CN208750736U - The system of cement bypass of kiln incineration disposal aluminium cell slag from delining - Google Patents

The system of cement bypass of kiln incineration disposal aluminium cell slag from delining Download PDF

Info

Publication number
CN208750736U
CN208750736U CN201821361216.0U CN201821361216U CN208750736U CN 208750736 U CN208750736 U CN 208750736U CN 201821361216 U CN201821361216 U CN 201821361216U CN 208750736 U CN208750736 U CN 208750736U
Authority
CN
China
Prior art keywords
slag
delining
kiln
cement
aluminium cell
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
CN201821361216.0U
Other languages
Chinese (zh)
Inventor
肖喜才
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.)
Changsha Zhongsi Environmental Protection Technology Co., Ltd
Original Assignee
Changsha Silicon Cement Technology Development 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 Changsha Silicon Cement Technology Development Co Ltd filed Critical Changsha Silicon Cement Technology Development Co Ltd
Priority to CN201821361216.0U priority Critical patent/CN208750736U/en
Application granted granted Critical
Publication of CN208750736U publication Critical patent/CN208750736U/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Landscapes

  • Gasification And Melting Of Waste (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

The utility model provides a kind of system of cement bypass of kiln incineration disposal aluminium cell slag from delining, including sequentially connected slag from delining crushing system, cement bypass of kiln incineration system, conversion dealkalize system, cement kiln recycling treatment system, the cement bypass of kiln incineration system includes that method includes floated combination incinerator.The utility model designs special floated combination incinerator as calciner for the characteristic of aluminium cell slag from delining, not only simple in equipment is unique, easy to operate, low cost, and pass through the Particular crafts such as two segments combined cyclone firing, oxygen-enriched combusting, it may insure the completely burned for being graphitized useless carbon electrode, this system, which is able to achieve, disposes aluminium cell overhaul slag harmlessness, recycling, ultimateization, high-volume.

Description

The system of cement bypass of kiln incineration disposal aluminium cell slag from delining
Technical field
The utility model relates to Aluminium Industry hazardous waste disposal technical fields, and in particular to a kind of cement bypass of kiln The system of incineration disposal aluminium cell slag from delining.
Background technique
Aluminium cell slag from delining is the solid waste that aluminium cell is periodically discharged, the institute removed when being to electrolytic cell overhaul There is the general designation of waste and old inner lining material and carbonaceous electrode material.Wherein, carbonaceous material includes waste cathode carbon block and anode carbon granule;It gives up resistance to Fiery thermal insulation material includes the combined mixture such as refractory brick, insulating brick, Impervious Materials and thermal insulation board.One during aluminium cell overhaul As electrolytic cell do not discarded into flame-proof thermal insulation material and carbonaceous material etc. separately store, but useless carbonaceous electrode material and useless fire resisting are protected The mixture of adiabator.It must carry out large repairs within aluminium cell every 3~5 years, it is left will to generate 25kg for every 1 ton of electrolytic aluminium of production according to statistics Right aluminium cell slag from delining.Currently, China's accumulation stockpiling aluminium cell slag from delining is more than 7,000,000 tons, while increasing aluminium electricity year newly Groove overhaul slag is solved about more than 1,000,000 tons.
Aluminium cell slag from delining is beige solid cake mass, and bulk granularity is 30~40cm, and easy fragmentation is difficult to grind Carefully, there is certain viscosity and be varied with the length of its service life.Aluminium cell slag from delining chemical composition be C, NaF, Na3AIF6、A1203、Si02Material account for 90% or more and a small amount of other impurities.It is found by X- diffraction analysis, waste tank lining Object phase composition it is more complex, XRD spectrum in visible more fluoride.Fluoride in aluminium cell slag from delining with NaF, Na3AIF6And AlF3Form exists, and mostlys come from infiltration and erosion of the electrolyte to cathode inner lining.Furthermore in waste tank lining also Contain more graphite and β-NaAl11Ol7,β-NaAl11Ol7The production generated for flame-proof thermal insulation material and the electrolysis qualitative response penetrated into Object, slow graphitization of the graphite from carbonaceous material under electrolysis temperature.Due to each electrolytic aluminium factory current capacity, liner knot Structure, inner lining material type, Electrolytic conditions, operating duty, groove life difference are larger.The concrete composition thousand of each waste lining is poor Ten thousand are not, and content of fluoride therein also has difference certainly.Studies have shown that in the waste lining removed, generally based on carbonaceous material, Account for about 50% or so, mean calorie is greater than 8000kJ/kg;Furthermore contain ice crystal, sodium fluoride, nepheline, β-aluminium oxide, on a small quantity α-aluminium oxide, aluminium carbide, aluminium nitride, alfer and micro cyanide (about 0.2%).
Fluoride in aluminium cell slag from delining is with NaF, AlF3And Na3AlF6Presence, meet water hydrolysis generate F-, and release Severe toxicity HF is released, harmfulness is very big.Cyanide in slag from delining is with NaCN and Na (FeCN6) exist, meet the CN that water dissolution generates-, Also hypertoxic HCN can be released.Especially HCN can cause on a small quantity people poisoning and in seconds death, have skin abrasion wound into Enter blood or can make one to be poisoned into respiratory tract.Leachate fluorine content is up to 2800mg/L, CN in aluminium cell slag from delining- Content is up to 10~40mg/L (note: F-And CN-Content because of groove profile, service life, cell lining structure, operating procedure not It is same and different), substantially exceed national " one leaching characteristic identification of hazardous waste judging standard " standard.Meanwhile in slag from delining Metallic aluminium, AlN, Al2C3Equal hydrolysis may also generate NH3、H2、CH4Gas, these gases may cause burning and explosion thing Therefore.If carried out harmless treatment not in time, the harm to environment will be serious and long-term.Due to its fluorine containing noxious material Compound and Cyanide Leaching risk are defined as dangerous solid waste (classification: HW48) in " National Hazard waste register ", are Country prohibites the I class waste arbitrarily abandoned.
The country starts late to the research of aluminium cell slag from delining, and under the conditions of the prior art, electrolytic aluminium factory mostly uses greatly dew It is stacked or the method process aluminum electrolytic groove overhaul slag of soil-burial.A large amount of soil are not only taken up with land-fill method disposition slag from delining Ground, and soluble fluoride therein, cyanide can also flow into rivers with rainwater, permeate the ground contaminated soil and underground water, Surface water causes high risks to ecological environment around, human health and animal and plant growth.This disposal options are tantamount to bury One new environomental pollution source.
There is presently no heavy industrialization application, Shao Shuoqi to the harmless treatment of aluminium cell slag from delining for aluminium electrolysis enterprise Industry carried out some small-scale tests, and wherein floatation restores the utilities such as carbon and HF, ice crystal and has by burning disposal The experiment of the methods of evil substance achieves certain success, but since aluminium cell slag from delining is difficult to grinding and fluoride, cyaniding The characteristics such as object is readily volatilized are difficult to control in disposition, in the large amount of sewage newly increased containing harmful substances such as fluorine ions, make At the risk of secondary pollution, it is unable to reach innoxious, minimizing, ultimateization disposition target.And disposition investment is big, disposing capacity It is small, processing cost is high, less economical, project sustainability is bad.
It is exactly under cement kiln high-temperature and strong alkaline condition using cement kiln synergic processing aluminium cell slag from delining slag from delining High temperature incineration disposition is carried out, so that it is eliminated toxicity, and be fired into water using the calorific value of its carbonaceous material and other element components Mud clinker.This kind of mode disposes thorough, small investment, without secondary pollution.Innoxious, recycling, ultimateization disposition may be implemented. But largely disposed on single cement kiln slag from delining there is still a need for solve following problems:
1. process aluminum electrolytic groove overhaul slag may cause the Na for participating in cement kiln2O and CaF2It is excessive, thus will cause cement Kiln system Coating clogging etc. endangers long-term safety operation risk, it is also possible to adversely affect to cement quality.
2. since waste cathode carbon block is largely graphitized charcoal, while being also doped with ice crystal class electrolyte, flammability It can be excessively poor, it may be difficult to completely burned.
3. the graphite, alkali metal, fluorine and silicon carbide in aluminium electroloysis slag from delining are all good resource substances, how to select These utilities are therefrom extracted as far as possible, recycle or made good use of to easy disposal options, be develop a circular economy it is basic, It should be paid attention in cement kiln synergic processing.
CN107401746A discloses the processing system and its processing method of a kind of aluminium cell slag from delining, by by aluminium electroloysis It is mixed after groove overhaul slag is broken with lime fluorine fixing material, mixture is by grinding and powder is selected to recycle to obtain powder in cement kiln After being burnt, harm is completely eliminated, so that aluminium electroloysis overhaul slot loses toxicity completely.The aluminium cell that the documents provide Overhaul slag disposal system and method are that the powder after powder is carried out to burning removal toxicity in cement kiln, but this in cement The mode handled in kiln has that burning is insufficient, it is understood that there may be influences the operating of cement kiln long-term safety and influences cement Clinker quality can not achieve the recycling to useful resources in aluminium cell slag from delining, and project does not meet recycling economy development requirement, The Technical Economy of project is bad.
Utility model content
The technical problem to be solved by the present invention is to provide a kind of cement bypass of kiln incineration disposal aluminium cell slag from delining System, specifically in cement bypass of kiln setting suspension combined type incinerator by ultra-fine slag from delining in high temperature, oxygen-enriched and longer Incineration disposal is carried out under the conditions of residence time etc., enables the carbonaceous material full combustion in slag from delining, and the heat after burning is logical Flue gas is crossed to enter in cement kiln as the energy.Cyanide is oxidized elimination poison in the case where high temperature is aerobic and alkaline condition in slag from delining Property, a small amount of HF gas evaporation is solidified into stable CaF by CaO a large amount of in cement kiln into flue gas2Solid, to eliminate poison Property.Metallic aluminium, AlN, Al in slag from delining2C3Deng being oxidized into solid Al at high temperature2O3With gas N2、CO2, will not generate NH3、H2、 CH4Gas.Clinker after slag from delining burns is converted into aqueous stall fluorite ore agent by alkali liquid washing, and obtains To NaOH (caustic soda) byproduct.Aluminium cell overhaul slag harmlessness, recycling, ultimateization, high-volume are disposed to realize.
In order to solve the above-mentioned technical problem, the utility model uses following technical scheme:
The purpose of harmlessness disposing of aluminium cell slag from delining is the toxic hazard for eliminating the noxious materials such as fluorine and cyanogen, as far as possible Using the beneficiating ingredient of its high added value, strive turning waste into wealth.Its treatment principle is: in the premise for meeting environmental protection and safety in production Under, select the disposal options being simple and efficient, it is ensured that treatment process is simple, reliable, operating cost is low, realizes energy efficiency, comprehensive Utilization benefit is good and meets the direction of sustainable development.The basic ideas of the utility model are:
It is difficult to the characteristics of burning and containing toxic fluoride and cyanide for graphitized charcoal in aluminium cell slag from delining, Cement bypass of kiln is arranged floated combination incinerator and carries out high temperature incineration to slag from delining, and slag from delining fine particle high degree of dispersion suspends In high temperature gas phase, by providing oxygen-enriched atmosphere, extends the modes such as residence time, keep the carbonaceous material in slag from delining abundant Burning, the heat after burning are entered in cement kiln by flue gas as the energy.
Cyanide (NaCN) is oxidized elimination toxicity, a small amount of HF gas in the case where high temperature is aerobic and alkaline condition in slag from delining It is evaporated in flue gas and stable CaF is solidified by CaO a large amount of in cement kiln2Solid, to eliminate toxicity.Gold in slag from delining Belong to aluminium, AlN, Al2C3Deng being oxidized into solid Al at high temperature2O3With gas N2、CO2, NH will not be generated3、H2、CH4Gas, from And safety accident can be prevented.
Clinker after slag from delining burns is converted by alkali liquid washing and CaO containing 20~50%CaF2Fluorite mineralization Agent, and obtain NaOH (caustic soda) byproduct and completely eliminate secondary pollution to realize harmless treatment aluminium cell slag from delining Risk, environmental-friendly, safety in production.
The concrete scheme to solve the above problems is as follows:
Firstly, the utility model provides a kind of system of cement bypass of kiln incineration disposal aluminium cell slag from delining, it is specific to wrap It includes: sequentially connected slag from delining crushing system, cement bypass of kiln incineration system, conversion dealkalize system, cement kiln recycling treatment System;Device in whole system is all made of sealing device, and suction machine is arranged and is used to form tiny structure, prevents dust from drifting;
The cement bypass of kiln incineration system includes floated combination incinerator, the floated combination incinerator mainly by Eddy flow portion, boiling portion and cyclone separator composition;
Eddy flow portion includes top horn mouth, spin chamber, lower part horn mouth, and the bell-mouthed top in top is equipped with the first outlet air Mouthful, spin chamber is equipped with tangential air inlet mechanism, and tangential air inlet mechanism includes first air inlet tangentially-arranged with spin chamber, first into The air inlet pipeline in air port is equipped with first charging aperture;
Cyclone separator includes separator body, and the top of separator body is equipped with the second air outlet, and bottom is equipped with second Discharge port;
Boiling portion includes the boiling-house, fluidized bed, aeration tank set gradually from top to bottom, and the fluidized bed includes air point The bottom of fabric swatch and the fluidizing agent layer being arranged on dispersion plate, the aeration tank is equipped with the first slag notch, the air Distribution grid is equipped with the second slag notch, and first slag notch is connect with the second slag notch by a Y-shaped clinker overflow pipe;Institute The side for stating aeration tank is additionally provided with combustion air inlet, and the top of the boiling-house is exhanst gas outlet;
Eddy flow portion is connected to the first air outlet of cyclone separator by air hose;The bell-mouthed bottom in eddy flow subordinate portion and boiling Exhanst gas outlet connection at the top of portion;Second discharge port of cyclone separator is connected in boiling-house by feeder pipe.
When work, first air inlet in eddy flow portion is used to input the high temperature gas flow into spin chamber, i.e. circulating flue gas;First Air outlet rises flue gas to cyclone separator for being discharged;First charging aperture is for inputting smashed slag from delining powder;
Second air outlet of cyclone separator is for being discharged the flue gas after cyclonic separation dedusting;Second discharge port is used for cigarette Dust after gas separation, which is discharged, is delivered in boiling-house high temperature incineration again by feeder pipe.
Further,
The Y-shaped clinker overflow pipe, the third branch pipe of the first branch pipe, the second branch pipe and lower part including top, the One branch pipe is connect with the first slag notch, and the second branch pipe passes through aeration tank and protruded into boiling-house by the second slag notch.
When work, first slag notch in boiling portion falls into inflation from dispersion plate gap for being discharged after slag from delining burning Lime-ash in case;Second slag notch is for being discharged the lime-ash that slag from delining is fallen in after boiling-house completely burned on dispersion plate; Lime-ash imports the third branch pipe discharge of lower part by first, second branch pipe on Y-shaped clinker overflow pipe top.
Further,
The dispersion plate is the plate for being evenly arranged several mesh.
Further,
The fluidizing agent layer with a thickness of 10~50cm;The fluidizing agent is the lime stone rubble of 3~5mm.
Further,
The spin chamber is cylindrical structure, and draw ratio is 3~10.
Further,
The top horn mouth is back taper hopper construction, and angle of taper is 45 °~75 °.
Further,
The lower part horn mouth is positive broach hopper structure, and angle of taper is 45 °~75 °.
Further,
The boiling-house is the cylindrical structure that top is equipped with back taper exhanst gas outlet, and draw ratio is 3~10.
Further,
It leaks out in order to prevent, the feeder pipe is equipped with high temperature weighted valve.
Further,
The eddy flow portion, boiling portion casing include steel chassis ontology, the adiabator layer that is covered on casing ontology With the fire brick layer being covered on adiabator layer.When specifically manufacturing, i.e., patch plus thermal insulation material on steel chassis ontology It builds refractory material again afterwards, and refractory material may be selected according to substance performance in kiln.
Preferably,
The floated combination incinerator further includes inspection platform, stair and fixed bracket, will be suspended by fixed bracket Formula combination incinerator is fixed on building.
Further,
The outer wall of the spin chamber is equipped with the first observation door;The outer wall of the boiling-house is equipped with the second observation door, institute State the first observation door, the second observation door is respectively used to observation spin chamber, the indoor working condition of boiling.
Further,
The second observation door is also used to launch fuel, guarantees full combustion;And for launching fluidizing agent and setting Igniter.
Further,
The igniter is manual igniting device or automatic ignition system.
Preferably,
Several maintenance doors, pressure instrumentation mounting hole, temperature inspection is set as needed in the floated combination incinerator Survey instrument mounting hole.
Further,
The slag from delining crushing system includes crushing system and grinding system, and the crushing system includes sequentially connected one Grade crusher, secondary breaker and raw material repository;The grinding system include sequentially connected milling equipment, select powder equipment and The discharge port of powder repository, raw material repository is connected by the feed inlet of metering matching mechanism and milling equipment.
Further,
The level-one crusher, secondary breaker are all made of jaw crusher, impact fine crusher, pillar fine crusher, circular cone The combination of one or more of crusher, oppositely rolling roller crusher.
Further,
The milling equipment uses the combination of one or more of roll squeezer, vertical mill, Raymond mill, ball mill.
Further,
It is described that powder equipment is selected to select powder using V-type powder concentrator, centrifugation powder concentrator, cyclone separator, dynamic powder concentrator, O-sep The combination of one or more of machine.
Further,
The conversion dealkalize system includes sequentially connected mixing agitator, ball mill by wet process, kiln basin, the mixing Agitating device is equipped with lime-ash entrance, and the lime-ash entrance is connected with the floated Y-shaped clinker overflow pipe for combining incinerator;It is described Mixing agitator is additionally provided with auxiliary agent entrance;Auxiliary agent entrance is connect with converting additive storehouse;
The conversion dealkalize system further includes filter device, and filter device is equipped with slurry feed inlet, serum outlet and solid The discharge port of material outlet, slurry feed inlet and kiln basin connects, and serum outlet passes through piping connection to settling tank, solid matter Outlet is connected to fluorite ore agent slag storehouse by conveyer;The settling tank is equipped with upper clear supernate outlet and bottom insoluble matter goes out Mouthful, upper clear supernate outlet is connected to storehouse formula rapid steamer, and insoluble matter outlet in bottom is connected to filter device.
Preferably,
The mixing agitator is one or more of groups of biaxial rneader, rotary beater, wheel rolling homogenizer It closes.
Preferably, the filter device is one or more of plate and frame filter press, bag type filtering machine, spiral filter Combination.
Further,
The cement kiln recycling treatment system, including sequentially connected raw material mixing system, cement slurry preparation system, New dry process rotary kiln system, new dry process rotary kiln system include dry-process cement rotary kiln dore furnace, cement rotary kiln and cement Kiln kiln tail smoke-box, the feed inlet of slag from delining batch bin is connect with the solid slag storehouse of conversion dealkalize system in raw material mixing system.
The processing method of the system of above-mentioned cement bypass of kiln incineration disposal aluminium cell slag from delining, specifically includes following step It is rapid:
S1, slag from delining is crushed and grinding: aluminium cell slag from delining enters slag from delining crushing system and is crushed, grinding, selects powder, obtains To satisfactory slag from delining powder;
S2, cement bypass of kiln burn disinfection: slag from delining powder made from step S1 is sent to suspension through metering conveyor structure Formula combines incinerator, 800-1150 DEG C of high temperature incineration, and the cyanide (NaCN) in slag from delining is in the case where high temperature is aerobic and alkaline condition It is oxidized elimination toxicity, in the high-temperature flue gas after a small amount of HF gas evaporation to burning, high-temperature blower is used after cyclone dust collection It is sent into triple air hose of cement kiln and enters cement kiln, stable CaF is solidified by CaO a large amount of in cement kiln2Solid, to eliminate Poison;Meanwhile subsequent processing is directly sent to from the clinker that floated combination incinerator is drawn off and carries out conversion dealkalize disposition;
S3, conversion dealkalize: the clinker and converting additive, NaOH solution mixing and ball milling drawn off from floated combination incinerator turns Slurry is obtained after change, caustic soda byproduct is made in the slurries after slurries filtration, and fluorite ore agent slag is made in filtered solid matter;
S4, cement kiln recycling treatment: fluorite ore agent slag made from step S3 is required according to cement kiln using mineralizer Ingredient and calorific value require design mixture proportion, pass through together with cement raw material raw material mixing system ingredient, then by cement give birth to Cement raw meal is made in material preparation system, enters back into new dry process rotary kiln system through high-temperature calcination into clinker;
Above-mentioned ingredient proportion is that fluorite ore agent slag accounts for the 0.5~3% of cement raw material total amount;
In above-mentioned treatment process, all materials transhipment, crush, storage process seals progress, all devices in system, Solid material send the conveyings such as skewed slot, chain-linked conveyer to set using belt conveyor, elevator, screw conveyor, wind between feed bin Standby connection, and suction machine is set and is used to form tiny structure;After all gas carries out purified treatment with air hose feeding sack cleaner Discharge.
Further,
The crushing and grinding process of step S1 is specific as follows:
Aluminium cell slag from delining is delivered to level-one crusher by plate-type feeding, and the broken material of level-one is defeated through belt Machine is sent to be delivered to secondary breaker, the boosted machine of the material after two-stage crushing, which is delivered in raw material repository, to be stored, and two Realize that the slag from delining by feed size no more than 500mm is crushed to no more than 10mm after grade is broken;
Then by after the metering feeding mechanism metering feeding of raw material repository bottom storehouse with conveying equipment by broken object Material is delivered to milling equipment, through the laggard selected powder equipment of grinding selects powder again, and qualified material powder is not conformed to using the storage of powder repository Lattice material returns to milling equipment grinding;By grinding, select powder repeatedly to recycle after obtain the aluminium cell slag from delining of 300~500 mesh Powder.
Further,
The level-one crusher, secondary breaker are all made of jaw crusher, impact fine crusher, pillar fine crusher, circular cone The combination of one or more of crusher, oppositely rolling roller crusher;Level-one feed of crusher granularity control be not more than 500mm, two Grade crusher discharging size controlling is being not more than 10mm.
Further,
The milling equipment is combined using one or more of roll squeezer, vertical mill, Raymond mill, ball mill.
Further,
It is described that powder equipment is selected to select powder using V-type powder concentrator, centrifugation powder concentrator, cyclone separator, dynamic powder concentrator, O-sep The combination of one or more of machine.
Further,
The burning process of floated combination incinerator is specific as follows in step S2:
First charging aperture of the slag from delining powder in the middle part of floated combination incinerator accompanies what the first air inlet tangentially entered High temperature gas flow (circulating flue gas) is sent to together in the spin chamber in eddy flow portion, and the little particle powder in slag from delining powder is with eddy flow The air-flow that indoor rotation rises enters cyclone separator by the first air outlet at the top of eddy flow portion, after cyclone separator separates Powder be discharged through the second discharge port of its bottom and along feeder pipe enter boiling Indoor Combustion;High-temperature flue gas after separation is from rotation The second air outlet at the top of wind separator is aspirated by high-temperature blower and is discharged, a portion again from the first air inlet tangentially into Enter in spin chamber, realization recycles;And it is got rid of under the centrifugal force effect of bulky grain powder swirling eddy in rotating room therein It is slid downwards to edge along the inner wall of spin chamber, the lower part horn mouth in eddy flow portion sweeps along part to return in the ascending air of necking Into spin chamber, partially falls in boiling-house and burn;Return to the indoor powder of eddy flow part under the action of swirling eddy again Separate into cyclone separator with high temperature gas flow (circulating flue gas) and boiling-house burning is entered by feeder pipe or directly from rotation Flow chamber falls into boiling Indoor Combustion, so recycles, until slag from delining powder full combustion;Due to entering the indoor slag from delining that boils Powder is evenly distributed in it on fluidizing agent under the action of air-flow, combustion air from combustion air inlet through aeration tank from The dispersion plate of fluidized bed is blown into, and is entered in furnace by the gap between fluidizing agent, and slag from delining powder is made to form boiling-like State, which is suspended in air-flow, completes burning, and burned ashes are discharged by Y-shaped clinker overflow pipe, as dregs of incinerator.
In above-mentioned burning process, the indoor air-flow of eddy flow is by the circulating flue gas that enters along a tangential direction from the first air inlet It (high temperature gas flow) and is made of the flue gas that boiling portion high temperature incineration slag from delining powder is discharged;Since the air-flow that tangent line enters can will revolve It flows indoor air-flow traffic direction and changes into rotation ascending fashion, so as to extend air-flow runing time, also increase material With the time of gas heat exchange, the slag from delining powder in swirling eddy is made effectively to be spread and be fully warmed-up, guarantees it sufficiently Burning.To prevent from leaking out, high temperature weighted valve is set in the middle part of feeder pipe;
Further,
It slags tap after the burning of slag from delining powder from the lime-ash that dispersion plate gap is fallen into aeration tank from the first of aeration tank Mouth discharge;First branch pipe on the first slag notch connection Y-shaped clinker overflow pipe top;The lime-ash being deposited in after burning on fluidized bed It is discharged by the second slag notch on dispersion plate;Second branch pipe on the second grey cinder notch connection Y-shaped clinker overflow pipe top; Then lime-ash is imported third branch pipe and is discharged out of the furnace by the first branch pipe, the second branch pipe.
Further,
In step S2, fluidizing agent generally takes the limestone sand of 3~8mm, be conducive to CaO solidification burn in there may be Sour gas.
Further,
In step S2, combustion air is the oxygen-enriched air of industrial oxygen-enriched generator gas supply, to guarantee to enter boiling portion Air in oxygen content reach 25~30%.
Further,
In step S2, the middle part eddy flow elegance cyclic high-temperature wind tangentially entered from the first air inlet, using high temperature wind Power traction enters;The flue gas a part being discharged from the second air outlet at the top of cyclone separator is recycled, and another part introduces cement Kiln kiln tail smoke-box is further burnt, and recycles air hose and the flue of cement kiln tail smoke-box is gone to be equipped with high temperature air quantity tune It saves valve and controls air quantity.
Further,
It is specific as follows that step S3 converts dealkalize process:
The clinker (200 DEG C or so) drawn off from floated combination incinerator is by clinker: the mass ratio of transforming agent is 1:(0.2 ~1) converting additive is added in ratio, adds NaOH solution is stirred with mixing agitator, then is ground with ball mill by wet process Mill and conversion, the slurry after grinding is stored in kiln basin, and is continuously added 40~100 DEG C of hot water and continued to complete conversion reaction; Solid matter and slurries is obtained by filtration by filter device in slurry after conversion reaction is complete, and slurries enter settling tank;Solids Matter obtains the clean fluorite ore agent slag of comparison after the washing filtering of multiple clear water, is stored in fluorite ore agent slag storehouse stand-by; Cleaning solution adjusts workshop section before alkali concentration returns and uses or enter settling tank to handle as cleaning solution;Slurries are in standing, sedimentation separation Afterwards, upper clear supernate is directly evaporated with storehouse formula rapid steamer for lye and is concentrated to get caustic soda byproduct;Bottom insoluble matter returns Filter device carries out solid-liquor separation.
Further,
In step S3, kiln tail low-temperature flue gas waste heat and waste heat hair that heat source needed for spent liquor evaporation is concentrated is discarded using cement kiln Low Temperature Steam waste heat after electricity.
Further,
In step S3, the vapor that storehouse formula rapid steamer is evaporated is condensed using condenser, and obtained 40 DEG C or more condense Water is returned to be used as hot water needed for conversion reaction.
Further,
The vapor generated in the conversion reaction of step S3 is all sent to condenser with suction machine extraction and handles together.
Further,
In step S3, the mixing agitator be biaxial rneader, rotary beater, wheel roll over homogenizer one kind or Several combinations.
Further,
In step S3, the filter device is one or more of plate and frame filter press, band filter, spiral filter Combination.
Further,
In step S3, NaOH concentration of lye is not higher than 200mol/L;Outsourcing, production a period of time are used when producing for the first time After caustic soda byproduct made from step S3 itself can be used, part more than needed is re-used as byproduct sale.
Further,
Converting additive in step S3 is lime stone, lime, gypsum, carbide slag, desulfurized gypsum, a kind of or several in calcium chloride The combination of kind.
During step S4: CaF2As cement kiln mineralizer and admittedly it is fused to clinker, and it is wherein imperfect combustion Complete carbon dust all thoroughly burns at a high temperature of 1450~1550 DEG C in cement rotary kiln, the refractory brick powder based on silicon carbide It is further oxided under the conditions of high-temperature alkaline again, not oxidized a small amount of residue all fuses into clinker, other components (CaO、SiO2、 Al2O3And Fe2O3Deng) all as cement component.
Innoxious, recycling the final disposal of aluminium cell slag from delining may be implemented by the utility model, this is practical It is novel to have the advantages that
1, the utility model is to provide at a kind of cement kiln collaboration high-volume burning disposal aluminium cell slag from delining recycling Reason scheme, using this programme by eliminating its toxic hazard, the utility model energy for the processing of aluminium cell slag from delining high temperature incineration It economizes on resources, reduces energy consumption, saves production cost, meet the requirement developed a circular economy with sustainable development.
1. fluorine and aluminium in waste residue become the base stock of cement, in general, 1 ton of slag from delining slag can produce 0.4~ 0.6t contains 20~50%CaF2Fluorite ore agent.
2. the whole burning conversions of charcoal energy in waste residue are the energy needed for heat becomes manufacture of cement, general processing is per ton Aluminium cell slag from delining can save 0.3~0.4 ton of coal.
3. the influence of high-alkali raw material that mass disposal slag from delining may cause to cement kiln can not only be eliminated, and can be from It proposes to be worth higher soda bath in waste residue, in general, disposition available 100~200kg caustic soda (the solid-state meter of 1t slag from delining It calculates).
2, the utility model carries out harmless conversion to aluminium cell slag from delining by the method for science and system, and waste residue is located in advance It all operates under Sealing Arrangement and subnormal ambient in reason and cement pulverizing course, and is handled using high-effective dust-removing equipment, There is no dust pollution;It burns and waste water, exhaust gas and the available recycling of waste residue and effective benefit during disposal of resources With no secondary emission completely eliminates the possibility of secondary pollution.The corrosivity such as issuable a small amount of HF are strong in burning simultaneously Sour gas can be absorbed completely under cement kiln CaO strong alkaline condition to be solidified into CaF2 solid matter and enters clinker, no It can externally discharge.It is realized and is recycled by condensing recovery after all water vapour evaporations, do not need externally to discharge.All waste residues are complete Portion is used for cement producting material, gets utilization.
3, the present invention bypasses burning mode using cement bypass of kiln, and graphitized cathode carbon block is by fine-grinding and is suspending Can according to need the setting residence time in formula combination incinerator, oxygen-enriched air is added by heat, meet high temperature needed for it and Oxygen-enriched combusting condition compares complete oxidation burning to realize.Meanwhile floated combination incinerator is burned into the heat more than needed generated Amount is absorbed by cement kiln, energy saving;The exhaust gas of generation enters the processing of cement kiln high-temperature strong basicity system, thoroughly eliminates trend of environmental protection Danger.Aqueous slkali is concentrated by evaporation for the low-temperature flue gas after cogeneration using cement kiln, is not required to increase energy consumption.
4, the utility model uses unique technological equipment for material characteristic, can organize enlarged industry raw completely It produces:
1. the utility model is used as the special floated combination incinerator of characteristic design of aluminium cell slag from delining and forges Equipment is burnt, not only simple in equipment is unique, easy to operate, low cost, and passes through two segments combined cyclone firing, oxygen-enriched combustion The Particular crafts such as burning, it can be ensured that be graphitized the completely burned of useless carbon electrode.
2. the utility model, which is directed to, uses storehouse formula rapid steamer using low-temperature flue gas waste heat evaporated salt water, change rapid steamer structure letter It is single, by exhaust gas volumn it is big, resistance is small, can be with plural serial stage, evaporation efficiency is high, without secondary pollution.
3. the conversion mill that the utility model is used as using ball mill by wet process, using mature broken and milling equipment, technology Reliably.
Detailed description of the invention
In order to illustrate the embodiment of the utility model or the technical proposal in the existing technology more clearly, below will be to embodiment Or attached drawing needed to be used in the description of the prior art is briefly described, it should be apparent that, the accompanying drawings in the following description is only It is some embodiments of the utility model, for those of ordinary skill in the art, in the premise not made the creative labor Under, it is also possible to obtain other drawings based on these drawings.
Fig. 1 is the integrated stand composition of the utility model cement bypass of kiln incineration disposal aluminium cell overhaul slag system;
Fig. 2 is the process flow chart of the utility model cement bypass of kiln incineration disposal aluminium cell slag from delining;
Fig. 3 is the overall structure diagram of the floated combination incinerator of the utility model;
Fig. 4 cuts open for the tangential air inlet mechanism in the utility model eddy flow portion to structural schematic diagram;
Fig. 5 is the structural scheme of mechanism of dispersion plate;
Fig. 6 is casing structure schematic diagram;
Fig. 7 is Y-shaped clinker overflow pipe attachment structure schematic diagram;
Above-mentioned appended drawing reference:
111, level-one crusher;112, secondary breaker;113, raw material repository;13, matching mechanism is measured;121, grinding Equipment;122, powder equipment is selected;123, powder repository;
21, eddy flow portion;22, cyclone separator;23, boiling portion;
201, steel shell body;202, adiabator layer;203, refractory material layer;
211, spin chamber;212, top horn mouth;213, lower part horn mouth;214, the first air outlet;215, the first air inlet Mouthful;216, first charging aperture;217, the first observation door;
221, cyclone separator ontology;222, the second discharge port;223, the second air outlet;224, high temperature weighted valve;225, Feeder pipe;
231, boiling-house;232, exhanst gas outlet;233, dispersion plate;234, combustion air inlet;235, Y-shaped clinker Overflow pipe;236, the second observation door;237, aeration tank;238, the first slag notch;2331, the second slag notch;2351, first Pipe;2352, the second branch pipe;2353, third branch pipe;
24, fixed bracket;
301, mixing agitator;302, ball mill by wet process;303, kiln basin;304, filter device;305, settling tank; 306, storehouse formula rapid steamer;307, condenser;305, pond;309, caustic soda library;310, fluorite ore agent slag storehouse;
401, cement kiln dore furnace;402, cement kiln tail smoke-box;403, cement rotary kiln;
5, converting additive library;6, clinker storehouse;7, industrial oxygenerating device;8, high-temperature blower;
C1~C5, the first order to level V cyclone preheater.
Specific embodiment
Utility model is further illustrated below with reference to examples and drawings, but is not limited to the model of the utility model It encloses.
As shown in figs. 1 to 6, what the utility model provided a kind of cement bypass of kiln incineration disposal aluminium cell slag from delining is System, specifically includes: sequentially connected slag from delining crushing system, cement bypass of kiln incineration system, conversion dealkalize system, cement kiln money Source system;Device in whole system is all made of sealing device, and suction machine is arranged and is used to form tiny structure;
As shown in figure 4, the cement bypass of kiln incineration system includes floated combination incinerator, the floated combination is burnt Furnace is burnt mainly to be made of eddy flow portion, boiling portion and cyclone separator;
Eddy flow portion 21 includes top horn mouth 212, spin chamber 211, lower part horn mouth 213, the top of top horn mouth 212 Equipped with the first air outlet 214, spin chamber 211 is equipped with tangential air inlet mechanism, and tangential air inlet mechanism includes tangentially setting with spin chamber 211 The air inlet pipeline of the first air inlet 215 set, the first air inlet 215 is equipped with first charging aperture 216;
Cyclone separator 22 includes separator body 221, and the top of separator body 221 is equipped with 223 bottom of the second air outlet Portion is equipped with the second discharge port 222;
Boiling portion 23 includes boiling-house 231, fluidized bed, the aeration tank 237 set gradually from top to bottom, the fluidized bed packet The fluidizing agent layer for including dispersion plate 233 and being arranged on dispersion plate 233, in the present embodiment, the thickness of fluidizing agent layer Degree control is in 10~50cm;Fluidizing agent uses partial size for the lime stone rubble of 3~5mm.
The bottom of aeration tank 237 is equipped with the first slag notch 238, and dispersion plate 233 is equipped with the second slag notch 2331, the One slag notch 238 is connect with the second slag notch 2331 by a Y-shaped clinker overflow pipe 235;The side of aeration tank 237 is additionally provided with Combustion air inlet 234, the top of boiling-house 231 are exhanst gas outlet 232;
Eddy flow portion 21 is connected to cyclone separator 22 by the first air outlet 214;The lower part horn mouth 213 in eddy flow portion 21 Bottom is connected to the exhanst gas outlet 232 at 23 top of boiling portion;Second discharge port 222 of cyclone separator 22 passes through feeder pipe 225 It is connected in boiling-house 231;Feeder pipe 225 is equipped with high temperature weighted valve 224.
When work, first air inlet 215 in eddy flow portion 21 is used to input the high temperature gas flow into spin chamber 211, that is, recycles Flue gas;First air outlet 214 rises flue gas to cyclone separator 22 for being discharged;After first charging aperture 216 is for inputting crushing Slag from delining powder;
Second air outlet 223 of cyclone separator 22 is for being discharged the flue gas after cyclonic separation dedusting;Second discharge port 222 High temperature incineration again is delivered in boiling-house 231 by feeder pipe 225 for the dust discharge after separating flue gas.
In the present embodiment, Y-shaped clinker overflow pipe 235, the first branch pipe 2351, the second branch pipe 2352 including top and The third branch pipe 2353 of lower part, the first branch pipe 2351 are connect with the first slag notch 238, and the second branch pipe 2352 passes through aeration tank 237 And it is protruded into boiling-house 231 by the second slag notch 2331.
When work, first slag notch 238 in boiling portion 23 is for being discharged after slag from delining burns from 233 gap of dispersion plate Fall into the lime-ash in aeration tank 237;Second slag notch 2331 falls in sky after 231 completely burned of boiling-house for slag from delining to be discharged Lime-ash on gas distribution grid 233;Lime-ash passes through the first branch pipe 2351, second branch pipe 2352 on 235 top of Y-shaped clinker overflow pipe The third branch pipe 2353 for importing lower part is discharged.
As shown in figure 5, dispersion plate 235 is the circular plate for being evenly arranged several mesh in the present embodiment.
Spin chamber 211 in the present embodiment use draw ratio for 5 cylindrical structure, as other preferred embodiments, Draw ratio can control according to actual needs 3~10.
Top horn mouth 212 is back taper hopper construction, and angle of taper is 60 °, as other preferred embodiments, cone Shape angle can be controlled according to actual needs at 45 °~75 °.
Lower part horn mouth 213 is positive broach hopper structure, and angle of taper is 60 °, as other preferred embodiments, cone Shape angle can be controlled according to actual needs at 45 °~75 °.
Boiling-house 231 is the cylindrical structure that top is equipped with that the draw ratio of back taper exhanst gas outlet 232 is 5, as other Preferred embodiment, draw ratio can control according to actual needs 3~10.
Eddy flow portion 21, boiling portion 23 casing include steel chassis ontology 201, the heat preservation that is covered on casing ontology 201 Material layer 202 and the fire brick layer 203 being covered on adiabator layer 202.When specifically manufacturing, i.e., in steel chassis ontology Refractory material is built after upper patch plus thermal insulation material again, and refractory material may be selected according to substance performance in kiln.
Floated combination incinerator in the present embodiment is additionally provided with fixed bracket 24, by fixed bracket 24 by floated group Incinerator is closed to be fixed on building.
The outer wall of spin chamber 211 is equipped with the first observation door 217;The outer wall of boiling-house 231 is equipped with the second observation door 236, the first observation door 217, second observes door 236 and is respectively used to observation spin chamber 211, the working condition in boiling-house 231;The Two observation doors 236 can be used for launching fuel, guarantee full combustion;And for igniter to be arranged, the igniter is Manual igniting device or automatic ignition system use manual firing in the present embodiment.
The slag from delining crushing system includes crushing system and grinding system, and the crushing system includes being sequentially connected level-one Crusher 111, secondary breaker 112 and raw material repository 113;The grinding system includes sequentially connected milling equipment 121, powder equipment 122 and powder repository 123 are selected, the discharge port of raw material repository 113 passes through metering matching mechanism 13 and grinding The feed inlet of equipment 121 connects.
Level-one crusher 111 in the present embodiment preferably uses jaw crusher, and secondary breaker 112 is preferably using to roller Formula crusher, as other preferred embodiment level-one crushers 111, secondary breaker 112 can also using jaw crusher, Impact fine crusher, pillar fine crusher, gyratory crusher, one or more of oppositely rolling roller crusher combination or it is broken with jaw The combination of broken machine, oppositely rolling roller crusher.
Milling equipment 121 in the present embodiment uses Raymond mill, as other preferred embodiments, moreover it is possible to use roll-in The combination of one or more of machine, vertical mill, ball mill or the combination of itself and Raymond mill.
Powder equipment 122 is selected to select powder equipment using cyclone separator using described in the present embodiment, it is preferred real as other Apply mode, moreover it is possible to using the group of one or more of V-type powder concentrator, centrifugation powder concentrator, dynamic powder concentrator, O-sep powder concentrator Conjunction or the combination of itself and cyclone separator.
The conversion dealkalize system includes sequentially connected mixing agitator 301, ball mill by wet process 302, kiln basin 303, mixing agitator 301 is equipped with lime-ash entrance, the lime-ash entrance and the floated Y-shaped clinker overflow for combining incinerator Pipe 235 connects;Mixing agitator 301 is additionally provided with auxiliary agent entrance;Auxiliary agent entrance is connect with converting additive storehouse 5;
The conversion dealkalize system further includes filter device 304, and filter device 304 is equipped with slurry feed inlet, serum outlet And solid matter outlet, slurry feed inlet are connect with the discharge port of kiln basin 303, serum outlet passes through piping connection to settling tank 305, solid matter outlet passes through piping connection to solid slag storehouse 310;It is insoluble with bottom that settling tank 305 is equipped with upper clear supernate outlet Object outlet, upper clear supernate outlet are connected to storehouse formula rapid steamer 306, and insoluble matter outlet in bottom is connected to filter device 304.
In the present embodiment, mixing agitator 301 uses biaxial rneader, as other preferred embodiments, moreover it is possible to adopt The combination of one or more of homogenizer or the combination of itself and biaxial rneader are rolled over rotary beater, wheel.
In the present embodiment, filter device 304 uses plate and frame filter press, as other preferred embodiments, moreover it is possible to use bag The combination of one or more of formula filter, spiral filter or the combination of itself and plate and frame filter press.
The cement kiln recycling treatment system, including sequentially connected raw material mixing system, cement slurry preparation system, New dry process rotary kiln system, new dry process rotary kiln system include dry-process cement rotary kiln dore furnace 401, cement rotary kiln 402, with And cement kiln tail smoke-box 403, the solid slag of the feed inlet of slag from delining batch bin and conversion dealkalize system in raw material mixing system Storehouse 310 connects.
The processing method of the system of above-mentioned cement bypass of kiln incineration disposal aluminium cell slag from delining provided in this embodiment, tool Body is as follows:
S1, slag from delining is crushed and grinding:
Aluminium cell slag from delining is delivered to level-one crusher 111 by plate-type feeding, and the broken material of level-one is percutaneous Band conveyer be delivered to secondary breaker 112, the boosted machine of the material after two-stage crushing be delivered in raw material repository 113 into Row storage realizes that the slag from delining by feed size no more than 500mm is crushed to no more than 10mm after two-stage is broken;
Then by after 13 metering feeding of metering matching mechanism of 113 bottom storehouse of raw material repository with conveying equipment will it is broken after Material be delivered to milling equipment 121, through the laggard selected powder equipment 122 of grinding select powder again, qualified material powder is stored using powder Library 123 stores, and unqualified material returns to 121 grinding of milling equipment;By grinding, select powder repeatedly to recycle after obtain 300~500 mesh Aluminium cell slag from delining powder.
S2, cement bypass of kiln burn disinfection:
Slag from delining powder made from step S1 is sent to floated combination incinerator through metering conveyor structure, 800~1150 DEG C high temperature incineration, cyanide (NaCN) in slag from delining are oxidized elimination toxicity in the case where high temperature is aerobic and alkaline condition, a small amount of In high-temperature flue gas after HF gas evaporation to burning, triple air hose of cement kiln is sent into using high-temperature blower after cyclone dust collection and is entered Cement kiln is solidified into stable CaF by CaO a large amount of in cement kiln2Solid, to eliminate poison;Meanwhile it being burnt from floated combination The clinker that burning furnace is drawn off is directly sent to subsequent processing and carries out conversion dealkalize disposition;
The burning process of floated combination incinerator is specific as follows:
First charging aperture 216 retinue first air inlet 215 of the slag from delining powder in the middle part of floated combination incinerator is tangential The high temperature gas flow (circulating flue gas) of entrance is sent to together in the spin chamber 211 in eddy flow portion 21, the little particle in slag from delining powder Powder enters cyclone separator by first air outlet 215 at 211 top of eddy flow portion with the air-flow for rotating rising in spin chamber 211 22, the powder after the separation of cyclone separator 22, which enters through the second discharge port 222 discharge of its bottom along feeder pipe 225, to boil Burning in room 231;High-temperature flue gas after separation is taken out from second air outlet 223 at 22 top of cyclone separator by high-temperature blower Suction goes out, and a portion tangentially enters in spin chamber 211 from the first air inlet 215 again, and realization recycles;And it is therein It is downward along the inner wall of spin chamber 211 that edge is thrown under the centrifugal force effect of bulky grain powder swirling eddy in rotating room 211 It slides, the lower part horn mouth 213 in eddy flow portion 21 sweeps along part to return in spin chamber 211 in the ascending air of necking, partially falls It is burned in boiling-house 231;The powder in spin chamber 211 is returned to again under the action of swirling eddy partially with high temperature gas flow (circulating flue gas) enters cyclone separator 22 and carries out separation by feeder pipe 225 into the burning of boiling-house 231 or directly from eddy flow Room 211 falls into burning in boiling-house 231, so recycles, until slag from delining powder full combustion;Due to entering in boiling-house 231 Slag from delining powder be evenly distributed in it on fluidizing agent under the action of air-flow, combustion air is from combustion air inlet 234 are blown into through aeration tank 237 from the dispersion plate 233 of fluidized bed, and are entered in furnace by the gap between fluidizing agent, make Slag from delining powder forms fluidized state and is suspended in completion burning in air-flow, and burned ashes pass through Y-shaped clinker overflow pipe 235 Discharge, as dregs of incinerator.
In above-mentioned burning process, air-flow in spin chamber 211 is by the circulation that enters along a tangential direction from the first air inlet 215 The flue gas composition of flue gas (high temperature gas flow) and the discharge of 23 high temperature incineration slag from delining powder of boiling portion;The air-flow entered due to tangent line Air-flow traffic direction in spin chamber 211 can be changed into rotation ascending fashion, so as to extend air-flow runing time, also just increased The time for having added material Yu gas heat exchange makes the slag from delining powder in swirling eddy effectively be spread and be fully warmed-up, and protects Demonstrate,prove its full combustion.
Bottom combustion air is the oxygen-enriched air of industrial oxygen-enriched generator gas supply, to guarantee to enter the air in boiling portion Middle oxygen content reaches 25~30%.The middle part eddy flow elegance circulated air that first air inlet 215 enters, is introduced using blower; It recycles air hose and cement kiln flue gas pipeline is gone to be equipped with high-temp air-quantity regulating valve and control air quantity.From the first air inlet 215 tangentially into The middle part eddy flow elegance cyclic high-temperature wind entered, is introduced using high-temperature blower;The second outlet air from 22 top of cyclone separator Flue gas a part of 223 discharge of mouth are recycled, and another part introduces cement kiln tail smoke-box 402 and further burnt, and follow Bostle pipe and the flue for removing cement kiln tail smoke-box 402 are equipped with high-temp air-quantity regulating valve and control air quantity.
S3, conversion dealkalize: from the floated clinker (200 DEG C or so) that draws off of combination incinerator be stored in clinker storehouse 6 to With then in clinker: the mass ratio of transforming agent is 1:(0.2~1) ratio converting additive is added, adds NaOH solution with mixed Expect that agitating device 301 stirs, then ground and converted with ball mill by wet process 302, the slurry after grinding is stored in kiln basin 303 It is interior, and continuously add 40~100 DEG C of hot water and continue to complete conversion reaction;Slurry after conversion reaction is complete, passes through filter device 304 are obtained by filtration solid matter and slurries, and slurries enter settling tank 305;Solid matter obtains after the washing filtering of multiple clear water Compare clean fluorite ore agent slag to be stored in fluorite ore agent slag storehouse 310 for use;Cleaning solution adjusts work before alkali concentration returns Duan Zuowei cleaning solution is handled using or into settling tank 305;Slurries are being stood, after sedimentation separation, and upper clear supernate is that lye is direct It is evaporated with storehouse formula rapid steamer 306 and is concentrated to get caustic soda byproduct;It is solid that bottom insoluble matter returns the progress liquid of filter device 304 Separation.
In the present embodiment, kiln tail low-temperature flue gas waste heat and waste heat that heat source needed for spent liquor evaporation is concentrated uses cement kiln to discard Low Temperature Steam waste heat after power generation.The vapor that storehouse formula rapid steamer 306 is evaporated is condensed using condenser 307, and obtained 40 DEG C or more water condensate storage return in pond 308 and used as hot water needed for conversion reaction.The water generated in conversion reaction steams Gas is all sent to condenser 307 with suction machine extraction and handles together.
NaOH concentration of lye needed for converting is not higher than 200mol/L;Outsourcing, production a period of time are used when producing for the first time After caustic soda byproduct made from step S3 itself can be used, part more than needed is re-used as byproduct sale.Converting additive selects stone Lime stone, lime, gypsum, carbide slag, desulfurized gypsum, combination one or more of in calcium chloride.
S4, cement kiln recycling treatment: the ingredient and calorific value required according to cement kiln using mineralizer requires design cooperation Than fluorite ore agent slag made from step S3 is pressed the 0.5~3% of cement raw material total amount, passes through raw material together with cement raw material It is milled into cement raw meal, subsequently into new dry process rotary kiln dore furnace 401 through high-temperature calcination at clinker;Entering water Before stall dore furnace 401, cement raw meal is preheated by C1~C5 five-stage cyclone preheater, the mistake of high-temperature calcination Cheng Zhong, the CaF in fluorite ore agent slag2As cement kiln mineralizer and admittedly it is fused to clinker, and it is wherein imperfect combustion complete Carbon dust in cement rotary kiln 403 at a high temperature of 1450~1550 DEG C all thoroughly burn, the refractory brick based on silicon carbide Powder is further oxided under the conditions of high-temperature alkaline again, and not oxidized a small amount of residue all fuses into clinker, other components (CaO、SiO2、Al2O3And Fe2O3Deng) all as cement component.
In above-mentioned treatment process, all materials transhipment, crush, storage process seals progress, all devices in system, Solid material send the conveyings such as skewed slot, chain-linked conveyer to set using belt conveyor, elevator, screw conveyor, wind between feed bin Standby connection, and suction machine is set and is used to form tiny structure;After all gas carries out purified treatment with air hose feeding sack cleaner Discharge.
Innoxious, recycling the final disposal of aluminium cell slag from delining may be implemented by the utility model, this is practical It is novel to have the advantages that
1, the utility model is to provide at a kind of cement kiln collaboration high-volume burning disposal aluminium cell slag from delining recycling Reason scheme, using this programme by eliminating its toxic hazard, the utility model energy for the processing of aluminium cell slag from delining high temperature incineration It economizes on resources, reduces energy consumption, saves production cost, meet the requirement developed a circular economy with sustainable development.
1. fluorine and aluminium in waste residue become the base stock of cement, in general, 1 ton of slag from delining slag can produce 0.4~ 0.6t contains 20~50%CaF2Fluorite ore agent.
2. the whole burning conversions of charcoal energy in waste residue are the energy needed for heat becomes manufacture of cement, general processing is per ton Aluminium cell slag from delining can save 0.3~0.4 ton of coal.
3. the influence of high-alkali raw material that mass disposal slag from delining may cause to cement kiln can not only be eliminated, and can be from It proposes to be worth higher soda bath in waste residue, in general, disposition available 100~200kg caustic soda (the solid-state meter of 1t slag from delining It calculates).
2, the utility model carries out harmless conversion to aluminium cell slag from delining by the method for science and system, and waste residue is located in advance It all operates under Sealing Arrangement and subnormal ambient in reason and cement pulverizing course, and is handled using high-effective dust-removing equipment, There is no dust pollution;It burns and waste water, exhaust gas and the available recycling of waste residue and effective benefit during disposal of resources With no secondary emission completely eliminates the possibility of secondary pollution.The corrosivity such as issuable a small amount of HF are strong in burning simultaneously Sour gas can be absorbed completely under cement kiln CaO strong alkaline condition to be solidified into CaF2 solid matter and enters clinker, no It can externally discharge.It is realized and is recycled by condensing recovery after all water vapour evaporations, do not need externally to discharge.All waste residues are complete Portion is used for cement producting material, gets utilization.
3, the present invention bypasses burning mode using cement bypass of kiln, and graphitized cathode carbon block is by fine-grinding and is suspending Can according to need the setting residence time in formula combination incinerator, oxygen-enriched air is added by heat, meet high temperature needed for it and Oxygen-enriched combusting condition compares complete oxidation burning to realize.Meanwhile floated combination incinerator is burned into the heat more than needed generated Amount is absorbed by cement kiln, energy saving;The exhaust gas of generation enters the processing of cement kiln high-temperature strong basicity system, thoroughly eliminates trend of environmental protection Danger.Aqueous slkali is concentrated by evaporation for the low-temperature flue gas after cogeneration using cement kiln, is not required to increase energy consumption.
4, the utility model uses unique technological equipment for material characteristic, can organize enlarged industry raw completely It produces:
1. the utility model is used as the special floated combination incinerator of characteristic design of aluminium cell slag from delining and forges Equipment is burnt, not only simple in equipment is unique, easy to operate, low cost, and passes through two segments combined cyclone firing, oxygen-enriched combustion The Particular crafts such as burning, it can be ensured that be graphitized the completely burned of useless carbon electrode.
2. the utility model, which is directed to, uses storehouse formula rapid steamer using low-temperature flue gas waste heat evaporated salt water, change rapid steamer structure letter It is single, by exhaust gas volumn it is big, resistance is small, can be with plural serial stage, evaporation efficiency is high, without secondary pollution.
3. the conversion mill that the utility model is used as using ball mill by wet process, using mature broken and milling equipment, technology Reliably.
Basic principles, main features, and advantages of the present invention has been shown and described above.Current row The technical staff of industry is described in above embodiments and description it should be appreciated that the present utility model is not limited to the above embodiments Only illustrate the principles of the present invention, the utility model can also on the premise of not departing from the spirit and scope of the utility model There are various changes and modifications, these various changes and improvements fall within the scope of the claimed invention.The utility model is wanted Protection scope is asked to be defined by appended claims and its equivalent.

Claims (10)

1. the system of cement bypass of kiln incineration disposal aluminium cell slag from delining, which is characterized in that specifically include: sequentially connected big Repair slag crushing system, cement bypass of kiln incineration system, conversion dealkalize system, cement kiln recycling treatment system;In whole system Device be all made of sealing device, and suction machine is set and is used to form tiny structure;
The cement bypass of kiln incineration system includes floated combination incinerator, and the floated combination incinerator is mainly by eddy flow Portion, boiling portion and cyclone separator composition;
Eddy flow portion includes top horn mouth, spin chamber, lower part horn mouth, and the bell-mouthed top in top is equipped with the first air outlet, rotation Flow chamber is equipped with tangential air inlet mechanism, and tangential air inlet mechanism includes first air inlet tangentially-arranged with spin chamber, the first air inlet Air inlet pipeline be equipped with first charging aperture;
Cyclone separator includes separator body, and the top of separator body is equipped with the second air outlet, and bottom is equipped with the second discharging Mouthful;
Boiling portion includes the boiling-house, fluidized bed, aeration tank set gradually from top to bottom, and the fluidized bed includes dispersion plate With the fluidizing agent layer being arranged on dispersion plate, the bottom of the aeration tank is equipped with the first slag notch, the air distribution Plate is equipped with the second slag notch, and first slag notch is connect with the second slag notch by a Y-shaped clinker overflow pipe;It is described to fill The side of gas tank is additionally provided with combustion air inlet, and the top of the boiling-house is exhanst gas outlet;
Eddy flow portion is connected to the first air outlet of cyclone separator by air hose;The bell-mouthed bottom in eddy flow subordinate portion and boiling portion are pushed up The exhanst gas outlet in portion is connected to;Second discharge port of cyclone separator is connected in boiling-house by feeder pipe.
2. the system of cement bypass of kiln incineration disposal aluminium cell slag from delining according to claim 1, which is characterized in that
The Y-shaped clinker overflow pipe, the third branch pipe of the first branch pipe, the second branch pipe and lower part including top, first Pipe is connect with the first slag notch, and the second branch pipe passes through aeration tank and protruded into boiling-house by the second slag notch.
3. the system of cement bypass of kiln incineration disposal aluminium cell slag from delining according to claim 1 or 2, feature exist In,
The spin chamber is cylindrical structure, and draw ratio is 3~10;
The top horn mouth is back taper hopper construction, and angle of taper is 45 °~75 °;
The lower part horn mouth is positive broach hopper structure, and angle of taper is 45 °~75 °;
The boiling-house is the cylindrical structure that top is equipped with back taper exhanst gas outlet, and draw ratio is 3~10;The air point Fabric swatch is the circular plate for being evenly arranged several mesh.
4. the system of cement bypass of kiln incineration disposal aluminium cell slag from delining according to claim 1, which is characterized in that
The eddy flow portion, boiling portion casing include steel chassis ontology, the adiabator layer being covered on casing ontology and cover Cover the fire brick layer on adiabator layer.
5. the system of cement bypass of kiln incineration disposal aluminium cell slag from delining according to claim 3, which is characterized in that
The outer wall of the spin chamber is equipped with the first observation door;The outer wall of the boiling-house is equipped with the second observation door, and described the Two observation place be arranged igniter.
6. the system of cement bypass of kiln incineration disposal aluminium cell slag from delining according to claim 1, which is characterized in that
The slag from delining crushing system includes crushing system and grinding system, and the crushing system includes that sequentially connected level-one is broken Broken machine, secondary breaker and raw material repository;The grinding system includes sequentially connected milling equipment, selects powder equipment and powder The discharge port of repository, raw material repository is connected by the feed inlet of metering matching mechanism and milling equipment.
7. the system of cement bypass of kiln incineration disposal aluminium cell slag from delining according to claim 6, which is characterized in that
The level-one crusher, secondary breaker are all made of jaw crusher, impact fine crusher, pillar fine crusher, cone crusher The combination of one or more of machine, oppositely rolling roller crusher;
The milling equipment uses the combination of one or more of roll squeezer, vertical mill, Raymond mill, ball mill;
It is described to select powder equipment using in V-type powder concentrator, centrifugation powder concentrator, cyclone separator, dynamic powder concentrator, O-sep powder concentrator One or more of combinations.
8. the system of cement bypass of kiln incineration disposal aluminium cell slag from delining according to claim 1, which is characterized in that institute Stating conversion dealkalize system includes sequentially connected mixing agitator, ball mill by wet process, kiln basin, and the mixing agitator is set There is lime-ash entrance, the lime-ash entrance is connected with the floated slag notch for combining incinerator;The mixing agitator is additionally provided with Auxiliary agent entrance;Auxiliary agent entrance is connect with converting additive storehouse;
The conversion dealkalize system further includes filter device, and filter device is equipped with slurry feed inlet, serum outlet and solid matter The discharge port of outlet, slurry feed inlet and kiln basin connects, and serum outlet passes through piping connection to settling tank, solid matter outlet Fluorite ore agent slag storehouse is connected to by conveyer;The settling tank is equipped with upper clear supernate outlet and the outlet of bottom insoluble matter, on Portion's purified liquor outlet is connected to storehouse formula rapid steamer, and insoluble matter outlet in bottom is connected to filter device.
9. the system of cement bypass of kiln incineration disposal aluminium cell slag from delining according to claim 8, which is characterized in that
The mixing agitator is the combination of one or more of biaxial rneader, rotary beater, wheel rolling homogenizer;
The filter device is the combination of one or more of plate and frame filter press, bag type filtering machine, spiral filter.
10. the system of cement bypass of kiln incineration disposal aluminium cell slag from delining according to claim 1, which is characterized in that
The cement kiln recycling treatment system, including it is sequentially connected raw material mixing system, cement slurry preparation system, novel Cement produced with the dry method kiln system, new dry process rotary kiln system include dry-process cement rotary kiln dore furnace, cement rotary kiln and cement kiln The feed inlet of tail smoke-box, the slag from delining batch bin in raw material mixing system is connect with the solid slag storehouse of conversion dealkalize system.
CN201821361216.0U 2018-08-23 2018-08-23 The system of cement bypass of kiln incineration disposal aluminium cell slag from delining Active CN208750736U (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201821361216.0U CN208750736U (en) 2018-08-23 2018-08-23 The system of cement bypass of kiln incineration disposal aluminium cell slag from delining

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201821361216.0U CN208750736U (en) 2018-08-23 2018-08-23 The system of cement bypass of kiln incineration disposal aluminium cell slag from delining

Publications (1)

Publication Number Publication Date
CN208750736U true CN208750736U (en) 2019-04-16

Family

ID=66080962

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201821361216.0U Active CN208750736U (en) 2018-08-23 2018-08-23 The system of cement bypass of kiln incineration disposal aluminium cell slag from delining

Country Status (1)

Country Link
CN (1) CN208750736U (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114689789A (en) * 2022-04-11 2022-07-01 国网浙江省电力有限公司电力科学研究院 Flexibility is reformed transform unit oxygen boosting burning and hydrogen energy storage safety and is utilized experimental system

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114689789A (en) * 2022-04-11 2022-07-01 国网浙江省电力有限公司电力科学研究院 Flexibility is reformed transform unit oxygen boosting burning and hydrogen energy storage safety and is utilized experimental system
CN114689789B (en) * 2022-04-11 2023-08-15 国网浙江省电力有限公司电力科学研究院 Flexibility reforms transform unit oxygen boosting burning and hydrogen energy storage safety utilization experimental system

Similar Documents

Publication Publication Date Title
CN207394865U (en) The processing system of aluminium cell slag from delining
CN107401746B (en) Treatment system and treatment method for aluminum electrolysis overhaul slag
CN108585564B (en) System and method for co-processing electrolytic aluminum waste residues and co-producing double quick cement by cement kiln
US7189074B2 (en) Method and process for co-combustion in a waste to-energy facility
CN111410446B (en) Method and production system for recycling solid waste in aluminum industry by rotary kiln
CN105385844B (en) One kind roasting defluorinate device and technique
CN214937074U (en) Waste incineration residue recycling system
CN204529994U (en) The treatment unit of waste cathode carbon block in electrolysis of aluminum waste tank lining
CN109108050A (en) Containing sodium, the method for transformation of fluorochemical and system in a kind of aluminium electroloysis slag from delining
CN108787718A (en) A kind of aluminium electroloysis is given up mechanochemistry conversion and recovery method in breeze containing sodium, fluorochemical
CN113913618A (en) Method and system for regenerating calcium aluminate by using harmless secondary aluminum ash
CN106669962B (en) A kind of application method for the beneficiation method of the siliceous phosphorus ore of calcareous or calcium, ore-sorting system and ore-sorting system
CN109108049A (en) Containing sodium, the method for transformation of fluorochemical and system in a kind of aluminium electroloysis dangerous waste slag
CN212222804U (en) Production system for recycling aluminum industry solid waste in rotary kiln
CN114054469A (en) Aluminum ash harmless treatment and resource recycling method and system
CN109078964A (en) A kind of Changing Urban Garbage into Resources processing method
CN208545315U (en) The system of cement kiln synergic processing waste slag of electrolytic aluminium coproduction double-quick cement
CN105945028B (en) Consumer waste incineration regeneration technique
CN113121082A (en) Device and method for resource utilization and harmless treatment of oily sludge
CN108679628A (en) The System and method for of cement bypass of kiln incineration disposal aluminium cell slag from delining
CN112317517A (en) Pretreatment system and method suitable for co-processing electrolytic aluminum overhaul residues in cement kiln
CN109127655A (en) A kind of aluminium electroloysis is given up in breeze containing sodium, the method for transformation of fluorochemical and system
CN208750736U (en) The system of cement bypass of kiln incineration disposal aluminium cell slag from delining
CN109465277A (en) A kind of daily-life garbage without environmental pollution recycling treatment system utilized with effluent cycle
CN109127657A (en) Mechanochemistry conversion and recovery method in a kind of aluminium electroloysis slag from delining containing sodium, fluorochemical

Legal Events

Date Code Title Description
GR01 Patent grant
GR01 Patent grant
CP01 Change in the name or title of a patent holder
CP01 Change in the name or title of a patent holder

Address after: 410075 D-244, No. 199 Lugu Road, Lugu Lu, high tech Zone, Changsha, Hunan

Patentee after: Changsha Zhongsi Environmental Protection Technology Co., Ltd

Address before: 410075 D-244, No. 199 Lugu Road, Lugu Lu, high tech Zone, Changsha, Hunan

Patentee before: Changsha silicon cement technology development Co Ltd