METHOD OF PURIFYING ALUMINIUM

Abstract: A method of purifying aluminium contaminated with cerium or other rare earth metal comprises bringing the molten metal into contact with a halogenating agent. Preferred halogenating agents are aluminum fluoride for reducing cerium levels to around 0.1% to 0.3%, and chlorine gas for reducing cerium levels still further, and these may advantageously be used in sequence. Particulate aluminium fluoride may be introduced into the vortex of a stirred body of the molten metal. The controlled addition of chlorine may be affected by bubbling a mixture of chlorine and an inert gas into a body of the molten metal. The cerium contamina­ tion may arise from the use of a dimensionally stable anode comprising cerium dioxide in an aluminium reduction cell.

Description: This invention relates to a method of producing aluminium free from contamination by cerium and other rare earth metals. In the conventional Hall-Heroult cell for aluminium production, one or more overhead anodes of carbonaceous material are suspended in an electrolyte of molten cryolite containing dissolved alumina. The cell cathode may be a pool of molten product aluminium metal on the floor of the cell, or a solid cathode mounted in the floor may be provided. Passage of electricity through the cell generates aluminium at the cathode and carbon oxides at the anodes, as a result of which the carbonaceous anodes are progressively consumed. Thus the life of a pre-bake anode is typically 2 - 3 weeks, after which time the butt must be removed and a fresh anode installed. During the century or so since Hall and Heroult designed their cell, many proposals for dimensionally stable anodes have been put forward, but none has achieved commercial success. A promising approach described in European Patent Specification 114085 A involves providing a protective coating of an oxide of cerium or other rare earth element on the surface of the anode. The coating may be formed in situ by including a minor proportion of cerium or other rare earth metal compound in the electrolyte. During operation of the cell, an equilibrium is set up between trivalent cerium or other rare earth metal ion dissolved in the electrolyte, and a protective oxide coating of tetravalent cerium or other rare earth metal on the surface of the anode. Even when the protective coating on the anode is pre-applied, an equilibrium is set up between rare earth metal oxide in the coating and rare earth metal ion in the electrolyte. Unfortunately, a proportion of the cerium or other rare earth metal ion in the electrolyte is reduced during electrolysis to zero valency, in which state it alloys with and contaminates the molten product aluminium The contaminant concentration depends on various factors but may reach as high as 4%. For various reasons, this contamination is not desired. Cerium is fairly expensive and needs to be recovered for re-use, and the same is even more true of other rare earth metals. The contaminant may spoil the metallurgical properties of aluminium and is not a constituent of the commonly used aluminium alloys. This invention is concerned with the problem of removing the contaminant. The present invention provides a method of purifying molten aluminium contaminated with cerium or other rare earth metal, which method comprises bringing the molten aluminium into contact with a halogenating agent selected from chlorine, aluminium chloride and aluminium fluoride to convert contaminant cerium or other rare earth metal to a halide, and separating the contaminant halide from the molten aluminium product. The present invention further provides a method of producing aluminium by electrolysis of a molten fluoride electrolyte containing dissolved alumina, said electrolyte containing cerium or other rare earth metal ion in the trivalent state in a concentration to maintain a tetravalent oxide coating on the surface of the anode, recovering molten aluminium contaminated with cerium or other rare earth metal, bringing the molten aluminium into contact with a halogenating agent selected from chlorine, aluminium chloride and aluminium fluoride to convert contaminant cerium or other rare earth metal to a halide, and separating the contaminant halide from the molten aluminium product. Reference has been made above to cerium or other rare earth metals. It is likely that cerium would be used in practice, but where reference is made below to cerium, it should be understood that other rare earth elements are also contemplated. The cerium concentration is generally from 0.1 to 4%. In the electrolytic cell, cerium is reduced from the fluoride to the metal. It is therefore somewhat surprising that thermodynamic conditions permit aluminium fluoride to be used to convert cerium metal to cerium fluoride in the presence of aluminium. The equilibrium constant (K) for the reaction where "a" represents thermodynamic activity. Of these quantities a Al is approximately 1 since substantially pure Al is always present. Hence the activity of cerium, which governs the quantity of cerium in the metal, is given by It follows that raising the activity of aluminium fluoride will lower the activity of cerium and drive reaction (1) to the right. In the electrolyte of a typical electrolysis cell the activity of AlF₃ is of the order of 10⁻³ (with respect to the pure solid as standard state). If, therefore, metal which has been equilibrated with such an electrolyte (containing also CeF₃) is removed from the cell and brought into contact with AlF₃ at unit activity, the cerium content of the metal will be to some extent converted to CeF₃. It was not predictable how fast or how far that reaction would go. It was also somewhat surprising that thermodynamic considerations favour the conversion of cerium metal to cerium chloride using aluminium chloride or chlorine gas in the presence of aluminium metal. Even after it had been established that these halogenation reactions were thermodynamically possible, it was not predictable whether they would go with sufficient speed and efficiency to be practicable. For many purposes, aluminium fluoride is the preferred halogenating agent. It has the advantage that its use leads to no net loss of product, since for every mole of cerium converted from metal to fluoride, a mole of aluminium is converted from fluoride to metal. Its use furthermore gives rise to a mixture of aluminium and cerium fluorides which can simply be recycled to the electrolytic cell to make up for operating losses of fluoride and cerium. Aluminium fluoride and cerium fluoride and mixtures of the two are solid at likely operating temperatures and are not significantly wetted by aluminium, so that they are easily separated from molten aluminium. Aluminium fluoride is conventionally used to purify molten aluminium from alkali metal, and alkaline earth metal contaminants. With the proviso that the cerium concentration (at up to 4%) may be much higher than the alkali or alkaline earth metal concentration (at up to 100 ppm), the same techniques may be used. The contaminated molten product metal may be passed through a granular bed of, or containing, aluminium fluoride. More preferably, particulate aluminium fluoride may be introduced into the vortex of a stirred body of contaminated molten product metals according to the method described in European Patent Specifications 65854 and 108178. Stirring is continued for a sufficient time to effect reaction to a desired extent, after which the product metal is allowed to settle. Cerium fluoride either floats to the surface, from which it is easily skimmed off, or adheres to the walls of the retaining vessel and remains behind when the purified metal is poured off. In order to keep the cerium concentration in the electrolyte on a constant level (to maintain the CeO₂ layer on the anode) the amount of recycled cerium should be balanced with the amount of cerium which goes from the electrolyte into the product metal plus that which is lost from the system by other means. In a typical reduction cell it is necessary to add about 15-20 kg. of AlF₃ per tonne of metal produced in order to maintain the fluorine balance in the system. This amount of AlF₃ is thus available at no extra cost for use in the presently contemplated process, since its conversion to CeF₃ before introduction into the cell does not change the fluorine balance. Thus the process is very favourable economically provided that no more than this amount of AlF₃ is needed to remove cerium from the product aluminium. If this amount of AlF₃ is not sufficient to remove all the cerium from the product then more must be used, but obviously such additional AlF₃ must be paid for and it ultimately ends up as unwanted cryolite bath. The process is technically feasible but the economics deteriorate progessively as the amount of AlF₃ used exceeds that which is necessary to maintain the fluorine balance. The rate of reduction in cerium concentration of the product metal depends also on the temperature, being greater at higher temperatures, and on the stirring. Stirring times of 1 to 60 minutes are typical. It may be useful to add the aluminium fluoride in increments, with a period of stirring followed by settling and skimming following each incremental addition. Temperature limits are generally set by the need to keep the product metal molten and to avoid excessive volatilisation of the fluorides. Instead of using pure solid aluminium fluoride as a halogenating agent, it is quite possible, and may be desirable to use a cryolite bath rich in aluminium fluoride. Although the AlF₃ activity may not be quite unity, it is sometimes advantageous to handle a liquid instead of a solid, and the liquid also provides a solvent for the cerium fluoride which is formed. Such a bath may preferably be made by adding aluminium fluoride to electrolyte withdrawn from a cell. It is impossible using aluminium fluoride to reduce the contaminant cerium concentration much below 0.1% because that is the level set by equilibrium (1) above. It is therefore preferred to use aluminium fluoride in an amount of from 95% to 140% of the stoichiometric amount required for reaction with all the cerium (or other rare earth metal) present, and to continue treatment for long enough to reduce the cerium content to a level in the range 0.1% to 0.3%. Further reduction of the cerium content of the molten metal is best effected using chlorine. Chlorine gas may be used to precipitate cerium preferentially to aluminium, provided that the chlorine addition is controlled (either by small dosage or by admixture with an inert gas) to keep activity low enough. The use of chlorine as a halogenating agent is preferred for molten metals contaminated with less than 0.3% of cerium. By bubbling chlorine through the contaminated product metal. the cerium content can readily be reduced to 50 ppm in a reasonable time. Instead of using pure chlorine, a mixture of chlorine with an inert gas such as nitrogen may be used to provide better agitation and better metal/gas contact. The metal/gas contact may be further improved by stirring the metal. If the temperature is kept below 800°C, the cerium chloride separates as a solid and is easily removed by skimming. As a halogenating agent, aluminium chloride is generally less preferred than aluminium fluoride, because it is undesirable to add chlorides to an electrolytic cell since they ultimately lead to corrosion and environmental problems. Also aluminium chloride, being a gas at the temperatures in question and very subject to reaction with moisture, is difficult to handle. It is, of course, formed in situ any time that chlorine is brought into contact with molten aluminium so that the description given above of the effects of chlorine generally applies to aluminium chloride. As noted above in relation to aluminium fluoride, the amount of halogenating agent must be at least stoichiometric with the amount of cerium to be removed. Larger amounts may improve reaction kinetics. Contact times should be sufficient to effect the desired reduction in cerium content and will generally be in the range of 1 - 60 minutes. When the cerium is separated as cerium chloride, it may be converted to the fluoride, by known techniques, prior to being recycled to the electrolytic reduction cell, or may be returned direct to the cell without prior treatment. Reference is directed to the accompanying drawing which is a flowsheet showing one embodiment of the invention. Referring to the drawing, an aluminium reduction cell 10 is fed with Al₂O₃ via line 12, with CeO₂ via line 14, and with a CeF₃ /AlF₃ mixture via line 16. The product metal, an Al - 3% Ce alloy passes to a station 18 for treatment with AlF₃ supplied from a plant 20. While the dross and mixed fluorides are recycled to the cell 10, the product metal, now contaminated with only 0.1 - 0.2% Ce, passes to a station 22 for treatment with chlorine. The skim is leached at 24 for cerium recovery, and the cerium oxidised at 26 to CeO₂ which is mixed with fresh CeO₂ at 27 and recycled via line 14 to the reduction cell 10. The unwanted residue from stations 24 and 26 passes to waste at 30. Pure product metal is recovered at 28 from the chlorine treatment. The following Examples illustrate the invention. The cerium-contaminated aluminium samples were specially prepared for the purposes of this invention. Example 1 150 kg of Al 3.5 weight percent Ce was heated to 780°C. 2.1 kg of AlF₃ powder was stirred into the melt with an impeller. After 20 minutes the melt was skimmed and a sample of metal was found to contain 1.57 weight percent Ce. A further 1.55 kg of AlF₃ was then stirred into the melt for 20 minutes after which the remaining aluminium was found to contain 0.55 weight percent Ce. Example 2 150 kg of Al-0.5% Ce alloy was treated at about 800°C with 1 kg of aluminium fluoride powder. The powder was stirred into the aluminium for 30 minutes. Samples taken after the dross had been removed analysed 0.10 weight percent cerium. Another kilogram of aluminium fluoride powder was stirred into the melt for 30 minutes. After removing the dross a sample was taken which analysed at 0.097 weight percent cerium. The addition of 1 kg of AlF₃ was repeated again. After another 30 minutes of stirring the cerium concentration of the melt was 0.089 weight percent. Example 3 Pure Cl₂ gas was bubbled at a rate of about 1 L/min through a 4.5 kg Al-Ce alloy for 10 minutes. The Ce concentration fell from a value of 0.097 weight percent, corresponding to the material left at the end of Example 2 Stage 1, to 0.015 weight percent. Example 4 A 90% N₂-10% Cl₂ gas mixture was bubbled through 68 kg of Al-0.15% Ce alloy at a rate of approximately 14 l/min. The target temperature of the metal was 800°C. Over a 72 minute period the Ce concentration was reduced to 0.045 weight percent. Example 5 A 90% N₂-10% Cl₂ gas mixture was bubbled through 68 kg of Al-0.15% Ce alloy at a rate of 20 L/min. The target metal temperature was 800°C. An impeller was stirring the aluminium at a rate of 800 r.p.m. The concentration of Ce was reduced to less than 0.005 weight percent in 25 minutes.

Claims: A method of purifying molten aluminium contaminated with cerium or other rare earth metal, which method comprises bringing the molten aluminium into contact with a halogenating agent selected from chlorine, aluminium chloride and aluminium fluoride to convert contaminant cerium or other rare earth metal to a halide, and separating the contaminant halide from the molten aluminium product. A method as claimed in claim 1, wherein the molten aluminium is contaminated with from 0.1 - 4% of cerium, and aluminium fluoride is used to convert contaminant cerium to cerium fluoride. A method as claimed in claim 1 or claim 2, wherein particulate aluminium fluoride is introduced into the vortex of a stirred body of the contaminated molten aluminium to convert cerium or other rare earth metal to a fluoride. A method as claimed in claim 2 or claim 3, wherein aluminium fluoride is used in an amount of from 95% to 140% of the stoichiometric amount required for reaction with all the cerium or other rare earth metal present. A method as claimed in claim 1 , wherein the molten aluminium is contaminated with up to 0.3% of cerium, and chlorine is used to convert contaminant cerium to cerium chloride. A method as claimed in claim 5, wherein controlled addition of chlorine is effected by bubbling a mixture of chlorine with an inert gas into a body of the molten aluminium. A method as claimed in claim 1, wherein the purification treatment is effected in two stages, the first stage comprising contacting the molten aluminium with aluminium fluoride, and the second stage comprising contacting the molten aluminium with chlorine. A method as claimed in claim 7, wherein the first stage is effected to an extent to reduce the cerium content of the molten aluminium down to a level of 0.1% to 0.3%, and the second stage is effected to an extent to further lower the cerium content of the molten aluminium. A method of producing aluminium by electrolysis of a molten fluoride electrolyte containing dissolved alumina, said electrolyte containing cerium or other rare earth metal ion in the trivalent state in a concentration to maintain a tetravalent oxide coating on the surface of the anode, recovering molten aluminium contaminated with cerium or other rare earth metal, bringing the molten aluminium into contact with a halogenating agent selected from chlorine, aluminium chloride and aluminium fluoride to convert contaminant cerium or other rare earth metal to a halide, and separating the contaminant halide from the molten aluminium product. A method as claimed in claim 9, wherein the cerium or other rare earth metal halide is recycled to the electrolyte of an aluminium reduction cell. A method as claimed in claim 9 or claim 10, wherein the molten aluminium is contaminated with 0.1% to 4% of cerium, aluminium fluoride is used to convert contaminant cerium to cerium fluoride, and a mixture of unreacted aluminium fluoride and cerium fluoride is separated from the molten aluminium and recycled to the electrolyte of the aluminium reduction cell.

Inventors: DEWING, ERNEST WILLIAM, REESOR, DOUGLAS NEIL
Applicants: MOLTECH INVENT S.A.
Application year: 1985
Main classification: C22B21
IPC codes: C22B21