CN107376609A - A kind of flue gas ash removal filters heat utilization integrated technique - Google Patents

A kind of flue gas ash removal filters heat utilization integrated technique Download PDF

Info

Publication number
CN107376609A
CN107376609A CN201710756763.2A CN201710756763A CN107376609A CN 107376609 A CN107376609 A CN 107376609A CN 201710756763 A CN201710756763 A CN 201710756763A CN 107376609 A CN107376609 A CN 107376609A
Authority
CN
China
Prior art keywords
heat utilization
flue gas
filter layer
ash removal
integrated technique
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
CN201710756763.2A
Other languages
Chinese (zh)
Inventor
陆维光
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.)
Taicang Dust Removal Equipment Factory
Original Assignee
Taicang Dust Removal Equipment Factory
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 Taicang Dust Removal Equipment Factory filed Critical Taicang Dust Removal Equipment Factory
Priority to CN201710756763.2A priority Critical patent/CN107376609A/en
Publication of CN107376609A publication Critical patent/CN107376609A/en
Pending legal-status Critical Current

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation 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
    • B01D53/14Separation 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 by absorption
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation 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
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G7/00Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
    • F23G7/06Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases
    • F23G7/061Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases with supplementary heating
    • F23G7/063Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases with supplementary heating electric heating
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2258/00Sources of waste gases
    • B01D2258/02Other waste gases
    • B01D2258/0283Flue gases
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2201/00Pretreatment
    • F23G2201/60Separating
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2206/00Waste heat recuperation
    • F23G2206/20Waste heat recuperation using the heat in association with another installation

Landscapes

  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Chemical & Material Sciences (AREA)
  • Analytical Chemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Health & Medical Sciences (AREA)
  • Biomedical Technology (AREA)
  • Mechanical Engineering (AREA)
  • General Engineering & Computer Science (AREA)
  • Treating Waste Gases (AREA)

Abstract

The invention discloses a kind of flue gas ash removal to filter heat utilization integrated technique, including step:Flue gas is introduced into packed tower from bottom with air-introduced machine, as absorbing liquid, organic phase and aqueous phase volume ratio are 1 for the mixing of the organic phase and aqueous phase that are introduced on packed tower top:(4.5~10), absorbing liquid recycles;If the smoke mixture that packed tower is treated passes through dried layer filler filter layer successively, the filler filter layer includes the dry load and screen pack being continually fed into, and obtains handling gas;Obtained processing gas is passed through the fiery room of electricity, the fiery room of electricity is beaten electric arc and supplied oxygen, and burning obtains ashes gas;Obtained ashes gas reclaims heat utilization by hot channel.Place's pollution of the present invention and heat utilization mode are ingenious, thorough, can be handled a variety of flue gases of complicated component, and obtain relatively effective Land use systems heat utilization, so saved bit by bit a valuable experience again for engineering.

Description

A kind of flue gas ash removal filters heat utilization integrated technique
Technical field
The present invention relates to cleaner and technology field, especially a kind of flue gas ash removal filtering heat utilization integrated technique.
Background technology
For chemical industry, environmental project and daily life, the control of flue gas seems more and more important, but mesh There is the problem of such or such in the processing of preceding flue gas, be difficult to reasonably be handled for certain form of flue gas and sharp With.
The dedusting of industrial smoke and using seemingly two problems, however, removing generally directed to flue gas under current situation The problem of dirt has been individual headache, if it is desired to which its purification may undertake to do what is apparently beyond one's ability.And also tend to handle for the equipment of purification This higher suspension content gas mixture of flue gas.But flue gas ash removal, purification and heat utilization are again in some cases to unite One, so both solved the problems, such as smoke pollution environment, and also solved resource utilization issue and recuperation of heat along band, it is more at one stroke , it is to have very much valuable process exploitation in the transitional period one.
The content of the invention
Goal of the invention:In order to improve the processing of the summation of this multiphase mixture of flue gas, present invention design is a kind of high performance Flue gas ash removal filters heat utilization integrated technique, to solve problems of the prior art.
The content of the invention:A kind of flue gas ash removal filters heat utilization integrated technique, comprises the following steps:
(1), with air-introduced machine by flue gas from bottom introduce packed tower, packed tower top introduce organic phase and aqueous phase mixing make For absorbing liquid, organic phase and aqueous phase volume ratio are 1:(4.5~10), absorbing liquid recycles;
(2)If, by packed tower treat smoke mixture pass through dried layer filler filter layer successively, the filler filter layer includes The dry load and screen pack being continually fed into, obtain handling gas;
(3), by step(2)Obtained processing gas is passed through the fiery room of electricity, and the fiery room of electricity is beaten electric arc and supplied oxygen, and incendivity thing is in electric arc and oxygen Effect is lower to burn, and obtains ashes gas;
(4), step(3)Obtained ashes gas reclaims heat utilization by hot channel.
Preferably, step(2)In, the treated smoke mixture of packed tower is successively by the first filler filter layer, the Two filler filter layers, the 3rd filler filter layer, the dry load of the first filler filter layer are to contain calcium chloride and copper chloride Mixture, the dry load of the second filler filter layer is the mixture comprising sodium acid carbonate, potassium carbonate, and the described 3rd fills out Expect filter layer dry load be comprising mesopore molecular sieve, activated carbon, bentonite, nano material mixture.Filler filter layer Materialization set and the restriction of dry load considers alkaline gas, sour gas and fuel gas, and make cost and effect Benefit is obtained for optimization.
Preferably, step(1)In, the organic phase include alcohols, esters, ketone, one kind in halogenated hydrocarbon or Its mixture.Several organic phases represent the material of most of polarity and molecular characterization above, compatible more can have Machine thing.
Further, the alcohols is the band side chain saturated monohydroxy alcohol of carbon number 3 ~ 5, and the esters are carbon number 4 ~ 8 Saturation monobasic ester, the ketone is the aliphatic ketone that carbon number is 3 ~ 6, and the halogenated hydrocarbon is the hydrocarbon of carbon number 3 ~ 8 Chloro thing or bromo-derivative.The setting of several organic matters considers the optimization that material is easy to get with power efficiency cost above.
Preferably, step(4)Described in hot channel there is heat insulation layer.Heat insulation layer is incubated to hot channel.
Further, the heat insulation layer is one kind in pearl cotton, mineral wool, ethylene propylene diene rubber, nitrile rubber.It is several above Kind material heat insulating ability performance is fabulous.
Preferably, step(3)In, the burning voltage of the electric arc is 25 ~ 50V.The burning voltage of electric arc makes electric arc Excite combustible combustion reliable and stable and composite economy principle.
Compared to the prior art, the beneficial effects of the present invention are:A kind of flue gas ash removal filtering heat utilization one of the present invention Body technology, the simple efficiency high of technique.The enterprise of packed tower, which exchanges and strengthens to absorb, reaches the material of flue gas and liquid and heat exchange To a greater part of;The various levels of material that filler filter layer includes flue gas screens one by one, and igniting chamber obtains combustible combustion Certain energy is simultaneously used.Place's pollution of the present invention and heat utilization mode are ingenious, thorough, can be by a variety of cigarettes of complicated component Gas is handled, and obtains relatively effective Land use systems -- heat utilization, so again for engineering saved bit by bit one it is valuable Experience.
Embodiment
In order to illustrate more clearly of the embodiment of the present application or technical scheme of the prior art, letter will be made to embodiment below Single introduction.
A kind of flue gas ash removal filters heat utilization integrated technique, comprises the following steps:
(1), with air-introduced machine by flue gas from bottom introduce packed tower, packed tower top introduce organic phase and aqueous phase mixing make For absorbing liquid, organic phase and aqueous phase volume ratio are 1:(4.5~10), absorbing liquid recycles;The organic phase includes alcohols, ester One kind or its mixture in class, ketone, halogenated hydrocarbon, the alcohols are the band side chain saturated monohydroxy alcohol of carbon number 3 ~ 5, The esters are the saturation monobasic ester of carbon number 4 ~ 8, and the ketone is the aliphatic ketone that carbon number is 3 ~ 6, the halogenated hydrocarbons Class is the chloro thing or bromo-derivative of the hydrocarbon of carbon number 3 ~ 8;
(2), the treated smoke mixture of packed tower fills out by the first filler filter layer, the second filler filter layer, the 3rd successively Expect filter layer, the filler filter layer includes the dry load and screen pack being continually fed into, and obtains handling gas;First filler The dry load of filter layer is the mixture containing calcium chloride and copper chloride, and the dry load of the second filler filter layer is bag Mixture containing sodium acid carbonate, potassium carbonate, the dry load of the 3rd filler filter layer are to include mesopore molecular sieve, activity Charcoal, bentonite, the mixture of nano material;
(3), by step(2)Obtained processing gas is passed through the fiery room of electricity, and the fiery room of electricity is beaten electric arc and supplied oxygen, and incendivity thing is in electric arc and oxygen Effect is lower to burn, and obtains ashes gas, the burning voltage of the electric arc is 25 ~ 50V;
(4), step(3)Obtained ashes gas reclaims heat utilization by hot channel, and the hot channel has heat insulation layer, the thermal insulation Layer is pearl cotton, one kind in mineral wool, ethylene propylene diene rubber, nitrile rubber.
Finally, it is to be noted that, term " comprising ", "comprising" or its any other variant be intended to it is non-exclusive Property includes, so that process, method, article or equipment including a series of elements not only include those key elements, and Also include the other element that is not expressly set out, or also include for this process, method, article or equipment inherently Key element.

Claims (7)

1. a kind of flue gas ash removal filters heat utilization integrated technique, it is characterised in that comprises the following steps:
(1), with air-introduced machine by flue gas from bottom introduce packed tower, packed tower top introduce organic phase and aqueous phase mixing make For absorbing liquid, organic phase and aqueous phase volume ratio are 1:(4.5~10), absorbing liquid recycles;
(2)If, by packed tower treat smoke mixture pass through dried layer filler filter layer successively, the filler filter layer includes The dry load and screen pack being continually fed into, obtain handling gas;
(3), by step(2)Obtained processing gas is passed through the fiery room of electricity, and the fiery room of electricity is beaten electric arc and supplied oxygen, and incendivity thing is in electric arc and oxygen Effect is lower to burn, and obtains ashes gas;
(4), step(3)Obtained ashes gas reclaims heat utilization by hot channel.
A kind of 2. flue gas ash removal filtering heat utilization integrated technique according to claim 1, it is characterised in that step(2)In, The treated smoke mixture of packed tower passes through the first filler filter layer, the second filler filter layer, the 3rd filler filter layer successively, The dry load of the first filler filter layer is the mixture containing calcium chloride and copper chloride, the second filler filter layer Dry load is the mixture comprising sodium acid carbonate, potassium carbonate, and the dry load of the 3rd filler filter layer is comprising mesoporous Molecular sieve, activated carbon, bentonite, the mixture of nano material.
A kind of 3. flue gas ash removal filtering heat utilization integrated technique according to claim 1, it is characterised in that step(1)In, The organic phase includes alcohols, esters, ketone, one kind in halogenated hydrocarbon or its mixture.
4. a kind of flue gas ash removal filtering heat utilization integrated technique according to claim 3, it is characterised in that the alcohols is The band side chain saturated monohydroxy alcohol of carbon number 3 ~ 5, the esters are the saturation monobasic ester of carbon number 4 ~ 8, and the ketone is carbon Atomicity is 3 ~ 6 aliphatic ketone, and the halogenated hydrocarbon is the chloro thing or bromo-derivative of the hydrocarbon of carbon number 3 ~ 8.
A kind of 5. flue gas ash removal filtering heat utilization integrated technique according to claim 1, it is characterised in that step(4)In The hot channel has heat insulation layer.
A kind of 6. flue gas ash removal filtering heat utilization integrated technique according to claim 5, it is characterised in that the heat insulation layer For one kind in pearl cotton, mineral wool, ethylene propylene diene rubber, nitrile rubber.
A kind of 7. flue gas ash removal filtering heat utilization integrated technique according to claim 1, it is characterised in that step(3)In, The burning voltage of the electric arc is 25 ~ 50V.
CN201710756763.2A 2017-08-29 2017-08-29 A kind of flue gas ash removal filters heat utilization integrated technique Pending CN107376609A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201710756763.2A CN107376609A (en) 2017-08-29 2017-08-29 A kind of flue gas ash removal filters heat utilization integrated technique

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201710756763.2A CN107376609A (en) 2017-08-29 2017-08-29 A kind of flue gas ash removal filters heat utilization integrated technique

Publications (1)

Publication Number Publication Date
CN107376609A true CN107376609A (en) 2017-11-24

Family

ID=60346504

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201710756763.2A Pending CN107376609A (en) 2017-08-29 2017-08-29 A kind of flue gas ash removal filters heat utilization integrated technique

Country Status (1)

Country Link
CN (1) CN107376609A (en)

Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102049181A (en) * 2009-10-27 2011-05-11 中国石油化工股份有限公司 Purification method of sulfur-containing organic waste gas
CN102068890A (en) * 2010-12-24 2011-05-25 环境保护部华南环境科学研究所 Method and device for treating complex industrial organic waste gas
CN104524947A (en) * 2015-01-07 2015-04-22 广东红棉乐器有限公司 Spraying organic waste gas treatment system and treatment method based on molecular sieve adsorption technology
CN105080269A (en) * 2015-08-19 2015-11-25 江苏大德能源科技发展有限公司 Carbon black tail gas purification system
CN205570019U (en) * 2016-04-21 2016-09-14 于立东 Multi -functional dust peculiar smell absorbs purification unit
CN106237820A (en) * 2016-10-19 2016-12-21 中冶焦耐(大连)工程技术有限公司 A kind of process technique containing VOCs industrial waste gas and system
CN106362547A (en) * 2015-07-23 2017-02-01 中国石油化工股份有限公司 Sulfur-containing organic waste gas treatment method and sulfur-containing organic waste gas treatment apparatus
CN206152611U (en) * 2016-10-19 2017-05-10 中冶焦耐(大连)工程技术有限公司 Processing system who contains VOCs industrial waste gas

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102049181A (en) * 2009-10-27 2011-05-11 中国石油化工股份有限公司 Purification method of sulfur-containing organic waste gas
CN102068890A (en) * 2010-12-24 2011-05-25 环境保护部华南环境科学研究所 Method and device for treating complex industrial organic waste gas
CN104524947A (en) * 2015-01-07 2015-04-22 广东红棉乐器有限公司 Spraying organic waste gas treatment system and treatment method based on molecular sieve adsorption technology
CN106362547A (en) * 2015-07-23 2017-02-01 中国石油化工股份有限公司 Sulfur-containing organic waste gas treatment method and sulfur-containing organic waste gas treatment apparatus
CN105080269A (en) * 2015-08-19 2015-11-25 江苏大德能源科技发展有限公司 Carbon black tail gas purification system
CN205570019U (en) * 2016-04-21 2016-09-14 于立东 Multi -functional dust peculiar smell absorbs purification unit
CN106237820A (en) * 2016-10-19 2016-12-21 中冶焦耐(大连)工程技术有限公司 A kind of process technique containing VOCs industrial waste gas and system
CN206152611U (en) * 2016-10-19 2017-05-10 中冶焦耐(大连)工程技术有限公司 Processing system who contains VOCs industrial waste gas

Similar Documents

Publication Publication Date Title
Chen et al. Influences of activation agent impregnated sewage sludge pyrolysis on emission characteristics of volatile combustion and De-NOx performance of activated char
CN106622121A (en) Saturated activated carbon regeneration system with low energy consumption and method thereof
CN203810391U (en) Novel ultra-low emission power generation system by burning low-calorific value fuel
Yang et al. Experimental and kinetic study on Hg0 removal by microwave/hydrogen peroxide modified seaweed-based porous biochars
CN105195092A (en) Sludge-based charcoal and preparation method thereof
CN103480336B (en) A kind of modified biomass activates burnt demercuration adsorbent and preparation method thereof
CN110104646A (en) A kind of utilization of resources system and method for active carbon preparation
CN104984743A (en) Preparation method of waste-derived adsorbent for removing mercury, and product thereof
CN103693643A (en) Bamboo-based activated carbon for flue gas desulfurization
CN106402898A (en) Dioxin treatment system of hazardous waste incineration furnace
CN104624018A (en) Method for separating and comprehensively utilizing gases in carbon black tail gas and device for realizing method
CN106378120B (en) Regenerating active carbon system and regeneration method
CN203540263U (en) Efficient purification system for power station flue gas
CN110054185A (en) The system and method for active carbon is produced in a kind of thermal power plant coal pyrolysis charring activation
CN103900076A (en) Ultralow-emission power generation system using low-calorific-value fuel for combustion
CN101648771B (en) Sludge drying and carbonizing processing device
CN201511035U (en) Indirect thermal desorption equipment
CN201147667Y (en) Oxygen-enriched desorption recovery device for pressure swing adsorption nitrogen making
CN107376609A (en) A kind of flue gas ash removal filters heat utilization integrated technique
CN210568466U (en) Device for modifying high-temperature fly ash generated in waste incineration
CN106482120A (en) The method and apparatus for organic solid waste process being carried out using recirculating fluidized bed
CN208859618U (en) A kind of useless activated coke Incineration in CFB system
CN111017884A (en) Method for preparing industrial sulfuric acid from desulfurization waste liquid by slurry spraying method
CN103215077B (en) Control device of thermal cycle continuous coal gangue pyrolysis gasification comprehensive device
CN205367741U (en) Regeneration system is retrieved to useless charcoal with burning furnace is burnt in gyration

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication
RJ01 Rejection of invention patent application after publication

Application publication date: 20171124