WO2005118222A2 - Phosphogypsum treatment process - Google Patents

Phosphogypsum treatment process

Info

Publication number
WO2005118222A2
WO2005118222A2 PCT/US2005/018980 US2005018980W WO2005118222A2 WO 2005118222 A2 WO2005118222 A2 WO 2005118222A2 US 2005018980 W US2005018980 W US 2005018980W WO 2005118222 A2 WO2005118222 A2 WO 2005118222A2
Authority
WO
WIPO (PCT)
Prior art keywords
organic acid
calcium
ammonium
reacting
salt
Prior art date
Application number
PCT/US2005/018980
Other languages
French (fr)
Other versions
WO2005118222A3 (en
Inventor
Xiangsheng Meng
Lawrence A. Peacock
Paraskevas Tsobanakis
Ronald E. Olson
Donald R. Clark
Charles Sanderson
Original Assignee
Cargill, Incorporated
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Cargill, Incorporated filed Critical Cargill, Incorporated
Publication of WO2005118222A2 publication Critical patent/WO2005118222A2/en
Publication of WO2005118222A3 publication Critical patent/WO2005118222A3/en

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01FCOMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
    • C01F11/00Compounds of calcium, strontium, or barium
    • C01F11/46Sulfates
    • C01F11/468Purification of calcium sulfates
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B25/00Phosphorus; Compounds thereof
    • C01B25/16Oxyacids of phosphorus; Salts thereof
    • C01B25/26Phosphates
    • C01B25/28Ammonium phosphates
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B25/00Phosphorus; Compounds thereof
    • C01B25/16Oxyacids of phosphorus; Salts thereof
    • C01B25/26Phosphates
    • C01B25/32Phosphates of magnesium, calcium, strontium, or barium
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01CAMMONIA; CYANOGEN; COMPOUNDS THEREOF
    • C01C1/00Ammonia; Compounds thereof
    • C01C1/02Preparation, purification or separation of ammonia
    • C01C1/026Preparation of ammonia from inorganic compounds
    • C01C1/028Preparation of ammonia from inorganic compounds from ammonium sulfate or sulfite
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01CAMMONIA; CYANOGEN; COMPOUNDS THEREOF
    • C01C1/00Ammonia; Compounds thereof
    • C01C1/24Sulfates of ammonium
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01CAMMONIA; CYANOGEN; COMPOUNDS THEREOF
    • C01C1/00Ammonia; Compounds thereof
    • C01C1/24Sulfates of ammonium
    • C01C1/244Preparation by double decomposition of ammonium salts with sulfates
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/10Process efficiency

Definitions

  • Phosphoric acid which is a source material for producing phosphates such as calcium phosphate, is produced by a conventional wet process in which sulfuric acid is used to treat a fine phosphate rock as shown in the following reaction. (Reaction 1).
  • the phosphate rock contains several impurities including uranium.
  • the impure gypsum cannot be used commercially unless the uranium in the gypsum is reduced to an acceptable level.
  • the gypsum produced in the fertilizer and phosphoric acid plants from the phosphate rock, such as shown in Reaction 1 is piled on the ground according to such conventional process.
  • a very large pile of the gypsum on the ground is referred to as a "gypsum stack.” Since, the impure gypsum produced from Reaction 1 cannot be used as a calcium resource, an extra calcium resource such as lime (calcium hydroxide) has to be used in order to produce feed grade phosphate (calcium phosphate).
  • the phosphoric acid obtained from the wet process described in Reaction 1 is reacted with lime to produce calcium phosphate according to the conventional process.
  • the conventional process there is no method of using calcium in the phosphogypsum to produce among other useful products.
  • DISCLOSURE OF THE INVENTION To address the above and/or different concerns, the inventors propose a method of treating phosphogypsum, which produces calcium carbonate and ammonium sulfate from the phosphogypsum.
  • the calcium carbonate contains impurities from the phosphogypsum.
  • the calcium carbonate is reacted with an organic acid to produce a liquid calcium salt of the organic acid and un-reacted solid impurities.
  • the calcium salt of the organic acid is consumed through at least one of two processes.
  • the calcium salt of the organic acid may be reacted with phosphoric acid to produce calcium phosphate.
  • the calcium salt of the organic acid may be reacted with the ammonium sulfate to produce the ammonium salt of the organic acid and gypsum, the ammonium salt of the organic acid being reacted with the phosphoric acid to produce ammonium phosphate.
  • the gypsum produced in the second process may have a reduced impurity level relative to phosphogypsum and so be useful in traditional gypsum applications.
  • the calcium salt of the organic acid may also be consumed in a reaction with sulfuric acid to produce gypsum.
  • the process of reacting the ammonium salt of the organic acid with the phosphoric acid will reproduce the organic acid, which can be recycled to react with the calcium carbonate.
  • the calcium salt of the organic acid is reacted with phosphoric acid to produce calcium phosphate
  • there is excess ammonium sulfate when the calcium salt of the organic acid is reacted with phosphoric acid to produce calcium phosphate, there is excess ammonium sulfate.
  • the excess ammonium sulfate may be reacted with calcium hydroxide to produce gypsum, which has a reduced impurity level relative to the phosphogypsum.
  • ammonia may be produced, in which case, the ammonia may be used to produce the calcium carbonate and ammonium sulfate from the phosphogypsum.
  • the inventors also propose to treat phosphogypsum, by (i) producing calcium carbonate and ammonium sulfate from the phosphogypsum through a reaction with ammonium carbonate, the calcium carbonate containing impurities from phosphogypsum, (ii) reacting calcium carbonate with an ammonium salt of an organic acid to produce a liquid calcium salt of the organic acid and un-reacted solid impurities, and (iii) reacting the calcium salt of the organic acid with the ammonium sulfate to produce the ammonium salt of the organic acid and gypsum.
  • the ammonium salt of the organic acid may be recycled for reaction with the calcium carbonate.
  • the calcium salt of the organic acid may be produced by reacting calcium carbonate with the ammonium salt of the organic acid, at a temperature of 60 degree C or higher.
  • the inventors further propose purifying impure gypsum by (i) reacting the impure gypsum with an ammonia-carbon dioxide source, producing ammonium sulfate and calcium carbonate, (ii) reacting the ammonium sulfate with a calcium salt of an organic acid and water, producing substantially purified gypsum and the ammonium salt of the organic acid, and (iii) reacting the ammonium salt of the organic acid with the calcium carbonate, producing ammonium carbonate, which is recycled back to react with the impure gypsum and the calcium salt the organic acid, which is recycled back to react with the ammonium sulfate.
  • Uranium may be removed from an impure, uranium-containing gypsum, by (i) reacting the uranium-containing gypsum with an ammonia-carbon dioxide source, producing calcium carbonate, and (ii) reacting an ammonium salt of an organic acid with the calcium carbonate to produce a liquid, a gas, and a uranium-concentrated solid.
  • the inventors propose producing calcium phosphate by (i) reacting calcium carbonate with an organic acid to produce the calcium salt of the organic acid, (ii) reacting phosphoric acid and the calcium salt of the organic acid, producing calcium phosphate and the organic acid, which is recycled back to react with calcium carbonate, and (iii) reacting the ammonium sulfate with lime, producing substantially purified gypsum and ammonia.
  • the calcium carbonate may be produced by reacting impure gypsum with an ammonia-carbon dioxide source, producing ammonium sulfate and calcium carbonate. It is also an aspect of the present invention to provide an integrated process for producing feed grade phosphates while substantially reducing the amount of gypsum waste generated.
  • a calcium salt of an organic acid is produced when calcium carbonate produced from phosphogypsum is reacted with the organic acid.
  • substantially pure phosphoric acid is produced that is substantially free of impurities found in phosphate rock. It is another aspect of the present invention to produce calcium phosphate by reacting the phosphoric acid produced from phosphate rock with the calcium salt of the organic acid.
  • substantially purified gypsum being substantially free of uranium is produced by reacting the ammonium sulfate and the calcium salt of the organic acid.
  • ammonium phosphate is produced by reacting the phosphoric acid from phosphate rock and an ammonium salt of the organic acid.
  • calcium phosphate is produced by reacting the ammonium phosphate with the calcium salt of the organic acid.
  • the organic acid is produced and replenished in the process by reacting the phosphoric acid produced from phosphate rock with the ammonium or calcium salt of the organic acid.
  • radioactive materials such as uranium may be efficiently removed from the impure gypsum produced in Reaction 1 , without consuming substantially any extra chemicals in the overall phosphate production process.
  • Fig. 1 is a flow diagram showing a process for producing phosphoric acid.
  • Fig. 2 is a flow diagram of a process for treating phosphate rock to produce useful chemicals, according to a first aspect of the invention.
  • Fig. 3 is a schematic drawing of a reactor and associated components, which reactor is shown in Fig. 2.
  • Figs. 4A and 4B are schematic views of alternate embodiments for the settling velocity filter shown in Fig. 1.
  • Fig. 5 shows a flow diagram for a process for treating phosphate rock, according to a second aspect of the invention.
  • Fig. 6 is a flow diagram of a first alternative embodiment for the process shown in
  • Fig. 7 is a flow diagram of a third alternative embodiment for the process shown in Fig. 2.
  • Fig. 1 is a flow diagram showing a process for producing phosphoric acid. Reaction 1 , which is repeated below, occurs in Fig. 1. Ca 5 F(PO 4 ) 3 + 5H 2 S0 4 + 10H 2 O -» 5CaS0 4 -2H 2 O j + 3H 3 PO 4 + HF (1) Reaction 1 shows phosphate rock being reacted with sulfuric acid.
  • Reaction 1 is performed as two separate reactions, Reactions
  • Fig. 1 shows the reaction of sulfuric acid as having six stages. After the sixth stage, a portion of the phosphoric acid/phosphogypsum slurry is recycled to the first reactor while the balance is filtered to separate the product phosphoric acid from the calcium sulfate in a filter feed tank. Calcium sulfate is subjected to three filtration stages with counter-current washing before repulping.
  • a dilute phosphoric acid is separated from phosphogypsum and recycled back to the first reactor for Reaction 1a.
  • the phosphogypsum is repulped with water.
  • Fig. 2 is a flow diagram of a process for treating phosphate rock to produce useful chemicals, which expands upon the phosphoric acid process shown in Fig. 1.
  • the phosphate rock after being finely ground, is sent to a pretreatment area.
  • the phosphate rock is soaked in phosphoric acid.
  • Reaction 1a occurs in the pretreatment area, as discussed above. From pretreatment, the produced calcium phosphate is sent to Reactor 1.
  • Reactor 1 sulfuric acid is added.
  • Reaction 1 b occurs in Reactor 1 in a manner similar to that shown in Fig. 1.
  • the pretreatment area corresponds with the H 3 PO 4 acid attack tank shown in Fig. 1.
  • Reactor 1 corresponds with the H 2 S0 4 acid attack tank shown in Fig. 1.
  • Fig. 1 shows 6 stages for the phosphoric acid and sulfuric acid reactions. A staged reaction is not shown in Fig. 2 for simplicity. A staged reaction is certainly possible.
  • the process that occurs in Fig. 2 produces a slurry of dihydrated calcium sulfate
  • Reactors 2 and 3 The purpose of Reactors 2 and 3 is to treat the impure gypsum with an ammonia-water solution in the presence of carbon dioxide (Reaction 2). In Reactors 2 and 3, at least one of the following Reactions 2-4 occurs.
  • Stream 32 may be a liquid, which is sent to Reactor 2.
  • Reactors 2 and 3 serve as a counter current reaction mode to react the gypsum.
  • Calcium sulfate is gradually converted to calcium carbonate.
  • stream 22 exits Reactor 2 having maximum purity ammonium sulfate
  • stream 34 exits Reactor 3 having maximum purity calcium carbonate.
  • a quantitative conversion from CaSO 4 to (NH 4 ) 2 SO 4 can be reached in about 50 min at room temperature. To do this, in Reactor 2, the remaining excess ammonia and C0 2 (ammonium carbonate or ammonium bicarbonate) in stream 32 is reacted with fresh gypsum from filter 15 to produce ammonium sulfate.
  • the product stream 22 contains ammonium sulfate.
  • Reactor 3 has excess ammonia and CO 2 , all remaining gypsum in the stream 24 is converted to ammonium sulfate. With Reactors 2 and 3, the quantitative conversion from CaSO to (NH ) 2 SO 4 is reached.
  • Reactor 2 can be a stirred reactor. On a batch scale, all remaining excess ammonia and CO 2 in stream 32 may be reacted after approximately 30 min of mixing. According to an alternative embodiment, these conditions can also be utilized in a continuous process.
  • the ammonium sulfate exits Reactor 2 via stream 22.
  • the ammonium sulfate in stream 22 is sufficiently pure to have commercial use outside the process shown in Fig. 2. That is, stream 22 contains substantially no free ammonia or ammonium carbonate or ammonium bicarbonate.
  • the solids produced in Reactor 2 are a mixture of calcium sulfate and calcium carbonate.
  • the solids exit Reactor 2 in stream 24.
  • the calcium sulfate and calcium carbonate are treated with a fresh ammonia solution in presence of carbon dioxide gas, as discussed above, in Reactor 3.
  • the quantitative conversion changes all of the calcium sulfate to ammonium sulfate.
  • the solids from Reactor 3 (calcium carbonate and impurities) exit via stream 34.
  • the solids in stream 34 may be treated with 3-hydroxypropionic acid (3-HP), HOCH 2 CH 2 CO 2 H according to a preferred embodiment.
  • 3-HP is an organic acid, which reacts with calcium carbonate to form calcium 3-hydroxypropionate and releases carbon dioxide gas and water. This reaction is shown below as Reaction 5, which occurs in Reactor 5.
  • Reaction 5 is an acid-base reaction, which is likely to proceed to the right hand side of the equilibrium rapidly and C0 2 is removed. Carbon dioxide gas from Reactor 5 is sent to Reactor 3 via stream 52. One embodiment for Reactor 5 is shown in more detail in Fig. 3. Reaction 5 occurs as in Reactor 5A. Solids and liquids exit Reactor 5A via stream 58. A gas stream 55 is sent to an adsorption column 5B. In column 5B, carbon dioxide is collected or trapped by an ammonia water solution, which enters via stream 56.
  • Stream 52 from adsorption column 5B contains carbon dioxide, ammonia and water (or ammonium carbonate or ammonium bicarbonate), and is sent to Reactor 3. Although stream 56 is necessary, it is not shown in Fig. 2.
  • Stream 52 is used as the ammonia source for Reactor 3.
  • Fig. 3 shows adsorption column 5B, it is possible to run the process without carbon dioxide adsorption.
  • Gas stream 55 contains primarily carbon dioxide. Instead of supplying Reactor 3 via stream 52, carbon dioxide can be supplied as a gas, from gas stream 55 to Reactor 3. In this case, the ammonia source from stream 56 is lost. Therefore, a separate ammonia stream must be introduced into Reactor 3 together with the carbon dioxide stream 55.
  • Stream 55 is a gas, and the ammonia source for Reactor 3 may also be a gas. These two gases could be supplied separately or combined before introduction into Reactor 3. If gaseous, the carbon dioxide and ammonia are bubbled through Reactor 3. With adsorption column 5B, Reactor 3 is supplied with stream 52, which is at least partially a liquid. Without adsorption column 5B, Reactor 3 may be supplied with a gas. In either case, Reactor 3 is supplied with carbon dioxide and ammonia. In addition to adsorbing carbon dioxide, adsorption column 5B may also function as a reservoir.
  • the solids in stream 16 may include gypsum and 5 wt.% to 10 wt.% impurities. If stream
  • Reaction 6 One use is adding the calcium 3-HP into a phosphoric acid solution to produce calcium phosphate precipitates and release 3-HP according to Reaction 6 below.
  • Reaction 6 occurs in Reactor 6.
  • the released 3-HP exits Reactor 6 on stream 61.
  • Stream 61 is sent to Reactor 5 along with stream 34 for Reaction 5.
  • One product of Reactor 6 is CaHPO 4 .
  • Reactor 6 is supplied with phosphoric acid on stream 62. This stream is labeled “Pure H 3 PO 4 ".
  • the phosphoric acid produced in the wet process (Reaction 1) is not pure.
  • the phosphoric acid contains HF, H 2 SiF 6 and H 3 AIF 6 .
  • stream 63 from Reaction 1 is sent to Reactor 6/7/8 in which Reactions 6, 7, 8 and 8A occur. Reaction 6 is shown above, and Reactions 7, 8 and 8A are shown below.
  • stream 65 contains the products of Reaction 6/7/8.
  • Reaction 6 competes with Reactions 7, 8 and 8A for the calcium 3-HP, Reaction 6 is not substantially completed in Reactor 6/7/8.
  • stream 65 also contains phosphoric acid.
  • Filter 68 can be used to separate the liquids from the solids.
  • the solids exit filter 68 via stream 67 and include CaHPO 4 , CaF 2 , Si0 2 and AIP0 4 .
  • Reactor 6/7/8 may be a key component in the separation. Together with filter 68, separation may be performed based on the differences in settling velocities of the precipitates.
  • CaF 2 forms fine solid particles, which stay in suspension and do not readily precipitate.
  • AIP0 4 forms the flake-like precipitates that also exist in suspension. If this behavior occurs in this system, then AIPO 4 may have a higher settling velocity than CaF 2 .
  • CaHP0 4 forms large crystalline precipitates that easily settle. CaHP0 4 therefore has the highest settling velocity.
  • Fig. 4A is a schematic view showing how Reactor 6/7/8 and filter 68 work together to perform
  • Reactions 6, 7 and 8 and separate the products thereof.
  • Reaction 8A removes H 2 SiF 6 by converting H 2 SiF 6 to SiO 2 .
  • SiO 2 may be produced and separated using Reactor 6/7/8 and filter 68. However, the production and separation is not shown in Fig. 4A. Together, Reactor 6/7/8 and filter 68 form a gravity filter.
  • Fig. 4A shows an embodiment where filter 68 is embodied as two filters, filter 68a and filter 68b.
  • a belt filter or a centrifuge can be used as the filters 68a, 68b for streams 65a, 65b.
  • two filters are shown in Fig. 4A, it may not be necessary to separate the calcium fluoride from the aluminum phosphate. Both can be treated as impurities.
  • Silicon dioxide which is not shown in Fig. 4A, may be removed together with CaF 2 and AIPO 4 in this single filter 68 according to an alternative embodiment. In this case, streams 65a and 65b would be combined, and a single filter 68 would be used to separate phosphoric acid from impurities.
  • liquid from streams 105/63 and 57 can be added to a liquid capacity of about 90 % of the total volume of the reactor 6/7/8.
  • Fig. 4A shows streams 57 and 105/63 supplying Reactor 6/7/8 at an upper portion thereof. The place of liquid introduction is not restricted to an upper portion.
  • Reactor 6/7/8 he solids with a higher settling velocity proceed to the bottom of the Reactor.
  • Aluminum phosphate a flake-like precipitate, has a lower settling velocity than calcium phosphate.
  • Aluminum phosphate exits Reactor 6/7/8 from a middle portion, at stream 65b.
  • Calcium fluoride a fine solid, has the lowest settling velocity.
  • Fig. 4A shows liquid phosphoric acid being removed from Reactor 6/7/8 via filters 68a and 68b. In a gravity reactor/filter, perhaps the bottom 10 % of the volume contains mainly the heavier solids, CaHP0 4 . Other configurations are of course possible.
  • Fig. 4B is an alternate embodiment to the embodiment shown in Fig. 4A.
  • CaHP0 4 is a commercially valuable chemical.
  • Calcium phosphate which may be the heaviest solid may exit as a slurry. The calcium phosphate could be separated from stream 62c with a filter, in the same manner as the separation for CaF 2 and AIPO 4 .
  • Reactor 6 is designed for producing calcium phosphate.
  • the CaHPO slurry in stream 62c of Fig. 4A could be combined with the phosphoric acid solution (stream 62) obtained from the filters 68a and 68b and sent to Reactor 6 to produce calcium phosphate (Reaction 6).
  • Reactors 6/7/8 and 6 use calcium 3-HP as a calcium source.
  • Reaction 9 occurs in Reactor 9.
  • Reactor 9 represents a third use for the calcium 3-HP produced in Reactor 5, exiting via stream 57. In Reactor 9, Reaction 9 proceeds quickly. On a batch scale, calcium sulfate is produced almost immediately after calcium
  • 3-HP is added to an ammonium sulfate solution. After separation, solids are produced in stream 91. These solids comprise substantially pure calcium sulfate. The calcium sulfate is substantially free of radioactive materials and can be used commercially.
  • Stream 93 contains the liquids from Reactor 9, including ammonium 3-HP. The ammonium 3-HP can be reacted with phosphoric acid to produce ammonium phosphate and release 3-HP according to Reaction 10 below.
  • Reaction 10 occurs in Reactor 10.
  • Reactor 10 is supplied with the impure H 3 PO 4 from the wet process (Reaction 1).
  • Pure ammonium phosphate can be obtained from stream 101 using crystallizer 103. After crystallization, some ammonium phosphate remains in the mother liquor solution exiting crystallizer 103 via stream 105.
  • Stream 105 contains 3-HP, the phosphoric acid impurities and remaining ammonium phosphate.
  • Stream 105 can be combined with the phosphoric acid solution in stream 63 to produce calcium phosphate.
  • calcium phosphate is produced with calcium 3-HP in Reactor 6.
  • the calcium phosphate exits Reactor 6 via stream 69.
  • the ammonium phosphate remaining in the mother liquor can be converted into calcium phosphate by adding calcium 3-HP according to Reaction 11 and 1 1 A below.
  • the calcium salt thereof has a relatively high solubility in water.
  • Calcium carbonate which enters Reactor 5 on stream 34 contains uranium.
  • the products of Reaction 5 are calcium 3-HP (the calcium salt of the acid), carbon dioxide gas, and water.
  • the calcium salt of 3-HP is highly soluble in water and will be present as a liquid.
  • the uranium is not reacted in Reaction 5.
  • the uranium stays in a solid state with the residue from Reactor 5.
  • the solid stream 54 contains uranium, but substantially no Ca-3HP according to one embodiment.
  • the calcium salt of the organic acid had a lower solubility in water, then some of the calcium salt would be present as a solid.
  • the uranium-containing residue would be mixed with the calcium salt of the organic acid according to one embodiment.
  • the organic acid For all of the calcium salt lost, the organic acid must be replenished, representing additional cost.
  • the acid should have a calcium salt with a water solubility greater than 5%, more particularly with a water solubility greater than 10%, and still more particularly with a water solubility greater than 20%.
  • Propionic acid (HPA) is one alternative. Calcium propionate, the calcium salt of HPA, is produced in a reaction corresponding to Reaction 5 above.
  • the solubility of calcium propionate in water is 33% at 20°C.
  • a dilute solution can be used in stream 57, for example.
  • the amount of propionic acid required to complete the above processes may be somewhat higher because of the lower solubility of its calcium salt.
  • Acetic acid (HAc) may also be used to replace 3-HP.
  • the solubility of calcium acetate, the calcium salt of HAc, in water is about 25% at 20°C. This solubility is also lower than that of calcium 3-hydroxypropionate.
  • the amount of acetic acid required to complete the above processes may be higher because of the lower solubility of its calcium salt.
  • 3-HP has an advantage of higher efficiency.
  • the method described above may enable the production of feed grade ammonium and calcium phosphates and purified byproducts of calcium and ammonium sulfates while generating substantially reduced quantities of wastes.
  • DISCUSSION - INTRODUCTION TO PROCESS OPTIONS Referring to reaction 1 , the primary component of phosphate rock used for the above process is calcium phosphate.
  • the phosphoric acid protons are derived from sulfuric acid. Each phosphoric acid requires three protons. Each sulfuric acid only provides two protons.
  • one and one half moles of sulfuric acid are necessary to produce one mole of phosphoric acid.
  • a mole of calcium sulfate (gypsum) is formed for every mole of sulfuric acid consumed.
  • gypsum calcium sulfate
  • 1.5 moles of gypsum are produced for every one mole of phosphoric acid.
  • the phosphate rock is not pure calcium phosphate.
  • Phosphate rock also contains fluorine. Because of reactions with fluorine, two moles of sulfuric acid are necessary to produce one mole of phosphoric acid. These two moles of sulfuric acid produced two moles of gypsum.
  • reaction 1 contains impurities including uranium. It is a goal to treat the gypsum to produce useful chemicals.
  • reaction 2 contains impurities including uranium. It is a goal to treat the gypsum to produce useful chemicals.
  • reactions 2, 3 and 4 produce calcium carbonate from the gypsum.
  • Each mole of calcium sulfate (gypsum) produces one mole of calcium carbonate.
  • reaction 5 calcium carbonate is converted to the calcium salt of an organic acid.
  • Calcium 3-HP is one example of such a salt.
  • the molar ratio of calcium carbonate to calcium 3-HP is one to one.
  • phosphate rock produces two moles of calcium 3-HP for every one mole of phosphoric acid.
  • one mole of gypsum or calcium 3-HP remains.
  • the third use for stream 57 is the production of ammonium phosphate, through reactors 9 and 10 and crystallizer 103.
  • the molar ratio of phosphoric acid to calcium 3- HP is 1 :2.
  • every mole of calcium 3-HP produces two moles of ammonium 3-HP. Therefore, for every mole of phosphoric acid produced, four moles of ammonium 3-HP are produced.
  • one mole of ammonium 3-HP is consumed for every one mole of phosphoric acid.
  • Calcium phosphate is formed rapidly when calcium 3-hydroxypropionate is added into the phosphoric acid solution.
  • the released 3-HP is recycled back to Reactor 5 via stream 61 to react with calcium carbonate to produce calcium 3-hydroxypropionate. If all calcium 3-hydroxypropionate produced from the reaction 5 is used to react with all the phosphoric acid produced in reaction 1 to produce calcium phosphate, about 50 mol % of the calcium 3-HP would be consumed. This translates to eliminating 50% of the raw gypsum.
  • one possible way to consume the excess calcium 3- hydroxypropionate is by treating it with sulfuric acid to form pure calcium sulfate and regenerate 3-HP according to reaction 12 below.
  • reaction 12 occurs in Reactor 12.
  • the 3-HP can be recycled via stream 121 to treat CaC0 3 in Reactor 5.
  • a further advantage of the formation of calcium phosphate in this manner is that fluorine impurities in the raw phosphoric acid stream (in the forms of H 3 AIF 6 , HF and H 2 SiF 6 ), can be removed in the form of CaF 2 , a solid which can be precipitated by mixing an excess of raw phosphoric acid with calcium 3-hydroxypropionate.
  • the calcium phosphate produced in this mode may have a low enough fluorine content to meet the feed grade or technical grade specifications.
  • PROCESS OPTION 2 The ammonium sulfate in stream 22 produced from the reaction of gypsum with ammonia solution and CO 2 (Reactions 2-4) can be sold as a fertilizer. Excess ammonium sulfate will have to be treated, otherwise it will generate a new waste and consume ammonia. In addition to or instead of selling the ammonium sulfate, it can be reacted with calcium 3-hydroxypropionate to produce high purity calcium sulfate and ammonium 3- hydroxypropionate (Reactor 9). The calcium sulfate precipitates immediately after calcium 3-hydroxypropionate is added to the ammonium sulfate solution.
  • purer CaSO 4 2H 2 0 is obtained at stream 91.
  • This pure CaSO 4 2H 2 O may be free of radioactive material and may be commercially usable.
  • the ammonium 3-hydroxypropionate solution (stream 93) can be used to react with phosphoric acid in Reactor 10 to produce mono-ammonium phosphate (MAP) and release 3-HP (stream 101).
  • MAP mono-ammonium phosphate
  • 3-HP released from Reaction 10 can be sent to react with calcium carbonate to produce calcium 3-hydroxypropionate (Reaction 5) as shown in Fig. 2, via streams 105, 65, 62 and 61.
  • ammonium 3-HP is one compound that should be eliminated.
  • the process can produce more ammonium 3-HP than can be consumed with phosphoric acid.
  • ammonium 3-HP is reacted with the CaCO 3 according to reaction 14 below.
  • Fig. 7 is a flow diagram of a further alternative to the process shown in Fig. 2, relating to reaction 14.
  • CaCO 3 is reacted ammonium 3-HP instead of 3-HP.
  • Reaction 14 occurs in Reactor 14.
  • Ammonium 3-HP is supplied to Reactor 14 from
  • Reactor 9 via stream 141.
  • the process shown in Fig. 7 converts all of the impure gypsum to pure gypsum.
  • Stream 16 is impure gypsum.
  • Stream 91 is pure gypsum.
  • an acid (3-HP) is reacted with a salt, CaC0 3 . This reaction can be done at room temperature.
  • Ammonium 3-HP is a salt. Most ammonia salts of an organic acid are unstable at high temperatures. Ammonium carbonate has a boiling point of 60 Deg C. If the reaction is at 60°C or higher the ammonium carbonate produced can be evaporated from the reaction system.
  • ammonium 3- hydroxypropionate is unstable and decomposes to ammonia and 3-HP.
  • the released 3- HP reacts with calcium carbonate to form calcium 3-HP and carbonic acid.
  • a quantitative conversion from ammonium 3-hydroxypropionate to calcium 3-hydroxypropionate can be reached in about 1 hour at about 100°C by reacting CaC0 3 with ammonium 3-hydroxypropionate.
  • Reaction 14 forms calcium 3-hydroxypropionate and releases ammonium carbonate (or ammonia and C0 2 ), which is recycled back to Reactors 2 and 3 via stream 52.
  • This process demonstrates that all gypsum waste produced in the fertilizer plant can be treated without consuming substantial additional chemicals. Further, the existing gypsum waste from the gypsum stacks can also be treated with this technology. In this technology the only discharged material is uranium containing material, which may be used directly to produce uranium by a conventional technology. The amount of discharged material will be about 5% of the amount of the gypsum waste produced in the fertilizer plant. 3-HP, NH 3 and C0 2 used in this invention are all recycled and are not consumed.
  • the third option is based upon uranium compounds remaining insoluble when exposed to a C0 2 / NH 3 / 3-HP environment.
  • the uranium compounds in the gypsum waste have been exposed to phosphoric acid (reaction 1a) and sulfuric acid (reaction 1b), but did not dissolve.
  • the chemicals of the CO 2 / NH 3 / 3-HP are much weaker chemicals (or acids and base) than sulfuric acid or phosphoric acid. If phosphoric acid and sulfuric acid did not dissolve the uranium compounds, the ammonium sulfate and the CO 2 / NH 3 / 3-HP environment are unlikely dissolve the uranium compounds.

Abstract

A method of treating phosphogypsum produces calcium carbonate and ammonium sulfate from the phosphogypsum. The calcium carbonate contains impurities from the phosphogypsum. The calcium carbonate is reacted with an organic acid to produce a liquid calcium salt of the organic acid and un-reacted solid impurities. The calcium salt of the organic acid is consumed through at least one of two processes. First, the calcium salt of the organic acid may be reacted with phosphoric acid to produce calcium phosphate. Second, the calcium salt of the organic acid may be reacted with the ammonium sulfate to produce the ammonium salt of the organic acid and gypsum, the ammonium salt of the organic acid being reacted with the phosphoric acid to produce ammonium phosphate. The gypsum produced in the second process may have a reduced impurity level relative to phosphogypsum. An integrated process for producing feed grade phosphates while substantially reducing the amount of gypsum waster generated by the production of impure phosphogypsum and impure phosphoric acid from phosphate rock is also disclosed.

Description

TITLE OF THE INVENTION PHOSPHOGYPSUM TREATMENT PROCESS
CROSS-REFERENCE TO RELATED APPLICATIONS This application is based on and hereby claims priority to U.S. Provisional Application Nos. 60/574,930 filed May 28, 2004, 60/575,415 filed June 1 , 2004,
60/615,954 filed October 6, 2004, 60/574,927 filed May 28, 2004, 60/575,416 filed June 1 , 2004, and 60/615,955 filed October 6, 2004, the contents of which are hereby incorporated by reference.
BACKGROUND ART Phosphoric acid, which is a source material for producing phosphates such as calcium phosphate, is produced by a conventional wet process in which sulfuric acid is used to treat a fine phosphate rock as shown in the following reaction. (Reaction 1). The phosphate rock contains several impurities including uranium.
Ca5F(PO4)3 + 5H2S04 + 10H2O -» 5CaS04-2H20| + 3H3PO4 + HF (1) In the reaction described in Reaction 1 , dihydrated calcium sulfate (also known as gypsum or phosphogypsum) is produced. The phosphate rock (Ca5F(PO )3) contains among other impurities about 50 to 100 ppm of uranium. During the wet process (shown in Reaction 1), at least some of the uranium from the phosphate rock stays with the gypsum produced. Therefore, the impure gypsum cannot be used commercially unless the uranium in the gypsum is reduced to an acceptable level. Currently, the gypsum produced in the fertilizer and phosphoric acid plants from the phosphate rock, such as shown in Reaction 1 , is piled on the ground according to such conventional process. A very large pile of the gypsum on the ground is referred to as a "gypsum stack." Since, the impure gypsum produced from Reaction 1 cannot be used as a calcium resource, an extra calcium resource such as lime (calcium hydroxide) has to be used in order to produce feed grade phosphate (calcium phosphate). The phosphoric acid obtained from the wet process described in Reaction 1 is reacted with lime to produce calcium phosphate according to the conventional process. In the conventional process, there is no method of using calcium in the phosphogypsum to produce among other useful products. DISCLOSURE OF THE INVENTION To address the above and/or different concerns, the inventors propose a method of treating phosphogypsum, which produces calcium carbonate and ammonium sulfate from the phosphogypsum. The calcium carbonate contains impurities from the phosphogypsum. The calcium carbonate is reacted with an organic acid to produce a liquid calcium salt of the organic acid and un-reacted solid impurities. The calcium salt of the organic acid is consumed through at least one of two processes. First, the calcium salt of the organic acid may be reacted with phosphoric acid to produce calcium phosphate. Second, the calcium salt of the organic acid may be reacted with the ammonium sulfate to produce the ammonium salt of the organic acid and gypsum, the ammonium salt of the organic acid being reacted with the phosphoric acid to produce ammonium phosphate. The gypsum produced in the second process may have a reduced impurity level relative to phosphogypsum and so be useful in traditional gypsum applications. In addition, the calcium salt of the organic acid may also be consumed in a reaction with sulfuric acid to produce gypsum. The process of reacting the ammonium salt of the organic acid with the phosphoric acid will reproduce the organic acid, which can be recycled to react with the calcium carbonate. In the first process, when the calcium salt of the organic acid is reacted with phosphoric acid to produce calcium phosphate, there is excess ammonium sulfate. The excess ammonium sulfate may be reacted with calcium hydroxide to produce gypsum, which has a reduced impurity level relative to the phosphogypsum. In reacting the excess ammonium sulfate with calcium hydroxide, ammonia may be produced, in which case, the ammonia may be used to produce the calcium carbonate and ammonium sulfate from the phosphogypsum. The inventors also propose to treat phosphogypsum, by (i) producing calcium carbonate and ammonium sulfate from the phosphogypsum through a reaction with ammonium carbonate, the calcium carbonate containing impurities from phosphogypsum, (ii) reacting calcium carbonate with an ammonium salt of an organic acid to produce a liquid calcium salt of the organic acid and un-reacted solid impurities, and (iii) reacting the calcium salt of the organic acid with the ammonium sulfate to produce the ammonium salt of the organic acid and gypsum. The ammonium salt of the organic acid may be recycled for reaction with the calcium carbonate. The calcium salt of the organic acid may be produced by reacting calcium carbonate with the ammonium salt of the organic acid, at a temperature of 60 degree C or higher. The inventors further propose purifying impure gypsum by (i) reacting the impure gypsum with an ammonia-carbon dioxide source, producing ammonium sulfate and calcium carbonate, (ii) reacting the ammonium sulfate with a calcium salt of an organic acid and water, producing substantially purified gypsum and the ammonium salt of the organic acid, and (iii) reacting the ammonium salt of the organic acid with the calcium carbonate, producing ammonium carbonate, which is recycled back to react with the impure gypsum and the calcium salt the organic acid, which is recycled back to react with the ammonium sulfate. Uranium may be removed from an impure, uranium-containing gypsum, by (i) reacting the uranium-containing gypsum with an ammonia-carbon dioxide source, producing calcium carbonate, and (ii) reacting an ammonium salt of an organic acid with the calcium carbonate to produce a liquid, a gas, and a uranium-concentrated solid. Still further, the inventors propose producing calcium phosphate by (i) reacting calcium carbonate with an organic acid to produce the calcium salt of the organic acid, (ii) reacting phosphoric acid and the calcium salt of the organic acid, producing calcium phosphate and the organic acid, which is recycled back to react with calcium carbonate, and (iii) reacting the ammonium sulfate with lime, producing substantially purified gypsum and ammonia. The calcium carbonate may be produced by reacting impure gypsum with an ammonia-carbon dioxide source, producing ammonium sulfate and calcium carbonate. It is also an aspect of the present invention to provide an integrated process for producing feed grade phosphates while substantially reducing the amount of gypsum waste generated. It is another aspect of the present invention to react phosphogypsum with an ammonia-carbon dioxide source to produce ammonium sulfate and calcium carbonate. In a further aspect of the present invention a calcium salt of an organic acid is produced when calcium carbonate produced from phosphogypsum is reacted with the organic acid. In yet another aspect of the present invention substantially pure phosphoric acid is produced that is substantially free of impurities found in phosphate rock. It is another aspect of the present invention to produce calcium phosphate by reacting the phosphoric acid produced from phosphate rock with the calcium salt of the organic acid. In a further aspect of the present invention substantially purified gypsum being substantially free of uranium, is produced by reacting the ammonium sulfate and the calcium salt of the organic acid. In yet another aspect of the present invention ammonium phosphate is produced by reacting the phosphoric acid from phosphate rock and an ammonium salt of the organic acid. It is another aspect of the present invention to produce calcium phosphate by reacting the ammonium phosphate with the calcium salt of the organic acid. In a further aspect of the present invention the organic acid is produced and replenished in the process by reacting the phosphoric acid produced from phosphate rock with the ammonium or calcium salt of the organic acid. In yet another aspect of the present invention radioactive materials such as uranium may be efficiently removed from the impure gypsum produced in Reaction 1 , without consuming substantially any extra chemicals in the overall phosphate production process. Other features and advantages of the present invention will be apparent from the following description taken in conjunction with the accompanying drawings, in which like reference characters designate the same or similar elements throughout the figures thereof.
BRIEF DESCRIPTION OF THE DRAWINGS The accompanying drawings, which are incorporated in and constitute a part of the specification, illustrate embodiments of the invention and, together with the description, serve to explain the principles of the invention. Fig. 1 is a flow diagram showing a process for producing phosphoric acid. Fig. 2 is a flow diagram of a process for treating phosphate rock to produce useful chemicals, according to a first aspect of the invention. Fig. 3 is a schematic drawing of a reactor and associated components, which reactor is shown in Fig. 2. Figs. 4A and 4B are schematic views of alternate embodiments for the settling velocity filter shown in Fig. 1. Fig. 5 shows a flow diagram for a process for treating phosphate rock, according to a second aspect of the invention. Fig. 6 is a flow diagram of a first alternative embodiment for the process shown in
Fig. 2. Fig. 7 is a flow diagram of a third alternative embodiment for the process shown in Fig. 2.
BEST MODE(S) FOR CARRYING OUT THE INVENTION Reference will now be made in detail to the preferred embodiments of the present invention, examples of which are illustrated in the accompanying drawings, wherein like reference numerals refer to like elements throughout. Fig. 1 is a flow diagram showing a process for producing phosphoric acid. Reaction 1 , which is repeated below, occurs in Fig. 1. Ca5F(PO4)3 + 5H2S04 + 10H2O -» 5CaS04-2H2O j + 3H3PO4 + HF (1) Reaction 1 shows phosphate rock being reacted with sulfuric acid. However, even if phosphate rock is very well ground when it is reacted with sulfuric acid, calcium sulfate will form only on the outside of the particles. The inside of the particles remains unreacted, which can increase the gypsum byproduct as well as lower phosphate recovery. To address this, Reaction 1 is performed as two separate reactions, Reactions
1 a and 1 b below.
Ca10F2(PO4)6 + 14 H3PO4 » 10 Ca(H2PO4)2 + 2 HF (1a)
10 Ca(H2P04)2 + 10 H2S04 + 20 H20 -» 20 H3P04 + 10 CaS04-2H2O (1b) In Reaction 1a, the phosphate rock is first reacted with phosphoric acid to produce calcium phosphate. Then, in Reaction 1b, the calcium phosphate is reacted with sulfuric acid to produce calcium sulfate. The process for producing phosphoric acid is described in The Fertilizer Manual published by the International Fertilizer Development Center. Herein, the terms "calcium sulfate" and "gypsum" are used somewhat synonymously. Referring to Fig. 1 , after grinding the phosphate rock, it is introduced to a phosphoric acid attack tank, where Reaction 1a occurs. Phosphoric acid reacts the phosphate rock to form mono calcium phosphate, which is more soluble in water than the starting material. The mono calcium phosphate is then reacted with sulfuric acid. Fig. 1 shows the reaction of sulfuric acid as having six stages. After the sixth stage, a portion of the phosphoric acid/phosphogypsum slurry is recycled to the first reactor while the balance is filtered to separate the product phosphoric acid from the calcium sulfate in a filter feed tank. Calcium sulfate is subjected to three filtration stages with counter-current washing before repulping. In the second, intermediate stage a dilute phosphoric acid is separated from phosphogypsum and recycled back to the first reactor for Reaction 1a. The phosphogypsum is repulped with water. Fig. 2 is a flow diagram of a process for treating phosphate rock to produce useful chemicals, which expands upon the phosphoric acid process shown in Fig. 1. In Fig. 2, the phosphate rock, after being finely ground, is sent to a pretreatment area. In the pretreatment area, the phosphate rock is soaked in phosphoric acid. Reaction 1a occurs in the pretreatment area, as discussed above. From pretreatment, the produced calcium phosphate is sent to Reactor 1. In Reactor 1 , sulfuric acid is added. Reaction 1 b occurs in Reactor 1 in a manner similar to that shown in Fig. 1. In Fig. 2, the pretreatment area corresponds with the H3PO4 acid attack tank shown in Fig. 1. In Fig. 2, Reactor 1 corresponds with the H2S04 acid attack tank shown in Fig. 1. Fig. 1 shows 6 stages for the phosphoric acid and sulfuric acid reactions. A staged reaction is not shown in Fig. 2 for simplicity. A staged reaction is certainly possible. The process that occurs in Fig. 2 produces a slurry of dihydrated calcium sulfate
(also called gypsum) at stream 10. This slurry is sent to a filter 15 to separate the gypsum from the phosphoric acid. The gypsum exits the filter 15 via stream 16. The impure phosphoric acid is recycled from the filter 15 to the pretreatment area via stream 17. Stream 16 containing impure gypsum is then processed in Reactors 2 and 3. The purpose of Reactors 2 and 3 is to treat the impure gypsum with an ammonia-water solution in the presence of carbon dioxide (Reaction 2). In Reactors 2 and 3, at least one of the following Reactions 2-4 occurs.
CaSO4-2H2O + 2NH3 + CO2 -» (NH4)2SO4 + H2O + CaC03| (2) CaSO4-2H2O + (NH4)2CO3 - (NH4)2SO4 + 2H2O + CaCO3 | (3)
CaSO4-2H2O + 2NH4HCO3 - (NH4)2SO4 + CaCO3 j + CO2 t + 3H2O (4) All of the Reactions 2-4 produce calcium carbonate, which is precipitated, and ammonium sulfate. Uranium and other impurities in the calcium sulfate may stay with the calcium carbonate precipitates. Process conditions determine which reaction(s) of Reactions 2-4 occur. At sufficiently high temperatures and sufficiently low pressures, ammonia is a gas, thus favoring Reaction 2. However, at ambient temperature and pressure, ammonia reacts with water and converts to ammonium hydroxide according to Reaction 2a below. NH3 (g) + H20 (I) <=> NH4OH (aq) (2a) In addition, if both water and carbon dioxide are present with ammonia, then ammonium carbonate or ammonium bicarbonate are formed respectively according to Reaction 2b or 2c below.
2NH3 (g) + 2 H2O (I) + CO2 (g) <=> (NH4)2CO3 (aq) (2b) NH3 (g) + H20 (I) + C02 (g) <=> (NH4)HC03 (aq) (2c) In view of the foregoing, if the temperature is sufficiently high and the pressure is sufficiently low, Reaction 2 primarily occurs in Reactors 2 and 3. If the temperature is lower and/or the pressure is higher, then Reactions 3 and/or 4 primarily occur in Reactors 2 and 3. In practice, stream 52 leaving Reactor 5 may contain a gaseous stream (CO2 and NH3), which is bubbled through liquid contained in Reactor 3. Stream 32 may be a liquid, which is sent to Reactor 2. Reactors 2 and 3 serve as a counter current reaction mode to react the gypsum. Calcium sulfate is gradually converted to calcium carbonate. According to a particularly preferred embodiment, stream 22 exits Reactor 2 having maximum purity ammonium sulfate, and stream 34 exits Reactor 3 having maximum purity calcium carbonate. A quantitative conversion from CaSO4 to (NH4)2SO4 can be reached in about 50 min at room temperature. To do this, in Reactor 2, the remaining excess ammonia and C02 (ammonium carbonate or ammonium bicarbonate) in stream 32 is reacted with fresh gypsum from filter 15 to produce ammonium sulfate. Because there is excess gypsum, substantially all of the remaining ammonia and CO2 is reacted. The product stream 22 contains ammonium sulfate. Reactor 3 has excess ammonia and CO2, all remaining gypsum in the stream 24 is converted to ammonium sulfate. With Reactors 2 and 3, the quantitative conversion from CaSO to (NH )2SO4 is reached. Reactor 2 can be a stirred reactor. On a batch scale, all remaining excess ammonia and CO2 in stream 32 may be reacted after approximately 30 min of mixing. According to an alternative embodiment, these conditions can also be utilized in a continuous process. The ammonium sulfate exits Reactor 2 via stream 22. The ammonium sulfate in stream 22 is sufficiently pure to have commercial use outside the process shown in Fig. 2. That is, stream 22 contains substantially no free ammonia or ammonium carbonate or ammonium bicarbonate. The solids produced in Reactor 2 are a mixture of calcium sulfate and calcium carbonate. The solids exit Reactor 2 in stream 24. The calcium sulfate and calcium carbonate are treated with a fresh ammonia solution in presence of carbon dioxide gas, as discussed above, in Reactor 3. The quantitative conversion changes all of the calcium sulfate to ammonium sulfate. The solids from Reactor 3 (calcium carbonate and impurities) exit via stream 34. The solids in stream 34 may be treated with 3-hydroxypropionic acid (3-HP), HOCH2CH2CO2H according to a preferred embodiment. 3-HP is an organic acid, which reacts with calcium carbonate to form calcium 3-hydroxypropionate and releases carbon dioxide gas and water. This reaction is shown below as Reaction 5, which occurs in Reactor 5.
CaC03 + 2HOCH2CH2C02H - Ca(HOCH2CH2C02)2 + C02 | + H2O (5) Reaction 5 is an acid-base reaction, which is likely to proceed to the right hand side of the equilibrium rapidly and C02 is removed. Carbon dioxide gas from Reactor 5 is sent to Reactor 3 via stream 52. One embodiment for Reactor 5 is shown in more detail in Fig. 3. Reaction 5 occurs as in Reactor 5A. Solids and liquids exit Reactor 5A via stream 58. A gas stream 55 is sent to an adsorption column 5B. In column 5B, carbon dioxide is collected or trapped by an ammonia water solution, which enters via stream 56.
Stream 52 from adsorption column 5B contains carbon dioxide, ammonia and water (or ammonium carbonate or ammonium bicarbonate), and is sent to Reactor 3. Although stream 56 is necessary, it is not shown in Fig. 2. Stream 52 is used as the ammonia source for Reactor 3. Although Fig. 3 shows adsorption column 5B, it is possible to run the process without carbon dioxide adsorption. Gas stream 55 contains primarily carbon dioxide. Instead of supplying Reactor 3 via stream 52, carbon dioxide can be supplied as a gas, from gas stream 55 to Reactor 3. In this case, the ammonia source from stream 56 is lost. Therefore, a separate ammonia stream must be introduced into Reactor 3 together with the carbon dioxide stream 55. Stream 55 is a gas, and the ammonia source for Reactor 3 may also be a gas. These two gases could be supplied separately or combined before introduction into Reactor 3. If gaseous, the carbon dioxide and ammonia are bubbled through Reactor 3. With adsorption column 5B, Reactor 3 is supplied with stream 52, which is at least partially a liquid. Without adsorption column 5B, Reactor 3 may be supplied with a gas. In either case, Reactor 3 is supplied with carbon dioxide and ammonia. In addition to adsorbing carbon dioxide, adsorption column 5B may also function as a reservoir. It is known that in the traditional process a significant proportion of the Uranium in the rock is in a chemical form that dissolves when subjected to concentrated sulphuric acid. The residual uranium compounds, together other impurities, are not leached significantly in that harsh environment, so it is unlikely that they will be significantly solublized under the conditions in reactors 2, 3 and 5. The solids and liquids in stream 58 (see Fig. 3) are sent to separator 5C, which produces a solid stream 54 and a liquid stream 57. The solids in stream 54 contain uranium, which may be used to produce uranium compounds. The uranium level may be about 0.1-0.2 weight %. This concentration assumes that original uranium concentration in gypsum is about 50 to 100 ppm (0.005 weight % to 0.01 weight %). The solids in stream 16 (see Fig. 2) may include gypsum and 5 wt.% to 10 wt.% impurities. If stream
16 (phosphogypsum) contains 95 % of gypsum and all the gypsum is reacted, then the only solids that remain are the impurities, originally 5 wt.%, now approaching 100 wt.%. The removal of gypsum represents a concentration of about 20 times. Thus, an original concentration of 0.005 weight % to 0.01 weight % becomes 0.1 weight % to 0.2 weight %. With regard to the liquid stream 57, calcium 3-hydroxypropionate freely dissolves in water. Hence, stream 57 contains both water and calcium 3-hydroxypropionate. The calcium 3-HP water solution in stream 57 has a plurality of uses in the Fig. 2 processes. One use is adding the calcium 3-HP into a phosphoric acid solution to produce calcium phosphate precipitates and release 3-HP according to Reaction 6 below. H3PO4 + Ca(HOCH2CH2CO2)2 » CaHPO4 j + 2HOCH2CH2CO2H (6) Reaction 6 occurs in Reactor 6. The released 3-HP exits Reactor 6 on stream 61. Stream 61 is sent to Reactor 5 along with stream 34 for Reaction 5. One product of Reactor 6 is CaHPO4. This chemical is also referred to as "dical." A related chemical, Ca(H2P04)2, is referred to as "monocal." If phosphoric acid is used in Reactor 6, it is possible to select between dical and monocal by varying the amount of calcium 3HP. As can be seen from Fig. 2, Reactor 6 is supplied with phosphoric acid on stream 62. This stream is labeled "Pure H3PO4". However, the phosphoric acid produced in the wet process (Reaction 1) is not pure. For example, the phosphoric acid contains HF, H2SiF6 and H3AIF6. In order to purify the phosphoric acid, stream 63 from Reaction 1 is sent to Reactor 6/7/8 in which Reactions 6, 7, 8 and 8A occur. Reaction 6 is shown above, and Reactions 7, 8 and 8A are shown below.
2HF + Ca(HOCH2CH2C02)2 -» CaF2 [ + 2HOCH2CH2CO2H (7) H3AIF6 + H3P04 + 3Ca(HOCH2CH2C02)2 -» 3CaF2 j + AIPO4 J. + 6HOCH2CH2CO2H..(8)
H2SiF6 + 2H20 + 3Ca(HOCH2CH2C02)2 » 3CaF21 + SiO2 j + 6HOCH2CH2CO2H...(8A) Stream 65 contains the products of Reaction 6/7/8. In addition, because Reaction 6 competes with Reactions 7, 8 and 8A for the calcium 3-HP, Reaction 6 is not substantially completed in Reactor 6/7/8. Thus, stream 65 also contains phosphoric acid. Filter 68 can be used to separate the liquids from the solids. The solids exit filter 68 via stream 67 and include CaHPO4, CaF2, Si02 and AIP04. Assuming that Reactions 7/8 proceed further than reaction 6, the liquid (stream 62) that remains will have an increased phosphoric acid purity, which is supplied to Reactor 6. Reactor 6/7/8 may be a key component in the separation. Together with filter 68, separation may be performed based on the differences in settling velocities of the precipitates. In other systems, CaF2 forms fine solid particles, which stay in suspension and do not readily precipitate. In other systems, AIP04 forms the flake-like precipitates that also exist in suspension. If this behavior occurs in this system, then AIPO4 may have a higher settling velocity than CaF2. CaHP04 forms large crystalline precipitates that easily settle. CaHP04 therefore has the highest settling velocity. Although Fig. 2 shows a stream 67 as the only solid stream exiting filter 68, there may be two or three solid streams, one for CaF2, one for CaHPO4 and perhaps one for AIPO4. Settling velocity concepts are described, for example, in U.S. Patent No. 4,540,484, U.S. Patent No. 5,549,734 and U.S. Patent No. 6,432,298. Fig. 4A is a schematic view showing how Reactor 6/7/8 and filter 68 work together to perform
Reactions 6, 7 and 8 and separate the products thereof. In addition to Reactions 7 and 8, Reaction 8A removes H2SiF6 by converting H2SiF6 to SiO2. SiO2 may be produced and separated using Reactor 6/7/8 and filter 68. However, the production and separation is not shown in Fig. 4A. Together, Reactor 6/7/8 and filter 68 form a gravity filter. Fig. 4A shows an embodiment where filter 68 is embodied as two filters, filter 68a and filter 68b.
A belt filter or a centrifuge, for example, can be used as the filters 68a, 68b for streams 65a, 65b. Although two filters are shown in Fig. 4A, it may not be necessary to separate the calcium fluoride from the aluminum phosphate. Both can be treated as impurities. Silicon dioxide, which is not shown in Fig. 4A, may be removed together with CaF2 and AIPO4 in this single filter 68 according to an alternative embodiment. In this case, streams 65a and 65b would be combined, and a single filter 68 would be used to separate phosphoric acid from impurities. According to one potential embodiment, in a gravity reactor, liquid from streams 105/63 and 57 can be added to a liquid capacity of about 90 % of the total volume of the reactor 6/7/8. Fig. 4A shows streams 57 and 105/63 supplying Reactor 6/7/8 at an upper portion thereof. The place of liquid introduction is not restricted to an upper portion. In Reactor 6/7/8, he solids with a higher settling velocity proceed to the bottom of the Reactor. Aluminum phosphate, a flake-like precipitate, has a lower settling velocity than calcium phosphate. Aluminum phosphate exits Reactor 6/7/8 from a middle portion, at stream 65b. Calcium fluoride, a fine solid, has the lowest settling velocity. Calcium fluoride exits Reactor 6/7/8 from an upper portion at stream 65a. Fig. 4A shows liquid phosphoric acid being removed from Reactor 6/7/8 via filters 68a and 68b. In a gravity reactor/filter, perhaps the bottom 10 % of the volume contains mainly the heavier solids, CaHP04. Other configurations are of course possible. Fig. 4B is an alternate embodiment to the embodiment shown in Fig. 4A. CaHP04 is a commercially valuable chemical. Calcium phosphate which may be the heaviest solid may exit as a slurry. The calcium phosphate could be separated from stream 62c with a filter, in the same manner as the separation for CaF2 and AIPO4. Reactor 6 is designed for producing calcium phosphate. Accordingly, the CaHPO slurry in stream 62c of Fig. 4A could be combined with the phosphoric acid solution (stream 62) obtained from the filters 68a and 68b and sent to Reactor 6 to produce calcium phosphate (Reaction 6). Reactors 6/7/8 and 6 use calcium 3-HP as a calcium source. Chinese Patent
Publication CN 1022556C, published October 27, 1993 proposed to use calcium hydroxide, calcium oxide and calcium carbonate as calcium sources. However, using these reactants entails a solid-liquid reaction, which takes longer and requires excess calcium. In addition, both the reactants and the products are solids. On the other hand, reactions 6, 7 and 8 use liquid reactants and produce solid products. It is relatively easy to determine when reactions 6, 7 and 8 are complete. When both the reactants and the products contain solids it is more difficult to judge completion. Furthermore, with calcium hydroxide, calcium oxide and calcium carbonate, a batch process may be required. When the reactants are liquid and the products are solid, the reaction can be run continuously. As mentioned above, Reactor 2 produces ammonium sulfate in stream 22. This ammonium sulfate may be sold as a fertilizer or can be reacted with calcium 3-HP to produce high purity calcium sulfate and ammonium 3-HP according to Reaction 9.
(NH4)2SO4 + Ca(HOCH2CH2CO2)2 2H20→- CaS04-2H2O 1 +
2NH4HOCH2CH2C02 (9) Reaction 9 occurs in Reactor 9. Reactor 9 represents a third use for the calcium 3-HP produced in Reactor 5, exiting via stream 57. In Reactor 9, Reaction 9 proceeds quickly. On a batch scale, calcium sulfate is produced almost immediately after calcium
3-HP is added to an ammonium sulfate solution. After separation, solids are produced in stream 91. These solids comprise substantially pure calcium sulfate. The calcium sulfate is substantially free of radioactive materials and can be used commercially. Stream 93 contains the liquids from Reactor 9, including ammonium 3-HP. The ammonium 3-HP can be reacted with phosphoric acid to produce ammonium phosphate and release 3-HP according to Reaction 10 below.
H3PO4 + NH4HOCH2CH2C02 » NH4H2PO4 + HOCH2CH2CO2H (10) Reaction 10 occurs in Reactor 10. Reactor 10 is supplied with the impure H3PO4 from the wet process (Reaction 1). The products of Reaction 10, and the impurities contained in phosphoric acid, exit Reactor 10 via stream 101. Pure ammonium phosphate can be obtained from stream 101 using crystallizer 103. After crystallization, some ammonium phosphate remains in the mother liquor solution exiting crystallizer 103 via stream 105. Stream 105 contains 3-HP, the phosphoric acid impurities and remaining ammonium phosphate. Stream 105 can be combined with the phosphoric acid solution in stream 63 to produce calcium phosphate. As discussed above, calcium phosphate is produced with calcium 3-HP in Reactor 6. The calcium phosphate exits Reactor 6 via stream 69. As an alternative, after crystallization, the ammonium phosphate remaining in the mother liquor can be converted into calcium phosphate by adding calcium 3-HP according to Reaction 11 and 1 1 A below.
2NH4H2PO4 + Ca(HOCH2CH2C02)2 » Ca(H2PO4)2j + 2NH4HOCH2CH2C02 (11)
NH4H2PO4 + Ca(HOCH2CH2CO2)2^ CaHPO4| + NH4HOCH2CH2C02+ HOCH2CH2CO2H (11 A) Referring to Fig. 5, this reaction occurs in Reactor 11. Ca 3-HP is provided via stream 57. Thus, with the alternative shown in Fig. 5, there are four uses for the Ca 3-HP produced in Reactor 5. The solids from Reactor 11 are calcium phosphate in stream 111. The liquids exit in stream 113, and comprise ammonium 3-HP and 3-HP. Stream 113 can be combined with stream 61 and sent to Reactor 5 to produce calcium 3-HP. As an alternative to the process described above, 3-HP may be replaced with a different organic acid. One qualification for the organic acid is that the calcium salt thereof has a relatively high solubility in water. Calcium carbonate which enters Reactor 5 on stream 34 contains uranium. The products of Reaction 5 are calcium 3-HP (the calcium salt of the acid), carbon dioxide gas, and water. The calcium salt of 3-HP is highly soluble in water and will be present as a liquid. On the other hand, the uranium is not reacted in Reaction 5. The uranium stays in a solid state with the residue from Reactor 5. Thus, the solid stream 54 contains uranium, but substantially no Ca-3HP according to one embodiment. On the other hand, if the calcium salt of the organic acid had a lower solubility in water, then some of the calcium salt would be present as a solid.
In this case, the uranium-containing residue would be mixed with the calcium salt of the organic acid according to one embodiment. For all of the calcium salt lost, the organic acid must be replenished, representing additional cost. To avoid this cost, it is desirable for the calcium salt of the organic acid to have a high water solubility. To be more specific regarding the solubility guideline, the acid should have a calcium salt with a water solubility greater than 5%, more particularly with a water solubility greater than 10%, and still more particularly with a water solubility greater than 20%. Propionic acid (HPA) is one alternative. Calcium propionate, the calcium salt of HPA, is produced in a reaction corresponding to Reaction 5 above. With propionic acid, the solubility of calcium propionate in water is 33% at 20°C. To accommodate this, a dilute solution can be used in stream 57, for example. With more water, there is less calcium salt. The amount of propionic acid required to complete the above processes may be somewhat higher because of the lower solubility of its calcium salt. However, functionality is preserved. Acetic acid (HAc) may also be used to replace 3-HP. The solubility of calcium acetate, the calcium salt of HAc, in water is about 25% at 20°C. This solubility is also lower than that of calcium 3-hydroxypropionate. The amount of acetic acid required to complete the above processes may be higher because of the lower solubility of its calcium salt. Thus, although it is entirely possible to use any organic acid to proceed with the processes described above, 3-HP has an advantage of higher efficiency. The method described above may enable the production of feed grade ammonium and calcium phosphates and purified byproducts of calcium and ammonium sulfates while generating substantially reduced quantities of wastes. DISCUSSION - INTRODUCTION TO PROCESS OPTIONS Referring to reaction 1 , the primary component of phosphate rock used for the above process is calcium phosphate. When phosphoric acid is produced from phosphate rock according to reaction 1 , the phosphoric acid protons are derived from sulfuric acid. Each phosphoric acid requires three protons. Each sulfuric acid only provides two protons. Accordingly, one and one half moles of sulfuric acid are necessary to produce one mole of phosphoric acid. For every mole of sulfuric acid consumed, a mole of calcium sulfate (gypsum) is formed. Thus, 1.5 moles of gypsum are produced for every one mole of phosphoric acid. In addition, the phosphate rock is not pure calcium phosphate. Phosphate rock also contains fluorine. Because of reactions with fluorine, two moles of sulfuric acid are necessary to produce one mole of phosphoric acid. These two moles of sulfuric acid produced two moles of gypsum. Thus, based on the usual impurity content, for every mole of phosphoric acid produced from phosphate rock, two moles of gypsum are produced. The gypsum produced from the wet process (Reaction 1) contains impurities including uranium. It is a goal to treat the gypsum to produce useful chemicals. As a first step, reactions 2, 3 and 4 produce calcium carbonate from the gypsum. Each mole of calcium sulfate (gypsum) produces one mole of calcium carbonate. With reaction 5, calcium carbonate is converted to the calcium salt of an organic acid. Calcium 3-HP is one example of such a salt. In reaction 5, the molar ratio of calcium carbonate to calcium 3-HP is one to one. Therefore, the two to one ratio with phosphoric acid is not changed through reactions 2-5. Two moles of calcium 3-HP are produced for every single mole of phosphoric acid. 1 mol H3P04 = 2 mol CaSO4 2 mol CaS04= 2 mol CaCO3 2 mol CaCO3= 2 mol calcium 3-HP 1 mol H3P04 = 2 mol calcium 3-HP In Fig. 2, three uses for stream 57 are shown. The first and second uses relate to producing calcium phosphate with phosphoric acid, according to reaction 6. In reaction 6, one mole of calcium phosphate is produced from one mole of phosphoric acid and one mole of calcium 3-HP. Therefore, according to a molar balance, 50% of the gypsum can be consumed. That is, phosphate rock produces two moles of calcium 3-HP for every one mole of phosphoric acid. For each mole of phosphoric acid used in reaction 6, one mole of gypsum (or calcium 3-HP) remains. The third use for stream 57 is the production of ammonium phosphate, through reactors 9 and 10 and crystallizer 103. The molar ratio of phosphoric acid to calcium 3- HP is 1 :2. Referring to reaction 9, every mole of calcium 3-HP produces two moles of ammonium 3-HP. Therefore, for every mole of phosphoric acid produced, four moles of ammonium 3-HP are produced. Referring to reaction 10, one mole of ammonium 3-HP is consumed for every one mole of phosphoric acid. Three moles of ammonium 3-HP remain unreacted. Based on a molar balance, 25% of the gypsum can be consumed to produce ammonium phosphate. The above description assumes that all of the phosphoric acid is used to produce either ammonium phosphate or calcium phosphate. On the other hand, phosphoric acid itself is a valuable chemical. If all of the phosphoric acid is sold, then none of the gypsum is consumed. PROCESS OPTION 1 Referring to Fig. 2, calcium 3-hydroxypropionate can be added directly into Reactor 6 via stream 57 together with the phosphoric acid solution (stream 62) obtained from the wet process to precipitate calcium phosphate (stream 69) and release 3-HP (stream 61). Calcium phosphate is formed rapidly when calcium 3-hydroxypropionate is added into the phosphoric acid solution. The released 3-HP is recycled back to Reactor 5 via stream 61 to react with calcium carbonate to produce calcium 3-hydroxypropionate. If all calcium 3-hydroxypropionate produced from the reaction 5 is used to react with all the phosphoric acid produced in reaction 1 to produce calcium phosphate, about 50 mol % of the calcium 3-HP would be consumed. This translates to eliminating 50% of the raw gypsum. Referring to Fig. 6, one possible way to consume the excess calcium 3- hydroxypropionate is by treating it with sulfuric acid to form pure calcium sulfate and regenerate 3-HP according to reaction 12 below.
H2SO4 + Ca(HOCH2CH2C02)2 -» CaSO42H2O J, + 2HOCH2CH2C02H (12) In Fig. 6, reaction 12 occurs in Reactor 12. The 3-HP can be recycled via stream 121 to treat CaC03 in Reactor 5. A further advantage of the formation of calcium phosphate in this manner is that fluorine impurities in the raw phosphoric acid stream (in the forms of H3AIF6, HF and H2SiF6), can be removed in the form of CaF2, a solid which can be precipitated by mixing an excess of raw phosphoric acid with calcium 3-hydroxypropionate. The calcium phosphate produced in this mode may have a low enough fluorine content to meet the feed grade or technical grade specifications.
PROCESS OPTION 2 The ammonium sulfate in stream 22 produced from the reaction of gypsum with ammonia solution and CO2 (Reactions 2-4) can be sold as a fertilizer. Excess ammonium sulfate will have to be treated, otherwise it will generate a new waste and consume ammonia. In addition to or instead of selling the ammonium sulfate, it can be reacted with calcium 3-hydroxypropionate to produce high purity calcium sulfate and ammonium 3- hydroxypropionate (Reactor 9). The calcium sulfate precipitates immediately after calcium 3-hydroxypropionate is added to the ammonium sulfate solution. After separation of the solids from the solution, purer CaSO42H20 is obtained at stream 91. This pure CaSO42H2O may be free of radioactive material and may be commercially usable. The ammonium 3-hydroxypropionate solution (stream 93) can be used to react with phosphoric acid in Reactor 10 to produce mono-ammonium phosphate (MAP) and release 3-HP (stream 101). The 3-HP released from Reaction 10 can be sent to react with calcium carbonate to produce calcium 3-hydroxypropionate (Reaction 5) as shown in Fig. 2, via streams 105, 65, 62 and 61. If all the phosphoric acid obtained from the wet process is used to produce mono- ammonium phosphate (MAP) in Reactor 10, about 25% of the gypsum waste will be consumed (the production of 1 phosphoric acid produces 2.0 gypsum, one gypsum generates one ammonium sulfate which produces two ammonium 3-hydroxypropionate and one MAP requires only one ammonium 3-hydroxypropionate). Therefore, a maximum of 25% of the gypsum waste can be treated according to this process option. If calcium phosphate has a larger market than ammonium phosphates (MAP can act as a precursor for diammonium phosphate production), using all calcium 3- hydroxypropionate to produce calcium phosphate will consume more gypsum waste (one CaHP0 requires one calcium 3-hydroxypropionate). However, if calcium 3-hydroxypropionate and all phosphoric acid produced in the wet process are used to produce CaHP04, not all ammonium sulfate produced from the treatment of the gypsum waste (Reactions 2-4) can be treated by calcium 3- hydroxypropionate (50% remains). In order to avoid generating the new waste of ammonium sulfate, alternative treatment can be used. One option is to use lime or calcium hydroxide to treat remained ammonium sulfate to form pure gypsum and release ammonia which can be recycled back to Reactors 2 and 3 according to reaction 13 below.
(NH4)2S04 + Ca(OH)2 » CaSO4-2H20 j + 2NH3| (13)
PROCESS OPTION 3 In treating phosphogypsum, ammonium 3-HP is one compound that should be eliminated. The process can produce more ammonium 3-HP than can be consumed with phosphoric acid. According to option 3, ammonium 3-HP is reacted with the CaCO3 according to reaction 14 below.
2NH4HOCH2CH2CO2 + CaCO3 (NH4)2CO3 + Ca(HOCH2CH2C02)2 (14) Fig. 7 is a flow diagram of a further alternative to the process shown in Fig. 2, relating to reaction 14. In Fig. 7, CaCO3 is reacted ammonium 3-HP instead of 3-HP. Reaction 14 occurs in Reactor 14. Ammonium 3-HP is supplied to Reactor 14 from
Reactor 9 via stream 141. The process shown in Fig. 7 converts all of the impure gypsum to pure gypsum. Stream 16 is impure gypsum. Stream 91 is pure gypsum. In Reactor 5 of Fig. 2, an acid (3-HP) is reacted with a salt, CaC03. This reaction can be done at room temperature. Ammonium 3-HP is a salt. Most ammonia salts of an organic acid are unstable at high temperatures. Ammonium carbonate has a boiling point of 60 Deg C. If the reaction is at 60°C or higher the ammonium carbonate produced can be evaporated from the reaction system. At the 60 degree C or higher reaction temperature ammonium 3- hydroxypropionate is unstable and decomposes to ammonia and 3-HP. The released 3- HP reacts with calcium carbonate to form calcium 3-HP and carbonic acid. On a batch scale, a quantitative conversion from ammonium 3-hydroxypropionate to calcium 3-hydroxypropionate (or from CaCO3 to (NH )2CO3) can be reached in about 1 hour at about 100°C by reacting CaC03 with ammonium 3-hydroxypropionate. This demonstrates that ammonium 3-hydroxypropionate from Reaction 9 can be recycled back to treat CaC03 produced from the gypsum waste (Reactions 2-4). Reaction 14 forms calcium 3-hydroxypropionate and releases ammonium carbonate (or ammonia and C02), which is recycled back to Reactors 2 and 3 via stream 52. This process demonstrates that all gypsum waste produced in the fertilizer plant can be treated without consuming substantial additional chemicals. Further, the existing gypsum waste from the gypsum stacks can also be treated with this technology. In this technology the only discharged material is uranium containing material, which may be used directly to produce uranium by a conventional technology. The amount of discharged material will be about 5% of the amount of the gypsum waste produced in the fertilizer plant. 3-HP, NH3 and C02 used in this invention are all recycled and are not consumed. The third option is based upon uranium compounds remaining insoluble when exposed to a C02 / NH3 / 3-HP environment. The uranium compounds in the gypsum waste have been exposed to phosphoric acid (reaction 1a) and sulfuric acid (reaction 1b), but did not dissolve. The chemicals of the CO2 / NH3 / 3-HP are much weaker chemicals (or acids and base) than sulfuric acid or phosphoric acid. If phosphoric acid and sulfuric acid did not dissolve the uranium compounds, the ammonium sulfate and the CO2 / NH3 / 3-HP environment are unlikely dissolve the uranium compounds. The invention has been described in detail with particular reference to preferred embodiments thereof and examples, but it will be understood that variations and modifications can be effected. For example, there have been substantial discussions regarding the use of 3-HP. However, other organic acids, such as propionic acid, formic acid, lactic acid and acetic acid can be used. These variations and modifications are within the spirit and scope of the invention.

Claims

What is Claimed is: 1. A method of treating phosphogypsum, comprising: producing calcium carbonate and ammonium sulfate from the phosphogypsum, the calcium carbonate containing impurities from the phosphogypsum; reacting calcium carbonate with an organic acid to produce a liquid calcium salt of the organic acid and un-reacted solid impurities; consuming the calcium salt of the organic acid through at least one process selected from the group consisting of: (i) reacting the calcium salt of the organic acid with phosphoric acid to produce calcium phosphate, and (ii) reacting the calcium salt of the organic acid with the ammonium sulfate to produce the ammonium salt of the organic acid and gypsum, and reacting the ammonium salt of the organic acid with the phosphoric acid to produce ammonium phosphate.
2. The method according to claim 1 , wherein the calcium salt of the organic acid is also consumed by reaction with sulfuric acid to produce gypsum.
3. The method according to claim 1 , further comprising using at least a portion of the ammonium sulfate to produce commercial grade ammonium sulfate.
4. The method according to claim 1 , wherein reacting the calcium salt of the organic acid with the ammonium sulfate also produces calcium sulfate, the method further comprising using at least a portion of the ammonium sulfate to produce commercial grade gypsum.
5. The method according to claim 1 , wherein reacting the ammonium salt of the organic acid with the phosphoric acid also produces the organic acid, the method further comprising recycling the organic acid to react with the calcium carbonate.
6. The method according to claim 1 , further comprising reacting the ammonium sulfate with calcium hydroxide to produce calcium sulfate.
7. The method according to claim 1 , wherein in process (ii), the gypsum produced from reaction with ammonium sulfate, has a reduced impurity level relative to the phosphogypsum.
8. The method according to claim 1 , wherein at least a portion of the calcium salt of the organic acid is reacted with phosphoric acid to produce calcium phosphate leaving excess ammonium sulfate, and the method further comprises reacting the excess ammonium sulfate with calcium hydroxide to produce gypsum, which has a reduced impurity level relative to the phosphogypsum.
9. The method according to claim 8, wherein reacting the excess ammonium sulfate with calcium hydroxide also produces ammonia, the ammonia is used to produce the calcium carbonate and ammonium sulfate from the phosphogypsum.
10. A method of treating phosphogypsum, comprising: producing calcium carbonate and ammonium sulfate from the phosphogypsum, the calcium carbonate containing impurities from phosphogypsum; reacting calcium carbonate with an ammonium salt of an organic acid to produce a liquid calcium salt of the organic acid and un-reacted solid impurities; and reacting the calcium salt of the organic acid with the ammonium sulfate to produce the ammonium salt of the organic acid and gypsum.
11. The method according to claim 10, further comprising recycling the ammonium salt of the organic acid for reaction with the calcium carbonate.
12. The method according to claim 10, wherein calcium carbonate and ammonium sulfate are produced from the phosphogypsum by reaction with ammonium carbonate, the ammonium carbonate is produced by reacting calcium carbonate with the ammonium salt of an organic acid, and the method further comprises recycling the ammonium salt of the organic acid for reaction with the calcium carbonate.
13. The method according to claim 10, wherein the calcium salt of the organic acid is produced by reacting calcium carbonate with the ammonium salt of the organic acid, at a temperature of 60 degree C or higher.
14. A process for purifying impure gypsum comprising: reacting the impure gypsum with an ammonia-carbon dioxide source, producing ammonium sulfate and calcium carbonate; reacting the ammonium sulfate with a calcium salt of an organic acid and water, producing substantially purified gypsum and the ammonium salt of the organic acid; and reacting the ammonium salt of the organic acid with the calcium carbonate, producing ammonium carbonate, which is recycled back to react with the impure gypsum - and the calcium salt the organic acid, which is recycled back to react with the ammonium sulfate.
15. A method for removing uranium from an impure, uranium-containing gypsum, comprising: reacting the uranium-containing gypsum with an ammonia-carbon dioxide source, producing calcium carbonate; and reacting an ammonium salt of an organic acid with the calcium carbonate to produce a liquid, a gas, and a uranium-concentrated solid.
16. A process for substantially reducing ammonium sulfate waste comprising: reacting ammonium sulfate produced from phosphogypsum with lime, producing gypsum and ammonia.
17. A process for producing calcium phosphate comprising: reacting calcium carbonate with an organic acid, producing the calcium salt of the organic acid; reacting phosphoric acid and the calcium salt of the organic acid, producing calcium phosphate and the organic acid, which is recycled back to react with calcium carbonate; and reacting the ammonium sulfate with lime, producing substantially purified gypsum and ammonia.
18. The process according to claim 17, wherein the calcium carbonate is produced by: reacting impure gypsum with an ammonia-carbon dioxide source, producing ammonium sulfate and calcium carbonate.
19. A process comprising reacting phosphogypsum with an ammonia-carbon dioxide source to produce ammonium sulfate and calcium carbonate.
20. The process according to claim 19, wherein phosphogypsum is reacted with an ammonia-carbon dioxide source according to at least one of the following reactions; CaS04-2H2O + 2NH3 + C02 -» (NH4)2S04 + H20 + CaC03 , CaS04-2H20 + (NH4)2CO3 » (NH4)2SO4 + 2H20 + CaC03 j, and CaS04-2H2O + 2NH4HCO3 -» (NH4)2SO4 + CaC03 j + C02 | + 3H20.
21. The process according to claim 19 wherein phosphogypsum is reacted with an ammonia-carbon dioxide source in a counter current reaction mode with phosphogypsum being added and ammonium sulfate being removed upstream and the ammonia-carbon dioxide source being added and calcium carbonate being removed downstream.
22. The process according to claim 19, further comprising reacting the calcium carbonate with an organic acid to produce a calcium salt of the organic acid.
23. The method according to claim 22, wherein the organic acid is selected from the group consisting of propionic, 3-HP, acetic acid, formic acid and lactic acid.
24. The process according to claim 22, wherein carbon dioxide is produced in reacting the calcium carbonate with the organic acid, and the carbon dioxide is recycled to serve as a carbon dioxide source in reacting phosphogypsum with the ammonia-carbon dioxide source.
25. The process according to claim 24, wherein the carbon dioxide is produced in a gas stream, the carbon dioxide is adsorbed from the gas stream using an ammonia water solution, and the ammonia water solution, with carbon dioxide trapped therein is used as the ammonia-carbon dioxide source.
26. The process according to claim 22, wherein the phosphogypsum contains impurities, the calcium salt of the organic acid stays in a liquid, and most of the impurities remain as un-reacted solids.
27. The process according to claim 22, further comprising reacting the calcium salt of the organic acid with phosphoric acid to produce calcium phosphate and the organic acid.
28. The process according to claim 27, further comprising recycling the organic acid to react with the calcium carbonate.
29. The process according to claim 27, further comprising controlling the amount of the calcium salt of the organic acid to select between CaHPO4 and Ca(H2PO4)2..
30. The process according to claim 22 further comprising reacting the ammonium sulfate with the calcium salt of the organic acid to produce calcium sulfate and an ammonium salt of the organic acid.
31. The process according to claim 30, wherein the ammonium salt of the organic acid stays in a liquid.
32. The process according to claim 30, further comprising reacting the ammonium salt of the organic acid with phosphoric acid to produce ammonium phosphate and the organic acid.
33. The process according to claim 32, further comprising recycling the organic acid to react with the calcium carbonate.
34. The process according to claim 32, wherein the phosphoric acid contains liquid impurities, a portion of the ammonium phosphate remains in solution, and the method further comprises crystallizing the ammonium phosphate.
35. The process according to claim 32, wherein the phosphoric acid contains liquid impurities, and after reacting the ammonium salt of the organic acid with the phosphoric acid, reaction liquids remain comprising the organic acid, the liquid impurities and a portion of ammonium phosphate.
36. The process according to claim 35, further comprising: combining the reaction liquids with phosphoric acid containing liquid impurities to produce a combined stream; reacting the combined stream the calcium salt of the organic acid to produce calcium phosphate and the organic acid; and recycling the organic acid to react with the calcium carbonate.
37. The process according to claim 35, further comprising reacting the reaction liquids with the calcium salt of the organic to produce calcium phosphate.
38 A process comprising reacting phosphoric acid containing impurities with a calcium salt of an organic acid to produce calcium phosphate, solid impurities, and the organic acid.
39. The process according to claim 38, wherein the calcium salt of an organic acid stays in a liquid.
40. The process according to claim 38, wherein phosphoric acid containing liquid impurities is reacted with the calcium salt of the organic acid in a continuous process.
41. The process according to claim 38, wherein the calcium phosphate is separated from the solid impurities in a gravity reactor.
42. The process according to claim 41 , wherein solid impurities with a slower settling velocity are removed from the gravity reactor at a higher elevation than solid impurities with a faster settling velocity.
43. The process according to claim 38, wherein the phosphoric acid is produced from phosphate rock, the impurities comprise HF and H3AIF6, H2SiF6 and the solid impurities comprise CaF2 SiO2 and AIPO4.
44. The process according to claim 38, wherein a portion of the phosphoric acid remains un-reacted, and substantially all of the impurities are reacted.
45. The process according to claim 44, wherein the phosphoric acid that remains un-reacted and the calcium phosphate are reacted in a separate reactor with the calcium salt of the organic acid to produce the organic acid and calcium phosphate.
46. A method for producing a calcium salt of an organic acid, comprising: reacting calcium carbonate produced from phosphogypsum with the organic acid to produce the calcium salt of the organic acid.
47. The method according to claim 46, further comprising reacting the calcium salt of the organic acid with ammonium sulfate to produce gypsum.
48. The method according to claim 47, wherein the step of reacting the calcium salt of the organic acid with ammonium sulfate also produces an ammonium salt of the organic acid, and the method further comprises reacting phosphoric acid with the ammonium salt of the organic acid to produce ammonium phosphate.
49. The method according to claim 38, wherein the phosphoric acid is produced from phosphate rock.
50. A method for producing 3-HP, comprising: reacting phosphoric acid produced from phosphate rock with an ammonium or calcium salt of 3-HP to produce the 3-HP and ammonium or calcium phosphate.
PCT/US2005/018980 2004-05-28 2005-05-31 Phosphogypsum treatment process WO2005118222A2 (en)

Applications Claiming Priority (12)

Application Number Priority Date Filing Date Title
US57492704P 2004-05-28 2004-05-28
US57493004P 2004-05-28 2004-05-28
US60/574,930 2004-05-28
US60/574,927 2004-05-28
US57541604P 2004-06-01 2004-06-01
US57541504P 2004-06-01 2004-06-01
US60/575,416 2004-06-01
US60/575,415 2004-06-01
US61595404P 2004-10-06 2004-10-06
US61595504P 2004-10-06 2004-10-06
US60/615,955 2004-10-06
US60/615,954 2004-10-06

Publications (2)

Publication Number Publication Date
WO2005118222A2 true WO2005118222A2 (en) 2005-12-15
WO2005118222A3 WO2005118222A3 (en) 2006-07-20

Family

ID=35463393

Family Applications (1)

Application Number Title Priority Date Filing Date
PCT/US2005/018980 WO2005118222A2 (en) 2004-05-28 2005-05-31 Phosphogypsum treatment process

Country Status (1)

Country Link
WO (1) WO2005118222A2 (en)

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101830494A (en) * 2010-05-11 2010-09-15 安徽工业大学 Method for preparing active calcium carbonate by taking gypsum as raw material
CN102616811A (en) * 2012-04-12 2012-08-01 瓮福(集团)有限责任公司 Method for controlling pH (potential of hydrogen) of ammonium sulphate solution prepared by phosphogypsum
US8758719B2 (en) 2012-08-10 2014-06-24 Sparstane Technologies LLC Process for converting FGD gypsum to ammonium sulfate and calcium carbonate
CN104211099A (en) * 2014-08-23 2014-12-17 耿兆翔 Resource recycling method of industrial phosphogypsum waste residues
CN104907010A (en) * 2014-03-13 2015-09-16 中国科学院过程工程研究所 Reactor for mineralization fixation of carbon dioxide by fortified calcium-base solid wastes in ammonia medium system and application method thereof
CN106348316A (en) * 2016-08-25 2017-01-25 太仓市新星轻工助剂厂 Preparation method of ammonium sulfate
CN108975374A (en) * 2018-09-20 2018-12-11 秦皇岛天鼎化工有限公司 The method and calcium nitrate of calcium nitrate are prepared using ardealite
WO2020041507A1 (en) * 2018-08-21 2020-02-27 Evoqua Water Technologies Llc Methods and systems for treating phosphogypsum-containing water

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3951675A (en) * 1972-10-02 1976-04-20 Centre D'etudes Et De Recherches Des Phosphates Mineraux Cerphos Method for the treatment of phosphogypsum
US4328189A (en) * 1979-01-29 1982-05-04 Dr. C. Otto & Comp. G.M.B.H. Apparatus for the granulation of precipitation products formed from ammonium compounds

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3951675A (en) * 1972-10-02 1976-04-20 Centre D'etudes Et De Recherches Des Phosphates Mineraux Cerphos Method for the treatment of phosphogypsum
US4328189A (en) * 1979-01-29 1982-05-04 Dr. C. Otto & Comp. G.M.B.H. Apparatus for the granulation of precipitation products formed from ammonium compounds

Cited By (13)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101830494A (en) * 2010-05-11 2010-09-15 安徽工业大学 Method for preparing active calcium carbonate by taking gypsum as raw material
CN102616811A (en) * 2012-04-12 2012-08-01 瓮福(集团)有限责任公司 Method for controlling pH (potential of hydrogen) of ammonium sulphate solution prepared by phosphogypsum
US8758719B2 (en) 2012-08-10 2014-06-24 Sparstane Technologies LLC Process for converting FGD gypsum to ammonium sulfate and calcium carbonate
WO2014026120A3 (en) * 2012-08-10 2015-07-30 Sparstane Technologies LLC Process for converting fgd gypsum
JP2015528431A (en) * 2012-08-10 2015-09-28 スパーステイン テクノロジーズ エルエルシー Process for converting FGD gypsum to ammonium sulfate and calcium carbonate
CN104907010B (en) * 2014-03-13 2018-03-16 中国科学院过程工程研究所 A kind of reactor and application method for strengthening calcium base solid waste mineralising fixation carbon dioxide for ammonia solution system
CN104907010A (en) * 2014-03-13 2015-09-16 中国科学院过程工程研究所 Reactor for mineralization fixation of carbon dioxide by fortified calcium-base solid wastes in ammonia medium system and application method thereof
CN104211099A (en) * 2014-08-23 2014-12-17 耿兆翔 Resource recycling method of industrial phosphogypsum waste residues
CN106348316A (en) * 2016-08-25 2017-01-25 太仓市新星轻工助剂厂 Preparation method of ammonium sulfate
WO2020041507A1 (en) * 2018-08-21 2020-02-27 Evoqua Water Technologies Llc Methods and systems for treating phosphogypsum-containing water
WO2020041458A1 (en) * 2018-08-21 2020-02-27 Evoqua Water Technologies Llc Methods and systems for treating phosphogypsum-containing water
CN108975374A (en) * 2018-09-20 2018-12-11 秦皇岛天鼎化工有限公司 The method and calcium nitrate of calcium nitrate are prepared using ardealite
CN108975374B (en) * 2018-09-20 2020-12-18 秦皇岛天鼎化工有限公司 Method for preparing calcium nitrate by using phosphogypsum and calcium nitrate

Also Published As

Publication number Publication date
WO2005118222A3 (en) 2006-07-20

Similar Documents

Publication Publication Date Title
WO2005118222A2 (en) Phosphogypsum treatment process
JP5807284B2 (en) Method for producing high-purity ammonium sulfate and calcite using gypsum
US7374740B2 (en) Process for producing high purity phosphates
US4981664A (en) Method of production of high purity silica and ammonium fluoride
KR101518008B1 (en) Manufacturing method of ammonium sulfate
US5180569A (en) Process for the production of phosphoric acid and hydrogen fluoride from phosphate rock and fluosilicic acid
US4105748A (en) Method of producing phosphoric acid and potassium dihydrogen phosphate from phosphate rock in the substantial absence of fluorine evolution
CN108025923B (en) Method for preparing calcium fluoride from fluosilicic acid
US5165907A (en) Method of production of high purity silica and ammonium fluoride
CN101531384A (en) Technique for preparing electronic grade magnesium hydrate and ammonium sulphate by cycle serum featuring in flue gas desulfurization by method of magnesium oxidization
CN102438947B (en) Sodium cyanide process
US4331640A (en) Process for removing sulfur dioxide from an exhaust gas containing the same
US5531975A (en) Process for the production of phosphoric acid and calcium fluoride
CN105819415B (en) A kind of production method for the full utilization of resources of phosphorus ore that hydrochloric acid produces calcium hydrogen phosphate fodder
US5679315A (en) Method of production of high purity silica
WO1994018360A1 (en) Process for recovering solid sodium bicarbonate from diaphragm cell
CN114560486B (en) CO with leaching aid capable of being recycled 2 Indirect mineralization method
US4191734A (en) Fluoride-free phosphate reactions
US4062929A (en) Production of hydrogen fluoride
CN111392754B (en) Method and equipment for purifying calcium chloride from fluorine-containing solid waste
JPH04228401A (en) Production of hydrogen fluoride
JP3912878B2 (en) Method for producing SiF4 from phosphoric acid production process
JPS5827207B2 (en) Method for producing monocalcium phosphate and phosphoric acid
CN213416277U (en) Sewage recycling system for preparing hydrogen fluoride from fluosilicic acid
US20220332620A1 (en) Simplified sulphate removal for effluent treatment

Legal Events

Date Code Title Description
AK Designated states

Kind code of ref document: A2

Designated state(s): AE AG AL AM AT AU AZ BA BB BG BR BW BY BZ CA CH CN CO CR CU CZ DE DK DM DZ EC EE EG ES FI GB GD GE GH GM HR HU ID IL IN IS JP KE KG KM KP KR KZ LC LK LR LS LT LU LV MA MD MG MK MN MW MX MZ NA NG NI NO NZ OM PG PH PL PT RO RU SC SD SE SG SK SL SM SY TJ TM TN TR TT TZ UA UG US UZ VC VN YU ZA ZM ZW

AL Designated countries for regional patents

Kind code of ref document: A2

Designated state(s): BW GH GM KE LS MW MZ NA SD SL SZ TZ UG ZM ZW AM AZ BY KG KZ MD RU TJ TM AT BE BG CH CY CZ DE DK EE ES FI FR GB GR HU IE IS IT LT LU MC NL PL PT RO SE SI SK TR BF BJ CF CG CI CM GA GN GQ GW ML MR NE SN TD TG

121 Ep: the epo has been informed by wipo that ep was designated in this application
NENP Non-entry into the national phase

Ref country code: DE

WWW Wipo information: withdrawn in national office

Country of ref document: DE

122 Ep: pct application non-entry in european phase