CN109530387B - Harmless treatment process for electrolytic aluminum dross - Google Patents

Harmless treatment process for electrolytic aluminum dross Download PDF

Info

Publication number
CN109530387B
CN109530387B CN201811271941.3A CN201811271941A CN109530387B CN 109530387 B CN109530387 B CN 109530387B CN 201811271941 A CN201811271941 A CN 201811271941A CN 109530387 B CN109530387 B CN 109530387B
Authority
CN
China
Prior art keywords
aluminum dross
aluminum
reactant
catalyst
content
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.)
Active
Application number
CN201811271941.3A
Other languages
Chinese (zh)
Other versions
CN109530387A (en
Inventor
李振中
高峰
赵建辉
段中波
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.)
Gansu Dongxing Aluminium Co ltd
Original Assignee
Gansu Dongxing Aluminium Co ltd
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 Gansu Dongxing Aluminium Co ltd filed Critical Gansu Dongxing Aluminium Co ltd
Priority to CN201811271941.3A priority Critical patent/CN109530387B/en
Publication of CN109530387A publication Critical patent/CN109530387A/en
Application granted granted Critical
Publication of CN109530387B publication Critical patent/CN109530387B/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
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • B09B3/40Destroying solid waste or transforming solid waste into something useful or harmless involving thermal treatment, e.g. evaporation
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/006General arrangement of incineration plant, e.g. flow sheets
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/02Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment
    • F23G5/033Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment comminuting or crushing

Landscapes

  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Mechanical Engineering (AREA)
  • General Engineering & Computer Science (AREA)
  • Physics & Mathematics (AREA)
  • Thermal Sciences (AREA)
  • Electrolytic Production Of Metals (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

The invention discloses a harmless treatment process of electrolytic aluminum dross, belonging to the technical field of recycling of solid wastes in the aluminum electrolysis industry. The aluminum dross after being crushed and impurity removed is uniformly mixed with a catalyst (a mixture of potassium nitrate and sodium chloride) and a reactant (a mixture of orthocryolite and metallurgical-grade aluminum oxide), and when the aluminum dross is combusted in a combustion furnace at the temperature of 600-; the sodium chloride plays a role in promoting and catalyzing the decomposition of ammonium nitrate substances; the metallurgical-grade aluminum oxide can effectively adsorb melted cryolite and fluoride salt. By adopting the process, the carbon content in the residual ash of the aluminum dross after combustion is less than 3 percent, and the regenerated electrolyte is obtained by adjusting the molecular ratio; the content of fluoride salt in the combustion flue gas is less than 3mg/m3The content of dust particles is less than 20mg/m3The aluminum electrolysis fume purification system is connected to purify the aluminum electrolysis fume and then the aluminum electrolysis fume can be directly discharged into the atmosphere, thereby realizing the purpose of harmless treatment of the electrolytic aluminum scum.

Description

Harmless treatment process for electrolytic aluminum dross
Technical Field
The invention belongs to the technical field of recycling of solid wastes in the aluminum electrolysis industry, and particularly relates to a harmless treatment process of electrolytic aluminum dross.
Technical Field
At present, prebaked anode carbon blocks used in aluminum electrolysis cells are all formed by kneading and roasting carbon materials. During the aluminum electrolysis reaction, the generation of carbon slag in the liquid aluminum electrolyte is inevitable due to the heterogeneity of the carbon material in the anode carbon block. Carbon residue floating in the aluminum electrolyte, namely aluminum dross, can cause the anode effect of aluminum electrolysis, and simultaneously can increase the voltage of the aluminum electrolyte, reduce the current efficiency of the aluminum electrolysis and increase the power consumption per ton of aluminum.
Through analytical research, the main components of the aluminum dross are carbon powder, fluoride salt, metallic aluminum and a small amount of impurities, and the valuable components are cryolite (sodium hexafluoroaluminate), cryolite (sodium pentafluoroaluminate), carbon materials and metallic aluminum. Wherein, the carbon powder content in the aluminum dross is 30-50% and the fluoride salt content is 50-70% by mass percentage.
According to the national records of hazardous waste (No. 39 of the 2016 ministry of environmental protection), aluminum dross belongs to industrial hazardous waste, waste class HW48 (non-ferrous smelting waste), waste code: 321-025-48, hazard characteristics: and T. Fluoride salt contained in the aluminum dross pollutes the environment seriously and is one of important pollutants for national environmental protection key management and control.
At present, with the further implementation of the national environmental protection law, the treatment method aiming at the aluminum dross in the industry is mainly stockpiling, but the method has serious environmental pollution and high stockpiling cost. In view of this, some research institutions and enterprises are also conducting research and experiments on the harmless treatment of aluminum dross, but a process suitable for the harmless treatment of electrolytic aluminum dross has not yet been developed.
Disclosure of Invention
The invention aims to overcome the defects of the prior art and provides a harmless treatment process of electrolytic aluminum dross, which has the advantages of simple process, low cost and environmental friendliness.
The purpose of the invention is realized by the following technical scheme: a harmless treatment process of electrolytic aluminum dross specifically comprises the following steps:
(1) crushing electrolytic aluminum dross to the particle size of 0.1-0.25mm, then removing impurities by adopting a filter screen, wherein the aperture of the filter screen is 0.25-0.3mm, and the content of Fe element in the electrolytic aluminum dross after the impurities are removed is less than 0.3%;
(2) the method comprises the following steps of taking a mixture of potassium nitrate and sodium chloride as a catalyst, taking a mixture of orthocryolite and metallurgical-grade alumina as a reactant, and respectively crushing the catalyst and the reactant to obtain particles with the particle size of 0.1-0.25 mm;
(3) removing impurities from the aluminum dross in the step (1), and preparing the catalyst and the reactant in the step (2) into a uniform mixed material according to the mass ratio of 6-8: 0.7-1.3: 0.7-3.3;
(4) putting the mixed material in the step (3) into a combustion furnace, and combusting for 8-15min at 600-; the carbon content in the residual ash of the aluminum dross is less than 3 percent, and the fluoride salt content in the combustion flue gas is less than 3mg/m3The content of dust particles is less than 20mg/m3
(5) Introducing the combustion flue gas obtained in the step (4) into an aluminum electrolysis flue gas purification system for purification and then discharging the purified combustion flue gas into the atmosphere; the residual ash of the aluminum dross is determined by fluorescence analysis to determine NaF and AlF3By additional addition of AlF3Reacting NaF and AlF3The ratio of the amounts of the substances (A) to (B) is maintained at 2.1-2.3:1 to obtain a regenerated electrolyte.
Further, the mass ratio of potassium nitrate to sodium chloride in the catalyst is 7-9: 1-3, preferably 9: 1.
The mass ratio of the orthocryolite to the metallurgical-grade alumina in the reactant is 7-9: 1-3, and preferably 4: 1.
The invention has the beneficial effects that:
the invention uniformly mixes the aluminum dross after crushing and impurity removal with a certain proportion of catalyst (mixture of potassium nitrate and sodium chloride) and reactant (mixture of orthocryolite and metallurgical-grade aluminum oxide), and when the aluminum dross is combusted in a combustion furnace at the temperature of 600-:
(1) the potassium nitrate is decomposed to produce combustion-supporting oxygen, which can promote the carbon in the aluminum dross to be fully combusted.
(2) The sodium chloride plays a role in promoting and catalyzing the decomposition of ammonium nitrate substances.
(3) The reactant consists of orthocryolite and metallurgical-grade alumina, and can promote the generation of cryolite when the reactant is combusted at the temperature of 600-760 ℃, wherein the metallurgical-grade alumina can effectively adsorb melted cryolite and fluoride salt.
(4) By adopting the process, the carbon content in the residual ash of the aluminum dross after combustion is less than 3 percent, and the regenerated electrolyte is obtained by adjusting the molecular ratio; the content of fluoride salt in the combustion flue gas is less than 3mg/m3The content of dust particles is less than 20mg/m3Electrolysis of aluminumThe purified flue gas can be directly discharged into the atmosphere, thereby realizing the purpose of harmless treatment of the electrolytic aluminum dross.
Detailed Description
The process for detoxifying electrolytic aluminum dross according to the present invention will be described in further detail below with reference to specific examples.
In the following examples, the proportions of the respective mixtures are mass ratios, which are not specifically described.
Example 1
(1) Crushing electrolytic aluminum dross by using a ball mill until the particle size is 0.1mm, then removing impurities by using a 0.25m filter screen, wherein the content of Fe element in the electrolytic aluminum dross after the impurities are removed is 0.25%;
(2) a mixture of 73 percent of potassium nitrate and 27 percent of sodium chloride is used as a catalyst, a mixture of 70 percent of orthocryolite and 30 percent of metallurgical-grade alumina is used as a reactant, and the catalyst and the reactant are crushed by a ball mill until the particle size is 0.1 mm;
(3) conveying the aluminum dross subjected to impurity removal in the step (1), the catalyst and the reactant in the step (2) into a mixer through a conveyor, and preparing a uniform mixed material according to a mass ratio of 6: 0.7: 3.3;
(4) conveying the mixed material in the step (3) to a combustion furnace through a conveyor, and combusting for 8 min at 600 ℃ to obtain residual ash of aluminum dross and combustion flue gas; the carbon content in the residual ash of the aluminum dross is 2.7 percent, and the fluoride salt content in the combustion flue gas is 2.9mg/m3The content of dust particles is 17mg/m3
(5) Introducing the combustion flue gas obtained in the step (4) into an aluminum electrolysis flue gas purification system for purification and then discharging the purified combustion flue gas into the atmosphere; the residual ash of the aluminum dross is determined by fluorescence analysis to determine NaF and AlF3In a ratio of 2.5:1, and then by additional addition of AlF3Reacting NaF and AlF3The mass ratio of (a) to (b 2.2:1, a regenerated electrolyte consisting mainly of cryolite and alumina was obtained.
Example 2
(1) Crushing electrolytic aluminum dross by using a ball mill until the grain size is 0.25mm, then removing impurities by using a 0.3m filter screen, wherein the content of Fe element in the electrolytic aluminum dross after the impurities are removed is 0.27%;
(2) taking a mixture of 82% potassium nitrate and 19% sodium chloride as a catalyst, taking a mixture of 80% orthocryolite and 20% metallurgical-grade alumina as a reactant, and crushing the catalyst and the reactant to a particle size of 0.25mm through a ball mill;
(3) conveying the aluminum dross subjected to impurity removal in the step (1), the catalyst and the reactant in the step (2) into a mixer through a conveyor, and preparing a uniform mixed material according to a ratio of 7: 1: 3;
(4) conveying the mixed material in the step (3) to a combustion furnace through a conveyor, and combusting for 13min at 760 ℃ to obtain residual ash of aluminum dross and combustion flue gas; the carbon content in the residual ash of the aluminum dross is 2.8 percent, and the fluoride salt content in the combustion flue gas is 3mg/m3The content of dust particles is 19mg/m3
(5) Introducing the combustion flue gas obtained in the step (4) into an aluminum electrolysis flue gas purification system for purification and then discharging the purified combustion flue gas into the atmosphere; the residual ash of the aluminum dross is determined by fluorescence analysis to determine NaF and AlF3In a ratio of 2.4:1, and then by additional addition of AlF3Reacting NaF and AlF3The mass ratio of (a) to (b) was 2.3:1, resulting in a regenerated electrolyte composed mainly of cryolite and alumina.
Example 3
(1) Crushing electrolytic aluminum dross by using a ball mill until the particle size is 0.2mm, then removing impurities by using a 0.3m filter screen, wherein the content of Fe element in the electrolytic aluminum dross after the impurities are removed is 0.29%;
(2) taking a mixture of 81% potassium nitrate and 19% sodium chloride as a catalyst, taking a mixture of 85% orthocryolite and 15% metallurgical-grade alumina as a reactant, and crushing the catalyst and the reactant to a particle size of 0.2mm through a ball mill;
(3) conveying the aluminum dross subjected to impurity removal in the step (1), the catalyst and the reactant in the step (2) into a mixer through a conveyor, and preparing a uniform mixed material according to the ratio of 8: 1.2: 0.8;
(4) conveying the mixed material in the step (3) to a combustion furnace through a conveyor at 700 DEG CBurning for 15min to obtain residual ash of aluminum dross and burning smoke; the carbon content in the residual ash of the aluminum dross is 2.5 percent, and the fluoride salt content in the combustion flue gas is 2.9mg/m3The content of dust particles is 14mg/m3
(5) Introducing the combustion flue gas obtained in the step (4) into an aluminum electrolysis flue gas purification system for purification and then discharging the purified combustion flue gas into the atmosphere; the residual ash of the aluminum dross is determined by fluorescence analysis to determine NaF and AlF3In a ratio of 2.5:1, and then by additional addition of AlF3Reacting NaF and AlF3The mass ratio of (a) to (b 2.1:1, a regenerated electrolyte consisting mainly of cryolite and alumina was obtained.

Claims (4)

1. A process for the harmless treatment of electrolytic aluminum dross, comprising the steps of:
(1) crushing electrolytic aluminum dross to the particle size of 0.1-0.25mm, then removing impurities by adopting a filter screen, wherein the aperture of the filter screen is 0.25-0.3mm, and the content of Fe element in the electrolytic aluminum dross after the impurities are removed is less than 0.3%;
(2) the method comprises the following steps of taking a mixture of potassium nitrate and sodium chloride as a catalyst, taking a mixture of orthocryolite and metallurgical-grade alumina as a reactant, and respectively crushing the catalyst and the reactant to obtain particles with the particle size of 0.1-0.25 mm;
(3) removing impurities from the aluminum dross in the step (1), and preparing the catalyst and the reactant in the step (2) into a uniform mixed material according to the mass ratio of 6-8: 0.7-1.3: 0.7-3.3;
(4) spraying the mixed material in the step (3) into a combustion furnace, and combusting for 8-15min at 600-; the carbon content in the residual ash of the aluminum dross is less than 3 percent, and the fluoride salt content in the combustion flue gas is less than 3mg/m3The content of dust particles is less than 20mg/m3
(5) Introducing the combustion flue gas obtained in the step (4) into an aluminum electrolysis flue gas purification system for purification and then discharging the purified combustion flue gas into the atmosphere; the residual ash of the aluminum dross is determined by fluorescence analysis to determine NaF and AlF3By additional addition of AlF3Reacting NaF and AlF3Of (2) aMaintaining the quantity ratio at 2.1-2.3:1 to obtain regenerated electrolyte;
the mass ratio of orthocryolite to metallurgical-grade alumina in the reactant is 7-9: 1-3.
2. The process of claim 1 for the innocent treatment of electrolytic aluminum dross, wherein: the mass ratio of potassium nitrate to sodium chloride in the catalyst is 7-9: 1-3.
3. The process of claim 2, wherein the process comprises: the mass ratio of potassium nitrate to sodium chloride in the catalyst is 9: 1.
4. The process of claim 1 for the innocent treatment of electrolytic aluminum dross, wherein: the mass ratio of orthocryolite to metallurgical-grade alumina in the reactant is 4: 1.
CN201811271941.3A 2018-10-29 2018-10-29 Harmless treatment process for electrolytic aluminum dross Active CN109530387B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201811271941.3A CN109530387B (en) 2018-10-29 2018-10-29 Harmless treatment process for electrolytic aluminum dross

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201811271941.3A CN109530387B (en) 2018-10-29 2018-10-29 Harmless treatment process for electrolytic aluminum dross

Publications (2)

Publication Number Publication Date
CN109530387A CN109530387A (en) 2019-03-29
CN109530387B true CN109530387B (en) 2022-02-25

Family

ID=65845424

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201811271941.3A Active CN109530387B (en) 2018-10-29 2018-10-29 Harmless treatment process for electrolytic aluminum dross

Country Status (1)

Country Link
CN (1) CN109530387B (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114309006B (en) * 2021-12-13 2022-11-25 生态环境部华南环境科学研究所 Process and treatment equipment for harmless recycling of barium slag
CN115365269A (en) * 2022-08-26 2022-11-22 甘肃东兴铝业有限公司 Method for treating electrolytic aluminum waste material

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1055768A (en) * 1991-05-22 1991-10-30 抚顺铝厂 Fluidized-bed roasting treatment method for aluminium electrolytic flue ash
JPH0929209A (en) * 1995-07-24 1997-02-04 Nippon Technic Kk Pollution free treatment method for aluminum residual ash
CN101381647A (en) * 2008-10-21 2009-03-11 梁宴邱 High-efficiency coal-saving burning additive
CN106247340A (en) * 2016-10-08 2016-12-21 淄博海慧工程设计咨询有限公司 A kind of processing method and processing device of electrolytic aluminium carbon slag

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1055768A (en) * 1991-05-22 1991-10-30 抚顺铝厂 Fluidized-bed roasting treatment method for aluminium electrolytic flue ash
JPH0929209A (en) * 1995-07-24 1997-02-04 Nippon Technic Kk Pollution free treatment method for aluminum residual ash
CN101381647A (en) * 2008-10-21 2009-03-11 梁宴邱 High-efficiency coal-saving burning additive
CN106247340A (en) * 2016-10-08 2016-12-21 淄博海慧工程设计咨询有限公司 A kind of processing method and processing device of electrolytic aluminium carbon slag

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
氯化钠的助燃性对煤矿***作业安全性的影响;刘祖亮;《中国学术期刊》;19860501;第24-26页 *

Also Published As

Publication number Publication date
CN109530387A (en) 2019-03-29

Similar Documents

Publication Publication Date Title
CN211247720U (en) Plasma fusion vitrification device and waste incineration fly ash treatment system
US5723097A (en) Method of treating spent potliner material from aluminum reduction cells
JP7204156B2 (en) Pre-dechlorination and sintering process for highly chlorinated metallurgical waste and incineration fly ash
EP0542404A1 (en) Detoxification of aluminum spent potliner
Zhao et al. Recycling and utilization of spent potlining by different high temperature treatments
CN109530387B (en) Harmless treatment process for electrolytic aluminum dross
CN1233478C (en) Method of treating waste matter using plasma electric arc technology and its device
CN110976481B (en) Copper-containing hazardous waste treatment process
CN105457972A (en) Aluminum electrolysis waste slot lining hazard-free treatment method for carrying out wet strengthening for defluorination after heat treatment
CN103343363A (en) Method for producing electrolyte for electrolytic aluminum
CN107338358A (en) Heavy metal in flying ash is Ji the removal methods of bioxin
CN101440500A (en) Method for processing waste cathode carbon block from aluminum cell overhaul residue
CN112958587A (en) Method and device for co-processing and utilizing aluminum ash and overhaul slag
CN114349477B (en) High chromium slag detoxification formula and synergistic lightweight aggregate production process
CN112317517A (en) Pretreatment system and method suitable for co-processing electrolytic aluminum overhaul residues in cement kiln
CN115921501A (en) Secondary aluminum ash treatment method for removing salt and fixing fluorine by wet and dry combined nitrogen and fluorine removal
CN112456797B (en) Glass body preparation method and harmless disposal method of waste incineration fly ash and aluminum cell overhaul residues
CN108531737B (en) Comprehensive treatment system for copper-containing sludge and circuit board
CN111454008A (en) Zero-landfill technical method for waste incineration fly ash
CN101307905B (en) Carbon product calcining furnace flue gas cleaning treatment process
CN214270947U (en) System for harmless, resourceful processing of aluminium industry waste cathode carbon piece
WO2019214507A1 (en) Comprehensive processing method and comprehensive processing system for copper-containing sludge and circuit boards
CN111551027A (en) Smelting furnace and smelting method for recycling electrolyte from aluminum electrolysis carbon slag
CN112538557A (en) System and method for harmless and resource treatment of aluminum industry waste cathode carbon blocks
CN113020218A (en) Method for treating waste cell lining of aluminum cell

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