CN106337139A - Method for recovering germanium from germanium-containing material - Google Patents

Method for recovering germanium from germanium-containing material Download PDF

Info

Publication number
CN106337139A
CN106337139A CN201610715681.9A CN201610715681A CN106337139A CN 106337139 A CN106337139 A CN 106337139A CN 201610715681 A CN201610715681 A CN 201610715681A CN 106337139 A CN106337139 A CN 106337139A
Authority
CN
China
Prior art keywords
germanium
resin
containing material
acid
germanic
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.)
Pending
Application number
CN201610715681.9A
Other languages
Chinese (zh)
Inventor
王朋
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.)
Individual
Original Assignee
Individual
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 Individual filed Critical Individual
Priority to CN201610715681.9A priority Critical patent/CN106337139A/en
Publication of CN106337139A publication Critical patent/CN106337139A/en
Priority to CN201710234873.2A priority patent/CN107010655B/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01GCOMPOUNDS CONTAINING METALS NOT COVERED BY SUBCLASSES C01D OR C01F
    • C01G17/00Compounds of germanium
    • C01G17/02Germanium dioxide
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B41/00Obtaining germanium
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B33/00Silicon; Compounds thereof
    • C01B33/20Silicates
    • C01B33/32Alkali metal silicates
    • 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
    • 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)
  • Organic Chemistry (AREA)
  • Engineering & Computer Science (AREA)
  • Metallurgy (AREA)
  • Manufacturing & Machinery (AREA)
  • Materials Engineering (AREA)
  • Mechanical Engineering (AREA)
  • Inorganic Chemistry (AREA)
  • Geology (AREA)
  • General Life Sciences & Earth Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • Silicon Compounds (AREA)
  • Treatment Of Water By Ion Exchange (AREA)

Abstract

The invention discloses a method for recovering germanium from a germanium-containing material. According to the method, a resin adsorption principle is adopted in the germanium separation process so as to thoroughly adsorb germanium into resin and let silicon enter a solvent in the form of sodium silicate. Therefore, germanium is separated thoroughly, recovery rate of germanium reaches about 95%, and the problem that lots of germanium is brought into silica precipitate in the silicon precipitation process of electrolyte produced by the electrolyte separation method of germanium is avoided. After resin adsorption, part of water is evaporated from a sodium silicate solution and then the product can be used as a soluble glass product for sale. Thus, sewage treatment problem is avoided, and production cost is reduced. Defects of a hydrofluoric acid method for processing a germanium-containing material, such as high production cost, severe equipment corrosion and environmental pollution, are eliminated; and the problem of low recovery rate in an alkali dissolution precipitation method is avoided. By the method of the invention, equipment corrosion, environmental pollution and other problems are not caused in the germanium-containing waste material dissolving process.

Description

A kind of method of germanium in recovery germanium-containing material
Technical field
The present invention relates to technical field of wet metallurgy and in particular to a kind of recovery contain germanium waste material in germanium method.
Background technology
Germanium is a kind of dissipated metal, and nature reserves are less, the copper mine in brown coal, Pb-Zn deposits and South Africa for the main association it In.8600 tons of the explored germanium reserves in the whole world, by the consumption calculating only enough more than 40 years of current germanium;Germanium is a kind of important Strategic resource, suffer from replacing in high-technology fields such as Aero-Space, fiber optic communication, infrared optics, new energy technologies The application in generation, with the development of China's new and high technology, the continuous upgrading of the industrial structure, the level of consumption of germanium will keep increasing at a high speed Long.
The raw materials for production of germanium include two aspects at present, and one is the side-product extraction germanium from Pb-Zn deposits and colliery, such raw material The technological process of production long, alternately, the response rate is low for pyrogenic process wet method, high cost.Two is to produce from the course of processing of germanium Containing extracting germanium in germanium waste material, such germanium-containing raw material is that germanium reclaims important regenerated resources, extracts germanium tool from such germanium-containing raw material There are preferable economic benefit and social meaning, belong to country and support that resource reclaim recycles industry.
When germanium is used for producing optical fiber and glasses for infrared use, produce substantial amounts of germanium-containing material, at silicon and germanium in germanium-containing material Same main group in the periodic table of chemical element, chemical property is similar with physical property, and the separation of the two is always an industry difficult problem. Conventional method includes (1) and distills oxidizer direct chlorination after germanium-containing material pulverizing, and this technique can hardly be by raw material Germanium extracts.(2) germanium-containing material is carried out after oxidizing roasting chlorinated distillation again, the parcel problem due to silicon dioxide makes The response rate of germanium is relatively low, and secondly silicon dioxide forms silica gel in acid medium and makes filtration difficulty.(3) by germanium-containing material pulverizing After carry out high temperature alkali dissolution, obtain sodium silicate and germanic acid sodium solution, add electrolyte and adjust ph value and carry out sinking silicon and heavy germanium operation, Though this technique can be effectively by germanic separation, the heavy silicon time is long, has a large amount of germanium also with silicon coprecipitation, make during heavy silicon The response rate obtaining germanium is less than 75%, does not make full use of germanium resource.(4) hydrofluoric acid dissolution, tannin are used by after germanium-containing material pulverizing Heavy germanium, this technique productions high cost is serious to equipment corrosion, because the presence of fluorion is to environment.To sum up several Conventional treatment germanium-containing material technique, have such problems as that the response rate is low, production cost is high, equipment corrosion, environmental pollution.
Substantial amounts of acid slag is produced, germanic amount is in 0.2%~1% acid slag during the production process chlorinated distillation of germanium Although germanic taste is high, also contain substantial amounts of chloride and silicon dioxide so that germanium is wrapped in silicate simultaneously, even if Obtain germanium in these slags under acid condition also will not be dissolved in solution.Each smeltery is all using pyrogenic attack acid slag at present, But during pyrogenic attack acid slag, the volatilization temperature of germanium is higher than 1100 DEG C, produces a large amount of poison gas, company's environmental protection is produced very big Pressure, and serious to equipment corrosion, and production cost is high.
Content of the invention
In order to solve above-mentioned technical barrier, improve the direct yield of germanium and reduce production cost, the invention provides a kind of return Receive the high method containing germanium in germanium waste material.
What the present invention provided reclaims the high method containing germanium in germanium waste material, specifically comprises the following steps that
1) germanic waste material is pulverized and be milled to 80 mesh~300 mesh, be added in sodium hydroxide solution, be heated to 120 DEG C ~250 DEG C of insulation reaction 2~3 hours, are cooled to room temperature, obtain the alkaline solution of sodium silicate and sodium germanate;
2) by step 1) alkaline solution of the sodium silicate that obtains and sodium germanate adds equipped with the tank of resin, obtains containing germanium The resin of acid ion and the alkaline solution of sodium silicate;
3) the diluted acid resin containing germanic acid radical ion for the addition is carried out the parsing of germanium, obtain germanic acid solution and parsing Resin afterwards, in case the absorption of germanium next time after resin washes with water, cleaning mixture is incorporated to germanic desorbed solution, germanic to gained Add iron salt to carry out the enrichment procedure of germanium in acid solution, adjusting its ph value is 7~8, then carries out filter operation, obtain germanium essence Ore deposit;
4) by step 3) germanium concentrate that obtains carries out chlorinated distillation, and obtain germanium tetrachloride, germanium tetrachloride hydrolysis is obtained two Germanium oxide.
Step 1) described in include the production process chlorinated distillation of germanium containing germanium waste material during the acid slag that produces and germanium use The germanium-containing material producing when production optical fiber and glasses for infrared use.
Described sodium hydroxide and described germanium are used for producing the quality of the germanium-containing material producing when optical fiber and glasses for infrared use It is 3~5:1 than the mass ratio of the acid slag for producing during 1.5~2.5:1, with the production process chlorinated distillation of described germanium.
Step 2) described in resin be alkalescence epoxy type anion exchange resin or styrene series anion exchange resin, Resin is 2~3:1 with the mass ratio containing germanium in germanium waste material, and including d301 alkalescence epoxy type anion exchange resin, d201 is weak Alkaline epoxy type anion exchange resin and 201 × 7mb weakly basic styrene type anion exchange resin.
Step 3) described in diluted acid be dilute sulfuric acid or dilute hydrochloric acid, concentration range be 0.5mol/l~1mol/l, described iron salt For ferrum oxide, the mass ratio of the germanium in ferrum oxide and germanium-containing solution is 1~4:1.
The present invention also provides a kind of preparation method of waterglass: is used for produce optical fiber and infrared containing germanium waste material for germanium when described The germanium-containing material producing during optical glass, by step 2) obtain sodium silicate alkaline solution heating evaporation remove account for solution gross mass 10%~30% moisture content, can obtain waterglass, when described containing germanium waste material for the production process chlorinated distillation of germanium during produce In the alkaline solution of produced sodium silicate during acid slag, silicic acid sodium content is too low to for producing waterglass.
The present invention adopt in germanic separation process resin absorption principle by germanium thoroughly absorption in resin silicon then with silicon Sour sodium enters in solution, so that germanic separation is thoroughly so that the response rate of germanium reaches 95%, it is to avoid electrolyte separates and contains A large amount of germanium are had to be brought to the problem in the precipitation of silicon dioxide during the heavy silicon of electrolyte that germanium method produces.After resin absorption Sodium silicate solution can sell as waterglass product after evaporating part water, it is to avoid sewage handling problem, reduce production Cost.Sodium germanate parses through resin, and trivalent iron salt absorbing process can get the germanium concentrate that mass fraction is 10%~15%.
The production cost that hydrogen fluoride process germanium-containing material generation has been abandoned in this technology invention is high, equipment corrosion is serious, ring The shortcoming of border pollution, it is to avoid the alkali soluble sedimentation method process the low problem of the response rate producing containing germanium waste material, are dissolving containing germanium waste material During do not cause the problems such as equipment corrosion, environmental pollution.
Specific embodiment
With reference to specific embodiment, the invention will be further described, so that those skilled in the art can be more preferable Understand the present invention and can be practiced, but illustrated embodiment is not as a limitation of the invention.
Embodiment 1
Weigh 200kg germanium for producing the germanium-containing material producing when optical fiber and glasses for infrared use, Ge content is 0.6%, Obtain the germanic silicon dioxide powder of 300 mesh after broken pulverizing, the sodium hydroxide that silicon dioxide powder addition mass concentration is 30% In solution, sodium hydroxide solution quality is 1000kg;With pump, reactant liquor is extracted in autoclave, is heated to 150 DEG C, insulation 3 hours, obtain the sodium silicate alkaline solution containing sodium germanate;It is 1m that solution is added volume3The d301 equipped with quality for 2.4kg In the tank of alkalescence epoxy type anion exchange resin, the sodium silicate solution obtaining is evaporated concentrating, evaporates mother solution matter The water of amount 15%, output water glass product;By excessively above-mentioned for the dilute sulfuric acid 100l for 0.5mol/l for the concentration tank equipped with resin, obtain Containing germanic solion;3kg ferrum oxide is added to containing in germanic solion, and adds sodium hydroxide to adjust ph It is worth to 8, stir a hour and filtered, after drying, obtain germanium concentrate 12kg;Germanium concentrate is carried out conventional chlorinating distillation, hydrolysis Technique obtains high-purity germanium dioxide 1.6kg, and the response rate of germanium is 95%.
Embodiment 2
Weigh 300kg germanium for producing the germanium-containing material producing when optical fiber and glasses for infrared use, Ge content is 0.8%, Obtain the germanic silicon dioxide powder of 200 mesh after broken pulverizing, the sodium hydroxide solution that silicon dioxide powder addition concentration is 30% In, sodium hydroxide solution quality is 1200kg;With pump, reactant liquor is extracted in autoclave, is heated to 180 DEG C, insulation 2 is little When, obtain the sodium silicate alkaline solution containing sodium germanate;By solution through volume be 1m3The d201 equipped with quality for 3.6kg weak In the tank of alkaline epoxy type anion exchange resin, the sodium silicate solution obtaining is evaporated concentrating, evaporates mother solution quality 25% water, output water glass product;By excessively above-mentioned for the dilute sulfuric acid 100l for 0.5mol/l for the concentration tank equipped with resin, contained There is germanic solion;3kg ferrum oxide is added to containing in germanic solion, and adds sodium hydroxide to adjust ph value To 7, stir a hour and filtered, after drying, obtain germanium concentrate 34kg;Germanium concentrate is carried out conventional chlorinating distillation, hydrolysis Technique obtains high-purity germanium dioxide 3.4kg, and the response rate of germanium is 97%.
Embodiment 3
Weigh 500kg germanium for producing the germanium-containing material producing when optical fiber and glasses for infrared use, Ge content is 0.4%, Obtain the germanic silicon dioxide powder of 200 mesh after broken pulverizing, the sodium hydroxide solution that silicon dioxide powder addition concentration is 30% In, sodium hydroxide solution quality is 1400kg;With pump, reactant liquor is extracted in autoclave, is heated to 120 DEG C, insulation 2 is little When, obtain the sodium silicate alkaline solution containing sodium germanate;By solution through volume be 1m3201 × 7mb equipped with quality for 3kg In the tank of weakly basic styrene type anion exchange resin, the sodium silicate solution obtaining is evaporated concentrating, evaporates mother solution The water of quality 30%, output water glass product;By excessively above-mentioned for the dilute sulfuric acid 100l for 0.5mol/l for the concentration tank equipped with resin, obtain To containing germanic solion;2.5kg ferrum oxide is added to containing in germanic solion, and adds sodium hydroxide to adjust Section ph value, to 8, stirs two hours and is filtered, obtain germanium concentrate 34kg after drying;By germanium concentrate carry out conventional chlorinating distillation, Hydrolysis process obtains high-purity germanium dioxide 2.6kg, and the response rate of germanium is 92%.
Embodiment 4
The acid slag producing during weighing the production process chlorinated distillation of 500kg germanium, Ge content is 0.8%, drying To 80 mesh after broken pulverizing, gained powder addition concentration is in 1% sodium hydroxide solution, sodium hydroxide solution quality is 1200kg;With pump, reactant liquor is extracted in autoclave, is heated to 130 DEG C, be incubated 2.5 hours, obtain the silicon containing sodium germanate Sour sodium alkaline solution;By solution through volume be 1m3Equipped with 201 × 7mb weakly basic styrene type anion exchange resin's In tank, the sodium silicate solution obtaining acid adding is carried out acid-base neutralization process;The dilute sulfuric acid 120l for 0.5mol/l for the concentration is gone up excessively State the tank equipped with resin, obtain containing germanic solion;15kg ferrum oxide is added to containing germanic solion In, and add sodium hydroxide to adjust ph value to 8, stir two hours and filtered, after drying, obtain germanium concentrate 40kg;By germanium essence Ore deposit carries out conventional chlorinating distillation, hydrolysis process obtains high-purity germanium dioxide 5.5kg, and the response rate of germanium is 95%.
Embodiment 5
The acid slag producing during weighing the production process chlorinated distillation of 400kg germanium, Ge content is 0.5%, through broken To 100 mesh after pulverizing, gained powder addition concentration is in 1% sodium hydroxide solution, sodium hydroxide solution quality is 800kg;With pump, reactant liquor is extracted in autoclave, is heated to 140 DEG C, be incubated 3 hours, obtain the sodium silicate containing sodium germanate Alkaline solution;By solution through volume be 1m3The tank equipped with 201 × 7mb weakly basic styrene type anion exchange resin in, The sodium silicate solution obtaining acid adding is carried out acid-base neutralization process;By excessively above-mentioned for the dilute sulfuric acid 100l for 0.5mol/l for the concentration equipped with The tank of resin, obtains containing germanic solion;6kg ferrum oxide is added to containing in germanic solion, and adds Sodium hydroxide adjusts ph value to 8, stirs two hours and is filtered, obtains germanium concentrate 13kg after drying;Germanium concentrate is carried out often Rule chlorinated distillation, hydrolysis process obtain high-purity germanium dioxide 2.8kg, and the response rate of germanium is 96%.
Ultimate principle, principal character and the advantages of the present invention of the present invention have been shown and described above.The technology of the industry , it should be appreciated that the present invention is not restricted to the described embodiments, the simply explanation described in above-described embodiment and description is originally for personnel Invention principle, without departing from the spirit and scope of the present invention the present invention also have various changes and modifications, these change Change and improvement both falls within scope of the claimed invention.

Claims (7)

1. a kind of method reclaiming germanium in germanium-containing material is it is characterised in that specifically comprise the following steps that
1) germanic waste material is pulverized and be milled to 80 mesh~300 mesh, be added in sodium hydroxide solution, be heated to 120 DEG C~250 DEG C insulation reaction 2~3 hours, is cooled to room temperature, obtains the alkaline solution of sodium silicate and sodium germanate;
2) by step 1) alkaline solution of the sodium silicate that obtains and sodium germanate adds equipped with the tank of resin, obtaining containing germanic acid root The resin of ion and the alkaline solution of sodium silicate;
3) the diluted acid resin containing germanic acid radical ion for the addition is carried out the parsing of germanium, after obtaining germanic acid solution and parsing Resin, in case the absorption of germanium next time after resin washes with water, cleaning mixture is incorporated to germanic desorbed solution, to the germanic acidity of gained Iron salt is added to carry out the enrichment procedure of germanium in solution, adjusting its ph value is 7~8, then carries out filter operation, obtains germanium concentrate;
4) by step 3) germanium concentrate that obtains carries out chlorinated distillation, and obtain germanium tetrachloride, germanium tetrachloride hydrolysis is obtained titanium dioxide Germanium.
2. the method reclaiming germanium in germanium-containing material according to claim 1 is it is characterised in that step 1) described in germanic useless When the acid slag producing during expecting to include the production process chlorinated distillation of germanium and germanium are used for producing optical fiber and glasses for infrared use The germanium-containing material producing.
3. according to claim 2 reclaim germanium-containing material in germanium method it is characterised in that described sodium hydroxide with described The mass ratio that germanium is used for producing the germanium-containing material producing when optical fiber and glasses for infrared use is 1.5~2.5:1, the life with described germanium The mass ratio of the acid slag producing during producing operation chlorinated distillation is 3~5:1.
4. the method reclaiming germanium in germanium-containing material according to claim 1 is it is characterised in that step 2) described in resin be Alkalescence epoxy type anion exchange resin or styrene series anion exchange resin, resin and the mass ratio containing germanium in germanium waste material For 2~3:1.
5. the method reclaiming germanium in germanium-containing material according to claim 4 is it is characterised in that include d301 alkalescence epoxy Series anion exchange resin, d201 alkalescence epoxy type anion exchange resin and 201 × 7mb alkalescence styrene series anion Exchanger resin.
6. the method reclaiming germanium in germanium-containing material according to claim 1 is it is characterised in that step 3) described in diluted acid be Dilute sulfuric acid or dilute hydrochloric acid, concentration range is 0.5mol/l~1mol/l, and described iron salt is ferrum oxide, in ferrum oxide and germanium-containing solution Germanium mass ratio be 1~4:1.
7. a kind of preparation method of waterglass it is characterised in that include claim 1 step 1) and step 2), wherein said It is used for producing the germanium-containing material producing when optical fiber and glasses for infrared use, now, step 2 for germanium containing germanium waste material) also obtain silicic acid The alkaline solution of sodium, the alkaline solution heating evaporation of the sodium silicate obtaining is removed the water accounting for solution gross mass 10%~30% Part, obtain waterglass.
CN201610715681.9A 2016-08-23 2016-08-23 Method for recovering germanium from germanium-containing material Pending CN106337139A (en)

Priority Applications (2)

Application Number Priority Date Filing Date Title
CN201610715681.9A CN106337139A (en) 2016-08-23 2016-08-23 Method for recovering germanium from germanium-containing material
CN201710234873.2A CN107010655B (en) 2016-08-23 2017-04-12 Method for recovering germanium from germanium-containing material

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201610715681.9A CN106337139A (en) 2016-08-23 2016-08-23 Method for recovering germanium from germanium-containing material

Publications (1)

Publication Number Publication Date
CN106337139A true CN106337139A (en) 2017-01-18

Family

ID=57825277

Family Applications (2)

Application Number Title Priority Date Filing Date
CN201610715681.9A Pending CN106337139A (en) 2016-08-23 2016-08-23 Method for recovering germanium from germanium-containing material
CN201710234873.2A Active CN107010655B (en) 2016-08-23 2017-04-12 Method for recovering germanium from germanium-containing material

Family Applications After (1)

Application Number Title Priority Date Filing Date
CN201710234873.2A Active CN107010655B (en) 2016-08-23 2017-04-12 Method for recovering germanium from germanium-containing material

Country Status (1)

Country Link
CN (2) CN106337139A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111118293A (en) * 2020-01-14 2020-05-08 华中科技大学 Method for recovering germanium from germanium-containing solution and application thereof
CN111647760A (en) * 2020-06-16 2020-09-11 中南大学 Method for selectively recovering germanium, bismuth and silicon from bismuth-doped silica optical fiber
CN112593083A (en) * 2020-11-26 2021-04-02 胡冲丽 Process for recovering germanium from germanium-containing luminescent glass microcrystalline material
CN116555596A (en) * 2023-03-31 2023-08-08 云南驰宏国际锗业有限公司 Method for comprehensively recovering germanium from germanium tetrachloride hydrolysis mother solution and washing water

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN115504502B (en) * 2022-06-17 2023-11-03 灵宝市民生高新材料有限公司 Method for recycling and preparing high-purity germanium dioxide from abandoned germanium-containing glass

Family Cites Families (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1552923A (en) * 2003-06-03 2004-12-08 贵州工业大学 Method for enrichment recovering germanium from acid solution
CN102618721A (en) * 2012-02-24 2012-08-01 云南五鑫实业有限公司 Method for extracting germanium, indium and zinc from high iron, silicon and manganese materials containing germanium, indium and zinc
CN103388086B (en) * 2012-05-09 2014-12-10 深圳市格林美高新技术股份有限公司 Method for extracting germanium from germanium-containing abandoned element
CN104357688B (en) * 2014-11-19 2016-06-22 辽宁大学 The method of Levextrel Resin separating Ge

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111118293A (en) * 2020-01-14 2020-05-08 华中科技大学 Method for recovering germanium from germanium-containing solution and application thereof
CN111118293B (en) * 2020-01-14 2021-01-22 华中科技大学 Method for recovering germanium from germanium-containing solution and application thereof
CN111647760A (en) * 2020-06-16 2020-09-11 中南大学 Method for selectively recovering germanium, bismuth and silicon from bismuth-doped silica optical fiber
CN111647760B (en) * 2020-06-16 2021-03-23 中南大学 Method for selectively recovering germanium, bismuth and silicon from bismuth-doped silica optical fiber
CN112593083A (en) * 2020-11-26 2021-04-02 胡冲丽 Process for recovering germanium from germanium-containing luminescent glass microcrystalline material
CN116555596A (en) * 2023-03-31 2023-08-08 云南驰宏国际锗业有限公司 Method for comprehensively recovering germanium from germanium tetrachloride hydrolysis mother solution and washing water

Also Published As

Publication number Publication date
CN107010655A (en) 2017-08-04
CN107010655B (en) 2020-06-05

Similar Documents

Publication Publication Date Title
CN106337139A (en) Method for recovering germanium from germanium-containing material
Xing et al. Rubidium extraction from mineral and brine resources: A review
CN106185989B (en) A kind of method that inorganic salts are reclaimed in domestic garbage incineration flyash
CN102212697B (en) Tungsten slag treatment method
CN111233003A (en) Acid-base combined process for completely realizing resource utilization of high-fluorine secondary aluminum ash
CN104030332B (en) A kind of method reclaiming sodium aluminum fluoride from pesticide industry fluorine-containing waste residue
CN107217156A (en) The method that rubidium cesium salt is extracted from spodumene lithium liquor
CN114105171A (en) Method for recycling and comprehensively utilizing lepidolite and lithium hydroxide prepared by method
CN113955775B (en) Method for extracting lithium carbonate from lithium-rich clay by acid-base combined method
CN106086481B (en) A method of germanium in the germanic waste liquid of recycling
CN105369042A (en) Method for efficiently extracting rare earths from fluoride system rare earth molten salt electrolysis slag
CN117327923B (en) Method for jointly extracting lithium from waste aluminum electrolyte and overhaul slag
CN104060095A (en) Method of recovering palladium from palladium-loading aluminum oxide waste catalyst
CN109055737A (en) A kind of method of sulfuric acid leaching lepidolite ore
CN103014334B (en) Method for replacement dissolution of bastnaesite (bastnasite)
CN108516569B (en) Method for preparing lithium sulfate solution by roasting lepidolite
CN102345017A (en) Method for recovering germanium from germanium oxide dust by carrying out alkali fusion under condition of microwave heating
CN203284447U (en) System used for recovering lithium, rubidium and / or cesium from lepidolite ore
CN115403061A (en) High-purity calcium chloride and concentration method thereof
CN103451452A (en) Method for recovering tin from tin-containing waste liquid
CN106319229A (en) Method for recovering silver from silver particles in silver production waste liquid
CN107354323A (en) A kind of method of separation and Extraction rubidium, caesium from coal
CN102321803B (en) Method for removing chloride ion from waste molasses for manganese dioxide reduction
CN107827149B (en) A kind of production method of the sodium stannate of low leaded antimony arsenic iron tramp
Han et al. Recycling of lithium and fluoride from LiF wastewater from LiF synthesis industry by solvent extraction

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
WD01 Invention patent application deemed withdrawn after publication
WD01 Invention patent application deemed withdrawn after publication

Application publication date: 20170118