WO2000029094A1 - Method for operating a combustion plant - Google Patents
Method for operating a combustion plant Download PDFInfo
- Publication number
- WO2000029094A1 WO2000029094A1 PCT/EP1999/008040 EP9908040W WO0029094A1 WO 2000029094 A1 WO2000029094 A1 WO 2000029094A1 EP 9908040 W EP9908040 W EP 9908040W WO 0029094 A1 WO0029094 A1 WO 0029094A1
- Authority
- WO
- WIPO (PCT)
- Prior art keywords
- reducing agent
- nitrogen
- zone
- substoichiometric
- flame zone
- Prior art date
Links
Classifications
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J7/00—Arrangement of devices for supplying chemicals to fire
Definitions
- the invention relates to a method for operating a combustion device while reducing nitrogen oxides.
- the SCR process is mainly used to reduce nitrogen oxide emissions from industrial plants.
- SCR stands for Selective Catalytic Reduction.
- the burned-out flue gas is passed behind the burnout zone with the addition of a reducing agent through a catalytic reactor in which the nitrogen oxides are split up at temperatures of 300-400 ° C. to form molecular nitrogen.
- the investment required by the catalytic reactor is considerable.
- the SNCR method is also known.
- SNCR stands for Selective Non-Catalytic Reduction.
- the reducing agent is introduced into the overstoichiometric, high-temperature burnt flue gas directly after the burnout zone.
- Reducing agent is carried away by the flue gas as an ineffective base.
- the effectiveness of the SNCR process presupposes that the reducing agent is very intensive and uniform, for example over lances and the like, using a propellant with the burnt out
- Flue gas is mixed. Accordingly, the large-scale use of this process is prohibited. Its application is limited to smaller incinerators, e.g. B. on thermal power stations and waste incineration plants. A large-scale use would presuppose that a mixing over a cross-section of 100-500 m 2 is carried out in a uniform manner, which is obviously excluded.
- the reducing agent is fed into a reduction zone, which is located between the burner zone and the burnout zone. Burner zone and reduction zone are operated stoichiometrically. For this it may be necessary to work with fuel grading, ie one Enter the remaining portion of the fuel in the reduction zone. A carrier medium is required to introduce the reducing agent. Air is out of the question since the reduction zone must remain substoichiometric. In turn, nitrogen is too expensive. This leaves water vapor and vaporizable liquids, reducing the efficiency of the process in both cases. The same applies to the introduction of ammonia water, the water content of which is to be evaporated is approx. 75%. In the burnout zone following the reduction zone, the air ratio is increased to over 1 by adding additional combustion air.
- the proportion of the NO produced is comparatively low.
- the NO is broken down to form molecular nitrogen.
- the invention has for its object to provide a method of the type mentioned which is suitable for large-scale use in an effective and reliable manner with low investment and operating costs.
- Method according to the invention characterized in that a substoichiometric flame zone is generated and that the nitrogen oxide reducing agent is introduced into the substoichiometric flame zone.
- the substoichiometric flame zone has a comparatively small cross-section, so that there is none Difficulties in distributing the reducing agent evenly over this cross section. Load changes also play no role here.
- the method according to the invention is free from the temperature restrictions to which the SNCR method is subject. Rather, it has proven to be particularly advantageous to set a temperature of over 1,100 ° C. in the substoichiometric flame zone.
- Ammonia as well as ammonia water, urea and similar nitrogen compounds, as well as hydrocarbons, especially natural gas (CH 4 ), are usually suitable as reducing agents.
- reducing agents In the sub-stoichiometric flame zone, practically all of the available oxygen is used for the partial oxidation of the carbon. NO is only produced to a small extent.
- the presence of the reducing agent causes the concentration of the radicals NHi, CHi, HCN to increase. These radicals react with the resulting nitrogen monoxide, reduce it and thereby generate molecular nitrogen.
- the temperature of the process should preferably be carried out in such a way that during subsequent burn-out, i. H. with later air supply, the nitrogen molecules (as well as the N2 molecules of the combustion air) do not thermally decompose again and form nitrogen oxides.
- the temperature must not exceed 1400 ° C.
- Reducing agent slip cannot occur because the reducing agent is completely converted during the subsequent burnout with the addition of oxygen.
- the residues can therefore be used without restrictions.
- the substoichiometric flame zone be generated as a flame core from fuel and primary air and with a veil made of secondary air, preferably with another veil made of tertiary air.
- the decomposition and reduction of the NO takes place in the substoichiometric flame core.
- the veils of secondary air, and preferably of tertiary air subsequently burn out the fuel and decompose excess reducing agent.
- the flue gas therefore does not come into contact with the surrounding walls in a substoichiometric state. This effectively prevents the occurrence of high-temperature corrosion, which is to be seen as a further significant advantage of the invention.
- the nitrogen oxide reducing agent can be introduced into the substoichiometric flame zone through lateral or central lances. However, it is preferably introduced together with the fuel into the substoichiometric flame zone. It may also be advantageous to introduce the nitrogen oxide reducing agent together with the primary air into the substoichiometric flame zone. Possibly. the fuel will already be mixed with the primary air or part of the primary air. Under these circumstances, the mixture consists of fuel, primary air and reducing agent.
- the invention preferably develops its advantages wherever the fuel contains a high proportion of nitrogen. This is the case, for example, with hard coal, tar oil, heavy oil, residual oil, process gas and the like.
- Solid fuels are ground before combustion.
- the reducing agent can be in solid form (also ground) or else in liquid or gaseous form.
- the process is suitable for all performance levels and works without additional pressure loss.
- the main field of application of the invention is power plant technology.
- the burners are arranged in several levels one above the other in the side of the boiler wall, whereby the cross section of the boiler can be 100-500 m 2 . Upper air is blown in above the top burner level.
- Each burner represents its own sub-stoichiometric NO reduction system and delivers super-stoichiometric flue gases into the boiler. Obviously, it is not difficult to switch individual burner levels on or off.
Landscapes
- Engineering & Computer Science (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Regulation And Control Of Combustion (AREA)
- Cylinder Crankcases Of Internal Combustion Engines (AREA)
- Gas Separation By Absorption (AREA)
- Control Of Steam Boilers And Waste-Gas Boilers (AREA)
- Engine Equipment That Uses Special Cycles (AREA)
Abstract
Description
Claims
Priority Applications (7)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
AT99972122T ATE232133T1 (en) | 1998-11-18 | 1999-10-22 | METHOD FOR OPERATING A COMBUSTION DEVICE |
DK99972122T DK1131150T3 (en) | 1998-11-18 | 1999-10-22 | Process for operating a combustion device. |
CA002351663A CA2351663A1 (en) | 1998-11-18 | 1999-10-22 | Method for operating a combustion plant |
EP99972122A EP1131150B1 (en) | 1998-11-18 | 1999-10-22 | Method for operating a combustion plant |
PL99348340A PL194273B1 (en) | 1998-11-18 | 1999-10-22 | Method for operating a combustion plant |
DE59904247T DE59904247D1 (en) | 1998-11-18 | 1999-10-22 | METHOD FOR OPERATING A COMBUSTION DEVICE |
US11/879,212 US20080286704A1 (en) | 1998-11-18 | 2007-07-16 | Method of burning a nitrogen-containing fuel |
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
DE19853162A DE19853162C2 (en) | 1998-11-18 | 1998-11-18 | Process for burning a nitrogenous fuel |
DE19853162.1 | 1998-11-18 |
Publications (1)
Publication Number | Publication Date |
---|---|
WO2000029094A1 true WO2000029094A1 (en) | 2000-05-25 |
Family
ID=7888204
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
PCT/EP1999/008040 WO2000029094A1 (en) | 1998-11-18 | 1999-10-22 | Method for operating a combustion plant |
Country Status (8)
Country | Link |
---|---|
EP (1) | EP1131150B1 (en) |
AT (1) | ATE232133T1 (en) |
CA (1) | CA2351663A1 (en) |
DE (2) | DE19853162C2 (en) |
DK (1) | DK1131150T3 (en) |
ES (1) | ES2192417T3 (en) |
PL (1) | PL194273B1 (en) |
WO (1) | WO2000029094A1 (en) |
Families Citing this family (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
DE10142804A1 (en) * | 2000-10-17 | 2002-08-08 | Bosch Gmbh Robert | Emission control system and method for emission control |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
FR2484277A1 (en) * | 1980-06-11 | 1981-12-18 | Steinmueller Gmbh L & C | Nitrogen oxide redn. by ammonia - using burner with reductant fed to flame through a curtain of gas or liq. |
WO1991010864A1 (en) * | 1990-01-08 | 1991-07-25 | Transalta Resources Investment Corporation | Combustion process |
Family Cites Families (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US4023921A (en) * | 1975-11-24 | 1977-05-17 | Electric Power Research Institute | Oil burner for NOx emission control |
DE3331989A1 (en) * | 1983-09-05 | 1985-04-04 | L. & C. Steinmüller GmbH, 5270 Gummersbach | METHOD FOR REDUCING NO (DOWN ARROW) X (DOWN ARROW) EMISSIONS FROM THE COMBUSTION OF NITROGENOUS FUELS |
NL8902963A (en) * | 1989-12-01 | 1991-07-01 | Int Flame Research Foundation | PROCESS FOR BURNING FUEL OF LOW NOX CONTENT IN THE COMBUSTION GASES USING THROUGH STAGE FUEL SUPPLY AND BURNER. |
-
1998
- 1998-11-18 DE DE19853162A patent/DE19853162C2/en not_active Expired - Fee Related
-
1999
- 1999-10-22 CA CA002351663A patent/CA2351663A1/en not_active Abandoned
- 1999-10-22 ES ES99972122T patent/ES2192417T3/en not_active Expired - Lifetime
- 1999-10-22 WO PCT/EP1999/008040 patent/WO2000029094A1/en active IP Right Grant
- 1999-10-22 PL PL99348340A patent/PL194273B1/en not_active IP Right Cessation
- 1999-10-22 DK DK99972122T patent/DK1131150T3/en active
- 1999-10-22 AT AT99972122T patent/ATE232133T1/en not_active IP Right Cessation
- 1999-10-22 DE DE59904247T patent/DE59904247D1/en not_active Expired - Fee Related
- 1999-10-22 EP EP99972122A patent/EP1131150B1/en not_active Expired - Lifetime
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
FR2484277A1 (en) * | 1980-06-11 | 1981-12-18 | Steinmueller Gmbh L & C | Nitrogen oxide redn. by ammonia - using burner with reductant fed to flame through a curtain of gas or liq. |
WO1991010864A1 (en) * | 1990-01-08 | 1991-07-25 | Transalta Resources Investment Corporation | Combustion process |
Also Published As
Publication number | Publication date |
---|---|
PL194273B1 (en) | 2007-05-31 |
DE59904247D1 (en) | 2003-03-13 |
DE19853162A1 (en) | 2000-05-31 |
ES2192417T3 (en) | 2003-10-01 |
PL348340A1 (en) | 2002-05-20 |
EP1131150B1 (en) | 2003-02-05 |
EP1131150A1 (en) | 2001-09-12 |
ATE232133T1 (en) | 2003-02-15 |
DE19853162C2 (en) | 2003-04-30 |
DK1131150T3 (en) | 2003-06-02 |
CA2351663A1 (en) | 2000-05-25 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
DE3601378C2 (en) | ||
DE60308728T2 (en) | DEVICE AND METHOD FOR REGULATING NOX EMISSIONS FROM CARBON FUEL-BOILED BOILERS WITHOUT USING AN EXTERNAL REAGENT | |
EP0350706B1 (en) | Process for reducing nitrogen oxides in combustion gases | |
DE3331989A1 (en) | METHOD FOR REDUCING NO (DOWN ARROW) X (DOWN ARROW) EMISSIONS FROM THE COMBUSTION OF NITROGENOUS FUELS | |
DE2807076A1 (en) | USE OF CALCIUM OXIDE AS AN AGENT TO REDUCE SULFUR EMISSIONS IN BOILER FIRING | |
EP0977708B1 (en) | Method and device for converting hydrogen sulfide into elemental sulfur | |
EP0132584B1 (en) | Method and installation for reducing the emission of noxious matter in the flue gases of combustion plants | |
EP0302910B1 (en) | Coal combustion with a fluidized incineration bed | |
WO1984004053A1 (en) | Method and installation for the purification of combustion gas from domestic heatings, combustion engines or similar heatings | |
EP1131150B1 (en) | Method for operating a combustion plant | |
DE10123402A1 (en) | Removal of ammoniacal components from flue gas treated by selective non-catalytic reduction process, e.g. in waste incineration plants, involves contacting flue gas with ferro-oxide catalyst | |
DE3502866A1 (en) | Two-stage process and apparatus for purifying combustion gases | |
DE3823848A1 (en) | METHOD FOR REDUCING SO (ARROW DOWN) 2 (ARROW DOWN) AND / OR NO (ARROW DOWN) X (ARROW DOWN) EMISSIONS IN COMBUSTION PROCESSES | |
DE10051733B4 (en) | Process for the gradual combustion of fuels | |
EP0783916A1 (en) | Process for the denitration of flue gases | |
WO2001066233A1 (en) | Method and device for catalytically treating exhaust gas containing dust and oxygen | |
EP0671201B1 (en) | Process for separating sulphurtrioxid and for operating a catalytic denitration device | |
EP0363812A2 (en) | Method and installation for generating steam, especially in heat power plants | |
DE2852336C2 (en) | Process for the separation of NO? X? and SO? x? from combustion exhaust gases | |
DE4116950A1 (en) | METHOD AND DEVICE FOR REDUCING NO (ARROW DOWN) X (ARROW DOWN) EMISSION | |
DE3823223A1 (en) | Process for purifying flue gases containing sulphur oxides and nitrogen oxides | |
DE3522820A1 (en) | Process and device for reducing the pollutant emissions of combustion plants | |
DE2150687A1 (en) | Waste-gas sulphur dioxide removal - by conversion to sulphates on metal oxide mixtures | |
DE3729482A1 (en) | METHOD FOR REDUCING NO (ARROW DOWN) X (ARROW DOWN) EMISSIONS FROM SMOKE GASES FROM COMBUSTION SYSTEMS | |
DE19962743A1 (en) | Reduction of nitrogen oxide emissions from material stream involves producing material stream from sub-stoichiometric combustion of fuels, forming product |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
AK | Designated states |
Kind code of ref document: A1 Designated state(s): BR CA CN CZ IL IN JP KR PL TR UA US |
|
AL | Designated countries for regional patents |
Kind code of ref document: A1 Designated state(s): AT BE CH CY DE DK ES FI FR GB GR IE IT LU MC NL PT SE |
|
121 | Ep: the epo has been informed by wipo that ep was designated in this application | ||
DFPE | Request for preliminary examination filed prior to expiration of 19th month from priority date (pct application filed before 20040101) | ||
ENP | Entry into the national phase |
Ref document number: 2351663 Country of ref document: CA Ref country code: CA Ref document number: 2351663 Kind code of ref document: A Format of ref document f/p: F |
|
WWE | Wipo information: entry into national phase |
Ref document number: 1999972122 Country of ref document: EP |
|
WWE | Wipo information: entry into national phase |
Ref document number: 09856342 Country of ref document: US |
|
ENP | Entry into the national phase |
Ref country code: US Ref document number: 2001 856342 Date of ref document: 20010825 Kind code of ref document: A Format of ref document f/p: F |
|
WWP | Wipo information: published in national office |
Ref document number: 1999972122 Country of ref document: EP |
|
WWG | Wipo information: grant in national office |
Ref document number: 1999972122 Country of ref document: EP |