CN115074530A - Method for comprehensively recovering valuable metals from neodymium iron boron waste acid leaching residues under hydrochloric acid system - Google Patents

Method for comprehensively recovering valuable metals from neodymium iron boron waste acid leaching residues under hydrochloric acid system Download PDF

Info

Publication number
CN115074530A
CN115074530A CN202210360332.5A CN202210360332A CN115074530A CN 115074530 A CN115074530 A CN 115074530A CN 202210360332 A CN202210360332 A CN 202210360332A CN 115074530 A CN115074530 A CN 115074530A
Authority
CN
China
Prior art keywords
solution
acid
ferrous chloride
acid leaching
purity
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.)
Granted
Application number
CN202210360332.5A
Other languages
Chinese (zh)
Other versions
CN115074530B (en
Inventor
肖燕飞
黄莉
饶明璐
陈金发
文彬
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Jiangxi University of Science and Technology
Original Assignee
Jiangxi University of Science and Technology
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Jiangxi University of Science and Technology filed Critical Jiangxi University of Science and Technology
Priority to CN202210360332.5A priority Critical patent/CN115074530B/en
Publication of CN115074530A publication Critical patent/CN115074530A/en
Application granted granted Critical
Publication of CN115074530B publication Critical patent/CN115074530B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • 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
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01GCOMPOUNDS CONTAINING METALS NOT COVERED BY SUBCLASSES C01D OR C01F
    • C01G49/00Compounds of iron
    • C01G49/02Oxides; Hydroxides
    • C01G49/06Ferric oxide [Fe2O3]
    • 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
    • C22B23/0423Halogenated 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
    • C22B23/00Obtaining nickel or cobalt
    • C22B23/04Obtaining nickel or cobalt by wet processes
    • C22B23/0453Treatment or purification of solutions, e.g. obtained by leaching
    • C22B23/0461Treatment or purification of solutions, e.g. obtained by leaching by chemical methods
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B59/00Obtaining rare earth metals
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01PINDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
    • C01P2004/00Particle morphology
    • C01P2004/30Particle morphology extending in three dimensions
    • C01P2004/32Spheres
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01PINDEXING SCHEME RELATING TO STRUCTURAL AND PHYSICAL ASPECTS OF SOLID INORGANIC COMPOUNDS
    • C01P2006/00Physical properties of inorganic compounds
    • C01P2006/80Compositional purity
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling

Landscapes

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

Abstract

The invention discloses a method for comprehensively recovering valuable metals from neodymium iron boron waste acid leaching residues in a hydrochloric acid system, which comprises the steps of fully dissolving the acid leaching residues by using a hydrochloric acid solution, reducing the obtained acid solution to obtain a ferrous chloride-containing solution, then adding sodium hydroxide, sodium sulfide and sodium bicarbonate in stages to realize fractional precipitation and enrichment of the valuable metals, and finally performing spray pyrolysis on the high-purity ferrous chloride solution after recovering the valuable metals to obtain alpha-Fe with spherical shape and purity of more than 99.2 percent 2 O 3 And (3) powder. The method can enrich and recover rare earth, cobalt and other elements in the neodymium iron boron waste acid leaching residue, improve the utilization value of iron element, and reduce solid residuePiling and reducing environmental pollution.

Description

Method for comprehensively recovering valuable metals from neodymium iron boron waste acid leaching residues under hydrochloric acid system
Technical Field
The invention relates to the field of neodymium iron boron waste recovery, in particular to a method for comprehensively recovering valuable metals from neodymium iron boron waste acid leaching residues under a hydrochloric acid system.
Background
With the rapid development of new energy fields, the demand of the neodymium-iron-boron magnet is rapidly increased. However, during the production process of the neodymium iron boron magnet, from raw material pretreatment to final product detection, waste materials are inevitably generated at each step; in addition, as time goes on, more and more devices using the neodymium iron boron magnet are scrapped due to the fact that the devices are out of service, and a large amount of neodymium iron boron waste materials are generated, so that the annual production amount of the neodymium iron boron waste materials is increased, for example, 2.8 ten thousand tons of waste materials are generated in 2016, and 5.0 ten thousand tons of waste materials are generated in 2021. The content of rare earth in the neodymium iron boron waste material is about 30%, the main elements comprise Ce, Pr, Nd, Gd and the like, and the rest are elements such as iron, aluminum, cobalt and the like. Therefore, the neodymium iron boron waste contains valuable elements with higher content, and has higher comprehensive recycling value.
At present, the valuable metals in the neodymium iron boron waste materials are mainly recovered by a hydrochloric acid optimum solution method in the industry, and the main processes comprise oxidizing roasting, hydrochloric acid optimum solution, extraction separation, precipitation roasting and the like. In the process of oxidizing and roasting the neodymium iron boron waste, the iron element is fully oxidized to form ferric oxide which is difficult to dissolve in acid, and the rare earth element is oxidized to be rare earth oxide; then the roasted product is put into hydrochloric acid for preferential dissolution, so that the rare earth oxide is dissolved and leached preferentially. In the preferential dissolution process of the hydrochloric acid, a certain amount of ferric oxide or incompletely oxidized ferrous oxide is still dissolved and leached into the leachate, at the moment, an oxidant is added into the leachate, the pH value of the leachate is regulated, the dissolved iron element is precipitated in the form of ferric hydroxide and enters acid leaching residue, and finally, the aim of separating most of rare earth from iron is fulfilled by filtering and washing with weak acid. However, the main component of the acid leaching residue is Fe 2 O 3 /Fe(OH) 3 However, the slag still contains a few tenths to a few percent of rare earth elements and metal elements such as cobalt. At present, the acid leaching slag in industry is added into the ferrous metallurgy process to recover the iron element, and valuable metals such as rare earth, cobalt and the like in the slag are not recovered, so that the waste of resources is caused.
There have been some studies on the comprehensive recovery of acid leaching residue, for example, wu zhan and the like, in the study on the comprehensive recovery and utilization technology of secondary waste of neodymium iron boron magnetic materials in the thesis, hydrochloric acid is adopted for complete dissolution, after metal is transferred into solution, hydrolysis of Fe is firstly carried out, beta-FeOOH is obtained by separation, and iron oxide red with the purity of 98.01% is obtained by roasting; then hydrolyzing the solution with NH 4 HCO 3 And (4) a precipitator, namely recovering the rare earth and the cobalt by fractional precipitation through pH adjustment. However, in the process of Fe/RE/Co precipitation separation, the comprehensive recovery rate of relevant valuable metals is not high, namely 89% of iron, 88% of cobalt and only 79% of rare earth. At the same time, in patent CN201610246932.3, sulfuric acid is used for decomposing acid-dissolving slag, and then Fe is reduced by scrap iron 3+ Production of Fe 2+ In the patent, rare earth/cobalt elements in acid leaching slag are recycled and enriched step by step in a solution in the processes of acid decomposition, purification and impurity removal and washing of the iron oxide red, the whole process flow is very complex, the industrial production efficiency is seriously influenced, and the requirement on equipment is high. The patent CN201810865627.1 recovers rare earth elements by a multi-stage acid washing mode, but the recovery rate is not high, the concentration of the obtained solution is low, and the rare earth is difficult to enrich; cobalt also did not collect well. CN201910009567.8 adopts flash reduction mode to separate iron and rare earth, thereby recovering rare earth and iron with high efficiency.
In summary, how to provide a method for efficiently separating valuable elements such as rare earth and iron under the condition that iron element occupies a main body for comprehensive recovery of acid leaching residue generated in the recovery process of neodymium iron boron waste, and meanwhile, high-valued utilization of iron element is performed to improve the recovery benefit of waste in industry, which is a technical problem to be solved urgently at present.
Disclosure of Invention
The invention mainly aims to develop a method for treating neodymium iron boron waste acid leaching residue so as to enrich and recover elements such as rare earth, cobalt and the like, improve the utilization value of iron elements, reduce the stockpiling of solid residue and reduce the environmental pollution.
In order to achieve the purpose, the method for comprehensively recovering the valuable metals from the neodymium iron boron waste acid leaching residue under the hydrochloric acid system specifically comprises the following steps.
(1) Acid leaching residue two-stage countercurrent acid dissolution reduction: carrying out two-stage countercurrent acid leaching on the acid leaching residue by adopting 6.0-9.0mol/L hydrochloric acid solution, controlling the temperature to be 60-90 ℃, and carrying out solid-liquid separation to obtain acid solution and acid leaching residue; then reducing agent is introduced to reduce the acid solution to obtain ferrous chloride-containing solution.
(2) And (3) precipitation and enrichment of valuable metals step by step: firstly, adding a sodium hydroxide solution into the ferrous chloride-containing solution to adjust the pH value to 3.1-3.4, then adding a sodium sulfide solution, wherein the addition amount of sodium sulfide is 3-6 times of the theoretical amount required by complete precipitation of cobalt ions in the ferrous chloride-containing solution, finally adding a mixed solution containing sodium sulfide and sodium bicarbonate to adjust the pH value of the ferrous chloride-containing solution to 4.4-4.7, and carrying out solid-liquid separation to obtain a high-purity ferrous chloride solution and a valuable metal concentrate.
(3) Preparing iron oxide red by spray pyrolysis: diluting high-purity ferrous chloride solution to 30-60g/L (calculated by ferric ions), and then carrying out spray pyrolysis to prepare alpha-Fe 2 O 3 And (3) powder.
Further, the molar ratio of sodium sulfide to sodium bicarbonate in the mixed solution containing sodium sulfide and sodium bicarbonate is 0.2-0.45.
Further, before the step of fractional precipitation and enrichment of valuable metals, one or more of tartaric acid, malic acid, phytic acid, polyvinyl alcohol, hydroxylamine salt and citric acid are added into the ferrous chloride-containing solution.
Further, the reducing agent is waste iron sheet.
Further, the spray pyrolysis temperature is 700-.
Further, the obtained alpha-Fe 2 O 3 The powder is spherical, and the purity reaches more than 99.2%.
According to the composition and characteristics of neodymium iron boron waste acid leaching residue, in order to fully separate iron ions and other non-iron ions and better realize the recovery of valuable metals such as rare earth, cobalt and the like and the high-value utilization of iron elements, 6.0-9.0mol/L hydrochloric acid is adopted to fully dissolve the acid leaching residue at the temperature of 60-90 ℃, the obtained acid solution is reduced to obtain a ferrous chloride-containing solution, then the step-by-step precipitation and enrichment of the valuable metals are realized by adding sodium hydroxide, sodium sulfide and sodium bicarbonate, the elements such as rare earth, cobalt and the like can be recovered as much as possible by controlling the adding sequence and the using amount of a precipitator, and the loss rate of iron is reduced; before the addition of the precipitant, it is preferable to add a solution containing thionyl chlorideOne or more of tartaric acid, malic acid, phytic acid, polyvinyl alcohol, hydroxylamine salt and citric acid are added into the iron solution, so that iron ions and rare earth/cobalt ions can be separated more efficiently; finally, the obtained high-purity ferrous chloride solution is subjected to spray pyrolysis at the temperature of 700- 2 O 3 And (3) powder.
Detailed Description
It should be noted that the embodiments and features of the embodiments in the present application may be combined with each other without conflict. The present application will be described in detail with reference to examples.
The existing method for recovering valuable metals from neodymium iron boron waste acid-soluble slag is mainly a flash method, an acid dissolving-precipitating method and the like, but the methods have some defects, such as low recovery rate of rare earth, cobalt and the like, low purity of iron oxide red and the like, and limit the application field of the methods.
The invention provides a method for comprehensively recovering valuable metals from neodymium iron boron waste acid leaching residues under a hydrochloric acid system, so as to realize the recovery of valuable metals such as rare earth, cobalt and the like and the high-value utilization of iron elements. The method specifically comprises the following steps.
(1) Acid leaching residue two-stage countercurrent acid dissolution reduction: carrying out two-stage countercurrent acid leaching on the acid leaching residue by adopting 6.0-9.0mol/L hydrochloric acid solution, controlling the temperature to be 60-90 ℃, and carrying out solid-liquid separation to obtain acid solution and acid leaching residue; at the moment, the leaching rate of the rare earth reaches more than 95 percent, the leaching rate of the cobalt reaches more than 98 percent, and the leaching rate of the iron exceeds 90 percent. Then reducing the acid solution by introducing a reducing agent to obtain a ferrous chloride-containing solution, wherein the solution is detected by KSCN to generate no red precipitate, and the content of ferric ions in the ferrous chloride-containing solution is less than 0.2 g/L; the preferable reducing agent is waste iron sheet, waste resources can be fully utilized, other impurities are not introduced, and the concentration of the iron element in the ferrous chloride-containing solution can be increased.
(2) And (3) precipitation and enrichment of valuable metals step by step: firstly, adding a sodium hydroxide solution into a ferrous chloride-containing solution to adjust the pH value to 3.1-3.4, and completely precipitating and hydrolyzing aluminum ions in the solution, so that the phenomenon that the existence of the aluminum ions increases the dosage of a subsequent sodium sulfate precipitator can be avoided; then adding a sodium sulfide solution, wherein the addition amount of the sodium sulfide is 3-6 times of the theoretical amount required by the complete precipitation of the cobalt ions in the ferrous chloride-containing solution, and precipitating most of the cobalt ions in the solution; finally, adding a mixed solution of sodium sulfide and sodium bicarbonate, adjusting the pH value of the ferrous chloride solution to 4.4-4.7, basically precipitating rare earth ions and residual cobalt ions, and finally performing solid-liquid separation to obtain a high-purity ferrous chloride solution and a valuable metal concentrate; in the whole process, the precipitation rate of rare earth and cobalt elements is more than 95%, the precipitation rate of aluminum is more than 99%, and the loss rate of ferrous ions is less than 5%. Particularly, the order of the three precipitants cannot be adjusted, otherwise, the problems of large sodium sulfide consumption, high ferrous precipitation rate, low valuable metal precipitation rate and the like are easily caused; moreover, for the mixed solution of sodium sulfide and sodium bicarbonate, the single solution of sodium sulfide or sodium bicarbonate cannot be simply used as the precipitant, because if the single solution of sodium sulfide is used as the precipitant, the rare earth ions are not completely precipitated; if sodium bicarbonate is used as a precipitator, the cobalt ions are not completely precipitated; if a large portion of the cobalt and rare earth are to be precipitated using sodium sulfide or sodium bicarbonate precipitants, the rate of iron loss is greatly increased. Meanwhile, the molar ratio of the sodium sulfide to the sodium bicarbonate in the mixed solution of the sodium sulfide and the sodium bicarbonate is 0.2-0.45, and the rare earth/cobalt and iron elements can be better separated under the condition. If the molar ratio is more than 0.45, the alkalinity of the mixed solution is higher, so that more carbonate is contained in the solution, and the precipitation rate of the iron element is increased in the precipitation process; if the molar ratio is less than 0.2, most of the precipitation of cobalt cannot be achieved while the precipitation of rare earth is complete. Particularly, before the step of fractional precipitation and enrichment of the valuable metal, one or more of tartaric acid, malic acid, phytic acid, polyvinyl alcohol, hydroxylamine salt and citric acid are preferably added into ferrous chloride. By adding the auxiliary agents, ferrous ions can be preferentially complexed more, so that the iron precipitation is reduced when rare earth or cobalt is precipitated, the yield of iron element is finally improved, and the purity of rare earth and cobalt in valuable metal concentrate is increased.
(3) Preparing iron oxide red by spray pyrolysis: diluting high-purity ferrous chloride solution to 30-60g/L, wherein the concentration is calculated by ferric ionsThen spray pyrolysis is carried out at the temperature of 700-1100 ℃, and the obtained alpha-Fe is prepared 2 O 3 And (3) powder. alpha-Fe obtained 2 O 3 The powder is spherical, and the purity reaches more than 99.2%.
The method for comprehensively recovering valuable metals from neodymium iron boron waste acid leaching residues under a hydrochloric acid system provided by the invention will be further described by combining the embodiment.
Comparative example 1
10g of neodymium iron boron waste acid leaching residue is taken, 40mL of 8.0mol/L hydrochloric acid solution is adopted to carry out two-stage countercurrent leaching on the acid leaching residue, the reaction temperature is controlled to be 80 ℃, solid-liquid separation is carried out to obtain the acid solution and the acid leaching residue, at the moment, the rare earth leaching rate is 95.6%, the cobalt leaching rate is 98.4%, and the iron leaching rate is 91.2%; and then, carrying out reduction treatment on the acid solution by adopting waste iron sheets until the solution detects the generation of red precipitates by adopting KSCN (KSCN), thus obtaining a ferrous chloride-containing solution. Adding a sodium hydroxide solution into a ferrous chloride-containing solution to adjust the pH value to 3.2, adding 0.4mol/L sodium sulfide solution, wherein the adding amount of the sodium hydroxide solution is 6 times of the theoretical amount required by complete precipitation of cobalt ions in the ferrous chloride-containing solution, and performing solid-liquid separation to obtain a high-purity ferrous chloride solution and a valuable metal concentrate, wherein the precipitation rate of aluminum ions is 99.1%, the precipitation rate of rare earth ions is 31.5%, the precipitation rate of cobalt ions is 90.2%, and the precipitation rate of iron ions is 0.8%. Diluting high-purity ferrous chloride solution to 45g/L by using purified water, wherein the concentration is calculated by ferric ions, and then carrying out spray pyrolysis at 800 ℃ to prepare the spherical alpha-Fe with the purity of 97.6 percent 2 O 3 And (3) powder.
Comparative example 2
10g of neodymium iron boron waste acid leaching residue is taken, 40mL of 8.0mol/L hydrochloric acid solution is adopted to carry out two-stage countercurrent leaching on the acid leaching residue, the reaction temperature is controlled to be 80 ℃, solid-liquid separation is carried out to obtain the acid solution and the acid leaching residue, at the moment, the rare earth leaching rate is 95.6%, the cobalt leaching rate is 98.4%, and the iron leaching rate is 91.2%; and then, carrying out reduction treatment on the acid solution by adopting waste iron sheets until the solution detects the generation of red precipitates by adopting KSCN (KSCN), thus obtaining a ferrous chloride-containing solution. Adding sodium hydroxide solution into ferrous chloride-containing solution for regulationAnd (2) when the pH value is 3.2, adding 0.4mol/L sodium sulfide solution, wherein the addition amount of the sodium sulfide solution is 6 times of the theoretical amount required by the complete precipitation of cobalt ions in the ferrous chloride-containing solution, finally adding a mixed solution with the molar ratio of sodium sulfide to sodium bicarbonate being 0.6, adjusting the pH value of the ferrous chloride solution to be 4.6, and carrying out solid-liquid separation to obtain a high-purity ferrous chloride solution and a valuable metal concentrate, wherein the precipitation rate of aluminum ions is 99.2%, the precipitation rate of rare earth ions is 86.2%, the precipitation rate of cobalt ions is 96.2%, and the precipitation rate of iron ions is 9.1%. Diluting high-purity ferrous chloride solution to 45g/L by using purified water, wherein the concentration is calculated by ferric ions, and then carrying out spray pyrolysis at 800 ℃ to prepare alpha-Fe with spherical shape and 98.1% purity 2 O 3 And (3) powder.
Comparative example 3
10g of neodymium iron boron waste acid leaching residue is taken, 40mL of 8.0mol/L hydrochloric acid solution is adopted to carry out two-stage countercurrent leaching on the acid leaching residue, the reaction temperature is controlled to be 80 ℃, solid-liquid separation is carried out to obtain the acid solution and the acid leaching residue, at the moment, the rare earth leaching rate is 95.6%, the cobalt leaching rate is 98.4%, and the iron leaching rate is 91.2%; and then, carrying out reduction treatment on the acid solution by adopting waste iron sheets until the solution detects the generation of red precipitates by adopting KSCN (KSCN), thus obtaining a ferrous chloride-containing solution. Adding a sodium hydroxide solution into a ferrous chloride-containing solution to adjust the pH value to 3.2, adding a mixed solution of sodium sulfide and sodium bicarbonate with the molar ratio of 0.4, adjusting the pH value of the ferrous chloride solution to 4.6, and carrying out solid-liquid separation to obtain a high-purity ferrous chloride solution and a valuable metal concentrate, wherein the precipitation rate of aluminum ions is 99.2%, the precipitation rate of rare earth ions is 96.1%, the precipitation rate of cobalt ions is 86.4%, and the precipitation rate of iron ions is 8.3%. Diluting high-purity ferrous chloride solution to 45g/L with purified water, wherein the concentration is calculated by ferric ions, and then carrying out spray pyrolysis at 800 ℃ to prepare spherical alpha-Fe with the purity of 97.8 percent 2 O 3 And (3) powder.
Comparative example 4
10g of neodymium iron boron waste acid leaching residue is taken, 40mL of 8.0mol/L hydrochloric acid solution is adopted to carry out two-stage countercurrent leaching on the acid leaching residue, the reaction temperature is controlled to be 80 ℃, solid-liquid separation is carried out to obtain the acid solution and the acid leaching residue, and at the moment, the rare earth leaching rate is higher95.6 percent, the leaching rate of cobalt is 98.4 percent, and the leaching rate of iron is 91.2 percent; and then, carrying out reduction treatment on the acid solution by adopting waste iron sheets until the solution detects the generation of red precipitates by adopting KSCN (KSCN), thus obtaining a ferrous chloride-containing solution. Adding a sodium hydroxide solution into a ferrous chloride-containing solution to adjust the pH value to 3.2, adding 0.4mol/L sodium sulfide solution, wherein the adding amount of the sodium hydroxide solution is 6 times of the theoretical amount required by the complete precipitation of cobalt ions in the ferrous chloride-containing solution, finally adding a sodium bicarbonate solution to adjust the pH value of the ferrous chloride solution to 4.6, and performing solid-liquid separation to obtain a high-purity ferrous chloride solution and a valuable metal concentrate, wherein the precipitation rate of aluminum ions is 99.2%, the precipitation rate of rare earth ions is 97.1%, the precipitation rate of cobalt ions is 83.2%, and the precipitation rate of iron ions is 6.8%. Diluting high-purity ferrous chloride solution to 45g/L by using purified water, wherein the concentration is calculated by ferric ions, and then carrying out spray pyrolysis at 800 ℃ to prepare the spherical alpha-Fe with the purity of 97.9 percent 2 O 3 And (3) powder.
Example 1
10g of neodymium iron boron waste acid leaching residue is taken, 40mL of 8.0mol/L hydrochloric acid solution is adopted to carry out two-stage countercurrent leaching on the acid leaching residue, the reaction temperature is controlled to be 80 ℃, solid-liquid separation is carried out to obtain the acid solution and the acid leaching residue, at the moment, the rare earth leaching rate is 95.6%, the cobalt leaching rate is 98.4%, and the iron leaching rate is 91.2%; and then, carrying out reduction treatment on the acid solution by adopting waste iron sheets until the solution detects the generation of red precipitates by adopting KSCN (KSCN), thus obtaining a ferrous chloride-containing solution. Adding a sodium hydroxide solution into a ferrous chloride-containing solution to adjust the pH value to 3.2, adding 0.4mol/L sodium sulfide solution, wherein the adding amount of the sodium sulfide solution is 6 times of the theoretical amount required by complete precipitation of cobalt ions in the ferrous chloride-containing solution, finally adding a mixed solution of sodium sulfide and sodium bicarbonate with the molar ratio of 0.4, adjusting the pH value of the ferrous chloride solution to 4.6, and carrying out solid-liquid separation to obtain a high-purity ferrous chloride solution and a valuable metal concentrate, wherein the precipitation rate of aluminum ions is 99.2%, the precipitation rate of rare earth ions is 96.5%, the precipitation rate of cobalt ions is 96.2%, and the precipitation rate of iron ions is 4.4%. Diluting high-purity ferrous chloride solution to 45g/L with purified water, wherein the concentration is calculated by ferric ions, and then carrying out spray pyrolysis at 800 ℃ to prepare the shapeIs spherical alpha-Fe with purity up to 99.2% 2 O 3 And (3) powder.
Example 2
10g of neodymium iron boron waste acid leaching residue is taken, 40mL of hydrochloric acid solution with the concentration of 7.0mol/L is adopted to carry out two-stage countercurrent leaching on the acid leaching residue, the reaction temperature is controlled to be 90 ℃, solid-liquid separation is carried out to obtain the acid solution and the acid leaching residue, at the moment, the rare earth leaching rate is 96.4%, the cobalt leaching rate is 99.1%, and the iron leaching rate is 92.0%; and then, reducing the acid solution by using ascorbic acid until the solution detects the generation of red precipitate by using KSCN, thereby obtaining a ferrous chloride-containing solution. Adding a sodium hydroxide solution into a ferrous chloride-containing solution to adjust the pH value to 3.3, adding 0.4mol/L sodium sulfide solution, wherein the addition amount of the sodium sulfide solution is 4 times of the theoretical amount required by complete precipitation of cobalt ions in the ferrous chloride-containing solution, finally adding a mixed solution of sodium sulfide and sodium bicarbonate with the molar ratio of 0.3, adjusting the pH value of the ferrous chloride solution to 4.5, and carrying out solid-liquid separation to obtain a high-purity ferrous chloride solution and a valuable metal concentrate, wherein the precipitation rate of aluminum ions is 99.2%, the precipitation rate of rare earth ions is 95.7%, the precipitation rate of cobalt ions is 96.7%, and the precipitation rate of iron ions is 4.0%. Diluting high-purity ferrous chloride solution to 55g/L by using purified water, wherein the concentration is calculated by ferric ions, and then carrying out spray pyrolysis at 1000 ℃ to prepare the spherical alpha-Fe with the purity of 99.4 percent 2 O 3 And (3) powder.
Example 3
10g of neodymium iron boron waste acid leaching residue is taken, 40mL of 9.0mol/L hydrochloric acid solution is adopted to carry out two-stage countercurrent leaching on the acid leaching residue, the reaction temperature is controlled to be 70 ℃, solid-liquid separation is carried out to obtain the acid solution and the acid leaching residue, at the moment, the rare earth leaching rate is 95.6%, the cobalt leaching rate is 98.6%, and the iron leaching rate is 91.4%; and then, carrying out reduction treatment on the acid solution by adopting waste iron sheets until the solution detects the generation of red precipitates by adopting KSCN (KSCN), thus obtaining a ferrous chloride-containing solution. Adding tartaric acid into ferrous chloride-containing solution to make the concentration of tartaric acid in the solution be 0.5g/L, regulating pH to 3.1 by using sodium hydroxide solution, then adding 0.4mol/L sodium sulfide solution, its addition quantity is 5 times of required theoretical dosage for completely precipitating cobalt ion in the above-mentioned ferrous chloride-containing solution, and its optimum dosage isThen adding a mixed solution with the molar ratio of sodium sulfide to sodium bicarbonate being 0.2, adjusting the pH value of the ferrous chloride solution to be 4.7, and carrying out solid-liquid separation to obtain a high-purity ferrous chloride solution and a valuable metal concentrate, wherein the precipitation rate of aluminum ions is 99.3%, the precipitation rate of rare earth ions is 96.9%, the precipitation rate of cobalt ions is 97.7%, and the precipitation rate of iron ions is 3.5%. Diluting high-purity ferrous chloride solution to 30g/L by using purified water, wherein the concentration is calculated by ferric ions, and then carrying out spray pyrolysis at 700 ℃ to prepare the spherical alpha-Fe with the purity of 99.5 percent 2 O 3 And (3) powder.
Example 4
10g of neodymium iron boron waste acid leaching residue is taken, 40mL of 6.0mol/L hydrochloric acid solution is adopted to carry out two-stage countercurrent leaching on the acid leaching residue, the reaction temperature is controlled to be 65 ℃, solid-liquid separation is carried out to obtain the acid solution and the acid leaching residue, at the moment, the rare earth leaching rate is 95.3%, the cobalt leaching rate is 98.9%, and the iron leaching rate is 91.8%; and then, carrying out reduction treatment on the acid solution by adopting waste iron sheets until the solution detects the generation of red precipitates by adopting KSCN (KSCN), thus obtaining a ferrous chloride-containing solution. Adding phytic acid into a ferrous chloride-containing solution to enable the concentration of the phytic acid in the solution to be 1.0g/L, adjusting the pH to be 3.4 by adopting a sodium hydroxide solution, then adding 0.4mol/L sodium sulfide solution, wherein the adding amount of the sodium sulfide solution is 3 times of the theoretical amount required by the complete precipitation of cobalt ions in the ferrous chloride-containing solution, finally adding a mixed solution with the molar ratio of sodium sulfide to sodium bicarbonate being 0.45, adjusting the pH of the ferrous chloride solution to be 4.4, and carrying out solid-liquid separation to obtain a high-purity ferrous chloride solution and valuable metal concentrate, wherein the precipitation rate of aluminum ions is 99.4%, the precipitation rate of rare earth ions is 96.1%, the precipitation rate of cobalt ions is 98.7%, and the precipitation rate of iron ions is 3.2%. Diluting high-purity ferrous chloride solution to 60g/L by using purified water, wherein the concentration is calculated by ferric ions, and then carrying out spray pyrolysis at 900 ℃ to prepare the spherical alpha-Fe with the purity of 99.4 percent 2 O 3 And (3) powder.

Claims (6)

1. A method for comprehensively recovering valuable metals from neodymium iron boron waste acid leaching residues under a hydrochloric acid system is characterized by comprising the following steps:
(1) acid leaching residue two-stage countercurrent acid dissolution reduction: carrying out two-stage countercurrent acid leaching on the acid leaching residue by adopting 6.0-9.0mol/L hydrochloric acid solution, controlling the temperature to be 60-90 ℃, and carrying out solid-liquid separation to obtain acid solution and acid leaching residue; then introducing a reducing agent to carry out reduction treatment on the acid solution to obtain a ferrous chloride-containing solution;
(2) and (3) precipitation and enrichment of valuable metals step by step: firstly, adding a sodium hydroxide solution into the ferrous chloride-containing solution to adjust the pH value to 3.1-3.4, then adding a sodium sulfide solution, wherein the addition amount of sodium sulfide is 3-6 times of the theoretical amount required by complete precipitation of cobalt ions in the ferrous chloride-containing solution, finally adding a mixed solution containing sodium sulfide and sodium bicarbonate to adjust the pH value of the ferrous chloride-containing solution to 4.4-4.7, and carrying out solid-liquid separation to obtain a high-purity ferrous chloride solution and a valuable metal concentrate;
(3) preparing iron oxide red by spray pyrolysis: diluting high-purity ferrous chloride solution to 30-60g/L (calculated by ferric ions), and then carrying out spray pyrolysis to prepare alpha-Fe 2 O 3 And (3) powder.
2. The method according to claim 1, wherein the molar ratio of sodium sulfide to sodium bicarbonate in the mixed solution containing sodium sulfide and sodium bicarbonate in the step (2) is 0.2 to 0.45.
3. The method of claim 1, wherein step (2) is preceded by the addition of one or more of tartaric acid, malic acid, phytic acid, polyvinyl alcohol, hydroxylamine salts, citric acid to the acid solution.
4. The method of claim 1, wherein the reducing agent is scrap iron.
5. The method as claimed in claim 1, wherein the spray pyrolysis temperature is 700-.
6. The method of claim 1, wherein α -Fe 2 O 3 The morphology of the powder isSpherical, and the purity reaches more than 99.2 percent.
CN202210360332.5A 2022-04-07 2022-04-07 Method for comprehensively recovering valuable metals from neodymium iron boron waste acid leaching residues under hydrochloric acid system Active CN115074530B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202210360332.5A CN115074530B (en) 2022-04-07 2022-04-07 Method for comprehensively recovering valuable metals from neodymium iron boron waste acid leaching residues under hydrochloric acid system

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202210360332.5A CN115074530B (en) 2022-04-07 2022-04-07 Method for comprehensively recovering valuable metals from neodymium iron boron waste acid leaching residues under hydrochloric acid system

Publications (2)

Publication Number Publication Date
CN115074530A true CN115074530A (en) 2022-09-20
CN115074530B CN115074530B (en) 2023-07-18

Family

ID=83246850

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202210360332.5A Active CN115074530B (en) 2022-04-07 2022-04-07 Method for comprehensively recovering valuable metals from neodymium iron boron waste acid leaching residues under hydrochloric acid system

Country Status (1)

Country Link
CN (1) CN115074530B (en)

Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB662051A (en) * 1948-01-06 1951-11-28 Davide Primavesi Improved chemical process for producing powdered iron
CA1171608A (en) * 1982-06-21 1984-07-31 Xuan T. Nguyen Recovery process for kraft black liquor
CN105734296A (en) * 2016-04-20 2016-07-06 南阳东方应用化工研究所 Comprehensive utilization method of neodymium iron boron waste acid leaching slag
CN106319227A (en) * 2016-08-23 2017-01-11 赣州市恒源科技股份有限公司 Comprehensive utilization method for acid leaching slag of neodymium iron boron waste
CN108913918A (en) * 2018-07-09 2018-11-30 武汉工程大学 A method of utilizing extremely dilute earth solution recovering rare earth of weathered superficial leaching rare-earth ore Situ Leaching
CN113104901A (en) * 2021-04-13 2021-07-13 江西理工大学 Method for preparing iron oxide yellow from rare earth waste acid leaching residues
CN113293307A (en) * 2021-06-03 2021-08-24 中国科学院江西稀土研究院 Method for extracting iron and cobalt from neodymium iron boron waste iron tailings obtained by hydrochloric acid optimum dissolution method

Patent Citations (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB662051A (en) * 1948-01-06 1951-11-28 Davide Primavesi Improved chemical process for producing powdered iron
CA1171608A (en) * 1982-06-21 1984-07-31 Xuan T. Nguyen Recovery process for kraft black liquor
CN105734296A (en) * 2016-04-20 2016-07-06 南阳东方应用化工研究所 Comprehensive utilization method of neodymium iron boron waste acid leaching slag
CN106319227A (en) * 2016-08-23 2017-01-11 赣州市恒源科技股份有限公司 Comprehensive utilization method for acid leaching slag of neodymium iron boron waste
CN108913918A (en) * 2018-07-09 2018-11-30 武汉工程大学 A method of utilizing extremely dilute earth solution recovering rare earth of weathered superficial leaching rare-earth ore Situ Leaching
CN113104901A (en) * 2021-04-13 2021-07-13 江西理工大学 Method for preparing iron oxide yellow from rare earth waste acid leaching residues
CN113293307A (en) * 2021-06-03 2021-08-24 中国科学院江西稀土研究院 Method for extracting iron and cobalt from neodymium iron boron waste iron tailings obtained by hydrochloric acid optimum dissolution method

Also Published As

Publication number Publication date
CN115074530B (en) 2023-07-18

Similar Documents

Publication Publication Date Title
EP4269337A1 (en) Method for recovering lithium in lithium iron phosphate waste and application thereof
CN104831065B (en) Manganese cobalt high is than method that nickel cobalt in nickel cobalt manganese raw material with manganese separate
CN110093506B (en) Method for efficiently extracting valuable metals from germanium-containing zinc leaching residues and reducing valuable metals
AU2018252056A1 (en) Method for comprehensively recycling copper-nickel sulfide ore and system thereof
CN111945002B (en) Method for removing copper from waste lithium batteries by recovery wet process
CN108707748B (en) Method for purifying stone coal pickle liquor and recovering aluminum, potassium and iron
KR101713600B1 (en) Method of recovering lithium in wastewater obtained from waste lithium battery recycling process
CN109929997B (en) Method for producing germanium concentrate by using N235 extracting agent
CN111286604B (en) Method for preparing and recycling valuable metal by using crude nickel hydroxide
CN113046574B (en) Method for preparing high-purity nickel and cobalt products by treating crude cobalt hydroxide with copper electrolysis decoppering post-treatment solution
WO2023000847A1 (en) Nickel-iron wet treatment method and application thereof
CN111575491A (en) Resource comprehensive utilization method for purifying cobalt-nickel slag by zinc hydrometallurgy arsenic salt
CN113279048A (en) Method for preparing high-purity iron phosphate from iron-containing slag
CN113186405A (en) Comprehensive treatment and recovery method for high-chlorine zinc-manganese-copper-cobalt material
CN105274352B (en) A kind of method that copper cobalt manganese is separated in the manganese cobalt calcium zinc mixture from copper carbonate
CN112410568A (en) Method for preparing cobalt ferrite from cobalt-containing slag
CN111549239B (en) Resourceful treatment method of magnesium-containing raw material
CN113512652B (en) Method for extracting gallium metal from coal-series solid waste
CN112981124A (en) Method for separating and enriching thallium from thallium-containing cobalt oxide waste residue
CN115074530B (en) Method for comprehensively recovering valuable metals from neodymium iron boron waste acid leaching residues under hydrochloric acid system
CN114875241B (en) Method for comprehensively recovering valuable metals from neodymium iron boron waste acid leaching residues under sulfuric acid system
CN114015880B (en) Metal recovery processing method for battery reclaimed material
WO2020181607A1 (en) Method for extracting ions from ore solution
KR20230136948A (en) Selective recovery method of valuable metals using solvent extraction from lithium secondary battery waste
KR20150076345A (en) Method for extracting iron in nickel smelting process

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant