Forms of Phosphorus available for Plant Uptake
The orthophosphates, H2PO4- and HPO42-, are the primary forms of phosphorus taken up by plants.
When the soil pH is less than 7.0, H2PO4- is the predominate form in the soil.
Although less common, certain organic phosphorus forms can also be directly taken up by plants.
Functions of Phosphorus in Plants
Phosphorus is involved in many plant processes, including:
Energy transfer reactions
Development of reproductive structures
Crop maturity
Root growth
Protein synthesis
Phosphorus Cycle or Transformation
Phosphorus is only second to nitrogen as a mineral nutrient required for plants, animals and microorganisms. It is a major constituent of nucleic acids in all living systems essential in the accumulation and release of energy during cellular metabolism. This element is added to the soil in the form of chemical fertilizers, or in the form of organic phosphates present in plant and animal residues. In cultivated soils it is present in abundance (i.e. 1100 kg/ha), but most of which is not available to plants, only 15 % of total soil phosphorus is in available form. Both inorganic and organic phosphates exist in soil and occupy a critical position both in plant growth and in the biology of soil.
Microorganisms are known to bring a number of transformations of phosphorus, these include:
(i) Altering the solubility of inorganic compounds of phosphorus,
(ii) Mineralization of organic phosphate compounds into inorganic phosphates,
(iii) Conversion of inorganic, available anion into cell components i.e. an immobilization process and
(iv) Oxidation or reduction of inorganic phosphorus compounds. Of these mineralization and immobilization are the most important reactions / processes in phosphorus cycle.
Insoluble inorganic compounds of phosphorus are unavailable to plants, but many microorganisms can bring the phosphate into solution. Soil phosphates are rendered available either by plant roots or by soil microorganisms through secretion of organic acids (eg. lactic, acetic, formic, fumaric, succinic acids etc). Thus, phosphate-dissolving / solubilizing soil microorganisms (eg. species of Pseudomonas, Bacillus, Micrococcus, Mycobacterium, Flavobacterium, Penicillium, Aspergillus, Fusarium etc.) plays important role in correcting phosphorus deficiency of crop plants. They may also release soluble inorganic phosphate (H2PO4), into soil through decomposition of phosphate-rich organic compounds.
Solubilization of phosphate by plant roots and soil microorganisms is substantially influenced by various soil factors, such as PH, moisture and aeration.
In neutral or alkaline soils solubilization of phosphate is more as compared to acidic soils. Many phosphates solubilizing microorganisms are found in close proximity of root surfaces and may appreciably enhance phosphate assimilation by higher plants.
By their action, fungi bacteria and actinomycetes make available the organically bound phosphorus in soil and organic matter and the process is known as mineralization. On the other hand, certain microorganisms especially bacteria assimilate soluble phosphate and use for cell synthesis and on the death of bacteria, the phosphate is made available to plants. A fraction of phosphate is also lost in soil due to leaching.
Mineralization of phosphate is generally rapid and more in virgin soils than cultivated land. Mineralization is favored by high temperatures (thermophilic range) and more in acidic to neutral soils with high organic phosphorus content. The enzyme involved in mineralization (cleavage) of phosphate from organic phosphorus compound is collectively called as “Phospatases".
Phosphorus Uptake by Plant Roots
Plant roots absorb phosphorus from the soil solution. In comparison to other macronutrients, the phosphorus concentration in the soil solution is much lower and ranges from 0.001 mg/L to 1 mg/L (Brady and Weil, 2002). In general, roots absorb phosphorus in the form of orthophosphate, but can also absorb certain forms of organic phosphorus. Phosphorus moves to the root surface through diffusion. However, the presence of mycorrhizal fungi, which develop a symbiotic relationship with plant roots and extend threadlike hyphae into the soil, can enhance the uptake of phosphorus, as well especially in acidic soils that are low in phosphorus.
Phosphorus Sorption and Desorption
P-sorption occurs when the orthophosphates, H2PO4- and HPO42-, bind tightly to soil particles.
Since phosphate is an anion, particles that generate an anion exchange capacity will form strong bonds with phosphate.
Particles with anion exchange capacity:
Aluminum and iron oxides
Highly weathered kaolin clays (under acidic conditions)
Amorphous materials.
These particles are commonly found in many of the most highly weathered soils and high weathered volcanic soils of Hawaii. Since P-sorption results in a decrease of plant available phosphorus, P-sorption can become a major issue in many Hawaii soils.
Additionally, in calcareous soils P-sorption may occur as phosphates sorb to impurities such as aluminum and iron hydroxides or displace carbonates in calcium carbonate minerals.
Factors that affect P-sorption
Soil Mineral Type: Mineralogy of the soil has a great effect on P-sorption.
Volcanic soils tend to have the greatest P-sorption of all soils since volcanic soils contain large amounts of amorphous material.
Following volcanic soils, highly weathered soils (such as Oxisols and Ultisols) have the next greatest P-sorption capacities. This is due to the presence of large amounts of aluminum and iron oxides and highly weathered kaolin clays.
On the other end of the spectrum, less weathered soils and organic soils have low P-sorption capacities.
Amount of clay: As the amount of clay increases in the soil, the P-sorption capacity increases as well. This is because clay particles have a tremendous amount of surface area for which phosphate sorption can take place.
pH: At low pH, soils have greater amounts of aluminum in the soil solution, which forms very strong bonds with phosphate. In fact, a soil binds twice the amount of phosphorus under acidic conditions, and these bonds are five times stronger.
Temperature: Generally, P-sorption increases as temperature increases.
Factors that decrease P-sorption:
Other anions, such as silicates, carbonates, sulfates, arsenate, and molybdate, compete with phosphate for a position on the anion exchange site. As a result, these anions can cause the displacement, or desorption, of phosphate from the soil exchange site. Desorption causes phosphate availability in the soil solution to increase.
Organic matter increases P availability in four ways.
First, organic matter forms complexes with organic phosphate which increases phosphate uptake by plants.
Second, organic anions can also displace sorbed phosphate.
Third, humus coats aluminum and iron oxides, which reduces P sorption.
Finally, organic matter is also a source of phosphorus through mineralization reactions.
Flooding the soil reduces P-sorption by increasing the solubility of phosphates that are bound to aluminum and iron oxides and amorphous minerals.
Phosphate Precipitation and Dissolution
Phosphate precipitation is a process in which phosphorus reacts with another substance to form a solid mineral.
In contrast, dissolution of phosphate minerals occurs when the mineral dissolves and releases phosphorus.
Precipitation and dissolution reactions greatly influence the availability of phosphate in the soil.
Phosphate minerals can dissolve over time to replenish the phosphate in the soil solution. This reaction increases the availability of phosphorus.
On the other hand, phosphate minerals form by removing phosphate from soil solution. This reaction decreases the availability of phosphorus.
However, both precipitation and dissolution are very slow processes.
Solubility of Phosphate Minerals
The solubility of phosphate minerals is very dependent upon soil pH.
The soil pH for optimum phosphorus availability is 6.5
At high or neutral pH, phosphate reacts with calcium to form minerals, such as apatite.
Under acidic conditions, phosphorus may react with aluminum and iron to form minerals, such as strengite and varescite.
Mineralization and Immobilization of Phosphate
In an average soil, approximately 50% of total phosphorus is organic. Thus, soil organic phosphorus is a very important aspect of the P cycle.
The various sources of organic phosphorus include:-
Phytin
Nucleic acids
Phospholipids
Like nitrogen, organic phosphorus is converted to inorganic phosphate through the process of mineralization.
The immobilization of inorganic phosphate, in contrast, is the reverse reaction of mineralization. During immobilization, microorganisms convert inorganic forms to organic phosphate, which are then incorporated into their living cells.
Mineralization and immobilization of phosphorus occur simultaneously in the soil. Ultimately, the C:P ratio determines whether there is net mineralization or net immobilization.
When the C:P ratio is less than 200:1, net mineralization prevails. Net mineralization indicates that there is enough phosphorus in the soil to sustain both plants and microorganisms.
When the C:P ration is between 200:1 and 300:1, immobilization and mineralization rates are fairly equal.
When the C:P ratio is greater than 300:1, net immobilization occurs. During immobilization there is not enough P to sustain both plants and microorganisms; and so, microorganisms scavenge the soil for P.
Factors affecting mineralization and immobilization
The factors that affect P mineralization and immobilization are the same that affect nitrogen mineralization and immobilization:
· Temperature
· Moisture
· Aeration
Management of phosphorus—P-fixation
P-fixation is a term that is used to describe both P-sorption and P precipitation. Since both P-sorption and P precipitation reduce phosphorus availability, a soil with a great P-fixation capacity has less available phosphorus after fertilization than a soil with a low P-fixation capacity.
In other words, when the same amount of fertilizer is applied to a volcanic soil and a moderately weathered grassland soil, the volcanic soil has less P available due to its greater P-fixation capacity.
Phosphorus leaching and runoff
In Maui County and other tropical regions, highly weathered soils often provide little available phosphorus for plant growth. To further compound this issue, agricultural systems can experience phosphorus losses as the result of erosion by wind and runoff water. Erosion by wind can carry particles that contain sorbed-P to water systems, where phosphorus may later desorb. Sediments containing phosphorus can also contaminate ground and/or surface waters. Additionally, phosphorus availability is reduced by the removal of plant material (which can serve as a source of organic phosphorus) during harvest.
Although phosphorus leaching is normally limited in most Hawaii soils due to their high P-fixing characteristics, phosphorus leaching can occur if the soil reaches maximum phosphorus holding capacity, especially when P fertilizers are over applied. Sandy soils are most susceptible to phosphorus leaching. The consequence of phosphorus leaching is the contamination of ground water reserves.
Phosphorus
Involved in photosynthesis, respiration, energy storage and transfer, cell division, and enlargement
Promotes early root formation and growth
Improves quality of fruits, vegetables, and grains
Vital to seed formation
Helps plants survive harsh winter conditions
Increases water-use efficiency
Hastens maturity (early maturity)
Phosphorus deficiency
Reduced growth; leaves dark green; purple or red color in older leaves, especially on the underside of the leaf along the veins; leaf shape may be distorted; thin stems; limited root growth.
Toxicity (excess)
Shows up as micronutrient deficiency of Zn, Fe, or Co.