%.The water vapor content of the atmosphere is expected to increase in response to increase in temperatures. The increased water vapor in turn leads to an increase in the greenhouse effect and thus a further increase in temperature; the increase in temperature leads to still further increase in atmospheric water vapor; and the feedback cycle continues until equilibrium is reached. Thus water vapor acts as a positive feedback to the forcing provided by human-released greenhouse gases such as CO2.
Microorganisms produce N2O by performing aerobic nitrification and anaerobic denitrification. Nitrification is the conversion of ammonia to nitrate. Nitrobacter hamburgensis and Nitrosococcus oceani are examples of nitrifying bacteria. Denitrification is the reduction of nitrate to nitrogen gas, with N2O as a side product. Pseudomonas and Flavobacterium are examples of denitrifying bacteria. For more information on nitrogen transformation visit this page: Nitrogen cycle including GHG
Microorganisms produce CO2 through the decomposition of organic matter. The balance between microbial repiration of CO2 and plant fixation of CO2 is important when considering microbial contribution to the greenhouse effect.
Methane is the end product of anaerobic respiration. This process is called methanogenesis. Microorganisms that produce methane through respiration are called Methanogens. There are two processes by which methanogens produce methane: CO2 reduction and acetate fermentation.
Methanotrophy is the process by which microorganisms utilize methane as a carbon source. Carbon dioxide is a product of the reaction. These microorganisms are called methanotrophs.Methylobacterium
Nitrous oxides not only contribute to the greenhouse effect, but also to acid rain. Acid rain is corrosive, and increases the acidity of surface water and soils.
Professor Joshua Schimel is studying the effect of global warming on the soil organic matter in the Arctic. The increasing temperature could result in increased evolution of CO2 to the atmosphere. On the other hand, plant growth could be fostered by the increased presence of nutrients from soil organic matter, making the Arctic a sink for CO2. The nature of the organic matter present in the Arctic soils will determine the type of environmental feedback. http://www.lifesci.ucsb.edu/eemb/faculty/schimel/research/research.html
The Urban Water Research Center at UC Irvine is conducting research on the effect of stengthened anaerobic degradation of manure on methane generation. http://www.uwrc.uci.edu/research-urban-water/UCI-UWRC-Research-Areas.php
Enter summaries of recent research here--at least three required
Fuhrmann, J.J., Hartel, P.G., Sylvia, D.M., Zuberer, D.A. 2005. Principles and Applications of Soil Microbiology, Second Edition. Prentice Hall, Upper Saddle River, NJ, 346,359,497-501 and 285-287 pp.
http://www.blackwell-synergy.com/doi/abs/10.1046/j.1365-2486.1997.00100.x KEITH SMITH (1997) "The potential for feedback effects induced by global warming on emissions of nitrous oxide by soils" Global Change Biology 3 (4) , 327–338 doi:10.1046/j.1365-2486.1997.00100.x
realclimate.org http://web.archive.org/web/20070624015308/http://www.realclimate.org/index.php?p=142 "Water vapour: feedback or forcing?"
http://www.gfdl.noaa.gov/reference/bibliography/2006/ih0601.pdf Issac M. Held, Brian J. Soden. (2006) "Robust Responses of the Hydrological Cycle to Global Warming " Journal of Climate volume19,issue = 21,pages5686-5699
Edited by student of Kate Scow