CN110252097A - A kind of aluminium stone kiln breaks key denitration device and method of denitration - Google Patents

A kind of aluminium stone kiln breaks key denitration device and method of denitration Download PDF

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Publication number
CN110252097A
CN110252097A CN201910679972.0A CN201910679972A CN110252097A CN 110252097 A CN110252097 A CN 110252097A CN 201910679972 A CN201910679972 A CN 201910679972A CN 110252097 A CN110252097 A CN 110252097A
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denitration
aluminium stone
stone kiln
ammonia
key
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张久明
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Star Yu Energy-Saving Polytron Technologies Inc
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Star Yu Energy-Saving Polytron Technologies Inc
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    • 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
    • B01D53/46Removing components of defined structure
    • B01D53/54Nitrogen compounds
    • B01D53/56Nitrogen oxides
    • 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
    • B01D53/77Liquid phase processes
    • B01D53/79Injecting reactants
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23LSUPPLYING AIR OR NON-COMBUSTIBLE LIQUIDS OR GASES TO COMBUSTION APPARATUS IN GENERAL ; VALVES OR DAMPERS SPECIALLY ADAPTED FOR CONTROLLING AIR SUPPLY OR DRAUGHT IN COMBUSTION APPARATUS; INDUCING DRAUGHT IN COMBUSTION APPARATUS; TOPS FOR CHIMNEYS OR VENTILATING SHAFTS; TERMINALS FOR FLUES
    • F23L7/00Supplying non-combustible liquids or gases, other than air, to the fire, e.g. oxygen, steam
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F27FURNACES; KILNS; OVENS; RETORTS
    • F27DDETAILS OR ACCESSORIES OF FURNACES, KILNS, OVENS, OR RETORTS, IN SO FAR AS THEY ARE OF KINDS OCCURRING IN MORE THAN ONE KIND OF FURNACE
    • F27D17/00Arrangements for using waste heat; Arrangements for using, or disposing of, waste gases
    • F27D17/004Systems for reclaiming waste heat
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2258/00Sources of waste gases
    • B01D2258/02Other waste gases
    • B01D2258/0283Flue gases
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/25Process efficiency

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

Abstract

The invention discloses a kind of aluminium stone kilns to break key denitration device and method of denitration, including aluminium stone kiln, aluminium stone kiln outer wall upper and lower part is connected with flue, fresh air pipeline respectively, and smoke backflow pipeline is connected on flue, and wind-mixer is arranged in smoke backflow pipeline and fresh air pipeline intersection;Flue end connects desulphurization denitration deduster one, catcher, desulphurization denitration deduster two, desulphurization denitration deduster one, two sewage draining exit of desulphurization denitration deduster and circulatory pool connection, two air outlet connection water mist separator of desulfurization and dedusting reaction kettle, water mist separator wind pipe is connect with chimney, it further include tank used for storing ammonia, the broken key machine of nitrogen oxides, wherein nitrogen oxides breaks key machine upper end and is equipped with pipe-line mixer, and pipe-line mixer passes through the fume high-temperature area connection of mixing duct and aluminium stone kiln;Tank used for storing ammonia by for ammonia pump and pipe-line mixer connection for ammonia.The entire simple process of the present invention, scrap build is low in cost, and denitration efficiency is high, fully meets environmental requirement.

Description

A kind of aluminium stone kiln breaks key denitration device and method of denitration
Technical field:
The present invention relates to field of environment protection equipment more particularly to a kind of aluminium stone kiln to break key denitration device and method of denitration.
Background technique:
National stove carries out minimum discharge transformation within 2019.New rule boiler emission limit specific requirement: soot dust granule object 10mg/m3, sulfur dioxide 20mg/m3, nitrogen oxides 50mg/m3, stove is the equipment that present stove industry all generallys use, this Kind of stove is unenclosed construction, and stove feeds from front, behind discharge, center is high-temperature region, causes flue gas oxygen content super in this way It marks (18%), also, calcination process is also open type, control flue gas oxygen content is extremely important.
China's stove energy consumption accounts for industrial energy consumption and accounts for about 1/3, and the stove thermal efficiency that is averaged is lower by 20% or so than external, national If the average energy conservation 10% of industrial furnace, the energy of saving is equivalent to 100,000,000 tons of standard coals.Furnace flue gas discharge uses conventional cloth bag Dedusting, desulfurizing tower, nitrogen oxide emission are generally being much larger than 50mg/m3, conventional cloth bag dedusting, desulfurizing tower, SCR, SNCR are de- Nitre method is helpless, is unable to reach high efficiency denitration index.
Therefore, for stove minimum discharge transformation project particularity, complete set renovation technique scheme is designed.
Summary of the invention:
In order to make up the deficiency of prior art problem, the object of the present invention is to provide a kind of aluminium stone kiln break key denitration device and Method of denitration after aluminium stone kiln is mixed and burned by fresh air, low nitrogen wind, breaks key machine in aluminium stone kiln for ammonia cooperation nitrogen oxides for ammonia pump Fume high-temperature area denitrating flue gas, most afterwards through subsequent denitrating technique, simple process, scrap build is low in cost, and denitration efficiency is high.
Technical scheme is as follows:
Aluminium stone kiln breaks key denitration device, including aluminium stone kiln, and aluminium stone kiln outer wall upper and lower part is connected with flue, fresh wind tube respectively Road, fresh air pipeline end air blower, which is characterized in that smoke backflow pipeline, smoke backflow pipeline are connected on the flue On smoke backflow air-introduced machine is installed, wind-mixer is arranged in smoke backflow pipeline and fresh air pipeline intersection;
Flue end connects desulphurization denitration deduster one, catcher, desulphurization denitration deduster two, desulphurization denitration deduster One, two sewage draining exit of desulphurization denitration deduster and circulatory pool connection, two air outlet connection water mist separator of desulfurization and dedusting reaction kettle, water Mist separator wind pipe is connect with chimney, is equipped with air-introduced machine on water mist separator wind pipe;
Further include the tank used for storing ammonia being arranged between aluminium stone kiln furnace and desulphurization denitration deduster one, nitrogen oxides break key machine, Wherein nitrogen oxides breaks key machine upper end and is equipped with pipe-line mixer, and pipe-line mixer is high by the flue gas of mixing duct and aluminium stone kiln Warm area connection;The tank used for storing ammonia by for ammonia pump and pipe-line mixer connection for ammonia.
The aluminium stone kiln breaks key denitration device, which is characterized in that the desulphurization denitration deduster two and water mist separation Desulfurization filter net device is also linked between device, desulfurization filter net device link position is located at desulphurization denitration deduster two and water mist separation Device middle and upper part.
The aluminium stone kiln breaks key denitration device, which is characterized in that it is described for ammonia pump and pipe-line mixer connection for ammonia, It is vertical with medium emission direction in the broken key machine of nitrogen oxides that ammonium hydroxide enters pipe-line mixer direction.
The aluminium stone kiln breaks key denitration device, which is characterized in that the fume high-temperature zone position of the aluminium stone kiln is in ring Shape is evenly distributed with multiple nozzles, and nozzle sprays medical fluid and covers entire aluminium stone kiln sectional area.
The aluminium stone kiln breaks key denitration device, which is characterized in that and the nitrogen oxides breaks in key machine and medium is added, and When the pressure that the nitrogen oxides breaks key machine is 0.6MPa, temperature is 220 DEG C.
The aluminium stone kiln breaks key denitration device, which is characterized in that the medium is softened water and foaming agent, and foaming agent is Denitration common foaming, and the ratio of foaming agent and water is 1/10000~1.5/10000.
The aluminium stone kiln breaks key denitration device, which is characterized in that the tank used for storing ammonia is that the plastics of polyethylene material store up Tank.
The aluminium stone kiln breaks key denitration device, which is characterized in that the polyethylene is rotation molding polyethylene plastics.
The aluminium stone kiln breaks the method for denitration of key denitration device, which comprises the steps of:
1), debugging and detection system fault-free, each link of starting device are adjusted into fresh-air volume, smoke backflow amount, mix The mixing wind air output of wind device, it is 100% that mixed air volume, which controls valve opening, the aperture of fresh-air volume regulating valve is 70%~ 85%, the aperture of smoke backflow adjustable valve is 15%~50%;
2), each equipment of system operates normally, and cooperates the variable frequency adjustment of air blower, smoke backflow air-introduced machine, it is ensured that flue gas Regurgitant volume and fresh-air volume are according to 18%-32% ratio;
3), starting is carried out towards pipe-line mixer for ammonia for ammonia pump;
4), nitrogen oxides breaks in key machine and medium is added, and starts the temperature-pressure device that nitrogen oxides breaks key machine, works as pressure Reach 0.5MPa, temperature reaches 200 DEG C, and medium enters pipe-line mixer by pipeline, and medium enters pipeline lag and supplies for ammonia pump 1~3S of ammonia enters the fume high-temperature area of aluminium stone kiln after pipe-line mixer mixing;
5), medium is softened water and foaming agent in step 4), and foaming agent is denitration common foaming, ratio foaming agent: water =(0.8~2): (9000~10000);
6) after, aluminium stone kiln is mixed and burned by fresh air, low nitrogen wind, key machine is broken for ammonia cooperation nitrogen oxides using for ammonia pump In the fume high-temperature area denitrating flue gas of aluminium stone kiln, enters follow-up link finally along flue, eventually enter into smoke stack emission;
7), the sensor with nitrogen oxides detection NOx component concentration in chimney, sensor acquire data feedback to DCS The controller of control system is lower than 45mg/m through detection through detection discharged nitrous oxides3
The invention has the advantages that
1, after aluminium stone kiln of the present invention is mixed and burned by fresh air, low nitrogen wind, effective denitration is carried out in the burning primary stage, On the one hand the low nitrogen wind that smoke backflow pipeline provides can preheat fresh air, on the other hand reducing aluminium stone kiln oxygen content has energy conservation effect Fruit reduces the generation of nitrogen oxides simultaneously;
2, the present invention breaks key machine in the fume high-temperature area denitrating flue gas of aluminium stone kiln, in aluminium for ammonia cooperation nitrogen oxides for ammonia pump Denitration in stone kiln reduces nitrogen oxides in effluent of coming out of the stove again;
3, aluminium stone kiln of the present invention enters chimney, entire simple process, scrap build by flue after subsequent denitration link Low in cost, denitration efficiency is high;
4, in addition, the present invention also has excellent desulfurization, dedusting link, short time limit is transformed in whole equipment, and operating cost is low, Small investment is compared with tradition, short time limit 70%, operating cost decline 60~80%.
Detailed description of the invention:
Fig. 1 is the structural diagram of the present invention.
Fig. 2 is aluminium stone kiln fume high-temperature area of the present invention arrangement of nozzles figure.
Specific embodiment:
In order to make the objectives, technical solutions, and advantages of the present invention clearer, with reference to embodiments, to the present invention It is further elaborated.It should be appreciated that the specific embodiments described herein are merely illustrative of the present invention, it is not used to Limit the present invention.
Referring to attached drawing 1, aluminium stone kiln breaks key denitration device, including aluminium stone kiln 1, and 1 outer wall upper and lower part of aluminium stone kiln is connected with respectively Flue 2, fresh air pipeline 3,3 end air blower 4 of fresh air pipeline are connected with smoke backflow pipeline 5, smoke backflow pipeline 5 on flue 2 On smoke backflow air-introduced machine 6 is installed, wind-mixer 7 is arranged in smoke backflow pipeline 5 and 3 intersection of fresh air pipeline, and guarantee ensures back Stream flue gas is uniformly mixed with fresh air.
2 end of flue connects desulphurization denitration deduster 1, catcher 9, desulphurization denitration deduster 2 10, and desulphurization denitration removes 11 connection of dirt device 1,2 10 sewage draining exit of desulphurization denitration deduster and circulatory pool, 2 10 air outlet connection water of desulfurization and dedusting reaction kettle Mist separator 12,12 wind pipe of water mist separator are connect with chimney 13, are equipped with air inducing on 12 wind pipe of water mist separator Machine 14.
It further include the tank used for storing ammonia 15 being arranged between aluminium stone kiln furnace 1 and desulphurization denitration deduster 1, the broken key of nitrogen oxides Machine 16, wherein nitrogen oxides breaks 16 upper end of key machine and is equipped with pipe-line mixer 17, pipe-line mixer 17 by mixing duct 18 with The fume high-temperature area connection of aluminium stone kiln;Tank used for storing ammonia 14 by for ammonia pump 19 and 17 connection of pipe-line mixer for ammonia.
According to one embodiment, nitrogen oxides, which is broken in key machine 10, medium, and starts the heating that nitrogen oxides breaks key machine 10 Pressurizing device, when pressure reaches 0.6MPa, temperature reaches 220 DEG C;Medium is softened water and foaming agent, and foaming agent is common for denitration Ratio=1/10000~1.5/10000 of foaming agent, foaming agent and water.
Since ammonium hydroxide is alkaline reaction, there is strong corrosivity, strong to metal protections such as copper, aluminium, iron, ammonium hydroxide is to eyes There is the stimulation detrimental effect arranged by force with human bodies mucous membranes such as respiratory tracts.Therefore, in the embodiments of the present disclosure, ammonium hydroxide can use polyethylene The plastic storage tank of material is stored.Rotation molding polyethylene plastic storage tank, material material performance is excellent, plastic storage tank object produced Reason and chemical property are excellent, and using international advanced rotational moulding one-shot forming technique, bulky, sealability is good, and storage ammonium hydroxide is complete It can satisfy requirement entirely.
Desulfurization filter net device 20, desulfurization filter net device are also linked between desulphurization denitration deduster 2 10 and water mist separator 20 link positions are located at desulphurization denitration deduster 2 10 and 12 middle and upper part of water mist separator.
Referring to attached drawing 2, for ammonia pump 19 and 17 connection of pipe-line mixer for ammonia, ammonium hydroxide enters 17 direction of pipe-line mixer and nitrogen It is vertical that oxide breaks medium emission direction in key machine 16.
The fume high-temperature zone position of aluminium stone kiln 1 is evenly distributed with multiple nozzles 21 in a ring, and nozzle 21 sprays medical fluid covering Entire aluminium stone kiln sectional area.
Aluminium stone kiln breaks the method for denitration of key denitration device, includes the following steps:
1), debugging and detection system fault-free, each link of starting device are adjusted into fresh-air volume, smoke backflow amount, mix The mixing wind air output of wind device 7, it is 100% that mixed air volume, which controls valve opening, the aperture of fresh-air volume regulating valve is 70%~ 85%, the aperture of smoke backflow adjustable valve is 15%~50%, and each valve belongs to conventional design in each pipeline;
2), each equipment of system operates normally, and cooperates the variable frequency adjustment of air blower, smoke backflow air-introduced machine, it is ensured that flue gas Regurgitant volume and fresh-air volume are according to 18%-32% ratio;
3), starting is carried out towards pipe-line mixer for ammonia for ammonia pump;
4), nitrogen oxides breaks in key machine and medium is added, and starts the temperature-pressure device that nitrogen oxides breaks key machine, works as pressure Reach 0.5MPa, temperature reaches 200 DEG C, and medium enters pipe-line mixer by pipeline, and medium enters pipeline lag and supplies for ammonia pump 1~3S of ammonia enters the fume high-temperature area of aluminium stone kiln after pipe-line mixer mixing;
5), medium is softened water and foaming agent in step 4), and foaming agent is denitration common foaming, ratio foaming agent: water =(0.8~2): (9000~10000);
6) after, aluminium stone kiln is mixed and burned by fresh air, low nitrogen wind, key machine is broken for ammonia cooperation nitrogen oxides using for ammonia pump In the fume high-temperature area denitrating flue gas of aluminium stone kiln, enters follow-up link finally along flue, eventually enter into smoke stack emission;
7), the sensor with nitrogen oxides detection NOx component concentration in chimney 13, sensor belong to the prior art, mesh Preceding common detection means, sensor acquire data feedback to the controller of DCS control system, through detection discharged nitrous oxides through examining It surveys and is lower than 45mg/m3
Preferable specific embodiment of the invention is described in detail above.It should be appreciated that those skilled in the art It according to the present invention can conceive without creative work and make many modifications and variations.Therefore, all skills in the art Art personnel are available by logical analysis, reasoning, or a limited experiment on the basis of existing technology under this invention's idea Technical solution, all should be within the scope of protection determined by the claims.

Claims (9)

1. a kind of aluminium stone kiln breaks key denitration device, including aluminium stone kiln, aluminium stone kiln outer wall upper and lower part is connected with flue, fresh air respectively Pipeline, fresh air pipeline end air blower, which is characterized in that smoke backflow pipeline, smoke backflow pipe are connected on the flue Smoke backflow air-introduced machine is installed, wind-mixer is arranged in smoke backflow pipeline and fresh air pipeline intersection on road;
Flue end connects desulphurization denitration deduster one, catcher, desulphurization denitration deduster two, and desulphurization denitration deduster one takes off Two sewage draining exit of sulphur denitration dust collecting device and circulatory pool connection, two air outlet connection water mist separator of desulfurization and dedusting reaction kettle, water mist point It is connect from device wind pipe with chimney, air-introduced machine is installed on water mist separator wind pipe;
Further include the tank used for storing ammonia being arranged between aluminium stone kiln furnace and desulphurization denitration deduster one, nitrogen oxides break key machine, wherein Nitrogen oxides breaks key machine upper end and is equipped with pipe-line mixer, and pipe-line mixer passes through the fume high-temperature area of mixing duct and aluminium stone kiln Connection;The tank used for storing ammonia by for ammonia pump and pipe-line mixer connection for ammonia.
2. aluminium stone kiln according to claim 1 breaks key denitration device, which is characterized in that the desulphurization denitration deduster two Desulfurization filter net device is also linked between water mist separator, desulfurization filter net device link position is located at desulphurization denitration deduster two With water mist separator middle and upper part.
3. aluminium stone kiln according to claim 1 breaks key denitration device, which is characterized in that described to be mixed for ammonia pump with pipeline For device connection for ammonia, it is vertical with medium emission direction in the broken key machine of nitrogen oxides that ammonium hydroxide enters pipe-line mixer direction.
4. aluminium stone kiln according to claim 1 breaks key denitration device, which is characterized in that the fume high-temperature of the aluminium stone kiln Zone position is evenly distributed with multiple nozzles in a ring, and nozzle sprays medical fluid and covers entire aluminium stone kiln sectional area.
5. aluminium stone kiln according to claim 1 breaks key denitration device, which is characterized in that the nitrogen oxides, which is broken in key machine, to be added Enter medium, and when the pressure that the nitrogen oxides breaks key machine is 0.6MPa, temperature is 220 DEG C.
6. aluminium stone kiln according to claim 5 breaks key denitration device, which is characterized in that the medium is softened water and foaming Agent, foaming agent is denitration common foaming, and the ratio of foaming agent and water is 1/10000~1.5/10000.
7. aluminium stone kiln according to claim 1 breaks key denitration device, which is characterized in that the tank used for storing ammonia is polyethylene material The plastic storage tank of matter.
8. aluminium stone kiln according to claim 7 breaks key denitration device, which is characterized in that the polyethylene is rotation molding polyethylene Plastics.
9. the method for denitration that a kind of aluminium stone kiln as described in any one of claim 1~8 breaks key denitration device, which is characterized in that packet Include following steps:
1), debugging and detection system fault-free, each link of starting device are adjusted into fresh-air volume, smoke backflow amount, wind-mixer Mixing wind air output, it is 100% that mixed air volume, which controls valve opening, and the aperture of fresh-air volume regulating valve is 70%~85%, cigarette The aperture of gas reflux adjustable valve is 15%~50%;
2), each equipment of system operates normally, and cooperates the variable frequency adjustment of air blower, smoke backflow air-introduced machine, it is ensured that smoke backflow Amount and fresh-air volume are according to 18%-32% ratio;
3), starting is carried out towards pipe-line mixer for ammonia for ammonia pump;
4), nitrogen oxides breaks in key machine and medium is added, and starts the temperature-pressure device that nitrogen oxides breaks key machine, when pressure reaches 0.5MPa, temperature reach 200 DEG C, and medium enters pipe-line mixer by pipeline, medium enter pipeline lag for ammonia pump for ammonia 1~ 3S enters the fume high-temperature area of aluminium stone kiln after pipe-line mixer mixing;
5), in step 4) medium be softened water and foaming agent, foaming agent be denitration common foaming, ratio foaming agent: water= (0.8~2): (9000~10000);
6) after, aluminium stone kiln is mixed and burned by fresh air, low nitrogen wind, key machine is broken in aluminium for ammonia cooperation nitrogen oxides using for ammonia pump The fume high-temperature area denitrating flue gas of stone kiln, enters follow-up link finally along flue, eventually enters into smoke stack emission;
7), the sensor with nitrogen oxides detection NOx component concentration in chimney, sensor acquire data feedback and control to DCS The controller of system is lower than 45mg/m through detection through detection discharged nitrous oxides3
CN201910679972.0A 2019-07-26 2019-07-26 A kind of aluminium stone kiln breaks key denitration device and method of denitration Pending CN110252097A (en)

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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112696663A (en) * 2020-12-29 2021-04-23 四川省洪雅青衣江元明粉有限公司 Method for controlling low-nitrogen combustion of boiler

Citations (18)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1945116A (en) * 2006-09-05 2007-04-11 汕头市联美投资(集团)有限公司 Circulation fixing bed split phase combustion technology
CN101482262A (en) * 2009-02-04 2009-07-15 哈尔滨工业大学 Lignite boiler combustion method capable of reducing nitrogen oxide emission
CN201445911U (en) * 2009-08-07 2010-05-05 华南理工大学 Long spray gun type bubble atomizing nozzle
CN102671533A (en) * 2012-06-11 2012-09-19 杭州浙大天元科技有限公司 Low-air consumption effervescent atomizer applicable to SNCR (selective non-catalytic reduction) denitrification technology
CN202638200U (en) * 2012-04-10 2013-01-02 吴来田 High-efficiency desulfurization dust collector
CN104456615A (en) * 2014-12-05 2015-03-25 苏州华瑞能泰发电技术有限公司 Integrated debugging method of opposed firing pulverized coal boiler
CN205164477U (en) * 2015-10-30 2016-04-20 孙迎涛 Honeycomb panel fluid foam SOx/NOx control dust remover
CN205340518U (en) * 2016-01-13 2016-06-29 山东龙之源节能环保科技有限公司 Flue gas denitration device that low -nitrogen combustion and SNCR combined together
CN106322360A (en) * 2016-09-12 2017-01-11 西安交通大学 Selective non-catalytic reduction (SNCR) and flue gas recirculation coupling denitration system for chain furnace
CN106352325A (en) * 2016-10-28 2017-01-25 华中科技大学 Compound control system for nitrogen oxide discharge amount of grate-fired furnace
CN106352363A (en) * 2016-08-31 2017-01-25 吕宜德 Industrial boiler low-nitric-oxide combustion and environment protection system and technological method
CN206130962U (en) * 2016-09-12 2017-04-26 西安交通大学 A SNCR and gas recirculation coupling deNOx systems for chain furnace
CN107138005A (en) * 2016-12-19 2017-09-08 佛山市瑞淇环保设备有限公司 A kind of desulphurization denitration deduster
CN107441903A (en) * 2017-08-04 2017-12-08 谢辉 The equipment for denitrifying flue gas that a kind of low nitrogen burning is combined with non-selective catalytic reduction
CN108355483A (en) * 2018-02-02 2018-08-03 东华大学 A kind of wet denitration system and method absorbing flue gas based on catalytic ozonation
CN108905568A (en) * 2018-08-20 2018-11-30 山东省建设高压容器有限公司 A kind of circulating fluidized bed boiler flue gas desulfuration and denitrification system and its remodeling method
CN109631598A (en) * 2018-12-06 2019-04-16 海南中航特玻科技有限公司 A kind of all-oxygen combustion glass kiln denitration system and method based on flue gas recirculating technique
CN210332225U (en) * 2019-07-26 2020-04-17 启明星宇节能科技股份有限公司 Broken key denitration device of aluminum stone kiln

Patent Citations (18)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1945116A (en) * 2006-09-05 2007-04-11 汕头市联美投资(集团)有限公司 Circulation fixing bed split phase combustion technology
CN101482262A (en) * 2009-02-04 2009-07-15 哈尔滨工业大学 Lignite boiler combustion method capable of reducing nitrogen oxide emission
CN201445911U (en) * 2009-08-07 2010-05-05 华南理工大学 Long spray gun type bubble atomizing nozzle
CN202638200U (en) * 2012-04-10 2013-01-02 吴来田 High-efficiency desulfurization dust collector
CN102671533A (en) * 2012-06-11 2012-09-19 杭州浙大天元科技有限公司 Low-air consumption effervescent atomizer applicable to SNCR (selective non-catalytic reduction) denitrification technology
CN104456615A (en) * 2014-12-05 2015-03-25 苏州华瑞能泰发电技术有限公司 Integrated debugging method of opposed firing pulverized coal boiler
CN205164477U (en) * 2015-10-30 2016-04-20 孙迎涛 Honeycomb panel fluid foam SOx/NOx control dust remover
CN205340518U (en) * 2016-01-13 2016-06-29 山东龙之源节能环保科技有限公司 Flue gas denitration device that low -nitrogen combustion and SNCR combined together
CN106352363A (en) * 2016-08-31 2017-01-25 吕宜德 Industrial boiler low-nitric-oxide combustion and environment protection system and technological method
CN106322360A (en) * 2016-09-12 2017-01-11 西安交通大学 Selective non-catalytic reduction (SNCR) and flue gas recirculation coupling denitration system for chain furnace
CN206130962U (en) * 2016-09-12 2017-04-26 西安交通大学 A SNCR and gas recirculation coupling deNOx systems for chain furnace
CN106352325A (en) * 2016-10-28 2017-01-25 华中科技大学 Compound control system for nitrogen oxide discharge amount of grate-fired furnace
CN107138005A (en) * 2016-12-19 2017-09-08 佛山市瑞淇环保设备有限公司 A kind of desulphurization denitration deduster
CN107441903A (en) * 2017-08-04 2017-12-08 谢辉 The equipment for denitrifying flue gas that a kind of low nitrogen burning is combined with non-selective catalytic reduction
CN108355483A (en) * 2018-02-02 2018-08-03 东华大学 A kind of wet denitration system and method absorbing flue gas based on catalytic ozonation
CN108905568A (en) * 2018-08-20 2018-11-30 山东省建设高压容器有限公司 A kind of circulating fluidized bed boiler flue gas desulfuration and denitrification system and its remodeling method
CN109631598A (en) * 2018-12-06 2019-04-16 海南中航特玻科技有限公司 A kind of all-oxygen combustion glass kiln denitration system and method based on flue gas recirculating technique
CN210332225U (en) * 2019-07-26 2020-04-17 启明星宇节能科技股份有限公司 Broken key denitration device of aluminum stone kiln

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112696663A (en) * 2020-12-29 2021-04-23 四川省洪雅青衣江元明粉有限公司 Method for controlling low-nitrogen combustion of boiler
CN112696663B (en) * 2020-12-29 2023-06-02 四川省洪雅青衣江元明粉有限公司 Method for controlling low-nitrogen combustion of boiler

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