Download - Soil fertility
Microbial Mediated Micronutrient
Transformation in soil
Fe
Zn
Cu
Mo
Mn
• Plants require some elements in such minute or smaller amounts that these element have been designated as minor/trace element or Micro nutrient.
• Plants absorbed micronutrient in lower concentration ppm level.
Micronutrient
Iron, Zinc, Copper, Manganese, Boron, Molybdenum, Nickel, Chloride
• Source- Goethite, Haematite, Magnetite, Limonite, Olivine
• Forms of Fe- Ferrous & Ferric (Two oxidation state)• Two fraction- Organic & mineral
• Sufficient range of Fe in plants : 50 – 250 ppm.
• Below 50 ppm – Deficiency appears young leaves- Interveinal chlorosis.
• Above 250 ppm- Leaf bronzing.
Iron (Fe)
Fe in soilMineral Fe• 4th most abundant element in earth crust 5%• Solubility is low.
Soil solution• Well drained , oxidised soil has a more Fe3+
• Water logged soil – More Fe2+
Iron bacteria (micro organisms) play a major role
in transformation
Bacteria & fungi oxidise ferrous state to ferric
state.
Heterotrophic microorganism attacks soluble
organic Fe in to inorganic Fe salts.
Bacteria & fungi produce specific enzyme.
Transformation of iron in soil by Micro organisms
Bacteria oxidise ferrous Fe to ferric Fe state which precipitate as ferric hydroxide – Iron Bacteria
• Gallinonella• Siderocapsa• Siderosphaera• Ferribacterium• Naumanniela• Sideromonas• Ferro-bacillus• Siderobacter• Siderococus
• Obligate Chemoautotrophs- Capable of utilizing energy released in the process of ferric hydroxide formation.
(E.g) Gallionella ferruginea
Thiobacillus ferroxidans
Ferrobacillus ferroxidans
Classification
• Facultative Chemoautotrophs-Utilizing energy derived in the process of ferric hydroxide formation or from organic matter.
• (E,g) Leptothrix ochraceae
• Heterotrophs- Do not energy derived in the process of ferric hydroxide formation but depend on organic matter for nutrition.
• (E.g) Naumanniela
• Cyanophycea
• Volvocales
• Chlorococcales
• Eugleninaea
• Conjugales
Transform ferrous salts to ferric salt
Algae
• Source: Limestone, Sandstone.• Forms: Zn2+
• Sufficient range of Zn in plants : 25 – 150 ppm
• Mineral: Zn in lithosphere is 80 ppm• Soil solution: Depends on the soil pH . If pH is
more
Zn2+ availability is more.
Zinc (Zn)
Two fraction
Organic- Small amount 0.01%- 0.05%Inorganic- Source is Zinc sulphate- soluble in soil
Below and above the range cause Rosetting or clustering of young leaves.
Young leaves become chlorotic spot.
• Omnipotent bacteria- Increase concentration of Zn • Fungi also influence solubilize the mineral
from of Zn in soil by production of organic acids.
• Organic material increase the availability of micro organisms in soil
• Increase the availability of Zn in soil
Transformation of Zinc in soil by Micro organisms
• Several zinc solubilizing bacteria (ZSB)- Tropical and temperate soils to provide plant available Zn. (Hafeez et al., 2013).• Gluconacetobacter – sugarcane. • Bacillus, Pseudomonas - Soybean, rice
and wheat capable of solubilizing Zn. (Saravanan et al., 2011).
Omnipotent bacteria
Zinc solubilizing bacteria
•Pseudomonas
•Bacillus
•Gluconacetobacter
•Burkholderia
•Acinetobacter
•Serratia
• Flavobacter
• Enterobacter
Comparison• ZSB• ZSB soil bacteria, able to solubilize the inorganic Zn
• These ZSB strains produce variety of low molecular weight organic acids, particularly gluconic acid, dissolute the insoluble Zn
• Reduce the pH of the soil solution - increase the plant available zinc (Hafeez et al., 2013). • Zn-fertilizers - 1-5% use efficiency for most of the
crops • ZSB soil bacteria, able to solubilize the inorganic
Zn and thereby increase the bioavailability for crop assimilation.
• Source: Pyrolusite, Hausmannite, Manganite.
• Forms: Mn2+
• Sufficient range of plant: 20 – 500 ppm.
• Fraction: Solution, Exchangeable, Organic, Mineral
Manganese
Mineral Mn
• Mn is found in most Fe-Mg rocks- weathering of primary mineral.• Pyrolusite• Manganite
Soil solution Mn:
• MnSO4 is the most common Mn sources in soil.
• Most common form Mn2+ - 90%.• High pH- Solubility of Mn2+ is low
• Manganese transformation include bacteria, fungi and yeasts. • Bacteria – Leptothrix mobilis - aquatic environment-
oxidizing both iron, manganese. (Nelson et al. 1998)• Oxidize manganous compounds to manganic oxides
(MnO.,) at pH values as low as 6 & some times below 6. (Mulder 1964, Mulder and van Veen 1963).
Transformation of Manganese in soil by
Micro organisms
• Manganese oxidation by a mixture of two bacteria Corynebacterium sp. Chromobacterium sp. has been recorded by Bromfield and Skerman (1950) • Roots of living plants may promote the
solubilization of MnO, by excreting organic acids or other compounds stimulating bacterial activity.
• Source: Malachite, Cupric ferrite, Carbonates, Silicates, Sulfates, Chlorides.• Sufficient range in plants: 5 to 20 ppm.• Forms: Cuprous (Cu+), Cupric (Cu2+)
Copper
• Availability of copper in soil related with the presence of black organic humus.
• H2S forming microorganisms may be involved in copper precipitation.
Transformation of Copper in soil by Micro organisms
Copper precipitation by hydrogen-sulphide-producing
bacteria• Clostridia, Proteus vulgaris, Escherichia coli -
producing H2S from sulphur-containing amino acids (cystine, methionine, glutathion, etc.)- precipitate the Cu • Sulphate-reducing bacteria- precipitate the Cu-
Insoluble form- Assimilatory sulfate reduction
• Sulfate-reducing bacteria are responsible - hydrogen sulfide will react with metal ions to produce metal sulphides. These metal sulphides- insoluble
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