GB2127003A - Gypsum conversion to potassium sulphate using anion exchange - Google Patents
Gypsum conversion to potassium sulphate using anion exchange Download PDFInfo
- Publication number
- GB2127003A GB2127003A GB08323073A GB8323073A GB2127003A GB 2127003 A GB2127003 A GB 2127003A GB 08323073 A GB08323073 A GB 08323073A GB 8323073 A GB8323073 A GB 8323073A GB 2127003 A GB2127003 A GB 2127003A
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- GB
- United Kingdom
- Prior art keywords
- potassium
- sulphate
- anion exchanger
- sodium
- slurry
- Prior art date
- Legal status (The legal status 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 status listed.)
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Classifications
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01F—COMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
- C01F11/00—Compounds of calcium, strontium, or barium
- C01F11/20—Halides
- C01F11/24—Chlorides
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J41/00—Anion exchange; Use of material as anion exchangers; Treatment of material for improving the anion exchange properties
- B01J41/04—Processes using organic exchangers
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01D—COMPOUNDS OF ALKALI METALS, i.e. LITHIUM, SODIUM, POTASSIUM, RUBIDIUM, CAESIUM, OR FRANCIUM
- C01D5/00—Sulfates or sulfites of sodium, potassium or alkali metals in general
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01D—COMPOUNDS OF ALKALI METALS, i.e. LITHIUM, SODIUM, POTASSIUM, RUBIDIUM, CAESIUM, OR FRANCIUM
- C01D5/00—Sulfates or sulfites of sodium, potassium or alkali metals in general
- C01D5/06—Preparation of sulfates by double decomposition
- C01D5/10—Preparation of sulfates by double decomposition with sulfates of magnesium, calcium, strontium, or barium
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- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Inorganic Chemistry (AREA)
- Engineering & Computer Science (AREA)
- Materials Engineering (AREA)
- Life Sciences & Earth Sciences (AREA)
- Geology (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Removal Of Specific Substances (AREA)
- Compounds Of Alkaline-Earth Elements, Aluminum Or Rare-Earth Metals (AREA)
- Treatment Of Water By Ion Exchange (AREA)
Abstract
Gypsum byproduct in the manufacture of phosphoric acid is converted into potassium sulphate or sodium sulphate by subjecting an aqueous slurry to anion exchange under acidic conditions. Adding solid potassium chloride to the obtained solution of potassium sulphate causes the latter to crystallize in pure state, the potassium chloride solution recovered after filtering off the crystallized potassium sulphate being used for the regeneration of the anion exchanger.
Description
SPECIFICATION
Gypsum conversion
This invention relates to a method for converting calcium sulphate into metal sulphates of higher value, and more particularly to a method for converting gypsum, which is obtained as a byproduct in the manufacture of phosphoric acid, into potassium or sodium sulphate by ion exchange.
Phosphoric acid is produced in large quantities for use in fertilizer manufacture. The phosphoric acid is generally produced by reacting phosphate rock with sulphuric acid. Phosphate rock is a naturally occurring product, the main constituent of which is fluorapatite substantially corresponding to the formula Ca5(PO4)3F. Thus, the chemical reaction for producing phosphoric acid can be written: Cas(PO4)3F+5H2SO4+ 1 OH2Oo 3H3PO4+H F+5CaSO4, 2H2O (1)
The phosphoric acid is separated from the byproduct gypsum by filtration. For each ton of H3PO4 about 3 tons of byproduct is produced.
This byproduct is known as phosphogypsum and is a product of low value due to impurities and high moisture content. It is therefore in most cases considered a waste product and discarded.
The safe disposal of the huge quantities of phosphogypsum being produced today represents an increasing environmental problem. In some areas it is deposited in ponds or piles, in which case care must be taken to prevent ground water contamination due to seepage. In other areas the gypsum is slurried with water and pumped into the ocean or into rivers. In such cases there is an increasing concern not only regarding the deposition of undissolved gypsum but also regarding the environmental effects due to the impurities, especially heavy metals, which originate from the phosphate rock.
From a natural resources point of view, also, the phosphogypsum represents a problem. The sulphuric acid used in equation (1) is produced from sulphur according to the following reactions: S+O2osO2 (2) SQ±2102+H2OH2SO4 (3)
The prices of sulphur have increased dramatically in recent years and thereby put a heavy economic burden on the phosphoric acid production. At the same time it can be seen from equation (1), that all the expensive sulphur ends up in the waste product and only the hydrogen ions from the sulphuric acid go into the valuable product, the phosphoric acid.
On the other hand, sulphates like potassium and sodium sulphates are produced from sulphuric acid and the corresponding chlorides in the so-called Mannheim processes: 2KCI+H2SO4oK2SO4+2HCI (4) 2NaCl+H2SO4oNa2SO4+2HCI (5)
Here, it can be seen that it is the sulphate that ends up in the main product, whereas the hydrogen ions go into the byproduct.
From a resource point of view, therefore, it would be desirable to develop a process whereby phosphogypsum could be converted into potassium or sodium sulphate in the following way: CaSQ+2KClK2SQ+CaCI2 (6) CaS04+2NaClNa2SQ+CaCl2 (7)
In that way the sulphuric acid could be used twice, firstly for supplying hydrogen ions for phosphoric acid production, and secondly for supplying sulphate ions for potassium and sodium sulphate production. At the same time the environmental problems relating to the phosphogypsum disposal could be solved, because it is technically possible to remove heavy metals from a calcium chloride solution, whereas it is not possible to remove them from gypsum crystals.
It is well known, that for solubility reasons the reactions (6) and (7) cannot be carried through by simple salt conversion in aqueous media.
It is the object of the present invention to provide a process whereby the overall reactions (6) and (7) are obtained by ion exchange.
The British Patent No. 1,1 66,930 describes an ion exchange process where calcium ions from a solution of phosphate rock in a mineral acid are exchanged with potassium ions from a cation exchanger. The spent ion exchanger is regenerated, i.e. recharged with potassium ions, by treatment with a potassium chloride solution.If the mineral acid is nitric acid, the reactions may be written as follows, where R indicates the organic portion of the ion exchanger:
Production: Ca(N03)2+2 KR2KNO3+CaR2 (8)
Regeneration: CaR2+2KClo2KR+Cacl2 (9)
Overall: Ca(N03)2+2KCk2KNO3+CaCl2 (10)
If phosphogypsum is slurried with water and similar processes attempted, the corresponding reactions can be written as follows:
Production: CaSO4+2KRoK2SO4+CaR2 (11)
Regeneration: CaR2+2KClo2KR+Cacl2 (12)
Overall: CaSO4+2KCleK2SO4+Cacl2 (6) This method is not industrially feasible due to the low solubility of calcium sulphate.A saturated solution of gypsum contains only about 2 grams per litre of CaSO4 in solution, and when the reaction (11) takes place, the sulphate ions are not removed, which due to the solubility product limits the amount of calcium ions that can go into solution from the slurried gypsum and thereby made available for further ion exchange according to reaction (11). The result is large quantities of solutions of low concentrations and poor efficiency of the ion exchanger. The method becomes industrially unattractive.
However, it has been found that the problems can be overcome and very good results obtained, if anion exchange under acidic conditions is employed as follows:
Production: 2KCI+R2SO4oK2SO4+2RCI (13)
Regeneration: 2RCl+CaSO4eR2SO4+cacl2 (14)
Overall: CaSQ+2KCIK2SQ+CaCI2 (6)
The acidic conditions in reaction (14), e.g. pH between 0 and 4, can be obtained by adding sulphuric or hydrochloric acid to the gypsum slurry.
By this method the ion exchange process in reaction (14) does not come to a stop like in reaction (1 1), because the solubility of gypsum in the calcium chloride solution at low pH appears to be higher than in water in spite of the high calcium ion concentration in the calcium chloride solution, i.e. the solubility product of calcium ions and sulphate ions is higher. For instance, in a 4% calcium chloride solution at pH 1-obtained by adding HCl-a solubility of 4 grams per litre of CaSO4 has been found.
This means, that when phosphogypsum is slurried with water and brought into contact at low pH with a chloride-loaded anion exchanger, the reaction (14) will start, and along with the removal of sulphate ions from the solution more gypsum will go into solution to supply more sulphate ions for ion exchange. In this case the further solubilization of gypsum will not be impeded like in reaction (1 1).
In the industrial application of the method it is important for economic reasons to avoid excessive dilution of the product solution from reaction (1 3) containing the potassium sulphate. Such dilution occurs in the conventional ion exchange technique using fixed bed exchangers. The British Patent No.
1,307,218 describes a method and plant for effecting mass transfer processes, whereby this dilution is avoided. We have found that when using this method and plant for the present purpose it is preferable to use upflow instead of downflow movement of the liquids through the resin beds in order to avoid biocking of the resin bed due to the suspended gypsum crystals in reaction (14).
Furthermore, it has been found that the evaporation costs relating to the product solution from reaction (13) can be minimized by solubilizing solid potassium chloride in said production solution, whereby potassium sulphate can be crystallized out and separated, and the mother liquor can be recycled and used for reacting with the sulphate-loaded anion exchange resin in reaction (13). At the same time this procedure permits a very high surplus of KCI over the theoretical amount in reaction (13) to be used without any losses of KCI.
It is well known that an addition of a solubility depressor, f.inst. methanol, for the sulphate, to media corresponding to the recycling mother liquor will increase the ratio of chloride to sulphate in such media.
This can be utilized in the present invention to increase the efficiency of the ion exchange process and hence decrease the investment costs of a plant, and since the mother liquor is still recycled in the present process, such addition can be done without any further costs for recovering the solubility depressor.
If sodium sulphate instead of potassium sulphate is wanted, the reactions are:
Production: 2NaCI +R2SO4oNa2SO4+2RCI (1 5) Regeneration: 2RCI +CaSO4eR2SO4+CaCl2 (1 6) Overall: CaSO4+2NaCleNa2SO4+cacl2 (7)
If sea water is available and fresh water supply scarce or expensive, the phosphogypsum may be slurried with sea water instead of fresh water. Thereby the economics of the process may be further improved.
It is well known that anion exchangers generally have a higher selectivity for SC4- than HSQ and Cl and that the different types of exchangers have different selectivity coefficients. For the purpose of the present invention it is preferable to use a type with a very high selectivity for the sulphate ion, f.inst.
Dowex WGR, which is epoxy-based, or Duolite A374 or Amberlite IRA 60 which are acryl-based.
The following examples are illustrative of the process of the invention:
Example 1
5 kg of phosphogypsum crystals from a phosphoric acid filter were wet ground and slurried with 100 kg of sea water. The pH was adjusted to about 3 by adding sulphuric acid and the slurry was reacted with 35 litre of Duolite A 374 (a polyfunctional amine type anion exchanger based on an acrylic matrix) loaded with chloride ions. The effluent contained 2.5% CaCI2. The treated anion exchanger was reacted with 40 kg of the recirculating KCI-solution mentioned below containing 25% KCI. To the effluent was added 3.5 kg solid KCI during agitation which resulted in 4 kg of K2S04 crystallising out.
After separation of the K2S04-crystals the mother liquor was recirculated for reacting with the abovementioned anion exchanger.
Example2
A pilot ion exchange plant according to British Patent No. 1 307,21 8 comprising 11 resin beds each containing 12 litre of Duolite A 374 anion exchange resin was used for this experiment. 350 litre per hour of an aqueous slurry containing 5% calcium sulphate and having a pH of 2.5 (obtained by adding sulphuric acid) was pumped into the ion exchange loop. Simultaneously, a recirculating potassium chloride solution containing 25% KCI was pumped into the loop at a rate of 1 60 litre per hour. The product solution containing KCI and K2S04 was fed continuously to a crystallizer which also received solid KCI at a rate of 13 kg per hour.The overflow from the crystallizer went to a classifier in order to separate the potassium sulphate crystals from the potassium chloride solution which was recycled to the ion exchange loop. 14 kg per hour of high purity K2S04 was produced. A washed and dried sample of the product showed 44.7% K, 54.6% SO4 and 0.02% Cl.
Example 3
1.5 kg of calcium sulphate was slurried with 30 litre of fresh water and the pH adjusted to about 3 by adding sulphuric acid. The slurry was reacted with 1 2 litre of Duolite A 374 anion exchange resin loaded with chloride ions. In a sample from the effluent a content of 3% CaCI2 was measured. The treated anion exchanger was reacted with 1 2 kg of a 24% NaCI-solution. To the effluent was added 0.85 kg solid NaCI and 1 kg of Na2SO4 was recovered by crystallization and separation.
Claims (1)
- Claims1. A process for converting calcium sulphate into potassium sulphate by ion exchange, characterized in reacting an aqueous calcium sulphate slurry at a low pH with an anion exchanger with chloride ions, recovering potassium or sodium sulphate from the effluent from the exchanger, and regenerating the anion exchanger with a potassium or sodium chloride solution.2. A process according to claim 1 in which a pH between 0 and 4 in the calcium sulphate slurry is obtained by adding sulphuric or hydrochloric acid.3. A process according to claim 1 in which solid potassium or sodium sulphate is recovered from the potassium or sodium sulphate containing solution by solubilizing solid potassium or sodium chloride in said solution, separating the precipitated potassium or sodium sulphate crystals and recycling the mother liquor after separation for reacting with the sulphate loaded anion exchanger.4. A process according to claim 1 in which the fresh water used for preparing the calcium sulphate slurry is partly or fully replaced by sea water.5. A process according to claim 1, substantially as hereinbefore described with reference to any of the Examples.6. Potassium or sodium sulphate when prepared by a process according to any of claims 1 to 5.New claims or amendments to claims filed on 21 November, 83 Superseded claim 1 New or amended claims:1. A process for converting calcium sulphate into potassium or sodium sulphate by ion exchange characterized in reacting an aqueous calcium sulphate slurry at low pH with an anion exchanger charged with chloride ions, separating the treated slurry from the treated anion exchanger and recovering a potassium or sodium sulphate containing solution by reacting the treated anion exchanger with a potassium or sodium chloride solution.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
GB08323073A GB2127003B (en) | 1982-09-02 | 1983-08-26 | Gypsum convertion to potassium sulphate using anion exchange |
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
GB8225006 | 1982-09-02 | ||
GB08323073A GB2127003B (en) | 1982-09-02 | 1983-08-26 | Gypsum convertion to potassium sulphate using anion exchange |
Publications (3)
Publication Number | Publication Date |
---|---|
GB8323073D0 GB8323073D0 (en) | 1983-09-28 |
GB2127003A true GB2127003A (en) | 1984-04-04 |
GB2127003B GB2127003B (en) | 1986-09-17 |
Family
ID=26283718
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
GB08323073A Expired GB2127003B (en) | 1982-09-02 | 1983-08-26 | Gypsum convertion to potassium sulphate using anion exchange |
Country Status (1)
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GB (1) | GB2127003B (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
FR2580617A1 (en) * | 1985-04-17 | 1986-10-24 | Kali & Salz Ag | Process for the manufacture of potassium sulphate from potassium chloride by means of an ion exchanger |
EP0199104A2 (en) * | 1985-03-27 | 1986-10-29 | Potash Corporation of Saskatchewan | The production of potassium sulphate |
-
1983
- 1983-08-26 GB GB08323073A patent/GB2127003B/en not_active Expired
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
EP0199104A2 (en) * | 1985-03-27 | 1986-10-29 | Potash Corporation of Saskatchewan | The production of potassium sulphate |
EP0199104A3 (en) * | 1985-03-27 | 1987-10-28 | Potash Corporation of Saskatchewan | The production of potassium sulphate |
FR2580617A1 (en) * | 1985-04-17 | 1986-10-24 | Kali & Salz Ag | Process for the manufacture of potassium sulphate from potassium chloride by means of an ion exchanger |
Also Published As
Publication number | Publication date |
---|---|
GB2127003B (en) | 1986-09-17 |
GB8323073D0 (en) | 1983-09-28 |
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Legal Events
Date | Code | Title | Description |
---|---|---|---|
732 | Registration of transactions, instruments or events in the register (sect. 32/1977) | ||
PE20 | Patent expired after termination of 20 years |