CN206986110U - A kind of Denitration in Boiler system using ammonia-contaminated gas as denitrfying agent - Google Patents

A kind of Denitration in Boiler system using ammonia-contaminated gas as denitrfying agent Download PDF

Info

Publication number
CN206986110U
CN206986110U CN201720040429.2U CN201720040429U CN206986110U CN 206986110 U CN206986110 U CN 206986110U CN 201720040429 U CN201720040429 U CN 201720040429U CN 206986110 U CN206986110 U CN 206986110U
Authority
CN
China
Prior art keywords
ammonia
boiler
import
outlet
stripper
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Active
Application number
CN201720040429.2U
Other languages
Chinese (zh)
Inventor
邵永飞
李先亮
段永升
徐辉
刘鑫
郝晓彬
石运锋
季作明
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.)
Inner Mongolia Jiutai New Material Technology Co.,Ltd.
Original Assignee
JIUTAI ENERGY INNER MONGOLIA Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by JIUTAI ENERGY INNER MONGOLIA Co Ltd filed Critical JIUTAI ENERGY INNER MONGOLIA Co Ltd
Priority to CN201720040429.2U priority Critical patent/CN206986110U/en
Application granted granted Critical
Publication of CN206986110U publication Critical patent/CN206986110U/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Landscapes

  • Chimneys And Flues (AREA)
  • Treating Waste Gases (AREA)

Abstract

It the utility model is related to a kind of Denitration in Boiler system using ammonia-contaminated gas as denitrfying agent, system includes gasification furnace, carbon washes tower, change furnace, heat-exchange system, ammonia stripping tower, stripper, exhaust mixer, boiler supply air system, boiler, air-introduced machine and chimney, the import that gasification furnace washes tower by pipeline with carbon is connected, the outlet that carbon washes tower is connected by the import of pipeline and change furnace, the outlet of change furnace and the import of heat-exchange system connect, the outlet of heat-exchange system is connected with the import of ammonia stripping tower, ammonia stripping tower is provided with gas vent and liquid outlet, the import of the liquid outlet and stripper of ammonia stripping tower connects, the outlet of stripper and the import of exhaust mixer connect, exhaust mixer connects by the bottom of boiler supply air system and boiler, the outlet of boiler is connected by air-introduced machine with chimney.The utility model significantly reduces the cost of Denitration in Boiler, reduces denitrification apparatus investment, while ammonia-contaminated gas can also be made to get utilization, and reduces environmental pollution.

Description

A kind of Denitration in Boiler system using ammonia-contaminated gas as denitrfying agent
Technical field
A kind of Denitration in Boiler system using ammonia-contaminated gas as denitrfying agent is the utility model is related to, belongs to denitration of boiler smoke skill Art field.
Background technology
In Chemical Manufacture, conventional utility boiler produces vapor.In boiler combustion process, coal produces titanium dioxide with oxygen reaction Carbon, release heat.In combustion, because also containing element sulphur and nitrogen in coal, except producing carbon dioxide, also simultaneously Sulfur dioxide and NOx can be produced, because NOx is one of Air Pollutant Discharge, so needing to take off the NOx in boiler smoke Remove.
Denitration of boiler smoke technology mainly selective catalytic reduction technique (SCR), SNCR technology (SNCR), hybrid SC R+SNCR technologies etc., wherein traditional SNCR technologies typically using the chemical reducing agent such as ammoniacal liquor, urea and NOx reacts, by NOx conversion into nitrogen and water.Usual Chemical Manufacture enterprise needs the chemical reducing agents such as outsourcing ammoniacal liquor, urea as de- Nitre agent simultaneously builds denitrification apparatus, and the NOx in boiler smoke is removed, and the annual denitration process expense of such boiler will be very It is high;And traditional denitration technology amount of ammonia slip is big, the problem of easily causing back-end ductwork to be blocked.
Gasification furnace can produce the thick process gas containing ammonia in Chemical Manufacture.Carbon monoxide, hydrogen, carbon dioxide in thick process gas As effective process gas, transformed stove is reacted part carbon monoxide, changes into carbon dioxide and hydrogen, through heat-exchange system Process gas after cooling strips through the washing of ammonia stripping tower and stripper decompression, heating, obtains the ammonia-contaminated gas containing gaseous ammonia.Should Contain a certain amount of ammonia in ammonia-contaminated gas, while also directly discharged containing carbon dioxide, carbon monoxide, hydrogen, ammonia-contaminated gas Serious environmental pollution can be caused into air.
The content of the invention
The utility model provides a kind of Denitration in Boiler system using ammonia-contaminated gas as denitrfying agent, significantly reduces boiler and takes off The cost of nitre, reduce denitrification apparatus investment, while ammonia-contaminated gas can also be made to get utilization, reduce environmental pollution. The technical solution of the utility model is as follows:
A kind of Denitration in Boiler system using ammonia-contaminated gas as denitrfying agent, system includes gasification furnace, carbon is washed tower, change furnace, changed Hot systems, ammonia stripping tower, stripper, exhaust mixer, boiler supply air system, boiler, air-introduced machine and chimney, gasification furnace pass through pipe The import that tower is washed in road with carbon is connected, and the outlet that carbon washes tower is connected by the import of pipeline and change furnace, and the outlet of change furnace is with changing The import connection of hot systems, the outlet of heat-exchange system are connected with the import of ammonia stripping tower, and ammonia stripping tower is provided with gas vent and liquid Body is exported, and the liquid outlet of ammonia stripping tower is connected by the import of pipeline and stripper, and the outlet of stripper by pipeline and is given up The import connection of gas blender, exhaust mixer connect by the bottom of boiler supply air system and boiler, and the outlet of boiler is passed through Air-introduced machine is connected with chimney.
On the basis of above-mentioned technical proposal, the import of the ammonia stripping tower is located at the bottom of ammonia stripping tower;Unskilled workman containing ammonia Skill gas is inversely contacted in scrubbing tower with shower water, and ammonia is dissolved in water, and forms water containing ammonia stripping.
On the basis of above-mentioned technical proposal, the import of the stripper is located at the upper end of stripper;In the stripper Also include nozzle, the import of stripper is connected with spray head.Water containing ammonia stripping sprays into stripper upper end, and middle part adds steam, steams Vapour exchanges heat with the counter current contacting of water containing ammonia stripping, and the ammonia stripping being dissolved in washings turns into the ammonia-contaminated gas containing gaseous ammonia.
A kind of Denitration in Boiler technique using ammonia-contaminated gas as denitrfying agent, comprise the following steps that:
(1) in gasification furnace, coal and water react in the case of oxygen-enriched, produce based on process gas while the ammonia of thing containing side reaction The thick process gas of gas, thick process gas wash tower into carbon, are washed in carbon and solid particulate matter is removed in tower;
(2) the thick process gas containing ammonia enters change furnace after carbon washes tower, in change furnace inside points carbon monoxide and vapor Carbon dioxide and hydrogen are changed into the presence of catalyst, side reaction thing ammonia is not involved in reacting;
(3) the thick process gas containing ammonia enters heat-exchange system after change furnace, is cooled in heat-exchange system, thick process gas Temperature drops to 40 DEG C from 430 DEG C, pressure 6.0MPa;
(4) the thick process gas containing ammonia enters ammonia stripping tower after heat-exchange system, the thick process gas containing ammonia in scrubbing tower with spray Water drenching is inversely contacted, and under 6.0MPa pressure, ammonia is dissolved in water, and forms water containing ammonia stripping, and water containing ammonia stripping enters vapour Stripper;
(5) in stripper, pressure 0.2MPa, water containing ammonia stripping sprays into stripper upper end, and middle part adds steam, steam Exchanged heat with the counter current contacting of water containing ammonia stripping, the ammonia stripping being dissolved in washings turns into the ammonia-contaminated gas containing gaseous ammonia;
(6) ammonia-contaminated gas enters exhaust mixer after stripper, uniform with boiler secondary air in exhaust mixer The volume ratio of mixing, ammonia-contaminated gas and Secondary Air is 7:5000-15000;
Preferably, the volume ratio of ammonia-contaminated gas and Secondary Air is 7:10000.
(7) with boiler secondary air uniformly mixed ammonia-contaminated gas by exhaust mixer come out after by boiler blow be System, enters boiler with gaseous state from the bottom of boiler, under the conditions of temperature is 850-1150 DEG C, ammonia-contaminated gas and the flue gas in boiler Fully contact, carry out denitration reaction, the ammonia-contaminated gas reduction reaction such as formula (1) and formula (2) with NOx in flue gas in the boiler:
4NO+4NH3+O2→4N2+6H2O (1)
2NO2+4NH3+O2→3N2+6H2O (2)
In addition, the reaction such as formula (3) and formula (4) such as also occurs in boiler for ammonia-contaminated gas:
2CO+O2→2CO2 (3)
2H2+O2→2H2O (4);
(8) waste gas after Denitration in Boiler is discharged by air-introduced machine by chimney.
Preferably, in the step (5), ammonia-contaminated gas includes ammonia, carbon monoxide, carbon dioxide, hydrogen, methane, nitrogen Gas, hydrogen sulfide and carbonyl sulfide, temperature be 75 DEG C, pressure be 0.25MPa under the conditions of, ammonia, carbon monoxide, carbon dioxide, The volume fraction that hydrogen, methane, nitrogen, hydrogen sulfide and carbonyl sulfide account for ammonia-contaminated gas is respectively 20.35%, 13.82%, 51.36%th, 13.58%, 0.04%, 0.13%, 0.01%, 0.67% and 0.01%.
In gasification furnace, coal and water mainly produce carbon monoxide, carbon dioxide, hydrogen when being reacted in the case of oxygen-enriched, Due to containing nitrogen in coal, while side reaction occurs and produces ammonia.Wherein carbon monoxide, hydrogen, carbon dioxide are as effective The transformed stove of process gas is reacted part carbon monoxide, changes into carbon dioxide and hydrogen, through heat-exchange system by process gas Temperature is reduced to 40 DEG C from 430 DEG C, and the process gas after temperature reduces washes away ammonia caused by side reaction through Ammonic washing tower, clean The next workshop section of technique pneumatic transmission, the washings rich in ammonia depressurize through stripper, heat stripping, the ammonolysis being dissolved in washings Inhaling turns into the ammonia-contaminated gas containing gaseous ammonia, and in caused ammonia-contaminated gas, the content of ammonia reaches more than 20%.
Traditional denitration technology is simply reaction zone in furnace outlet to superheater entrance, has little time the ammonia of reaction then Escape to rear workshop section.(3m is left to 850-1100 DEG C of furnace outlet (37m or so), furnace outlet to superheater entrance for lower furnace portion It is right) it is 850-950 DEG C, this two sections comfort zones for Denitration in Boiler, and this technology is because be with gaseous state side in boiler bottom Formula adds ammonia-contaminated gas, is reaction zone from lower furnace portion to the process of superheater entrance 40m or so flue gas circulation, with tradition SNCR technologies carry out addition with 5% or so ammoniacal liquor in boiler furnace outlet and compared, and add the residence time of reactant, increase The time that reactant is reacted, reaction efficiency is improved, because being in all the time in reaction temperature in the whole course of reaction, and Contain fuel gas in ammonia-contaminated gas, ensure that the reaction temperature in course of reaction, because whole reaction temperature is protected, reacts The thing residence time is increased, and is fully reacted between reactant, so as to reduce the reactant for having neither part nor lot in reaction, is reduced Amount of ammonia slip.
The ammonia that traditional Denitration in Boiler is escaped is reacted after temperature reduction with the sulfur dioxide in flue gas, is generated Ammonium sulfate, the larger crystal of ammonium sulfite viscosity, crystal are combined with the Boiler Ash in flue gas, be bonded in air preheater and It is dirty stifled so as to produce on desulfurization and dedusting cloth bag.
The utility model has advantages below compared with prior art:
By the utility model, reduce pollution from exhaust emission, significantly reduce denitrating flue gas cost, it is new by this practicality The Denitration in Boiler system of type so that discharged nitrous oxides concentration is less than 100mg/m3.The utility model causes the stop of reactant Time lengthening, reaction temperature is ensure that, reduce amount of ammonia slip, achieve good economic benefit and environmental benefit, simultaneously Reduce back-end ductwork and dirty stifled possibility occurs because crystal is mixed with ash.
Brief description of the drawings
Fig. 1 is the utility model process chart;
Fig. 2 is import and spray head attachment structure schematic diagram in stripper.
Symbol description
1. gasification furnace, 2. carbon wash tower, 3. change furnaces, 4. heat-exchange systems, 5. ammonia stripping towers, 6. strippers, the mixing of 7. waste gas Device, 8. boiler supply air systems, 9. boilers, 10. air-introduced machines, 11. chimneys, 12. spray heads.
Embodiment
The utility model is further described with reference to specific embodiment, and the advantages of the utility model and feature will be with Description and it is apparent.But embodiment is only exemplary, does not form any restrictions to the scope of the utility model.Ability Field technique personnel should be understood that can be to the utility model technical side under without departing from spirit and scope of the present utility model The details and form of case are modified or replaced, but these modifications and replacement are each fallen within the scope of protection of the utility model.
A kind of Denitration in Boiler system using ammonia-contaminated gas as denitrfying agent of embodiment 1, as shown in figure 1, system includes gasification furnace 1st, carbon washes tower 2, change furnace 3, heat-exchange system 4, ammonia stripping tower 5, stripper 6, exhaust mixer 7, boiler supply air system 8, boiler 9th, air-introduced machine 10 and chimney 11, the import that gasification furnace 1 washes tower 2 by pipeline with carbon are connected, carbon wash the outlet of tower 2 by pipeline with The import connection of change furnace 3, the outlet of change furnace 3 are connected with the import of heat-exchange system 4, the outlet of heat-exchange system 4 and ammonia stripping The import connection of tower 5, ammonia stripping tower 5 are provided with gas vent and liquid outlet, and the liquid outlet of ammonia stripping tower 5 passes through pipeline and vapour The import connection of stripper 6, the outlet of stripper 6 are connected by pipeline with the import of exhaust mixer 7, and exhaust mixer 7 is passed through Boiler supply air system 8 is connected with the bottom of boiler 9, and the outlet of boiler 9 is connected by air-introduced machine 10 with chimney 11.
Embodiment 2
On the basis of embodiment 1, as depicted in figs. 1 and 2, the import of the ammonia stripping tower 5 is located under ammonia stripping tower 5 Portion;The import of the stripper 6 is located at the upper end of stripper 6;Also include spray head 12 in the stripper 6, stripper 6 Import is connected with spray head 12.

Claims (5)

  1. A kind of 1. Denitration in Boiler system using ammonia-contaminated gas as denitrfying agent, it is characterised in that system includes gasification furnace, carbon washes tower, Change furnace, heat-exchange system, ammonia stripping tower, stripper, exhaust mixer, boiler supply air system, boiler, air-introduced machine and chimney, gas The import that change stove washes tower by pipeline with carbon is connected, and the outlet that carbon washes tower is connected by the import of pipeline and change furnace, change furnace Outlet and the import of heat-exchange system connect, the outlet of heat-exchange system is connected with the import of ammonia stripping tower, and ammonia stripping tower is provided with gas Body exports and liquid outlet, and the import of the liquid outlet and stripper of ammonia stripping tower connects, and the outlet of stripper mixes with waste gas The import connection of device, exhaust mixer connect by the bottom of boiler supply air system and boiler, and air-introduced machine is passed through in the outlet of boiler It is connected with chimney.
  2. A kind of 2. Denitration in Boiler system using ammonia-contaminated gas as denitrfying agent according to claim 1, it is characterised in that the ammonia The import of scrubbing tower is located at the bottom of ammonia stripping tower.
  3. A kind of 3. Denitration in Boiler system using ammonia-contaminated gas as denitrfying agent according to claim 1, it is characterised in that the vapour The import of stripper is located at the upper end of stripper.
  4. A kind of 4. Denitration in Boiler system using ammonia-contaminated gas as denitrfying agent according to claim 3, it is characterised in that the vapour Also include nozzle in stripper, the import of stripper is connected with spray head.
  5. 5. a kind of Denitration in Boiler system using ammonia-contaminated gas as denitrfying agent according to claim 1, it is characterised in that described to change Hot systems are vapour-water heat-exchange system.
CN201720040429.2U 2017-01-13 2017-01-13 A kind of Denitration in Boiler system using ammonia-contaminated gas as denitrfying agent Active CN206986110U (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201720040429.2U CN206986110U (en) 2017-01-13 2017-01-13 A kind of Denitration in Boiler system using ammonia-contaminated gas as denitrfying agent

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201720040429.2U CN206986110U (en) 2017-01-13 2017-01-13 A kind of Denitration in Boiler system using ammonia-contaminated gas as denitrfying agent

Publications (1)

Publication Number Publication Date
CN206986110U true CN206986110U (en) 2018-02-09

Family

ID=61423200

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201720040429.2U Active CN206986110U (en) 2017-01-13 2017-01-13 A kind of Denitration in Boiler system using ammonia-contaminated gas as denitrfying agent

Country Status (1)

Country Link
CN (1) CN206986110U (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106582226A (en) * 2017-01-13 2017-04-26 久泰能源内蒙古有限公司 Boiler denitration process taking ammonia-containing waste gas as denitration agent
CN108970353A (en) * 2018-07-16 2018-12-11 西安华大骄阳绿色科技有限公司 A kind of synthesis desulfurating method of denitration being catalyzed flue gas and the sour gas containing ammonia
CN110261546A (en) * 2019-06-28 2019-09-20 中冶南方都市环保工程技术股份有限公司 The experimental rig and method of active coke desulphurizing and denitration performance can be tested simultaneously
CN113617199A (en) * 2021-09-03 2021-11-09 山西化美环保科技有限公司 Process method for treating tail gas containing hydrogen sulfide by using double-alkali method

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN106582226A (en) * 2017-01-13 2017-04-26 久泰能源内蒙古有限公司 Boiler denitration process taking ammonia-containing waste gas as denitration agent
CN108970353A (en) * 2018-07-16 2018-12-11 西安华大骄阳绿色科技有限公司 A kind of synthesis desulfurating method of denitration being catalyzed flue gas and the sour gas containing ammonia
CN108970353B (en) * 2018-07-16 2021-04-30 西安华大骄阳绿色科技有限公司 Comprehensive desulfurization and denitrification method for catalytic flue gas and ammonia-containing acid gas
CN110261546A (en) * 2019-06-28 2019-09-20 中冶南方都市环保工程技术股份有限公司 The experimental rig and method of active coke desulphurizing and denitration performance can be tested simultaneously
CN113617199A (en) * 2021-09-03 2021-11-09 山西化美环保科技有限公司 Process method for treating tail gas containing hydrogen sulfide by using double-alkali method

Similar Documents

Publication Publication Date Title
CN206986110U (en) A kind of Denitration in Boiler system using ammonia-contaminated gas as denitrfying agent
CN103212284A (en) Method and device for combined removal of nitric oxide and sulfide in flue gas
CN104941410B (en) Flue gas desulfurization and denitrification integrated method and device based on two-step oxidation process of active molecules O3 at low temperature
CN100427391C (en) Tail gas treatment and reutilization for calcium carbide stove
CN105457486A (en) Coke oven flue gas integrated treatment method
CN106237851A (en) A kind of utilize ozone to carry out SCR denitration to carry the System and method for of effect
CN103263828A (en) Fume gas denitration system of coal-fired boiler based on SNCR (Selective Non-catalytic Reduction) and SCR (Selective Catalytic Reduction) combination method
CN105194991B (en) Glass kiln flue gas desulfurization and denitrification system and technique
CN110841450A (en) Flue gas treatment system and method for step ozone oxidation
CN113864789A (en) Incineration system for treating sulfur-containing, nitrogen-containing and salt-containing waste liquid
CN103100294A (en) Method for removing oxynitride from flue gas through ozone oxidation method
CN104329946B (en) A kind of coke oven flue exhaust gas denitration and the integral system of waste heat recovery
CN102309920B (en) Method for removing NOx and SOx from fluid catalytic cracking (FCC) flue gas
CN205627628U (en) Low temperature coke oven smoke SOx/NOx control integrated device
CN107308812A (en) The system and method for low temperature organic catalysis oxidizing and denitrating ozone
CN109028106B (en) Method for reducing NOx in catalytic cracking incomplete regeneration flue gas
CN106582226B (en) It is a kind of using ammonia-contaminated gas as the Denitration in Boiler technique of denitrfying agent
CN206253015U (en) Low temperature is from heat exchange type SCR denitration reaction tower
CN108654363A (en) Couple waste heat of coke-oven flue gas and amounts of sulphur contaminants acid-making process
CN111804138A (en) Biomass boiler flue gas denitration system and application process thereof
CN107096378A (en) The flue gas desulphurization system and sulfur method of a kind of floatation glass production line
CN209476008U (en) A kind of low-temperature denitration of flue gas catalytic reaction system
CN206526661U (en) A kind of waste heat boiler and Benitration reactor combined unit
CN206222345U (en) A kind of waste heat boiler with denitration function
CN202962241U (en) Device for synergistically removing flue gas mercury

Legal Events

Date Code Title Description
GR01 Patent grant
GR01 Patent grant
CP03 "change of name, title or address"

Address after: 010321 Dalu New District, Zhungeer banner, Ordos City, Inner Mongolia Autonomous Region

Patentee after: Inner Mongolia Jiutai New Material Technology Co.,Ltd.

Address before: 010321 Dalu New District, Ordos City, Inner Mongolia Autonomous Region

Patentee before: JIUTAI ENERGY INNER MONGOLIA Co.,Ltd.

CP03 "change of name, title or address"