GB1560873A - Nickel recovery - Google Patents

Nickel recovery Download PDF

Info

Publication number
GB1560873A
GB1560873A GB6002/78A GB600278A GB1560873A GB 1560873 A GB1560873 A GB 1560873A GB 6002/78 A GB6002/78 A GB 6002/78A GB 600278 A GB600278 A GB 600278A GB 1560873 A GB1560873 A GB 1560873A
Authority
GB
United Kingdom
Prior art keywords
nickel
ammonia
solution
ammine
line
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.)
Expired
Application number
GB6002/78A
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Tohoku University NUC
Original Assignee
Tohoku University NUC
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 Tohoku University NUC filed Critical Tohoku University NUC
Publication of GB1560873A publication Critical patent/GB1560873A/en
Expired legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B23/00Obtaining nickel or cobalt
    • C22B23/04Obtaining nickel or cobalt by wet processes
    • C22B23/0407Leaching processes
    • C22B23/0446Leaching processes with an ammoniacal liquor or with a hydroxide of an alkali or alkaline-earth metal
    • 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
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling

Description

(54) NICKEL RECOVERY (71) I, The President of Tohoku University is a Japanese citizen of No. 1-1, Katahira 2-chome, Sendai-shi, Miyagi-ken, Japan 980, do hereby declare the invention, for which I pray that a patent may be granted to me, and the method by which it is to be performed, to be particularly described in and by the following statement:- This invention relates to a method of recovering nickel from a nickel-containing residue such as coal ash, and more particularly, to a method of recovering nickel selectively from a residue obtained after a carbonaceous material such as coal is gasified in the presence of a nickelcontaining catalyst.
It is well known that carbonaceous materials like coal are gasified, for example, to produce coal gas. According to conventional methods, carbonaceous materials or those pretreated with heat and/or various solvents are gasified at elevated temperatures in the absence of a catalyst using a gasifying agent such as hydrogen, steam, carbon dioxide and the like.
The present inventors have previously proposed an improvement in such gasification, which is disclosed in Patent Specification No. 1,496,410. Carbonaceous materials are gasified by pretreating them with liquid ammonia at room temperature to 1500C to extract the matters soluble in ammonia and treating the extraction residue with a gasifying agent at a temperature of 400 to 1,0000C at atmospheric pressure or under pressure in the presence or absence of a catalyst.
Nickel-containing catalysts are useful in the above gasification. Nickel catalysts should be present in an amount which is effective for catalytically promoting the gasification of carbonaceous materials.
Upon gasification, the nickel used is discharged partly with the gas produced and partly with residues such as coke and ash.
Loss of nickel is detrimental because nickel is so expensive. In order to carry out such catalytic gasification methods commercially advantageously and successfully, it is important to recover expensive nickel efficiently in a more simple manner and to regenerate it for reuse. However, no method has yet succeeded in the efficient separation or recovery of nickel because nickel is contained in minor amounts and relatively large amounts of impurities coexist.
The present inventors have made intensive and extensive investigations on the recovery of nickel; and have found that nickel can be selectively extracted or separated in the form of an aqueous nickel amine solution from a nickel-containing residue obtained after gasification and that, although the solubility of nickel ammine in water is considerably high at about room temperature, it rapidly decreases to a substantially insoluble level as the concentration of free ammonia increases.
The concentration of free ammonia can be increased simply by adding ammonia to the solution. The term "free ammonia" used herein designates an excess amount of ammonia which exceeds 6 molar equivalents per mole of nickel in the residue.
According to the present invention there is provided a method of recovering nickel from a nickel-containing residue such as coal ash remaining after a carbonaceous material is gasified in the presence of a nickel-containing catalyst, which comprises the steps of: (a) adding an aqueous ammonia solution or aqueous solution containing ammonia and an ammonium salt to the nickelcontaining residue in the presence of oxygen and/or air to dissolve the nickel in the solution in the form of a nickel ammine complex salt: (b) separating the aqueous nickel ammine solution from insoluble contents; (c) further adding ammonia to the separated aqueous nickel ammine solution to increase the concentration of free ammonia to a value high enough to precipitate the nickel ammine; and (d) separating the nickel ammine precipitate from the solution.
The separated nickel ammine may be converted into nickel oxide or nickel salts or into any desired form ready for reuse in a circulating manner, for example, metallic nickel. Such conversion is generally performed by heating.
The term "nickel ammine" designates a nickel ammine complex salt in this specification.
A preferred embodiment of the invention includes the following additional steps: (e) heating the separated nickel ammine to decompose it into nickel oxide or a nickel salt and ammonia; and (f) circulating the saturated nickel ammine solution resulting from the separation step (d) to step (a) and the ammonia resulting from the decomposition step (e) to step (c) for the reuse thereof.
The carbonaceous materials used herein include brown coal, lignite, bituminous coal, tar pitch, coke and their analogues.
After they are gasified with a gasifying agent in the presence of a nickel-containing catalyst, there remains a residue which contains the catalyst as well as ash. The nickel in the residue, which may vary depending upon the type of the gasifying agent, temperature and other reaction conditions, is generally present in the form of metallic nickel or nickel sulfide because it is subject to a reducing atmosphere.
The nickel which is metallic in the residue may be dissolved in the form of a nickel ammine by adding an aqueous ammonia solution or an aqueous solution containing ammonia and an ammonium salt to the nickel-containing residue in the presence of oxygen and/or air. Illustrative of the dissolution process are the following reaction equations. When ammonium chloride is used as the ammonium salt, nickel is dissolved in the form of nickel ammine chloride. Similarly, when ammonium carbonate, sulfate, and nitrate are used, nickel is dissolved in the form of nickel ammine carbonate, sulfate, and nitrate, respectively.
Ni+2NH4C1+4NH3+, 2= Ni(NH3)6C12+ H2O Ni+(NH4)2CO3+4NH3±02= Ni(NH3)6CO3+H2O & (NH4)2S 4+4NH3+ v 2= Ni(NH,),SO,+H,O Ni+2NH4NO3+4NH3++02= Ni(NH3)6(NO3)2+H2O The ammonium salts added dissociate into anions which can form nickel ammine salts as complex salts. Therefore, other ammonium salts which dissociate into anions capable of forming complex salts may also be employed to gain a similar effect.
It is only required to recover nickel in the form of a nickel ammine complex salt according to the invention. The ammonium salt need not be added when nickel ispresent as nickel sulfide in the residue.
Nickel sulfide reacts with ammonia as follows.
NiS+6NH3+202=Ni(NHa)6SO4 In this case, an aqueous ammonia solution is added to a nickel-containing residue.
In order that the invention may be more readily understood, reference will now be made to the accompanying drawings, in which: Fig. I is a graph showing solubility curves of nickel ammine chloride at different temperatures, the concentration ( t by weight) of free ammonia in the saturated nickel ammine chloride solution being plotted as abscissa and the solubility (g/100 g-saturated solution) as ordinate; Fig. 2 is a graph similar to Fig. 1, showing solubility curves of nickel ammine carbonate; Fig. 3 is a graph similar to Fig. 1, showing solubility curves of nickel ammine sulfate; Fig. 4 is a graph similar to Fig. 1, showing solubility curves of nickel ammine nitrate; Fig. 5 is a block diagram showing an embodiment of the invention in which nickel is recovered as nickel chloride; and Fig. 6 is a block diagram showing another embodiment of the invention in which nickel is recovered as nickel carbonate.
As clearly shown in Figs. 1 to 4, the nickel ammine complex salts are highly soluble at room temperature. When free ammonia has a concentration of 0 to 3 ' by weight, both nickel ammine chloride and nitrate have solubilities of about 20 to 25 g per 100 g of the saturated solution and both nickel ammine carbonate and sulfate have higher solubilities of about 40 to 50 g per 100 g of the saturated solution at a temperature of 55"C.
Although the nickel ammine complex salts are highly soluble at comparatively lower concentrations of free ammonia, the solubility rapidly decreases and eventually reaches near zero as the concentration of free ammonia increases.
The present process utilizes this difference in solubility. The nickel ammine can effectively be precipitated by increasing the concentration of free ammonia from a low level at which the solubility is high to a high level at which the solubility is low. In addition, the temperature may be lowered to precipitate nickel ammine more effectively.
The type of the ammonium salt to be added, the concentration of free ammonia.
the temperature of the solution, the partial pressure of oxygen and other conditions may be adjusted to any desired values.
depending upon the content and chemical state of nickel in the residue.
In step (a), nickel is dissolved and extracted in the form of a nickel ammine complex salt from the residue. To this end, the concentration of free ammonia may generally be 0 to 18.0 /" by weight, preferably 3.5 to 150 by weight to maintain the solubility of a nickel ammine high enough. Although lower concentrations of free ammonia are advantageous in view of solubility as described above in connection with Figs. 1--4, it takes a comparatively long time for nickel to react with an ammonium salt at a concentration of free ammonia below 3.5 /n by weight. Therefore, the above range is preferred from the point of view of commerical dissolution and extraction efficiency.Further, a larger partial pressure of oxygen is advantageous as understood from the reaction equations set forth above. The partial pressure of oxygen may generally be 1 to 50 atm, preferably 2 to 10 atm, in consideration of design and maintenance of equipment including a reactor. The temperature of the solution may generally be 10 to 1500C, preferably 30 to 1200C.
According to the invention, after a nickel containing residue is mixed with an aqueous ammonia solution to dissolve and extract the nickel in the solution, the resulting aqueous nickel ammine solution and the insoluble contents consisting of ash and other impurities are separated from each other, for example, by filtration. Thereafter the nickel ammine is precipitated from its solution by adding ammonia to the separated aqueous solution to increase the concentration of free ammonia. At the same time, the temperature of the separated aqueous solution may preferably be lowered to facilitate precipitation.
When crystals are precipitated from the aqueous nickel ammine solution in step (c), it is preferred to maintain the temperature of the solution to below 25"C, especially below 15"C and the concentration of free ammonia to 15 to 300/, by weight, as understood from Figs. 1 to 4. In order that those skilled in the art may better understand how to practice the present invention, the following examples are given by way of illustration.
EXAMPLE PLE Into an autoclave were admitted 88.8 g of a residue containing 16.9",, by weight of nickel which was obtained after coal was gasified in the presence of a nickel chloride catalyst to produce coal gas mainlv consisting of hydrogen. and 200 ml of an ammoniacal. aqueous ammonium carbonate solution containing 1.5 moles/liter of ammonium carbonate solution containing 1.5 moles/liter of ammonium carbonate and 8.0 moledliter of free ammonia and having a specific gravity of 1.01. The mixture was allowed to react for 60 minutes at a temperature of 50"C. an oxygen partial pressure of 4 atm. and an agitation rate of 2,000 r.p.m. It was found that 98 , of nickel was dissolved in the form of nickel ammine carbonate.
The insoluble contents were then removed by filtration. With cooling in an ice bath, ammonia gas was bubbled into the filtrate until the concentration of free ammonia reached 35 ,, by weight. There was precipitated 75.8 g of crystals. Analysis was carried out to determine the composition. It was found that 97.0", of nickel was recovered. The results are shown below.
Ni (when) NH3 (wt0',) Found 18.8 32.4 Calculated for Ni(NH3)6.5H2O 18.9 32.8 EXAMPLE 2 Into an autoclave were admitted 87.2 g of a residue containing 17.2% by weight of nickel which was obtained after coal was gasified in the presence of a nickel chloride catalyst to produce coal gas mainly consisting of steam, and 200 ml of an ammoniacal, aqueous ammonium sulfate solution which contained 1.5 moles/liter of ammonium sulfate and 8.0 moles/liter of free ammonia and had a specific gravity of 1.04. The mixture was allowed to react for 75 minutes at a temperature of 50"C. an oxygen partial pressure of 4 atm. and an agitation rate of 2,000 r.p.m.It was found that 96.5", of nickel was dissolved in the form of nickel ammine sulfate.
The insoluble contents were then removed by filtration. With cooling in an ice bath, ammonia gas was bubbled into the filtrate until the concentration of free ammonia reached 35/n by weight. There was precipitated 66.4 g of crystals. Analysis was carried out to determine the composition. It was found that 98*5 ó of nickel was recovered. The results are shown below.
Ni (wit%) NH3 (wit0,0) Found 21.5 38.2 Calculated for Ni(NH3)6 22.1 38.4 SO4.+H2O Reference is again made to the drawings.
Fig. 5 shows a preferred embodiment, in which the starting material is a nickelcontaining residue which is obtained after coal is gasified in the presence of a nickel chloride catalyst. In a reactor 10 for gasifying coal are supplied a carbonaceous material (in this example, coal), a nickel chloride catalyst, and a gasifying agent through lines 1, 2, and 3, respectively. The gasification is carried out in the reactor maintained under predetermined conditions. A useful gas mixture containing hydrogen, methane and the like is generated, while a nickel-containing residue including ash remains. The useful gas mixture is taken out from the reactor 10 to a washing unit 11 by way of a line 5. Into the washing unit 11 is also introduced a washing liquid, for example, water or an aqueous, diluted hydrochloric acid solution through a line 7.The washing liquid serves to remove hydrochloric acid from the gas, which is then taken out through a line 6. The removed hydrochloric acid is fed to a unit 12 for forming ammonium chloride through a line 8. Ammonia fed through a line 9a is added to hydrochloric acid in the unit 12 to form ammonium chloride, which, in turn, is fed through a line 9b to an extractor 20 for dissolving and extracting nickel in the form of nickel ammine. The washing unit 11 and the ammonium chloride-forming unit 12 may be combined to perform both the removal of hydrochloric acid and the formation of ammonium chloride.
The catalyst may sometimes be activated before it is used in gasification. In this case, ammonia or hydrogen chloride gas is discharged together with an activating gas.
By feeding the gas mixture to the washing unit 11, ammonium chloride may be recovered. Alternatively, an activation apparatus may separately be installed in addition to the gasifying reactor 10 in order to carry out the activation of the catalyst.
On the other hand, the residue in the gasifying reactor 10 is introduced into the extractor 20 through a line 4. Into the extractor 20 are also introduced ammonia, oxygen and/or air, and water through lines 21, 22, and 23, respectively. In addition, the aqueous ammonium chloride solution is fed to the extractor 20 through the line 9b, as described above. With temperature, oxygen partial pressure and other conditions set to predetermined levels, nickel in the residue is dissolved and extracted in the form of nickel ammine chloride. The mixture may preferably be stirred to facilitate dissolution. This dissolution and extraction process may be carried out in any desired manner, for example, by a batchwise or continuous, parallel current or counter current operation. The operation may be chosen according to the amount of the residue to be treated and the nickel content.
After the dissolution and extraction process is completed, the treated mixture is transferred to a separator 30 through a line 24. The insoluble contents including ash are separated therein and discharged through a line 32, while the aqueous nickel ammine chloride solution is fed to a precipitator 40 through a line 31. Ammonia fed through a branch line 66 is added to the solution to increase the concentration of free ammonia in the solution, precipitating nickel ammine chloride. The temperature of the solution may optionally be reduced in the precipitator 40.
The precipitate is transferred together with the solution to a separator 50 through a line 41. In the separator 50, the precipitate is separated from the solution, which is then fed to a first recovery apparatus 51 through a line 54. Ammonia gas is liberated from the solution due to temperature rise or pressure reduction and then combined with another ammonia gas flow from a second recovery apparatus 61 to be described hereinafter.
The combined ammonia gas is circulated through lines 55 and 65 for reuse. The remaining solution in the first recovery apparatus 51, which contains a small amount of nickel ammine chloride, is returned to the precipitator 40 or extractor 20 through the line 56 or 57 for reuse. If the amount of impurities accumulated in the solution becomes larger due to repeated use, such a contaminated solution is discharged through a line 53 and a fresh solution is supplied.
The separated precipitate of nickel ammine chloride is introduced into a heater 60 for decomposing the complex salt through a line 52, in which nickel ammine chloride is decomposed into nickel chloride and ammonia by heating. The separated nickel chloride is, if necessary, circulated to the gasifying reactor 10 through a line 63 for reuse as the catalyst, while the ammonia is fed to the second recovery apparatus 61 through a line 62 and dried therein. If desired, the dried ammonia gas is circulated to the ammonium chloride-forming unit 12 and the precipitator 40 through the lines 65, 66 and 9a for reuse. The waste water resulting from the above drying procedure may optionally be discharged through a line 64.
The above-described system may be designed so that when any of reagents, for example, ammonium chloride or ammonia deviates from the range ensuring a suitable relative proportion, such a deviation may immediately be compensated.
The embodiment employing nickel chloride as the catalyst is illustratively described above, whereas the invention can be applied in a similar manner to the cases employing nickel salts such as nickel sulfate, nitrate and carbonate, metallic nickel and nickel oxide as the catalyst. It is to be noted that when metallic nickel or nickel oxide is used as the catalyst, the nickel salt resulting from decomposition by heating in the heater 60 may further be treated by conventional methods before it is circulated.
Another preferred embodiment is shown in Fig. 6, in which nickel in the residue is recovered as nickel carbonate. Referring to Fig. 6, the residue is introduced in an extractor 20 for dissolving nickel through an inlet line 75. To this extractor 20 is also fed water through a line 74. Oxygen or air, carbon dioxide, and ammonia fed through lines 71, 72, and 73, respectively, are blown into the water. With stirring, nickel in the residue is dissolved and extracted in the form of nickel ammine carbonate. The treated mixture is fed to a separator 30 through a line 76. The insoluble contents including ash are separated therein and discharged through a line 77, while the separated solution of nickel ammine carbonate is fed to a precipitator 40 through a line 78.Ammonia fed through a branch line 87 is added to the solution to increase the concentration of free ammonia in the solution, precipitating nickel ammine carbonate I he precipitate is transferred together with the solution to a separator 50 through a line 79. In the separator 50, the precipitate is separated from the solution, which is then fed to a recovery apparatus 82 through a line 80. The solution is subject to elevated temperature or reduced pressure to recover ammonia and the remaining waste liquid is discharged from a line 83. The above recovered ammonia is combined with another ammonia flow from a heater 60 to be described hereinafter. The combined ammonia gas is circulated to the extractor 20 and the precipitator 40 for reuse.
The separated precipitate of nickel ammine carbonate is introduced into the heater 60 through a line 81, in which nickel ammine carbonate is decomposed into nickel carbonate or nickel oxide and ammonia by heating. The generated ammonia is fed to the extractor 20 and the precipitator 30 through lines 85, 87, and 73 for reuse. The resulting nickel carbonate or nickel oxide is taken out through a line 86 and then may either be circulated to the gasifying reactor or be stored in a suitable reservoir (not shown).
As described above, nickel can be effectively recovered from a residue resulting from the gasification of carbonaceous materials using nickelcontaining catalysts.
In the present invention, modification and variation may be made depending upon the type of a nickel compound used as the catalyst. For example, when nickel ammine is used as the catalyst, the nickel ammine crystals separated after precipitation may be readily circulated for reuse without further processing.
Moreover. if nickel in the residue takes a form other than metallic nickel or nickel sulfide, it should be converted into metallic nickel or nickel sulfide before the invention is applied thereto.
Since nickel is fixed and recovered in the form of a nickel ammine salt according to the invention, useful reagents, for example, ammonia can easily be circulated for reuse.
As a result, nickel is economically recovered and environmental pollution is minimized.
WHAT WE CLAIM IS: 1. A method of recovering nickel from nickel-containing residue obtained after a carbonaceous material is gasified in the presence of a nickel-containing catalyst.
which comprises the steps of: (a) adding an aqueous ammonia solution or an aqueous solution containing ammonia and an ammonium salt to said nickelcontaining residue in the presence of oxygen and/or air to dissolve and extract the nickel in the solution in the form of a nickel ammine complex salt; (b) separating the mixture into an aqueous nickel ammine solution and insoluble contents; (c) further adding ammonia to the separated aqueous nickel ammine solution to increase the concentration of free ammonia to a value high enough to precipitate the nickel ammine, and (d) separating the nickel ammine precipitate.
2. A method as claimed in claim 1 which further comprises a step (e) of converting the separated nickel ammine into nickel oxide, a nickel salt or metallic nickel.
3. A method as claimed in claim I or 2 wherein said carbonaceous material from which said nickel-containing residue is obtained is selected from brown coal, lignite, bituminous coal, tar pitch, coke and their analogues.
4. A method as claimed in claim 1, 2 or 3 wherein an aqueous solution containing ammonia and an ammonium salt is added to said nickel-containing residue in step (a) when the nickel is present in a metallic form.
5. A method as claimed in claim 4 wherein said ammonium salt is selected from ammonium chloride, ammonium carbonate, ammonium sulfate and ammonium nitrate.
6. A method as claimed in claim 1, 2 or 3
**WARNING** end of DESC field may overlap start of CLMS **.

Claims (19)

**WARNING** start of CLMS field may overlap end of DESC **. be applied in a similar manner to the cases employing nickel salts such as nickel sulfate, nitrate and carbonate, metallic nickel and nickel oxide as the catalyst. It is to be noted that when metallic nickel or nickel oxide is used as the catalyst, the nickel salt resulting from decomposition by heating in the heater 60 may further be treated by conventional methods before it is circulated. Another preferred embodiment is shown in Fig. 6, in which nickel in the residue is recovered as nickel carbonate. Referring to Fig. 6, the residue is introduced in an extractor 20 for dissolving nickel through an inlet line 75. To this extractor 20 is also fed water through a line 74. Oxygen or air, carbon dioxide, and ammonia fed through lines 71, 72, and 73, respectively, are blown into the water. With stirring, nickel in the residue is dissolved and extracted in the form of nickel ammine carbonate. The treated mixture is fed to a separator 30 through a line 76. The insoluble contents including ash are separated therein and discharged through a line 77, while the separated solution of nickel ammine carbonate is fed to a precipitator 40 through a line 78.Ammonia fed through a branch line 87 is added to the solution to increase the concentration of free ammonia in the solution, precipitating nickel ammine carbonate I he precipitate is transferred together with the solution to a separator 50 through a line 79. In the separator 50, the precipitate is separated from the solution, which is then fed to a recovery apparatus 82 through a line 80. The solution is subject to elevated temperature or reduced pressure to recover ammonia and the remaining waste liquid is discharged from a line 83. The above recovered ammonia is combined with another ammonia flow from a heater 60 to be described hereinafter. The combined ammonia gas is circulated to the extractor 20 and the precipitator 40 for reuse. The separated precipitate of nickel ammine carbonate is introduced into the heater 60 through a line 81, in which nickel ammine carbonate is decomposed into nickel carbonate or nickel oxide and ammonia by heating. The generated ammonia is fed to the extractor 20 and the precipitator 30 through lines 85, 87, and 73 for reuse. The resulting nickel carbonate or nickel oxide is taken out through a line 86 and then may either be circulated to the gasifying reactor or be stored in a suitable reservoir (not shown). As described above, nickel can be effectively recovered from a residue resulting from the gasification of carbonaceous materials using nickelcontaining catalysts. In the present invention, modification and variation may be made depending upon the type of a nickel compound used as the catalyst. For example, when nickel ammine is used as the catalyst, the nickel ammine crystals separated after precipitation may be readily circulated for reuse without further processing. Moreover. if nickel in the residue takes a form other than metallic nickel or nickel sulfide, it should be converted into metallic nickel or nickel sulfide before the invention is applied thereto. Since nickel is fixed and recovered in the form of a nickel ammine salt according to the invention, useful reagents, for example, ammonia can easily be circulated for reuse. As a result, nickel is economically recovered and environmental pollution is minimized. WHAT WE CLAIM IS:
1. A method of recovering nickel from nickel-containing residue obtained after a carbonaceous material is gasified in the presence of a nickel-containing catalyst.
which comprises the steps of: (a) adding an aqueous ammonia solution or an aqueous solution containing ammonia and an ammonium salt to said nickelcontaining residue in the presence of oxygen and/or air to dissolve and extract the nickel in the solution in the form of a nickel ammine complex salt; (b) separating the mixture into an aqueous nickel ammine solution and insoluble contents; (c) further adding ammonia to the separated aqueous nickel ammine solution to increase the concentration of free ammonia to a value high enough to precipitate the nickel ammine, and (d) separating the nickel ammine precipitate.
2. A method as claimed in claim 1 which further comprises a step (e) of converting the separated nickel ammine into nickel oxide, a nickel salt or metallic nickel.
3. A method as claimed in claim I or 2 wherein said carbonaceous material from which said nickel-containing residue is obtained is selected from brown coal, lignite, bituminous coal, tar pitch, coke and their analogues.
4. A method as claimed in claim 1, 2 or 3 wherein an aqueous solution containing ammonia and an ammonium salt is added to said nickel-containing residue in step (a) when the nickel is present in a metallic form.
5. A method as claimed in claim 4 wherein said ammonium salt is selected from ammonium chloride, ammonium carbonate, ammonium sulfate and ammonium nitrate.
6. A method as claimed in claim 1, 2 or 3
wherein an aqueous ammonia solution is added to said nickel-containing residue in step (a) when the nickel is present in the form of nickel sulfide.
7. A method as claimed in any one of claims I to 6 wherein the concentration of free ammonia in the solution is in the range of 0 to 18.0 ' by weight in step (a).
8. A method as claimed in claim 7 wherein the concentration of free ammonia is in the range of 3.5 to 15.0% by weight.
9. A method as claimed in any one of claims 1 to 8 wherein the partial pressure of oxygen is in the range of 1 to 50 atm. in step (a).
10. A method as claimed in claim 9 wherein the partial pressure of oxygen is in the range of 2 to 10 atm.
11. A method as claimed in any one of claims I to 10 wherein the temperature of the solution is in the range of 10 to 1500C in step (a).
12. A method as claimed in claim 11 wherein the temperature of the solution is in the range of 30 to 1200C.
13. A method as claimed in any one of claims 1 to 12 wherein the concentration of free ammonia in the solution is in the range of 15 to 30% by weight in step (c).
14. A method as claimed in any one of claims 1 to 13 wherein the temperature of the solution is lowered to promote precipitation in step (c).
15. A method as claimed in claim 14 wherein the temperature of the solution is lowered to below 25"C.
16. A method as claimed in claim 14 wherein the temperature of the solution is lowered to below 15 C.
17. A method as claimed any one of claims 2 to 16 which further comprises a step (e) of heating the separated nickel ammine to decompose it into nickel oxide or a nickel salt and ammonia, and a step (f) of circulating the saturated nickel ammine solution remaining after the separating step (d) to step (a) and the ammonia resulting from the decomposition step (e) to step (c).
18. A method of recovering nickel from a nickel containing residue obtained after a carbonaceous material is gasified in the presence of a nickel containing catalyst substantially as described in Example 1 or Example 2, or with reference to Figure 5 or Figure 6 of the accompanying drawings.
19. Nickel or a nickel compound recovered by a method according to any one of claims 1 to 18.
GB6002/78A 1977-03-01 1978-02-15 Nickel recovery Expired GB1560873A (en)

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2081077A JPS53106623A (en) 1977-03-01 1977-03-01 Method of recovering nickel from coal ash residue containing nickel

Publications (1)

Publication Number Publication Date
GB1560873A true GB1560873A (en) 1980-02-13

Family

ID=12037385

Family Applications (1)

Application Number Title Priority Date Filing Date
GB6002/78A Expired GB1560873A (en) 1977-03-01 1978-02-15 Nickel recovery

Country Status (8)

Country Link
JP (1) JPS53106623A (en)
AU (1) AU513480B2 (en)
CA (1) CA1097927A (en)
DE (1) DE2808263C2 (en)
FR (1) FR2382505A1 (en)
GB (1) GB1560873A (en)
IN (1) IN150307B (en)
NL (1) NL7802008A (en)

Cited By (39)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB2127393A (en) * 1982-09-24 1984-04-11 Chevron Res Leaching metals from spent hydroprocessing catalysts
GB2130566A (en) * 1982-09-24 1984-06-06 Chevron Res Recovering metals from spent hydroprocessing catalysts
EP2181177A2 (en) * 2007-08-01 2010-05-05 Nagarjuna Energy Private Limited A process for preventing polymerization of cracked volatile products during pyrolysis and gasification
WO2012116003A1 (en) * 2011-02-23 2012-08-30 Greatpoint Energy, Inc. Hydromethanation of a carbonaceous feedstock with nickel recovery
US8286901B2 (en) 2008-02-29 2012-10-16 Greatpoint Energy, Inc. Coal compositions for catalytic gasification
US8297542B2 (en) 2008-02-29 2012-10-30 Greatpoint Energy, Inc. Coal compositions for catalytic gasification
US8328890B2 (en) 2008-09-19 2012-12-11 Greatpoint Energy, Inc. Processes for gasification of a carbonaceous feedstock
US8349039B2 (en) 2008-02-29 2013-01-08 Greatpoint Energy, Inc. Carbonaceous fines recycle
US8361428B2 (en) 2008-02-29 2013-01-29 Greatpoint Energy, Inc. Reduced carbon footprint steam generation processes
US8366795B2 (en) 2008-02-29 2013-02-05 Greatpoint Energy, Inc. Catalytic gasification particulate compositions
US8479833B2 (en) 2009-10-19 2013-07-09 Greatpoint Energy, Inc. Integrated enhanced oil recovery process
US8479834B2 (en) 2009-10-19 2013-07-09 Greatpoint Energy, Inc. Integrated enhanced oil recovery process
US8502007B2 (en) 2008-09-19 2013-08-06 Greatpoint Energy, Inc. Char methanation catalyst and its use in gasification processes
US8557878B2 (en) 2010-04-26 2013-10-15 Greatpoint Energy, Inc. Hydromethanation of a carbonaceous feedstock with vanadium recovery
US8647402B2 (en) 2008-09-19 2014-02-11 Greatpoint Energy, Inc. Processes for gasification of a carbonaceous feedstock
US8653149B2 (en) 2010-05-28 2014-02-18 Greatpoint Energy, Inc. Conversion of liquid heavy hydrocarbon feedstocks to gaseous products
US8652696B2 (en) 2010-03-08 2014-02-18 Greatpoint Energy, Inc. Integrated hydromethanation fuel cell power generation
US8652222B2 (en) 2008-02-29 2014-02-18 Greatpoint Energy, Inc. Biomass compositions for catalytic gasification
US8669013B2 (en) 2010-02-23 2014-03-11 Greatpoint Energy, Inc. Integrated hydromethanation fuel cell power generation
US8728182B2 (en) 2009-05-13 2014-05-20 Greatpoint Energy, Inc. Processes for hydromethanation of a carbonaceous feedstock
US8728183B2 (en) 2009-05-13 2014-05-20 Greatpoint Energy, Inc. Processes for hydromethanation of a carbonaceous feedstock
US8734548B2 (en) 2008-12-30 2014-05-27 Greatpoint Energy, Inc. Processes for preparing a catalyzed coal particulate
US8734547B2 (en) 2008-12-30 2014-05-27 Greatpoint Energy, Inc. Processes for preparing a catalyzed carbonaceous particulate
US8733459B2 (en) 2009-12-17 2014-05-27 Greatpoint Energy, Inc. Integrated enhanced oil recovery process
US8748687B2 (en) 2010-08-18 2014-06-10 Greatpoint Energy, Inc. Hydromethanation of a carbonaceous feedstock
US9012524B2 (en) 2011-10-06 2015-04-21 Greatpoint Energy, Inc. Hydromethanation of a carbonaceous feedstock
US9034061B2 (en) 2012-10-01 2015-05-19 Greatpoint Energy, Inc. Agglomerated particulate low-rank coal feedstock and uses thereof
US9034058B2 (en) 2012-10-01 2015-05-19 Greatpoint Energy, Inc. Agglomerated particulate low-rank coal feedstock and uses thereof
US9127221B2 (en) 2011-06-03 2015-09-08 Greatpoint Energy, Inc. Hydromethanation of a carbonaceous feedstock
US9234149B2 (en) 2007-12-28 2016-01-12 Greatpoint Energy, Inc. Steam generating slurry gasifier for the catalytic gasification of a carbonaceous feedstock
US9273260B2 (en) 2012-10-01 2016-03-01 Greatpoint Energy, Inc. Agglomerated particulate low-rank coal feedstock and uses thereof
US9328920B2 (en) 2012-10-01 2016-05-03 Greatpoint Energy, Inc. Use of contaminated low-rank coal for combustion
US9353322B2 (en) 2010-11-01 2016-05-31 Greatpoint Energy, Inc. Hydromethanation of a carbonaceous feedstock
US10344231B1 (en) 2018-10-26 2019-07-09 Greatpoint Energy, Inc. Hydromethanation of a carbonaceous feedstock with improved carbon utilization
US10435637B1 (en) 2018-12-18 2019-10-08 Greatpoint Energy, Inc. Hydromethanation of a carbonaceous feedstock with improved carbon utilization and power generation
US10464872B1 (en) 2018-07-31 2019-11-05 Greatpoint Energy, Inc. Catalytic gasification to produce methanol
US10618818B1 (en) 2019-03-22 2020-04-14 Sure Champion Investment Limited Catalytic gasification to produce ammonia and urea
CN113802001A (en) * 2021-08-13 2021-12-17 广东邦普循环科技有限公司 Method for recovering and purifying nickel from nickel iron
CN114426889A (en) * 2020-10-29 2022-05-03 中国石油化工股份有限公司 Utilization method of hydrocracking molybdenum-containing tailings

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CU22856A1 (en) * 1997-02-18 2003-05-26 Ct De Investigaciones Para La Ind Minero Metalurgi HYDROMETALURGICAL PROCEDURE FOR THE RECOVERY OF NICKEL AND COBALT
JP5598778B2 (en) * 2013-01-25 2014-10-01 住友金属鉱山株式会社 Method for producing high-purity nickel sulfate and method for removing impurity element from solution containing nickel
CN115821041A (en) * 2022-09-01 2023-03-21 广东邦普循环科技有限公司 Method for recovering nickel

Family Cites Families (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
FR332596A (en) * 1903-05-06 1903-10-31 Miranda Malzac Wet desulphurization process of nickel, copper, zinc, etc. and hydroxidation of their metals, with a view to their extraction
FR460322A (en) * 1912-06-20 1913-11-28 Ernst Ellenberger Process for the treatment of cuttings from sheets coated with copper, nickel, zinc, tin, etc., or alloys of these metals by detaching the covering metals and by recovering the underlying metals
DE887871C (en) * 1941-03-05 1953-08-27 Kupferwerk Ilsenburg A G Process for separating copper-nickel-zinc alloys
BE514331A (en) * 1951-09-21 1900-01-01
DE1583911A1 (en) * 1967-11-11 1970-10-15 Ruhrchemie Ag Process for the recovery of nickel and / or cobalt from spent catalyst masses
ZA731519B (en) * 1972-06-23 1973-11-28 Anaconda Co Recovery of nickel
CA970167A (en) * 1972-07-19 1975-07-01 Herman F. Bakker Selective precipitation of cobalt and nickel ammine complexes
US3967957A (en) * 1973-03-26 1976-07-06 Continental Oil Company Aqueous ammonia oxidative leach and recovery of metal values

Cited By (44)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB2127393A (en) * 1982-09-24 1984-04-11 Chevron Res Leaching metals from spent hydroprocessing catalysts
GB2130566A (en) * 1982-09-24 1984-06-06 Chevron Res Recovering metals from spent hydroprocessing catalysts
EP2181177A2 (en) * 2007-08-01 2010-05-05 Nagarjuna Energy Private Limited A process for preventing polymerization of cracked volatile products during pyrolysis and gasification
EP2181177A4 (en) * 2007-08-01 2012-10-10 Nagarjuna Energy Private Ltd A process for preventing polymerization of cracked volatile products during pyrolysis and gasification
US9234149B2 (en) 2007-12-28 2016-01-12 Greatpoint Energy, Inc. Steam generating slurry gasifier for the catalytic gasification of a carbonaceous feedstock
US8349039B2 (en) 2008-02-29 2013-01-08 Greatpoint Energy, Inc. Carbonaceous fines recycle
US8297542B2 (en) 2008-02-29 2012-10-30 Greatpoint Energy, Inc. Coal compositions for catalytic gasification
US8652222B2 (en) 2008-02-29 2014-02-18 Greatpoint Energy, Inc. Biomass compositions for catalytic gasification
US8361428B2 (en) 2008-02-29 2013-01-29 Greatpoint Energy, Inc. Reduced carbon footprint steam generation processes
US8366795B2 (en) 2008-02-29 2013-02-05 Greatpoint Energy, Inc. Catalytic gasification particulate compositions
US8286901B2 (en) 2008-02-29 2012-10-16 Greatpoint Energy, Inc. Coal compositions for catalytic gasification
US8328890B2 (en) 2008-09-19 2012-12-11 Greatpoint Energy, Inc. Processes for gasification of a carbonaceous feedstock
US8502007B2 (en) 2008-09-19 2013-08-06 Greatpoint Energy, Inc. Char methanation catalyst and its use in gasification processes
US8647402B2 (en) 2008-09-19 2014-02-11 Greatpoint Energy, Inc. Processes for gasification of a carbonaceous feedstock
US8734547B2 (en) 2008-12-30 2014-05-27 Greatpoint Energy, Inc. Processes for preparing a catalyzed carbonaceous particulate
US8734548B2 (en) 2008-12-30 2014-05-27 Greatpoint Energy, Inc. Processes for preparing a catalyzed coal particulate
US8728183B2 (en) 2009-05-13 2014-05-20 Greatpoint Energy, Inc. Processes for hydromethanation of a carbonaceous feedstock
US8728182B2 (en) 2009-05-13 2014-05-20 Greatpoint Energy, Inc. Processes for hydromethanation of a carbonaceous feedstock
US8479833B2 (en) 2009-10-19 2013-07-09 Greatpoint Energy, Inc. Integrated enhanced oil recovery process
US8479834B2 (en) 2009-10-19 2013-07-09 Greatpoint Energy, Inc. Integrated enhanced oil recovery process
US8733459B2 (en) 2009-12-17 2014-05-27 Greatpoint Energy, Inc. Integrated enhanced oil recovery process
US8669013B2 (en) 2010-02-23 2014-03-11 Greatpoint Energy, Inc. Integrated hydromethanation fuel cell power generation
US8652696B2 (en) 2010-03-08 2014-02-18 Greatpoint Energy, Inc. Integrated hydromethanation fuel cell power generation
US8557878B2 (en) 2010-04-26 2013-10-15 Greatpoint Energy, Inc. Hydromethanation of a carbonaceous feedstock with vanadium recovery
US8653149B2 (en) 2010-05-28 2014-02-18 Greatpoint Energy, Inc. Conversion of liquid heavy hydrocarbon feedstocks to gaseous products
US8748687B2 (en) 2010-08-18 2014-06-10 Greatpoint Energy, Inc. Hydromethanation of a carbonaceous feedstock
US9353322B2 (en) 2010-11-01 2016-05-31 Greatpoint Energy, Inc. Hydromethanation of a carbonaceous feedstock
CN104711026A (en) * 2011-02-23 2015-06-17 格雷特波因特能源公司 Hydromethanation of a carbonaceous feedstock with nickel recovery
US8648121B2 (en) 2011-02-23 2014-02-11 Greatpoint Energy, Inc. Hydromethanation of a carbonaceous feedstock with nickel recovery
WO2012116003A1 (en) * 2011-02-23 2012-08-30 Greatpoint Energy, Inc. Hydromethanation of a carbonaceous feedstock with nickel recovery
US9127221B2 (en) 2011-06-03 2015-09-08 Greatpoint Energy, Inc. Hydromethanation of a carbonaceous feedstock
US9012524B2 (en) 2011-10-06 2015-04-21 Greatpoint Energy, Inc. Hydromethanation of a carbonaceous feedstock
US9034061B2 (en) 2012-10-01 2015-05-19 Greatpoint Energy, Inc. Agglomerated particulate low-rank coal feedstock and uses thereof
US9273260B2 (en) 2012-10-01 2016-03-01 Greatpoint Energy, Inc. Agglomerated particulate low-rank coal feedstock and uses thereof
US9328920B2 (en) 2012-10-01 2016-05-03 Greatpoint Energy, Inc. Use of contaminated low-rank coal for combustion
US9034058B2 (en) 2012-10-01 2015-05-19 Greatpoint Energy, Inc. Agglomerated particulate low-rank coal feedstock and uses thereof
US10464872B1 (en) 2018-07-31 2019-11-05 Greatpoint Energy, Inc. Catalytic gasification to produce methanol
US10344231B1 (en) 2018-10-26 2019-07-09 Greatpoint Energy, Inc. Hydromethanation of a carbonaceous feedstock with improved carbon utilization
US10435637B1 (en) 2018-12-18 2019-10-08 Greatpoint Energy, Inc. Hydromethanation of a carbonaceous feedstock with improved carbon utilization and power generation
US10618818B1 (en) 2019-03-22 2020-04-14 Sure Champion Investment Limited Catalytic gasification to produce ammonia and urea
CN114426889A (en) * 2020-10-29 2022-05-03 中国石油化工股份有限公司 Utilization method of hydrocracking molybdenum-containing tailings
CN114426889B (en) * 2020-10-29 2023-10-10 中国石油化工股份有限公司 Utilization method of hydrocracking molybdenum-containing tailings
CN113802001A (en) * 2021-08-13 2021-12-17 广东邦普循环科技有限公司 Method for recovering and purifying nickel from nickel iron
CN113802001B (en) * 2021-08-13 2022-11-22 广东邦普循环科技有限公司 Method for recovering and purifying nickel from nickel iron

Also Published As

Publication number Publication date
FR2382505A1 (en) 1978-09-29
AU3334978A (en) 1979-08-23
DE2808263C2 (en) 1983-10-27
JPS5536692B2 (en) 1980-09-22
FR2382505B1 (en) 1981-04-10
AU513480B2 (en) 1980-12-04
JPS53106623A (en) 1978-09-16
CA1097927A (en) 1981-03-24
DE2808263A1 (en) 1978-09-07
IN150307B (en) 1982-09-04
NL7802008A (en) 1978-09-05

Similar Documents

Publication Publication Date Title
GB1560873A (en) Nickel recovery
US4163043A (en) Process for removing H2 S and CO2 from gases and regenerating the adsorbing solution
US4192854A (en) Process for removing hydrogen sulfide and ammonia from gaseous streams
JPS6053730B2 (en) Nickel refining method
RO114320B1 (en) Method of removing nitrogen from nitrogen compounds in aqueous phase
JPH07500147A (en) Extraction or recovery of metal components
US4643886A (en) Automatic pH control in a process for removal of hydrogen sulfide from a gas
US3953577A (en) Process for purifying gases containing HCN
US3909211A (en) Coal desulfurization process
US4146572A (en) Simultaneous extraction of metal values other than copper from manganese nodules
US4218431A (en) Removal of sulfide contaminants from carbonate waters with production of CO2 -free H2 S
US4029498A (en) Process for treating manganese nodules
KR890004978A (en) Method of producing ammonia and sulfur dioxide
EP0047076A1 (en) A process of making cobalt metal powder
US3950492A (en) Process for removal of ammonia, hydrogen sulfide and hydrogen cyanide from gases containing these substances
US4235852A (en) Process for treating an exhaust gas containing nitrogen oxides and sulfur oxides
JPH11137959A (en) Removing method of nitrogen oxide and device therefor
CA1140730A (en) Process for producing magnesium oxide from an aqueous magnesium sulphate solution
CA1117769A (en) Winning nickel and cobalt with mercaptide extractants and carbon monoxide strip
US3966891A (en) Process for manufacturing sulfur from a solution of sodium sulfite
US3962410A (en) Process for purifying industrial gases containing hydrogen sulfide with sulfur production
US3740200A (en) Process for extracting uranium from its ores
Rudyk Aqueous reduction of sulphur dioxide by pyrrhotite to elemental sulphur
JP2550575B2 (en) Recovery method of ammonium thiocyanate
GB2026455A (en) Method for the wet extraction of impurities from gases of an elevated temperature

Legal Events

Date Code Title Description
PS Patent sealed [section 19, patents act 1949]
PCNP Patent ceased through non-payment of renewal fee