NO164665B - PROCEDURE FOR RECOVERING ALUMINUM FROM WASTE MATERIAL. - Google Patents

PROCEDURE FOR RECOVERING ALUMINUM FROM WASTE MATERIAL. Download PDF

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Publication number
NO164665B
NO164665B NO852281A NO852281A NO164665B NO 164665 B NO164665 B NO 164665B NO 852281 A NO852281 A NO 852281A NO 852281 A NO852281 A NO 852281A NO 164665 B NO164665 B NO 164665B
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aluminum
sulfuric acid
scrap
solution
precipitation
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NO852281A
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Norwegian (no)
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NO852281L (en
NO164665C (en
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Ernst Haberfellner
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Austria Metall
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Publication of NO852281L publication Critical patent/NO852281L/en
Publication of NO164665B publication Critical patent/NO164665B/en
Publication of NO164665C publication Critical patent/NO164665C/en

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    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01FCOMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
    • C01F5/00Compounds of magnesium
    • C01F5/40Magnesium sulfates
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01FCOMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
    • C01F7/00Compounds of aluminium
    • C01F7/02Aluminium oxide; Aluminium hydroxide; Aluminates
    • C01F7/20Preparation of aluminium oxide or hydroxide from aluminous ores using acids or salts
    • C01F7/26Preparation of aluminium oxide or hydroxide from aluminous ores using acids or salts with sulfuric acids or sulfates
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B21/00Obtaining aluminium
    • C22B21/0015Obtaining aluminium by wet processes
    • C22B21/0023Obtaining aluminium by wet processes from waste materials
    • 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
    • C22B7/04Working-up slag
    • CCHEMISTRY; METALLURGY
    • C25ELECTROLYTIC OR ELECTROPHORETIC PROCESSES; APPARATUS THEREFOR
    • C25CPROCESSES FOR THE ELECTROLYTIC PRODUCTION, RECOVERY OR REFINING OF METALS; APPARATUS THEREFOR
    • C25C3/00Electrolytic production, recovery or refining of metals by electrolysis of melts
    • C25C3/06Electrolytic production, recovery or refining of metals by electrolysis of melts of aluminium
    • 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

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Engineering & Computer Science (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Metallurgy (AREA)
  • Geology (AREA)
  • Materials Engineering (AREA)
  • Manufacturing & Machinery (AREA)
  • Inorganic Chemistry (AREA)
  • General Life Sciences & Earth Sciences (AREA)
  • Mechanical Engineering (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Electrochemistry (AREA)
  • Geochemistry & Mineralogy (AREA)
  • Environmental & Geological Engineering (AREA)
  • Manufacture And Refinement Of Metals (AREA)
  • Compounds Of Alkaline-Earth Elements, Aluminum Or Rare-Earth Metals (AREA)

Abstract

En fremgangsmåte for gjenvinning av aluminium fra aluminiumskrap og annet aluminiumhydroksydholdig avfall, særlig metallfattig avfallsstøv, qår ut på at fornyet innføring i elektrolysecellen gjøres mulig ved varmtvannutvaskina og etter-følgende surppslemning. I tillegg gjenvinnes ved saltut-felling (gjenværende rest av Al-utsmeltingen) fra filtratet av varmtvannsutvaskingen atter omsmeltesaltene ved krystallisering. Det oppløste aluminium ved svovelsyreoppslemningen gjenvinnes ved utfelling under tilsats av natronlut, og til-føres elektrolysecellen etter tørking og kalsinering.A method for recovering aluminum from aluminum scrap and other aluminum hydroxide-containing waste, in particular metal-poor waste dust, means that re-introduction into the electrolysis cell is made possible by the hot water washing machine and subsequent slurry slurrying. In addition, upon salt precipitation (remaining residue of the Al melt), the remelting salts are recovered again by crystallization from the hot water leaching by crystallization. The dissolved aluminum in the sulfuric acid slurry is recovered by precipitation with the addition of sodium hydroxide solution, and is fed to the electrolytic cell after drying and calcination.

Description

Foreliggende oppfinnelse angår en fremgangsmåte for kjemisk gjenvinning av aluminiumskrappulver ved innføring på nytt i en elektrolysecelle. The present invention relates to a method for the chemical recovery of aluminum scrap powder by reintroducing it into an electrolysis cell.

Vanligvis blir forekommende aluminiumskrap etter behandling i møller oppdelt i en grovkornet fraksjon, som har en høy aluminiumandel, samt metallfattig men oksydrik skrappulver. Den fraksjon som er rik på metallisk aluminium blandes med salter i smelteovner for utsmeltning av aluminiumet. Skrappulveret, som fremdeles inneholder betraktelige andeler av metallisk aluminium og aluminiumoksyd, kan imidlertid på grunn av sitt store innhold av forurensende substanser ikke tilføres elektrolysecellen uten kjemisk behandling. Generally, aluminum scrap that occurs after processing in mills is divided into a coarse-grained fraction, which has a high proportion of aluminium, as well as metal-poor but oxide-rich scrap powder. The fraction that is rich in metallic aluminum is mixed with salts in smelting furnaces to melt out the aluminum. The scrap powder, which still contains considerable proportions of metallic aluminum and aluminum oxide, however, due to its high content of polluting substances, cannot be supplied to the electrolysis cell without chemical treatment.

Det er kjent at karbider, nitrider og klorider kan fjernes ved behandling med varmt vann, hvorved karbider og nitrider under avspalting av metan eller ammoniakkgass går over i aluminiumhydroksyd. Kloridene av smeltesalttilsatsene oppløses og kan ved gjentatt inndampning og krystallisering tilbakeføres til smelteprosessen. Hittil frembragt skrapstøv inneholder imidlertid fremdeles, alt etter sin opprinnelse, magnesium i overveiende grad som oksyd, og som ville forstyrre smelteelektrolyseprosessen, særlig etterhvert som smeltens densitet øker, således at aluminium ikke lenger avsettes. Videre vil magnesium også delvis utskilles katodisk. It is known that carbides, nitrides and chlorides can be removed by treatment with hot water, whereby carbides and nitrides during the splitting off of methane or ammonia gas turn into aluminum hydroxide. The chlorides from the molten salt additives dissolve and can be returned to the smelting process by repeated evaporation and crystallization. However, scrap dust produced so far still contains, depending on its origin, magnesium predominantly as oxide, which would disturb the melt electrolysis process, especially as the density of the melt increases, so that aluminum is no longer deposited. Furthermore, magnesium will also be partially excreted cathodically.

Det er derfor et formål for oppfinnelsen å angi en fremgangsmåte av innledningsvis angitt art og hvorved de ovenfor omtalte ulemper kan overvinnes. It is therefore an object of the invention to specify a method of the kind indicated at the outset and by which the disadvantages mentioned above can be overcome.

Oppfinnelsen gjelder således fremgangsmåte for gjenvinning av aluminium fra skrap og annet aluminiumholdig avfall, hvor skrapet etter en nedbrytning til mindre bestanddeler, særlig oppmaling, deles opp i en grovfraksjon som fremdeles inneholder meget rent metall og som innsmeltes i saltbad i en smelteovn, og en finfraksjon som overveiende inneholder oksyd. The invention thus relates to a method for recycling aluminum from scrap and other aluminum-containing waste, where the scrap, after breaking it down into smaller components, in particular grinding, is divided into a coarse fraction which still contains very pure metal and which is melted in a salt bath in a smelting furnace, and a fine fraction which predominantly contains oxide.

Fremgangsmåtens særtrekk i henhold til oppfinnelsen ligger da i at den saltrike rest fra smelteovnen for grovfraksjonen etter skylling med varmt vann på kjent måte og filtrering for å adskille lakeaktig saltløsning og sammen med den utfiltrerte finfraksjon, atter filtreres under oppslemning i fortynnede syrer, særlig svovelsyre, hvoretter filterkaken i tørket og oppmalt tilstand tilføres en elektrolysecelle og den dannede løsning av aluminiumsulfat med innhold av metallisk aluminium nøytraliseres med natriumlut, således at aluminium utfelles i form av aluminiumhydroksyd, som tørkes, kalsineres og atter innføres i smelteelektrolysecellen. The distinguishing feature of the method according to the invention then lies in the fact that the salty residue from the melting furnace for the coarse fraction, after rinsing with hot water in a known manner and filtering to separate the brine-like salt solution and together with the filtered out fine fraction, is again filtered under suspension in dilute acids, especially sulfuric acid, after which the filter cake in a dried and ground state is fed to an electrolysis cell and the formed solution of aluminum sulphate containing metallic aluminum is neutralized with sodium hydroxide solution, so that aluminum is precipitated in the form of aluminum hydroxide, which is dried, calcined and reintroduced into the melting electrolysis cell.

For fjerning av magnesiumforbindelser og andre oksyder, såvel som også forskjellige aluminiumsilikater, utføres således i henhold til oppfinnelsen behandling med fortynnet svovelsyre. Herunder oppløses også en del av det metalliske aluminium, som imidlertid ved den etterfølgende påkrevede nøytralisasjon av det svovelsure behandlingsvann, atter kan gjenvinnes som hydroksyd. Etter filtrasjon og skylling av det behandlede skrapstøv tilføres dette elektrolysecellen etter kalsinering. For the removal of magnesium compounds and other oxides, as well as various aluminum silicates, treatment with dilute sulfuric acid is thus carried out according to the invention. Part of the metallic aluminum also dissolves here, which, however, can be recovered as hydroxide in the subsequent required neutralization of the sulfuric acid treatment water. After filtration and rinsing of the treated scrap dust, this is fed to the electrolysis cell after calcination.

Svovelsyrebehandlingsvannet innstilles med fortynnet lut under omrøring på en pH-verdi på 6 - 7 for å oppnå en adskil-lelse av aluminium og magnesium på grunn av pH-avhengigheten, således at aluminiumsulfatet utfelles som hydroksyd, mens magnesiumsulfatet fremdeles forblir i løsningen. Etter filtrering, skylling og kalsinering tilføres aluminiumoksydet smelteelektrolyseprosessen. Ved siden av magnesiumoksydene og foreliggende metallisk magnesium fremkommer ved oppslem-ningen i svovelsyre også andre metalliske oksyder, slik som ZnO, Fe203, CuO og TiC>2 ^ delvis oppløsning. The sulfuric acid treatment water is adjusted with diluted lye while stirring to a pH value of 6 - 7 to achieve a separation of aluminum and magnesium due to the pH dependence, so that the aluminum sulfate is precipitated as hydroxide, while the magnesium sulfate still remains in the solution. After filtering, rinsing and calcining, the aluminum oxide is fed to the melt electrolysis process. In addition to the magnesium oxides and the metallic magnesium present, the suspension in sulfuric acid also produces other metallic oxides, such as ZnO, Fe2O3, CuO and TiC>2 ^ partial solution.

Fra skrapstøvet fjernes ikke eventuelt forekommende silisium-forbindelser, slik som kvarts, mulitt eller spinell. Any silicon compounds, such as quartz, mullite or spinel, are not removed from the scrap dust.

Eksempel på et prosessforløp i henhold til foreliggende oppfinnelse er angitt på vedlagte skjematiske tegning og omfatter følgende prosesstrinn: An example of a process sequence according to the present invention is indicated on the attached schematic drawing and includes the following process steps:

1. Den metallfattige siktfraksjon av partikkelstørrelse < 1,0 mm kommer sammen med de bearbeidede smelte- og saltrester fra ovnen 2 for grovfraksjonen til reaksjonsbeholderen 1. 2. Behandling med varmt vann ved ca. 96°C finner sted med omtrent 5 ganger skrapstøwolumet i to trinn, for derved å oppnå utfelling av karbider og nitrider samt oppløsning av saltene fra smelteovnen 2. 3. Filtrering gjennom vakuumfilter 3 til en saltlake-beholder 4 for gjenvinning av omsmeltesaltene ved inndampning og krystallisering. 4. Tilbakeføring av det utvaskede skrapstøv i reaksjonsbeholderen 1 og behandling med 10 %ig varm svovelsyre ved ca. 90°C (2 liter 10 %ig H2S04 til 1 kg skrapstøv). 5. Filtrering gjennom vakuumfilter 3 til en mellombeholder 1. The metal-poor sieve fraction of particle size < 1.0 mm comes together with the processed melt and salt residues from the furnace 2 for the coarse fraction to the reaction vessel 1. 2. Treatment with hot water at approx. 96°C takes place with approximately 5 times the scrap dust volume in two stages, thereby achieving precipitation of carbides and nitrides as well as dissolution of the salts from the melting furnace 2. 3. Filtration through vacuum filter 3 to a brine container 4 for recovery of the remelt salts by evaporation and crystallization. 4. Return of the washed scrap dust into the reaction container 1 and treatment with 10% hot sulfuric acid at approx. 90°C (2 liters of 10% H2S04 to 1 kg scrap dust). 5. Filtration through vacuum filter 3 into an intermediate container

6 samt avskylling inntil syrefrihet oppnås. 6 and rinsing until freedom from acid is achieved.

6. Tørking og kalsinering 7 av det behandlede skrapstøv ved 500°C. Delvis innføring i elektrolysecellen 8. 7. Tilbakeføring av det svovelsyrefiltrat fra mellom beholderen 6 til reaksjonsbeholderen 1. Langsom tilførsel av kald 10 %ig natronlut 9 under omrøring inntil en pH verdi på 6 - 7 er oppnådd, for derved å frembringe utfelling av aluminiumhydroksyd og nøytrali-sering for fjerning av avløpsvannet. Magnesiumsulfat forblir herunder fremdeles i løsning. 8. Filtrering av aluminiumhydroksydet gjennom vakuumfilter 3 til mellombeholderen 6 for fjerning av avløpsvann. 6. Drying and calcination 7 of the treated scrap dust at 500°C. Partial introduction into the electrolysis cell 8. 7. Return of the sulfuric acid filtrate from between the container 6 to the reaction container 1. Slow supply of cold 10% caustic soda 9 with stirring until a pH value of 6 - 7 is achieved, thereby producing precipitation of aluminum hydroxide and neutralization to remove the waste water. Magnesium sulfate still remains in solution below. 8. Filtration of the aluminum hydroxide through vacuum filter 3 to the intermediate container 6 for the removal of waste water.

Etter tørking og kalsinering 7 av det utvaskede aluminiumhydroksyd innføres dette i elektrolysecellen 8. Ut i fra dette finner det således sted en oppdeling av aluminiumskrapet etter oppmalingen i en fraksjon rik på metallisk aluminium, fortrinnsvis i en kornstørrelse < 1 mm for gjentatt nedsmelting under tilssats av omsmeltesalter, og metallfattig skrapstøv med kornstørrelse < 1 mm. Frem-gangsmåten i henhold til oppfinnelsen går videre ut på gjeninnsetning av skrapstøv sammen med de saltrike rester fra smelteovnene under samtidig tilbakevinning av omsmeltesaltene. After drying and calcining 7 of the washed out aluminum hydroxide, this is introduced into the electrolysis cell 8. Based on this, a division of the aluminum scrap after grinding into a fraction rich in metallic aluminum, preferably in a grain size < 1 mm, takes place for repeated melting down with the addition of remelting salts, and metal-poor scrap dust with a grain size < 1 mm. The method according to the invention further involves the reintroduction of scrap dust together with the salt-rich residues from the melting furnaces while simultaneously recovering the remelting salts.

Videre finner ny innføring i elektrolysecellen sted ved oppslemning ved fortynnede syrer, for derved å oppnå fjerning av magnesium, særlig fra legeringsskrap. Herunder oppløses imidlertid også andre forurensende oksyder, fremfor alt oksyder av sink, kobber, kalsium, jern og titan i stor utstrekning. Furthermore, new introduction into the electrolysis cell takes place by slurrying with dilute acids, thereby achieving the removal of magnesium, particularly from alloy scrap. However, other polluting oxides also dissolve below, above all oxides of zinc, copper, calcium, iron and titanium to a large extent.

En sur oppslemning utføres fortrinnsvis med 1 - 90 % svovelsyre, helst 10 %ig varm svovelsyre. An acid slurry is preferably carried out with 1 - 90% sulfuric acid, preferably 10% hot sulfuric acid.

Gjenvinning av det oppløste metalliske aluminium ved den svovelsure oppslemning finner fortrinnsvis sted ved den påkrevede nøytralisering for fjerning av behandlingsvannet under tilsats av 1 - 50 % lut, fortrinnsvis 5 %ig kald natronlut. Recovery of the dissolved metallic aluminum in the sulfuric acid slurry preferably takes place during the required neutralization to remove the treatment water with the addition of 1 - 50% lye, preferably 5% cold caustic soda.

Til slutt fraskilles magnesiumioner ved utfelling av aluminiumhydroksyd ved innstilling av pH-området på 3 - 11, fortrinnsvis 6-7, under langsom tilsetning av 5 %ig kald natronlut under omrøring, hvorved en kvantitativ utfelling av aluminiumhydroksyd oppnås, samtidig som magnesium forblir i løsning i form av sulfat. Finally, magnesium ions are separated by precipitation of aluminum hydroxide by setting the pH range to 3 - 11, preferably 6-7, during the slow addition of 5% cold caustic soda with stirring, whereby a quantitative precipitation of aluminum hydroxide is achieved, while magnesium remains in solution in the form of sulfate.

Claims (5)

1. Fremgangsmåte for gjenvinning av aluminium fra skrap og annet aluminiumholdig avfall, hvor skrapet etter en nedbrytning til mindre bestanddeler, særlig oppmaling, deles opp i en grovfraksjon som fremdeles inneholder meget rent metall og som innsmeltes i saltbad i en smelteovn, og en finfraksjon som overveiende inneholder oksyd, karakterisert ved at den saltrike rest fra smelteovnen for grovfraksjonen etter skylling med varmt vann på kjent måte og filtrering for å adskille lakeaktig saltløsning og sammen med den utfiltrerte finfraksjon, atter filtreres under oppslemning i fortynnede syrer, særlig svovelsyre, hvoretter filterkaken i tørket og oppmalt tilstand tilføres en elektrolysecelle og den dannede løsning av aluminiumsulfat med innhold av metallisk aluminium nøytraliseres med natriumlut, således at aluminium utfelles i form av aluminiumhydroksyd, som tørkes, kalsineres og atter innføres i smelteelektrolysecellen.1. Process for recycling aluminum from scrap and other aluminum-containing waste, where the scrap, after breaking it down into smaller components, especially grinding, is divided into a coarse fraction which still contains very pure metal and which is melted in a salt bath in a smelting furnace, and a fine fraction which mainly contains oxide, characterized in that the salty residue from the melting furnace for the coarse fraction after rinsing with hot water in a known manner and filtering to separate the brine-like salt solution and, together with the filtered out fine fraction, is again filtered under suspension in dilute acids, especially sulfuric acid, after which the filter cake in dried and ground state is fed to an electrolysis cell and the formed solution of aluminum sulphate containing metallic aluminum is neutralized with sodium hydroxide solution, so that aluminum is precipitated in the form of aluminum hydroxide, which is dried, calcined and reintroduced into the melting electrolysis cell. 2. Fremgangsmåte som angitt i krav 1, karakterisert ved at fraksjonsskillet finner sted ved en kornstørrelse på omtrent 1 mm.2. Method as stated in claim 1, characterized in that the fractional separation takes place at a grain size of approximately 1 mm. 3. Fremgangsmåte som angitt i krav 1 eller 2, karakterisert ved at den sure oppslemning finner sted med 1-90 %ig svovelsyre, fortrinnsvis 10 %ig varm svovelsyre.3. Method as stated in claim 1 or 2, characterized in that the acidic slurry takes place with 1-90% sulfuric acid, preferably 10% hot sulfuric acid. 4. Fremgangsmåte som angitt i krav 1 - 3, karakterisert ved at nøytraliseringen for awannsfjerning utføres med 1-50 %ig lut, fortrinnsvis 5 %ig kald natronlut.4. Method as specified in claims 1 - 3, characterized in that the neutralization for dewatering is carried out with 1-50% lye, preferably 5% cold soda ash. 5. Fremgangsmåte som angitt i krav 1 - 4, karakterisert ved at magnesiumioner fraskilles ved utfelling av aluminiumhydroksyd under innstilling av pH-området på 3 - 11, fortrinnsvis 6-7, ved langsom tilsats av 5 %ig kald natronlut under omrøring, således at en kvantitativ utfelling av aluminiumhydroksyd oppnås, mens magnesium forblir i løsning i form av sulfat.5. Method as stated in claims 1 - 4, characterized in that magnesium ions are separated by precipitation of aluminum hydroxide under setting of The pH range of 3 - 11, preferably 6-7, by slow addition of 5% cold caustic soda with stirring, so that a quantitative precipitation of aluminum hydroxide is achieved, while magnesium remains in solution in the form of sulphate.
NO852281A 1984-06-08 1985-06-06 PROCEDURE FOR RECOVERING ALUMINUM FROM WASTE MATERIAL. NO164665C (en)

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
AT189584A AT383105B (en) 1984-06-08 1984-06-08 METHOD FOR RECOVERY OF ALUMINUM FROM SCRATCHES

Publications (3)

Publication Number Publication Date
NO852281L NO852281L (en) 1985-12-09
NO164665B true NO164665B (en) 1990-07-23
NO164665C NO164665C (en) 1990-10-31

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NO852281A NO164665C (en) 1984-06-08 1985-06-06 PROCEDURE FOR RECOVERING ALUMINUM FROM WASTE MATERIAL.

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EP (1) EP0167789B1 (en)
AT (1) AT383105B (en)
DE (1) DE3567913D1 (en)
NO (1) NO164665C (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108396150A (en) * 2018-01-29 2018-08-14 环境保护部华南环境科学研究所 A kind of secondary recovery product line device of aluminium lime-ash

Families Citing this family (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
AT390965B (en) * 1988-02-17 1990-07-25 Austria Metall TREATMENT AND DISPOSAL OF SCRATCHES, SALT SLAG AND ALUMINUM-BASED WASTE
CH685562A5 (en) * 1992-03-17 1995-08-15 Alusuisse Lonza Services Ag Use of mixt. of combustible material and aluminium or alloy in metal mfr.
DE4425424C1 (en) * 1994-07-19 1996-02-22 Harzer Dolomitwerke Gmbh Process for processing slag or dross from magnesium production
US6110434A (en) * 1998-02-25 2000-08-29 Alumitech Of Cleveland, Inc. Recovery of products from non-metallic products derived from aluminum dross
EP3825426A1 (en) * 2019-11-22 2021-05-26 Befesa Aluminio, S.L. Process for transforming secondary aluminium oxide into alternative raw material and uses thereof

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE887270C (en) * 1944-02-22 1953-08-20 Vaw Ver Aluminium Werke Ag Process for the recovery of the metal from light metal scrapers

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108396150A (en) * 2018-01-29 2018-08-14 环境保护部华南环境科学研究所 A kind of secondary recovery product line device of aluminium lime-ash

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Publication number Publication date
AT383105B (en) 1987-05-25
DE3567913D1 (en) 1989-03-02
NO852281L (en) 1985-12-09
EP0167789A1 (en) 1986-01-15
NO164665C (en) 1990-10-31
ATA189584A (en) 1986-10-15
EP0167789B1 (en) 1989-01-25

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