CN109959016A - A kind of processing system of hazardous waste - Google Patents

A kind of processing system of hazardous waste Download PDF

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Publication number
CN109959016A
CN109959016A CN201910312968.0A CN201910312968A CN109959016A CN 109959016 A CN109959016 A CN 109959016A CN 201910312968 A CN201910312968 A CN 201910312968A CN 109959016 A CN109959016 A CN 109959016A
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CN
China
Prior art keywords
unit
kiln
burning
hazardous waste
waste
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.)
Pending
Application number
CN201910312968.0A
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Chinese (zh)
Inventor
陈德喜
胡立琼
姚建明
李兴杰
高术杰
赵发敏
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.)
China ENFI Engineering Corp
Original Assignee
China ENFI Engineering Corp
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 China ENFI Engineering Corp filed Critical China ENFI Engineering Corp
Priority to CN201910312968.0A priority Critical patent/CN109959016A/en
Publication of CN109959016A publication Critical patent/CN109959016A/en
Pending legal-status Critical Current

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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
    • B09B3/40Destroying solid waste or transforming solid waste into something useful or harmless involving thermal treatment, e.g. evaporation
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B5/00Operations not covered by a single other subclass or by a single other group in this subclass
    • 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
    • F23G5/08Incineration of waste; Incinerator constructions; Details, accessories or control therefor having supplementary heating
    • F23G5/14Incineration of waste; Incinerator constructions; Details, accessories or control therefor having supplementary heating including secondary combustion
    • F23G5/16Incineration of waste; Incinerator constructions; Details, accessories or control therefor having supplementary heating including secondary combustion in a separate combustion chamber
    • 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
    • F23G5/20Incineration of waste; Incinerator constructions; Details, accessories or control therefor having rotating or oscillating drums
    • 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
    • F23G5/44Details; Accessories
    • F23G5/442Waste feed arrangements
    • 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
    • F23G5/44Details; Accessories
    • F23G5/46Recuperation of heat
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23JREMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES 
    • F23J15/00Arrangements of devices for treating smoke or fumes
    • F23J15/02Arrangements of devices for treating smoke or fumes of purifiers, e.g. for removing noxious material
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23JREMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES 
    • F23J15/00Arrangements of devices for treating smoke or fumes
    • F23J15/02Arrangements of devices for treating smoke or fumes of purifiers, e.g. for removing noxious material
    • F23J15/022Arrangements of devices for treating smoke or fumes of purifiers, e.g. for removing noxious material for removing solid particulate material from the gasflow
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23JREMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES 
    • F23J15/00Arrangements of devices for treating smoke or fumes
    • F23J15/06Arrangements of devices for treating smoke or fumes of coolers
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23JREMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES 
    • F23J15/00Arrangements of devices for treating smoke or fumes
    • F23J15/08Arrangements of devices for treating smoke or fumes of heaters
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23JREMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES 
    • F23J2217/00Intercepting solids
    • F23J2217/10Intercepting solids by filters
    • F23J2217/101Baghouse type

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

Abstract

The present invention provides a kind of processing systems of hazardous waste, unit, melt element, the second burning unit and gas cleaning unit are burned including first, wherein, the second burning unit is connected with the first burning unit, and the gas cleaning unit is connected with the second burning unit.The processing system of the hazardous waste of an embodiment of the present invention can not only make the flue gas of discharge up to standard, and can be realized the resource utilization of hazardous waste.

Description

A kind of processing system of hazardous waste
Technical field
The present invention relates to a kind of processing system of hazardous waste, specially a kind of achievable hazardous waste harmless treatment and The processing equipment of resource utilization.
Background technique
With the continuous propulsion of China's process of industrialization, the hazardous waste quantity generated in industrial processes increases year by year Add, ecological environment and health of the masses are caused and seriously threatened.China's hazardous waste is many kinds of, complicated component, disposes and controls Manage that at high cost, processing capacity is limited, handled by hazardous waste, it is mishandling cause environmental pollution and risk accidents to take place frequently, danger Waste pollution prevention and control situation is severe.
Currently, burning is the mainstream technology of dangerous waste disposal.Existing burning disposal equipment, it is easily raw during processing At dioxin predecessor, cause the dioxins concentration in the flue gas of discharge exceeded.And it is still fallen within by burning the lime-ash generated Hazardous waste generally requires and carries out chelating solidification landfill disposal, can generate potential threat to the environment on landfill yard periphery;Meanwhile The lime-ash heavy metal toxicity that dangerous waste incineration generates is exceeded, clinker ignition loss is low.
Summary of the invention
A primary object of the present invention is providing a kind of processing system of hazardous waste, including first burns unit, melts Melt unit, the second burning unit and gas cleaning unit, wherein described second, which burns unit and described first, burns unit phase Even, the gas cleaning unit is connected with the second burning unit.
According to an embodiment of the present invention, the first burning unit includes counterflow rotary kiln, the counterflow rotary kiln Feedstock direction is contrary with flue gas emission.
According to an embodiment of the present invention, the first burning unit includes rotary kiln and feeding device, the rotary kiln Including kiln body, the kiln body includes the kiln hood and kiln tail positioned at both ends, and the kiln hood is provided with kiln head cover, the kiln head cover packet Mouth and slag notch are included, the outlet flue is connected with the second burning unit;The feeding device passes through the kiln head cover It is set to the kiln hood, the feeding device includes feed opening, and the feed opening is slagged tap adjacent to the outlet flue, far from described Mouthful.
According to an embodiment of the present invention, the melt element includes electric furnace, the electric furnace be selected from ore-smelting electric furnace or wait from Daughter electric furnace.
According to an embodiment of the present invention, the melt element includes coring furnace and crystallization furnace.
According to an embodiment of the present invention, the melt element includes centrifuge, cotton collecting machine and pleating machine.
According to an embodiment of the present invention, the melt element includes water quenching slag bath and ball mill.
According to an embodiment of the present invention, the gas cleaning unit include heat-exchanger rig, cooling device, deacidifying device, One of dust-extraction unit, wash mill are a variety of.
According to an embodiment of the present invention, the gas cleaning unit include waste heat boiler, flash cold column, dry type extracting tower, Bag filter and single-stage or multistage scrubbing tower.
According to an embodiment of the present invention, the system comprises pretreatment units and fused raw material supply unit, described pre- Processing unit is used for the pretreatment of the hazardous waste, and the fused raw material supply unit is used to for fused raw material being delivered to described Melt element.
The processing system of the hazardous waste of an embodiment of the present invention can not only make the flue gas of discharge up to standard, and can Realize the resource utilization of hazardous waste.
Detailed description of the invention
Fig. 1 is the structural schematic diagram of the processing system of the hazardous waste of an embodiment of the present invention.
Specific embodiment
The exemplary embodiment for embodying feature of present invention and advantage will describe in detail in the following description.It should be understood that The present invention can have various variations in different embodiments, neither depart from the scope of the present invention, and theory therein Bright and diagram inherently is illustrated as being used, rather than to limit the present invention.
An embodiment of the present invention provides a kind of processing system of hazardous waste, including first burns unit, melting list Member, second burn unit and gas cleaning unit;Wherein, the second burning unit burns unit, gas cleaning with first respectively Unit is connected.
In an embodiment, hazardous waste includes the waste that can be burned in addition to explosive and have radioactivity, can Think one of solid-state, semisolid, liquid hazardous waste or a variety of.
In an embodiment, hazardous waste can be the higher organic pollutant of calorific value.
In an embodiment, hazardous waste can be medical waste, rectification residue, organic resin class waste, You Jirong Agent, halogenated material waste (HW45), coating waste (HW12), surface treatment waste (HW17), emulsion (HW09), waste containing phenol (HW39), clinical waste (HW01), asbestos (HW36), organic cyanide waste (HW38), dead catalyst (HW50), distillation One of residue (HW11), waste mineral oil (HW08), pesticide waste (HW04) and spent acid (HW34) are a variety of.
The processing system of the hazardous waste of an embodiment of the present invention burns hazardous waste by the first burning unit Burning processing, obtains bottom ash and the first flue gas;Melt process is carried out to bottom ash by melt element, and burns unit pair by second First flue gas carries out secondary burning processing, further to remove the substances such as remaining dioxin, imflammable gas;It is burnt for the second time After burning processing, flying dust and the second flue gas are obtained, melt process can be carried out to flying dust by melt element, and pass through gas cleaning list The purified treatments such as member exchanges heat to the second flue gas, cools down, depickling, dedusting, denitration, washing, to realize the qualified discharge of flue gas.
In an embodiment, the processing system of hazardous waste includes pretreatment unit, enters the in hazardous waste raw material Before one burns unit, can first pass through pretreatment unit raw material is crushed, is neutralized etc. pretreatment in order to subsequent burning at The progress of reason, such as pretreatment unit may include crusher or the device neutralized.
As shown in Figure 1, first, which burns unit, includes revolution in the processing system of the hazardous waste of an embodiment of the present invention Kiln, feeding device and feeding device.
Rotary kiln includes the kiln body 11 for carrying out burning disposal, and for the kiln head cover 12 and kiln hood 13 of sealing, To keep the airtightness of dangerous waste incineration process.Kiln body 11 includes kiln hood and kiln tail, and kiln hood and kiln tail are located in the axial direction The both ends of kiln body 11, kiln head cover 12 are set to kiln hood, and kiln hood 13 is set to kiln tail.Kiln head cover 12 is whole in long strip, has The cavity of both ends open;Kiln head cover 12 can be cuboid, be also possible to cylinder, and the two-port of kiln head cover 12 can be used separately as Through the resulting bottom ash of burning disposal and the first flue gas rotary kiln can be discharged from outlet flue, slag notch respectively in outlet flue and slag notch. Outlet flue can be connected with the second burning unit, and slag notch can be connected with batch can 41, in order to which bottom ash enters melting by batch can 41 Unit.
Feeding device is used to burn solid-state hazardous waste feeding kiln body 11, passes through kiln head cover 12 and 11 phase of kiln body Connection.Feeding device may include feed opening 14 and push rod 15.When operation, material enters feeding device from feed opening 14, and is pushing away (being also possible to screw feeder) enters kiln body 11 under the action of bar 15.The feedstock direction of feed opening 14 can be parallel to the cigarette of outlet flue Gas emission direction, and feedstock direction is opposite with the holding of flue gas emission direction.
Feeding device may be disposed at kiln tail, can be the device such as spray gun 16, in order to by the danger of liquid or semisolid It is burned in the kiln body 11 of dangerous waste penetrating rotary kiln, feeding device can also be set to other positions according to burning situation. Spray gun 16 can be set to kiln hood 13 along the axis direction of kiln body 11;Kiln hood 13 has slag notch, the slag notch of kiln hood 13 It is parallel to the slag notch setting of kiln head cover 12, and batch can 41 can be connected to together with the slag notch of kiln head cover 12;In kiln hood 13 On be additionally provided with smoke pipe, in order to melt element generate flue gas be passed through in rotary kiln, to rotary kiln carry out concurrent heating.
In an embodiment, the second burning unit includes dual firing chamber 21, and dual firing chamber can fire to be existing for high temperature The device of burning.Dual firing chamber 21 is connected with the outlet flue of kiln head cover 12, from rotary kiln be discharged flue gas can in dual firing chamber 21 into Second of burning disposal of row, obtains flying dust and the second flue gas;The flue gas for being passed through dual firing chamber 21 is generated including the first burning disposal Flue gas and generated by melt element and be passed through the flue gas of rotary kiln.Flying dust can directly pass through chute (not shown), It can be lifted into melt element by batch can and carry out melt process, the second flue gas enters subsequent gas cleaning unit and purified Processing.
In an embodiment, gas cleaning unit include the heat-exchanger rig being sequentially communicated, cooling device, deacidifying device, Dust-extraction unit, wash mill.Wherein, heat-exchanger rig can be waste heat boiler 31, and cooling device can be flash cold column 32, depickling dress It sets and can be dry type extracting tower 33, dust-extraction unit can be bag filter 34, and wash mill can be single-stage or multistage washing Tower can specifically be selected according to smoke components.For example, wash mill can be wet process extracting tower, including level-one wet type depickling Tower 351 and second level wet type extracting tower 352.
The flue gas being discharged from dual firing chamber 21 can carry out heat exchange processing in waste heat boiler 31;Flue gas after heat exchange is through flash cold column Depickling processing, the settable alkaline matter in dry type extracting tower 33 can be carried out by dry type extracting tower 33 after 32 coolings, such as disappeared Lime, to absorb sour gas;Through depickling, treated that flue gas can be dusted processing by bag filter 34, enters later Level-one wet type extracting tower 351 and second level wet type extracting tower 352 carry out carrying out washing treatment.Flue gas after being cleaned can be through flue gas heater 36 heat temperature raisings, and under the action of air-introduced machine 37, it is drained into atmosphere by chimney 38.
In addition, waste heat boiler 31, flash cold column 32, dry type extracting tower 33, bag filter 34 can be produced during processing Raw flying dust is collected, and is delivered to melt element by scrapper conveyor.In addition to scraper plate conveying, flying dust can also pass through pneumatic conveying Or other modes are sent into melt element.
In an embodiment, melt element includes melting plant, and energy source is electric energy.Melting plant can be electricity Furnace 51, electric furnace can be ore-smelting electric furnace, plasma electric furnace etc..Ore-smelting electric furnace generates heat using lime-ash resistance and realizes lime-ash Gas plasmaization is generated high temperature to melt lime-ash by melt process, plasma electric furnace.
The materials such as bottom ash, flying dust are melt through high-temperature process in electric furnace 51, and the flue gas that electric furnace 51 generates can pass through smoke pipe It is passed through in rotary kiln, concurrent heating is carried out to rotary kiln.
In an embodiment, in addition to electric furnace 51, melt element further includes coring furnace and crystallization furnace (not shown), is melted Body can be made into devitrified glass through the processing of coring furnace, crystallization furnace.
In another embodiment, in addition to electric furnace 51, melt element further includes centrifuge, cotton collecting machine and pleating machine (in figure Do not show), melt can be made into cellucotton through the processing of centrifuge, cotton collecting machine and pleating machine.
In another embodiment, in addition to electric furnace 51, melt element further includes that water quenching slag bath and ball mill (are not shown in figure Show), melt can be made into cement admixture through the processing of water quenching slag bath and ball mill.
In an embodiment, under the high temperature conditions, the solid waste after burning is melted by melt process as glass State, is made devitrified glass after solidification, the compact texture of devitrified glass can ensure the permanent stability of solidified body.In addition, solid-state The organic pollutant of waste passes through high temperature pyrolysis in melting process and is thoroughly decomposed, and the harmful elements such as heavy metal are cured In vitreum, the harmlessness disposing of hazardous waste is realized.
In an embodiment, it is big that area is mixed using counterflow rotary kiln incinerator gas and solid, heat transfer efficiency is high, Be conducive to increase burn rate, be suitble to the biggish hazardous waste of calorific value floatability;And the bottom ash that rotary kiln generates is sent directly into electricity In furnace, the glass dregs that handle by high-temperature fusion can not only the harmful elements such as curing heavy metal, and height can be made The building material product of added value realizes the resource utilization of hazardous waste.
In an embodiment, the processing system of hazardous waste includes fused raw material supply unit, is used for fused raw material Bottom ash, flying dust etc. are delivered to electric furnace 51 and carry out melt process.Fused raw material supply unit may include chute, batch can 41, scrapper conveyor Deng.Remaining bottom ash directly can be delivered to electric furnace 51 by chute after burning disposal, can also be in driving (not shown) Effect is lower to be lifted into electric furnace 51 by batch can 41.
In an embodiment, the slag notch of kiln head cover 12 and the slag notch of kiln hood 13 can be connected with batch can 41 Logical, after the bottom ash that rotary kiln generates enters batch can 41, batch can 41 can move to feed bin 42, feed bin 42 and electric furnace under the action of driving 51 are connected.
Below in conjunction with Fig. 1 and specific embodiment to the operator of the processing system of the hazardous waste of an embodiment of the present invention Formula is further described.
Embodiment
(1) medical waste, rectification residue and organic resin class waste add certainly after pretreatment unit carries out broken pretreatment Material mouth 14 enters feeding device, and carries out burning disposal in the kiln body 11 for being pushed into counterflow rotary kiln under the action of push rod 15; Meanwhile the hazardous waste of the liquid such as spent organic solvent and waste mineral oil being sprayed into kiln body 11 using spray gun 16 and is carried out at burning Reason;
(2) temperature of kiln head of counterflow rotary kiln is maintained at 800 DEG C or so progress burning disposals, keeps full combustion, The kiln hood and kiln tail of rotary kiln obtain bottom ash, and tapping temperature is 800 DEG C, and clinker ignition loss 2.5%, hot bottom ash is discharged into from slag notch Batch can 41, and electric furnace 51 is moved under the action of driving, entered in electric furnace 51 (ore-smelting electric furnace) by feed bin 42 and is carried out at melting Reason;
(3) enter dual firing chamber 21 from the flue gas that rotary kiln end is discharged and carry out burning disposal, ignition temperature is 1200 DEG C;Two Remaining flying dust enters electric furnace 51 in combustion room 21, and the flue gas of discharge enters waste heat boiler 31 and realizes heat conversion, boiler export Flue-gas temperature is 550 DEG C;The flue gas being discharged from waste heat boiler 31 enters flash cold column 32, is cooled to 200 DEG C rapidly;From flash cold column 32 The flue gas of outlet discharge enters dry type extracting tower 33, and the calcium hydroxide in dry type extracting tower 33 absorbs the partially acidic gas in flue gas Body, exit gas temperature are 180 DEG C;The flue gas that self-drying type extracting tower 33 is discharged continues through bag filter 34, outlet temperature It is 170 DEG C;Enter scrubbing tower by the flue gas of bag filter 34 --- level-one wet type extracting tower 351, second level wet type extracting tower 352, sour gas therein is absorbed by the NaOH solution in extracting tower, and exit gas temperature is 60 DEG C;Finally, being arranged from scrubbing tower Flue gas out is heated up to 135 DEG C by flue gas heater 36, is drained into atmosphere by air-introduced machine 37 by chimney 38;
(4) by the flying dust generated in waste heat boiler 31, flash cold column 32, dry type extracting tower 33 and bag filter 34 by scraping Trigger is delivered in electric furnace 51, is melt into slag together with the flying dust that bottom ash and dual firing chamber generate;In addition, quartz sand conduct is added Constituent adjustment agent, mass fraction are the 10% of fused raw material (bottom ash+flying dust) quality;
(5) fused raw material and constituent adjustment agent are melt through high-temperature process in electric furnace 51, and melt temperature is 1350 DEG C, is glued Degree is 2Pas, and is entered by melt discharge outlet and obtain the melt of stable homogeneous in clarifying and homogenizing pond;Electric furnace 51 is generated Flue gas is passed through in counterflow rotary kiln by smoke pipe, carries out concurrent heating to rotary kiln;
(6) melt is sent into 650 DEG C of coring furnaces, keeps the temperature 5h, obtains the vitreum of certain shapes;Nucleating glass body is sent Enter into crystallization furnace, crystallization furnace is warming up to 950 DEG C by 650 DEG C, and heating rate is 2 DEG C/min, and keeps the temperature 3h at 950 DEG C;It protects After temperature, room temperature is cooled to the furnace, take out the devitrified glass of semi-finished product;
(7) semi-finished product devitrified glass is obtained into the devitrified glass product of shiny appearance by cutting, polishing, technique for grinding.
In another embodiment, step (6), (7), which may is that, send melt into four-roller centrifuge, in the work of centrifugal force Fibrous product is obtained under, adding mass fraction thereto is 4% (using fibrous product and the gross mass of phenolic resin as base It is quasi-) phenolic resin as bonding agent, 450g/m is formed in cotton collecting machine2A blanket;Gained blanket is sent into pleating machine It is interior, so that being mutually lapped and being engaged between fiber;Obtained cellucotton is sent into 300 DEG C of curing ovens, the water in cellucotton is removed Point, while rapid curing phenolic resin, obtain the Semifinished fibre cotton for meeting performance indicator;By Semifinished fibre cotton by cutting It cuts, cool down, packing process obtains the cellucotton product for meeting performance indicator.
In another embodiment, step (6), (7) may is that the water quenching that melt Water Quenching is obtained to partial size < 5mm Slag;After fishing out slag drying and processing, being milled to specific surface area is 250m3The powder of/kg can be used as cement admixture use.
Unless limited otherwise, term used herein is the normally understood meaning of those skilled in the art.
Embodiment described in the invention is merely for exemplary purpose, the protection scope being not intended to limit the invention, Those skilled in the art can be made within the scope of the invention various other replacements, changes and improvements, thus, the present invention is not limited to Above embodiment, and be only defined by the claims.

Claims (10)

1. a kind of processing system of hazardous waste characterized by comprising
First burns unit;
Melt element;
Second burns unit, is connected with the first burning unit;And
Gas cleaning unit is connected with the second burning unit.
2. system according to claim 1, which is characterized in that the first burning unit includes counterflow rotary kiln, described The feedstock direction of counterflow rotary kiln is contrary with flue gas emission.
3. system according to claim 1, which is characterized in that the first burning unit includes rotary kiln and charging dress It sets, the rotary kiln includes kiln body, and the kiln body includes the kiln hood and kiln tail positioned at both ends, and the kiln hood is provided with kiln hood Cover, the kiln head cover include outlet flue and slag notch, and the outlet flue is connected with the second burning unit;
The feeding device is set to the kiln hood by the kiln head cover, and the feeding device includes feed opening, the charging The neighbouring outlet flue of mouth, the separate slag notch.
4. system according to claim 1, which is characterized in that the melt element includes electric furnace, and the electric furnace is selected from mine Electrothermal stove or plasma electric furnace.
5. system according to claim 4, which is characterized in that the melt element includes coring furnace and crystallization furnace.
6. system according to claim 4, which is characterized in that the melt element includes centrifuge, cotton collecting machine and pleating Machine.
7. system according to claim 4, which is characterized in that the melt element includes water quenching slag bath and ball mill.
8. system according to claim 1, which is characterized in that the gas cleaning unit includes heat-exchanger rig, cooling dress It sets, one of deacidifying device, dust-extraction unit, wash mill or a variety of.
9. system according to claim 1, which is characterized in that the gas cleaning unit include waste heat boiler, flash cold column, Dry type extracting tower, bag filter and single-stage or multistage scrubbing tower.
10. system according to claim 1, which is characterized in that including pretreatment unit and fused raw material supply unit, institute Pretreatment of the pretreatment unit for the hazardous waste is stated, the fused raw material supply unit is for fused raw material to be delivered to The melt element.
CN201910312968.0A 2019-04-18 2019-04-18 A kind of processing system of hazardous waste Pending CN109959016A (en)

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CN109020231A (en) * 2018-10-11 2018-12-18 清华大学 A method of preparing alloyed iron and devitrified glass

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CN107434985A (en) * 2016-05-25 2017-12-05 北京科立科盈科技有限公司 A kind of processing system and method for fluidized gasification converter fly ash and lime-ash
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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112619561A (en) * 2020-11-27 2021-04-09 深圳市捷晶能源科技有限公司 Heavy metal-containing material treatment system and treatment method thereof

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