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CN1043250C - Method for recovering platinum and aluminum from waste aluminum-based catalyst and digestion furnace - Google Patents

Method for recovering platinum and aluminum from waste aluminum-based catalyst and digestion furnace Download PDF

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CN1043250C
CN1043250C CN95109350A CN95109350A CN1043250C CN 1043250 C CN1043250 C CN 1043250C CN 95109350 A CN95109350 A CN 95109350A CN 95109350 A CN95109350 A CN 95109350A CN 1043250 C CN1043250 C CN 1043250C
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platinum
water
aluminum
furnace
solution
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CN1143682A (en
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杨茂才
孙萼庭
周杨霁
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KUNMING NOBLE METAL INST CHINA NONFERROUS METAL INDUSTRY GENERAL Co
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KUNMING NOBLE METAL INST CHINA NONFERROUS METAL INDUSTRY GENERAL Co
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    • 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
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Abstract

A method and a digester for recovering platinum and aluminum from a waste aluminum-based catalyst. The method comprises the steps of alkali digestion, water leaching dealuminization, chlorination and platinum dissolution of an aqueous solution, flocculation of silica gel by animal glue, destruction of animal glue by dilute sulfuric acid, replacement of zinc (or iron) to obtain crude platinum, refining of the crude platinum to obtain pure platinum, and preparation of sodium alum or other aluminum salts by water leaching dealuminization. The digestion furnace is composed of a furnace bottom, a refractory brick furnace building wall, a lining heat preservation layer, a furnace top, a heat source and a temperature thermocouple, is in a cuboid shape, adopts a movable top structure, and uses a kerosene blowtorch as the heat source.

Description

Method for recovering platinum and aluminum from waste aluminum-based catalyst and digestion furnace
A method and a digester for recovering platinum and aluminum from a waste aluminum-based catalyst. The present invention belongs to noble metal metallurgy.
Noble metal catalysts are widely used in the petrochemical industry and consist of a substrate and a noble metal active part. After long-term use, the active component in the catalyst is expensiveMetals are contaminated with various impurities and lose their activity, and become spent catalysts. Noble metals are widely used, but the resources are limited, so the noble metals are expensive, and the waste materials containing the noble metals naturally become very important secondary resources. The method for recovering noble metal from the spent catalyst includes a noble metal selective dissolution method, a soluble carrier dissolution method, a dry volatilization method, a plasma smelting method, a copper smelting trapping method and the like. Patent ZL91104386.1 "method for recovering platinum from waste catalyst" (application date: 91.06.24) adopts a method of selective dissolution of noble metal to treat T-12 waste platinum catalyst, and provides a simple method with high platinum recovery rate and high purity, but the application is limited to a catalyst with insoluble matrix, and the matrix is not recovered and utilized. The 1-5 aluminum-based platinum catalyst is Al2O3The pellet catalyst as matrix consists of Al as main component%2O396Pt 0.36-0.37SiO21.67Fe 0.37Mn 0.11Pb trace Ni, 1.5-2mm pellet diameter, all calcined at 1150 deg.C, and Al matrix2O3The crystal form of (A) has been changed from r-type to a-type, wherein the powder accounts for about 30-40%, and most of platinum is distributed in Al in a micro-fine particle state2O3The middle or edge area of the matrix is coated by the matrix, belongs to a material difficult to process, and is processed by a method of selective dissolution of noble metal, so that the recovery rate of platinum is not high.
The object of the present invention is to provide a catalyst derived from Al2O3Recovery of platinum for any crystalline form of the spent aluminum-based catalystHigh efficiency, high purity, simple and easy operation, and can comprehensively recover aluminum, and special equipment for effectively implementing the method.
The method provided by the invention comprises the steps of alkali digestion, water leaching and dealuminization, aqueous solution chlorination and platinum dissolution, animal glue flocculation silica gel, dilute sulfate nitrate animal glue, zinc replacement (or iron replacement) to obtain crude platinum, refining the crude platinum to obtain pure platinum, and water leaching and dealuminization of aluminum liquid to prepare sodium alum Na2AL2(SO4)4·24H2O]The method comprises the following specific steps: (1) mixing the waste catalyst with sodium hydroxide in the weight ratio of waste catalyst to sodium hydroxide of 1: 1-3, preferably 1: 1-1.2, performing alkali digestion reaction in a digestion furnace designed and manufactured at the temperature of 500-850 ℃, preferably 600-800 ℃, so that the alumina with any crystal form in the matrix reacts with the sodium hydroxide to produce water-soluble aluminum salt: (ii) a (2) Leaching the alkaline digestion slag by water, wherein the ratio of the weight gram of the alkaline digestion slag to the volume milliliter of water is 1: 5-12, preferably 1: 5-10, the temperature is the boiling temperature of water, the time is 5-30 minutes, the aluminum removal rate is more than or equal to 98 percent, and the platinum content of a water leaching aluminum removal liquid is less than 0.0005 gram/liter; (3) dissolving water-immersed slag in 3-6mol/LHCl medium at 80-85 deg.C for 1 time at a ratio of weight gram of slag to volume milliliter of HCl solution of about 1: 4, wherein platinum is activated by alkali digestion, most of the platinum can be dissolved in HCl for 1-2 hours, after extracting supernatant, adding sodium chlorate oxidant into the residual slag under the conditions of HCl medium with the same concentration, dosage ratio and temperature, wherein the addition amount of the sodium chlorate oxidant is 10% of the weight of the residual slag, and the time is 1-2 hours, and dissolving the sodium chlorate oxidant once again; (4) mixing the two platinum solutions, adding 5-10% gelatin solution (volume ratio) = 1: 10000-25: 1000) into platinum solution at room temperature, stirring slowly to flocculate silica gel, filtering to remove silica gel and platinum-dissolving residue, and adding into solution2-3% concentrated sulfuric acid at 90-100 deg.C, and breaking animal glue for 20-30 min; (5) gradually adding zinc powder (or iron powder) into the solution obtained in the step (4) at normal temperature for replacement to obtain crude platinum precipitate, filtering, dissolving the crude platinum once again by a aqua regia dissolving method or a sodium chlorate oxidation aqueous solution chlorination method, hydrolyzing by sodium bromate, hydrolyzing by a carrier, precipitating platinum by ammonium chloride, and calcining to obtain pure sponge platinum powder refined by a traditional refining method; (6) adding sulfuric acid into the water leaching dealumination solution for reaction, evaporating the obtained solution to obtain sodium alum [ Na]2AL2(SO4)4·24H2O]And (4) crystallizing.
In order to realize high implementation efficiency of the method, the alkali digestion furnace is designed and manufactured, and is now described with reference to the attached drawings, wherein fig. 1 is a schematic view of a digestion furnace (I), a1 is a front view, b1 is a side view, C1 is a top view, 1, a furnace top steel frame, 2, a furnace top heat-insulating brick, 3, a hanging ring, 4, a furnace wall, 5, an inner lining heat-insulating layer, 6, a heat source fire spraying hole, 7 and a thermocouple. FIG. 2 is a schematic view of the charging of a digester (I), A is a schematic view of the charging of a bottom tray, B2-5 layers of trays are schematic views of the charging of the digester, C is a schematic view of arrangement of refractory brick pads of a hearth, 8 is a refractory brick pad, 9 is a flame path of the hearth, FIG. 3 is a schematic view of the charging and the charging of a digester (II),
a2 is a front view, b2 is a side view, C2 is a top view,
(1) (2), (3), (4), (5), (6), (7) show the same as in FIG. 1,
(10) is a fire-resisting brick.
The designed and manufactured digestion furnace consists of furnace bottoms (8,9), a furnace wall (4), an inner lining heat-insulating layer (5), furnace tops (1,2,3), a heat source (6) and a thermocouple (7), and is in a cuboid shape, and is characterized in that the furnace bottom is provided with a cross-shaped flame channel (9), furnace bottom refractory brick cushion blocks (8) are laid above the channel, and the cushion blocks are arranged above and around the flame channel and are spaced from each other; the furnace wall (4) is built by refractory bricks, and a light insulating brick layer (5) is built in the furnace wall; the furnace top is movable and is formed by alternately stacking a steel frame (1) with a lifting ring (3) and 2 or 3 layers of light heat-insulating bricks in the steel frame; kerosene blowtorch is used as heat source, and the lower part of the furnace is simultaneously sprayed into the furnace from the four-side flame spraying holes (6), and the flame flowing direction is adjusted by the fire blocking bricks (10) and the material tray for fire isolation and the coordination with the flame channel at the bottom of the furnace. The digestion furnace with the structure has high heating speed, good heat preservation performance and energy consumption saving; the movable furnace top structure is convenient for hoisting and placing, is convenient for charging and discharging, ensures that the furnace top has uniform air permeability and enough heat preservation, is favorable for volatilization of combustion waste gas and water vapor of reaction products and flame diffusion, can ensure that the upper area of the furnace reaches the temperature required by reaction, and can also be provided with a material drying steel disc above the furnace top to bake wet materials by utilizing waste heat; the material in the furnace can fill the whole furnace chamber, so the processing capacity of the equipment is high; the size of the furnace body can be adjusted according to the production scale, the adaptability is strong, the material tray can be made of materials such as burning-resistant cast iron, steel plates, stainless steel plates and the like, and can bear the corrosion of caustic alkali at the temperature of 800 ℃; the operation atmosphere is good, and a separate ventilation and dust collection system is not required to be established.
The invention has the advantages that: 1. the recovery rate of platinum is more than or equal to 97 percent, the purity is as high as 99.95 to 99.99 percent, and the platinum can be directly used for preparing a new catalyst; 2. The method is simple and easy toimplement, 3, the aluminum energy can be comprehensively recovered, 4, the digestion furnace has reasonable structure, stable and reliable operation, low energy consumption and no environmental pollution.
Examples
Two kinds of digestion furnaces are built by using refractory bricks, light insulating bricks, steel, a blast lamp and a thermocouple according to the structural design in the specification:
the effective size of the furnace of the digestion furnace (I) is 1400 multiplied by 1100 multiplied by 1000mm, each furnace can be provided with 104 small material trays with the size of 290 multiplied by 220 multiplied by 140mm, the material is charged with 800 multiplied by 880Kg, 8 kerosene blowlamps are used for blasting fire, the heating and digestion time is 6 to 7 hours per furnace, the coal oil consumption is 70Kg per furnace, the primary water leaching and dealuminization rate is 88 to 92 percent, the noble metal platinum is enriched by 8.3 to 12.5 times, and the platinum content of the water leaching dealuminization liquid is less than 0.0005 g/l (the same below). The effective size of the furnace of the digestion furnace (II) is 1100 multiplied by 900mm, each furnace is provided with 6 large charging trays with the size of 900 multiplied by 430 multiplied by 420mm, the furnace is charged with 400 plus materials/furnace, 4 blowlamps are used for blasting fire, the heating and digestion time is 3 to 3.5 hours/furnace, the coal consumption oil is 25 Kg/furnace, the cumulative dealuminization rate of the secondary digestion water is 98 to 98.5 percent, and the platinum enrichment is 50 to 66.6 times.
Example 1 pellet-shaped spent aluminum-based platinum catalyst 1000g, content of a-Al2O396.5 percent and Pt 3650g/t, (1) carrying out alkaline digestion reaction for 1.5 hours under the conditions that the temperature is 700 ℃, and the weight ratio of the waste catalyst to the sodium hydroxide is not less than 1: 1; (2) leaching alkali to eliminate slag with water in the weight ratio of slag to water volume of 1 to 5 at boiling temperature for 6 min and aluminum eliminating rate of 98%; (3) placing the water leaching slag in a 6N HCl medium, wherein the ratio of the weight gram of the slag to the volume milliliter of the HCl solution is 1: 4, and adding sodium chlorate with the weight of 10 percent of the slag as an oxidant to chloridize and dissolve platinum; (4) gradually adding zinc powder into the platinum solution at normal temperature to replace crude platinum, filtering the crude platinum powder, dissolving the crude platinum powder for 1 time by the method (3), hydrolyzing the platinum solution obtained in the step (5) and the step (4) by sodium bromate, hydrolyzing a carrier, hydrolyzing ammonium chloride to precipitate platinum, and calcining by the traditional refining method to obtain 3.563g of spongy platinum, wherein the purity is 99.95 percent, and the recovery rate is 97.6 percent; (6) water immersion aluminium removing liquidAdding industrial sulfuric acid to react, evaporating the solution to obtain sodium alum crystals Na2AL2(SO4)4·24H2O]And recovering the aluminum.
Example 2 pellet-shaped waste aluminum-based platinum catalyst 10g containing r-Al2O396.5%, Pt4000g/t (1) alkali digested for 1 hour at 800 ℃ with spent catalyst sodium hydroxide = 1: 2.82; (2) the conditions of water leaching dealumination are the same as example 1, the aluminum removal rate is 98.50%, platinum concentrate is produced, the grade is 26.6%, the weight is 0.15g, the platinum is enriched by 66.5 times, and the recovery rate is more than 99%.
EXAMPLE 3 pellet-shaped spent aluminum-based platinum catalyst 902.2g, containing 2Al2O396.5percent of Pt897g/t, (1) carrying out alkali digestion for 2 hours under the conditions of waste material and sodium hydroxide = 1: 1 and the temperature of 600 ℃, and (2) carrying out water leaching dealumination under the same conditions as example 1, wherein the aluminum removal rate is 98 percent, a platinum concentrate is produced, the grade is 5.93 percent, the weight is 13.659, the platinum enrichment is 66 times, and the recovery rate is more than 99 percent.
Example 4 pellet-shaped spent alumina-based platinum catalyst 300Kg containing a-Al2O396.5% and 0.36% of Pt0, and (1) mixing the waste catalyst with sodium hydroxide, wherein the ratio of waste to sodium hydroxide is = 1: 1.2, reacting for 6 hours in a designed and manufactured alkali digestion furnace (I) at the temperature of 800 ℃, and (2) leaching alkali digestion slag by water, wherein the ratio of the weight kilogram of the slag to the volume liter of the water is 1: 10, and the temperature is as follows: boiling water at the temperature of 30 minutes, wherein the leaching rate of aluminum is 92 percent, the leaching solution contains less than 0.0005 g/L of platinum, (3) leaching slag with water is 24Kg (containing Pt4.48 percent), platinum is dissolved once at the leakage rate of 85 ℃ (platinum is activated by alkaline digestion and HCl is soluble) under the condition that 3molHCl medium and the ratio of the weight kilogram of slag to the volume liter of hydrochloric acid is 1: 4), extracting supernatant, dissolving the slag with dilute aqua regia (concentrated nitric acid: concentrated hydrochloric acid = 1: 3, and adding water for diluting 1 time), nitrotizing the aqua regia dissolving solution, converting the aqua regia dissolving solution into hydrochloric acid medium, mixing with the 1 st HCl dissolving solution, adding 5 percent animal glue solution at normal temperature, wherein the glue solution to the feed solution (volume ratio) = 25: 1000, stirring, filtering after flocculating silica gel, washing slag, and obtaining 18Kg (containing Pt 0.116 percent) of platinum residue, and the platinum rate is 98.07 percent; returning the platinum-dissolved residue to the digestion process to recover platinum again.
The method is not more suitable for recovering platinum and aluminum by using the aluminum-based platinum-containing catalyst, but also suitable for recovering noble metal and aluminum by using the aluminum-based platinum-containing catalyst, palladium-containing catalyst and rhodium-containing catalyst.

Claims (3)

1. A process for recovering Pt and Al from waste Al-base catalyst includes alkali digestion, water immersion for dealuminization, dissolving Pt in aqueous solution by chlorination, flocculating silica gel with animal glue, breaking animal glue by diluted sulfuric acid, zinc displacement (or iron displacement) to obtain coarse Pt, refining to obtain pure Pt, water immersion for dealuminization to prepare Na alum2AL2(SO4)4·24H2O]The method comprises the following steps: 1.1 alkaline digestion conditions were: mixing the waste catalyst with alkali, wherein the alkali is sodium hydroxide, the dosage of the alkali is the waste catalyst and the sodium hydroxide (weight ratio) = 1: 1-3, the temperature is 500-;
1.2 the water immersion dealumination conditions are as follows: leaching aluminum salt from the alkaline digestion residue with water to remove aluminum, wherein the ratio of the weight gram of the alkaline digestion residue to the volume milliliter of the water is 1: 5-12, the temperature is the boiling temperature of the water, and the time is 5-30 minutes;
1.3 the conditions for dissolving platinum by water solution chlorination are as follows: dissolving the water leached aluminum-removed slag in 3-6mol/LHCl medium at 80-85 deg.C for 1 time for 1-2 hours in a ratio of weight gram of slag to volume milliliter of HCl solution of about 1: 4, extracting supernatant, adding sodium chlorate oxidant into the residue under the conditions of HCl medium with the same concentration, dosage ratio and temperature, wherein the addition is 10% of the weight of the residue, and dissolving for 1 time for 1-2 hours;
1.4 flocculating the silica gel with the conditions for destroying the gelatin by dilute sulfuric acid are as follows: at normal temperature, adding 5-10% animal glue solution into platinum solution, wherein the volume ratio of glue solution to feed solution is = 1: 10000-25: 1000, slowly stirring to flocculate silica gel, filtering, adding 2-3% concentrated sulfuric acid into the solution, and keeping the temperature at 90-100 ℃ for 20-30 minutes;
1.5 zinc displacement or iron displacement to obtain crude platinum → the refining method of the crude platinum is as follows: adding zinc powder (or iron powder) into the solution obtained in step 1.4 at normal temperature, gradually replacing to obtain crude platinum precipitate, dissolving the crude platinum after filtering by aqua regia or sodium chlorate oxidation aqueous solution chlorination method, hydrolyzing with sodium bromate, hydrolyzing the carrier, precipitating platinum with ammonium chloride, and calcining to obtain pure sponge platinum powder refined platinum by traditional refining method;
1.6 the method for preparing the sodium alum by leaching the molten aluminum by water comprises the following steps: adding sulfuric acid into the water leaching dealumination solution for reaction, evaporating the obtained solution to obtain sodium alum [ Na]2AL2(SO4)4·24H2O]And (4) crystallizing.
2. The method for recovering platinum and aluminum from a waste aluminum-based catalyst according to claim 1, wherein:
2.1 the alkaline digestion conditions are: mixing the waste catalyst and sodium hydroxide, wherein the dosage of the waste catalyst and the sodium hydroxide is (weight ratio) = 1: 1-1.2, the temperature is 600-;
2.2 the water leaching dealumination conditions are as follows: the alkaline digestion residue is subjected to dealuminization by leaching aluminum salt with water, wherein the dosage of the aluminum salt is that the ratio of the weight gram of the alkaline digestion residue to the volume milliliter of water is 1: 5-10, the temperature is the boiling temperature of the water, and the time is 5-30 minutes.
3. A digester for carrying out the method according to claim 1, consisting of a bottom (8,9), walls (4), an insulating layer (5) for the lining, a top (1,2,3), a heat source (6) and a thermocouple (7) for measuring temperature, which is-cuboid, characterized in that the bottom has a cross-shaped flame channel (9), over which are laid bottom refractory brick spacers (8) arranged with a spacing between them, above and around the flame channel; the furnace wall is built by refractory bricks, and a light insulating brick layer is built in the furnace wall; the furnace top is movable and is formed by stacking a steel frame (1) with a hanging ring (3) and 2 or 3 layers of light heat-insulating bricks (2) in the steel frame in a crossed manner; kerosene blowtorch is used as heat source (6), and the lower part of the furnace is simultaneously sprayed into the furnace from the four-side flame spraying holes, and flame flowing direction is adjusted by the fire blocking bricks (10) and the material tray fire isolation and the coordination with the flame channel at the bottom of the furnace.
CN95109350A 1995-08-23 1995-08-23 Method for recovering platinum and aluminum from waste aluminum-based catalyst and digestion furnace Expired - Fee Related CN1043250C (en)

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CN103194606B (en) * 2013-03-28 2014-06-04 贵研资源(易门)有限公司 Method for concentrating platinum group metals from alumina-based waste catalyst
CN103361499A (en) * 2013-07-23 2013-10-23 昆明贵金属研究所 Method for recovering rare earth elements from spent automobile catalyst
CN103398865B (en) * 2013-07-24 2015-11-18 贵研资源(易门)有限公司 The sampling of platinum group metal high-area carbon spent catalyst and method for making sample
CN104694768B (en) * 2013-12-05 2016-09-07 陈怡雯 Method from aluminium slag reducing metal aluminium
CN104342558A (en) * 2014-05-12 2015-02-11 上海派特贵金属环保科技有限公司 A method for recycling palladium from a spent precious metal catalyst
CN104060095A (en) * 2014-06-17 2014-09-24 励福实业(江门)贵金属有限公司 Method of recovering palladium from palladium-loading aluminum oxide waste catalyst
CN107841628A (en) * 2017-10-31 2018-03-27 昆明理工大学 A kind of microwave treatment platinum dead catalyst separation aluminium and the method for being enriched with platinum
CN108929958B (en) * 2018-07-27 2020-11-10 江苏北矿金属循环利用科技有限公司 Method for enriching platinum from oxidized leached sediment of silicon-aluminum-based platinum-containing dead catalyst

Citations (2)

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Publication number Priority date Publication date Assignee Title
FR2671104A1 (en) * 1990-12-28 1992-07-03 Inst Francais Du Petrole Process for antipollution treatment of a deactivated catalyst containing at least one noble metal and total recovery of the said metal and of the support alumina
CN1067926A (en) * 1991-06-24 1993-01-13 中国有色金属工业总公司昆明贵金属研究所 Method for recovering platinum from waste catalyst

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
FR2671104A1 (en) * 1990-12-28 1992-07-03 Inst Francais Du Petrole Process for antipollution treatment of a deactivated catalyst containing at least one noble metal and total recovery of the said metal and of the support alumina
CN1067926A (en) * 1991-06-24 1993-01-13 中国有色金属工业总公司昆明贵金属研究所 Method for recovering platinum from waste catalyst

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