CN101988154B - New technology for preparing electrolytic manganese metal solution and recycling iron by reducing pyrolusite with iron scraps - Google Patents

New technology for preparing electrolytic manganese metal solution and recycling iron by reducing pyrolusite with iron scraps Download PDF

Info

Publication number
CN101988154B
CN101988154B CN201010535033A CN201010535033A CN101988154B CN 101988154 B CN101988154 B CN 101988154B CN 201010535033 A CN201010535033 A CN 201010535033A CN 201010535033 A CN201010535033 A CN 201010535033A CN 101988154 B CN101988154 B CN 101988154B
Authority
CN
China
Prior art keywords
pyrolusite
iron
electrolytic manganese
reaction
solution
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Fee Related
Application number
CN201010535033A
Other languages
Chinese (zh)
Other versions
CN101988154A (en
Inventor
易清风
蔡振勇
刘汉勇
方明略
龚学华
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.)
XIANGXI AUTONOMOUS PREFECTURE JIN GE MANGANESE INDUSTRY Co Ltd
Hunan University of Science and Technology
Original Assignee
XIANGXI AUTONOMOUS PREFECTURE JIN GE MANGANESE INDUSTRY Co Ltd
Hunan 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 XIANGXI AUTONOMOUS PREFECTURE JIN GE MANGANESE INDUSTRY Co Ltd, Hunan University of Science and Technology filed Critical XIANGXI AUTONOMOUS PREFECTURE JIN GE MANGANESE INDUSTRY Co Ltd
Priority to CN201010535033A priority Critical patent/CN101988154B/en
Publication of CN101988154A publication Critical patent/CN101988154A/en
Application granted granted Critical
Publication of CN101988154B publication Critical patent/CN101988154B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • 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

  • Manufacture And Refinement Of Metals (AREA)
  • Electrolytic Production Of Metals (AREA)

Abstract

The invention discloses a new technology for preparing manganese sulfate solution which is used for electrolyzing manganese metal and recycling iron through the atmospheric pressure leaching of pyrolusite and iron scraps. The technology comprises the following steps: adding pyrolusite in a certain concentration of sulphuric acid solution, mixing evenly; adding iron scraps used as the reductant in a reaction tank, performing mechanical agitation for 1h-3h under different reaction temperatures to obtain reaction leachate; according to the changes of the reaction time and the pH value, adding heavy calcium carbonate and ammonia water in turn to adjust the pH value of the solution to 6.3-6.7; then adding sodium N,N-dimethyl dithiocarbaminate (SDD) to remove impurities such as heavy metal ions and purify; filtering, adding additive to obtain manganese sulfate solution used for electrolyzing manganese; and recycling iron from filter residue through alkali leaching and acid leaching to produce polyferric sulfate. The invention has the advantage that iron scraps are used as the reductant which have wide sources and rich raw materials and can be leached out under the atmospheric pressure; and iron scraps can be recycled to produce the water purification agent and have great economic benefit.

Description

The waste iron filing reducing pyrolusite prepares electrolytic manganese metal solution and reclaims the novel process of iron
Technical field
The present invention relates to a kind of be reductive agent with the waste iron filing, normal pressure leaches the manganese sulfate solution be used for electrolytic metal Mn from pyrolusite novel process, the novel process that exploitation is simultaneously reclaimed iron and produced bodied ferric sulfate belongs to the hydrometallurgy field.
Background technology
Waste iron filing produces in mechanical workout or machinofacture process, and waste iron filing just can be used as industrial chemicals or production chemical product through after the oil removal treatment, turns waste into wealth, and reduces the waste of resource.China all will produce a large amount of waste iron filings every year; A lot of recycling becomes particularly important owing to utilizing improper or directly abandoning as sub product, not only can increase economic added value; And be the development trend of comprehensive utilization of waste materials, meet the strategy of sustainable development.
At present, the reductive agent that is used as pyrolusite mainly contains sulfurous iron ore, sulfurous gas, ferrous sulfate, cane molasses alcohol slops etc., the suitability for industrialized production that has, and what have is also carrying out the test of theory study and Small Scale Industry.Comprehensive various bibliographical information, pyrolusite reduction preparation manganous sulfate mainly contains following several method:
1, reduction roasting method: with pyrolusite and reductive agent (C, CO, H 2, CH 4Deng) reaction, being reduced to bivalent manganese to tetravalence manganese, the bivalent manganese that reduction obtains is dissolved in sulphuric acid soln, and through purification and impurity removal, finally producing various manganese is product, is a traditional technology.But this technological equipment investment is big, and big energy-consuming produces a large amount of waste gas waste residues in process of production, and is seriously polluted, and country prohibites time technology and uses.
2, two ore deposit single stage method: with a certain proportion of pyrolusite, sulfurous iron ore pulverize mix after, leach with sulfuric acid, can make the Manganse Dioxide in the pyrolusite be reduced to manganous sulfate; Compare reduction roasting method and save the high-temperature roasting operation, simplified apparatus and technical process thereof, the price of sulfurous iron ore is lower; Wide material sources reduce cost, but the manganese leaching yield of two ore deposit single stage method is low; Filter residue is many, and the purification and impurity removal difficulty is difficult to obtain qualified electrolytic manganese solution.
3, sulfurous gas lixiviation process: sulfurous gas directly is passed in the pulp bucket that pyrolusite is housed reduces; Be a kind of sophisticated technology; In leaching reaction process, produce the by product manganous dithionate, influence the quality of product, so far also not widespread use in industry.
A kind of gray manganese ore leaching out process like one Chinese patent application 200610122400.5; Adopting the cane molasses alcohol slops is reductive agent; The leach liquor that stirring reaction 0.5-4h obtains reacting under 50-98 ℃ of temperature; But cane molasses alcohol is prone to produce organism in reaction, has introduced new impurity in the solution, and organism is difficult for purifying to be removed.And for example a kind of of one Chinese patent application 200710151596.5 produces the method for manganous sulfate by manganese oxide ore, and adopting ferrous sulfate or sulphur is reductive agent, under certain temperature and pressure, reacts; Though this technology is comparatively ripe, the manganese leaching yield is high, and cost is high; The quantity of slag is big, the filtering and impurity removing difficulty.
Summary of the invention
The purpose of this invention is to provide the novel process that pyrolusite and waste iron filing normal pressure leach the manganese sulfate solution that is used for electrolytic metal Mn; As reductive agent, not only technical process is simple relatively, mild condition with waste iron filing for it; Speed of response is fast; The leaching yield of manganese is high in the pyrolusite, and is pollution-free, and filter residue can be recycled production water purification agent bodied ferric sulfate.
For achieving the above object, embodiment of the present invention are: a kind of waste iron filing reducing pyrolusite prepares electrolytic manganese metal solution and reclaims the novel process of iron, may further comprise the steps:
(1) pyrolusite is dropped in the reaction kettle, the anolyte that produces when adding zero(ppm) water or electrolytic manganese, the weight proportion of the anolyte that produces when pyrolusite and zero(ppm) water or electrolytic manganese is 1:5.0 ~ 15.0;
(2) under mechanical stirring, add the vitriol oil and ammonium sulfate in the reaction kettle, make that sulfuric acid concentration reaches 100-200g/L in the mixed solution, ammonium sulfate concentrations reaches 100 ~ 200g/L;
(3) add waste iron filing, leach reaction 0.5 ~ 1h in 25 ~ 60 ℃ of following mechanical stirring of temperature, reaction 1-2h is leached in elevated temperature to 70 ~ 100 a ℃ continuation, impels material reaction complete;
(4) water-ground limestone of adding pyrolusite weight 10% ~ 25%, after reacting completely, using concentration again is pH value to 6.3 ~ 6.7 of 20% ~ 28% ammoniacal liquor regulator solution;
(5) 0.2% ~ 1.5% of adding pyrolusite weight Sodium dimethyldithiocarbamate 40min, reaction 0.5 ~ 1h, removal of impurities removing heavy metals ion filters cooling, adds tin anhydride in the filtrating, obtains directly being used for the manganese sulfate solution of electrolytic manganese.
(6) after filtration back gained filter residue and zero(ppm) water mix in the step (5); Under 50 ~ 90 ℃ of temperature of reaction, add quicklime or calcium hydroxide or both mixtures, mechanical stirring reaction 0.5 ~ 1.5h; Filtration washing; The filter residue of gained adds dilute sulphuric acid and leaches reaction 0.5 ~ 1h at normal temperatures, filters and obtains ferrum sulfuricum oxydatum solutum, obtains bodied ferric sulfate through underpressure distillation.
In the step (2), the mol ratio of Manganse Dioxide is 1.2 ~ 2.8:1 in the vitriol oil of adding and the pyrolusite.
In the step (2), churned mechanically speed is 800 ~ 2500r/min.
In the step (3), the mol ratio of Manganse Dioxide is 0.5 ~ 1.5: 1 in the waste iron filing of adding and the pyrolusite.
In the step (5), the tin anhydride concentration of adding is 0.02 ~ 0.08g/L.
In the step (6), the mol ratio of quicklime or calcium hydroxide or both mixtures and waste iron filing is 0.5 ~ 2.5: 1.
In the step (6), churned mechanically speed is 400 ~ 1000r/min.
In the step (6), the concentration of dilute sulphuric acid is 1.0 ~ 4.5mol/L.
In the process of electrolysis production manganese metal, manganese sulfate solution there is strict requirement, not only the acidity of solution will maintain certain scope, and the content of other metals ions is also had strict restriction.Generally speaking, the foreign matter content in the solution requires: iron is less than 0.2mg/L, and cobalt is less than 0.5 mg/L; Nickel is less than 1 mg/L, and silicon is less than 10 mg/L, and copper is less than 0.5 mg/L; If the pH value of solution or the heavy metal ion of solution exceed standard, in the process of electrolytic manganese, might cause the anti-of manganese to be dissolved.The present invention is provided for the manganese sulfate solution of electrolysis production manganese.The present invention has realized the novel process with waste iron filing is made reductive agent, extraction can be used for the manganese sulfate solution of electrolysis production manganese from pyrolusite; Extraction temperature is divided into two sections; Make that Manganse Dioxide leaches in the short period of time in the pyrolusite, the leaching yield of manganese is more than 95%, and slag manganese content is below 1%.The present invention has following advantage:
1, compare with traditional technology, simplify technical process, mild condition, speed of response is fast, under normal pressure, just can leach.
2, with adopt the cane molasses alcohol slops to do former dose to compare, in the reaction leaching process, can not produce organism, the removal of impurities ratio of subsequent solution be easier to and electrolysis unaffected.
3, the leaching yield of manganese is high in the pyrolusite, and is pollution-free, and filter residue can be recycled and produce the water purification agent bodied ferric sulfate, and inclusion-free is discharged to outward in the environment, is a green production process, for low-grade pyrolusite development of resources new application approach.
Embodiment
Embodiment 1: pyrolusite contains manganese 33.15%.
The pyrolusite that will contain manganese 33.15% joins in the reaction kettle that can hold 500 milliliters, and it is 10:1 that adding distil water makes its liquid-solid ratio, under the condition of mechanical stirring intensity 1000r/min; Adding the vitriol oil in the reaction kettle makes its concentration reach 100g/L; Ammonium sulfate concentrations reaches 100g/L, and the temperature that mixes the afterreaction still is elevated to 30 ℃, and the mol ratio 1:0.6 that presses Manganse Dioxide and waste iron filing in the pyrolusite adds waste iron filing; Be warmed up to 70 ℃ behind the reaction 60min and continue reaction 60min; Keep adding water-ground limestone successively under the temperature-resistant condition and ammoniacal liquor is regulated pH value 6.5, add SDD and remove heavy metal, carry out the separation of slag liquid; The manganese leaching yield is 96.12%, and slag contains manganese 0.5%.The solution non-shock chilling that obtains; Adding tin anhydride solid makes content reach 0.03g/L and is the manganese sulfate solution that is used for electrolytic manganese production; And filter residue, zero(ppm) water mix the back temperature and are raised to 60 ℃ in reaction kettle, and adding quicklime, to make the mol ratio of its add-on and waste iron filing be 1:1, under the condition of mechanical stirring intensity 400r/min, reacts 60min; Carry out filtration washing; The filter residue of gained adds an amount of 1.5mol/L dilute sulphuric acid and leaches reaction 30min at normal temperatures, and solution filters and obtains ferrum sulfuricum oxydatum solutum, can obtain qualified polyaluminum sulfate iron product through underpressure distillation again.
Embodiment 2 pyrolusites contain manganese 33.15%
The pyrolusite that will contain manganese 33.15% joins in the reaction kettle that can hold 500 milliliters, the anolyte that produces when adding electrolytic manganese (anolyte staple: Mn 2+11.0g/L, sulfuric acid 31.5 g/L, ammonium sulfate 90 g/L) and to make its liquid-solid ratio be 8:1; Under the condition of mechanical stirring intensity 1500r/min, add the vitriol oil in the reaction kettle and make its concentration reach 150g/L, ammonium sulfate concentrations reaches 100g/L; The temperature that mixes the afterreaction still is elevated to 40 ℃, and the mol ratio 1:1.2 that presses Manganse Dioxide and waste iron filing in the pyrolusite adds waste iron filing, is warmed up to 100 ℃ behind the reaction 60min and continues reaction 60min; Keep adding water-ground limestone successively under the temperature-resistant condition and ammoniacal liquor is regulated pH value 6.3, add SDD and remove heavy metal, carry out the separation of slag liquid; The manganese leaching yield is 95.02%, and slag contains manganese 0.8%.The solution non-shock chilling that obtains; Adding tin anhydride solid makes content reach 0.07g/L and is the manganese sulfate solution that is used for electrolytic manganese production; And filter residue, zero(ppm) water mix the back temperature and are raised to 80 ℃ in reaction kettle, and adding calcium hydroxide, to make the mol ratio of its add-on and waste iron filing be 2:1, under the condition of mechanical stirring intensity 900r/min, reacts 30min; Carry out filtration washing; The filter residue of gained adds an amount of 2.5mol/L dilute sulphuric acid and leaches reaction 30min at normal temperatures, and solution filters and obtains ferrum sulfuricum oxydatum solutum, can obtain qualified polyaluminum sulfate iron product through underpressure distillation again.
Embodiment 3 pyrolusites contain manganese 33.15%
The pyrolusite that will contain manganese 33.15% joins in the reaction kettle that can hold 500 milliliters, and it is 13:1 that adding distil water makes its liquid-solid ratio, under the condition of mechanical stirring intensity 2000r/min; Add the vitriol oil in the reaction kettle and make its concentration reach 200g/L, ammonium sulfate concentrations reaches 100g/L, and the temperature that mixes the afterreaction still is elevated to 60 ℃; The mol ratio 1:1.0 that presses Manganse Dioxide and waste iron filing in the pyrolusite adds waste iron filing, is warmed up to 90 ℃ behind the reaction 60min and continues reaction 60min, keeps adding water-ground limestone and ammoniacal liquor adjusting pH value 6.7 successively under the temperature-resistant condition; Add SDD and remove heavy metal; Carry out slag liquid and separate, the manganese leaching yield is 98.41%, and slag contains manganese 1%.The solution non-shock chilling that obtains; Adding tin anhydride solid makes content reach 0.08g/L and is the manganese sulfate solution that is used for electrolytic manganese production; And filter residue, zero(ppm) water mix the back temperature and are raised to 70 ℃ in reaction kettle, and it is 1.5:1 that the mixture that adds quicklime and calcium hydroxide makes the mol ratio of its add-on and waste iron filing, under the condition of mechanical stirring intensity 600r/min, reacts 45min; Carry out filtration washing; The filter residue of gained adds an amount of 4.2mol/L sulfuric acid and leaches reaction 60min at normal temperatures, and solution filters and obtains ferrum sulfuricum oxydatum solutum, can obtain qualified polyaluminum sulfate iron product through underpressure distillation again.

Claims (8)

1. a waste iron filing reducing pyrolusite prepares electrolytic manganese metal solution and reclaims the technology of iron, it is characterized in that, may further comprise the steps:
(1) pyrolusite is dropped in the reaction kettle, the anolyte that produces when adding zero(ppm) water or electrolytic manganese, the weight proportion of the anolyte that produces when pyrolusite and zero(ppm) water or electrolytic manganese is 1:5.0 ~ 15.0;
(2) under mechanical stirring, add the vitriol oil and ammonium sulfate in the reaction kettle, make that sulfuric acid concentration reaches 100-200g/L in the mixed solution, ammonium sulfate concentrations reaches 100 ~ 200g/L;
(3) add waste iron filing, leach reaction 0.5 ~ 1h in 25 ~ 60 ℃ of following mechanical stirring of temperature, reaction 1-2h is leached in elevated temperature to 70 ~ 100 a ℃ continuation, impels material reaction complete;
(4) water-ground limestone of adding pyrolusite weight 10% ~ 25%, after reacting completely, using concentration again is pH value to 6.3 ~ 6.7 of 20% ~ 28% ammoniacal liquor regulator solution;
(5) 0.2% ~ 1.5% of adding pyrolusite weight Sodium dimethyldithiocarbamate 40min, reaction 0.5 ~ 1h, removal of impurities removing heavy metals ion filters cooling, adds tin anhydride in the filtrating, obtains directly being used for the manganese sulfate solution of electrolytic manganese;
After gained filter residue and zero(ppm) water mix after filtering in the described step (5); Under 50 ~ 90 ℃ of temperature of reaction, add quicklime or calcium hydroxide or both mixtures, mechanical stirring reaction 0.5 ~ 1.5h; Filtration washing; The filter residue of gained adds dilute sulphuric acid and leaches reaction 0.5 ~ 1h at normal temperatures, filters and obtains ferrum sulfuricum oxydatum solutum, obtains bodied ferric sulfate through underpressure distillation.
2. a kind of waste iron filing reducing pyrolusite according to claim 1 prepares electrolytic manganese metal solution and reclaims the technology of iron, it is characterized in that, in the step (2), the mol ratio of Manganse Dioxide is 1.2 ~ 2.8:1 in the vitriol oil of adding and the pyrolusite.
3. prepare electrolytic manganese metal solution according to the said a kind of waste iron filing reducing pyrolusite of claim 1 and reclaim the technology of iron, it is characterized in that in the step (2), churned mechanically speed is 800 ~ 2500r/min.
4. a kind of waste iron filing reducing pyrolusite according to claim 1 prepares electrolytic manganese metal solution and reclaims the technology of iron, it is characterized in that, in the step (3), the mol ratio of Manganse Dioxide is 0.5 ~ 1.5: 1 in the waste iron filing of adding and the pyrolusite.
5. a kind of waste iron filing reducing pyrolusite according to claim 1 prepares electrolytic manganese metal solution and reclaims the technology of iron, it is characterized in that the concentration of the tin anhydride of adding is 0.02 ~ 0.08g/L.
6. a kind of waste iron filing reducing pyrolusite according to claim 1 prepares electrolytic manganese metal solution and reclaims the technology of iron, it is characterized in that the mol ratio of quicklime or calcium hydroxide or both mixtures and waste iron filing is (0.5 ~ 2.5): 1.
7. a kind of waste iron filing reducing pyrolusite according to claim 1 prepares electrolytic manganese metal solution and reclaims the technology of iron, it is characterized in that, the said churned mechanically speed of step (5) is 400 ~ 1000r/min.
8. a kind of waste iron filing reducing pyrolusite according to claim 1 prepares electrolytic manganese metal solution and reclaims the technology of iron, it is characterized in that the concentration of dilute sulphuric acid is 1.0 ~ 4.5mol/L.
CN201010535033A 2010-11-09 2010-11-09 New technology for preparing electrolytic manganese metal solution and recycling iron by reducing pyrolusite with iron scraps Expired - Fee Related CN101988154B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201010535033A CN101988154B (en) 2010-11-09 2010-11-09 New technology for preparing electrolytic manganese metal solution and recycling iron by reducing pyrolusite with iron scraps

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201010535033A CN101988154B (en) 2010-11-09 2010-11-09 New technology for preparing electrolytic manganese metal solution and recycling iron by reducing pyrolusite with iron scraps

Publications (2)

Publication Number Publication Date
CN101988154A CN101988154A (en) 2011-03-23
CN101988154B true CN101988154B (en) 2012-09-26

Family

ID=43744945

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201010535033A Expired - Fee Related CN101988154B (en) 2010-11-09 2010-11-09 New technology for preparing electrolytic manganese metal solution and recycling iron by reducing pyrolusite with iron scraps

Country Status (1)

Country Link
CN (1) CN101988154B (en)

Families Citing this family (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102605188A (en) * 2011-10-10 2012-07-25 云南建水锰矿有限责任公司 Method for producing manganese sulfate by manganese alloy slag through pressure leaching
CN103469247A (en) * 2013-09-04 2013-12-25 宁夏天元锰业有限公司 Method for reducing ammonia consumption in production of electrolytic manganese metal
CN103469246A (en) * 2013-09-04 2013-12-25 宁夏天元锰业有限公司 Iron removal method in production of manganese metal through electrolysis
CN103451423A (en) * 2013-09-04 2013-12-18 宁夏天元锰业有限公司 Solution preparation method of electrolytic manganese metal
CN103540773A (en) * 2013-11-07 2014-01-29 广西桂柳化工有限责任公司 Method for preparing manganese sulfate by utilizing manganese oxide
CN103555959B (en) * 2013-11-07 2015-02-25 广西桂柳化工有限责任公司 Technology for comprehensively recycling leaching residue in production of electrolytic manganese metal and manganese dioxide
CN103937999B (en) * 2014-04-23 2015-09-23 北京科技大学 A kind of vacuum distilling ferromanganese extracts method and the device of manganese metal
CN104762466B (en) * 2015-04-17 2017-01-11 北京矿冶研究总院 Liquid preparation method for producing electrolytic manganese or manganese dioxide from low-grade manganese oxide ore
CN104862501B (en) * 2015-05-07 2017-01-18 张安良 Chemical clean beneficiation and accessory recycling process of lean manganese ore
CN105668641B (en) * 2016-03-04 2017-06-20 东北大学 A kind of method that sulfuric acid roasting direct pyrolusite prepares manganese sulfate solution

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1724697A (en) * 2004-07-19 2006-01-25 中南大学 Method of manufacturing electrolytic metal manganese using titanium white waste acid and manganese dioxide ore
CN101717956A (en) * 2009-12-21 2010-06-02 潘国武 Method for preparing electrolytic manganese metal electrolytic solution by pyrolusite water law

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1724697A (en) * 2004-07-19 2006-01-25 中南大学 Method of manufacturing electrolytic metal manganese using titanium white waste acid and manganese dioxide ore
CN101717956A (en) * 2009-12-21 2010-06-02 潘国武 Method for preparing electrolytic manganese metal electrolytic solution by pyrolusite water law

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
杜杰.某低品位软锰矿的化学浸出试验研究.《广西地质》.2002,第15卷(第1期),72-74. *
黄映恒.软锰矿直接浸取硫酸锰副产聚合硫酸铁的实验.《河池师专学报(理科)》.1995,第15卷(第2期),97-101. *

Also Published As

Publication number Publication date
CN101988154A (en) 2011-03-23

Similar Documents

Publication Publication Date Title
CN101988154B (en) New technology for preparing electrolytic manganese metal solution and recycling iron by reducing pyrolusite with iron scraps
CN102070198B (en) Method for preparing high-purity manganese sulfate and high-purity manganese carbonate by reduction leaching of pyrolusite through scrap iron
CN101812593B (en) Method for depositing vanadium wastewater by utilizing vanadium-extraction tailings and acid ammonium salt
CN104099474B (en) A kind of electroplating sludge recycles technique
CN104152687B (en) Aluminium, vanadium, molybdenum, the production technology of nickel element three-waste free discharge are extracted from black shale
CN101899582A (en) Method for extracting vanadium pentoxide from vanadium slag
CN102206755A (en) Method for separating and recovering valuable elements from neodymium-iron-boron wastes
CN102094119A (en) Method for preparing electrolytic manganese metal with low-grade pyrolusite wet leaching
CN102011010A (en) Method for totally extracting vanadium, gallium and scandium by using titanium dioxide hydrolysis waste acid to leach steel slag containing vanadium
CN105274344A (en) Method for recycling vanadium and molybdenum from waste petroleum catalyst
CN108754148B (en) Treatment method for recycling heavy metal waste residues containing copper, manganese, cobalt, zinc and nickel
CN101265524A (en) Method for extracting V2O5 from stone coal
CN102925686A (en) Method for selectively separating and extracting vanadium and chromium from solution containing vanadium and chromium
CN101956070A (en) Recovery method of molybdenum concentrates
CN104017999A (en) Vanadium extraction method for converter vanadium slag
CN101988153B (en) Novel process for efficiently and fast removing iron in manganese ore wet process reduction method
CN112553478A (en) Method for quickly leaching nickel hydroxide cobalt sulfuric acid system
CN104032131A (en) Method for processing high-tin anode slurry
CN113512652B (en) Method for extracting gallium metal from coal-series solid waste
CN113880149A (en) Process for preparing high-purity nickel sulfate by using ammonium salt-containing rough nickel sulfate as main raw material in copper electrolysis plant
CN105671324A (en) Method for preparing ammonium rhenate from rhenium-enriched slags
CN103553132B (en) Method for preparing ammonium tetramolybdate by treating molybdenum-rich wastewater and waste slag
CN111100996B (en) Method for preparing vanadium oxide from acidic low-concentration vanadium liquid
CN101134566B (en) Process for preparing amino-sulfonic acid nickel by nickel sulfide concentrate
CN110747343B (en) Method for preparing cobalt oxide from zinc smelting cobalt slag

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20120926

Termination date: 20161109