JPS6366370B2 - - Google Patents
Info
- Publication number
- JPS6366370B2 JPS6366370B2 JP16264582A JP16264582A JPS6366370B2 JP S6366370 B2 JPS6366370 B2 JP S6366370B2 JP 16264582 A JP16264582 A JP 16264582A JP 16264582 A JP16264582 A JP 16264582A JP S6366370 B2 JPS6366370 B2 JP S6366370B2
- Authority
- JP
- Japan
- Prior art keywords
- acid
- solution
- leaching
- nickel
- solid
- 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
Links
- 239000002253 acid Substances 0.000 claims description 46
- PXHVJJICTQNCMI-UHFFFAOYSA-N nickel Substances [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 claims description 46
- 239000003054 catalyst Substances 0.000 claims description 29
- 229910052759 nickel Inorganic materials 0.000 claims description 23
- 238000002386 leaching Methods 0.000 claims description 22
- 239000007788 liquid Substances 0.000 claims description 22
- 239000002699 waste material Substances 0.000 claims description 22
- 238000000034 method Methods 0.000 claims description 19
- 229910052718 tin Inorganic materials 0.000 claims description 19
- AUYOHNUMSAGWQZ-UHFFFAOYSA-L dihydroxy(oxo)tin Chemical compound O[Sn](O)=O AUYOHNUMSAGWQZ-UHFFFAOYSA-L 0.000 claims description 13
- 238000000926 separation method Methods 0.000 claims description 11
- 229910000480 nickel oxide Inorganic materials 0.000 claims description 10
- BFDHFSHZJLFAMC-UHFFFAOYSA-L nickel(ii) hydroxide Chemical compound [OH-].[OH-].[Ni+2] BFDHFSHZJLFAMC-UHFFFAOYSA-L 0.000 claims description 10
- GNRSAWUEBMWBQH-UHFFFAOYSA-N oxonickel Chemical compound [Ni]=O GNRSAWUEBMWBQH-UHFFFAOYSA-N 0.000 claims description 10
- 239000007787 solid Substances 0.000 claims description 10
- XOLBLPGZBRYERU-UHFFFAOYSA-N tin dioxide Chemical compound O=[Sn]=O XOLBLPGZBRYERU-UHFFFAOYSA-N 0.000 claims description 10
- 229910001887 tin oxide Inorganic materials 0.000 claims description 10
- 230000001590 oxidative effect Effects 0.000 claims description 8
- 229910018100 Ni-Sn Inorganic materials 0.000 claims description 7
- 229910018532 NiâSn Inorganic materials 0.000 claims description 7
- 239000003513 alkali Substances 0.000 claims description 5
- 229910052500 inorganic mineral Inorganic materials 0.000 claims description 5
- 239000011707 mineral Substances 0.000 claims description 5
- 239000000919 ceramic Substances 0.000 claims description 4
- 239000000243 solution Substances 0.000 description 22
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 20
- 239000002184 metal Substances 0.000 description 10
- 229910052751 metal Inorganic materials 0.000 description 10
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 8
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 8
- ATJFFYVFTNAWJD-UHFFFAOYSA-N Tin Chemical compound [Sn] ATJFFYVFTNAWJD-UHFFFAOYSA-N 0.000 description 6
- 239000000203 mixture Substances 0.000 description 6
- 239000007800 oxidant agent Substances 0.000 description 6
- 239000003795 chemical substances by application Substances 0.000 description 5
- 229910001220 stainless steel Inorganic materials 0.000 description 5
- 239000010935 stainless steel Substances 0.000 description 5
- 229910000831 Steel Inorganic materials 0.000 description 4
- 238000001914 filtration Methods 0.000 description 4
- 150000002739 metals Chemical class 0.000 description 4
- 239000010959 steel Substances 0.000 description 4
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 3
- 238000000605 extraction Methods 0.000 description 3
- 230000001939 inductive effect Effects 0.000 description 3
- 238000004519 manufacturing process Methods 0.000 description 3
- 238000001556 precipitation Methods 0.000 description 3
- 238000007873 sieving Methods 0.000 description 3
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N silicon dioxide Inorganic materials O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- TXUICONDJPYNPY-UHFFFAOYSA-N (1,10,13-trimethyl-3-oxo-4,5,6,7,8,9,11,12,14,15,16,17-dodecahydrocyclopenta[a]phenanthren-17-yl) heptanoate Chemical compound C1CC2CC(=O)C=C(C)C2(C)C2C1C1CCC(OC(=O)CCCCCC)C1(C)CC2 TXUICONDJPYNPY-UHFFFAOYSA-N 0.000 description 2
- XTEGARKTQYYJKE-UHFFFAOYSA-M Chlorate Chemical compound [O-]Cl(=O)=O XTEGARKTQYYJKE-UHFFFAOYSA-M 0.000 description 2
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 2
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 description 2
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 description 2
- NBIIXXVUZAFLBC-UHFFFAOYSA-N Phosphoric acid Chemical compound OP(O)(O)=O NBIIXXVUZAFLBC-UHFFFAOYSA-N 0.000 description 2
- 229910021626 Tin(II) chloride Inorganic materials 0.000 description 2
- 150000007513 acids Chemical class 0.000 description 2
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 2
- 238000007796 conventional method Methods 0.000 description 2
- 230000007423 decrease Effects 0.000 description 2
- 238000000502 dialysis Methods 0.000 description 2
- 238000004821 distillation Methods 0.000 description 2
- 238000010438 heat treatment Methods 0.000 description 2
- 239000003014 ion exchange membrane Substances 0.000 description 2
- 238000006386 neutralization reaction Methods 0.000 description 2
- 230000003472 neutralizing effect Effects 0.000 description 2
- 229910017604 nitric acid Inorganic materials 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 239000002244 precipitate Substances 0.000 description 2
- 239000002994 raw material Substances 0.000 description 2
- 238000011084 recovery Methods 0.000 description 2
- 239000000377 silicon dioxide Substances 0.000 description 2
- 239000001119 stannous chloride Substances 0.000 description 2
- 235000011150 stannous chloride Nutrition 0.000 description 2
- 238000003756 stirring Methods 0.000 description 2
- 239000000725 suspension Substances 0.000 description 2
- 229910018072 Al 2 O 3 Inorganic materials 0.000 description 1
- 229910000863 Ferronickel Inorganic materials 0.000 description 1
- 229910004298 SiO 2 Inorganic materials 0.000 description 1
- 229910021627 Tin(IV) chloride Inorganic materials 0.000 description 1
- 230000002378 acidificating effect Effects 0.000 description 1
- 239000012670 alkaline solution Substances 0.000 description 1
- 229910000147 aluminium phosphate Inorganic materials 0.000 description 1
- 239000007864 aqueous solution Substances 0.000 description 1
- 229910052791 calcium Inorganic materials 0.000 description 1
- 229910002091 carbon monoxide Inorganic materials 0.000 description 1
- 238000005119 centrifugation Methods 0.000 description 1
- 239000003153 chemical reaction reagent Substances 0.000 description 1
- 229910052804 chromium Inorganic materials 0.000 description 1
- 239000000084 colloidal system Substances 0.000 description 1
- 229910052802 copper Inorganic materials 0.000 description 1
- 239000013078 crystal Substances 0.000 description 1
- 238000006356 dehydrogenation reaction Methods 0.000 description 1
- 238000009792 diffusion process Methods 0.000 description 1
- 238000010790 dilution Methods 0.000 description 1
- 239000012895 dilution Substances 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- 238000000227 grinding Methods 0.000 description 1
- -1 hydrochloric acid Chemical class 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-M hydroxide Chemical compound [OH-] XLYOFNOQVPJJNP-UHFFFAOYSA-M 0.000 description 1
- 150000004679 hydroxides Chemical class 0.000 description 1
- 238000005342 ion exchange Methods 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- 239000006148 magnetic separator Substances 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 229910052750 molybdenum Inorganic materials 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 238000010979 pH adjustment Methods 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 238000005504 petroleum refining Methods 0.000 description 1
- 230000001376 precipitating effect Effects 0.000 description 1
- 238000003672 processing method Methods 0.000 description 1
- 238000010298 pulverizing process Methods 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 238000007670 refining Methods 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
- 238000009628 steelmaking Methods 0.000 description 1
- FAKFSJNVVCGEEI-UHFFFAOYSA-J tin(4+);disulfate Chemical compound [Sn+4].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O FAKFSJNVVCGEEI-UHFFFAOYSA-J 0.000 description 1
- HPGGPRDJHPYFRM-UHFFFAOYSA-J tin(iv) chloride Chemical compound Cl[Sn](Cl)(Cl)Cl HPGGPRDJHPYFRM-UHFFFAOYSA-J 0.000 description 1
- 229910052719 titanium Inorganic materials 0.000 description 1
- 229910052720 vanadium Inorganic materials 0.000 description 1
- 238000003809 water extraction Methods 0.000 description 1
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P10/00—Technologies related to metal processing
- Y02P10/20—Recycling
Landscapes
- Manufacture And Refinement Of Metals (AREA)
Description
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The present invention aims to effectively utilize Ni from Ni-Sn-based waste catalysts, especially as a Ni source for stainless steel.
This invention relates to a method for separating and recovering Sn and Ni. In general, nickel sources used in the production of stainless steel include ferronickel, metallic nickel, nickel scrap, and nickel oxide. When used Ni-containing waste catalyst is directly used as raw material for making stainless steel, Fe, Cr, Ti, and
Mo, Mg, Ca and Cu and as supports
Although the presence of Al 2 O 3 and SiO 2 is not particularly problematic, the presence of Sn is not desirable. Sn in steelmaking raw materials
They are hardly removed even during refining and remain in the steel, and they segregate significantly in large steel ingots, impairing hot workability and tending to impair the toughness of the steel. Therefore, in order to effectively utilize the Ni-Sn-based waste catalyst as a Ni source in stainless steel production, it is desired to establish a processing method for effectively separating and recovering Ni and Sn from the waste catalyst. Japanese Patent Publication No. 56-47254 discloses a method for separating and recovering valuable metals from waste catalysts. In the method of this patent publication, the catalyst is oxidized and roasted to remove S, and then subjected to alkaline roasting, water extraction, and filtration.
Mo, V, and even Ni, Co using a high-magnetic separator
, and Al, which is a carrier agent, is also recovered.
There is no mention of Sn. Therefore, an object of the present invention is to provide a method for substantially completely separating and recovering Ni and Sn from a Ni-Sn-based waste catalyst. According to the present invention, a Ni-Sn-based waste catalyst is digested with a non-oxidizing mineral acid, and the resulting liquid is deoxidized to a pH of 1.0 to 2.0.
It was found that the Sn content could be selectively separated as metastannic acid by curing with water. After separating the Sn component, the Ni component can be separated as nickel hydroxide.
The metastannic acid and nickel hydroxide are then converted to tin oxide and nickel oxide, respectively, by roasting, and if desired, the tin oxide and nickel oxide are further converted to metallic tin and metallic nickel, respectively, by reduction. In this way, Ni and Sn can be extracted from the Ni-Sn-based waste catalyst, which is made by supporting Ni and Sn on a ceramic carrier.
The method of the present invention for separating and recovering the catalyst includes the following steps (a) obtaining an acid solution containing dissolved Ni and Sn extracted by leaching the waste catalyst with a non-oxidizing mineral acid; b) A step of removing the acid content after removing the solid content from the acid solution in step (a); (c) A step of removing the acid content from the acid solution in step (b) to a pH of 1.0 to 2.0.
(d) solidifying the liquid containing metastannic acid suspended in step (c);
(e) Roasting the solid content obtained in step (d) to recover tin oxide; (f) Neutralizing the liquid obtained in step (d) with an alkali to produce hydroxide. a step of precipitating nickel; (g) a step of solid-liquid separation of the liquid containing suspended nickel hydroxide in step (f); and (h) a step of roasting and oxidizing the solid content obtained in step (g). and, if desired, (i) reducing the tin oxide recovered in step (e) to recover tin metal; and/or (j) reducing the nickel oxide recovered in step (h). The method may further include a step of reducing and recovering the nickel metal. The attached FIG. 1 is a flow sheet for explaining a preferred embodiment of the method of the present invention. The starting waste catalyst treated by the method of the present invention is a Ni-Sn-based waste catalyst in which Ni, Sn, and other metals are supported on a ceramic carrier such as alumina or alumina-silica, and its chemical composition is, for example, It can be as shown in Table 1.
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ãã[Table] Such waste catalysts are obtained, for example, from dehydrogenation processes in the petroleum refining industry. Referring to FIG. 1, the starting spent catalyst is preferably subjected to a pretreatment consisting of sieving 1, oxidative roasting 2 and grinding 3. That is, the starting spent catalyst is
After the carrier ceramic is removed as much as possible by sieving 1, it is subjected to oxidative roasting 2. This oxidation roasting 2 is a process for incinerating and removing oil and other organic substances adhering to the waste catalyst, and the roasting temperature is a temperature sufficient to ash the oil and other organic substances, for example, about 200â. The temperature can be from â to 800â. In the pulverization step 3, the waste catalyst is, for example,
Pulverize to a particle size that can pass through a 150 mesh mill. In the method of the present invention, the starting waste catalyst is preferably subjected to the above-mentioned pretreatment and then leached with a non-oxidizing mineral acid to obtain an acid solution containing the extracted Ni and Sn dissolved therein. Suitable leaching acids 4 are non-acidic mineral acids such as hydrochloric acid, dilute sulfuric acid and phosphoric acid. When using an oxidizing acid such as nitric acid,
Since a portion of Sn is hydrolyzed, the extraction rate of Sn decreases. Hydrochloric acid was found to be most preferred for substantially complete extraction of Ni and Sn. In this leaching 5, the leaching acid 4 and the pretreated waste catalyst are fed into a steel leaching tank lined with FRP and equipped with appropriate stirring means and heating means, and the leaching acid 4 and the pretreated waste catalyst are stirred and mixed under heating. It is convenient to do this by In this case, the volume of the leaching tank is determined by the amount of waste catalyst to be treated and the treatment time. Alternatively, leaching can be carried out by repeatedly passing heated leaching acid through a column filled with spent catalyst. Leaching involves Ni and
It is preferable to use an amount approximately 2 to 7 times the stoichiometric amount required to dissolve the entire amount of Sn. If the amount of leaching acid used is too small, the extraction rate of Ni and Sn will decrease, and if the amount of leaching acid used is too large, the load in the subsequent acid removal step will become excessive. The concentration of the leaching acid used is preferably 1 part hydrochloric acid to 2 parts water, or 1 part hydrochloric acid to 3 parts water, and in the case of dilute sulfuric acid, 1 part sulfuric acid to 4 parts water or 1 part sulfuric acid to 6 parts water. The leaching concentration is
The temperature is preferably 65°C to 100°C, particularly 75°C to 90°C. When leaching is performed under the preferred conditions described herein, approximately 100% of the Ni and 98.8% or more of the Sn in the starting spent catalyst can be extracted. The acid solution containing dissolved Ni and Sn obtained by acid leaching is subjected to solid-liquid separation 6, for example, to remove the solid content 7, which consists of acid-insoluble alumina and silica.
remove. To give an example of the composition of the resulting solution 8, (for example, sample 4 shown in Table 1 is mixed with an amount equivalent to four times the stoichiometric amount required to dissolve the entire amount of Ni and Sn in the sample) ( Composition of the solution obtained by treatment with 4 mol) of hydrochloric acid), Ni; 22.1 g/,
Sn: 4.15 g/, free hydrochloric acid: 1.9 mol. In the next step of the method of the present invention, the free acid content is removed from the solution obtained in this way that contains the dissolved Ni and Sn content and also contains the free acid content. This acid removal step 9 is conveniently carried out by diffusion dialysis using an ion exchange membrane. When a volatile acid, such as hydrochloric acid, is used as the leaching acid, the acid content can also be removed by thermal distillation. The acid recovered from the acid removal step 9 is reused as leaching acid 4. The next step is Step 10, in which metastannic acid is precipitated by adjusting the pH of the acid-free solution to 1 to 2. PH adjustment is conveniently carried out by dilution with water. For the precipitation of metastannic acid, a pH of 1.0 or higher is required, but a pH of 2.0 is required.
If it substantially exceeds this, there is a problem that hydroxides of other metals will precipitate. In adjusting the pH, in order to facilitate the precipitation of metastannic acid, it is preferable to heat the solution to a temperature of, for example, 40°C to 50°C, and it is also preferable to add the oxidizing agent 11 and/or the inducing agent 12. . Examples of the oxidizing agent 11 include nitric acid, chlorate or hydrogen peroxide, and the amount of oxidizing agent 11 is 2 to 5 per 30 to 50 g of Sn present in the solution.
It is preferable to add such an oxidizing agent in an amount of .g. Oxygen and oxygen-containing gases, i.e. air, are also oxidizing agents 11
For example, per solution, air
It is also good to perform air ration at 0.2 to 0.3 N/min. As the metastannic acid nucleus generation inducing agent 12, tin salts such as stannous chloride, stannic chloride,
Sn30~50g/0.3~0.5g of tin sulfate etc.
It can be added in an amount of The liquid containing precipitated metastannic acid in suspension is solid.
Subjected to liquid separation 13. Solid-liquid separation can be performed by filtration, centrifugation or other suitable techniques. The obtained solid content 14 (metastannic acid) is roasted 15 to recover tin oxide 16. The roasting temperature can be about 800-1000°C. The solution 17 obtained by solid-liquid separation 13 is
For example, in the above example, it contains 21.66g/Ni and trace trace, and its pH is 1.2 to 1.4.
It was hot. This liquid 17 is neutralized 18 with an alkali 19 to precipitate nickel hydroxide. As the alkali 19, Ca(OH) 2 , Na 2 CO 3 , NaOH and others can be used. The liquid containing nickel hydroxide in suspension is subjected to filtration or other solid-liquid separation 20, resulting in a solid content of 21
(Nickel hydroxide) is roasted 15 to recover nickel oxide 22. Roasting temperature is 800â~1000â
It can be â. On the other hand, the liquid 23 obtained from the solid-liquid separation 20 can be used to prepare the alkaline solution 19 for neutralization. The tin oxide 16 obtained by roasting 15 can be used as a chemical reagent as it is without purification, and if desired, it can be treated with H 3 CO, C by a conventional method at a temperature of, for example, 500°C to 800°C. Metal tin 25 can also be obtained by reducing 24 with, for example, the following. Nickel oxide 22 obtained by roasting 15
can be used directly as a source of Ni in stainless steel production, or if desired, it can be reduced by conventional methods, e.g. 24, it is also possible to use metal nickel 26. In this way, according to the method of the present invention, Ni-
Ni and Sn, which are valuable metals, can be effectively separated from Sn-based waste catalyst and recovered in high yield. Next, the method of the present invention will be further explained by giving specific examples. Example 1 The spent catalyst with the composition No. 3 shown in Table 1 was
The Ni in this waste catalyst is crushed into 100 to 150 mesh pieces.
and Digested with stirring at 80°C for 2 hours using an amount equivalent to 4 times the stoichiometric amount required to dissolve the entire amount of Sn, that is, 4 mol of hydrochloric acid (concentration 14.6%), and solidified. After separating Ni; 35.24g/,
An acid solution containing 2.37 g of Sn and 1.8 mol of free hydrochloric acid was obtained. This acid solution was passed through an ion exchange membrane with 40°C water flowing at a flow rate of 1.0/m 2 hr.
By dialysis by flowing in the opposite direction at a flow rate of /m 2 hr, deacidification was performed, and a deacidified solution and recovered acid were obtained. The composition of the obtained deoxidizing solution was Ni: 33.62 g/, Sn: 22.4
g/, 0.15 mol of free acid salt. The composition of the recovered acid was 1.62 g/Ni, 0.13 g/Sn, and 2.03 mol of free hydrochloric acid. Next, add this deoxidizing solution to 2
The colloid was diluted with twice the amount of water to bring the pH to 1.2 to 1.4, heated to about 45°C to complete the precipitation of metastannic acid, and cured by adding 2.5 g of stannous chloride crystals. β-metastannic acid was precipitated and solid-liquid separated by filtration. The precipitate was roasted at approximately 900°C to recover substantially pure tin oxide. The recovery rate was approximately 95%. Approximately 5% of the unrecovered material was transferred to the recovered acid side during ion exchange.
This Sn content is circulated as a leaching acid together with the recovered acid, so it is not carried away from the system. One solution was neutralized by adding Ca(OH) 2 aqueous solution,
Nickel hydroxide is precipitated, removed, and about
Nickel oxide was recovered by roasting at 1000â. The recovery rate was 95%. When the obtained tin oxide was reduced with hydrogen gas at a temperature of approximately 700°C, metallic tin was obtained with a conversion rate of 98.0%. In addition, the obtained nickel oxide was heated to about 700°C.
When reduced with hydrogen gas at a temperature of approximately
Metallic nickel was obtained with 100% conversion. When the above procedure was repeated except that deoxidation was carried out by a heated distillation method, substantially the same results were obtained.
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FIG. 1 is a flow sheet for explaining a preferred embodiment of the method of the present invention. In the figure, 1... sieving, 2... roasting, 3... crushing, 4... leaching acid, 5... leaching, 6... solid-liquid separation, 7... insoluble matter, 8... solution, 9... Acid content removal, 10... Metastannic acid curing, 11... Oxidizing agent,
12...Inducing agent, 13...Solid-liquid separation, 14...
Metastannic acid, 15...roasted, 16...tin oxide,
17... Solution, 18... Neutralization, 19... Alkali neutralizing agent, 20... Solid-liquid separation, 21... Nickel hydroxide, 22... Nickel oxide, 23... Solution,
24...reduction, 25...metal tin, 26...metal nickel.
Claims (1)
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ã«ããæ°Žé žåããã±ã«ãæåºããã (g) å·¥çš(f)ã®æ°Žé žåããã±ã«ãæžæ¿å«æããæ¶²ã
åºâæ¶²åé¢ãããã㊠(h) å·¥çš(g)ã§åŸãåºåœ¢åãççŒããŠé žåããã±ã«
ãååãã ããšãç¹åŸŽãšããæ¹æ³ã[Claims] 1. In separating and recovering Ni and Sn from a Ni-Sn-based waste catalyst formed by supporting Ni and Sn on a ceramic carrier, (a) leaching the waste catalyst with a non-oxidizing mineral acid; (b) remove the solid content from the acid solution in step (a) and then remove the acid content; (c) remove the acid content from the acid solution in step (b). The pH of the solution from which acid has been removed is 1.0 to 2.0.
(d) The liquid containing metastannic acid suspended in step (c) is solidified.
(e) Roast the solid content obtained in step (d) to recover tin oxide; (f) Neutralize the solution obtained in step (d) with an alkali to recover nickel hydroxide. (g) solid-liquid separation of the liquid containing suspended nickel hydroxide in step (f), and (h) roasting the solid content obtained in step (g) to recover nickel oxide. A method characterized by:
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP57162645A JPS5953638A (en) | 1982-09-18 | 1982-09-18 | Method for separating and recovering nickel and tin from waste nickel-tin catalyst |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP57162645A JPS5953638A (en) | 1982-09-18 | 1982-09-18 | Method for separating and recovering nickel and tin from waste nickel-tin catalyst |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5953638A JPS5953638A (en) | 1984-03-28 |
| JPS6366370B2 true JPS6366370B2 (en) | 1988-12-20 |
Family
ID=15758553
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP57162645A Granted JPS5953638A (en) | 1982-09-18 | 1982-09-18 | Method for separating and recovering nickel and tin from waste nickel-tin catalyst |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5953638A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0540072U (en) * | 1991-11-06 | 1993-05-28 | ããã³æ ªåŒäŒç€Ÿ | Brake fluid pressure control device |
Families Citing this family (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| NL9301133A (en) * | 1993-06-29 | 1995-01-16 | Tno | Process for recovering metals from AlêOë based catalysts. |
| KR100401995B1 (en) * | 1998-12-23 | 2003-12-18 | 죌ìíì¬ í¬ì€ìœ | A METHOD FOR PRODUCING HIGH-PURITY NiO BY USING WASTE Ni ANODE |
| JP5511291B2 (en) * | 2009-09-30 | 2014-06-04 | ïœïœïœãšã³ã·ã¹ãã æ ªåŒäŒç€Ÿ | Method for purifying tin-containing waste and glass foam |
| CN120513310A (en) | 2023-08-25 | 2025-08-19 | é«äžœäºé æ ªåŒäŒç€Ÿ | Method for preparing nickel sulfate aqueous solution from nickel-containing raw material |
| CN120513308A (en) | 2023-08-25 | 2025-08-19 | é«äžœäºé æ ªåŒäŒç€Ÿ | Integrated nickel smelting method for recovering nickel oxide from nickel-containing raw material |
-
1982
- 1982-09-18 JP JP57162645A patent/JPS5953638A/en active Granted
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0540072U (en) * | 1991-11-06 | 1993-05-28 | ããã³æ ªåŒäŒç€Ÿ | Brake fluid pressure control device |
Also Published As
| Publication number | Publication date |
|---|---|
| JPS5953638A (en) | 1984-03-28 |
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