Phosphorus fertilizers

Last updated: June 21, 2025

Phosphorus fertilizers — mineral substances containing phosphorus in a form available to plants, or in a form that, when it enters the soil, becomes available to plants, and serving to supply agricultural crops with phosphorus.

Circulation and balance of phosphorus in agriculture

Main page: Circulation and balance of phosphorus in agriculture

Raw materials for the production of phosphorus fertilizers

The raw materials for the production of phosphorus fertilizers are natural phosphorus-containing ores — apatite and phosphorite. Metallurgical industry wastes are also used as phosphorus fertilizers. The main world reserves of phosphate ores are in Morocco, the USA, and Russia.

According to phosphorus content, ores are divided into rich, up to 35%, and poor, with a content of 5–10%. Most often, because of the large amount of impurities, they are subject to enrichment.

Apatite

Apatite is a mineral; in a dispersed state it is present in soils and parent rocks. Deposits are rare. The world’s largest deposit was discovered in 1925 in the Khibiny Mountains on the Kola Peninsula. Small and less valuable in composition deposits occur in Russia in the Urals and the Southern Baikal region, in Brazil, Spain, Canada, the USA, and Sweden.

Apatites are rocks of endogenous origin. Pure apatite is a colorless, greenish, or yellow-green mineral; its phosphorus content is up to 42% calculated as P2O5. Apatite crystals are hexagonal prisms with high strength. The empirical formula is [Ca3(PO4)2]3⋅CaF2. Fluorine can be replaced by chlorine, carbonate, or hydroxyl groups. Accordingly, fluorapatite, chlorapatite, carbonateapatite, and hydroxylapatite are distinguished.

In the Khibiny Mountains, apatite is represented as apatite-nepheline rock. Nepheline is an aluminosilicate of composition (K, Na)2O⋅Al2O3⋅SiO2, containing up to 5–6% K2O. Apatite and nepheline make up approximately 90% of the ore mass; the rest is feldspar, hornblendes, and other minerals.

Nepheline on acidic soils can be used as a potassium fertilizer. It is insoluble in water, but in an acidic environment potassium passes into a plant-available form.

Apatite-nepheline ore is mined by open-pit and underground methods. By external signs it is sorted, yielding marketable ore with a content of up to 30–31% P2O5. Subsequently, the ore is enriched by flotation, owing to which nepheline is almost completely removed. The resulting apatite concentrate contains 39–40% P2O5 and is used for the production of phosphorus fertilizers.

Phosphorites

Phosphorites are sedimentary rocks, usually of marine origin, containing amorphous or crystalline calcium phosphate with an admixture of quartz, lime, clay particles, and other minerals.

Phosphorites formed as a result of the life activity of marine plant and animal organisms in past geological periods. The biological origin is confirmed by the content of organic matter (up to 0.5–1.0% by carbon). Deposits occur in sedimentary rocks in the form of nodules of various sizes and shapes (nodular phosphorites), less often in the form of beds of continuous mass (bedded phosphorites).

Phosphorites are characterized by greater particle strength than apatites; they can be amorphous and microcrystalline. Nodular (concretionary) phosphorites in the form of rounded stones and bedded (massive) phosphorites representing a fused mass are distinguished. The latter are less common. There are also granular shell types.

By geotectonic position, phosphorite deposits can be platform, that is, horizontally occurring over large areas of the Earth’s crust with a small layer thickness, and geosynclinal, that is, located in folded mountain regions. An example of a geosynclinal deposit is Karatau.

Most phosphorite deposits in Russia belong to the nodular type. Such phosphorites, as a rule, do not have a pronounced crystalline structure, are more easily decomposed, and therefore are of interest for direct (without chemical treatment) use as a phosphorus fertilizer.

The crystalline structure is more pronounced in phosphorites that are older by geological age.

The disadvantage of most phosphorite deposits is the low phosphorus concentration with a high content of sesquioxides in the raw material, which complicates processing and the production of superphosphate. An admixture of sesquioxides leads to additional acid consumption in the production of phosphorus fertilizers and to retrogradation, that is, the reverse transition of phosphates into poorly soluble compounds. Thus, to obtain 1 t of plant-available P2O5 in superphosphate for the decomposition of apatite concentrate, 1.89 t of sulfuric acid is required, whereas for phosphorites with impurities, 2.5 t is required.

Phosphorite deposits are quite widespread in the world, but, for example, in Western Europe they are small and almost unsuitable for development. The largest phosphorite deposits are in the countries of North Africa. In the USA, deposits are in Florida, Tennessee, and some other states.

In Russia, large reserves of phosphorites are concentrated, but most of them are poor in phosphorus and contain large impurities of sesquioxides (R2O3). Mainly, the deposits are concentrated in the European part of Russia.

Table. Chemical composition of phosphorites and apatites, % on dry matter.

DepositP2O5CaOR2O3CO2FInsoluble residue
Phosphorites
Vyatka-Kama23.537.25.44.52.515.6
Yegoryevskoye (Portland horizon)27.142.05.45.23.39.4
Seshchinskoye15.624.03.12.71.848.3
Shchigrovskoye16.126.23.03.11.945.8
Apatites
Khibiny:
- apatite-nepheline rock30.139.59.00.02.615.6
- apatite concentrate40.551.60.90.23.3—

The Vyatka-Kama deposit is located in the northeast of the European part of Russia, of nodular type, with a phosphorus content of 24–26% P2O5.

The Yegoryevskoye deposit is located in Moscow Oblast. The deposits are represented by two horizons separated by a layer of loose glauconitic sand: the upper one is the Ryazan horizon, the lower one is the Portland horizon. The quality of the latter is higher than that of the Ryazan: it contains 25–26% P2O5 and 4–5% sesquioxides. The Ryazan layer contains on average 21–23% P2O5 and 10–12% sesquioxides.

The Seshchinskoye deposit is located in Dubrovsky District of Bryansk Oblast. Phosphorites occur in three horizons of sandy concretions, sometimes cemented into a slab. For development, the upper layer about 0.5 m thick with a content of 14% P2O5 is important, as well as the middle layer 0.53 m thick with a content of 16% P2O5. Between these horizons there is an interlayer of glauconitic sand about 1 m thick.

The Shchigrovskoye deposit in Kursk Oblast belongs to sandy phosphorites. The nodules have different sizes and shapes and are cemented with sandy rock into a continuous slab (“samorod”). Sometimes such slabs contain accumulations of nodules freely occurring in loose sandy rock. This type of phosphorite occurs in Voronezh, Tambov, Oryol, Bryansk, Kaluga, and Smolensk Oblasts. The phosphorus content is 14–19% P2O5; they are poorly suitable for processing and are used as phosphorite flour.

The Karatau phosphorites formed on mobile areas of the Earth’s crust, in place of which mountain formations later arose. A distinctive feature of the deposit is the presence of thick phosphate-containing layers of complex occurrence with a high phosphorus content. The layers alternate with phosphate-siliceous and phosphate-carbonate rocks. In the main horizon of the deposit, the P2O5 content is 26–29%. The greatest value is represented by bedded layers up to 7 m thick; the P2O5 content in them reaches 30–35% with 2–2.5% sesquioxides. The disadvantage of Karatau phosphorites is their increased magnesium content, which gives them hygroscopicity. To eliminate this property, additional treatment is required, which entails an increase in the cost of production.

Classification of phosphorus fertilizers

Depending on solubility and availability to plants, phosphorus fertilizers are classified into three groups:

  • containing phosphorus in a water-soluble form: simple and double superphosphate; phosphorus is well available to plants;
  • containing phosphorus in a water-insoluble form but soluble in weak acids, for example, in 2% citric acid: precipitate, Thomas slag, open-hearth phosphate slag, defluorinated phosphate; phosphorus is available to plants;
  • containing phosphorus insoluble in water, poorly soluble in weak acids, soluble in strong acids: phosphorite flour, bone meal. These phosphorus fertilizers are not available to most crops, but can be assimilated by some plants (lupine, buckwheat) under the action of acidic root exudates.

Because most soils have a near-neutral reaction, water-soluble phosphorus fertilizers are considered the most effective; they are widely distributed in the world. The technology of raw material processing for the production of phosphorus fertilizers is aimed at converting phosphorus into a plant-available form.

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Fertilizers containing phosphorus in a water-soluble form

Phosphorus fertilizers containing phosphorus in a water-soluble form include superphosphates.

By method of production and P2O5 content, they are divided into simple, double, and triple.

By released form: powdered and granulated.

Water-soluble forms are applicable on all soil types, for all crops, and in different application methods. To increase their effectiveness, techniques aimed at reducing chemical absorption by the soil are used, that is, application of granulated forms, row, and local application.

Simple superphosphate

Simple superphosphate, or calcium dihydrogen orthophosphate, monobasic calcium phosphate, monocalcium phosphate — Ca(H2PO4)2 — is a phosphorus fertilizer with a P2O5 content of 16–20%. It is well soluble in water and weak acids.

The production technology was proposed by J. Liebig. The first production plant was built in 1843 in England by Lawes, the founder of the Rothamsted Agricultural Experiment Station.

Thanks to its simple and cheap production technology, superphosphate is the main phosphorus fertilizer used throughout the world.

The technological production scheme is continuous. The raw materials are natural phosphates — apatite concentrate or phosphorite flour. When phosphate raw material is treated with concentrated sulfuric acid, monobasic calcium phosphate and anhydrous calcium sulfate (gypsum) are formed:

$$\lbrack Ca_3(PO_4)_2 \rbrack_3 \cdot CaF_2 + 7H_2SO_4 + 3H_2O = 3Ca(H_2PO_4)_2 \cdot H_2O + 7CaSO_4 + 2HF.$$

The resulting gypsum remains in the fertilizer composition; it accounts for up to 40%.

Besides the formation of calcium dihydrogen orthophosphate, side reactions occur with the formation of free phosphoric acid:

$$\lbrack Ca_3(PO_4)_2 \rbrack_3 \cdot CaF_2 + 10H_2SO_4 = 6H_3PO_4 + 10CaSO_4 + 2HF.$$

The impurity of phosphoric acid in the final product can be 5.0–5.5%, which gives superphosphate an acidic reaction and hygroscopicity.

With a local deficiency of sulfuric acid in the reaction mixture, calcium hydrophosphate is formed:

$$\lbrack Ca_3(PO_4)_2 \rbrack_3 \cdot CaF_2 + 4H_2SO_4 + 12H_2O = 6CaHPO_4 \cdot 2H_2O + 4CaSO_4 + 2HF.$$

Since the resulting gypsum is not separated, the phosphorus content in the product is approximately 2 times lower than in the initial raw material. For this reason, phosphorites with a low P2O5 content are almost unsuitable for superphosphate production. From apatite concentrate, superphosphate is obtained with a content of not less than 19% citrate-soluble phosphorus; in the highest grade, not less than 19.5%.

88–98% of the phosphorus in superphosphate is contained in a plant-available form: water-soluble — calcium dihydrogen orthophosphate and phosphoric acid, and citrate-soluble — calcium hydrophosphate; it accounts for 10–25% of the available phosphorus.

Finished superphosphate contains small impurities of calcium, iron, and aluminum phosphates.

Free phosphoric acid in superphosphate prevents the saturation of gypsum (CaSO4⋅2H2O) with water, therefore calcium sulfate remains anhydrous or as CaSO4⋅0.5H2O.

The final production product is powdered superphosphate, a substance of light gray color. Free phosphoric acid causes hygroscopicity and moisture, which should be not more than 12–15%. During storage and transportation, powdered superphosphate cakes, loses flowability and spreadability. When applied to the soil, powdered superphosphate undergoes rapid chemical absorption, and phosphorus becomes unavailable to plants.

These disadvantages are eliminated by granulation of powdered superphosphate.

Granulated superphosphate does not clump, does not cake, and has reduced moisture. Due to the slow dissolution of granules in soil moisture and the reduction of the contact area of fertilizer particles with the soil, chemical binding decreases, which is especially important when applied on acidic soils with a high content of sesquioxides. Granulated superphosphate allows more uniform spreading.

Granulated superphosphate contains up to 1–2.5% free phosphoric acid and up to 1–4% moisture.

The granulation process is carried out in long (7.5 m) rotating drums, in which powdered superphosphate is moistened to 16%; during drum rotation it is rounded, acquiring the form of round small granules of different sizes. After drying, the granulate is sorted to remove particles less than 1 mm and more than 4 mm. A fraction from 1 to 4 mm in diameter is obtained. Larger granules are crushed and, together with small ones (“return”), returned for repeated granulation. The return acts as centers of granule formation.

During granulation, free phosphoric acid is neutralized by adding ammonia, lime, or phosphorite. When ammonia is used in the process, ammoniated superphosphate is obtained, which contains 1.5–3% nitrogen. When neutralized with phosphorite flour, the phosphorus content in the finished fertilizer increases to 20–22%, but simultaneously the relative content of water-soluble phosphorus decreases.

The quality of superphosphate is assessed by the content of phosphoric acid and the proportion of phosphorus soluble in water and citrate solution — an aqueous solution of ammonium citrate and ammonia.

Simple superphosphate is used on all soil types. Its main disadvantage is its low phosphorus content, which reduces its economic efficiency, primarily during transportation.

Double superphosphate

Double superphosphate is a concentrated phosphorus fertilizer obtained from apatite or phosphorite by treatment with phosphoric acid. It contains phosphorus in the form of calcium dihydrogen orthophosphate Ca(H2PO4)2, as does simple superphosphate, with an impurity of up to 2.5% free phosphoric acid. The main difference from simple superphosphate is the absence of gypsum.

The production technology includes two stages: in the first stage, phosphoric acid is obtained; in the second, double superphosphate.

Two methods are used to produce phosphoric acid.

In the wet extraction method, phosphoric acid is obtained by treating phosphorite, including low-phosphorus phosphorite, with sulfuric acid, with the formation of phosphoric acid:

$$Ca_3(PO_4)_2 + 3H_2SO_4 + 6H_2O = 2H_3PO_4 + CaSO_4 \cdot 2H_2O.$$

Phosphoric acid is extracted with a 20–25% sulfuric acid solution so as not to dissolve large amounts of the contained sesquioxides. After that, phosphoric acid is separated from the precipitate and concentrated by evaporation. The resulting phosphoric acid is used to treat phosphorite with a high phosphorus content and less contamination by impurities:

$$Ca_3(PO_4)_2 + 4H_3PO_4 + H_2O = 3Ca(H_2PO_4)_2 \cdot H_2O.$$

The second method of producing phosphoric acid is the method of producing it by sublimation of phosphorus from low-percentage phosphorites at a temperature of 1400–1500 °C in electric or blast furnaces. Here the released elemental phosphorus is collected under water, burned, and the resulting phosphorus oxide is neutralized with water:

$$P_2O_5 + 3H_2O = 2H_3PO_4.$$

The second stage of double superphosphate production is the reaction of phosphoric acid with phosphate raw material with a high phosphorus content:

$$\lbrack Ca_3(PO_4)_2 \rbrack_3 \cdot CaF_2 + 14H_3PO_4 + 10H_2O = 10Ca(H_2PO_4) \cdot H_2O + 2HF.$$

The initial raw material for the production of phosphorus fertilizers determines the composition of impurities. The best double superphosphate is obtained from apatite; its P2O5 content is 45–49%, free acid not more than 2.5%, and the proportion of water-soluble P2O5 not less than 85%.

Double superphosphate is produced in the form of light gray granules. The cost of 1 t of P2O5 of double superphosphate is 6–13% higher than that of simple superphosphate, but the high concentration of P2O5 determines savings during transportation and storage. The cost of applying P2O5 of double superphosphate is 8–13% less than that of simple superphosphate.

In action, double superphosphate in an equivalent dose does not differ from simple superphosphate. However, due to the absence of sulfur (in the form of gypsum), double superphosphate may be inferior to simple superphosphate on soils with a low sulfur content and under crops demanding sulfur nutrition, for example, legumes and crucifers. In these cases, the application of double superphosphate is combined with sulfur-containing fertilizers, for example, ammonium sulfate, potassium sulfate, and potassium-magnesium sulfate.

Superphos

Superphos is a new promising type of concentrated phosphorus fertilizer with prolonged action. It is obtained by chemical enrichment and treatment with a mixture of sulfuric and phosphoric acids of phosphorite flour.

The acid consumption for the production of 1 t of P2O5 in superphos is 1–1.3 t of sulfuric and 0.36 t of phosphoric acid — 2 times less than for the production of 1 t of P2O5 of double superphosphate. At the same time, the use of P2O5 of phosphate raw material reaches 95%.

Superphos is produced in granulated form; it contains 38–40% P2O5, 19–20% of which is in water-soluble form. In effectiveness it is not inferior to double superphosphate.

Fertilizers containing phosphorus insoluble in water but soluble in weak acids

Semi-soluble (citrate-soluble) forms of phosphorus fertilizers are used on all soil types and for all crops, but their effectiveness can strongly depend on the soil type. On acidic soils, the action of fertilizers with an alkaline reaction, for example, Thomas slag and phosphate slag, may be higher than that of superphosphate.

Precipitate (dicalcium phosphate)

Precipitate, or dicalcium phosphate, calcium hydrophosphate, monocalcium phosphate — CaHPO4⋅2H2O. It is obtained by the interaction of orthophosphoric acid and milk of lime (calcium hydroxide solution) or a calcium carbonate suspension:

$$2H_3PO_4 + 2Ca(OH)_2 = 2CaHPO_4 \cdot 2H_2O;$$
$$H_3PO_4 + CaCO_3 + H_2O = CaHPO_4 \cdot 2H_2O + CO_2.$$

The amounts of the initial substances are taken in a ratio corresponding to the chemical reaction equation.

Precipitate is separated from the liquid and dried at a temperature not more than 100 °C to prevent losses of crystallization water, which promotes the solubility of precipitate.

The technology of precipitate production as a fertilizer is economically unjustified, therefore it is mainly used for feed purposes. As a fertilizer, it is obtained during the utilization of weak orthophosphoric acid solutions, which are wastes of other productions, for example, in gelatin production at bone-processing plants.

Precipitate for fertilizer is a white or light gray powder, non-caking and well spreadable. Depending on the initial raw material, it contains 25–35% citrate-soluble form of P2O5. Feed precipitate contains 44% P2O5, not more than 0.2% P, 0.001% As, and 0.002% Pb.

In its effect on yield it is analogous to superphosphate, but it is used only for main application under plowing in the same doses of P2O5 as superphosphate. On soils not saturated with bases and on sierozems, the effectiveness of precipitate is higher than that of superphosphate, due to the stronger binding of superphosphate phosphorus. On chernozems, the action of superphosphate is equal to or somewhat superior to the action of precipitate.

Defluorinated phosphate

Defluorinated phosphate, or calcium orthophosphate, tricalcium phosphate — Ca3(PO4)2 — contains 28–32% citric-soluble P2O5. By P2O5 content, the fertilizer belongs to concentrated phosphorus fertilizers.

It is obtained by thermal treatment of phosphate raw material. The process consists in treating with water steam a mixture of apatite or phosphorite with 2–3% silica (sand) at a temperature of 1400–1550 °C. Here the fluorine contained in apatite is separated in the form of hydrogen fluoride. The degree of defluorination reaches 94–96%.

Chemical reaction of hydrothermal decomposition of apatite in the presence of silica:

$$n \lbrack Ca_3(PO_4)_2 \rbrack_3 CaF_2 + mSiO_2 + nH_2O = 10nCaO \cdot 3nP_2O_5 \cdot mSiO_2 + nHF.$$

In the obtained product, depending on the raw material, it contains up to 30–32% (from apatite) or up to 20–22% (from phosphorite) citrate-soluble P2O5.

Defluorinated phosphate has good physical properties. As the main phosphorus fertilizer on soddy-podzolic and chernozem soils, it is not inferior to superphosphate in effectiveness.

Defluorinated phosphate is mainly used for mineral feeding of animals.

Thomas slag

Thomas slag, or fused magnesium phosphates, contains phosphorus in the form of tetracalcium phosphate (4CaO⋅P2O5 or Ca4P2O9) or silicocarnotite (Ca4P2O9⋅CaSiO3). According to technical specifications, the content of citric-soluble P2O5 should be not less than 14%. They occupy a small part among the phosphorus fertilizers used.

They are obtained as a by-product of processing phosphoric pig iron into iron and steel by the S. Thomas method. Since a phosphorus impurity reduces the quality of the metal, to remove it S. Thomas in 1879 proposed binding phosphorus with freshly burned lime. At a temperature of 1800–2000 °C, phosphorus oxidizes to P2O5; the binding of P2O5 leads to the formation of lime salts of phosphoric acid. These compounds, together with calcium silicate and other impurities, float to the surface of the molten metal in the form of slag, which is separated, after cooling crushed, ground, and in this form used as a phosphorus fertilizer.

With an excess of SiO2, a double salt of tetracalcium phosphate and calcium silicate — silicocarnotite — is formed; with a deficiency of SiO2, tetracalcium phosphate is formed. Both salts are soluble in 2% citric acid. Thomas slag also contains poorly soluble phosphates.

Thomas slag is a dark heavy powder; it contains from 7–8% to 16–20% citrate-soluble P2O5. As impurities, it contains calcium silicate, compounds of iron, aluminum, vanadium, magnesium, manganese, molybdenum, and others.

It is used as a main fertilizer. It is more effective on acidic soils, since it has an alkaline reaction.

When applied to the soil, as a result of interaction with soil moisture containing dissolved carbon dioxide (carbonic acid), it gradually decomposes with the formation of freshly precipitated tricalcium phosphate, which is available to plants.

Thomas slag is used on all soil types on which phosphorus fertilizers have a positive effect on yield, but its effectiveness on different soils manifests unequally. On chernozems it is weaker than superphosphate; on soils of the Non-Chernozem zone, especially acidic peaty and sandy soils, Thomas slag is more effective, since it reduces acidity. The neutralizing ability of Thomas slag matters when combining phosphorus fertilizers with physiologically acidic forms of nitrogen fertilizers.

Open-hearth phosphate slag

Open-hearth phosphate slag is obtained as a by-product in steel smelting from pig iron in open-hearth production. Lime materials are also used to bind phosphorus.

The phosphorus content in open-hearth slag is from 8 to 12% P2O5, almost all in citrate-soluble form. Phosphate slag contains a double salt of tetracalcium phosphate and calcium silicate, and impurities of iron, manganese, and magnesium compounds.

It is used as a main phosphorus fertilizer. It has a strongly alkaline reaction, therefore it is more suitable for acidic soils. Due to its low phosphorus content, it is advisable to use it near production sites.

Thermophosphates

Thermophosphates contain 18–34% P2O5; they are obtained by fusion or sintering of natural phosphates with carbonates or silicates of sodium or potassium, as well as metallurgical slags, lime, and quartz. Here hard-to-access forms of phosphorus pass into a citric-soluble form.

The melting temperature of thermophosphates is 1000–1200 °C. During high-temperature treatment, destruction of the crystal lattice of the phosphate raw material occurs, fluorine is released in the form of hydrogen fluoride, and phosphorus passes into the plant-available amorphous form Ca3(PO4)2. The amorphous form is obtained and remains stable at a temperature of 1180 °C. With a decrease in temperature, it passes into a crystalline, poorly assimilable form. Therefore, to reduce such a transition, the reaction mass is rapidly cooled.

In composition and properties, thermophosphates are similar to Thomas slag and can be applied on all soils. Thermophosphates obtained by fusion with alkaline salts are soluble in citric acid and ammonium citrate solution and have greater availability to plants than Thomas slag. The advantage of this method of phosphorus fertilizer production is that low-percentage phosphorites and apatites unsuitable in superphosphate production can be used as the initial raw material.

On acidic soils they have a stronger action than superphosphate, especially on podzolic soils.

Bone (bone) meal

Bone meal is a by-product of bone processing. Defatted bones are treated with steam under a pressure of 1.5–2 atm, followed by washing with water to extract glue. Defatted and deglued bone mass is obtained, which is treated with hydrochloric acid. Here the mineral substances Ca3(PO4)2 and Mg3(PO4)2 dissolve, and the soft bone skeleton consisting of ossein separates. When heated with water, ossein gives high-quality gelatin.

The hydrochloric acid solution of phosphates is treated with “milk of lime”; here the phosphates precipitate with the formation of precipitate according to the equation:

$$H_3PO_4 + Ca(OH)_2 = CaHPO_4 \cdot 2H_2O.$$

Defatted and deglued bone meal contains 30–35% P2O5 and up to 1% nitrogen. Phosphorus in bone meal is in a water-insoluble form, but it is more available than the phosphorus of phosphorite flour. The effectiveness of bone meal is influenced by soil acidity. Even in a weakly acidic environment, bone meal has a good effect on crop yield.

Fused magnesium phosphate

Fused magnesium phosphate contains 20% P2O5 in citric-soluble form and 12% MgO. It is obtained by fusion of phosphorite with silicate olivinite or serpentinite.

It is advisable to use it on sandy loam soils, where crops respond well to magnesium.

Red phosphorus

Red phosphorus contains 229% phosphorus calculated as P2O5. It is a promising high-concentrated phosphorus fertilizer. To convert it into a plant-available form in the soil, a catalyst is used simultaneously, for example, copper, about 1% of the phosphorus mass.

On soddy-podzolic soil, 3 weeks after incorporation, 20% of red phosphorus passes into compounds available to cereal crops. In effectiveness it is not inferior to superphosphate; in aftereffect it is superior to it.

Garshinka

Fertilizers containing phosphorus poorly soluble in weak acids but soluble in strong acids

Poorly soluble fertilizers have a sufficiently good action on acidic soils of the Non-Chernozem zone and on soils of the northern part of the Chernozem zone (leached and podzolized chernozems).

Phosphorite flour

Phosphorite flour is finely ground phosphorite. It is used as a fertilizer on acidic soddy-podzolic, gray forest, and peaty soils, on podzolized and leached chernozem soils, and on red soils. On typical, ordinary, and southern chernozems, the action of phosphorite flour is weaker and unstable.

Phosphorite flour is the cheapest fertilizer. By volume of production and use, it occupies second place after superphosphate. Production is reduced to separating coarse impurities (sand, clay) from the phosphate raw material, crushing into pieces 1–3 cm, and grinding to fine flour. The fineness of grinding of phosphorite flour affects its effectiveness. According to technical specifications, not less than 80% of the mass of phosphorite flour should have a particle size less than 0.17 mm.

As raw material, nodular, often low-percentage phosphorites, without a pronounced crystal structure, are used. When grinding such raw material, flour is obtained suitable for direct application but poorly suitable for chemical processing. Such phosphorites include raw material obtained at the Yegoryevskoye, Shchigrovskoye, Seshchinskoye, Krylkovetskoye, and Kineshma deposits.

Phosphorite flour is a powder of gray, dark gray, or brown color. The P2O5 content in fertilizer of the first grade is 28–30%, of the second, 22–24%, and of the third, 19–21%. The fertilizer is non-hygroscopic, non-caking, well spread, and strongly dusty.

Phosphorus in phosphorite flour is contained in the form of fluorapatite — [Ca3(PO4)2]3CaF2, which is insoluble in water and poorly soluble in weak acids, therefore poorly available to most plants.

The effectiveness of phosphorite flour is influenced by the origin and composition of phosphorites, fineness of grinding, biological features of crops, soil properties, and the acidity of accompanying fertilizers.

Phosphorite flour interacts with soil having actual and potential acidity, with gradual decomposition of calcium phosphate and its transformation into dicalcium phosphate:

$$Ca_3(PO_4)_2 + 2H_2О + 2CO_2 \to 2CaHPO_4 + Ca(HCO_3)_2.$$

According to studies, soils with hydrolytic acidity less than 2.5 mg⋅eq/100 g poorly decompose phosphorite, therefore its effectiveness on such soils is low. Conversely, the higher the hydrolytic acidity, the more effective the action of phosphorite flour. This explains the positive action of phosphorite flour on degraded and leached chernozems, where exchangeable acidity is small but hydrolytic acidity is high.

Soils with a small absorption capacity at hydrolytic acidity of 3–3.5 mmol/100 g soil and base saturation of 50–60%, as a rule, have an acidic reaction (5.0–5.5), which is due to exchangeable acidity. At a large absorption capacity, hydrolytic acidity equal to 6–7 mmol/100 g soil, and degree of saturation of 75–85%, the reaction is close to neutral (6.0–6.5). Therefore, a high action of phosphorite flour will manifest at high acidity and a lower degree of soil saturation with bases.

The action of phosphorite flour is influenced by the absorption capacity and degree of saturation with bases of the soil. At the same hydrolytic acidity, effectiveness increases with a decrease in absorption capacity.

With an increase in the fineness of grinding, the total surface of interaction of phosphorite flour with the soil increases.

Table. Effect of fineness of grinding of phosphorite flour on its effectiveness (A. N. Lebedyantsev).

Average particle size, mmRelative increase
number of particlesparticle surface areaeffectiveness
0.510111
0.220122.32.2
0.0921705.53.6
0.041192012.44.9
0.0051061200102.06.0

The effectiveness of phosphorite flour depends on the biological features of plants. The results of experiments by D. N. Pryanishnikov, P. S. Kossovich, and other scientists allowed agricultural crops to be divided into groups by their ability to assimilate phosphorus from poorly soluble phosphates. Plants with a good ability to assimilate poorly soluble phosphates include lupine, buckwheat, and mustard; somewhat less so pea, sainfoin, sweet clover, and hemp. All cereals, flax, beet, potato, and vetch can assimilate phosphorus from phosphorite flour only after interaction with acidic soils. They do not assimilate phosphorus of phosphorite flour: barley, spring wheat, flax, millet, tomato, and turnip.

The ability of plants to assimilate poorly soluble phosphates changes with age. Most plants poorly assimilate hard-to-access forms in the first period of life; later this ability increases.

Most scientists explain the ability to assimilate poorly soluble phosphates by the quantity and composition of acid root exudates of plants. F. V. Chirikov explains this ability by increased calcium consumption: plants absorbing more calcium better assimilate phosphorus.

The assimilation of phosphorus from phosphorite flour, as established by D. N. Pryanishnikov, also depends on accompanying fertilizers: physiologically acidic fertilizers increase phosphorus availability; physiologically alkaline fertilizers and lime materials reduce it.

Phosphorite flour became widespread in the countries of the former USSR. Probably in the future its use will expand. The disadvantage of phosphorite flour is that it is very dusty. To reduce dusting, the following may be used:

  • mixtures of phosphorite flour with ammonium chloride in a ratio N:P2O5 = 1:1; here the content of each nutrient is 14%, dustiness is eliminated, and the content of citric-soluble phosphorus increases 1.5 times;
  • treatment of phosphorite flour with molten potassium disulfate at a temperature of 205–210 °C for 50–60 minutes in a screw mixer: dustiness is eliminated, the P2O5 content is 16%, of which 70% is in citric-soluble form, and the K2O content is up to 17%.

The effectiveness of phosphorite flour is influenced by the geological age and mineralogical composition of phosphorite. Phosphorites of ancient origin with a crystalline structure are characterized by poor availability to plants, especially apatite.

To increase availability, phosphorite flour is composted with high-moor peat or manure. In composts, effectiveness increases with acidic peat at a ratio of peat to flour of 100:1. Phosphorite flour is used for preparing peat-manure and manure-phosphorite composts.

Phosphorite flour, for better decomposition, is applied in advance under deep plowing into a moistened layer. Application in double or triple doses has a long aftereffect.

In Russia, acidic soils under arable land occupy about 50 million ha. They, as a rule, are characterized by a low content of mobile phosphorus.

Vivianite (bog ore)

Vivianite, or bog ore, ferrous phosphate — Fe3(PO4)2⋅8H2O. It contains 28% P2O5. It occurs under a peat layer in the form of a whitish mass.

It is a good source of phosphorus for crops on soddy-podzolic, gray forest soils, and leached chernozems. Vivianite easily loosens when drying and spreads well.

Phosphoritization

Phosphoritization — the application of poorly soluble phosphates (phosphorite flour) in crop rotation for several years ahead — is one of the methods of increasing soil fertility, especially of acidic soils, the effectiveness of mineral fertilizers, and increasing crop yields. Phosphorite flour is applied in large doses up to 1–1.5 t/ha, which provides phosphorus nutrition to plants for 6–8 years, improves the nutrient regime, and increases the productivity of the crop rotation.

Improvement of the phosphate regime leads to an increase in the effectiveness of other fertilizers. Phosphoritization is a reclamation method of increasing the fertility of acidic soils, the effectiveness of which depends on acidity and the supply of mobile phosphorus. First of all, phosphoritization is carried out at pH below 5.5 and a content of mobile phosphorus up to 5 mg/100 g soil.

Phosphoritization in crop rotation is optimally carried out in fallow for winter crops and cereals with undersowing of leguminous grasses, which are able to assimilate poorly soluble phosphorus, better accumulate nitrogen, and contribute to increasing the productivity of subsequent crops in the rotation.

Phosphoritization is used for radical improvement of meadows and pastures. Here the application of lime and phosphorite flour is carried out separately, for example, before plowing and after it, into different soil layers.

Phosphoritization is a mandatory method of improving newly developed low-fertility lands, during drainage, development of peatlands, and low-fertility acidic meadows on mineral soils. The norms of phosphorite flour application are not less than 200 kg P2O5, or 1 t of flour. For a more accurate calculation of the dose, standards of nutrient consumption for increasing mobile phosphorus by 1 mg/100 g soil are used.

Table. Fertilizer rates to increase mobile phosphorus content by 10 mg P2O5/kg soil (after Litvak Sh. I., 1990; Sychev V. G., Shafran S. A., 2013).

SoilParticle-size compositionDetermination methodFertilizer consumption, kg/ha
data variationstandard rate
Soddy-podzolicsandy and sandy loamby Kirsanov47–9050–70
light loam60–10870–80
medium loam60–11080–90
heavy loam90–120100–110
Gray forestsandy and sandy loamby Kirsanov70–8070–80
loamy80–11090–110
heavy loam120–140120–140
Podzolized chernozemlight loamby Chirikov74–10990–100
loam80–120100–110
Leached chernozemheavy loamby Chirikov90–135110–120
Typical chernozemheavy loamby Chirikov103–141120–130
Ordinary chernozemloamby Chirikov94–122100–110
heavy loam100–140120–130
Carbonate chernozemsaverageby Machigin—110–120
Chestnut soilsaverageby Machigin—90–110

Example.

Initial data: soil soddy-podzolic sandy loam; pH 4.5; content of mobile phosphorus 4.6 mg/100 g soil; planned — 9 mg/100 g soil.

The dose of phosphorite flour is determined by the formula:

$$Д = (В - А) \cdot С,$$

or

$$Д = (9,0 - 4,6) \cdot 60 = 264\ кг\ P_2O_5/га,$$

where

Д
— dose, kg/ha P2O5;
В
— planned level of content, mg P2O5/100 g soil;
А
— actual content, mg P2O5/100 g soil;
С
— consumption of P2O5 for increasing its content by 1 mg/100 g soil.
Максидом

Interaction of phosphorus fertilizers with soil

The solubility of phosphorus fertilizers, including water-soluble ones, is lower than that of nitrogen and potassium fertilizers. When applied to the soil, as dissolution proceeds, the phosphate ion passes into compounds characteristic of a certain soil type and caused by genetic features, physicochemical and mineralogical properties, and degree of cultivation. The rate of this process is slow, therefore part of the applied phosphorus fertilizers, especially in granulated form or in semi-soluble and insoluble forms, remains unchanged for a long time.

The transformation of soluble phosphorus of fertilizers may be due to:

  • chemical absorption of phosphate ions by cations of calcium, magnesium, oxides and hydroxides of iron, aluminum, manganese, and titanium;
  • colloid-chemical (exchange) absorption on the surface of the solid phase of the soil;
  • biological absorption by root systems of plants and soil microflora.

Exchange absorption (adsorption) of phosphate ions occurs on the surface of positively charged colloidal particles, for example, colloids of hydrates of sesquioxides, or on positively charged areas of negatively charged colloids, for example, on minerals of the kaolinite and montmorillonite groups and hydromicas, and colloids of the protein group. Exchange absorption is stronger in an acidic environment. For example, illite (a mineral of the hydromica group), bentonite (montmorillonite group), and kaolinite adsorbed at pH 4–4.5 from 7.7 to 9.7 mg⋅eq H2PO4- per 100 g of mineral. Significant differences in the absorption of anions by minerals of the montmorillonite and kaolinite groups, as in the case of exchange absorption of cations, were not noted. The reaction of the medium leads to a change in the electric potential of soil colloids. Acidification of the soil solution promotes better absorption of anions; alkalinization, conversely, causes a decrease in absorption. Therefore, for soils with a weakly acidic and neutral reaction, exchange absorption is weaker (Antipov — Karataev et al.):

SoilAdsorbed PO43- from 0.05 N H3PO4, meq/100 g soil
Chernozem18.3
Podzolic41.9
Krasnozem74.0

Exchange absorption of phosphate ions on ordinary chernozem of the Kamennaya Steppe is also confirmed by I. P. Serdobolsky.

According to data of VNIIUA, adsorption absorption by soddy-podzolic soils is 70–80% of the total amount of absorbed phosphates.

Exchange-absorbed anions of phosphoric acid can be displaced into solution (desorption) by other anions of mineral and organic acids, for example, bicarbonate ion, citric, malic, oxalic, formic, and humic acids. These anions are always present in the soil solution as a result of the respiration of plants and their root exudates, as well as the microbiological decomposition of plant residues and organic fertilizers. Thus, there is no shortage of anions for the desorption of phosphates. This determines the good mobility and availability to plants of exchange-absorbed phosphates. According to research results, the availability of exchange-absorbed phosphates is close to that of water-soluble phosphates. However, there are few of the latter in the soil solution, therefore it is exchange-absorbed phosphates that play an important role in phosphorus plant nutrition.

Part of the fertilizer phosphates dissolved in the soil solution is absorbed by the soil due to chemical binding. The features of chemical absorption are determined by the soil type and its acidity.

The value of pH of the soil determines the solubility of salts of calcium, magnesium, aluminum, iron, manganese, and titanium, which, upon interaction with water-soluble phosphates, convert it into poorly soluble compounds. For example, at pH less than 5, the content of aluminum ions increases in the soil, and at pH less than 3, iron ions. It is generally considered that the least binding of phosphates and the greatest mobility occur in the interval pH 5.0–5.5. On more acidic soils, absorption by aluminum and iron oxides occurs; on less acidic soils, by calcium and magnesium.

Thus, on soils with a near-neutral reaction medium, water-soluble phosphorus fertilizers — monophosphates [(Ca(H2PO4)2⋅H2O] — after some time turn, due to chemical absorption, into disubstituted calcium and magnesium phosphates (CaHPO4⋅2H2O or MgHPO4) and remain for a long time in a plant-available form. Subsequently, a gradual replacement of the hydrogen of the disubstituted salt by calcium or magnesium occurs with the formation of trisubstituted phosphates Ca3(PO4)2, Mg3(PO4)2, and later also basic phosphates, octacalcium phosphate [Ca4Н(PO4)3⋅3H2O]; solubility constantly decreases.

However, while these salts are in a freshly precipitated amorphous state, they retain the property of dissolving in weak acids, which causes some availability to plants. Only as trisubstituted and basic phosphates crystallize (“age”) do they lose the property of availability. The process of “aging” of phosphates is called retrogradation of phosphates.

In soddy-podzolic soils with an acidic and weakly acidic reaction, the chemical binding of phosphate ions is due to mobile sesquioxides:

$$Al(OH)_3 + H_3PO_4 \to AlPO_4 + 3H_2O;$$
$$Fe(OH)_3 + H_3PO_4 \to FePO_4 + 3H_2O.$$

Freshly precipitated amorphous phosphates of aluminum and iron also remain available to plants for some time, but as they “age” they become insoluble. Chemical absorption affects both water-soluble phosphates of fertilizers and phosphates that have passed into solution from the exchange-absorbed state as a result of desorption.

The intensity of chemical and colloid-chemical absorption of fertilizer phosphates is directly dependent on the content of mobile forms of sesquioxides. Phosphoric acid, as a result of biological absorption, is able to become fixed in the soil, in the body of microorganisms. By the energy of absorption of phosphates of soluble fertilizers, soils can be arranged in the following sequence: krasnozems > podzolic soils > chernozems > sierozems.

The process of absorption of fertilizer phosphates by the soil and further transformation proceed very slowly. The experience of long-term application of high doses of phosphate fertilizers several times exceeding P2O5 removal showed that most phosphorus accumulates in soils in an easily soluble form in amounts up to 600–1000 mg/kg soil.

Here phosphating of soils occurs. This phenomenon is noted in a number of European countries that used phosphorus fertilizers for more than a century. In the late 1980s, phosphating also occurred in Russia in the sugar beet zone and in some farms of Moscow Oblast.

Field and vegetation experiments showed that “residual,” that is, previously unused, phosphorus of fertilizers remains available to plants. Thus, aftereffects of previously applied phosphorus fertilizers at Rothamsted Experimental Station are noted for more than 50 years.

These experiments show that “dead” fixation of phosphates in the soil in significant amounts does not occur. There is information about the possibility of mobilization of phosphate resources of soils under conditions of phosphorus fertilizer deficiency. Here a gradual transformation of poorly soluble phosphates into soluble ones occurs.

However, long-term cultivation of crops under conditions of phosphorus fertilizer deficiency leads to depletion of soil reserves and their gradual degradation.

Application of phosphorus fertilizers

Main page: Application of phosphorus fertilizers

АгроСемФонд

Effectiveness of phosphorus fertilizers

Main page: Effectiveness of phosphorus fertilizers

List of sources

  1. B. A. Yagodin, Yu. P. Zhukov, V. I. Kobzarenko (2002). Agrochemistry. Ed. B. A. Yagodin. Moscow: Kolos.
  2. Yu. V. Evtefeev, G. M. Kazantsev (2013). Fundamentals of Agronomy: textbook. Moscow: FORUM.
  3. V. G. Mineev, V. G. Sychev, G. P. Gamzikov et al. (2017). Agrochemistry. Textbook. Ed. Mineev V. G. Moscow: Publishing House VNIIA named after D. N. Pryanishnikov.