Difference between revisions of "Flooded Soils"

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==Process ==
==Process ==
[[Image:phenomenon in aggregates.png|thumb|200px|schematic presentation of flooded soil adjusted from [[Prof. Kate lec #5]]]]
[[Image:phenomenon in aggregates.png|thumb|left|200px|Electron acceptor used in aggregates. adjusted from [[Prof. Kate lec #5]]]]
[[Image:phenomena in pollutant plume.png|thumb|200px|Order of electron acceptor in pollutant plume from [[USGA]]]]
[[Image:phenomena in pollutant plume.png|thumb|200px|Order of electron acceptor in pollutant plume from [[USGA]]]]
In general, flooded soil condition occurs due to seasonal flooding or agricultural activity.  
In general, flooded soil condition occurs due to seasonal flooding or agricultural activity.  

Revision as of 20:30, 9 March 2008


schematic presentation of flooded soil fromY.Chen and Y Avnimelech

When the pore spaces in soils are saturated with water, oxygen dissolved in water is gradually depleted because oxygen is used as terminal electron acceptor for respiration by some aerobes and the facultative anaerobes. This results in anaerobic condition of soils. This anoxic condition can be found in soil aggregates and pollutants plume. Under anoxic condition, some microbes can use alternative electron acceptors such as nitrate, ferric, manganese (IV) oxide, sulfate, and carbon dioxide. Anaerobic reduction processes do not occure simultaneously, but one after another according to presence of appropriate electron aceptors as well as the cometitive electron acceptors.


Electron acceptor used in aggregates. adjusted from Prof. Kate lec #5
Order of electron acceptor in pollutant plume from USGA

In general, flooded soil condition occurs due to seasonal flooding or agricultural activity. The flooded soils condition can be often converted into non-flooded soil condition by the water level fluctuation and drainage. Through this variation of soil condition, various gases are emitted into the atmosphere or environmental factors, such as redox potential (Eh), pH, acidity, alkalinity, and salinity, are continuously changed. As explained in the introduction, microorganism can use alternative terminal electron acceptor when dissolved oxygen is absent. They successively use electron acceptor according to the order of electron acceptor utilization based on electron tower. The order change of electron acceptor utilization is observed in soil aggregates and pollutant plume. (Figure aggregates and pollutant plume)

Oxidation/reduction (redox) reaction

Electron tower

Electron tower theory explains the utilization order of electron acceptor for respiration. Depending on the type of electron acceptors used by microorganisms, microbes can be classified into the strict aerobes, obligate anaerobes, and facultative anaerobes. The strict aerobes can not live under anoxic condition; on the contrary, obligate anaerobes can never use oxygen as electron acceptor. However, facultative anaerobes can live in both aerobic and anaerobic condition. If oxygen is plentiful, they tend to use oxygen because microorganisms gain much energy from reducing oxygen rather than other electron acceptors. When there is no more available oxygen in solution, they start to use nitrate as electron acceptor. Thus, obligate anaerobes and facultative anaerobes use alternative electron acceptor in the order of electron acceptor having more reducing energy. Oxygen is most efficient electron acceptor, while carbon dioxide has the less reducing energy.

Variation of pH and Eh


Neutral pH soil

When soil is saturated with water, pH drops at first due to organic acid produced from fermentation. Then, pH gradually starts to rise because H+ is consumed via respiration of the aerobes and anaerobes. The half reactions of hydrogen consumption are as follow;

Aerobic respiration: ½ O2 + 2e- + 2H+ -> H2O (by facultative anaerobe and aerobes)

Iron reduction: Fe(OH)3 + 3 H+ + 2e- -> Fe2+ + 2H2O (by Iron reducing bacteria)

Denitrification: 2NO3- + 12 H+ +10e- -> N2+6H2O (by Denitrifier)

Sulfate reduction: SO42- + 10H+ +8e- -> H2S + 4H2O (by sulfate reducing bacteria)

Methane production: CO2 + 8 H+ + 8e- -> CH4 +2 H2O (by Methanogeous)

Manganese reduction: MnO2 + 4H+ + 2e- ->Mn2+ + 2H2O (by Manganese reducing bacteria)


During the succetion of anaerobic oxidation processes, the redox potential (Eh) of the flooded soil will decrease as a result of the reduced products formed. The approximate redox potential values that indicate the start and end of a specific reduction oxidation process are as follows: (How to make a table??) Observation Eh (mV) Disappearance of oxygen +330 Disappearance of nitrate +220 Appearance of manganese ions +200 Appearance of ferrous ions +120 Disappearance of sulfate -150 Appearance of methane -250

Solubility/mobility of mineral

Since the toxicity, solubility, mobility,and bioavailability of a given element or compounds are mainly influenced by soil solution redox potenial and pH, flooded soil condition plays an important role in mobility of trace metal, nutrients, and mineral.

Effects on life

In flooded conditions microorganisms can no longer use oxygen, or it is severly limited

Plant nutrient availability

Flooded soils can prevent efficient gas exchange between the plant root and the soil. pH plays a main role in a healthy plant growth process. In flooded soils, under anaerobic conditions the pH value wil tend to rise. Denitrification of soil nitrate to nitrogen gas plays a major role in the rise of pH levels. Flooding results in poor soil aeration because the supply of oxygen to flooded soil is severely limited. Oxygen deficiency is likely the most important environmental factor that triggers growth inhibition and injury in flooded plants

Microorganism activity

In anaerobic respiration oxygen is replaced by other compounds as TEA (terminal electron acceptors). Iron is reduced from Fe3+ to Fe2+ during iron repiration. Manganese is also reduced. These processes occur because of microoganism activity. Energy yields are lower than for aerobic respiration.(1)

Key Microorganisms & exchanges of gases

The role of microorganisms under flooded soil

nitrate reducing bacteria

Denitrification is carried out by obligate respiratory bacteria belonging to the genra Agrobactterium, Alcaligenes, Bacillus, Paracoccus, Pesudomonas and Thiobacillus (Knowles, 1982). Nitrate ammonification found in facultative anaerobe bacteria belonging to the genera Bacillus, Citrobacter and Aeromonas, or in the memebers of the Enterobacteriaceae (Cole adn Brown, 1980; Smith adn Zimmerman, 1981; MacFarlane and Herbert, 1982). Strictly anaerobic bacteria belonging to the genus Clostridium are also able to reduce nitrate to ammonia (Hasan and Hall, 1975). Pure culture studies show evidance that nitrate reduction does occure in presence of oxygen (Kuenen and and Robertson, 1987).

Methaneous bacteria

Methanogen (e.g Methanobacterium formicum, Methanobacterium bryantii, Methanobacterium thermo-autrotrophicum, and etc ) can use CO2 and produce methane (Langston and Bebiano 1998)

Iron reducing bacteria

Ferrous iron is used as electron acceptor by iron-reducing bacteria such as G. metallireducens, G. sulfurreducens, and Shewanella putrefaciens.Different forms of ferric oxides exist in aaerobic drained as well as in waterlogged soils. Not all of these ferric oxides are equally suitable for reduction by ferric oxide reducer bacteria (Gotoh and Patrick, 1974; Schwertmann and Taylor, 1977). In general, amorphous forms are more efficient for ferric reducer bacteria than crystalline forms (Lovely adn Phillips, 1986). The reduction of ferric oxide may release phosphate and trace elements that are adsorbed to the amorphous ferric oxide and thus enhance availablity of these compounds in the soil (Lovely and Phillips, 1986).

Sulfate reducing bacteria

Bacteria can use acetate as electron donor and sulfate as electron acceptor. This reaction is as follow;

CH3COO- + SO42- + 3 H+ ---> 2CO2 + H2S + 2 H2O

This reaction is carried out by sulfate-reducing bacteria such as Desulfobacterales, Desulfovibrionales, and Syntrophobacterales (Langston and Bebiano 1998). Hydrogen sulfide gas produced via anaerobic respiration cause the rotten egg odor.

Manganese reducing bacteria

Current Research

Green house gases(nitrous oxides, methane, carbon dioxide ) emission from flooded soil(rice paddy,riverine, estuarine, and lacustrine sediments)


(1) Kate Scow lecture 5

x Appl Environ Microbiol, June 1998, p. 2181-2186, Vol. 64, No. 6 http://aem.asm.org/cgi/content/full/64/6/2181

Edited by students of Kate Scow