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CN115216629B - Method for comprehensively recovering metal elements in tungsten-doped ternary precursor waste - Google Patents

Method for comprehensively recovering metal elements in tungsten-doped ternary precursor waste Download PDF

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CN115216629B
CN115216629B CN202210753105.9A CN202210753105A CN115216629B CN 115216629 B CN115216629 B CN 115216629B CN 202210753105 A CN202210753105 A CN 202210753105A CN 115216629 B CN115216629 B CN 115216629B
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tungsten
acid leaching
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cobalt
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CN115216629A (en
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赵思佳
肖超
李攀
罗进爱
訚硕
翟世双
邓海龙
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Hunan Zhongwei New Energy Technology Co ltd
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    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B7/00Working up raw materials other than ores, e.g. scrap, to produce non-ferrous metals and compounds thereof; Methods of a general interest or applied to the winning of more than two metals
    • C22B7/006Wet processes
    • C22B7/007Wet processes by acid leaching
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    • C01INORGANIC CHEMISTRY
    • C01GCOMPOUNDS CONTAINING METALS NOT COVERED BY SUBCLASSES C01D OR C01F
    • C01G41/00Compounds of tungsten
    • 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
    • C22B23/0415Leaching processes with acids or salt solutions except ammonium salts solutions
    • C22B23/043Sulfurated acids or salts thereof
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B34/00Obtaining refractory metals
    • C22B34/30Obtaining chromium, molybdenum or tungsten
    • C22B34/36Obtaining tungsten
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    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B47/00Obtaining manganese
    • HELECTRICITY
    • H01ELECTRIC ELEMENTS
    • H01MPROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
    • H01M10/00Secondary cells; Manufacture thereof
    • H01M10/54Reclaiming serviceable parts of waste accumulators
    • 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
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    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
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    • Y02P10/20Recycling

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Abstract

The invention relates to the technical field of battery waste recovery, and discloses a method for comprehensively recovering metal elements in tungsten-doped ternary precursor waste. The method mainly comprises the following steps: carrying out primary acid leaching on the tungsten-doped ternary precursor waste and an acid solution to obtain primary acid leaching solution and primary acid leaching slag containing nickel, cobalt and manganese elements; in the presence of a reducing agent, carrying out secondary reducing acid leaching on the primary acid leaching slag and the acid solution to obtain secondary acid leaching liquid and secondary acid leaching slag; and regulating the pH value of the second-stage pickle liquor, filtering, and absorbing and recovering tungsten element in the filtrate by using weak-alkaline anion exchange resin to obtain sodium tungstate products and absorbed liquor containing nickel, cobalt and manganese elements. The method has the advantages of simple process, convenient operation and low cost, and ensures that the recovery rates of nickel, cobalt, manganese and tungsten in the tungsten-doped ternary precursor waste are all over 99 percent.

Description

Method for comprehensively recovering metal elements in tungsten-doped ternary precursor waste
Technical Field
The invention relates to the technical field of battery waste recovery, in particular to a method for comprehensively recovering metal elements in tungsten-doped ternary precursor waste.
Background
At present, a nickel-cobalt-manganese ternary material is one of main positive electrode materials of lithium ion batteries, and is widely applied to electric vehicles, electric bicycles, high-power batteries, middle-low grade mobile phones and notebook computers.
The ternary composite positive electrode material precursor product takes nickel salt, cobalt salt and manganese salt as raw materials, wherein the content ratio (x: y: z) of nickel, cobalt and manganese elements can be adjusted according to actual needs.
In order to improve the electrochemical performance of the positive electrode material, elements such as magnesium, aluminum, zirconium, tungsten and the like are mostly adopted to dope and modify the precursor at present. Unqualified tungsten-doped centrifugal materials, tungsten-doped slurrying groove materials, tungsten-doped sintering materials, tungsten-doped drying materials, ground reclaimed materials and other tungsten-doped ternary waste materials can be generated in the process of producing the tungsten-doped ternary precursor. The content of nickel element, cobalt element and manganese element in the tungsten-doped nickel-cobalt-manganese ternary precursor waste is high, and the tungsten-doped ternary precursor waste is directly treated by adopting a reduction acid leaching method, so that the later-stage tungsten element is difficult to separate from the nickel element, cobalt element and manganese element, the recovery rate of the nickel element, cobalt element, manganese element and tungsten element is low, and the effective recovery of the nickel element, cobalt element, manganese element and tungsten element is not realized.
However, the method of directly adopting alkaline leaching to obtain tungsten element with high recovery rate consumes a large amount of alkali, so that the treatment cost is high, and the separation and purification of tungsten and other metal elements cannot be thoroughly realized, therefore, the added value of the nickel, cobalt, manganese and tungsten metal element products is low.
CN108199106a discloses a process for recovering waste materials in the production process of nickel-cobalt-manganese ternary precursor, firstly, sulfuric acid solution is used for carrying out acid dissolution reaction on the nickel-cobalt-manganese ternary precursor waste materials, and then, the reducibility of valuable metal active sulfides recovered in the precipitation mother liquor of the nickel-cobalt-manganese ternary precursor is used for carrying out oxidation reduction reaction with partial oxides insoluble in acid in the nickel-cobalt-manganese ternary precursor waste materials, so that the purpose of recovery is achieved. However, the scheme only relates to recycling of nickel element, cobalt element and manganese element in the nickel-cobalt-manganese ternary precursor waste, and the recycling rate of the nickel element, cobalt element and manganese element is low, and comprehensive recycling of metal element in the tungsten-doped ternary precursor waste cannot be achieved through the scheme.
CN110607439a discloses a method for treating spherical nickel protoxide by sectional oxidation acid leaching, which comprises carrying out two-stage countercurrent oxidation acid leaching on mechanically activated nickel protoxide to obtain nickel leaching solution, taking nickel cobalt manganese ternary precursor waste as raw material for consuming residual acid, and using the leaching solution after acid consumption for synthesizing ternary precursor, preparing high-purity nickel plate, nickel sulfate, nickel chloride crystal and the like. However, the technical scheme disclosed in the prior art does not relate to recovery rates of nickel element, cobalt element and manganese element in the nickel-cobalt-manganese ternary precursor waste, and comprehensive recovery and utilization of metal elements in the tungsten-doped ternary precursor waste cannot be realized through the scheme.
Therefore, the method for treating the tungsten-doped ternary precursor waste has important practical significance, and is simple in process, low in cost and high in metal element recovery rate.
Disclosure of Invention
The invention aims to overcome the defects that the comprehensive recovery of nickel, cobalt, manganese and tungsten elements in tungsten-doped ternary precursor waste cannot be realized or the recovery rate is low and the separation of tungsten elements from nickel, cobalt and manganese elements is difficult in the prior art.
In order to achieve the above purpose, the invention provides a method for comprehensively recovering metal elements in tungsten-doped ternary precursor waste, which comprises the following steps:
(1) Carrying out primary acid leaching on the tungsten-doped ternary precursor waste and a first sulfuric acid solution to obtain primary acid leaching liquid I and primary acid leaching slag;
(2) In the presence of a reducing agent, carrying out secondary acid leaching on the primary acid leaching slag and a second sulfuric acid solution to obtain a secondary acid leaching liquid I and a secondary acid leaching slag;
(3) Adjusting the pH value of the second-stage pickle liquor I to 2-6 by using an alkaline substance I to obtain a second-stage pickle liquor II, and then filtering the second-stage pickle liquor II to obtain a second-stage pickle liquor III;
(4) Adopting ion exchange resin to carry out selective adsorption recovery on tungsten element in the two-stage pickle liquor III, and obtaining liquid I after adsorption and ion exchange resin loaded with tungsten element;
(5) Contacting the ion exchange resin loaded with tungsten element with an analysis solution to obtain a sodium tungstate solution through analysis;
the method further comprises the steps of: and recycling the residual elements contained in the first-stage pickle liquor I and the absorbed liquid I, wherein the residual elements contained in the first-stage pickle liquor I and the absorbed liquid I are respectively and independently selected from at least one of nickel element, cobalt element and manganese element.
The invention has at least the following advantages:
(1) The method for comprehensively recovering the metal elements in the tungsten-doped ternary precursor waste can realize effective separation of nickel, cobalt and manganese elements and tungsten elements;
(2) The method for comprehensively recovering the metal elements in the tungsten-doped ternary precursor waste can ensure that the recovery rates of the nickel, cobalt, manganese and tungsten are all over 99 percent;
(3) The method for comprehensively recovering the metal elements in the tungsten-doped ternary precursor waste has the advantages of simple process, convenient operation and low cost, and has strong practicability and high economic value.
Drawings
FIG. 1 is a process flow diagram of the treatment of tungsten doped ternary precursor waste.
Detailed Description
The endpoints and any values of the ranges disclosed herein are not limited to the precise range or value, and are understood to encompass values approaching those ranges or values. For numerical ranges, one or more new numerical ranges may be found between the endpoints of each range, between the endpoint of each range and the individual point value, and between the individual point value, in combination with each other, and are to be considered as specifically disclosed herein.
As described above, the invention provides a method for comprehensively recovering metal elements in tungsten-doped ternary precursor waste, which comprises the following steps:
(1) Carrying out primary acid leaching on the tungsten-doped ternary precursor waste and a first sulfuric acid solution to obtain primary acid leaching liquid I and primary acid leaching slag;
(2) In the presence of a reducing agent, carrying out secondary acid leaching on the primary acid leaching slag and a second sulfuric acid solution to obtain a secondary acid leaching liquid I and a secondary acid leaching slag;
(3) Adjusting the pH value of the second-stage pickle liquor I to 2-6 by using an alkaline substance I to obtain a second-stage pickle liquor II, and then filtering the second-stage pickle liquor II to obtain a second-stage pickle liquor III;
(4) Adopting ion exchange resin to carry out selective adsorption recovery on tungsten element in the two-stage pickle liquor III, and obtaining liquid I after adsorption and ion exchange resin loaded with tungsten element;
(5) Contacting the ion exchange resin loaded with tungsten element with an analysis solution to obtain a sodium tungstate solution through analysis;
the method further comprises the steps of: and recycling the residual elements contained in the first-stage pickle liquor I and the absorbed liquid I, wherein the residual elements contained in the first-stage pickle liquor I and the absorbed liquid I are respectively and independently selected from at least one of nickel element, cobalt element and manganese element.
Specifically, in the step (3), the second-stage pickling solution II is a solid-liquid mixture containing a small amount of solid particles or colloids.
Preferably, the method further comprises: regulating the pH value of the first-stage pickle liquor I to 2-6 by using an alkaline substance II to obtain a first-stage pickle liquor II, and filtering the first-stage pickle liquor II to obtain a feed liquid I containing nickel element, cobalt element and manganese element; and (3) using the feed liquid I as a raw material for producing a nickel, cobalt and manganese ternary precursor so as to recycle the nickel, cobalt and manganese ternary precursor.
Preferably, the method further comprises: and regulating the pH value of the adsorbed liquid I to 2-6 by using an alkaline substance III to obtain an adsorbed liquid II, concentrating the adsorbed liquid II to obtain a liquid II, and using the liquid II as a raw material for producing a nickel, cobalt and manganese ternary precursor so as to recycle.
Preferably, the concentration conditions are controlled so that the sum of the mass concentrations of nickel element, cobalt element and manganese element in the feed liquid II is more than or equal to 110g/L.
Preferably, the alkaline substance I, the alkaline substance II and the alkaline substance III according to the present invention are the same or different, and are each independently selected from at least one of NaOH solution, ammonia water and KOH solution.
The present invention is not particularly limited in the use concentration of the alkaline substance I, as long as the secondary pickle liquor I can be adjusted to reach a specified pH value, and the alkaline substance I is exemplified by a NaOH solution having a concentration of 30 wt%.
The present invention is not particularly limited in the concentration of the alkaline substance II to be used, as long as the first-stage pickle liquor I can be adjusted to achieve a prescribed pH value, and the alkaline substance II is exemplified by aqueous ammonia having a concentration of 25 to 28% by weight.
The present invention is not particularly limited in the concentration of the alkaline substance III to be used, as long as the post-adsorption liquid I can be adjusted to a specified pH, and the alkaline substance III is exemplified by a KOH solution having a concentration of 30% by weight.
Preferably, in step (1), the moisture content of the tungsten doped ternary precursor waste is 0.2-25wt%.
Preferably, in the step (1), the content of nickel element in the tungsten-doped ternary precursor waste is 20-75wt% based on metal element, the content of cobalt element is 0.3-15wt%, the content of manganese element is 0.1-22wt%, and the content of tungsten element is 0.05-0.5wt%.
Preferably, in step (1), the concentration of the first sulfuric acid solution is 20-35wt%.
Preferably, in step (1), the conditions of the one-stage acid leaching are controlled so that the pH value of the one-stage pickle liquor I obtained is 0 to 3.
Preferably, in step (1), the conditions of the one-stage acid leaching are such that: the leaching temperature is 40-94 ℃ and the leaching time is 0.5-4h. More preferably, in step (1), the conditions of the one-stage acid leaching satisfy: the leaching temperature is 70-90 ℃ and the leaching time is 1-2h.
Preferably, in the step (1), the concentration of the first sulfuric acid solution is controlled to be 20-35wt%, and the amount of the first sulfuric acid solution is 3-6mL for each 1g of the tungsten doped ternary precursor waste.
Preferably, in step (2), the concentration of the second sulfuric acid solution is 5-15wt%.
Preferably, in step (2), the conditions of the secondary acid leaching are controlled so that the pH value of the obtained secondary pickling solution I is 0-3.
Preferably, in step (2), the conditions of the second stage acid leaching include: the leaching temperature is 40-94 ℃ and the leaching time is 0.5-3h. More preferably, in step (2), the conditions of the second-stage acid leaching are such that: the leaching temperature is 70-90 ℃ and the leaching time is 1-2h.
Preferably, in step (2), the concentration of the second sulfuric acid solution is controlled to be 5-15wt%, and the amount of the second sulfuric acid solution is 4-9mL for each 1g of the first stage acid leaching residue.
Preferably, in step (2), the reducing agent is selected from at least one of hydrogen peroxide, sodium sulfite, ammonium sulfite, sodium thiosulfate and sodium metabisulfite.
Preferably, in step (2), the reducing agent is used in an amount of 3-9g per 100g of the tungsten doped ternary precursor waste. More preferably, in step (2), the reducing agent is used in an amount of 3.6 to 6.5g per 100g of the tungsten doped ternary precursor waste.
Preferably, in step (4), the ion exchange resin is a weakly basic anion exchange resin. More preferably, the weakly basic anion exchange resin is selected from at least one of D363, D354 and LSC-486.
The invention discloses a method for preparing a weak-alkaline anion exchange resin, which comprises the steps of (1) representing the model of the weak-alkaline anion exchange resin, wherein D363, D354 and LSC-486 represent the weak-alkaline anion exchange resin of macroporous acrylic series, D354 represents the weak-alkaline anion exchange resin of macroporous polystyrene, and LSC-486 represents the weak-alkaline anion exchange resin of macroporous acrylic series.
Particularly preferably, in step (4), the weakly basic anion exchange resin is a LSC-486 resin. The inventors have found that in this preferred case, the method of the present invention enables further improvements in the recovery of nickel, cobalt, manganese and tungsten elements from the tungsten doped ternary precursor waste.
Preferably, in the step (4), the conditions of the selective adsorption recovery are controlled so that the mass concentration of tungsten element in the adsorbed liquid I is less than 1mg/L.
Preferably, in step (5), the resolving liquid is a NaOH solution of 1-3 mol/L.
The method for selectively adsorbing and recovering the catalyst in the step (4) and the method for analyzing the catalyst in the step (5) preferably using 1 to 3mol/L NaOH solution as the analysis solution are not particularly limited, and those skilled in the art can perform the method according to conventional technical means known in the art, and those skilled in the art should not understand the limitation of the present invention.
In order to make the recovery rate of tungsten element higher, the invention provides a preferred specific method for selective adsorption recovery and analysis, which comprises the following steps:
s1: introducing the two-stage leaching solution III into a single-stage ion exchange resin column filled with LSC-486 weak-base anion exchange resin at the speed of 120-360mL/h to perform adsorption reaction to obtain a liquid I after adsorption and LSC-486 weak-base anion exchange resin I loaded with tungsten element;
s2: introducing water into the single-stage ion exchange resin column of the LSC-486 weak-base anion exchange resin I loaded with tungsten element obtained in the step S1 at a speed of 120-240mL/h to obtain a washing liquid and the LSC-486 weak-base anion exchange resin II loaded with tungsten element;
s3: introducing 1-3mol/L NaOH solution into the single-stage ion exchange resin column of the LSC-486 weak-alkali anion exchange resin II loaded with tungsten element obtained in the step S2 at a speed of 120-180mL/h to obtain the sodium tungstate solution.
Preferably, the single-stage ion exchange resin column has a height of 15-30cm and a diameter of 2-3cm.
Preferably, in step S1, the conditions of the adsorption reaction satisfy: the adsorption time is 0.5-7h, and the adsorption temperature is 20-40 ℃.
Preferably, in step S2, for every 100cm 3 The amount of water used is 120-300mL.
Preferably, in step S3, for every 100cm 3 The dosage of the NaOH solution of 1-3mol/L is 230-450mL.
Preferably, in step (5), the method further comprises: and concentrating, crystallizing, centrifuging and drying the sodium tungstate solution in sequence to obtain a sodium tungstate product.
It should be noted that the filtering, concentrating, crystallizing, centrifuging and drying methods described in the foregoing are not particularly limited, and those skilled in the art can select according to the techniques known in the art, and the present invention is not described herein in detail, and those skilled in the art should not understand the limitation of the present invention.
The present invention will be described in detail by examples.
Concentrated sulfuric acid of 95 wt.%: purchased from colone chemicals limited, adult city.
Hydrogen peroxide: purchased from national pharmaceutical group chemical company, inc.
LSC-486 weakly basic anion exchange resin: purchased from western amp, blue dawn technology materials, inc.
D354 weak basic anion exchange resin: purchased from Jining Malus hupehensis chemical Co.
D363 weakly basic anion exchange resin: purchased from Anhui tree chemical sales Co., ltd.
Precision filter: the model is LFD-1-1P, and the manufacturer is Li Feier Ten filter Co., ltd.
Tungsten doped ternary precursor waste I (source: hunan Zhongwei New energy technology Co., ltd.) is composed of: the water content is 15.81wt%, calculated as metal element, the nickel content in the tungsten-doped ternary precursor waste I is 44.77wt%, the cobalt content is 4.49wt%, the manganese content is 3.25wt%, and the tungsten content is 0.079wt% on a dry basis.
Tungsten doped ternary precursor waste II (source: hunan Zhongwei New energy technology Co., ltd.) is composed of: the water content is 0.48wt%, calculated as metal element, the nickel element content in the tungsten-doped ternary precursor waste I is 54.63wt%, the cobalt element content is 2.45wt%, the manganese element content is 3.18wt%, and the tungsten element content is 0.146wt% on a dry basis.
The calculation formula of the recovery rate of the metal element referred to in the following examples is:
nickel element recovery (%) = nickel element content in 1-two-stage acid leaching residue/nickel element content in tungsten doped ternary precursor waste x 100%;
cobalt element recovery (%) = cobalt element content in 1-two-stage acid leaching slag/cobalt element content in tungsten doped ternary precursor waste material x 100%;
manganese element recovery (%) = manganese element content in 1-two-stage acid leaching slag/manganese element content in tungsten doped ternary precursor waste material x 100%;
tungsten recovery (%) =1- (tungsten content in adsorbed liquid i+tungsten content in second-stage acid leaching residue)/tungsten content in tungsten-doped ternary precursor waste×100%;
the unit of the content of nickel, cobalt, manganese and tungsten elements in the calculation formula is g.
The content of nickel element in the second-stage acid leaching slag is measured by adopting an ICP method after digestion;
the cobalt element content in the second-stage acid leaching slag is measured by adopting an ICP method after digestion;
the manganese element content in the second-stage acid leaching slag is measured by adopting an ICP method after digestion;
measuring the tungsten element content in the second-stage acid leaching slag by adopting an ICP method after digestion;
the nickel element content in the tungsten-doped ternary precursor waste is measured by a dimethylglyoxime-EDTA complexometric titration method;
the cobalt element content in the tungsten-doped ternary precursor waste is measured by adopting a post-digestion ICP method;
determining the content of manganese element in the tungsten-doped ternary precursor waste by adopting a digestion ICP method;
measuring the content of tungsten element in the tungsten-doped ternary precursor waste by adopting a digestion ICP method;
the tungsten element content in the liquid I after adsorption is measured by adopting an ICP method.
Example 1
(1) Carrying out primary acid leaching on the tungsten-doped ternary precursor waste I and the first sulfuric acid solution to obtain primary acid leaching liquid I and primary acid leaching slag;
(2) Carrying out secondary acid leaching on all the obtained primary acid leaching residues, a reducing agent and a second sulfuric acid solution to obtain secondary acid leaching liquid I and secondary acid leaching residues;
(3) Regulating the pH value of the second-stage pickle liquor I by using a NaOH solution with the concentration of 30 weight percent to obtain a second-stage pickle liquor II, and filtering by using a precise filter to obtain a second-stage pickle liquor III with solid particles smaller than 15 mu m;
(4) Selectively adsorbing and recovering tungsten element in the second-stage pickle liquor III by adopting weak-alkali anion exchange resin to obtain a liquid I after adsorption and a weak-alkali anion exchange resin II loaded with tungsten element;
the method for selective adsorption recovery comprises the following steps:
s1: introducing the two-stage leaching solution III into a single-stage ion exchange resin column filled with weak-base anion exchange resin to perform adsorption reaction to obtain a liquid I after adsorption and a weak-base anion exchange resin I loaded with tungsten element;
s2: introducing water into the single-stage ion exchange resin column of the weak-alkaline anion exchange resin I loaded with tungsten element obtained in the step S1 to obtain washing liquid and weak-alkaline anion exchange resin II loaded with tungsten element;
(5) Introducing NaOH solution into the single-stage ion exchange resin column of the weak alkaline anion exchange resin II loaded with tungsten element obtained in the step S2 to obtain sodium tungstate solution;
(6) Concentrating, crystallizing, centrifuging and drying the sodium tungstate solution in sequence to obtain a sodium tungstate product;
(7) Regulating the pH value of the first-stage pickle liquor I by using a NaOH solution with the concentration of 30wt% to obtain a first-stage pickle liquor II, filtering the first-stage pickle liquor II by adopting a precise filter to obtain a feed liquid I with the solid particles containing nickel element, cobalt element and manganese element smaller than 15 mu m, and taking the feed liquid I as a raw material for producing ternary precursors of nickel, cobalt and manganese for recycling; the method comprises the steps of,
regulating the pH value of the adsorbed liquid I by using a NaOH solution with the concentration of 30wt% to obtain an adsorbed liquid II, concentrating the adsorbed liquid II to obtain a liquid II containing nickel element, cobalt element and manganese element, and taking the liquid II as a raw material for producing a nickel, cobalt and manganese ternary precursor for recycling;
the sum of the mass concentration of nickel element, cobalt element and manganese element in the feed liquid II is 110g/L.
The remaining specific parameters involved in this example are shown in table 1;
the recovery rate of the metal element in this example is shown in Table 2.
Example 2
This example was carried out using a procedure similar to example 1, except that in this example: the types of materials and process parameters used are different and are shown in Table 1.
The recovery rate of the metal element in this example is shown in Table 2.
Example 3
This example was carried out using a procedure similar to example 1, except that in this example: the types of materials and process parameters used are different and are shown in Table 1.
The recovery rate of the metal element in this example is shown in Table 2.
Example 4
This example was carried out using a procedure similar to example 1, except that in this example:
the amount of the reducing agent used was 3.5g per 100g of the tungsten doped ternary precursor waste I.
The remainder was the same as in example 1.
The remaining specific parameters involved in this example are shown in table 1;
the recovery rate of the metal element in this example is shown in Table 2.
Example 5
This example was carried out using a procedure similar to example 1, except that in this example:
the resin used in the selective adsorption recovery process is D363 weak base anion exchange resin.
The remainder was the same as in example 1.
The remaining specific parameters involved in this example are shown in table 1;
the recovery rate of the metal element in this example is shown in Table 2.
Comparative example 1
The comparative example adopts a one-stage acid leaching method to recover the metal elements in the tungsten-doped ternary precursor waste.
(1) Carrying out primary acid leaching on the tungsten-doped ternary precursor waste I and the first sulfuric acid solution to obtain primary acid leaching liquid I and primary acid leaching slag;
(2) And regulating the pH value of the first-stage pickle liquor I by using a NaOH solution with the concentration of 30wt% to obtain a first-stage pickle liquor II, filtering the first-stage pickle liquor II by adopting a precision filter to obtain a feed liquid with the solid particles containing nickel element, cobalt element and manganese element smaller than 15 mu m, and taking the feed liquid as a raw material for producing a nickel, cobalt and manganese ternary precursor for recycling.
See table 1 for the remaining specific parameters involved in this comparative example;
the recovery rates of the metal elements in this comparative example are shown in Table 2.
Comparative example 2
The comparative example adopts a method combining one-stage chlorogenic acid leaching and ion exchange resin adsorption to recover tungsten element so as to recover metal element in tungsten-doped ternary precursor waste.
(1) Performing primary acid leaching on the tungsten-doped ternary precursor waste I, hydrogen peroxide and a first sulfuric acid solution to obtain primary acid leaching liquid I and primary acid leaching residues;
(2) Regulating the pH value of the first-stage pickle liquor I by using a NaOH solution with the concentration of 30 weight percent to obtain a first-stage pickle liquor II, and filtering by using a precise filter to obtain a first-stage pickle liquor III with solid particles smaller than 15 mu m;
(3) Selectively adsorbing and recovering tungsten element in the first section of pickle liquor III by adopting weak-alkali anion exchange resin to obtain a liquid I after adsorption and weak-alkali anion exchange resin II loaded with tungsten element;
the method for selective adsorption recovery comprises the following steps:
s1: introducing the first-stage leaching solution III into a single-stage ion exchange resin column filled with weak-base anion exchange resin to perform adsorption reaction to obtain a liquid I after adsorption and a weak-base anion exchange resin I loaded with tungsten element;
s2: introducing water into the single-stage ion exchange resin column of the weak-alkaline anion exchange resin I loaded with tungsten element obtained in the step S1 to obtain washing liquid and weak-alkaline anion exchange resin II loaded with tungsten element;
(4) Introducing NaOH solution into the single-stage ion exchange resin column of the weak alkaline anion exchange resin II loaded with tungsten element obtained in the step S2 to obtain sodium tungstate solution;
(5) Concentrating, crystallizing, centrifuging and drying the sodium tungstate solution in sequence to obtain a sodium tungstate product;
(6) With H at a concentration of 5wt% 2 SO 4 And regulating the pH value of the adsorbed liquid I by using the solution to obtain adsorbed liquid II, concentrating the adsorbed liquid II to obtain a liquid containing nickel element, cobalt element and manganese element, and taking the liquid as a raw material for producing a ternary precursor of nickel, cobalt and manganese for recycling.
See table 1 for the remaining specific parameters involved in this comparative example;
the recovery rates of the metal elements in this comparative example are shown in Table 2.
Comparative example 3
This comparative example was conducted using a procedure similar to example 1, except that in this comparative example: the pH of the second-stage pickling solution II was adjusted to 1, and the rest was the same as in example 1.
The recovery rates of the metal elements in this comparative example are shown in Table 2.
TABLE 1
The recovery rate of the metal element in the tungsten doped ternary precursor waste is shown in table 2.
TABLE 2
In summary, the method for comprehensively recovering the metal elements in the tungsten-doped ternary precursor waste provided by the invention can ensure that the recovery rates of nickel element, manganese element, cobalt element and tungsten element are all over 99 percent, and the method provided by the invention can also greatly reduce the consumption of reducing agent, reduce the adsorption time, and has important significance in reducing the production cost, saving the resources and improving the production efficiency.
The preferred embodiments of the present invention have been described in detail above, but the present invention is not limited thereto. Within the scope of the technical idea of the invention, a number of simple variants of the technical solution of the invention are possible, including combinations of the individual technical features in any other suitable way, which simple variants and combinations should likewise be regarded as being disclosed by the invention, all falling within the scope of protection of the invention.

Claims (10)

1. The method for comprehensively recovering the metal elements in the tungsten-doped ternary precursor waste is characterized by comprising the following steps of:
(1) Carrying out primary acid leaching on the tungsten-doped ternary precursor waste and a first sulfuric acid solution to obtain primary acid leaching liquid I and primary acid leaching slag;
(2) In the presence of a reducing agent, carrying out secondary acid leaching on the primary acid leaching slag and a second sulfuric acid solution to obtain a secondary acid leaching liquid I and a secondary acid leaching slag;
(3) Adjusting the pH value of the second-stage pickle liquor I to 2-6 by using an alkaline substance I to obtain a second-stage pickle liquor II, and then filtering the second-stage pickle liquor II to obtain a second-stage pickle liquor III;
(4) Adopting ion exchange resin to carry out selective adsorption recovery on tungsten element in the two-stage pickle liquor III, and obtaining liquid I after adsorption and ion exchange resin loaded with tungsten element;
(5) Contacting the ion exchange resin loaded with tungsten element with an analysis solution to obtain a sodium tungstate solution through analysis;
the method further comprises the steps of: recycling residual elements contained in the first-stage pickle liquor I and the absorbed liquid I, wherein the residual elements contained in the first-stage pickle liquor I and the absorbed liquid I are respectively and independently selected from at least one of nickel element, cobalt element and manganese element;
wherein in the step (1), the condition of the primary acid leaching is controlled so that the pH value of the primary acid leaching solution I is 0-3; the conditions of the primary acid leaching are as follows: the leaching temperature is 40-94 ℃ and the leaching time is 0.5-4h;
in the step (2), controlling the condition of the secondary acid leaching so that the pH value of the obtained secondary acid leaching solution I is 0-3; the conditions of the two-stage acid leaching include: the leaching temperature is 40-94 ℃ and the leaching time is 0.5-3h; the amount of the reducing agent is 3-9g per 100g of the tungsten doped ternary precursor waste.
2. The method according to claim 1, wherein in step (2), the reducing agent is selected from at least one of hydrogen peroxide, sodium sulfite, ammonium sulfite, sodium thiosulfate, and sodium metabisulfite.
3. The process according to claim 1 or 2, wherein in step (4) the ion exchange resin is a weakly basic anion exchange resin.
4. A process according to claim 3, wherein the weakly basic anion exchange resin is selected from at least one of D363, D354 and LSC-486.
5. The method according to claim 1 or 2, wherein in step (4), the conditions of the selective adsorption recovery are controlled so that the mass concentration of tungsten element in the post-adsorption liquid I is < 1mg/L.
6. The method according to claim 1 or 2, wherein in step (5), the resolving liquid is a NaOH solution of 1-3 mol/L.
7. The method according to claim 1 or 2, wherein the method further comprises: and (3) concentrating, crystallizing, centrifuging and drying the sodium tungstate solution obtained in the step (5) in sequence to obtain a sodium tungstate product.
8. The method according to claim 1 or 2, wherein the method further comprises: regulating the pH value of the first-stage pickle liquor I to 2-6 by using an alkaline substance II to obtain a first-stage pickle liquor II, and filtering the first-stage pickle liquor II to obtain a feed liquid I containing nickel element, cobalt element and manganese element; and then the feed liquid I is used as a raw material for producing the nickel, cobalt and manganese ternary precursors so as to realize the recycling.
9. The method according to claim 1 or 2, wherein the method further comprises: and regulating the pH value of the adsorbed liquid I to 2-6 by using an alkaline substance III to obtain an adsorbed liquid II, concentrating the adsorbed liquid II to obtain a liquid II, and then using the liquid II as a raw material for producing a nickel, cobalt and manganese ternary precursor to realize recycling.
10. The method according to claim 9, wherein the concentration conditions are controlled so that the sum of the mass concentrations of nickel element, cobalt element and manganese element in the feed liquid II is not less than 110g/L.
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CN106611841A (en) * 2016-12-19 2017-05-03 中南大学 Method for preparing nickel-cobalt-manganese ternary material precursor by using nickel-cobalt slag material
JP2018021232A (en) * 2016-08-03 2018-02-08 Jx金属株式会社 Method for recovering valuable metals from cobalt and tungsten raw materials
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CN110629034A (en) * 2019-09-16 2019-12-31 厦门钨业股份有限公司 Method for recovering cobalt and nickel from tungsten waste recovery slag
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JP2015196845A (en) * 2014-03-31 2015-11-09 Jx日鉱日石金属株式会社 Method for separating cobalt and tungsten
JP2018021232A (en) * 2016-08-03 2018-02-08 Jx金属株式会社 Method for recovering valuable metals from cobalt and tungsten raw materials
CN106611841A (en) * 2016-12-19 2017-05-03 中南大学 Method for preparing nickel-cobalt-manganese ternary material precursor by using nickel-cobalt slag material
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