CN109108049A - Containing sodium, the method for transformation of fluorochemical and system in a kind of aluminium electroloysis dangerous waste slag - Google Patents

Containing sodium, the method for transformation of fluorochemical and system in a kind of aluminium electroloysis dangerous waste slag Download PDF

Info

Publication number
CN109108049A
CN109108049A CN201810867455.1A CN201810867455A CN109108049A CN 109108049 A CN109108049 A CN 109108049A CN 201810867455 A CN201810867455 A CN 201810867455A CN 109108049 A CN109108049 A CN 109108049A
Authority
CN
China
Prior art keywords
dangerous waste
conversion
slag
mill
fluorochemical
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
CN201810867455.1A
Other languages
Chinese (zh)
Other versions
CN109108049B (en
Inventor
刘恩辉
邵旭
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.)
Xiangtan University
Original Assignee
Xiangtan University
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 Xiangtan University filed Critical Xiangtan University
Priority to CN201810867455.1A priority Critical patent/CN109108049B/en
Publication of CN109108049A publication Critical patent/CN109108049A/en
Application granted granted Critical
Publication of CN109108049B publication Critical patent/CN109108049B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B2101/00Type of solid waste
    • B09B2101/02Gases or liquids enclosed in discarded articles, e.g. aerosol cans or cooling systems of refrigerators
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B5/00Operations not covered by a single other subclass or by a single other group in this subclass
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B9/00General methods of preparing halides
    • C01B9/08Fluorides
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01FCOMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
    • C01F11/00Compounds of calcium, strontium, or barium
    • C01F11/20Halides
    • C01F11/22Fluorides
    • 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
    • C01F5/26Magnesium halides
    • C01F5/28Fluorides

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Environmental & Geological Engineering (AREA)
  • Inorganic Chemistry (AREA)
  • Engineering & Computer Science (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Geology (AREA)
  • Physics & Mathematics (AREA)
  • Thermal Sciences (AREA)
  • Dispersion Chemistry (AREA)
  • Health & Medical Sciences (AREA)
  • General Health & Medical Sciences (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

The present invention relates in a kind of aluminium electroloysis dangerous waste slag containing sodium, the method for transformation of fluorochemical and system.Compounds containing sodium in aluminium electroloysis dangerous waste slag is transformed into not fluorine-containing soluble sodium compound including the use of transforming agent, by the mechanochemistry conversion reaction in conversion mill by method for transformation, fluorochemical is transformed into insoluble and harmless minerals fluorine compounds, cyanogen compound is oxidized and is transformed into innocuous gas, to thoroughly release the harm of fluoride and cyanide in aluminium electroloysis dangerous waste slag.Conversion system includes sequentially connected dangerous waste slag crushing plant, milling equipment, conversion mill, stirred reactor and solid-liquid separating equipment, solid-liquid separating equipment is directly connected to concentration or crystallizer, drying or Equipment for Heating Processing again, and dry or Equipment for Heating Processing connects disintegrating apparatus.Present invention process is simple, be easy to be mass produced, production cost is low, three-waste free pollution, environmentally friendly, can be realized the processing target of the innoxious and recycling of aluminium electroloysis dangerous waste slag.

Description

Containing sodium, the method for transformation of fluorochemical and system in a kind of aluminium electroloysis dangerous waste slag
Technical field
The present invention relates to, containing sodium, the method for transformation of fluorochemical and system, belong to electrolysis in a kind of aluminium electroloysis dangerous waste slag Aluminum i ndustry solid waste is innoxious with application technology as the second resource field.
Background technique
It is more than 36,000,000 tons, accounts for global electricity to built about 45,000,000 tons of the aluminium electroloysis production capacity of China in 2017, actual production Solve 50% or more of aluminium production capacity.During aluminum electrolysis, charcoal cathode due to fluorine-containing salts infiltration and expand, further cause The breakage of electrolytic cell is scrapped.Aluminium cell generally just needs to stop groove overhaul using 4-6 or so, takes out all waste and old liner materials Expect (referred to as slag from delining), slag from delining is inevitable solid waste during Aluminum Electrolysis Production.The every life of Aluminum Electrolysis Production The slag from delining that 1 ton of primary aluminum about discharges 10~30kg is produced, electrolytic aluminium slag from delining is defined as danger in " National Hazard waste register " Solid waste (classification are as follows: HW48).Slag from delining mainly accounts for about 55%, waste refractory materials by waste cathode carbon block (including thickener) (calcium silicate board, ceramic beaverboard, insulating brick, Impervious Materials, castable, lateral mass) accounts for about 45% composition.Aluminum electrolysis waste cathode carbon In block, carbon materials account for 30%~70%, remaining for electrolyte, mainly Na3[AlF6]、NaF、CaF2、MgF2、LiF、AlF3、 NaCN、Na4[Fe(CN)6] etc., there are also a small amount of Al, Al4C3, AlN, Na etc., these substances have soluble and react with water Activity can generate HF, HCN, H2、CH4、NH3Deng harmful or imflammable gas, it is fluorine-containing, enter environment containing cyanogen compound can be to the mankind And the health of animals and plants constitutes greatly harm with growth.
Aluminium electroloysis dangerous waste slag is a kind of valuable resource rich in high-graphitized carbon and fluorine-containing electrolyte.Therefore, how thorough Bottom releases the harm of fluoride and cyanide in aluminium electroloysis dangerous waste slag, realizes the innoxious and resource utilization of aluminium electroloysis dangerous waste slag Using being the industry difficulty for needing to capture, expert scholar and production line personnel have carried out unremitting for many years for this problem Exploratory development.
Chinese invention CN106745137A, CN106077038A, CN106077040A, CN106745137A, CN106587122A, CN101817521A, CN105821445A are proposed using alkali leaching or ultrasonic wave secondary flotation alkaline pressure of oxygen leaching Method process aluminum electrolytic waste and old cathode carbon or aluminium electroloysis waste material, extract ice crystal and carbon materials respectively.Chinese invention CN106077037A, CN106077036A, CN106180118A, CN101984984A propose auxiliary using acid processing or ultrasonic wave Help the method process aluminum electrolytic waste and old cathode carbon or slag from delining of flotation pressurization acid processing.Chinese invention CN107162061A proposition is adopted With alkali leaching, Ore Leaching and the united method of flyash, harmless treatment and resource are carried out to aluminum cell waste cathode carbon Change and utilizes.
105964659 A of Chinese invention CN106064813A, CN proposition protects waste and old cathode powdered carbon at 200~400 DEG C Temperature removes cyanogen, and except cyanogen material obtains breeze and electrolyte slag through FLOTATION SEPARATION, electrolyte slag heats at 550~800 DEG C removes charcoal Impurity obtains electrolyte powder, and breeze goes soluble matter to obtain the powdered carbon of purity is high by alkali leaching, and alkali lixivium leads to CO2Ice crystal is precipitated Stone and alumag.
102989744 A of Chinese invention CN, CN102989743A, CN102978659A, CN102992299A, CN102992300A, CN102976776A are separately recovered using the method process aluminum electrolytic waste residue of water logging, flotation and high-temperature calcination Carbon dust, refractory material.
Aluminum cell waste cathode carbon powder is soaked in water in 105772486 A of Chinese invention CN proposition, by soluble cyanogen Compound leaches, then hydrogen peroxide, stabilizer is added (selected from citric acid, tartaric acid, ethylenediamine tetra-acetic acid, amino three in leachate Methylene phosphonic acid, polyacrylic acid, maleic acid, borax, ammonium carbonate, ammonium hydrogen carbonate, ammonium acetate, in ammonium citrate), catalyst (choosing From ZnO, CuO, Fe3O4、WO3In) after so that cyanide oxidation product is resolved into CO in 30~70 DEG C of reactions2、NH3Gas.Document (China Environmental Science association Annual Conference collection of thesis in 2013: p5401~5407.) is reported using at water logging, flotation, chemistry The research of reason, evaporative crystallization, waste gas absorption process electrolytic aluminium danger solid waste.
103239828 A of Chinese invention CN proposes a kind of program-controlled, manual electrolytic aluminium slag from delining hamlessizing technology technique, Any one of sodium chlorate, calcium hypochlorite or hydrogen peroxide are used for except cyanogen agent, using calcium chloride, calcium oxide, calcium hydroxide or carbon Any one of sour calcium is defluorinating agent, regulates and controls the residual quantity of pH value and fluoride in fluorine conversion process by hydrochloric acid.The patent is same When provide the reaction warehouse and acid-regulating tank of a kind of strong acid-base resistance and strong oxidizer.
Chinese invention CN100542702C is by waste cathode of aluminum electrolytic cell carbon block and is rich in SiO2And Al2O3Flyash mixing Carry out calcination process, treated material H2SO4With lime resolution process, obtain waste cathode of aluminum electrolytic cell carbon block innoxious And resource utilization.Chinese invention CN107285354A by Aluminum carbonaceous dangerous waste, forge, make fluoride salt by the electricity at 1050~1200 DEG C It is melt into liquid and is saturated separation, again low fluorine carbon granules progress high-temperature electric forged to obtain high-purity carbon product.Chinese invention CN101054693A, CN101063215A are respectively by waste cathode of aluminum electrolytic cell powdered carbon and aluminium electrolysis anode breeze and organic binder Mixing compacting is agglomerating, carbonaceous complete oxidation was obtained 97.5% or more electricity in calcination process 4~6 hours at 650~900 DEG C again Solve matter product.Chinese invention CN103831285A provides a kind of including heating furnace, heat cycles devices, exhaust gas cleaner The aluminium electroloysis breeze that gives up is carried out 7~8h of harmless treatment by processing system in 1250~1350 DEG C of heating furnace.Chinese invention CN107628614A use 1200~1700 DEG C of temperature lower calcination electrolytic aluminium waste cathodes, by useless cathode carbon and fluorination Object, oxide and cyanide are separated, and realize its innoxious and resource utilization.
Chinese invention CN105642649A, CN106185818A, CN106269787A use 2000 DEG C or more of superhigh temperature With handle electrolytic aluminium waste cathode carbon block under vacuum condition, the fluoride therein of volatilizing decomposes cyanide therein, by carbon in cathode Element, fluoride and cyanide efficiently separate decomposition, realize its innoxious and resource utilization.
From the point of view of existing technological achievement, the innoxious of aluminium electroloysis dangerous waste slag, recycling treatment are utilized and are segmented into water The wet-treating of solution and two major class of pyrogenic attack under high temperature.Wet-treating further relate to washing (leaching), alkaline process, acid system, Acid-alkali combination method simultaneously cooperates floatation process, and mainly for the purpose of recycling electrolyte and carbon materials, oxygen is used in wet-treating Cyanide is resolved into harmless gaseous matter by agent.Pyrogenic attack technology is mainly negative for the purpose of innoxious, or based on giving up Extremely middle carbonaceous content 50% or more, its calorific value resource can be effectively utilized;Or electrolyte melting permeability and separation is returned It receives;Or HF is converted by fluoride and carries out sorption enhanced utilization again;Or it is converted into electrolyte by adding converting additive Harmless and insoluble fluorine minerals;Or take high-temperature vacuum technology that utilization is separately recovered in carbon materials and electrolyte.? In pyrogenic attack, it is oxidized at high temperature containing cyanogen compound and resolves into harmless gaseous matter.
From the point of view of existing technological achievement, the wet-treating and pyrogenic attack of aluminium electroloysis dangerous waste slag still have many urgent Problem to be solved.
At least there is following main problem in current wet processing technique: the first, generated a large amount of saliferous, fluoride waste It is not effectively addressed, causes secondary pollution;Generated H2、CH4、NH3Gas is not under control and utilizes, produced HF cause serious pollution.The second, the electrolyte and carbon materials impurity content recycled is excessively high, cannot directly utilize.The Three, process route is cumbersome, technology is complicated, equipment seriously corroded, and processing cost is excessively high.4th, due to aluminium electroloysis dangerous waste slag chute age And the influence of the factors such as fluctuation of the difference of capacity, material composition, cause process parameter control difficulty big.
At least there is following main problem in current pyrogenic attack technology: the first, producing a large amount of entrainment HF and dust Tail gas need to administer.The second, electrolytic salt recycling is not thorough, remains in carbon materials or clinker and need further to locate Reason.Third, low melting point electrolytic salt occur vitreous clinker in furnace, cause the incomplete residual quantity of Carbon Materials oxidizing fire big, Vitreous clinker causes production status deterioration, production stability poor in furnace.4th, reaction mass is difficult to realize the uniform of molecular level It mixes, conversion reaction is caused to be not thorough.5th, equipment seriously corroded, processing energy consumption are high.
Summary of the invention
In order to solve the above technical problem, the present invention provides turns in a kind of aluminium electroloysis dangerous waste slag containing sodium, fluorochemical Change method and system.The present invention has technical process convenient for control, is easy to industrialize that steady production, process costs are low, no three wastes The features such as pollution and equipment are corroded.
The invention is realized by the following technical scheme:
Method for transformation containing sodium, fluorochemical in a kind of aluminium electroloysis dangerous waste slag, including the use of transforming agent, by converting Compounds containing sodium in aluminium electroloysis dangerous waste slag is transformed into not fluorine-containing soluble sodium chemical combination by the mechanochemistry conversion reaction in mill Object, fluorochemical be transformed into insoluble and harmless minerals fluorine compounds, be oxidized containing cyanogen compound be transformed into it is harmless N2Or NH3And CO2, to thoroughly release the harm of fluoride and cyanide in aluminium electroloysis dangerous waste slag;Conversion system includes successively connecting The dangerous waste slag crushing plant that connects, milling equipment, conversion mill, stirred reactor and solid-liquid separating equipment, solid-liquid separating equipment again with Concentration or crystallizer, drying or Equipment for Heating Processing are directly connected to, and dry or Equipment for Heating Processing connects disintegrating apparatus.
Method for transformation containing sodium, fluorochemical in a kind of aluminium electroloysis dangerous waste slag, including following some or all of step (sequence of steps below is to express for convenience, does not indicate which part precedence relationship, contained step specifically include directly It is subject to literal logical specification or logical relation):
(1) aluminium electroloysis dangerous waste slag is broken, milling, screening and homogenizing, obtain the dangerous waste ground-slag of particle≤200 μm;Point Analyse the molal quantity or quality for determining sodium and fluorine in unit mass dangerous waste ground-slag;It analyzes and determines CN in unit mass dangerous waste ground-slag- The molal quantity or quality of ion;
Abrasive body is added in conversion mill, then conversion is ground and carries out air emptying or N2Displacement, by the dangerous waste of metering Ground-slag is added in conversion mill, and the mass ratio for controlling dangerous waste ground-slag and abrasive body is 1:(0.2~10), the water of metering is added to In conversion mill, the solid-liquid mass ratio for controlling dangerous waste ground-slag and water is 1:(1~10);
By in dangerous waste ground-slag containing sodium, fluorochemical be converted to corresponding product chemistry stoichiometry 1~3 times of amount, Or transforming agent is added in conversion mill by the amount of dangerous waste ground-slag quality 5~80%;
Grinding aid is added in conversion mill by the amount of dangerous waste ground-slag quality 0~1%;
(2) it completes to open conversion mill after step (1), the revolving speed of control conversion mill is 10~1000rpm, conversion temperature is 10~110 DEG C;In the conversion process, timing in batches is to slurry sampling analysis inspection, until Na in slurry solid formation+Ion contains Amount meets company standard, solubility F-Ion concentration stops conversion mill when meeting national emission standard;
(3) slurry is transferred to stirred reactor (reaction kettle or reactive tank or reactor tank) after completion step (2) and carries out brokenly glue With ripening, 60~150 DEG C of temperature is controlled, the processing time is 0.5~5h;
(4) by slurry that step (3) obtains using filtering or centrifuge separation mode is separated by solid-liquid separation and by aqueous solid phase Object in conversion mill or stirred reactor (reaction kettle or reactive tank or reactor tank), using water be detergent by 1:(1~10) consolidate Liquid quality than repeated several times dispensing laundry and be separated by solid-liquid separation, wash into solid formation soluble ion content meet enterprise mark Until standard, merges separating liquid, respectively obtain the i.e. aqueous solid formation of mixture and solubility of wet fluorine-containing minerals and carbon The weak solution of mixture;
(5) the aqueous solid formation that step (4) obtains is dried or is heat-treated 1 at a temperature of 80~300 DEG C~ 10h, crushed to obtain the mixed powder material of fluorine-containing minerals and carbon again, the average particle size of mixed powder material≤ 20 μm, which can be used as merchandise sales or further progress separating-purifying obtains high-quality carbon materials and fluorine Compound mineral raw material;
The high temperature mixed powder material of fluorine-containing minerals and carbon being placed at a temperature of air atmosphere and 700~1200 DEG C 0.5~5h, the mixture that carbon component complete oxidation therein burns, its residue is fluorine-containing minerals are calcined in furnace;
(6) by the Dilute mixed solutions that step (4) obtains carry out concentration or crystallization treatment obtain mixture concentrated solution or Person's solid-phase mixture, or Na, K, Li, Al, Mg, Ca compound separating-purifying in mixture are further obtained into more Gao Pin The series compound raw material of matter and value;
(7) by CN in dangerous waste ground-slag-Ion conversion is at N2Or NH3And CO2Chemical reaction metering ratio 1~5 times of amount, Perhaps by the amount of dangerous waste ground-slag quality 0.1~10% by cyanide transforming agent be added to or step (2) or step (3), Or the oxidation containing cyanogen compound is converted to harmless N in step (6)2Or NH3And CO2.Timing carries out transformation system in batches Analysis checks, until the CN in system-Ion concentration stops conversion reaction when meeting national emission standard;
(8) by generated NH in step (2) or step (3) or step (6)3、CO2、H2O gas carry out sorption enhanced and Dry, generated reducibility gas is collected or direct oxidation burning.
Above-mentioned aluminium electroloysis dangerous waste slag contains F caused by referring in Aluminum Electrolysis Production-Ionic compound contains CN-Ion combination Object is more than all solids waste of national emission standard.
There are Al, Al in above-mentioned aluminium electroloysis dangerous waste slag4C3, the substances such as AlN, Na, reaction institute is participated in conversion reaction Imflammable gas (including the H of generation2、CH4、NH3Deng) it is reducibility gas described in step (8).
In above-mentioned conversion mill, the synchronous effect of high energy mechanical power is anti-in the mechanochemistry conversion containing sodium and fluorochemical Answer so that solid particle is constantly ground, is levigate with conversion, make reactant and product constantly update from charcoal particle and Removing, realizes the quick of conversion reaction and is properly completed.
Further, in all steps, pH control does not use protonic acid material for not less than 6, used to contain sodium The transforming agent of compound and fluorochemical, cyanide transforming agent are free of chlorine element in grinding aid substance.
Further, the essential element that the dangerous waste cinder ladle includes is C (including graphitization C and non-graphitized C), Na, F, It is two or more in Al, Ca, O, N, Li, Mg, Si, K, Fe;The compounds containing sodium includes NaF, Na3AlF6、NaCN、Na4 [Fe(CN)6] in it is two or more;The fluorochemical includes NaF, Na3AlF6、AlF3、LiF、CaF2、MgF2, in KF It is two or more.
It further, include that Ca, Al, Mg, Sr, Ba, La, Ce each element are corresponding with the transforming agent of fluorochemical containing sodium One or more of oxide, hydroxide, sulfate, nitrate, carbonate, acetate, citrate.
After being converted using transforming agent, the not fluorine-containing solubility of the correspondence that the compounds containing sodium in dangerous waste slag is transformed into contains sodium Closing object includes NaOH, Na2SO4、NaNO3、NaOAc、Na2CO3、Na3C6H5O7、Na2AlO4、Na[Al(OH)6]2(OH)3、 NaAlSi2O6、Na2(H2SiO4)·7H2O、Na6Si8O19、Na2Al2SiO6、Na2Si2O5、Na2SiO3One or both of with On.
After being converted using transforming agent, the insoluble and harmless minerals of the correspondence that the fluorochemical in dangerous waste slag is transformed into Fluoride includes CaF2、MgF2、AlF3、SrF2、BaF2、CaF2、LaF3、CeF3、CeF4One or more of.
Further, the cyanide transforming agent includes Na2CO3·1.5H2O2、K2CO3·1.5H2O2、Na2O2、K2O2、 CaO2、SrO2、BaO2、H2O2、(NH4)2S2O8、Na2S2O8、K2S2O8、KMnO4、O2、O3One or more of.
Further, the grinding aid includes polymerized polyalcohol, polyalcohol amine, triisopropanolamine, ethylene glycol, the third two One of alcohol, glycerine, diethylene glycol, triethanolamine, amide, stearic acid, oleic acid, calgon, odium stearate or two Kind or more.
Further, the transforming agent, grinding aid be with the addition of solid, aqueous solution or gaseous state, using it is primary be added, Or the mode for being added or being continuously added in batches.
Conversion system containing sodium, fluorochemical in a kind of aluminium electroloysis dangerous waste slag, including sequentially connected dangerous waste slag are broken Equipment, milling equipment, conversion mill, stirred reactor and solid-liquid separating equipment, solid-liquid separating equipment again with concentration or crystallizer, Dry or Equipment for Heating Processing is directly connected to, and dry or Equipment for Heating Processing connects disintegrating apparatus.
It further, further include condensing plant, condensing plant is connect with concentration or crystallizer.
It further, further include exhaust collection absorption equipment, exhaust collection absorption equipment grinds with milling equipment, conversion, stirs Mix reactor, condensing plant is all connected with.
It further, further include storage facilities, storage facilities includes the dusty material storage arrangement connecting with disintegrating apparatus And the storage arrangement of concentrate or crystalline product.
It further, further include analysis Instrument equipment, analysis Instrument equipment is anti-to milling equipment, conversion mill, stirring is derived from The sample of the equipment such as device, concentration or crystallizer, drying or Equipment for Heating Processing, storage is answered to carry out analysis detection.
Further, the dangerous waste slag crushing plant include jaw crusher, cone crusher, pillar crusher, Double-shaft crusher or impact disintegrating machine.
Further, the milling equipment include column mill, Raymond mill, vertical mill, air swept mill or roll squeezer and with The matched equipment for selecting dressing sieve point and homogenization, to obtain uniform, particle≤200 μm the dangerous waste ground-slag of composition.
Further, concentration or crystallizer are multiple-effect evaporation concentration or crystallization apparatus, for being concentrated or crystallizing solid-liquid point Separating liquid from obtained soluble mixture is related to thermal energy and provides, evaporates the heat exchange and condensation, the recycling of condensed water of phase Utilize, concentrate or transmission of crystal etc..
Above-mentioned exhaust collection absorption equipment is used for being crushed, being milled, sieving and being homogenized, and conversion reaction is broken glue and washed Wash, be concentrated with crystallization etc. during generate tail gas be collected and absorption handle.Material composition in tail gas includes H2O、NH3、 CO2、H2、CH4、N2And micro dust;Gas phase H therein2O passes through condensation reuse, NH3、CO2, dust pass through absorbent absorb It utilizes, fuel gas H2、CH4It is collected storage or enters combustion furnace as fuel utilization.
Material component detection, substance changing effect and content of the above-mentioned analysis Instrument equipment for each link of production process Control detection, product quality detection, environmental emission standard monitoring.
Further, the described conversion mill is the air-tightness ball mill by transformation, body be equipped with abrasive body inlet and outlet, Powder import, liquid material import, gas vent, slurry outlet, clean-drain mouth, gas sample mouth, slurry sample tap;Abrasive body For one or more of corundum ball, zirconia ball, porcelain ball, steel ball, stainless steel ball, alloying pellet.
The beneficial effects of the present invention are:
(1) present invention has technical process convenient for control, is easy to industrialize that steady production, production cost are low, not will cause The features such as three-waste pollution and equipment are corroded.
(2) present invention solves the problems of existing wet-treating and pyrogenic attack production technology and deficiency.For Aluminium electroloysis dangerous waste slag harmlessness and resource utilization, which utilize, provides a kind of advanced, system solution.
Detailed description of the invention
Fig. 1 is the process flow diagram of method for transformation of the present invention.
Fig. 2 is the structural schematic diagram of system of the present invention.
Fig. 3 is the x-ray diffraction pattern of aluminium electroloysis dangerous waste slag used by embodiment.
Fig. 4 is the x-ray diffraction pattern of the obtained fluorine minerals C of embodiment 1.
The SEM that Fig. 5 is the obtained mixed powder material B of embodiment 1 schemes.
Specific embodiment
Below with specific embodiment further illustrate technical solution of the present invention, but the invention is not limited to embodiment, It is not intended to limit the scope of the invention.
As shown in Fig. 2, system of the invention includes sequentially connected dangerous waste slag crushing plant 1, milling equipment 2, conversion mill 3, stirred reactor 4 and solid-liquid separating equipment 5, solid-liquid separating equipment 5 are set with concentration or crystallizer 7, dry or heat treatment again Standby 6 are directly connected to, and dry or Equipment for Heating Processing 6 connects disintegrating apparatus 8;It further include condensing plant 9, exhaust collection absorption equipment 10 and storage facilities, condensing plant 9 connect with concentration or crystallizer 7, exhaust collection absorption equipment 10 and milling equipment 2, turn Change mill 3, stirred reactor 4, condensing plant 9 to be all connected with, storage facilities includes the dusty material storage dress connecting with disintegrating apparatus Set the storage arrangement 12 of 11 and concentrate or crystalline product.
It further include analysis Instrument equipment, analysis Instrument equipment is to being derived from milling equipment, conversion mill, stirred reactor, concentration Or the sample of the equipment such as crystallizer, drying or Equipment for Heating Processing, storage carries out analysis detection.
The dangerous waste slag crushing plant includes jaw crusher, cone crusher, pillar crusher, double-shaft crusher Or impact disintegrating machine.
The milling equipment includes column mill, Raymond mill, vertical mill, air swept mill or roll squeezer and matched choosing Dressing sieve divides the homogenization equipment of powder, to obtain uniform, particle≤200 μm the waste cathode carbon powder of composition.
Concentration or crystallizer be multiple-effect evaporation be concentrated or crystallization apparatus, for be concentrated or crystallize be separated by solid-liquid separation obtain can The separating liquid of soluble mixture is related to thermal energy and provides, evaporates the heat exchange and condensation, the recycling of condensed water, concentration of phase Liquid or the transmission of crystal etc..
Above-mentioned exhaust collection absorption equipment, for broken, milling and homogenizing, glue and washing, concentration to be broken in conversion reaction With crystallization etc. during generate tail gas be collected and absorption handle.Material composition in tail gas includes H2O、NH3、CO2、H2、 CH4、N2And micro dust;Gas phase H therein2O passes through condensation reuse, NH3、CO2, dust be absorbed and utilized by absorbent, can Combustion gas body H2、CH4It is collected storage or enters combustion furnace as fuel utilization.
The described conversion mill is the air-tightness ball mill by transformation, body be equipped with abrasive body inlet and outlet, powder import, Liquid material import, gas vent, slurry outlet, clean-drain mouth, gas sample mouth, slurry sample tap;Abrasive body be corundum ball, One or more of zirconia ball, porcelain ball, steel ball, stainless steel ball, alloying pellet.
Embodiment 1
(1) aluminium electroloysis dangerous waste slag is crushed in high speed disintegrator, is sieved with the sieve of 200 mesh, using screenings into Mechanochemistry conversion of the row containing sodium, fluorochemical.Sodium in unit mass aluminium electroloysis dangerous waste ground-slag is determined using chemical analysis With the mass content of fluorine element, CN in unit mass aluminium electroloysis dangerous waste ground-slag is determined using chemical analysis-The quality of ion contains Amount.
(2) 200g alloy steel ball is added in conversion mill, weighs 100g dangerous waste ground-slag, 45g CaSO4·2H2O、 2gCaO、1.5g Na2S2O8It is added in conversion mill and is uniformly mixed, use N2The air in conversion mill is replaced, then is added into conversion mill Enter 300gH2O.Unlatching conversion mill, revolving speed 100rpm, temperature are 25 DEG C, and the conversion reaction time is 3h.
Slurry is transferred to stirred reactor after conversion reaction, mixing speed 1000rpm, temperature are 95 DEG C, and constant temperature stirs Reaction 90min is mixed to stop.
By tail gas caused by step (1), step (2) respectively by being with the absorber that water is absorbent and with CaO The absorber of absorbent, dust therein, NH3、CO2It is absorbed, H2、CH4Carry out combustion oxidation.
(3) negative pressure leaching is carried out to the slurry after being stirred to react, filter cake is transferred in conversion mill after suction filtration, is added 200gH2O dispensing laundry in conversion mill filters again, wash repeatedly and filters, BaCl of the washing to last filtrate with 2mol/L2 Until solution is examined without precipitating, filtrate is merged.
Filtrate is evaporated under reduced pressure, be concentrated and is crystallized, dry 8h obtains solubility in 120 DEG C of vacuum ovens by it Mixture A.
(4) by aqueous filter cake under 100 DEG C of normal pressures dry 20h, dried object is crushed to obtain fluorine-containing minerals and carbon Mixed powder material B is calcined 3h in the Muffle furnace of air atmosphere and obtains containing without charcoal by mixed powder material B at 900 DEG C Fluorine minerals C.
As seen from Figure 3, the main object of aluminium electroloysis dangerous waste slag used by embodiment 1 coordinate be divided into C, NaF, Na3AlF6、AlF3、LiF、MgF2、SiC、Si3N4、Ca5MgSi3O12、Ca2SiO4、MgSiO3、CaSiO3
As seen from Figure 4, it is by the main component that embodiment 1 handles the obtained Fluoride-bearing Ore substance C without charcoal CaF2、MgF2、SiC、Si3N4、Al2O3、Al2SiO5、SiO2, illustrate NaF, Na in dangerous waste slag3AlF6、AlF3, the components such as LiF It is totally converted metallogenic material CaF2And MgF2, carbon content is fully oxidized burning.
As seen from Figure 5, the mixed powder material B of obtained fluorine-containing minerals and carbon is handled by embodiment 1 Grain diameter be no more than 8 μm, particle be random pattern.
From these testing and analysis datas: embodiment 1 realize in aluminium electroloysis dangerous waste slag containing sodium, fluorochemical it is complete Full conversion, thoroughly relieves the harm of fluoride and cyanide in aluminium electroloysis dangerous waste slag.
Embodiment 2
(1) aluminium electroloysis dangerous waste slag is crushed in high speed disintegrator, is sieved with the sieve of 200 mesh, using screenings into Mechanochemistry conversion of the row containing sodium, fluorochemical.Sodium in unit mass aluminium electroloysis dangerous waste ground-slag is determined using chemical analysis With the mass content of fluorine element, CN in unit mass aluminium electroloysis dangerous waste ground-slag is determined using chemical analysis-The quality of ion contains Amount.
(2) 300g alloy steel ball is added in conversion mill, weighs 100g dangerous waste ground-slag, 30g MgSO4, 1g polyethylene Alcohol, 4g K2S2O8It is added in conversion mill and is uniformly mixed, use N2Air in displacement conversion mill, then 400g is added into conversion mill H2O.Unlatching conversion mill, revolving speed 500rpm, temperature are 40 DEG C, and the conversion reaction time is 2.5h.
Slurry is transferred to stirred reactor after conversion reaction, mixing speed 700rpm, temperature are 105 DEG C, and constant temperature stirs Reaction 100min is mixed to stop.
By tail gas caused by step (1), step (2) respectively by being with the absorber that water is absorbent and with CaO The absorber of absorbent, dust therein, NH3、CO2It is absorbed, H2、CH4Carry out combustion oxidation.
(3) negative pressure leaching is carried out to the slurry after being stirred to react, filter cake is transferred in conversion mill after suction filtration, is added 400gH2O dispensing laundry in conversion mill filters again, wash repeatedly and filters, BaCl of the washing to last filtrate with 2mol/L2 Until solution is examined without precipitating, filtrate is merged.
Filtrate is evaporated under reduced pressure, be concentrated and is crystallized, dry 8h obtains solubility in 120 DEG C of vacuum ovens by it Mixture A.
(4) by aqueous filter cake under 100 DEG C of normal pressures dry 20h, dried object is crushed to obtain fluorine-containing minerals and carbon Mixed powder material B is calcined 3h in the Muffle furnace of air atmosphere and obtains containing without charcoal by mixed powder material B at 1000 DEG C Fluorine minerals C.
The experimental results showed that embodiment 2 realizes the complete conversion in aluminium electroloysis dangerous waste slag containing sodium, fluorochemical, it is thorough Bottom relieves the harm of fluoride and cyanide in aluminium electroloysis dangerous waste slag.
Embodiment 3
(1) aluminium electroloysis dangerous waste slag is crushed in high speed disintegrator, is sieved with the sieve of 200 mesh, using screenings into Mechanochemistry conversion of the row containing sodium, fluorochemical.Sodium in unit mass aluminium electroloysis dangerous waste ground-slag is determined using chemical analysis With the mass content of fluorine element, CN in unit mass aluminium electroloysis dangerous waste ground-slag is determined using chemical analysis-The quality of ion contains Amount.
(2) 350g alloy steel ball is added in conversion mill, weighs 100g dangerous waste ground-slag, 25g SrSO4、2g SrO2It is added It is uniformly mixed into conversion mill, uses N2Air in displacement conversion mill, then 350g H is added into conversion mill2O.Unlatching conversion mill, Revolving speed is 700rpm, temperature is 50 DEG C, and the conversion reaction time is 3.5h.
Slurry is transferred to stirred reactor after conversion reaction, mixing speed 500rpm, temperature are 100 DEG C, and constant temperature stirs Reaction 110min is mixed to stop.
By tail gas caused by step (1), step (2) respectively by being with the absorber that water is absorbent and with CaO The absorber of absorbent, dust therein, NH3、CO2It is absorbed, H2、CH4Carry out combustion oxidation.
(3) negative pressure leaching is carried out to the slurry after being stirred to react, filter cake is transferred in conversion mill after suction filtration, is added 350gH2O dispensing laundry in conversion mill filters again, wash repeatedly and filters, BaCl of the washing to last filtrate with 2mol/L2 Until solution is examined without precipitating, filtrate is merged.
Filtrate is evaporated under reduced pressure, be concentrated and is crystallized, dry 8h obtains solubility in 120 DEG C of vacuum ovens by it Mixture A.
(4) by aqueous filter cake under 100 DEG C of normal pressures dry 20h, dried object is crushed to obtain fluorine-containing minerals and carbon Mixed powder material B is calcined 3h in the Muffle furnace of air atmosphere and obtains containing without charcoal by mixed powder material B at 950 DEG C Fluorine minerals C.
The experimental results showed that embodiment 3 realizes the complete conversion in aluminium electroloysis dangerous waste slag containing sodium, fluorochemical, it is thorough Bottom relieves the harm of fluoride and cyanide in aluminium electroloysis dangerous waste slag.

Claims (10)

1. the method for transformation in a kind of aluminium electroloysis dangerous waste slag containing sodium, fluorochemical, which is characterized in that including following part or Overall Steps:
(1) aluminium electroloysis dangerous waste slag is broken, milling, screening and homogenizing, obtain the dangerous waste ground-slag of particle≤200 μm;Analysis is true Determine the molal quantity or quality of sodium and fluorine in unit mass dangerous waste ground-slag;It analyzes and determines CN in unit mass dangerous waste ground-slag-Ion Molal quantity or quality;
Abrasive body is added in conversion mill, then conversion is ground and carries out air emptying or N2Displacement, the dangerous waste ground-slag of metering is added Enter into conversion mill, the mass ratio for controlling dangerous waste ground-slag and abrasive body is 1:(0.2~10), the water of metering is added to conversion mill In, the solid-liquid mass ratio for controlling dangerous waste ground-slag and water is 1:(1~10);
By in dangerous waste ground-slag containing sodium, fluorochemical be converted to corresponding product chemistry stoichiometry 1~3 times of amount or Transforming agent is added in conversion mill by the amount of dangerous waste ground-slag quality 5~80%;
Grinding aid is added in conversion mill by the amount of dangerous waste ground-slag quality 0~1%;
(2) complete to open conversion mill after step (1), the revolving speed of control conversion mill is 10~1000rpm, conversion temperature be 10~ 110℃;In the conversion process, timing in batches is to slurry sampling analysis inspection, until Na in slurry solid formation+Ion concentration symbol Close company standard, solubility F-Ion concentration stops conversion mill when meeting national emission standard;
(3) complete slurry is transferred to stirred reactor after step (2) and carry out broken glue and ripening, control 60~150 DEG C of temperature, The processing time is 0.5~5h;
(4) slurry that step (3) obtains is separated by solid-liquid separation using filtering or centrifuge separation mode and aqueous solid formation is existed Be detergent in conversion mill or stirred reactor, using water by 1:(1~10) solid-liquid mass ratio repeated several times dispensing laundry simultaneously Be separated by solid-liquid separation, washing is until into solid formation, the content of soluble ion meets company standard, merge separating liquid, respectively obtain wet Fluorine-containing minerals and carbon mixture, that is, aqueous solid formation and soluble mixture weak solution;
(5) the aqueous solid formation that step (4) obtains is dried or is heat-treated 1~10h, again at a temperature of 80~300 DEG C It is crushed to obtain the mixed powder material of fluorine-containing minerals and carbon;
The mixed powder material of fluorine-containing minerals and carbon is placed in the high temperature furnace at a temperature of air atmosphere and 700~1200 DEG C Calcine 0.5~5h, the mixture that carbon component complete oxidation therein burns, its residue is fluorine-containing minerals;
(6) Dilute mixed solutions that step (4) obtains are subjected to concentration or crystallization treatment obtains mixture concentrated solution or solid Phase mixture;
(7) by CN in dangerous waste ground-slag-Ion conversion is at N2Or NH3And CO2Chemical reaction metering ratio 1~5 times of amount or press Cyanide transforming agent is added to or step (2) or step (3) or step by the amount of dangerous waste ground-slag quality 0.1~10% Suddenly the oxidation containing cyanogen compound is converted to harmless N in (6)2Or NH3And CO2.Timing carries out analysis inspection to transformation system in batches It looks into, until the CN in system-Ion concentration stops conversion reaction when meeting national emission standard;
(8) by generated NH in step (2) or step (3) or step (6)3、CO2、H2O gas carries out sorption enhanced and drying, Generated reducibility gas is collected or direct oxidation burning.
2. the method for transformation in aluminium electroloysis dangerous waste slag according to claim 1 containing sodium, fluorochemical, which is characterized in that In all steps, pH control does not use protonic acid material, used compounds containing sodium and fluorine-containing chemical combination for not less than 6 The transforming agent of object, cyanide transforming agent are free of chlorine element in grinding aid substance.
3. the method for transformation in aluminium electroloysis dangerous waste slag according to claim 1 containing sodium, fluorochemical, which is characterized in that The essential element that the dangerous waste cinder ladle includes is two or more in C, Na, F, Al, Ca, O, N, Li, Mg, Si, K, Fe;Described Compounds containing sodium includes NaF, Na3AlF6、NaCN、Na4[Fe(CN)6] in it is two or more;The fluorochemical includes NaF、Na3AlF6、AlF3、LiF、CaF2、MgF2, it is two or more in KF.
4. the method for transformation in aluminium electroloysis dangerous waste slag according to claim 1 containing sodium, fluorochemical, which is characterized in that Compounds containing sodium and the transforming agent of fluorochemical include the corresponding oxide of Ca, Al, Mg, Sr, Ba, La, Ce each element, hydrogen-oxygen One or more of compound, sulfate, nitrate, carbonate, acetate, citrate.
5. the method for transformation in aluminium electroloysis dangerous waste slag according to claim 1 containing sodium, fluorochemical, which is characterized in that The cyanide transforming agent includes Na2CO3·1.5H2O2、K2CO3·1.5H2O2、Na2O2、K2O2、CaO2、SrO2、BaO2、 H2O2、(NH4)2S2O8、Na2S2O8、K2S2O8、KMnO4、O2、O3One or more of.
6. the method for transformation in aluminium electroloysis dangerous waste slag according to claim 1 containing sodium, fluorochemical, which is characterized in that The grinding aid include polymerized polyalcohol, polyalcohol amine, triisopropanolamine, ethylene glycol, propylene glycol, glycerine, diethylene glycol, One or more of triethanolamine, amide, stearic acid, oleic acid, calgon, odium stearate.
7. the method for transformation in aluminium electroloysis dangerous waste slag according to claim 1 containing sodium, fluorochemical, which is characterized in that The transforming agent, grinding aid with the addition of solid, aqueous solution or gaseous state, using it is primary be added or be added in batches or The mode that person is continuously added to.
8. the conversion system in a kind of aluminium electroloysis dangerous waste slag containing sodium, fluorochemical, which is characterized in that including sequentially connected danger Waste residue crushing plant, milling equipment, conversion mill, stirred reactor and solid-liquid separating equipment, solid-liquid separating equipment again with concentration or Crystallizer, drying or Equipment for Heating Processing are directly connected to, and dry or Equipment for Heating Processing connects disintegrating apparatus.
9. the conversion system in aluminium electroloysis dangerous waste slag according to claim 8 containing sodium, fluorochemical, which is characterized in that It further include condensing plant, exhaust collection absorption equipment, storage facilities and analysis Instrument equipment, condensing plant is set with concentration or crystallization Standby connection, exhaust collection absorption equipment are all connected with milling equipment, conversion mill, stirred reactor, condensing plant, storage facilities packet Include the storage arrangement of the dusty material storage arrangement and concentrate or crystalline product that connect with disintegrating apparatus, analysis Instrument equipment pair It is derived from the sample of milling equipment, conversion mill, stirred reactor, concentration or crystallizer, drying or Equipment for Heating Processing, storage facilities Carry out analysis detection.
10. the conversion system in aluminium electroloysis dangerous waste slag according to claim 9 containing sodium, fluorochemical, which is characterized in that The dangerous waste slag crushing plant is jaw crusher, cone crusher, pillar crusher, double-shaft crusher or impact type fining Broken machine;The milling equipment is column mill, Raymond mill, vertical mill, air swept mill or roll squeezer and matched selects dressing sieve Divide the homogenization equipment of powder;The concentration or crystallizer is multiple-effect evaporation concentration or crystallization apparatus;The conversion mill For by transformation air-tightness ball mill, body be equipped with abrasive body inlet and outlet, powder import, liquid material import, gas vent, Slurry outlet, clean-drain mouth, gas sample mouth, slurry sample tap;Abrasive body be corundum ball, zirconia ball, porcelain ball, steel ball, One or more of stainless steel ball, alloying pellet.
CN201810867455.1A 2018-08-01 2018-08-01 Method and system for converting sodium-containing and fluorine-containing compounds in aluminum electrolysis hazardous waste residues Active CN109108049B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201810867455.1A CN109108049B (en) 2018-08-01 2018-08-01 Method and system for converting sodium-containing and fluorine-containing compounds in aluminum electrolysis hazardous waste residues

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201810867455.1A CN109108049B (en) 2018-08-01 2018-08-01 Method and system for converting sodium-containing and fluorine-containing compounds in aluminum electrolysis hazardous waste residues

Publications (2)

Publication Number Publication Date
CN109108049A true CN109108049A (en) 2019-01-01
CN109108049B CN109108049B (en) 2021-06-18

Family

ID=64863910

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201810867455.1A Active CN109108049B (en) 2018-08-01 2018-08-01 Method and system for converting sodium-containing and fluorine-containing compounds in aluminum electrolysis hazardous waste residues

Country Status (1)

Country Link
CN (1) CN109108049B (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110358581A (en) * 2019-08-16 2019-10-22 陕西延长石油(集团)有限责任公司 A kind of aqueous dregs of fat are granulated again the device and method of pyrolytic gasification
CN110470140A (en) * 2019-08-30 2019-11-19 王一浩 A kind of aluminium-scandium alloy smelting waste separation scandium oxide recovery furnace
CN113426807A (en) * 2021-06-29 2021-09-24 云南云铝润鑫铝业有限公司 Method for combined treatment and comprehensive utilization of resources of dangerous waste residues generated in aluminum electrolysis
CN113426808A (en) * 2021-06-29 2021-09-24 云南云铝润鑫铝业有限公司 Method for recovering fluoride salt from aluminum electrolysis overhaul residues through pressurized alkaline leaching
CN113429139A (en) * 2021-06-27 2021-09-24 浙江红狮环保股份有限公司 Method for cooperatively treating fluorine-containing inorganic compound by cement kiln

Citations (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB208712A (en) * 1922-12-21 1925-03-12 Aluminum Co Of America Improvements in or relating to methods of lining electrolytic cells for refining metals
GB997370A (en) * 1961-02-24 1965-07-07 Electro Chimie Metal Process for recovering fluorine values from the electrolytic production of aluminium
JPH072517A (en) * 1993-05-06 1995-01-06 Onoda Kagaku Kogyo Kk Production of anhydrous aluminum fluoride
CN1583301A (en) * 2004-05-24 2005-02-23 中国铝业股份有限公司 Harmless treating method for waste tank lining of aluminium electrolytic bath
CN101119943A (en) * 2005-02-16 2008-02-06 诺沃福特国际有限公司 Process and apparatus for converting spent potliners into a glass frit, and resulting products
CN101444660A (en) * 2008-12-30 2009-06-03 吴正建 Innocent treatment of cyanide and fluoride in solid waste residues and recycling process thereof
CN101804996A (en) * 2010-04-02 2010-08-18 北京矿冶研究总院 Method for recovering sodium fluoride from electrolytic aluminum waste cathode carbon block
CN102992299A (en) * 2012-12-04 2013-03-27 贵州铝城铝业原材料研究发展有限公司 High temperature calcination method of electrolytic aluminum cathode scrap residue
CN104768874A (en) * 2012-04-12 2015-07-08 科瑞瑟斯有限公司 Process and apparatus for obtaining material of value from a bauxite residue
CN105821445A (en) * 2016-05-27 2016-08-03 中南大学 Method for recycling carbon and electrolytes from waste cathode carbon block of aluminum electrolytic cell
CN205773365U (en) * 2016-04-12 2016-12-07 郑州鸿跃环保科技有限公司 A kind of aluminium electrolysis cell cathode carbon block reclaims the system of graphite
CN107282598A (en) * 2017-07-03 2017-10-24 李立安 A kind of aluminium cell discards the recoverying and utilizing method of cathode carbon pieces

Patent Citations (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB208712A (en) * 1922-12-21 1925-03-12 Aluminum Co Of America Improvements in or relating to methods of lining electrolytic cells for refining metals
GB997370A (en) * 1961-02-24 1965-07-07 Electro Chimie Metal Process for recovering fluorine values from the electrolytic production of aluminium
JPH072517A (en) * 1993-05-06 1995-01-06 Onoda Kagaku Kogyo Kk Production of anhydrous aluminum fluoride
CN1583301A (en) * 2004-05-24 2005-02-23 中国铝业股份有限公司 Harmless treating method for waste tank lining of aluminium electrolytic bath
CN101119943A (en) * 2005-02-16 2008-02-06 诺沃福特国际有限公司 Process and apparatus for converting spent potliners into a glass frit, and resulting products
CN101444660A (en) * 2008-12-30 2009-06-03 吴正建 Innocent treatment of cyanide and fluoride in solid waste residues and recycling process thereof
CN101804996A (en) * 2010-04-02 2010-08-18 北京矿冶研究总院 Method for recovering sodium fluoride from electrolytic aluminum waste cathode carbon block
CN104768874A (en) * 2012-04-12 2015-07-08 科瑞瑟斯有限公司 Process and apparatus for obtaining material of value from a bauxite residue
CN102992299A (en) * 2012-12-04 2013-03-27 贵州铝城铝业原材料研究发展有限公司 High temperature calcination method of electrolytic aluminum cathode scrap residue
CN205773365U (en) * 2016-04-12 2016-12-07 郑州鸿跃环保科技有限公司 A kind of aluminium electrolysis cell cathode carbon block reclaims the system of graphite
CN105821445A (en) * 2016-05-27 2016-08-03 中南大学 Method for recycling carbon and electrolytes from waste cathode carbon block of aluminum electrolytic cell
CN107282598A (en) * 2017-07-03 2017-10-24 李立安 A kind of aluminium cell discards the recoverying and utilizing method of cathode carbon pieces

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110358581A (en) * 2019-08-16 2019-10-22 陕西延长石油(集团)有限责任公司 A kind of aqueous dregs of fat are granulated again the device and method of pyrolytic gasification
CN110470140A (en) * 2019-08-30 2019-11-19 王一浩 A kind of aluminium-scandium alloy smelting waste separation scandium oxide recovery furnace
CN113429139A (en) * 2021-06-27 2021-09-24 浙江红狮环保股份有限公司 Method for cooperatively treating fluorine-containing inorganic compound by cement kiln
CN113426807A (en) * 2021-06-29 2021-09-24 云南云铝润鑫铝业有限公司 Method for combined treatment and comprehensive utilization of resources of dangerous waste residues generated in aluminum electrolysis
CN113426808A (en) * 2021-06-29 2021-09-24 云南云铝润鑫铝业有限公司 Method for recovering fluoride salt from aluminum electrolysis overhaul residues through pressurized alkaline leaching
CN113426808B (en) * 2021-06-29 2022-05-17 云南云铝润鑫铝业有限公司 Method for recovering fluoride salt from aluminum electrolysis overhaul residues through pressurized alkaline leaching
CN113426807B (en) * 2021-06-29 2022-05-17 云南云铝润鑫铝业有限公司 Method for combined treatment and comprehensive utilization of resources of dangerous waste residues generated in aluminum electrolysis

Also Published As

Publication number Publication date
CN109108049B (en) 2021-06-18

Similar Documents

Publication Publication Date Title
CN109047285A (en) Containing sodium, the method for transformation of fluorochemical and system in a kind of waste cathode of aluminum electrolytic cell carbon block
CN109108049A (en) Containing sodium, the method for transformation of fluorochemical and system in a kind of aluminium electroloysis dangerous waste slag
CN108941167A (en) Mechanochemistry conversion and recovery method in a kind of waste cathode of aluminum electrolytic cell carbon block containing sodium, fluorochemical
CN102515279B (en) Comprehensive extraction method of ferro-silico-aluminum in gangue
CN104445311B (en) Clean poly-generation preparation method for flyash with high-content silicon dioxide
CN108787718A (en) A kind of aluminium electroloysis is given up mechanochemistry conversion and recovery method in breeze containing sodium, fluorochemical
CN109108050A (en) Containing sodium, the method for transformation of fluorochemical and system in a kind of aluminium electroloysis slag from delining
CN109127655A (en) A kind of aluminium electroloysis is given up in breeze containing sodium, the method for transformation of fluorochemical and system
CN113426796A (en) Electrolytic aluminum overhaul slag, method for recycling overhaul slag leachate and application method of recycled materials
CN108584994A (en) A kind of method of lepidolite calcined by rotary kiln lithium carbonate
CN109108048A (en) Mechanochemistry conversion and recovery method in a kind of aluminium electrolysis anode breeze containing sodium, fluorochemical
US20220144658A1 (en) Method for preparing aluminum fluoride and aluminum oxide by decarburization and sodium removal of aluminum electrolysis carbon residue
CN109127657A (en) Mechanochemistry conversion and recovery method in a kind of aluminium electroloysis slag from delining containing sodium, fluorochemical
CN104263973B (en) The method being prepared APT by the many closed loops of tungsten mineral material
CN114031099A (en) Acidification roasting method for efficiently treating aluminum electrolysis solid waste
CN101987734A (en) Magnesite carbonization method for producing magnesium hydroxide and calcium carbonate product
CN1508092A (en) Method for preparing potash manure (kali salt) from potassium-rich rock using hydrothermal chemical reaction
CN104263975B (en) There is the tungsten mineral material metallurgical technology of multiple closed loop
CN113184890A (en) Method for preparing fluoride salt and lithium salt by using high-lithium electrolyte
CN106745124B (en) A kind of technique that aluminium hydroxide and concrete admixture are produced from Coaseries kaolin
CN109127656A (en) Mechanochemistry conversion and recovery method in a kind of aluminium electroloysis dangerous waste slag containing sodium, fluorochemical
CN110408790A (en) A kind of method that pressure leaching v-bearing steel slag produces vanadium product
CN115156238B (en) Comprehensive recycling method for aluminum electrolysis waste cathode carbon blocks and application thereof
CN104263976B (en) The tungsten mineral material metallurgical technology of omnidistance non-pollution discharge
CN103086433A (en) Method for preparing sodium dichromate by sodium-based molten salt oxidation continuous carbonization

Legal Events

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