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Elemental phosphorus, “P”, is highly reactive and is never found in nature as a free element. It occurs in nature as an inorganic mineral phosphate, “PO4 ”, combined with calcium, aluminum, iron, magnesium, and other elements. In common fertilizer terminology, “phosphate” refers to the regulatory expression as “phosphorus pentoxide” or “P2 O5 ”. (P x 2.28 = P2 O5 , P2 O5 x 0.44 = P)
Phosphorus required by plants in relatively large amounts
Requirements much lower than nitrogen and potassium
Requirement similar to sulfur, calcium, or magnesium
Total content in mature leaves ranges from 0.2% to 0.5% P
Found in various compounds
ATP (adenosine triphosphate): energy transfer
NADP (nicotinamide adenine dicucleotide phosphate): photosynthesis and respiration
Nucleic acids: DNA, RNA
Phospholipids: cell and organelle membranes
Mobile in plant
Most phosphorus taken up by roots as inorganic orthophosphate ions (HPO4 2- or H2 PO4 - )
Translocated from older leaves to young growing points
Phosphorus concentration in root cells and xylem sap 100 to 1000 times higher than soil concentration
Deficiency symptoms
Generally occurs when plant content is below 0.20% P
Stunted plants, poor root growth
Leaf discoloration
Darkish-green color in older leaves
Reddish-purple color with necrosis of leaf margins
Delayed maturity; reduced yield, quality
Purpling can be genetic response to stresses not related to soil phosphorus deficiency
Restricted or slow root growth is factor
Cold soils; wet, poorly drained or excessively dry soils
Damaged from herbicide, fertilizer, pests
Compaction, shallow rooting
Cool, night-time temperatures (≈ 40 to 45°F) with sunny, warm days (≈ 60 to 70°F )
Unmetabolized sugars accumulate in leaf and stem tissues of young plants
Triggers production of anthocyanins (red pigments) in some species and varieties
Symptoms often disappear when rapid growth resumes under more favorable conditions
Not directly toxic to plants or other organisms
Environmental problems with excess phosphorus
Stimulates growth of aquatic organisms, like algae
Accelerates eutrophication of surface waters
Excess soil phosphorus increases potential for offsite transport and loss
Particulate phosphorus contained in sediment that is transported off-sit by storm-water or irrigation runoff
Storm-water runoff also contains high concentrations of soluble phosphorus
Leaching can occur if preferential flow pathways are present in soil and subsoil
Common total phosphorus concentration in surface soil about 200 to 1000 ppm P
May range from 50 to 2500 ppm total P
Soil test phosphorus is poor predictor of total phosphorus
Phosphorus sources
Mineralization of organic matter
Organic matter can contain from 20% to 80% of total soil phosphorus
Weathering (dissolution) of primary soil minerals
Phosphorus widely distributed in many minerals
Apatite (an impure tri-calcium phosphate) is common mineral
Primary minerals are very slowly available, long-term phosphorus source
Dissolution of secondary soil minerals
Solubility of individual secondary minerals varies greatly and change with changes in soil pH
Predominantly iron and aluminum phosphates in acid soils
Predominantly calcium and magnesium phosphates in alkaline soils
Applications of manure, compost, biosolids, or commercial fertilizers
Phosphorus uptake
Most phosphorus taken up by roots as inorganic orthophosphate ion (HPO4 2- or H2 PO4 - )
H2 PO4 - uptake is more rapid than uptake of HPO4 2-
Related to divalent vs. monovalent charge
Roots absorb some organic phosphates (nucleic acids, phytin), but of minor importance to overall phosphorus nutrition
Phosphorus moves to plant roots primarily by diffusion
HPO4 2- , H2 PO4 - concentrations are low in solution
About 0.05 ppm P in agricultural soils
Relative amounts of HPO4 2- and H2 PO4 - depend upon soil solution pH
Present in equal amounts at pH 7.2
HPO4 2- concentrations higher in alkaline conditions
H2 PO4 - concentrations higher in acidic conditions
Cation/anion balance
Phosphate uptake increases Ca2+ , Mg2+ , K+ uptake
Charge balance, co-transport
Phosphate anion uptake can inhibit or compete with NO3 - and SO4 2- anion uptake
Rhizosphere pH helps control uptake
Roots release bicarbonate anion (HCO3 - ) and in turn absorb phosphate anion (H2 PO4 - )
For each phosphate anion (H2 PO4 - ) absorbed, one hydroxide ion (OH- ) is released into soil
Size and density of plant root systems very important for phosphorus uptake
Individual phosphate ion moves less than 1 mm (0.04 inch) in a growing season
Low phosphate concentrations in soil solution, so fewer ions than some other nutrients
Many adsorption, precipitation reactions in soil that “compete” with root uptake
Mycorrhizal infection of roots important for phosphorus uptake in some species
Mycorrhizae can serve as “surrogate root system”
Soil temperature important
Affects speed of root growth and of soil reactions that make phosphorus available
e.g., soil temperature reduced from 70°F to 58°F
Corn root growth decreased 5-fold
Phosphorus uptake by corn roots decreased 4-fold
Phosphorus transformations in soil (for further details, see Crop File 1.04.311 Phosphorus Transformations in the Soil)
Weathering down and formation of various “non-labile” primary and secondary soil minerals
Consists mainly of insoluble or sparingly soluble mineral phosphates
Mineralization
Organic phosphorus released as plant available inorganic phosphate
Immobilization
Microbial uptake of inorganic phosphate from the soil and incorporation into organic forms
Adsorption/desorption
Ionic exchange with sites on various mineral surfaces
Includes surfaces of clays, iron oxides, aluminum oxides, and carbonates
Precipitation/dissolution of “labile” secondary minerals
Consists mainly of highly to moderately soluble calcium, aluminum, and iron phosphates
Availability differs among various phosphorus fractions
Soil solution phosphorus
Considered “immediately available” for root uptake
About 0.01% of total soil phosphorus
Labile phosphorus
Labile: readily reactive (“changeable”) fractions
Rapidly replenishes solution phosphorus
About 10% to 20% of total soil phosphorus
Portion of adsorbed phosphorus that dissociates easily
Rapidly decomposed organic matter fractions
Readily soluble to moderately soluble phosphorus minerals
Non-labile phosphorus
Non-labile: slowly reactive or unreactive fractions
Slowly replenishes solution phosphorus or labile phosphorus fractions
About 80% to 90% of total soil phosphorus
Strongly adsorbed phosphorus
Stable organic compounds; not readily decomposed
Slowly soluble or insoluble phosphorus minerals
Phosphorus “intensity”
Intensity: soil solution phosphorus
Fixation: removal of inorganic phosphorus from soil solution
Assimilation as organic phosphorus by plants or microbes
Adsorption on mineral and clay surfaces
Precipitation of various minerals
Fixation reactions reduce solution phosphorus (reduces intensity)
Reactions also provide reservoir to replenish solution phosphorus (maintains intensity)
Phosphorus “capacity”
Quantity of solid soil fractions available to replenish solution phosphorus that is taken up by plant roots
Includes labile and non-labile fractions that are reserves for replenishing solution phosphorus
Adsorbed phosphate
Organic phosphorus fractions
Mineral phosphorus fractions
Relative amount and proportion of labile and non-labile fractions affect quantity
Phosphorus buffering
Buffering capacity: ability of soil to maintain phosphorus concentrations (intensity) in soil solution
Poorly buffered soil: Phosphorus reserves unable to sustain required intensity
Well buffered soil: Phosphorus reserves meet or exceed required intensity
Soil test provides relative index of buffering ability
Extracting solution and soil are in contact for only short time (e.g., five minutes)
Amount of extracted phosphorus indicates relative ability of soil to resupply soil solution phosphorus
Short-duration test methods intended to provide estimate of potential, season-long “availability”
Soil test must be calibrated to growth response or yield response by field research
Modes of action
Acidic solvent
Extracting solution with pH of 2 to
Mainly dissolves calcium phosphate, some iron and aluminum phosphates
Anion replacement
Targets phosphate adsorbed to surfaces of carbonates, iron oxides, and aluminum oxides
Adsorbed anion (HPO4 2- , H2 PO4 - ) is replaced by another anion, including:
Bicarbonate, HCO3 -
Sulfate, SO4 2-
Acetate, C2 H3 O2 −
Citrate, C6 H5 O7 3−
Cation complexation
Fluoride ion (F- ) is effective at complexing aluminum ions (Al3+ )
Reduces Al3+ concentration in solution
Aluminum phosphates dissolve to maintain Al3+ concentration in solution
Fluoride ion (F- ) reacts with calcium phosphates
Forms insoluble calcium fluoride (CaF2 )
Calcium phosphates dissolve to maintain Ca2+ concentration in solution
Bicarbonate (HCO3 - ) causes solution calcium to precipitate as calcium carbonate
Reduces Ca2+ concentration in solution
Calcium phosphates dissolve to maintain Ca2+ concentration in solution
Phosphorus determination
Extracting solution is separated from soil by filtering
Concentration of phosphate ions released to extracting solution measured by colorimetry or spectrometry
Soil analysis methods (See Crop File 1.01.231, Soil Test Phosphorus Methods)
Fertilizer phosphorus content expressed as “percent phosphate” or “% P2 O5 ”
Phosphorus not actually present in fertilizers as P2 O5
Holdover from 1800’s when chemists expressed elemental concentrations in “oxide” form
Many laws governing fertilizer guarantees originally written during this time; maintains expression today
Organic, biological source s
Manure
Ranges from 5 to 60 lb P2 O5 /ton depending on animal species and storage/handling methods
Biosolids
Typical range: freshly digested biosolids range about 3.5% to 8.0% P2 O5
Phosphorus content often elevated due to use of household and commercial detergents
Bone meal
Common analysis: 10% to 20% P2 O5
Common inorganic fertilizer materials
Rock phosphate
Base product for manufactured fertilizers
Total content about 20% to 36% P2 O5
Zero water soluble phosphorus
Ineffective if applied to soil with pH above 7
Normal superphosphate, Ca(H2 PO4 )2 •CaSO4
Common analysis: 0-20-0-12sul
Dry prilled product
Triple superphosphate (TSP), Ca(H2 PO4 )2
Common analysis: 0-45-0
Dry prilled product
Diammonium phosphate (DAP), (NH4 )2 HPO4
Common analysis: 18-46-0
Dry prilled product
Monoammonium phosphate (MAP), NH4 H2 PO4
Common analysis: 11-52-0
Dry prilled product
Used to produce suspension-grade fertilizers
Ammonium polyphosphate (APP), (NH4 )3 HP2 O7 + (NH4 )2 HPO4
Common analysis: 10-34-0, 11-37-0
Liquid solution
Able to “sequester” micronutrient in solution
Fertilizer placement
Topdress (surface broadcast, no incorporation)
Phosphorus has limited soil mobility
Surface-applied phosphorus will move to roots very slowly
Often ineffective for annual crops or newly planted perennial crops
Acceptable method for established perennial forages
Surface broadcast with soil incorporation
Places immobile phosphorus in root zone
Exposes phosphorus to large amount of soil surface area
Highest potential for phosphorus fixation under proper conditions
Placed in subsoil band or strip
Minimizes contact between soil and fertilizer
Less fixation potential compared to same amount of phosphorus broadcast and incorporated
Roots will proliferate in high phosphorus zone
Application method (See Crop File 2.01.120 , Phosphorus Fertilizer Placement: General Overview )
Depends upon:
Soil test phosphorus
Soil characteristics (texture, excess lime, etc.)
Crop root system characteristics
Soil conditions (temperature, moisture, etc.)
Banding generally most effective on low phosphorus soils with high fixation capacity
Broadcast/incorporate or banding generally have similar efficacy in high phosphorus soils or soils with low fixation capacity
Foliar or fertigation applications generally not effective
Application frequency
May be affected by soil’s phosphorus fixation capacity
Better to use smaller, more frequent applications or banding if fixation potential is high
Single broadcast applications every three to four years are effective if fixation potential is low
Application rates
Affected by:
Soil test value; soil type characteristics
Crop requirement, productivity
Land tenure (rent, own, lease)
Product cost, application cost, equipment availability
Return from yield over fertilizer cost
Sufficiency rate approach
Intended to optimize economic return during current year (e.g., single-year lease or rent)
Achieve 90% to 95% of maximum yield
Requires annual soil test to adjust rate
Build rate approach
Choose target soil test range to maximize yield
Target range should remove phosphorus as factor that limits yield (100% of maximum)
Not intended to optimize annual economic return; considers long-term view, future returns (e.g., land is owned)
Plan time frame for fertilizer applications, typically four to eight years
Calculate application rates from difference between current soil test level and target range
e.g., Apply 18 to 20 lb P2 O5 /ac for each 1 ppm soil test P
Divide total application required by time frame in years to calculate annual rate
Monitor by soil test every three to four years
When target range is reached, cease applications to build soil test
Lower rate maintenance applications or “starter” applications are optional
Maintenance rate approach
Rate based on phosphorus removed by annual grain or forage harvest
Does not require soil sampling; assumes no change in soil test from year-to-year
Combination approach
May utilizes different approaches, depending on soil test category or other factors
Sufficiency plus build in “low” category
Build plus maintenance in “medium” category
Maintenance in “high” category
Starter from “low” to “very high” category
Adjust rates based on economic return or on acceptable risk
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