Soil organic matter

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Soil organic matter (SOM) is the organic matter component of soil, consisting of plant and animal residues at various stages of decomposition, cells and tissues of soil organisms, and substances synthesized by soil organisms. SOM exerts numerous positive effects on soil physical and chemical properties, as well as the soil’s capacity to provide regulatory ecosystem services.[1] Particularly, the presence of SOM is regarded as being critical for soil function and soil quality.

The positive impacts of SOM result from a number of complex, interactive edaphic factors; a non-exhaustive list of SOM's effects on soil functioning includes improvements related to soil structure, aggregation, water retention, soil biodiversity, absorption and retention of pollutants, buffering capacity, and the cycling and storage of plant nutrients. SOM increases soil fertility by providing cation exchange sites and acting as reserve of plant nutrients, especially nitrogen (N), phosphorus (P), and sulfur (S), along with micronutrients, which are slowly released upon SOM mineralization. As such, there is a significant correlation between SOM content and soil fertility.

SOM also acts the major sink and source of soil carbon (C). Although the C content of SOM is known to vary considerably,[2][3] SOM is typically estimated to contain 58% C, and the terms 'soil organic carbon' (SOC) and SOM are often used interchangeably, with measured SOC content often serving as a proxy for SOM. Soil represents one of the largest C sinks on the planet and plays a major role in the global carbon cycle. Therefore, SOM/SOC dynamics and the capacity of soils to provide the ecosystem service of carbon sequestration through SOM management have received considerable attention in recent years.

The concentration of SOM in soils generally ranges from 1% to 6% of the total topsoil mass for most upland soils. Soils whose upper horizons consist of less than 1% organic matter are mostly limited to desert areas, while the SOM content of soils in low-lying, wet areas can be as high as 90%. Soils containing 12-18% SOC are generally classified as organic soils.[4]

It can be divided into three general pools: living biomass of microorganisms, fresh and partially decomposed residues, and humus: the highly stable (well-decomposed) organic material. Surface litter is generally not included as part of soil organic matter.[5][6]

Sources for soil organic matter[edit]

The primary source of organic matter contained in soil is vegetal. In forest or prairies, as well as agricultural fields, dead plants, trees, shrubs, grasses, are transformed by animals and different kinds of living organisms. This process involves several steps, the firsts being mostly mechanical, and becoming more chemical as it progresses. The small living beings that work on that decomposition chain are themselves part of the soil organic matter, and form a food web of organisms that pray and are prayed.

There are also other animals that consume living vegetal material, whose residues are passed to the soil. The products from the living organisms metabolism are the secondary sources of soil organic matter that also includes the dead corpses of these organisms. Some animals, like earthworms, ants, centipedes contribute to the horizontal translocation of organic material.[7]

Composition of vegetal residues[edit]

The water content of most vegetal residues is in the range of 60% to 90%. The dry matter consists mainly of carbon, oxygen and hydrogen, arranged in different kinds of molecules. Carbon and oxygen are heavier than hydrogen, so the numbers that represent the relative proportion of these components vary depending on the evaluation system used. Considering the number of atoms, there are 8 hydrogen atoms for every 3.7 carbon atoms and 2.5 oxygen atoms. In weight, carbon represents 44%, oxygen 40%, hydrogen 8%. Although these elements represent 92% of dry weight, there are other elements that are of great importance for the nutrition of plants. They include nitrogen, sulfur, phosphorus, potassium, calcium and magnesium. Other also important elements are present in even smaller quantities, and are called micronutrients.[7]

Composition compounds[edit]

The elements listed in the preceding section are combined and arranged to form different chemical compounds that can be grouped in a few categories.

Carbohydrates are made up of carbon, hydrogen and oxygen, and range in complexity from rather simple sugars to the big molecules of cellulose.

Fats consists of glycerids of fatty acids, like butyric, stearic, oleic. They are also made up of carbon, oxygen and hydrogen atoms.

Lignins are complex compounds that form the older parts of wood, and consists also mainly of carbon, oxygen and hydrogen. They are very resistant to decomposition.

Proteins contain nitrogen in addition to the three usual elements, and small amounts of sulfur, iron, and phosphorus.[7]

Decomposition process[edit]

The vegetal residues in general are not water soluble, and in any case they are not usable, as they are, by the plants. They constitute, nevertheless, the raw materials from which plant nutrients are derived. The decomposition process is carried out by enzymatic biochemical processes, done by soil michroorganisms, that obtain the necessary energy from the same residues, and produce the mineral compounds that are apt to be absorbed by plant roots. This process by which organic compounds are broken down and transformed into mineral (inorganic) compounds is also referred to as mineralization.[7]

The break down of the organic compounds is done at very different rates, depending on their nature. The ranking, from fast to slow rates is as follow.

1. Sugars, starches and simple proteins.

2. Proteins.

3. Hemicelluloses.

4. Cellulose.

5. Lignins and fats.

The reactions that take place can be included in one of three groups:

- Enzymatic oxidation, that produces carbon dioxide, water, and heat. It affects the bulk or major portion of the material.

- The essential elements, nitrogen, sulfur, phosphorus, are liberated and mineralized by a series of specific reactions.

- Compounds that are resistant to microbial action are formed by modification of original compounds or by synthesis of new ones by microbes, creating humus.[7]

The list of mineral end products is as follow

Element Mineral end products
Carbon CO2, CO32-, HCO3-, CH4, C
Nitrogen NH4-, NO2-, NO3-, N2 (gas)
Sulfur S, H2S, SO32-, SO42-, CS2
Phosphorus H2PO4-, HPO42-
Others H2O, O2, H2, H+, OH-, K+, Ca2+, Mg2+, etc

Humus[edit]

Main article: Humus

As vegetal material undergoes decomposition, some microbial resistant compounds are formed. These include modified lignins, oils, fats and waxes. Secondly, some new compounds are synthesized, like polysacarides and polyuronids. These materials form the basis for humus. New reactions take place between these compounds and some proteins and other nitrogen containing products, incorporating thus nitrogen and avoiding its mineralization. Other nutrients are also protected in this way from mineralization.

Humic substances classification. There is a classification into three groups, based on solubility in acids and alkalis, and also related to stability.

-Fulvic acid is the group which contains the materials that have the lowest molecular weight, and are soluble in acids and alkali, and susceptible to microbial attack.

-Humic acid group contains the intermediate materials, with medium molecular weight, soluble in alkali, but insoluble in acid, and intermediate resistance to microbial attack.

-Humin is the generic name for the materials with highest molecular weight, that are darkest in color, insoluble in acid and alkali, and with the most resistance to microbial attack.[7]

Role in carbon cycling[edit]

Soil plays a major role in the global carbon cycle, with the global soil carbon pool estimated at 2500 gigatons. This is 3.3 times the size of the atmospheric pool (750 gigatons) and 4.5 times the biotic pool (560 gigatons). The pool of organic carbon, which occurs primarily in the form of SOM, accounts roughly 1550 gigatons of the total global C pool, with the remainder accounted for by soil inorganic carbon (SIC). The pool of organic C exists in dynamic equilibrium between gains and losses; soil may therefore serve as either a sink or source of C, through sequestration or greenhouse gas emissions, respectively, depending on exogenous factors.[8]

See also[edit]

References[edit]

  1. ^ Brady, N.C., and Weil, R.R. 1999. The nature and properties of soils. Prentice Hall,Inc., Upper Saddle River, NJ.
  2. ^ Périé, C. and Ouimet, R. 2008. Organic carbon, organic matter and bulk density relationships in boreal forest soils. Canadian Journal of Soil Science 88: 315-325.
  3. ^ Jain, T.B., Graham, R.T. and Adams, D.L. 1997. Carbon to organic matter ratios for soils in Rocky Mountain coniferous forests. Soil Science Society of America Journal 61: 1190-1195.
  4. ^ Troeh, Frederick R., and Louis M. (Louis Milton) Thompson. Soils and Soil Fertility. 6th ed. Ames, Iowa: Blackwell Pub., 2005. [1]
  5. ^ Juma, N. G. 1999. Introduction to Soil Science and Soil Resources. Volume I in the Series "The Pedosphere and its Dynamics: A Systems Approach to Soil Science." Salman Productions, Sherwood Park. 335 pp.
  6. ^ Glossary | NRCS SQ
  7. ^ a b c d e f Brady, Nyle C. (1984). The Nature and Properties of Soils (Ninth ed.). New York: MacMillan. p. 254. ISBN 0-02-313340-6. 
  8. ^ Lal, R. 2004. Soil carbon sequestration to mitigate climate change. Geoderma 123(1): 1-22.