EP1579109A1 - Dispositif et procede de post-traitement de gaz d'echappement - Google Patents
Dispositif et procede de post-traitement de gaz d'echappementInfo
- Publication number
- EP1579109A1 EP1579109A1 EP03782415A EP03782415A EP1579109A1 EP 1579109 A1 EP1579109 A1 EP 1579109A1 EP 03782415 A EP03782415 A EP 03782415A EP 03782415 A EP03782415 A EP 03782415A EP 1579109 A1 EP1579109 A1 EP 1579109A1
- Authority
- EP
- European Patent Office
- Prior art keywords
- catalytic converter
- exhaust gas
- catalyst
- nitrogen oxide
- oxide storage
- 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.)
- Withdrawn
Links
Classifications
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
- F01N3/00—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
- F01N3/02—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for cooling, or for removing solid constituents of, exhaust
- F01N3/021—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for cooling, or for removing solid constituents of, exhaust by means of filters
- F01N3/033—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for cooling, or for removing solid constituents of, exhaust by means of filters in combination with other devices
- F01N3/035—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for cooling, or for removing solid constituents of, exhaust by means of filters in combination with other devices with catalytic reactors, e.g. catalysed diesel particulate filters
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/92—Chemical or biological purification of waste gases of engine exhaust gases
- B01D53/94—Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
- B01D53/9404—Removing only nitrogen compounds
- B01D53/9409—Nitrogen oxides
- B01D53/9431—Processes characterised by a specific device
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/92—Chemical or biological purification of waste gases of engine exhaust gases
- B01D53/94—Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
- B01D53/9459—Removing one or more of nitrogen oxides, carbon monoxide, or hydrocarbons by multiple successive catalytic functions; systems with more than one different function, e.g. zone coated catalysts
- B01D53/9477—Removing one or more of nitrogen oxides, carbon monoxide, or hydrocarbons by multiple successive catalytic functions; systems with more than one different function, e.g. zone coated catalysts with catalysts positioned on separate bricks, e.g. exhaust systems
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/92—Chemical or biological purification of waste gases of engine exhaust gases
- B01D53/94—Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
- B01D53/9495—Controlling the catalytic process
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/96—Regeneration, reactivation or recycling of reactants
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
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- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
- F01N13/00—Exhaust or silencing apparatus characterised by constructional features ; Exhaust or silencing apparatus, or parts thereof, having pertinent characteristics not provided for in, or of interest apart from, groups F01N1/00 - F01N5/00, F01N9/00, F01N11/00
- F01N13/009—Exhaust or silencing apparatus characterised by constructional features ; Exhaust or silencing apparatus, or parts thereof, having pertinent characteristics not provided for in, or of interest apart from, groups F01N1/00 - F01N5/00, F01N9/00, F01N11/00 having two or more separate purifying devices arranged in series
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
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- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
- F01N13/00—Exhaust or silencing apparatus characterised by constructional features ; Exhaust or silencing apparatus, or parts thereof, having pertinent characteristics not provided for in, or of interest apart from, groups F01N1/00 - F01N5/00, F01N9/00, F01N11/00
- F01N13/009—Exhaust or silencing apparatus characterised by constructional features ; Exhaust or silencing apparatus, or parts thereof, having pertinent characteristics not provided for in, or of interest apart from, groups F01N1/00 - F01N5/00, F01N9/00, F01N11/00 having two or more separate purifying devices arranged in series
- F01N13/0093—Exhaust or silencing apparatus characterised by constructional features ; Exhaust or silencing apparatus, or parts thereof, having pertinent characteristics not provided for in, or of interest apart from, groups F01N1/00 - F01N5/00, F01N9/00, F01N11/00 having two or more separate purifying devices arranged in series the purifying devices are of the same type
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
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- F01N13/00—Exhaust or silencing apparatus characterised by constructional features ; Exhaust or silencing apparatus, or parts thereof, having pertinent characteristics not provided for in, or of interest apart from, groups F01N1/00 - F01N5/00, F01N9/00, F01N11/00
- F01N13/011—Exhaust or silencing apparatus characterised by constructional features ; Exhaust or silencing apparatus, or parts thereof, having pertinent characteristics not provided for in, or of interest apart from, groups F01N1/00 - F01N5/00, F01N9/00, F01N11/00 having two or more purifying devices arranged in parallel
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
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- F01N3/00—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
- F01N3/02—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for cooling, or for removing solid constituents of, exhaust
- F01N3/021—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for cooling, or for removing solid constituents of, exhaust by means of filters
- F01N3/023—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for cooling, or for removing solid constituents of, exhaust by means of filters using means for regenerating the filters, e.g. by burning trapped particles
- F01N3/0231—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for cooling, or for removing solid constituents of, exhaust by means of filters using means for regenerating the filters, e.g. by burning trapped particles using special exhaust apparatus upstream of the filter for producing nitrogen dioxide, e.g. for continuous filter regeneration systems [CRT]
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- F01N3/00—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
- F01N3/08—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous
- F01N3/0807—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by using absorbents or adsorbents
- F01N3/0814—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by using absorbents or adsorbents combined with catalytic converters, e.g. NOx absorption/storage reduction catalysts
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
- F01N3/00—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
- F01N3/08—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous
- F01N3/0807—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by using absorbents or adsorbents
- F01N3/0821—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by using absorbents or adsorbents combined with particulate filters
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
- F01N3/00—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
- F01N3/08—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous
- F01N3/0807—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by using absorbents or adsorbents
- F01N3/0828—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by using absorbents or adsorbents characterised by the absorbed or adsorbed substances
- F01N3/0842—Nitrogen oxides
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- F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
- F01N3/00—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
- F01N3/08—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous
- F01N3/0807—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by using absorbents or adsorbents
- F01N3/0871—Regulation of absorbents or adsorbents, e.g. purging
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
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- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
- F01N3/00—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
- F01N3/08—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous
- F01N3/10—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust
- F01N3/103—Oxidation catalysts for HC and CO only
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- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
- F01N3/00—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
- F01N3/08—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous
- F01N3/10—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust
- F01N3/18—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust characterised by methods of operation; Control
- F01N3/20—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust characterised by methods of operation; Control specially adapted for catalytic conversion ; Methods of operation or control of catalytic converters
- F01N3/2006—Periodically heating or cooling catalytic reactors, e.g. at cold starting or overheating
- F01N3/2013—Periodically heating or cooling catalytic reactors, e.g. at cold starting or overheating using electric or magnetic heating means
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- F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
- F01N3/00—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
- F01N3/08—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous
- F01N3/10—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust
- F01N3/18—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust characterised by methods of operation; Control
- F01N3/20—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust characterised by methods of operation; Control specially adapted for catalytic conversion ; Methods of operation or control of catalytic converters
- F01N3/2066—Selective catalytic reduction [SCR]
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- F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
- F01N3/00—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
- F01N3/08—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous
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- F01N3/18—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust characterised by methods of operation; Control
- F01N3/20—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust characterised by methods of operation; Control specially adapted for catalytic conversion ; Methods of operation or control of catalytic converters
- F01N3/2066—Selective catalytic reduction [SCR]
- F01N3/208—Control of selective catalytic reduction [SCR], e.g. dosing of reducing agent
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- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
- F01N3/00—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
- F01N3/08—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous
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- F01N3/24—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for rendering innocuous by thermal or catalytic conversion of noxious components of exhaust characterised by constructional aspects of converting apparatus
- F01N3/28—Construction of catalytic reactors
- F01N3/2882—Catalytic reactors combined or associated with other devices, e.g. exhaust silencers or other exhaust purification devices
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- F01N3/00—Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
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- B01D2255/00—Catalysts
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- B01D2255/911—NH3-storage component incorporated in the catalyst
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- B—PERFORMING OPERATIONS; TRANSPORTING
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- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/92—Chemical or biological purification of waste gases of engine exhaust gases
- B01D53/94—Chemical or biological purification of waste gases of engine exhaust gases by catalytic processes
- B01D53/9404—Removing only nitrogen compounds
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- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/92—Chemical or biological purification of waste gases of engine exhaust gases
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- B01D53/9404—Removing only nitrogen compounds
- B01D53/9409—Nitrogen oxides
- B01D53/9413—Processes characterised by a specific catalyst
- B01D53/9422—Processes characterised by a specific catalyst for removing nitrogen oxides by NOx storage or reduction by cyclic switching between lean and rich exhaust gases (LNT, NSC, NSR)
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- F01N2510/068—Surface coverings for exhaust purification, e.g. catalytic reaction characterised by the distribution of the catalytic coatings
- F01N2510/0684—Surface coverings for exhaust purification, e.g. catalytic reaction characterised by the distribution of the catalytic coatings having more than one coating layer, e.g. multi-layered coatings
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- F01N2560/025—Exhaust systems with means for detecting or measuring exhaust gas components or characteristics the means being an exhaust gas sensor for measuring or detecting O2, e.g. lambda sensors
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
- F01N2570/00—Exhaust treating apparatus eliminating, absorbing or adsorbing specific elements or compounds
- F01N2570/18—Ammonia
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
- F01N2610/00—Adding substances to exhaust gases
- F01N2610/02—Adding substances to exhaust gases the substance being ammonia or urea
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
- F01N2610/00—Adding substances to exhaust gases
- F01N2610/03—Adding substances to exhaust gases the substance being hydrocarbons, e.g. engine fuel
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F01—MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
- F01N—GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL COMBUSTION ENGINES
- F01N2610/00—Adding substances to exhaust gases
- F01N2610/14—Arrangements for the supply of substances, e.g. conduits
- F01N2610/1453—Sprayers or atomisers; Arrangement thereof in the exhaust apparatus
- F01N2610/146—Control thereof, e.g. control of injectors or injection valves
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A50/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
- Y02A50/20—Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02T—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO TRANSPORTATION
- Y02T10/00—Road transport of goods or passengers
- Y02T10/10—Internal combustion engine [ICE] based vehicles
- Y02T10/12—Improving ICE efficiencies
Definitions
- the invention relates to an exhaust gas aftertreatment device according to the preamble of claim 1 and to an exhaust gas aftertreatment method that can be carried out with such a device.
- Such devices and methods are used in particular for exhaust gas aftertreatment or exhaust gas purification in predominantly lean-burn internal combustion engines in motor vehicles.
- nitrogen oxide storage catalysts also known as NO x storage catalysts or NO x adsorber catalysts or abbreviated as NSK
- NSK nitrogen oxide storage catalysts
- Lean operating phases of the internal combustion engine correspond to adsorption phases of the nitrogen oxide storage catalytic converter, in which it oxidizes nitrogen monoxide (MO) in nitrogen dioxide (N0 2 ) and stores them temporarily as nitrates.
- MO nitrogen monoxide
- N0 2 nitrogen dioxide
- the nitrogen oxide storage catalyst is freed from the stored nitrates by converting them to nitrogen dioxide and then nitrogen monoxide. The latter is then reduced to nitrogen using suitable reducing agents.
- a known technique of providing the necessary reducing agents is to switch the predominantly lean combustion device, the exhaust gas of which is aftertreated, briefly to rich operation, which means that in the exhaust gas Reducing agents hydrogen (H 2 ), carbon monoxide (CO) and unburned hydrocarbons (HC) are present.
- H 2 hydrogen
- CO carbon monoxide
- HC unburned hydrocarbons
- the nitrogen oxide reduction can also take place in a downstream, so-called DENOX catalyst, and post-engine metering of hydrocarbons can also be provided to provide the reducing agents, see, for example, EP 0 540 280 A1 and EP 0 573 672 AI.
- SCR process Another known exhaust gas aftertreatment process is the so-called selective catalytic reduction process, abbreviated as the SCR process.
- a selectively acting reducing agent is added to the exhaust gas for the purpose of nitrogen oxide reduction, typically ammonia.
- the ammonia is temporarily stored in a corresponding denitration catalytic converter, abbreviated as SCR catalytic converter, and is used by the latter to catalytically reduce nitrogen oxides (NO x ) contained in the exhaust gas with the formation of nitrogen and water.
- SCR catalytic converter a corresponding denitration catalytic converter
- the effectiveness of SCR catalysts is strongly dependent on the ratio N ⁇ / N0 2 at lower temperatures, with an effectiveness maximum at an N0 2 content of approx. 50% for temperatures below 200 ° C and significantly reduced effectiveness with a lower N0 2 content , At higher At temperatures above approx.
- the nitrogen oxide reduction is limited by the oxidation of ammonia.
- the ammonia storage capacity of the SCR catalytic converter decreases with increasing temperature.
- SCR catalysts are subject to thermal aging and should not be exposed to temperatures above approx. 700 ° C to 750 ° C.
- SCR catalytic converters can also store unburned hydrocarbons at low temperatures and, if the exhaust gas composition is rich, also oxidize hydrocarbons with a suitable design, especially if they contain vanadium oxide (V 2 0 5 ) as a catalytic material.
- a generic exhaust gas aftertreatment device is described in the published patent application EP 0 878 609 A1, in which an NO x storage catalytic converter and an SCR catalytic converter are arranged downstream of the exhaust gas system.
- the NO x storage catalytic converter can alternatively or additionally to a Three-way catalytic converter can be designed for ammonia formation with briefly rich engine operation, which is realized by post-injection of fuel into at least some of the engine combustion chambers.
- an exhaust gas aftertreatment device with an oxidation catalyst, a downstream NO x storage catalyst and a particle filter downstream of the NO x storage catalyst or between the oxidation catalyst and the NO x storage catalyst is described for particle and nitrogen oxide reduction.
- the oxidation catalytic converter favors the function of the NO x storage catalytic converter by formation of NO 2 , but no CRT effect can be achieved for the particle filter, since the nitrogen oxides are reduced to nitrogen even before the particle filter. If the oxidation Talysator is used for heating the particulate filter by burning post-injected fuel, this arrangement results in a high temperature load on the NO x storage catalytic converter and a relatively high fuel consumption.
- the exhaust gas upstream of the NO x storage catalytic converter predominantly contains NO and only a little N0 2 , since the latter is converted into NO by the CRT effect, as a result of which the storage behavior of the NO x storage catalytic converter deteriorates.
- the oxidation catalytic converter is used in this arrangement for the desulfation heating of the NO x storage catalytic converter by burning post-injected fuel, a relatively high temperature must be reached at the oxidation catalytic converter due to the high heat capacity and the heat transfer in the intermediate exhaust gas section, which can lead to thermal aging effects thereof ,
- the invention is based on the technical problem of providing an exhaust gas aftertreatment device of the type mentioned at the outset and an associated exhaust gas aftertreatment method with which as many of the following requirements as possible can be met to a high degree with relatively little effort: effective nitrogen oxide reduction in a wide temperature range, no additional reducing agent operating material , Avoidance of ammonia and hydrogen sulfide emissions, minimal particle emission, particle oxidation through N0 2 reaction, minimal CO and HC emissions, comparatively low temperature load of all exhaust gas cleaning components, minimal additional fuel consumption and little space requirement.
- the invention solves this problem by providing an exhaust gas aftertreatment device with the features of Claim 1 and an exhaust gas aftertreatment method with the features of claim 11 or 12.
- the exhaust gas aftertreatment device contains, in addition to a nitrogen oxide storage catalytic converter and an SCR catalytic converter connected downstream thereof, a particle filter and / or a NO 2 formation catalytic converter arranged upstream of the SCR catalytic converter.
- the nitrogen oxide storage catalytic converter enables effective nitrogen oxide reduction, especially in lean-burn internal combustion engines. Thanks to its NH 3 storage capacity, the downstream SCR catalytic converter prevents unwanted emissions of ammonia generated by the NO x storage catalytic converter. At the same time, the SCR catalytic converter is able to reduce nitrogen oxides, if any, with stored ammonia in the exhaust gas downstream of the NO x storage catalytic converter, the ammonia being simultaneously oxidized. This effect can be used to specifically form ammonia on the nitrogen oxide storage catalytic converter in order to use this as a reducing agent in the SCR catalytic converter.
- the N0 2 content is significantly lower and is, for example, a maximum of 20%.
- the effectiveness of the SCR catalyst is highest at low temperatures below 300 ° C, for example, with an N0 2 content of 50% a lower N0 2 share significantly reduced.
- the N0 2 formation catalyst can be connected upstream of it. This catalyst can have a comparatively small volume and have a coating which contains, inter alia, a noble metal (for example platinum) and is capable of at least in a temperature range from about 200 ° C. to 350 ° C. the NO 2 fraction of the NO x - Increase emissions to at least approximately 50%.
- the coating of the N0 2 formation catalyst has the property of not specifically oxidizing ammonia generated in the N0 X storage catalytic converter during operation with ⁇ ⁇ l, but allowing it to pass through unchanged. This can be achieved, for example, in that the coating contains no oxygen-storing component.
- control unit which can also be used, for example, to control the combustion device, such as an internal combustion engine
- functions are preferably implemented which decide on the necessity and possibility of specific NH 3 generation and the operating parameters, in particular the duration and enrichment depth at the NSK - Regeneration, specify appropriately.
- the NH 3 formation can be increased by a smaller air ratio and a longer regeneration period, provided the temperature of the NO x storage catalytic converter is in the range of possible NH 3 formation.
- the operation of the combustion device during the NSK regeneration can be adjusted in a manner known per se so that a high NO x raw emission thereof is achieved and the NH 3 formation on the NO x storage catalytic converter is thereby further increased.
- the SCR catalytic converter can also be used in order to avoid an H 2 S emission which arises, for example, during the desulfation.
- an SCR catalytic converter can, due to its specific Properties can oxidize to S0 2 even with rich exhaust gas composition ( ⁇ ⁇ l) during the desulfation. In this way, an unpleasant odor nuisance can be avoided.
- SCR catalysts if they contain vanadium oxide, can oxidize unburned hydrocarbons (HC) even under rich conditions ( ⁇ ⁇ 1). This can reduce the reduction agent breakthrough in NSK regeneration.
- the emission of potentially carcinogenic hydrocarbons such as benzene, toluene, ethylbenzene and xylene for example, can be reduced, which may result from rich conditions at the N0 X storage catalyst.
- the SCR catalytic converter Due to its property of also storing hydrocarbons at low temperatures, the SCR catalytic converter can also help to reduce HC emissions after a cold start. The HC stored at low temperatures are released again at higher temperatures and can be oxidized on the SCR catalytic converter or a downstream oxidation catalytic converter.
- a particle filter can be used for post-motor particle reduction. This retains the emitted particles with a high degree of effectiveness. As usual, the collected particles can be burned off at regular intervals by increasing the temperature to over 600 ° C. If the exhaust gas reaching the particle filter contains N0 2 , soot oxidation takes place in the temperature range between approximately 250 ° C and 400 ° C by reaction with N0 2 (CRT effect).
- the particle filter can generally be coated catalytically, wherein the coating can contain components such as a noble metal (eg platinum) and a washcoat.
- the occurring maximum temperature load of the individual components can be be adapted to specific requirements.
- it can be ensured by a suitable arrangement that the temperatures of the individual components during driving are in a range that is favorable for the respective function.
- the rich operation required for the regeneration of the NO x storage catalytic converter can be achieved by means of internal engine measures or an additional post-engine introduction of reducing agent (for example fuel or hydrogen).
- the NO x storage catalytic converter for desulfation and the particle filter for thermal regeneration can be heated by means of internal engine measures, including fuel post-injection.
- internal engine measures including fuel post-injection.
- incompletely burned hydrocarbons remaining in the exhaust gas lead to an additional exothermic reaction on an optionally arranged catalytic converter, which further increases the exhaust gas temperature.
- reducing agent for example fuel or hydrogen
- reducing agent eg fuel or hydrogen
- other methods of heating are also possible. These are not explicitly mentioned below, but can be used instead of the post-motor supply of reducing agent.
- an electrically heated catalytic converter, electrical heating of the particle filter or the use of a burner can be mentioned as customary conventional measures.
- the secondary air can be provided, for example, by an electrically driven secondary air pump or a compressor, or can be removed by a compressor in the case of supercharged engines.
- An optional combination or integration of two of the functionalities mentioned in one component can achieve a significant reduction in the space requirement.
- the exhaust gas treatment device includes one or more N0 X sensors after the NO x storage catalytic converter and / or the SCR catalyst and / or means for detecting the temperature of one or more of the exhaust gas purifying component and / or means for detecting the NH 3 - Loading the SCR catalytic converter.
- the method according to claim 11 enables a comparatively precise, model-based control of the point in time for the triggering of a respective regeneration of the nitrogen oxide storage catalytic converter.
- the method according to claim 12 allows a targeted control of the ammonia generation during a respective regeneration phase of the nitrogen oxide storage catalytic converter, taking into account the current conditions, in particular The temperatures of the ammonia-generating NO x storage catalyst and the SCR catalyst and / or the ammonia loading of the SCR catalyst, depending on the determined operating state, a variable amount of ammonia can be specified, which is to be generated in the upcoming regeneration phase of the NO x storage catalyst ,
- this method is used as a criterion for the completion of a regeneration phase of the NO x storage catalytic converter determining whether the exhaust air-fuel ratio after the N0 x storage catalyst falls below a value dependent on the desired amount of ammonia formation threshold.
- an external, for example post-engine, reducing agent supply can be provided in the exhaust line during the NSK regeneration in order to operate the combustion device lean also in this period and thereby achieve a high NO x raw emission thereof.
- a secondary air supply can be provided at a suitable point in the exhaust line during the rich operation phases in order to oxidize any proportions of NH 3 , H 2 S, CO and HC in these operating phases and thus to prevent corresponding pollutant emissions.
- FIG. 1 is a schematic block diagram representation of an internal combustion engine of a motor vehicle with closed, single-flow exhaust gas aftertreatment device, which, connected in series, contains a first oxidation catalytic converter, a particle filter, a NO x storage catalytic converter, a NO 2 formation catalytic converter, an SCR catalytic converter and a second oxidation catalytic converter,
- FIG. 2 shows a schematic block diagram representation corresponding to FIG. 1, but with a modified exhaust gas aftertreatment device which, in series, contains a NO x storage catalytic converter, a NO 2 formation catalytic converter, a particle filter, an SCR catalytic converter and an oxidation catalytic converter,
- FIG. 3 shows a schematic block diagram representation corresponding to FIG. 1 with a modified exhaust gas aftertreatment device which, connected in series, contains a NO x storage catalytic converter, an NO formation catalytic converter, an SCR catalytic converter, an oxidation catalytic converter and a particle filter,
- FIG. 4 is a schematic block diagram representation corresponding to FIG. 1, but with a modified exhaust gas aftertreatment device that includes a first oxidation catalyst, an integrated nitrogen oxide storage and SCR catalyst, a second oxidation catalyst and a particle filter, and
- FIG. 5 is a schematic block diagram representation corresponding to FIG. 1, but for a modified internal combustion engine with a double-flow exhaust line and orderly double-flow exhaust gas aftertreatment device.
- a control unit 2 serves to control the internal combustion engine 1, which can be, for example, a conventional diesel or gasoline engine, and the exhaust gas aftertreatment device. Furthermore, temperature sensors 8, NO x sensors 9, lambda probes 10, devices 11 for the post-engine supply of reducing agent, a device 12 for the supply of secondary air and pressure sensors 14 are provided at suitable points on the exhaust gas line 3, as shown.
- the internal combustion engine 1 delivers exhaust gas that contains NO x , particles, CO and HC, among other things.
- CO and HC are oxidized to C0 2 and H 2 0 on the oxidation catalyst 4.
- part of the NO contained in the exhaust gas is oxidized to N0 2 .
- the particles present in the exhaust gas are retained in the particle filter 5.
- a part of the soot particles accumulated in the particle filter 5 is oxidized by reaction with N0 2 , whereby N0 is reduced to NO.
- the nitrogen oxides contained in the exhaust gas are stored in the NO x storage catalytic converter 6.
- the N0 2 content is significantly lower and is, for example, a maximum of 20%.
- the effectiveness of the SCR catalytic converter 7 is highest and at low temperatures below 300 ° C., for example, with a NO 2 content of 50% significantly reduced with a lower N0 2 content. Therefore, the .SCR catalyst 7 is preceded by the N0 2 formation catalyst 13.
- This catalyst 13 has a coating containing, inter alia, noble metal (eg platinum) and is capable, at least in a temperature range of about 200 ° C to 35 ⁇ '° C the N0 2 content in the NO x emissions to at least approximately Increase 50%.
- the coating of the N0 2 formation catalyst has the property of not specifically oxidizing ammonia generated in operation with ⁇ ⁇ l in the NO x storage catalyst, but allowing it to pass through unchanged. This can be achieved, for example, in that the coating contains no oxygen-storing component.
- the SCR catalytic converter 7 is able to reduce the nitrogen oxides with the aid of NH 3 stored in it. Here, the effectiveness at temperatures below 300 ° C is increased by the upstream NO 2 formation catalyst 13.
- Heating measures can be used in order to achieve sufficient temperatures on all components, in particular on the NO x storage catalytic converter 6 and SCR catalytic converter 7, even during low-load operation and thus to achieve the best possible NO x reduction.
- These can be internal engine, for example a late relocation of the main injection or post-injection, or also post-engine by supplying a reducing agent upstream of the NO x storage catalytic converter for exothermic generation, provided the NO x storage catalytic converter 6 has reached a sufficient temperature for converting the reducing agent.
- Other measures to increase the exhaust gas temperature can include: increasing the idle speed, lengthening the afterglow time, switching on additional electrical consumers or increasing the EGR rate.
- the above-mentioned heating measures can be controlled, for example, by the control unit 2 depending on the incoming temperature sensor signals or by means of a model.
- the exhaust pipe 3 can be thermally insulated, to minimize heat loss from the exhaust gas. For example, air gap insulation can be used.
- NSK regenerations are required at regular intervals.
- the times for regenerations are determined with the help of the NO x sensor 9 behind the SCR catalytic converter.
- the signal from the NO x sensor 9 is recorded and evaluated in the control unit 2.
- the control unit 2 requests an NSK regeneration , If criteria taken into account in the control unit 2 are fulfilled, which are a prerequisite for the realization of an NSK regeneration on the engine side, for example operation in a part of the operating range of the engine 1 in which an NSK regeneration can be represented, the NSK regeneration is initiated.
- the control unit 2 contains models for the NO x raw emission, the NO x storage behavior of the NO x storage catalytic converter 6, the NH 3 formation on the NO x storage catalytic converter and the NH 3 storage in the SCR Catalyst 7 stored. These can be used for the evaluation of the NO x sensor signal behind the SCR catalytic converter and can also be used for diagnostic purposes. Based on the sensor signals, the models can be adapted to the current aging condition of the catalysts. Alternatively, by comparing the sensor signals of the NO x sensors 9 and / or the lambda probes 10 with the modeled behavior of the catalysts, a diagnosis of the aging state can be carried out without, however, adapting the model.
- an NSK Regeneration can be requested if the modeled SCR loading with NH 3 falls below a relative value, eg 5% of the possible NH 3 loading, or absolute value, eg 0.1 g NH 3 .
- the signal from the NO x sensor 9 after the NO x storage catalytic converter can also be viewed. This can be evaluated analogously to the procedure described above and can serve as a criterion for the request for NSK regeneration.
- the signal from the NO x sensor 9 after the N0 X storage catalytic converter can be used as an input variable for the NSK model in the control unit 2.
- the nitrate loading of the N0 2 storage catalytic converter 6 can be calculated and thus the NH 3 formation can be estimated taking into account the aging.
- the NH 3 loading of the SCR catalytic converter 7 is also calculated using a model, NSK regeneration can be requested if the modeled SCR loading with NH 3 has a relative value, for example 5% of the possible NH 3 loading, or absolute Value, for example 0.1 g NH 3 , falls below.
- both NO x sensors 9 can also be used, a sensor as described above providing a criterion for requesting NSK regeneration and the second NO x sensor being used for diagnosis and adaptation of the catalyst models in the control unit 2.
- an NH 3 sensor can be provided after the N0 X storage catalytic converter and also after the SCR catalytic converter (not shown in FIG. 1), the signal for adapting the models of the N0 X storage catalytic converter 6 and the SCR catalytic converter 7 or for Regulation of the regeneration parameters can be used.
- the control unit 2 contains functions which decide on the necessity and possibility of a specific NH 3 generation in the case of an upcoming NSK regeneration and which accordingly specify the operating parameters, in particular the duration and the enrichment level.
- temperatures of the NO x storage catalytic converter 6 and the SCR catalytic converter 7. are determined by the temperature sensors 8 in or behind the respective components.
- the temperature of the SCR catalytic converter 7 can be calculated on the basis of the measured temperature after the NO x storage catalytic converter with the aid of a model in the control unit 2, so that the sensor 8 after the SCR catalytic converter can be omitted.
- the current NH 3 loading of the SCR catalytic converter 7 calculated using the model can also be used as a criterion.
- the temperatures of the N0 X storage catalytic converter 6 and the SCR catalyst 7 are within predetermined ranges, the current NH 3 -load of the SCR catalyst 7 is low, and possibly other conditions are satisfied, a maximum NH 3 formation is sought , If the temperature of the NO x storage catalytic converter 6 is outside the predetermined range, which can be, for example, between 230 ° C. and 370 ° C., NH 3 formation is not possible or is possible only to a limited extent and is therefore also not sought. This avoids unnecessarily high fuel consumption and increased HC and CO emissions due to regeneration that is too long. If the temperature of the SCR catalytic converter 7 is outside the predetermined range, which can be, for example, between 200 ° C.
- temperature gradients for example a rapid increase, can also be taken into account or a temperature prediction can be implemented.
- the predicted temperature is then taken into account in addition to the current temperature. For example, less NH 3 formation is aimed for if a strong increase in the temperature of the SCR catalytic converter 7 is predicted, since otherwise there is a risk of subsequent NH 3 desorption in the SCR catalytic converter 7.
- the aging state of the NO x storage catalyst 6 is also taken into account 3 formation in deciding on the desired NH, since the NO x with increasing aging of the N0 X storage catalytic converter 6 - reduction in the SCR catalyst 7 is gaining in importance.
- the optimal air ratio is determined in the control unit 2 as a function of the desired NH 3 formation. If strong NH 3 formation is desired, an air ratio for maximum NH 3 formation is specified. If this is not the case, an air ratio is specified for little or no NH 3 formation. Intermediate values for average NH 3 formation are also possible.
- the air ratio can also be varied continuously or in stages during the NSK regeneration. For example, a lower air ratio can be set at the beginning and a larger air ratio with progressive regeneration in order to achieve a strong NH 3 formation with low HC and CO emissions during the NSK regeneration. The duration of the NSK regeneration is also set depending on the desired NH 3 formation.
- the regeneration is ended as soon as the air ratio determined with the lambda probe 10 after the NO x storage catalytic converter falls below a threshold value ⁇ l.
- it can also be extended beyond this point in time by a predetermined time or number of work cycles of the engine 1.
- the regeneration is ended immediately as soon as the air ratio downstream of the NO x storage catalytic converter falls below a threshold value ⁇ 2, where ⁇ 2 is greater than ⁇ l. This largely prevents HC / CO breakthroughs and low fuel consumption.
- the threshold values can be varied depending on the NSK aging and other parameters. Intermediate values are also possible in order to achieve a medium NH 3 formation.
- the engine operation during the NSK regeneration is additionally set in such a way that the highest possible N0 X raw emission of the engine 1 is achieved. This can be done in combination with a post-engine supply of reducing agent upstream of the N0 X storage catalytic converter 6. This further increases the NH 3 formation on the NO x storage catalytic converter 6. If no NH 3 formation is aimed for, on the other hand, the engine operation is set so that the lowest possible N0 X raw emission of the same is achieved.
- the device 11 arranged in front of the NO x storage catalytic converter 6 for the supply of reducing agent after the engine is used to convert the N0 X storage catalytic converter 6 for a desulfating heating up.
- This measure takes place in addition to motor measures for heating.
- the motor measures can be reduced by the support by means of the supply of a reducing agent after the motor, so that the thermal aging of the oxidation catalytic converter is reduced.
- the up heating of the N0 X storage catalytic converter 6 post-engine solely by supply of reducing agent is not desirable, since because of the large amount of reducing agent a strong exo- thermie would be produced on the N0 X storage catalytic converter 6, which would lead to thermal aging.
- the amount of reducing agent supplied is regulated, inter alia, depending on the following parameters: desired temperature of the NO x storage catalytic converter 6, actual temperature after the particle filter, actual temperature after the NO x storage catalytic converter and exhaust gas mass flow.
- At least one of the two devices 11 shown in FIG. 1 for the post-motor supply of reducing agent can be used to achieve the highest possible NO x raw emission of the engine 1 during the NSK regeneration.
- the air ratio can before N0 X storing catalyst to ⁇ ⁇ l are lowered.
- Thermal regeneration of the particle filter 5 is required at regular intervals. This can be the case, for example, if a high pressure drop across the particle filter 5 is determined with the pressure sensors 14 before and after the particle filter, which indicates an impermissibly high loading of the particle filter 5.
- the device 11 arranged in front of the particle filter 5 and the upstream oxidation catalytic converter 4 can be used to heat the particle filter 5 post-motor supply of reducing agents can be used. This measure takes place in addition to internal engine measures to raise the exhaust gas temperature. The measures taken within the engine can be reduced by the support by means of a supply of reducing agents after the engine.
- Heating of the oxidation catalytic converter 4 and thus of the particle filter 5 solely by supplying the motor with a reducing agent is not to be aimed at, since the large quantity of reducing agent would cause a strong exothermic reaction on the oxidation catalytic converter 4, which would lead to thermal aging.
- the amount of reducing agent supplied is regulated, inter alia, depending on the following parameters: desired temperature of the particle filter 5, actual temperature before the particle filter, actual temperature after the particle filter and exhaust gas mass flow.
- the device 12 for supplying secondary air and the further oxidation catalytic converter 4 are connected downstream of the SCR catalytic converter 7.
- This oxidation catalyst 4 can be made significantly smaller and, for example, also with a lower noble metal loading than the oxidation catalyst 4 upstream of the particle filter.
- the device 12 for supplying secondary air is always activated when the engine 1 is operated with ⁇ ⁇ 1. Unwanted emissions such as NH 3 , H 2 S and CO and HC can occur during these phases. These components can be oxidized in the oxidation catalytic converter 4 downstream of the device 12 for supplying secondary air, so that an emission of these undesired components is avoided.
- the quantity of secondary air supplied is set such that a lean exhaust gas composition ( ⁇ > l) is achieved on the downstream oxidation catalytic converter 4 despite engine operation with ⁇ ⁇ l.
- the signal of at least one lambda probe 10 and the exhaust gas mass flow are used in the control unit 2, among other things. If the device 12 for supplying secondary air is only able to provide a sufficient amount of secondary air after a certain lead time, it is activated with a corresponding lead time before the change to operation with ⁇ ⁇ l.
- the SCR catalytic converter 7 is protected from high temperatures after the particle filter during the thermal regeneration of the particle filter 5, since the exhaust gas line length significantly cools the exhaust gas until it reaches the SCR catalytic converter 7 and also the NO x storage catalyst 6 acts as a heat sink. In this way, the thermal aging of the SCR catalyst 7 can be kept low.
- the high thermal capacity of the particle filter 5 leads to a stabilization of the temperatures of the downstream components, even during unsteady driving. This ensures that the NO x storage catalytic converter 6 and the SCR catalytic converter 7 are usually in a favorable temperature range, even during unsteady driving, and the system therefore operates with high efficiency.
- the risk is minimized that undesired desorption of stored NH 3 occurs on the SCR catalytic converter 7 due to a rapid increase in temperature.
- the particle filter 5 can be catalytically coated.
- the catalytic coating of the particle filter 5 can be similar to the coating of one of the oxidation catalysts 4.
- the upstream oxidation catalyst 4 can be made smaller or with a lower noble metal content, which leads to space and cost advantages.
- the oxidizer connected upstream of the particle filter 5 can on catalyst 4 also completely eliminated.
- the temperature sensor 8 in front of the particle filter 5 is also omitted.
- the catalytic coating of the particle filter 5 can also be similar to the coating of the NO x storage catalytic converter 6.
- the downstream NO x storage catalytic converter 6 can be made smaller, which leads to space and cost advantages.
- the separate NO x storage catalytic converter 6 can also be dispensed with entirely, ie integrated into the particle filter 5.
- the temperature sensors 8 can also be omitted.
- Part or all of the NO x sensors 9 can also be omitted.
- the components contained in the exhaust gas aftertreatment system are modeled in the control unit 2 such that the temperatures or NO x concentrations occurring at the respective positions are available as output variables of the model.
- one or both devices 11 for the post-motor supply of reducing agent can be omitted.
- the device 12 for supplying secondary air and the downstream oxidation catalyst 4 can also be omitted.
- the N0 2 formation catalyst 13 can, as shown in Fig. 1, be carried out as a separate component. Alternatively, it is also possible to integrate this at the outlet end of the NO x storage catalytic converter 6 or at the inlet end of the SCR catalytic converter 7. Alternatively, the N0 2 formation catalyst 13 can also be omitted.
- the embodiment shown in FIG. 2 differs from that of FIG. 1 in that the NO x storage Catalyst 6 forms the first exhaust gas cleaning component, which then the N0 2 formation catalyst 13, the particle filter 5, the SCR catalyst 7 and the downstream oxidation catalyst 4 are connected in this order, while the other, upstream oxidation catalyst is omitted.
- Functionally identical components are given the same reference numerals in FIG. 2 as in FIG. 1.
- the following explanations for the exemplary embodiment of FIG. 2 can be limited to the differences resulting from the different order of the exhaust gas-cleaning components, otherwise the above applies to the exemplary embodiment 1 explained properties and advantages accordingly.
- the NO x storage catalytic converter 6 of the internal combustion engine takes in the example of Fig. 2, the function in the regular lean operation 1 CO and HC to C0 2 and to oxidise H 2 0 and rn a substantial part of vitespeiche in the exhaust nitrogen oxides contained '.
- the NO 2 formation catalyst 13 is connected directly upstream of the particle filter 5 in order to increase the NO 2 content of the nitrogen oxides, depending on the operating state after the NO x storage catalyst 6, still typically contained in the exhaust gas, from typically at most 20% to at least about 50% .
- the soot oxidation in the particle filter 5 can be promoted by reaction with NO 2 (CRT effect) and the effectiveness of the downstream SCR catalytic converter 7 can be increased.
- CRT effect reaction with NO 2
- These effects can be further enhanced by allowing a maximum NO x slip at the NO x storage catalytic converter 6, so that the NO x reduction potential of the SCR catalytic converter 7 can be used to the maximum.
- the effectiveness is also increased by the NO 2 formation catalyst 13 connected upstream of the particle filter 5.
- the device 11 positioned here directly in front of the NO 2 formation catalytic converter 13 can be used to heat the particle filter 5, so that internal engine measures can be reduced for this purpose, which reduces the aging effects of the NO x .
- Storage catalyst 6 reduced.
- the heating of the N0 2 formation catalytic converter 13 solely by supplying a reducing agent after the engine is not desirable because of the thermal aging effects thereof.
- the amount of reducing agent supplied is regulated, inter alia, depending on the following parameters: target temperature of the particle filter 5, actual temperature before the NO 2 formation catalyst or after the NO x storage catalyst, actual temperature after the particle filter and exhaust gas mass flow.
- the NO x storage catalytic converter 6 quickly reaches the required operating temperature after a cold start due to its position close to the engine. This means that small measures are required to raise the exhaust gas temperature. This leads to a reduction in fuel consumption through heating measures.
- the SCR catalytic converter 7 is protected from high temperatures during the desulfation of the NO x storage catalytic converter 6, since the exhaust gas line causes a significant cooling of the exhaust gas until it reaches the SCR catalytic converter 7 and also the particle filter 5 and the N0 2 formation catalyst 13 act as a heat sink. In this way, the thermal aging of the SCR catalyst 7 can be kept low.
- the high heat capacity of the particle filter 5 leads to a stabilization of the temperature of the downstream SCR catalytic converter 7, even during unsteady driving. This ensures that the SCR catalytic converter 7 even when the stationary driving is usually in a favorable temperature range and therefore works with high efficiency. In addition, the risk is minimized that undesired desorption of stored NH 3 occurs on the SCR catalytic converter 7 due to a rapid increase in temperature.
- the particle filter 5 can be catalytically coated.
- the catalytic coating of the particle filter 5 can be similar to the coating of the NO 2 formation catalyst 13.
- the upstream NO 2 formation catalyst 13 can be made smaller or with a lower noble metal content, which leads to space and cost advantages. If necessary, the N0 2 formation catalyst upstream of the particle filter 5 can also be dispensed with entirely.
- the catalytic coating of the particle filter 5 can also be similar to the coating of the NO x storage catalytic converter 6.
- the N0 X storage catalytic converter 6 arranged close to the engine can be made smaller, which leads to installation space and cost advantages.
- the separate NO x storage catalytic converter 6 can also be dispensed with entirely, ie its function can be integrated in the particle filter 5.
- the N0 2 formation catalyst 13 and the device 11 for the post-engine supply of reducing agent upstream of the N0 2 formation catalyst 13 can also be omitted.
- the pressure sensor 14 shown in front of the particle filter is retained, the NO x sensor 9 shown in FIG. 2 after the NO x storage catalytic converter 6 and the lambda probe 10 are then positioned behind the particle filter 5:
- the catalytic coating can also be similar to the coating of the downstream SCR catalytic converter 7.
- the SCR catalytic converter 7 can be made smaller, which leads to space and cost advantages.
- the SCR catalytic converter as a separate component can also be dispensed with entirely.
- the temperature sensor 8 shown in FIG. 2 between the particle filter and the SCR catalytic converter can be omitted, but the pressure sensor 14 shown after the particle filter is retained.
- the N0 2 formation catalyst 13 can also be integrated instead of upstream of the particle filter 5 at the outlet end of the NO x storage catalyst 6.
- the NO 2 formation catalyst 13 can also be arranged upstream of the SCR catalyst 7.
- the NO 2 formation catalyst 13 can also be integrated at the entry-side end of the SCR catalyst 7.
- the N0 2 formation catalyst 13 can also be omitted.
- a further oxidation catalytic converter can additionally be connected upstream of the NO x storage catalytic converter 6, which can lead to a further reduction in HC and CO emissions, particularly during a cold start.
- FIG. 3 shows, as a further variant, an exhaust gas aftertreatment device which differs from that of FIG. 2 in that the positions of the particle filter 5 and SCR catalyst 7 are interchanged and the oxidation catalyst 4 is connected directly upstream of the particle filter 5.
- the other components that is to say the various sensors 8, 9, 10, 14, the devices 11 for the post-motoric reducing agent supply and the secondary air supply device 12 are also suitable for the associated exhaust gas cleaning components 4 to 7 , 13 arranged in the exhaust line 3 at modified positions.
- the devices 11 for the post-motoric reducing agent supply and the secondary air supply device 12 are also suitable for the associated exhaust gas cleaning components 4 to 7 , 13 arranged in the exhaust line 3 at modified positions.
- Analogous to the embodiment of FIG. 2 above only those measures and the resulting effects of the example of FIG. 3 will be discussed below that 1 and 2 are different from those in the examples of FIGS. 1 and 2, while reference may otherwise be made to the above explanations regarding the examples of FIGS. 1 and 2 with regard to the corresponding functions and properties.
- the NO 2 formation catalyst 13 connected upstream of the SCR catalytic converter 7 in turn permits a noticeable increase in the effectiveness of the SCR catalytic converter 7, in particular in the temperature range below 300 ° C.
- the device 11 upstream of the oxidation catalyst 4 upstream of the particle filter 5 can be used to heat up the particle filter 5 for supplying the engine with a reducing agent.
- the NO x storage catalytic converter 6 and the SCR catalytic converter 7 are not thermally stressed by this measure.
- An exclusive heating of the particulate filter by the supply of a reducing agent after the engine is not sought, in order not to cause excessive thermal aging of the oxidation catalytic converter 4.
- the quantity of reducing agent supplied is regulated, inter alia, depending on the following parameters: target temperature of the particle filter 5, actual exhaust gas temperature upstream of the oxidation catalytic converter 4 or after the SCR catalytic converter 7, actual exhaust gas temperature after the particle filter 5 and exhaust gas mass flow.
- the SCR catalytic converter 7 also reaches the required operating temperature relatively quickly after a cold start due to its position behind the NO x storage catalytic converter 6. Another advantage is that no additional oxidation catalyst is required as the last system component in order to oxidize the undesired exhaust gas components by means of secondary air injection.
- the SCR catalytic converter 7 is protected against high temperatures. protected during thermal regeneration of the particle filter 5 by being positioned upstream of the particle filter 5.
- the particle filter 5 can be catalytically coated, the catalytic coating being similar to that of the upstream oxidation catalyst 4, so that the latter can be made smaller or with a lower noble metal content, which leads to space and cost advantages.
- the oxidation catalyst upstream of the particle filter 5 can also be completely dispensed with.
- the N0 2 formation catalyst 13 can, as shown in Fig. 3, be designed as a separate component. Alternatively, it can be integrated into the relevant component at the outlet-side end of the NO x storage catalytic converter 6 or at the inlet-side end of the SCR catalytic converter 7, or can be omitted entirely. In a manner not shown, a further oxidation catalytic converter can be connected upstream of the NO x storage catalytic converter 6, which can lead to a further reduction in HC and CO emissions, particularly during a cold start.
- FIG. 4 shows a further variant in which the exhaust gas aftertreatment device has a combined SCR and nitrogen oxide storage catalytic converter 15, which combines the functions of the NO x storage catalytic converter 6 and the SCR catalytic converter 7 of the examples in FIGS. 1 to 3.
- An oxidation catalytic converter 4 is directly connected upstream of this integrated catalytic converter 15 and the downstream particle filter 5.
- the remaining components according to the examples of FIGS. 1 to 3 are arranged to match the position of these exhaust gas cleaning components 4, 5, 15, as shown.
- the integrated catalytic converter 15 can be realized, for example, by using an SCR catalytic converter, which is produced as a full extrudate, the catalytic material of the SCR catalytic converter serving as a carrier for a further catalytic coating, namely a nitrogen oxide storage catalytic converter coating.
- a nitrogen oxide storage catalyst coating in addition to the SCR coating in the case of an SCR catalyst which is not produced as a full extrudate.
- both functional components reach the required operating temperature very quickly after the cold start, so that almost no additional heating measures are required, which would result in an increase in fuel consumption.
- the times for NSK regeneration are determined in the example of FIG. 4 with the help of the NO x sensor 9 behind the integrated, combined catalyst 15 or alternatively by one of the other methods mentioned above.
- the models stored in the control unit 2 include a model of the nitrogen oxide storage behavior, the ammonia storage behavior and the ammonia generation behavior of the combined catalytic converter 15.
- the temperature of the combined catalytic converter 15 as can be detected by the temperature sensor 8 connected downstream.
- the model-based, current ammonia loading of the combined catalyst 15, for example can also be used as a further criterion.
- a maximum NH 3 formation can be sought, for example, if the temperature of the combined catalytic converter 15 is within a predetermined range of, for example, between 230 ° C. and 370 ° C. and the current NH 3 load thereof is low and other conditions are possibly met ,
- the device 11 arranged in front of the oxidation catalytic converter 4 close to the engine for the supply of post-engine reductant can be used to heat the integrated, combined catalytic converter 15 for desulfating the nitrogen oxide storage catalytic converter coating, supplemented by additional engine heating measures, as explained above.
- the amount of reducing agent supplied is regulated, inter alia, depending on the following parameters: target temperature of the combined catalytic converter 15, actual temperature of the same and exhaust gas mass flow.
- the oxidation catalytic converter 4 connected upstream of the particle filter 5 and the device 11 connected upstream thereof for the supply of post-motor reducing agent can be used to heat the particle filter.
- the combined nitrogen oxide storage and SCR catalytic converter 15 in turn remains unloaded thermally by the particle filter heating.
- the amount of reducing agent supplied is regulated, inter alia, depending on the following parameters: the desired temperature of the particle filter 5, the actual exhaust gas temperature upstream of the oxidation catalytic converter 4, the actual exhaust gas temperature after the particle filter 5 and the exhaust gas mass flow. It is advantageous in the embodiment of FIG.
- the particle filter 5 can be catalytically coated, in particular with a catalytic coating similar to that of the upstream oxidation catalytic converter 4.
- the upstream oxidation catalytic converter 4 can be made smaller or with a lower noble metal content, which leads to corresponding installation space and cost advantages.
- the oxidation catalyst 4 upstream of the particle filter 5 can also be omitted.
- the SCR catalyst coating and the nitrogen oxide storage catalyst coating can be applied in a suitable manner mixed on a carrier in the combined catalyst 15.
- the two coatings can be applied alternately in the exhaust gas flow direction, so that the exhaust gas first flows through an area with nitrogen oxide storage catalyst coating, then an area with SCR catalyst coating, then again through an area with nitrogen oxide storage catalyst coating, etc.
- This embodiment can also be realized in that disks of a nitrogen oxide storage catalytic converter and disks of an SCR catalytic converter are alternately arranged one behind the other in a housing.
- the arrangement that changes several times in the exhaust gas flow direction has the advantage that there is an extended temperature window in which the system works efficiently. This is how temperature peaks whose area of the system is less noticeable with a multiple alternating arrangement of nitrogen oxide storage catalyst and SCR catalyst, for example in the formation of ammonia, than in an arrangement with a nitrogen oxide storage catalyst and a separately connected SCR catalyst.
- the internal combustion engine 1 has a double-flow section of the exhaust line 3 with a suitably assigned exhaust gas aftertreatment device.
- the latter comprises, in a similar and symmetrical manner, a NO x storage catalytic converter 6, a NO 2 formation catalytic converter 13 and an SCR catalytic converter 7 together with associated sensors 8, 9, 10 and device 11 for supplying post-motoric reductant at suitable positions in accordance with the examples in FIG 1 to 4.
- the two parallel exhaust gas lines are merged downstream of the two SCR catalytic converters 7 to form a subsequent, single line section, in which the particle filter 5, together with an upstream oxidation catalytic converter 4 and matching sensors 8, 9, 14, device 11 for the post-engine Reducing agent supply and secondary air supply device 12 are arranged as shown.
- Such a double-flow arrangement can be useful, for example, in engines whose cylinders are arranged in a V-shape.
- the prerequisite is that if an exhaust gas turbocharger is used, a separate turbocharger is used for each cylinder bank, since otherwise the two flows must be brought together before the turbine of the turbocharger.
- the operating strategy for this exhaust gas aftertreatment system is designed in such a way that only minor modifications are necessary compared to the operation of a single-flow system. This is important because otherwise complex new developments of additional functions in the control unit 2 of the internal combustion engine 1 would be required. In addition, this approach can limit the number of sensors used and thus the increase in costs for the overall system.
- the basic idea is to consider the two parallel strands as a single strand, so that basically the same processes take place in both strands. This is only possible if the two strands do not differ fundamentally in terms of raw engine emissions, catalyst types and catalyst volumes, etc.
- more complex approaches such as strands operated completely independently of one another and, for example, also staggered phases with rich exhaust gas, so that lean exhaust gas is always present after the two strands have been brought together, are possible.
- the signals from the NO x sensors 9 downstream of the NO x storage catalytic converters 6 can be used in an averaged or differently weighted manner as a representative nitrogen oxide concentration after the NO x storage catalytic converter for the NSK model in the control unit 2.
- the termination criterion for NSK regeneration can be a drop below the associated threshold value ⁇ l by one of the two lambda sensors 10 downstream of the two parallel NO x storage catalysts 6. If no ammonia formation is desired, the NSK regeneration is terminated, for example, immediately if the air ratio after one of the two parallel NO x storage catalytic converters 6 falls below the threshold value ⁇ 2.
- the two parallel exhaust gas section sections can also be merged directly behind the two parallel NO x storage catalytic converters 6 to form a subsequent single-flow section section, in which there is then only one SCR catalytic converter 7 with an optional NO 2 formation catalytic converter 13 connected upstream.
- the use of integrated nitrogen oxide storage and SCR catalysts in each of the plurality of strand sections is in accordance with the example of FIG. 4 and / or a different sequence of the exhaust gas-purifying Components possible, in particular according to the Fig. 1, 2 and 4.
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Abstract
L'invention se rapporte à un dispositif de post-traitement de gaz d'échappement comprenant un catalyseur de stockage d'oxyde d'azote et un catalyseur de réduction sélective (SCR), ainsi qu'à un procédé de post-traitement de gaz d'échappement correspondant. Le dispositif selon l'invention est caractérisé en ce qu'il comporte : un filtre à particules disposé en amont du catalyseur de stockage d'oxyde d'azote ou entre ce catalyseur de stockage d'oxyde d'azote et le catalyseur SCR ou en amont du catalyseur SCR, et/ou ; un catalyseur de formation de NO2 disposé en amont du catalyseur SCR. Il est possible de déterminer le moment des phases fonctionnelles de régénération du catalyseur de stockage d'oxyde d'azote, en fonction de la teneur en oxyde d'azote du gaz d'échappement en amont du catalyseur de stockage d'oxyde d'azote ou du catalyseur SCR, et/ou à partir de sa charge en ammoniac. Il est en outre possible de déterminer une quantité de production d'ammoniac théorique pour chaque phase fonctionnelle de régénération. La présente invention se rapporte en outre à l'utilisation de ce dispositif et de ce procédé, principalement pour des moteurs à combustion interne et à mélange pauvre de véhicule automobile.
Applications Claiming Priority (3)
Application Number | Priority Date | Filing Date | Title |
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DE10300298 | 2003-01-02 | ||
DE10300298A DE10300298A1 (de) | 2003-01-02 | 2003-01-02 | Abgasnachbehandlungseinrichtung und -verfahren |
PCT/EP2003/014313 WO2004061278A1 (fr) | 2003-01-02 | 2003-12-16 | Dispositif et procede de post-traitement de gaz d'echappement |
Publications (1)
Publication Number | Publication Date |
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EP1579109A1 true EP1579109A1 (fr) | 2005-09-28 |
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Application Number | Title | Priority Date | Filing Date |
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EP03782415A Withdrawn EP1579109A1 (fr) | 2003-01-02 | 2003-12-16 | Dispositif et procede de post-traitement de gaz d'echappement |
Country Status (5)
Country | Link |
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US (5) | US7210288B2 (fr) |
EP (1) | EP1579109A1 (fr) |
JP (1) | JP4541898B2 (fr) |
DE (1) | DE10300298A1 (fr) |
WO (1) | WO2004061278A1 (fr) |
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US6973776B2 (en) * | 2003-11-03 | 2005-12-13 | Ford Global Technologies, Llc | Exhaust gas aftertreatment systems |
US7062904B1 (en) * | 2005-02-16 | 2006-06-20 | Eaton Corporation | Integrated NOx and PM reduction devices for the treatment of emissions from internal combustion engines |
US7063642B1 (en) * | 2005-10-07 | 2006-06-20 | Eaton Corporation | Narrow speed range diesel-powered engine system w/ aftertreatment devices |
US7562522B2 (en) * | 2006-06-06 | 2009-07-21 | Eaton Corporation | Enhanced hybrid de-NOx system |
WO2008103113A1 (fr) * | 2007-02-21 | 2008-08-28 | Volvo Lastvagnar Ab | Procédé et système de diagnostic embarqué pour un système de post-traitement de gaz d'échappement |
US8448424B2 (en) * | 2009-01-16 | 2013-05-28 | Ford Global Technologies, Llc. | Emission control system with an integrated particulate filter and selective catalytic reduction unit |
DE102011085952A1 (de) * | 2011-11-08 | 2013-05-08 | Robert Bosch Gmbh | SCR-Katalysatorsystem und Verfahren zu seinem Betrieb |
-
2003
- 2003-01-02 DE DE10300298A patent/DE10300298A1/de not_active Withdrawn
- 2003-12-16 JP JP2004564200A patent/JP4541898B2/ja not_active Expired - Lifetime
- 2003-12-16 EP EP03782415A patent/EP1579109A1/fr not_active Withdrawn
- 2003-12-16 US US10/541,311 patent/US7210288B2/en not_active Expired - Fee Related
- 2003-12-16 WO PCT/EP2003/014313 patent/WO2004061278A1/fr not_active Application Discontinuation
-
2007
- 2007-03-23 US US11/690,214 patent/US7814747B2/en active Active
-
2010
- 2010-09-09 US US12/878,544 patent/US8297046B2/en not_active Expired - Lifetime
-
2012
- 2012-09-14 US US13/616,886 patent/US9057307B2/en not_active Expired - Lifetime
-
2015
- 2015-04-24 US US14/695,732 patent/US20150226100A1/en not_active Abandoned
Non-Patent Citations (1)
Title |
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See references of WO2004061278A1 * |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
EP1731727A1 (fr) * | 2004-03-24 | 2006-12-13 | Hitachi, Ltd. | Dispositif de clarification de gaz d'echappement derive de moteur a combustion interne, procede de clarification de gaz d'echappement, et agent de capture de constituant de soufre pour moteur a combustion interne |
EP1731727A4 (fr) * | 2004-03-24 | 2007-07-18 | Babcock Hitachi Kk | Dispositif de clarification de gaz d'echappement derive de moteur a combustion interne, procede de clarification de gaz d'echappement, et agent de capture de constituant de soufre pour moteur a combustion interne |
Also Published As
Publication number | Publication date |
---|---|
US20110005204A1 (en) | 2011-01-13 |
US7210288B2 (en) | 2007-05-01 |
US20130011313A1 (en) | 2013-01-10 |
US9057307B2 (en) | 2015-06-16 |
US7814747B2 (en) | 2010-10-19 |
US20060153761A1 (en) | 2006-07-13 |
US20150226100A1 (en) | 2015-08-13 |
JP2006512529A (ja) | 2006-04-13 |
US20070175208A1 (en) | 2007-08-02 |
US8297046B2 (en) | 2012-10-30 |
JP4541898B2 (ja) | 2010-09-08 |
DE10300298A1 (de) | 2004-07-15 |
WO2004061278A1 (fr) | 2004-07-22 |
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