EP0066988A2 - Method of recovering uranium - Google Patents

Method of recovering uranium Download PDF

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Publication number
EP0066988A2
EP0066988A2 EP82302566A EP82302566A EP0066988A2 EP 0066988 A2 EP0066988 A2 EP 0066988A2 EP 82302566 A EP82302566 A EP 82302566A EP 82302566 A EP82302566 A EP 82302566A EP 0066988 A2 EP0066988 A2 EP 0066988A2
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EP
European Patent Office
Prior art keywords
coprecipitate
uranium
leachate
nitric acid
silicate
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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Application number
EP82302566A
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German (de)
French (fr)
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EP0066988A3 (en
Inventor
Edward Jean Lahoda
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CBS Corp
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Westinghouse Electric Corp
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Publication of EP0066988A2 publication Critical patent/EP0066988A2/en
Publication of EP0066988A3 publication Critical patent/EP0066988A3/en
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    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B60/00Obtaining metals of atomic number 87 or higher, i.e. radioactive metals
    • C22B60/02Obtaining thorium, uranium, or other actinides
    • C22B60/0204Obtaining thorium, uranium, or other actinides obtaining uranium
    • C22B60/0217Obtaining thorium, uranium, or other actinides obtaining uranium by wet processes
    • C22B60/0221Obtaining thorium, uranium, or other actinides obtaining uranium by wet processes by leaching
    • C22B60/0226Obtaining thorium, uranium, or other actinides obtaining uranium by wet processes by leaching using acidic solutions or liquors
    • C22B60/0239Obtaining thorium, uranium, or other actinides obtaining uranium by wet processes by leaching using acidic solutions or liquors nitric acid containing ion as active agent
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B60/00Obtaining metals of atomic number 87 or higher, i.e. radioactive metals
    • C22B60/02Obtaining thorium, uranium, or other actinides
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B60/00Obtaining metals of atomic number 87 or higher, i.e. radioactive metals
    • C22B60/02Obtaining thorium, uranium, or other actinides
    • C22B60/0204Obtaining thorium, uranium, or other actinides obtaining uranium
    • C22B60/0217Obtaining thorium, uranium, or other actinides obtaining uranium by wet processes
    • C22B60/0252Obtaining thorium, uranium, or other actinides obtaining uranium by wet processes treatment or purification of solutions or of liquors or of slurries
    • C22B60/026Obtaining thorium, uranium, or other actinides obtaining uranium by wet processes treatment or purification of solutions or of liquors or of slurries liquid-liquid extraction with or without dissolution in organic solvents

Definitions

  • This invention relates to recovering uranium from a silicate-uranium coprecipitate.
  • a waste stream is produced which contains uranium, fluoride, ammonium, and nitrate ions.
  • a calcium hydroxide or lime slurry is added which precipitates calcium fluoride.
  • the ammonium diuranate waste stream is processed in an ammonia stripping column and the calcium fluoride slurry is sent to settling lagoons were excess water is decanted and run off. Some of the uranium remains in the calcium fluoride slurry as insoluble calcium uranate.
  • the calcium uranate waste creates an expensive disposal problem and is a loss of a valuable resource.
  • the quantity of uranium contaminated waste can be reduced by adding sodium silicate to the uranium waste stream prior to the addition of calcium hydroxide or lime as is described in Japanese Patent Specification No. 48-38320. This results in a silicate-uranium coprecipitate of significantly less volume than the calcium fluoride precipitate. The silicate-uranium coprecipitate is then disposed of by storage in drums.
  • the present invention resides in a method of recovering uranium from a silicate-uranium coprecipitate which comprises leaching said coprecipitate with a leachate having a pH of from 2 to 3 followed by filtering said coprecipitate.
  • uranium recovered that would otherwise be wasted, but it is recovered in a form which can be processed in a standard solvent extraction cycle. Moreover, if desired, sufficient uranium can be removed from the coprecipitate to permit its disposal as a non-nuclear waste material.
  • a silicate-uranium coprecipitate is typically formed by adding a solution of water glass to an ammonium fluoride solution containing uranium in order to concentrate the uranium in the coprecipitate.
  • a typical coprecipitate may contain about 15% (all percentages herein are by weight) by weight sodium silicate, about 85% water, and from 1,000 to 30,000 parts per million (ppm) of uranium, probably in the form of a uranyl silicate.
  • the typical coprecipitate is a toothpaste-like solid containing large amounts of bound water.
  • the invention will work with any silicate-uranium coprecipitate containing virtually any amount of uranium. It is preferable to wash the coprecipitate first in order to minimize the fluoride content in it as fluorides tend to attack silicates and increase their dissolution, thus reducing the degree of separation of the uranium.
  • the first step involves lowering the pH of the coprecipitate to from 2 to 3. It has been found that this pH range is essential to the successful operation of the invention because below a pH of 2 the silica begins to dissolve which interferes with the subsequent solvent extraction of the uranium from the filtrate, and above a pH of 3, the uranium is not solubilized. The optimum pH has been found to be about 2.3.
  • the leachate is an inorganic acid which can solubilize the uranium within the specified pH range.
  • Nitric acid is the preferred leachate as it has been found to work very well and it is compatible with the processes which follow the process of this invention, but hydrochloric or sulfuric acid could also be used if desired. If a nitric acid leachate is used, it is preferably from 5 to 20% aqueous nitric acid.
  • the weight ratio of coprecipitate to leachate is preferably from 1:1 to 3:1.
  • the leachate After the leachate has been mixed with the coprecipitate, it is desirable to filter as soon as possible, preferably within one-half hour, as the silica will gradually dissolve in the leachate and silica which does not dissolve will become hydrolyzed and difficult to filter.
  • the wash is preferably performed with from 5 to 20% aqueous nitric acid. From 4 to 7 washes are usually satisfactory as fewer washes will leave uranium behind in the coprecipitate and more washes will dilute the filtrate and dissolve more silica.
  • the weight ratio of coprecipitate to each wash is preferably from 0.5:1 to 1.5:1 as less wash will not recover all the uranium that could be recovered and more wash will dilute the filtrate.
  • the uranium in the filtrate can be recovered by any of a variety of well-known techniques.
  • the preferred technique is solvent extraction using an organic extractant containing di-2-ethylhexyl phosphoric acid and trioctyl phosphine oxide (DEPA-TOPO) as that method is very effective.
  • DEPA-TOPO trioctyl phosphine oxide
  • a silicate uranium coprecipitate was mixed with a nitric acid leachate in a leach tank. After filtering, for example, in a pressurized rotary filter, a wash was used which resulted in a liquid filtrate, leaving behind the solids.
  • a silicate uranium coprecipitate was prepared by mixing two compositions.
  • the first composition contained 2% ammonium fluoride, 4% ammonia (added as ammonium hydroxide), 91% water, and 15 ppm uranium (added as uranyl nitrate).
  • the second composition contained 6% silica (added as sodium silicate) and the remainder water. Ninety-nine parts of the first composition were mixed with one part of the second composition and the mixture was stirred for one minute and filtered.
  • Test No. 1 shows that this process will work well at nitric acid levels as high as 20%. However, since satisfactory results are obtained at 10% nitric acid (Test No. 4), the added nitric acid expense is not economically justified.
  • Test No. 2 shows that not all of the uranium is recovered when the pH is too high.
  • Test No. 3 shows that a low recovery is obtained with too much nitric acid, and the pH is too low.
  • Test No. 4 shows that better results are obtained when the coprecipitate is washed to remove fluoride first.
  • Test No. 5 shows that good results can be obtained even without washing to remove-fluoride if the nitric acid concentration is not too high.
  • Test No. 6 shows that an increased leach solution to cake ratio dilutes the final uranyl nitrate stream.

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  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • General Life Sciences & Earth Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Geology (AREA)
  • Manufacturing & Machinery (AREA)
  • Environmental & Geological Engineering (AREA)
  • Materials Engineering (AREA)
  • Mechanical Engineering (AREA)
  • Metallurgy (AREA)
  • Organic Chemistry (AREA)
  • Manufacture And Refinement Of Metals (AREA)
  • Inorganic Compounds Of Heavy Metals (AREA)
  • Removal Of Specific Substances (AREA)

Abstract

Method of recovering uranium from a silicate-uranium coprecipitate by leaching the coprecipitate with a leachate having a pH of from 2 to 3, followed by filtering the coprecipitate. The uranium is dissolved in the filtrate but the silicate is insoluble. The leachate is preferably an aqueous solution of nitric acid which is also used to wash the coprecipitate. The uranium can be extracted from the filtrate using an organic extractant containing DEPA-TOPO.

Description

  • This invention relates to recovering uranium from a silicate-uranium coprecipitate.
  • In an ammonium diuranate conversion process for producing uranium oxide powder, a waste stream is produced which contains uranium, fluoride, ammonium, and nitrate ions. To recover the ammonia and lower the fluoride levels, a calcium hydroxide or lime slurry is added which precipitates calcium fluoride. The ammonium diuranate waste stream is processed in an ammonia stripping column and the calcium fluoride slurry is sent to settling lagoons were excess water is decanted and run off. Some of the uranium remains in the calcium fluoride slurry as insoluble calcium uranate.
  • The calcium uranate waste creates an expensive disposal problem and is a loss of a valuable resource. The quantity of uranium contaminated waste can be reduced by adding sodium silicate to the uranium waste stream prior to the addition of calcium hydroxide or lime as is described in Japanese Patent Specification No. 48-38320. This results in a silicate-uranium coprecipitate of significantly less volume than the calcium fluoride precipitate. The silicate-uranium coprecipitate is then disposed of by storage in drums.
  • Accordingly, the present invention resides in a method of recovering uranium from a silicate-uranium coprecipitate which comprises leaching said coprecipitate with a leachate having a pH of from 2 to 3 followed by filtering said coprecipitate.
  • Not only is uranium recovered that would otherwise be wasted, but it is recovered in a form which can be processed in a standard solvent extraction cycle. Moreover, if desired, sufficient uranium can be removed from the coprecipitate to permit its disposal as a non-nuclear waste material.
  • A silicate-uranium coprecipitate is typically formed by adding a solution of water glass to an ammonium fluoride solution containing uranium in order to concentrate the uranium in the coprecipitate.- A typical coprecipitate, for example, may contain about 15% (all percentages herein are by weight) by weight sodium silicate, about 85% water, and from 1,000 to 30,000 parts per million (ppm) of uranium, probably in the form of a uranyl silicate. The typical coprecipitate is a toothpaste-like solid containing large amounts of bound water. The invention, however, will work with any silicate-uranium coprecipitate containing virtually any amount of uranium. It is preferable to wash the coprecipitate first in order to minimize the fluoride content in it as fluorides tend to attack silicates and increase their dissolution, thus reducing the degree of separation of the uranium.
  • The first step involves lowering the pH of the coprecipitate to from 2 to 3. It has been found that this pH range is essential to the successful operation of the invention because below a pH of 2 the silica begins to dissolve which interferes with the subsequent solvent extraction of the uranium from the filtrate, and above a pH of 3, the uranium is not solubilized. The optimum pH has been found to be about 2.3. The leachate is an inorganic acid which can solubilize the uranium within the specified pH range. Nitric acid is the preferred leachate as it has been found to work very well and it is compatible with the processes which follow the process of this invention, but hydrochloric or sulfuric acid could also be used if desired. If a nitric acid leachate is used, it is preferably from 5 to 20% aqueous nitric acid. The weight ratio of coprecipitate to leachate is preferably from 1:1 to 3:1.
  • After the leachate has been mixed with the coprecipitate, it is desirable to filter as soon as possible, preferably within one-half hour, as the silica will gradually dissolve in the leachate and silica which does not dissolve will become hydrolyzed and difficult to filter.
  • Once the leachate has been filtered from the coprecipitate, it is preferable to wash the coprecipitate several times in order to maximize the recovery of the uranium that is present in it. The wash is preferably performed with from 5 to 20% aqueous nitric acid. From 4 to 7 washes are usually satisfactory as fewer washes will leave uranium behind in the coprecipitate and more washes will dilute the filtrate and dissolve more silica. The weight ratio of coprecipitate to each wash is preferably from 0.5:1 to 1.5:1 as less wash will not recover all the uranium that could be recovered and more wash will dilute the filtrate.
  • The uranium in the filtrate can be recovered by any of a variety of well-known techniques. The preferred technique is solvent extraction using an organic extractant containing di-2-ethylhexyl phosphoric acid and trioctyl phosphine oxide (DEPA-TOPO) as that method is very effective.
  • If desired, further washes or higher concentrations of acids in the leachate can be used to reduce the uranium in the coprecipitate to a level sufficient for disposal as a non-nuclear waste. However, it may be less expensive to dispose of the small quantity of coprecipitate as a nuclear waste than to reduce its uranium content to such a low level.
  • The invention will now be illustrated with reference to the following Examples:
  • EXAMPLE 1
  • A silicate uranium coprecipitate was mixed with a nitric acid leachate in a leach tank. After filtering, for example, in a pressurized rotary filter, a wash was used which resulted in a liquid filtrate, leaving behind the solids.
    Figure imgb0001
  • EXAMPLE 2
  • A silicate uranium coprecipitate was prepared by mixing two compositions. The first composition contained 2% ammonium fluoride, 4% ammonia (added as ammonium hydroxide), 91% water, and 15 ppm uranium (added as uranyl nitrate). The second composition contained 6% silica (added as sodium silicate) and the remainder water. Ninety-nine parts of the first composition were mixed with one part of the second composition and the mixture was stirred for one minute and filtered.
  • In these experiments, various concentrations of a nitric acid leachate were poured over samples of the coprecipitate, stirred, and quickly filtered. The following table gives the results of three experiments where the concentration of silica leached by the nitric acid was determined.
    Figure imgb0002
  • The above table shows that only small quantities of silica were leached using 10 wt.% nitric acid and that much larger quantities of silica were leached using 20 wt.% nitric acid. It has been experimentally determined for the particular coprecipitate being tested that 10 wt.% nitric acid results in a pH of 2.3 (the pH obtained using 10 wt.% nitric acid, however, will depend on the particular composition of the coprecipitate used.)
  • In the next series of experiments, the amount of uranium leached under various conditions was determined. The following table gives the conditions and results.
    Figure imgb0003
    Figure imgb0004
  • Test No. 1 shows that this process will work well at nitric acid levels as high as 20%. However, since satisfactory results are obtained at 10% nitric acid (Test No. 4), the added nitric acid expense is not economically justified.
  • Test No. 2 shows that not all of the uranium is recovered when the pH is too high. Test No. 3 shows that a low recovery is obtained with too much nitric acid, and the pH is too low. Test No. 4 shows that better results are obtained when the coprecipitate is washed to remove fluoride first. Test No. 5 shows that good results can be obtained even without washing to remove-fluoride if the nitric acid concentration is not too high. Test No. 6 shows that an increased leach solution to cake ratio dilutes the final uranyl nitrate stream.

Claims (10)

1. A method of recovering uranium from a silicate-uranium coprecipitate characterized by leaching said coprecipitate with a leachate having a pH of from 2 to 3 followed by filtering said coprecipitate.
2. A method according to claim 1, characterized in that the leachate is aqueous nitric acid.
3. A method according to claim 2 characterized in that the nitric acid is from 5 to 20%.
4. A method according to claim 2 or 3, characterized in that, after leaching, the coprecipitate is washed with from 5 to 20% nitric acid.
5. A method according to claim 4, characterized in that the coprecipitate is washed 4 to 7 times.
6. A method according to any of claims 1 to 5, claim 1 characterized in that the weight ratio of the coprecipitate to the leachate is from 0.5 to 1 to 1.5 to 1.
7. A method according to any of claims 1 to 5, characterized in that the weight ratio of the coprecipitate to the leachate is from 1 to 1 to 3 to 1.
8. A method according to any of the preceding claims, characterized in that the coprecipitate is filtered within one-half hour after the leaching.
9. A method according to any of the preceding claims, characterized in that the coprecipitate is formed by the addition of water glass to an ammonium fluoride solution containing uranium.
10. A method according to any of the preceding claims, characterized in that in an additional last step uranium in the filtrate is extracted with a DEPA-TOPO extractant.
EP82302566A 1981-05-22 1982-05-20 Method of recovering uranium Withdrawn EP0066988A3 (en)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
US26667681A 1981-05-22 1981-05-22
US266676 1981-05-22

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EP0066988A2 true EP0066988A2 (en) 1982-12-15
EP0066988A3 EP0066988A3 (en) 1983-11-02

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EP (1) EP0066988A3 (en)
JP (1) JPS57200225A (en)
KR (1) KR830010209A (en)
ES (1) ES512465A0 (en)
YU (1) YU109182A (en)
ZA (1) ZA823094B (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0433860A2 (en) * 1989-12-20 1991-06-26 Westinghouse Electric Corporation Waterglass precipitate recovery process
CN105969987A (en) * 2016-06-16 2016-09-28 南华大学 Method for leaching uranium in radioactive alkali residues

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR101047985B1 (en) * 2010-11-26 2011-07-13 한국지질자원연구원 High efficient uranium leaching method using ultrasonic wave

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3394997A (en) * 1965-04-12 1968-07-30 Gen Electric Method of preparing uranium diuranate
JPS5327800A (en) * 1976-08-25 1978-03-15 Mitsubishi Metal Corp Uranium or/and thorium removingand recovering method from soln. containing uranium or/and thorium
JPS5692123A (en) * 1979-12-25 1981-07-25 Mitsubishi Metal Corp Removing and recovering method for uranium and/or thorium from solution containing uranium and/or thorium
JPS56109825A (en) * 1980-02-01 1981-08-31 Mitsubishi Metal Corp Removing and recovering method for uranium and/or thorium from liquor containing uranium and/or thorium

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3394997A (en) * 1965-04-12 1968-07-30 Gen Electric Method of preparing uranium diuranate
JPS5327800A (en) * 1976-08-25 1978-03-15 Mitsubishi Metal Corp Uranium or/and thorium removingand recovering method from soln. containing uranium or/and thorium
JPS5692123A (en) * 1979-12-25 1981-07-25 Mitsubishi Metal Corp Removing and recovering method for uranium and/or thorium from solution containing uranium and/or thorium
JPS56109825A (en) * 1980-02-01 1981-08-31 Mitsubishi Metal Corp Removing and recovering method for uranium and/or thorium from liquor containing uranium and/or thorium

Non-Patent Citations (3)

* Cited by examiner, † Cited by third party
Title
Patent Abstracts of Japan Vol. 2, no. 66, 19 May 1978 Page 1196M78 & JP-A-53-27800 *
Patent Abstracts of Japan Vol. 5, no. 160, 15 October 1981 & JP-A-56-92123 & US-A-4 349 513 (Cat. X,E) *
Patent Abstracts of Japan Vol. 5, no. 184, 21 November 1981 & JP-A-56-109825 & US-A-4 338 286 (Cat. X,E) *

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0433860A2 (en) * 1989-12-20 1991-06-26 Westinghouse Electric Corporation Waterglass precipitate recovery process
EP0433860A3 (en) * 1989-12-20 1992-07-08 Westinghouse Electric Corporation Waterglass precipitate recovery process
CN105969987A (en) * 2016-06-16 2016-09-28 南华大学 Method for leaching uranium in radioactive alkali residues
CN105969987B (en) * 2016-06-16 2018-01-09 南华大学 The leaching method of uranium in radioactivity alkaline residue

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Publication number Publication date
ZA823094B (en) 1983-06-29
YU109182A (en) 1985-03-20
KR830010209A (en) 1983-12-26
ES8403975A1 (en) 1984-04-01
ES512465A0 (en) 1984-04-01
EP0066988A3 (en) 1983-11-02
JPS57200225A (en) 1982-12-08

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