CN107120660A - A kind of domestic garbage pyrolysis incinerator flue gas purification system - Google Patents
A kind of domestic garbage pyrolysis incinerator flue gas purification system Download PDFInfo
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- CN107120660A CN107120660A CN201710266670.1A CN201710266670A CN107120660A CN 107120660 A CN107120660 A CN 107120660A CN 201710266670 A CN201710266670 A CN 201710266670A CN 107120660 A CN107120660 A CN 107120660A
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- flue gas
- dust collector
- carbon fiber
- dioxin
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- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 title claims abstract description 81
- 239000003546 flue gas Substances 0.000 title claims abstract description 81
- 238000000197 pyrolysis Methods 0.000 title claims abstract description 29
- 238000000746 purification Methods 0.000 title claims abstract description 23
- 239000010813 municipal solid waste Substances 0.000 title description 6
- 239000000428 dust Substances 0.000 claims abstract description 34
- 229920000049 Carbon (fiber) Polymers 0.000 claims abstract description 31
- 239000004917 carbon fiber Substances 0.000 claims abstract description 31
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 claims abstract description 31
- 238000010791 quenching Methods 0.000 claims abstract description 25
- 239000010791 domestic waste Substances 0.000 claims abstract description 24
- 238000001816 cooling Methods 0.000 claims abstract description 23
- 239000000126 substance Substances 0.000 claims abstract description 23
- 239000003054 catalyst Substances 0.000 claims abstract description 21
- 239000002918 waste heat Substances 0.000 claims abstract description 17
- 239000003344 environmental pollutant Substances 0.000 claims abstract description 11
- 231100000719 pollutant Toxicity 0.000 claims abstract description 11
- 230000000171 quenching effect Effects 0.000 claims abstract description 11
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 8
- 230000003197 catalytic effect Effects 0.000 claims abstract description 7
- KVGZZAHHUNAVKZ-UHFFFAOYSA-N 1,4-Dioxin Chemical compound O1C=COC=C1 KVGZZAHHUNAVKZ-UHFFFAOYSA-N 0.000 claims description 27
- 150000002013 dioxins Chemical class 0.000 claims description 22
- 239000007789 gas Substances 0.000 claims description 14
- 239000002253 acid Substances 0.000 claims description 10
- 239000007921 spray Substances 0.000 claims description 10
- 238000006243 chemical reaction Methods 0.000 claims description 9
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 claims description 5
- 239000000920 calcium hydroxide Substances 0.000 claims description 5
- 229910001861 calcium hydroxide Inorganic materials 0.000 claims description 5
- 239000004744 fabric Substances 0.000 claims description 5
- 239000012752 auxiliary agent Substances 0.000 claims description 4
- 230000003647 oxidation Effects 0.000 claims description 2
- 238000007254 oxidation reaction Methods 0.000 claims description 2
- 239000000779 smoke Substances 0.000 claims description 2
- 229910005965 SO 2 Inorganic materials 0.000 abstract description 4
- HGUFODBRKLSHSI-UHFFFAOYSA-N 2,3,7,8-tetrachloro-dibenzo-p-dioxin Chemical compound O1C2=CC(Cl)=C(Cl)C=C2OC2=C1C=C(Cl)C(Cl)=C2 HGUFODBRKLSHSI-UHFFFAOYSA-N 0.000 abstract 4
- MCJGNVYPOGVAJF-UHFFFAOYSA-N quinolin-8-ol Chemical compound C1=CN=C2C(O)=CC=CC2=C1 MCJGNVYPOGVAJF-UHFFFAOYSA-N 0.000 abstract 1
- 238000000034 method Methods 0.000 description 19
- 238000004056 waste incineration Methods 0.000 description 11
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 10
- 239000000654 additive Substances 0.000 description 8
- 238000005516 engineering process Methods 0.000 description 7
- 230000008569 process Effects 0.000 description 6
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 4
- 239000000498 cooling water Substances 0.000 description 4
- 238000010438 heat treatment Methods 0.000 description 4
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 3
- 238000009264 composting Methods 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- IXCSERBJSXMMFS-UHFFFAOYSA-N hydrogen chloride Substances Cl.Cl IXCSERBJSXMMFS-UHFFFAOYSA-N 0.000 description 3
- 229910000041 hydrogen chloride Inorganic materials 0.000 description 3
- 230000004048 modification Effects 0.000 description 3
- 238000012986 modification Methods 0.000 description 3
- 238000012545 processing Methods 0.000 description 3
- 238000001179 sorption measurement Methods 0.000 description 3
- 239000002699 waste material Substances 0.000 description 3
- 229910000831 Steel Inorganic materials 0.000 description 2
- 230000000996 additive effect Effects 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 2
- 239000001569 carbon dioxide Substances 0.000 description 2
- 229910002092 carbon dioxide Inorganic materials 0.000 description 2
- 238000006555 catalytic reaction Methods 0.000 description 2
- 238000010276 construction Methods 0.000 description 2
- 238000011161 development Methods 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 238000011038 discontinuous diafiltration by volume reduction Methods 0.000 description 2
- 230000007613 environmental effect Effects 0.000 description 2
- 229910001385 heavy metal Inorganic materials 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 239000013618 particulate matter Substances 0.000 description 2
- 239000010959 steel Substances 0.000 description 2
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 1
- 229910000975 Carbon steel Inorganic materials 0.000 description 1
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 1
- 229910002089 NOx Inorganic materials 0.000 description 1
- 235000011941 Tilia x europaea Nutrition 0.000 description 1
- 238000004458 analytical method Methods 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 229910052791 calcium Inorganic materials 0.000 description 1
- 239000011575 calcium Substances 0.000 description 1
- 230000000711 cancerogenic effect Effects 0.000 description 1
- 239000010962 carbon steel Substances 0.000 description 1
- 231100000357 carcinogen Toxicity 0.000 description 1
- 239000003183 carcinogenic agent Substances 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 238000006477 desulfuration reaction Methods 0.000 description 1
- 230000023556 desulfurization Effects 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 239000012717 electrostatic precipitator Substances 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 239000010419 fine particle Substances 0.000 description 1
- 239000005431 greenhouse gas Substances 0.000 description 1
- 229910052739 hydrogen Inorganic materials 0.000 description 1
- 239000001257 hydrogen Substances 0.000 description 1
- 125000004435 hydrogen atom Chemical class [H]* 0.000 description 1
- 230000002401 inhibitory effect Effects 0.000 description 1
- 239000004571 lime Substances 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 230000007246 mechanism Effects 0.000 description 1
- 239000005022 packaging material Substances 0.000 description 1
- 239000000123 paper Substances 0.000 description 1
- 239000004033 plastic Substances 0.000 description 1
- 229920003023 plastic Polymers 0.000 description 1
- YEBIHIICWDDQOL-YBHNRIQQSA-N polyoxin Chemical compound O[C@@H]1[C@H](O)[C@@H](C(C=O)N)O[C@H]1N1C(=O)NC(=O)C(C(O)=O)=C1 YEBIHIICWDDQOL-YBHNRIQQSA-N 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 239000011819 refractory material Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 238000005507 spraying Methods 0.000 description 1
- 238000005728 strengthening Methods 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
Classifications
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/44—Details; Accessories
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D46/00—Filters or filtering processes specially modified for separating dispersed particles from gases or vapours
- B01D46/02—Particle separators, e.g. dust precipitators, having hollow filters made of flexible material
- B01D46/023—Pockets filters, i.e. multiple bag filters mounted on a common frame
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/38—Removing components of undefined structure
- B01D53/40—Acidic components
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/75—Multi-step processes
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/81—Solid phase processes
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/86—Catalytic processes
- B01D53/8659—Removing halogens or halogen compounds
- B01D53/8662—Organic halogen compounds
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/44—Details; Accessories
- F23G5/46—Recuperation of heat
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J15/00—Arrangements of devices for treating smoke or fumes
- F23J15/006—Layout of treatment plant
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J15/00—Arrangements of devices for treating smoke or fumes
- F23J15/02—Arrangements of devices for treating smoke or fumes of purifiers, e.g. for removing noxious material
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J15/00—Arrangements of devices for treating smoke or fumes
- F23J15/02—Arrangements of devices for treating smoke or fumes of purifiers, e.g. for removing noxious material
- F23J15/022—Arrangements of devices for treating smoke or fumes of purifiers, e.g. for removing noxious material for removing solid particulate material from the gasflow
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J15/00—Arrangements of devices for treating smoke or fumes
- F23J15/02—Arrangements of devices for treating smoke or fumes of purifiers, e.g. for removing noxious material
- F23J15/022—Arrangements of devices for treating smoke or fumes of purifiers, e.g. for removing noxious material for removing solid particulate material from the gasflow
- F23J15/025—Arrangements of devices for treating smoke or fumes of purifiers, e.g. for removing noxious material for removing solid particulate material from the gasflow using filters
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J15/00—Arrangements of devices for treating smoke or fumes
- F23J15/02—Arrangements of devices for treating smoke or fumes of purifiers, e.g. for removing noxious material
- F23J15/04—Arrangements of devices for treating smoke or fumes of purifiers, e.g. for removing noxious material using washing fluids
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J15/00—Arrangements of devices for treating smoke or fumes
- F23J15/06—Arrangements of devices for treating smoke or fumes of coolers
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2251/00—Reactants
- B01D2251/40—Alkaline earth metal or magnesium compounds
- B01D2251/404—Alkaline earth metal or magnesium compounds of calcium
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2251/00—Reactants
- B01D2251/60—Inorganic bases or salts
- B01D2251/604—Hydroxides
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2253/00—Adsorbents used in seperation treatment of gases and vapours
- B01D2253/10—Inorganic adsorbents
- B01D2253/102—Carbon
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2257/00—Components to be removed
- B01D2257/93—Toxic compounds not provided for in groups B01D2257/00 - B01D2257/708
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2258/00—Sources of waste gases
- B01D2258/02—Other waste gases
- B01D2258/0283—Flue gases
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J2215/00—Preventing emissions
- F23J2215/30—Halogen; Compounds thereof
- F23J2215/301—Dioxins; Furans
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J2217/00—Intercepting solids
- F23J2217/10—Intercepting solids by filters
- F23J2217/101—Baghouse type
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J2217/00—Intercepting solids
- F23J2217/50—Intercepting solids by cleaning fluids (washers or scrubbers)
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A50/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
- Y02A50/20—Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A50/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
- Y02A50/20—Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
- Y02A50/2351—Atmospheric particulate matter [PM], e.g. carbon smoke microparticles, smog, aerosol particles, dust
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E20/00—Combustion technologies with mitigation potential
- Y02E20/30—Technologies for a more efficient combustion or heat usage
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- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- General Engineering & Computer Science (AREA)
- Mechanical Engineering (AREA)
- Environmental & Geological Engineering (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Biomedical Technology (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- General Chemical & Material Sciences (AREA)
- Analytical Chemistry (AREA)
- Health & Medical Sciences (AREA)
- Treating Waste Gases (AREA)
- Chimneys And Flues (AREA)
Abstract
本发明涉及一种生活垃圾热解焚烧装置烟气净化系统;包括急冷塔、电磁脉冲除尘器、余热利用与冷却装置、炭纤维过滤装置、换热装置、二噁英化学催化装置、供水系统、烟气管道和引风机;其特征是急冷塔的进口端与生活垃圾热解焚烧装置的烟气管道连接,急冷塔的出口端与所述电磁脉冲除尘器连接,电磁脉冲除尘器与余热利用与冷却装置连接,余热利用与冷却装置与所述炭纤维过滤装置连接,炭纤维过滤装置与所述引风机连接,引风机出口连接换热装置,换热装置出口连接二噁英化学催化装置,二噁英化学催化装置与烟囱连接,烟气经过一系列净化最终排入大气。够有效地去除焚烧烟气中的污染物,包括CO、SO2、NOX、二噁英等,二噁英浓度满足国家标准。
The invention relates to a flue gas purification system of a domestic waste pyrolysis incineration device; comprising a quench tower, an electromagnetic pulse dust collector, a waste heat utilization and cooling device, a carbon fiber filter device, a heat exchange device, a dioxin chemical catalyst device, a water supply system, Flue gas pipeline and induced draft fan; it is characterized in that the inlet end of the quenching tower is connected with the flue gas pipeline of the domestic waste pyrolysis incinerator, the outlet end of the quenching tower is connected with the electromagnetic pulse dust collector, and the electromagnetic pulse dust collector is connected with waste heat utilization and The cooling device is connected, the waste heat utilization and cooling device is connected with the carbon fiber filter device, the carbon fiber filter device is connected with the induced draft fan, the outlet of the induced draft fan is connected with a heat exchange device, and the outlet of the heat exchange device is connected with a dioxin chemical catalyst device. The oxin chemical catalytic device is connected to the chimney, and the flue gas is finally discharged into the atmosphere after a series of purification. It can effectively remove pollutants in the incineration flue gas, including CO, SO 2 , NO X , dioxin, etc., and the concentration of dioxin meets the national standard.
Description
技术领域technical field
本发明涉及生活垃圾处理处置与资源化利用领域系统,具体地涉及一种生活垃圾热解焚烧装置烟气净化系统。The invention relates to a system in the field of domestic waste treatment and resource utilization, in particular to a flue gas purification system of a domestic waste pyrolysis incineration device.
背景技术Background technique
目前我国常用的垃圾处理处置方式有:卫生填埋法、垃圾堆肥法和热处理法等。卫生填埋是我国当前垃圾处理的主要方式,这种处理方式技术简单,处理量大,但占用土地资源过大,存在选址难、渗滤液污染、温室气体排放等问题,且没有对垃圾进行资源化利用。由于生活垃圾中包装材料、纸类和塑料等成分的数量在不断增加,给垃圾堆肥带来了一些问题,且堆肥后容易造成土地盐碱化、产品的市场准入难,使其发展受到限制。而垃圾热处理技术在减容、减量、资源化利用方面具有明显优势,新型垃圾焚烧技术,近年来受到了国家的重视,将是今后垃圾处理处置与资源化利用的主要方向。At present, the commonly used garbage disposal methods in my country include: sanitary landfill method, garbage composting method and heat treatment method. Sanitary landfill is the main way of waste disposal in my country at present. This treatment method is simple in technology and has a large processing capacity, but it occupies too much land resources, and there are problems such as difficult site selection, leachate pollution, and greenhouse gas emissions. resource utilization. Due to the increasing amount of packaging materials, paper and plastics in domestic waste, it has brought some problems to waste composting, and after composting, it is easy to cause land salinization and difficult market access for products, which limits its development. . The waste heat treatment technology has obvious advantages in volume reduction, volume reduction, and resource utilization. The new waste incineration technology has received national attention in recent years and will be the main direction of waste treatment and resource utilization in the future.
热处理技术实质是在高温下将垃圾进行氧化和分解,以形成稳定的固态残渣,但热解焚烧期间会释放出大量的有害气体,粉尘和细小颗粒随风飞扬,致使空气中各种污染物指数超标,而且会产生大量的强致癌物质二噁英,这是目前制约热解焚烧处理技术的主要因素。The essence of heat treatment technology is to oxidize and decompose garbage at high temperature to form stable solid residues. However, during pyrolysis and incineration, a large amount of harmful gases will be released, and dust and fine particles will fly with the wind, resulting in various pollutants in the air. Exceeding the standard, and will produce a large amount of strong carcinogen dioxin, which is the main factor restricting pyrolysis incineration treatment technology at present.
为了防止垃圾焚烧处理过程中对环境产生二次污染,必须采取严格的措施,利用烟气净化系统控制垃圾焚烧烟气的排放。烟气中酸性气体的脱除有三种处理工艺:干法、半干法与湿法。半干法净化工艺可达到较高的净化效率,投资和运行费用低,流程简单,不产生废水,欧洲的焚烧厂采用半干法的较多。半干法在国内已有较多成功的应用实例,积累了一定的运行经验,适用于排放标准要求较高的焚烧厂,现在中国在建与待建的多数垃圾焚烧发电厂都选用半干法。干法净化工艺其工艺比较简单,投资低,运行维护方便,但干法工艺净化效率相对较低,在日本近年的焚烧厂建设中采用较多。湿法净化工艺的污染物净化效率最高,可满足最严格的排放标准要求。但由于流程复杂,配套设备较多,一次性投资和运行费用高,在经济发达国家应用较多,在中国得不到广泛应用。就NOx的去除效果而言,SCR对NOx的去除率达到了90%以上,而SNCR对NOx的去除率也可达到50%左右。就成本-效率分析,SCR和先进的焚烧控制系统基本相当,明显比SNCR技术昂贵。自20世纪80年代末开始,垃圾焚烧厂更多的采用布袋除尘器,其对粉尘的去除效率可达到99.9%以上。我国《生活垃圾焚烧处理工程技术规范》(CJJ90-2009)中明确规定生活垃圾焚烧炉除尘装置必须采用布袋除尘器。而静电除尘器自20世纪70年代起被广泛应用于垃圾焚烧厂。随着环保观念增强,活性炭对二恶英与重金属吸附作用越来越被垃圾焚烧发电厂运用。In order to prevent secondary pollution to the environment during the waste incineration process, strict measures must be taken to control the emission of waste incineration flue gas by using the flue gas purification system. There are three treatment processes for the removal of acid gases in flue gas: dry method, semi-dry method and wet method. The semi-dry purification process can achieve high purification efficiency, low investment and operating costs, simple process, and no waste water. Most European incineration plants use the semi-dry method. The semi-dry method has been successfully applied in many cases in China, and has accumulated a certain amount of operating experience. It is suitable for incineration plants with higher emission standards. Now most of the waste incineration power plants under construction and to be built in China use the semi-dry method. . The dry purification process is relatively simple in process, low in investment, and convenient in operation and maintenance, but the purification efficiency of the dry process is relatively low, and it has been widely used in the construction of incineration plants in Japan in recent years. The wet purification process has the highest pollutant purification efficiency and can meet the most stringent emission standards. However, due to the complex process, more supporting equipment, high one-time investment and high operating costs, it is widely used in economically developed countries, but not widely used in China. As far as the removal effect of NOx is concerned, the removal rate of SCR to NOx has reached more than 90%, while the removal rate of SNCR to NOx can also reach about 50%. In terms of cost-efficiency analysis, SCR is basically equivalent to advanced incineration control systems, and is obviously more expensive than SNCR technology. Since the late 1980s, more waste incineration plants have used bag filters, and their dust removal efficiency can reach more than 99.9%. my country's "Technical Specifications for Domestic Waste Incineration Treatment Engineering" (CJJ90-2009) clearly stipulates that the dust removal device of domestic waste incinerator must use a bag filter. Electrostatic precipitators have been widely used in waste incineration plants since the 1970s. With the strengthening of the concept of environmental protection, the adsorption of activated carbon on dioxins and heavy metals is increasingly used by waste incineration power plants.
生活垃圾焚烧过程产生的烟气中,主要含有SO2、HCl、NOx、重金属和二噁英类等有害物质。近年来,除了传统的脱硫脱硝以及颗粒物的控制,二恶英污染引起了世界各国人民的普遍关注,而垃圾焚烧厂又是产生二噁英的主要来源之一,由于目前对二恶英的形成机理还没有达成统一的共识,因此通过仅控制焚烧参数来抑制二恶英的生成,其效果很难确定,因此后续对二噁英的处理就变得尤其关键。随着经济的发展,垃圾焚烧烟气排放标准也越来越严格,二噁英从当初的1mg/m3到0.5mg/m3,再到如今的0.1mg/m3,针对二噁英的处理也亟需进行新的变革。The flue gas produced during the incineration process of domestic waste mainly contains harmful substances such as SO 2 , HCl, NOx, heavy metals and dioxins. In recent years, in addition to the traditional desulfurization and denitrification and the control of particulate matter, dioxin pollution has attracted widespread attention from people all over the world, and waste incineration plants are one of the main sources of dioxins. The mechanism has not yet reached a unified consensus, so it is difficult to determine the effect of inhibiting the formation of dioxins by only controlling the incineration parameters, so the subsequent treatment of dioxins becomes particularly critical. With the development of the economy, the emission standards of waste incineration flue gas are becoming more and more stringent. Dioxin has changed from 1mg/m 3 to 0.5mg/m 3 at the beginning, and now it is 0.1mg/m 3 . Processing is also in dire need of new changes.
发明内容Contents of the invention
本发明提供一种生活垃圾热解焚烧装置烟气净化系统,本能够有效地去除焚烧烟气中的污染物,包括CO、SO2、NOX、二噁英等,尤其针对较难处理的二噁英进行了多段地处理,排放烟气中的二噁英浓度可达到优于国家标准三倍以上,起到了环境保护的目的。The present invention provides a flue gas purification system of a domestic waste pyrolysis incineration device, which can effectively remove pollutants in the incineration flue gas, including CO, SO 2 , NO X , dioxin, etc., especially for dioxins, which are difficult to handle. The dioxins have been treated in multiple stages, and the concentration of dioxins in the exhaust flue gas can reach more than three times higher than the national standard, which has achieved the purpose of environmental protection.
本发明的技术方案如下:Technical scheme of the present invention is as follows:
一种生活垃圾热解焚烧装置烟气净化系统,包括急冷塔、电磁脉冲除尘器、余热利用与冷却装置、炭纤维过滤装置、换热装置、二噁英化学催化装置、供水系统、烟气管道和引风机;其特征是急冷塔的进口端与生活垃圾热解焚烧装置的烟气管道连接,急冷塔的出口端与所述电磁脉冲除尘器连接,电磁脉冲除尘器与余热利用与冷却装置连接,余热利用与冷却装置与所述炭纤维过滤装置连接,炭纤维过滤装置与所述引风机连接,引风机出口连接换热装置,换热装置出口连接二噁英化学催化装置,二噁英化学催化装置与烟囱连接,烟气经过一系列净化最终排入大气。A flue gas purification system of a domestic waste pyrolysis incineration device, including a quench tower, an electromagnetic pulse dust collector, a waste heat utilization and cooling device, a carbon fiber filter device, a heat exchange device, a dioxin chemical catalyst device, a water supply system, and a flue gas pipeline and an induced draft fan; it is characterized in that the inlet end of the quenching tower is connected to the flue gas pipeline of the domestic waste pyrolysis incineration device, the outlet end of the quenching tower is connected with the electromagnetic pulse dust collector, and the electromagnetic pulse dust collector is connected with the waste heat utilization and cooling device , the waste heat utilization and cooling device is connected with the carbon fiber filter device, the carbon fiber filter device is connected with the induced draft fan, the outlet of the induced draft fan is connected with the heat exchange device, the outlet of the heat exchange device is connected with the dioxin chemical catalytic device, and the dioxin chemical The catalytic device is connected to the chimney, and the flue gas is finally discharged into the atmosphere after a series of purification.
所述急冷塔内上部布有喷淋管;经过降温后烟气温度为160℃-180℃。Spray pipes are arranged on the upper part of the quench tower; the temperature of the flue gas after cooling is 160°C-180°C.
所述电磁脉冲除尘器内由许多布袋组成,烟气中的污染物吸附在滤袋表面。The electromagnetic pulse dust collector is composed of many cloth bags, and the pollutants in the flue gas are adsorbed on the surface of the filter bags.
所述电磁脉冲除尘器设有脉冲阀。The electromagnetic pulse dust collector is provided with a pulse valve.
所述急冷塔和所述电磁脉冲除尘器之间的烟气管道上安装有助剂投加装置;投加氢氧化钙和反应助剂,去除烟气中的各种酸性气体及二噁英,烟气温度减到100℃-140℃。An additive dosing device is installed on the flue gas pipeline between the quench tower and the electromagnetic pulse dust collector; calcium hydroxide and reaction additives are added to remove various acid gases and dioxins in the flue gas, The flue gas temperature is reduced to 100°C-140°C.
所述电磁脉冲除尘器和所述炭纤维过滤装置之间连接余热利用与冷却装置;热能利用后的烟气再进入冷却装置,使烟气温度降至40℃-60℃。A waste heat utilization and cooling device is connected between the electromagnetic pulse dust collector and the carbon fiber filter device; the flue gas after thermal energy utilization enters the cooling device to reduce the temperature of the flue gas to 40°C-60°C.
所述炭纤维过滤装置由若干个炭纤维滤芯有序排列组成。The carbon fiber filter device is composed of several carbon fiber filter elements arranged in an orderly manner.
所述引风机位于所述炭纤维过滤装置后,采用变频调速,保证在不同工况下热解焚烧装置所需要的炉堂压力。The induced draft fan is located behind the carbon fiber filter device, and adopts frequency conversion speed regulation to ensure the furnace pressure required by the pyrolysis incineration device under different working conditions.
所述换热装置位于热解焚烧炉的上方;温度达到210℃-250℃。The heat exchange device is located above the pyrolysis incinerator; the temperature reaches 210°C-250°C.
所述二噁英化学催化装置是由若干个催化剂模块组合而成,整体为一竖立的长方体,模块内的催化剂能将二恶英催化氧化分解,生成无害物质。The dioxin chemical catalytic device is composed of several catalyst modules, and the whole is an upright cuboid. The catalyst in the module can catalyze, oxidize and decompose dioxin to generate harmless substances.
具体说明如下:The specific instructions are as follows:
所述急冷塔主要作用是对垃圾热解焚烧装置产生的烟气进行降温处理,所述急冷塔内上部布有喷淋管,所述喷淋管安装在急冷塔上部,冷却水从所述喷淋管中喷洒下来,对烟气进行急剧降温,冷却水循环利用。The main function of the quenching tower is to cool down the flue gas produced by the garbage pyrolysis incineration device. The upper part of the quenching tower is equipped with a spray pipe, and the spraying pipe is installed on the upper part of the quenching tower. Spray down the shower pipe to cool down the flue gas rapidly, and the cooling water is recycled.
所述电磁脉冲除尘器内由许多布袋组成,烟气中的污染物吸附在滤袋表面,可有效除酸、吸附二噁英等有害气体。The electromagnetic pulse dust collector is composed of many cloth bags, and the pollutants in the flue gas are adsorbed on the surface of the filter bags, which can effectively remove acid and adsorb harmful gases such as dioxins.
所述电磁脉冲除尘器设有脉冲阀,每次开一组脉冲阀来除去它所控制的那部分布袋或滤筒的灰尘,而其他的布袋或滤筒正常工作,隔一段时间后下一组脉冲阀打开,清理下一部分所述除尘器。The electromagnetic pulse dust collector is equipped with a pulse valve, and each time a group of pulse valves is opened to remove the dust in the part of the bag or filter cartridge it controls, while other bags or filter cartridges work normally, after a period of time, the next group The pulse valve opens and cleans the dust collector as described in the next section.
所述急冷塔和所述电磁脉冲除尘器之间的烟气管道上安装有助剂投加装置,投加氢氧化钙和反应助剂(活性炭粉末),去除烟气中的各种酸性气体及二噁英。An additive dosing device is installed on the flue gas pipeline between the quench tower and the electromagnetic pulse dust collector, and calcium hydroxide and reaction additives (activated carbon powder) are added to remove various acid gases and Dioxins.
所述炭纤维过滤装置由若干个炭纤维滤芯有序排列组成,可进一步对烟气中二噁英等有害气体进行过滤吸附。The carbon fiber filter device is composed of several carbon fiber filter elements arranged in an orderly manner, which can further filter and adsorb harmful gases such as dioxins in the flue gas.
所述引风机位于所述炭纤维过滤装置后,采用变频调速,其作用一是保证不同工况下所述热解焚烧装置所需要的炉堂压力,二是将所述炭纤维过滤装置出口烟气抽吸到所述换热装置。The induced draft fan is located behind the carbon fiber filter device and adopts frequency conversion speed regulation. Its function is to ensure the furnace pressure required by the pyrolysis incineration device under different working conditions, and the second is to discharge the carbon fiber filter device. The flue gas is drawn into the heat exchange device.
所述换热装置位于所述热解焚烧炉的上方,烟气由所述引风机送入所述换热装置,进行升温处理。The heat exchange device is located above the pyrolysis incinerator, and the flue gas is sent into the heat exchange device by the induced draft fan for temperature rise treatment.
所述二噁英化学催化装置是由若干个催化剂模块组合而成,整体为一竖立的长方体,模块内的催化剂能将二恶英催化氧化分解,生成无害的水蒸汽、二氧化碳、氯化氢等物质,使用寿命为16000小时以上。The dioxin chemical catalytic device is composed of several catalyst modules, and the whole is a vertical cuboid. The catalyst in the module can catalyze and oxidize and decompose dioxin to generate harmless water vapor, carbon dioxide, hydrogen chloride and other substances , The service life is more than 16000 hours.
与现有技术相比,本发明具有以下有益效果:Compared with the prior art, the present invention has the following beneficial effects:
1、本系统能够将生活垃圾热焚烧排放的烟气净化达到甚至明显优于国家标准,并可考虑利用烟气中的显热来生产低压蒸汽供工厂生产生活使用;1. This system can purify the flue gas emitted by thermal incineration of domestic waste to meet or even significantly exceed the national standard, and can consider using the sensible heat in the flue gas to produce low-pressure steam for production and daily use in factories;
2、本系统采用两级处理烟气中二噁英的方法,处理后二噁英浓度可达到优于国家标准;2. This system adopts a two-stage method for treating dioxins in flue gas, and the concentration of dioxins after treatment can reach higher than the national standard;
3、本系统将经过炭纤维过滤装置的烟气吸入换热装置进行升温,利于后续的二噁英化学催化装置处理;3. This system sucks the flue gas through the carbon fiber filter device into the heat exchange device to heat up, which is beneficial to the subsequent treatment of dioxin chemical catalyst device;
4、本系统只有两个水泵,一个气泵和一个引风机,减少辅助设备,增加该系统的安全可靠性,降低该系统的运行成本;4. The system only has two water pumps, one air pump and one induced draft fan, which reduces auxiliary equipment, increases the safety and reliability of the system, and reduces the operating cost of the system;
5、对焚烧烟气进行了较为彻底的净化,减少了烟气的排放,降低了环境污染。5. The incineration flue gas has been thoroughly purified, reducing the emission of flue gas and reducing environmental pollution.
6、本发明提供的生活垃圾热解焚烧装置烟气净化系统能够有效地去除焚烧烟气中的污染物,包括CO、SO2、NOX、二噁英等,尤其是排放烟气中的二噁英浓度可满足国家标准(<0.03ng/m3)。6. The flue gas purification system of the domestic waste pyrolysis incineration device provided by the present invention can effectively remove pollutants in the incineration flue gas, including CO, SO 2 , NO X , dioxin, etc., especially dioxins in the exhaust flue gas. The concentration of oxins can meet the national standard (<0.03ng/m 3 ).
附图说明Description of drawings
图1:生活垃圾热解焚烧装置烟气净化系统的结构示意图。Figure 1: Schematic diagram of the structure of the flue gas purification system of the domestic waste pyrolysis incinerator.
其中,1、生活垃圾热解焚烧炉;2、急冷塔;3、电磁脉冲除尘器;4、余热利用与冷却装置;5、炭纤维过滤装置;6、引风机;7、换热装置;8、二噁英化学催化装置;9、烟囱;10、助剂投加装置1;11、助剂投加装置2;12、喷淋管;13、布袋。Among them, 1. Domestic waste pyrolysis incinerator; 2. Rapid cooling tower; 3. Electromagnetic pulse dust collector; 4. Waste heat utilization and cooling device; 5. Carbon fiber filter device; 6. Induced fan; 7. Heat exchange device; 8 1. Dioxin chemical catalyst device; 9. Chimney; 10. Auxiliary dosing device 1; 11. Auxiliary dosing device 2; 12. Spray pipe; 13. Cloth bag.
具体实施方式detailed description
下面结合附图对本发明作进一步说明:The present invention will be further described below in conjunction with accompanying drawing:
以下结合附图和具体实施例对本发明提出的生活垃圾热解焚烧装置烟气净化系统作进一步详细说明。根据下面说明和权利要求书,本发明的优点和特征将更清楚。需说明的是,附图均采用非常简化的形式且均使用非精准的比率,仅用以方便、明晰地辅助说明本发明实施例的目的。The flue gas purification system of the domestic waste pyrolysis incineration device proposed by the present invention will be further described in detail below in conjunction with the accompanying drawings and specific embodiments. Advantages and features of the present invention will be apparent from the following description and claims. It should be noted that the drawings are all in a very simplified form and use imprecise ratios, which are only used to facilitate and clearly assist the purpose of illustrating the embodiments of the present invention.
请参考图1,图1为本发明实施例提供的生活垃圾热解焚烧装置烟气净化系统的结构示意图。Please refer to FIG. 1 , which is a schematic structural diagram of a flue gas purification system of a domestic waste pyrolysis incineration device provided by an embodiment of the present invention.
本发明实施例提供一种生活垃圾热解焚烧装置烟气净化系统,其包括急冷塔(2)、电磁脉冲除尘器(3)、余热利用与冷却装置(4)、炭纤维过滤装置(5)、换热装置(7)、二噁英化学催化装置(8)、供水系统、烟气管道和引风机(6),所述急冷塔(2)的进口端与生活垃圾热解焚烧装置的烟气管道连接,所述急冷塔(2)的出口端与所述电磁脉冲除尘器(3)连接,所述电磁脉冲除尘器(3)与余热利用与冷却装置(4)连接,所述余热利用与冷却装置(4)与所述炭纤维过滤装置(5)连接,所述炭纤维过滤装置(5)与所述引风机(6)连接,烟气经过所述引风机(6)送入换热装置(7)升温后,进入所述二噁英化学催化装置(8),所述二噁英化学催化装置(8)与烟囱(9)连接,烟气经过一系列净化最终排入大气。An embodiment of the present invention provides a flue gas purification system of a domestic waste pyrolysis incineration device, which includes a quench tower (2), an electromagnetic pulse dust collector (3), a waste heat utilization and cooling device (4), and a carbon fiber filter device (5) , a heat exchange device (7), a dioxin chemical catalyst device (8), a water supply system, a flue gas pipeline and an induced draft fan (6), the inlet end of the quench tower (2) is connected to the smoke of the domestic waste pyrolysis incineration device The air pipeline is connected, the outlet end of the quench tower (2) is connected with the electromagnetic pulse dust collector (3), the electromagnetic pulse dust collector (3) is connected with the waste heat utilization and cooling device (4), and the waste heat utilization The cooling device (4) is connected with the carbon fiber filter device (5), the carbon fiber filter device (5) is connected with the induced draft fan (6), and the flue gas is sent into the fan (6) through the induced draft fan (6). After the heating device (7) heats up, it enters the dioxin chemical catalysis device (8), and the dioxin chemical catalysis device (8) is connected with the chimney (9), and the flue gas is finally discharged into the atmosphere after a series of purification.
所述急冷塔(2)内上部布有喷淋管(12),所述喷淋管(12)安装在所述急冷塔上部,冷却水从所述喷淋管12中喷洒下来。A spray pipe (12) is arranged on the inner upper part of the quench tower (2), and the spray pipe (12) is installed on the upper part of the quench tower, and cooling water is sprayed down from the spray pipe 12.
所述电磁脉冲除尘器(3)内由许多布袋(13)组成,烟气中的污染物吸附在滤袋表面,可有效除酸、吸附二噁英等有害气体。The electromagnetic pulse dust collector (3) is composed of many cloth bags (13), and the pollutants in the flue gas are adsorbed on the surface of the filter bags, which can effectively remove acid and adsorb harmful gases such as dioxins.
所述急冷塔(2)和所述电磁脉冲除尘器(3)之间的烟气管道上安装有助剂投加装置1(10)、助剂投加装置2(11),投加氢氧化钙和反应助剂(活性炭粉末),去除烟气中的各种酸性气体及二噁英。An auxiliary agent dosing device 1 (10), an auxiliary agent dosing device 2 (11) are installed on the flue gas pipeline between the quench tower (2) and the described electromagnetic pulse dust collector (3), and the hydrogen oxidation Calcium and reaction additives (activated carbon powder) to remove various acid gases and dioxins in the flue gas.
所述生活垃圾热解焚烧装置烟气净化系统的各个主要部位都安装有热电偶,运用PLC自动化控制系统来监控温度变化,同时还可以控制助剂的投加、风机的功率等。Thermocouples are installed in each main part of the flue gas purification system of the domestic waste pyrolysis incineration device, and the PLC automatic control system is used to monitor the temperature change, and at the same time, the addition of additives and the power of the fan can also be controlled.
当本系统正常运行时,生活垃圾在所述热解焚烧炉(1)中进行热分解,炉体直径1.2m,高度1.88m,采用Q235碳钢,内层是耐火高温材料,外壁钢板6mm厚,内胆钢板8mm厚,耐火材料层厚100mm,每天工作时长8-10h,处理量10t/d,炉内温度可达700℃-900℃。热解焚烧所产生的烟气通过烟气管道送入所述急冷塔(2),所述急冷塔(2)中的所述喷淋管(12)开始喷水,冷却水对烟气进行急剧冷却,并且冷却水可以循环利用,经过降温后烟气温度降为160℃-180℃,降温后在烟气管道中通过助剂投加装置1(10)加投氢氧化钙,通过助剂投加装置2(11)加投活性炭粉末;石灰泵和活性炭粉泵额定功率均为0.75kw,投加量由PLC自动化控制系统进行调节,主要降低烟气中的各种酸性气体及二噁英,氢氧化钙中和酸性气体,活性炭粉末吸附二噁英。烟气经过急冷降温、投加助剂反应后,温度衰减到100℃-140℃,其中未反应的氢氧化钙及反应助剂(活性炭粉末),进入所述电磁脉冲布袋除尘器(3),吸附在滤袋表面,可有效除酸、吸附二噁英等有害气体,烟气中的颗粒物含量降低到5mg/m3以下,NOx降低到400mg/m3左右,SO2降低到100mg/m3左右,二噁英降低到2~3ng/m3。因为炭纤维吸附所需温度较低,所述电磁脉冲除尘器(3)出口的高温烟气管道段设所述余热回收利用装置(4),将高温烟气中热能用换热装置收集起来,热能利用后的烟气再进入冷却装置继续降温,使烟气温度降至40℃-60℃。烟气冷却后进入所述炭纤维过滤装置(5),该装置由若干个炭纤维滤芯有序排列组成,活性炭吸附材料价格10w/t,用量150kg,可酸洗,进一步对烟气中二噁英等有害气体进行过滤吸附,处理完的烟气中二噁英含量降低到1ng/m3以下。所述引风机(6)设置在所述炭纤维过滤装置(5)后方,所述引风机(6)采用变频调速,其作用一是保证不同工况下垃圾热解焚烧装置(1)所需要的炉堂压力,使焚烧热解炉中处于负压状态;二是将所述炭纤维过滤装置(5)出口烟气抽吸到所述换热装置(7)中,因为所采用的新型脱二噁英催化剂适用温度为180℃-250℃,烟气经过所述换热装置(7)达到210℃-250℃,然后进入所述二噁英化学催化装置(8)。该装置由若干个催化剂模块组合而成,整体为一竖立的长方体,催化剂采用的是上海某公司开发的新型脱二噁英催化剂,催化剂为蜂窝状或颗粒状,价格为13w/m3,模块内的催化剂能将二恶英催化氧化分解,生成无害的水蒸汽、二氧化碳、氯化氢等物质,使用寿命为16000小时以上。经过处理后的烟气可达到表1所示效果,符合《生活垃圾焚烧污染控制标准》(GB18485-2014)中对于生活垃圾焚烧炉排放烟气污染物限值的要求,最后通过烟囱(9)排入大气。When the system is in normal operation, domestic garbage is thermally decomposed in the pyrolysis incinerator (1). The furnace body has a diameter of 1.2m and a height of 1.88m. It is made of Q235 carbon steel. The inner layer is refractory high-temperature material, and the outer wall steel plate is 6mm thick. , 8mm thick inner tank steel plate, 100mm thick refractory material layer, 8-10h working hours per day, 10t/d processing capacity, and 700°C-900°C furnace temperature. The flue gas produced by pyrolysis and incineration is sent into the quenching tower (2) through the flue gas pipeline, and the spray pipe (12) in the quenching tower (2) starts to spray water, and the cooling water rapidly cools the flue gas. Cooling, and the cooling water can be recycled. After cooling, the temperature of the flue gas is reduced to 160°C-180°C. Adding device 2 (11) adds activated carbon powder; the rated power of the lime pump and activated carbon powder pump is 0.75kw, and the dosage is adjusted by the PLC automatic control system, mainly to reduce various acid gases and dioxins in the flue gas, Calcium hydroxide neutralizes acid gas, and activated carbon powder adsorbs dioxins. After the flue gas is rapidly cooled and reacted by adding additives, the temperature decays to 100°C-140°C, and the unreacted calcium hydroxide and reaction additives (activated carbon powder) enter the electromagnetic pulse bag filter (3), Adsorbed on the surface of the filter bag, it can effectively remove acid and adsorb harmful gases such as dioxins. The content of particulate matter in the flue gas is reduced to below 5mg/ m3 , NOx is reduced to about 400mg/ m3 , and SO2 is reduced to 100mg/ m3 About 2 ~ 3ng/m 3 of dioxins. Because the temperature required for carbon fiber adsorption is low, the high-temperature flue gas pipeline section at the outlet of the electromagnetic pulse dust collector (3) is provided with the waste heat recovery and utilization device (4), which collects heat energy in the high-temperature flue gas with a heat exchange device, The flue gas after thermal energy utilization enters the cooling device to continue to cool down, so that the temperature of the flue gas drops to 40°C-60°C. After the flue gas is cooled, it enters the carbon fiber filter device (5), which is composed of several carbon fiber filter elements arranged in an orderly manner. The price of the activated carbon adsorption material is 10w/t, and the consumption is 150kg. Dioxin and other harmful gases are filtered and adsorbed, and the dioxin content in the treated flue gas is reduced to below 1ng/ m3 . The induced draft fan (6) is arranged behind the carbon fiber filtering device (5), and the induced draft fan (6) adopts frequency conversion speed regulation, and its function is to ensure The required furnace pressure makes the incineration pyrolysis furnace in a negative pressure state; the second is to suck the outlet flue gas of the carbon fiber filter device (5) into the heat exchange device (7), because the adopted new The applicable temperature of the dioxin removal catalyst is 180°C-250°C, the flue gas passes through the heat exchange device (7) to reach 210°C-250°C, and then enters the dioxin chemical catalyst device (8). The device is composed of several catalyst modules, and the whole is a vertical cuboid. The catalyst is a new type of de-dioxin catalyst developed by a company in Shanghai. The catalyst is honeycomb or granular, and the price is 13w/m 3 . The catalyst inside can catalyze and oxidize and decompose dioxin to produce harmless water vapor, carbon dioxide, hydrogen chloride and other substances, and the service life is more than 16,000 hours. The treated flue gas can achieve the effects shown in Table 1, and meets the requirements of the "Standards for Pollution Control of Domestic Waste Incineration" (GB18485-2014) for the limit value of flue gas pollutants emitted by domestic waste incinerators, and finally passes through the chimney (9) into the atmosphere.
表1处理后烟气污染物指标Table 1 Flue gas pollutant indicators after treatment
显然,本领域的技术人员可以对本发明进行各种改动和变形而不脱离本发明的精神和范围。这样,倘若本发明的这些修改和变型属于本发明权利要求及其等同技术的范围之内,则本发明也意图包含这些改动和变型在内。Obviously, those skilled in the art can make various changes and modifications to the present invention without departing from the spirit and scope of the present invention. Thus, if these modifications and variations of the present invention fall within the scope of the claims of the present invention and their equivalent technologies, the present invention also intends to include these modifications and variations.
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