WO2013005342A1 - Exhaust purification device for internal combustion engine - Google Patents
Exhaust purification device for internal combustion engine Download PDFInfo
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- WO2013005342A1 WO2013005342A1 PCT/JP2011/065648 JP2011065648W WO2013005342A1 WO 2013005342 A1 WO2013005342 A1 WO 2013005342A1 JP 2011065648 W JP2011065648 W JP 2011065648W WO 2013005342 A1 WO2013005342 A1 WO 2013005342A1
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- dpf
- ash
- regeneration
- atmosphere
- regeneration operation
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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
- B01D53/944—Simultaneously removing carbon monoxide, hydrocarbons or carbon making use of oxidation catalysts
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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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- 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
- F01N3/023—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
- F01N3/0232—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 removing incombustible material from a particle filter, e.g. ash
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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
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F02—COMBUSTION ENGINES; HOT-GAS OR COMBUSTION-PRODUCT ENGINE PLANTS
- F02D—CONTROLLING COMBUSTION ENGINES
- F02D41/00—Electrical control of supply of combustible mixture or its constituents
- F02D41/02—Circuit arrangements for generating control signals
- F02D41/021—Introducing corrections for particular conditions exterior to the engine
- F02D41/0235—Introducing corrections for particular conditions exterior to the engine in relation with the state of the exhaust gas treating apparatus
- F02D41/027—Introducing corrections for particular conditions exterior to the engine in relation with the state of the exhaust gas treating apparatus to purge or regenerate the exhaust gas treating apparatus
- F02D41/029—Introducing corrections for particular conditions exterior to the engine in relation with the state of the exhaust gas treating apparatus to purge or regenerate the exhaust gas treating apparatus the exhaust gas treating apparatus being a particulate filter
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/10—Noble metals or compounds thereof
- B01D2255/102—Platinum group metals
- B01D2255/1021—Platinum
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/10—Noble metals or compounds thereof
- B01D2255/102—Platinum group metals
- B01D2255/1023—Palladium
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/10—Noble metals or compounds thereof
- B01D2255/102—Platinum group metals
- B01D2255/1025—Rhodium
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/90—Physical characteristics of 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
- F01N2430/00—Influencing exhaust purification, e.g. starting of catalytic reaction, filter regeneration, or the like, by controlling engine operating characteristics
- F01N2430/06—Influencing exhaust purification, e.g. starting of catalytic reaction, filter regeneration, or the like, by controlling engine operating characteristics by varying fuel-air ratio, e.g. by enriching fuel-air mixture
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F02—COMBUSTION ENGINES; HOT-GAS OR COMBUSTION-PRODUCT ENGINE PLANTS
- F02D—CONTROLLING COMBUSTION ENGINES
- F02D41/00—Electrical control of supply of combustible mixture or its constituents
- F02D41/02—Circuit arrangements for generating control signals
- F02D41/021—Introducing corrections for particular conditions exterior to the engine
- F02D41/0235—Introducing corrections for particular conditions exterior to the engine in relation with the state of the exhaust gas treating apparatus
- F02D41/027—Introducing corrections for particular conditions exterior to the engine in relation with the state of the exhaust gas treating apparatus to purge or regenerate the exhaust gas treating apparatus
- F02D41/0285—Introducing corrections for particular conditions exterior to the engine in relation with the state of the exhaust gas treating apparatus to purge or regenerate the exhaust gas treating apparatus the exhaust gas treating apparatus being a SOx trap or adsorbent
Definitions
- the present invention relates to an exhaust purification device for an internal combustion engine.
- a diesel particulate filter (hereinafter referred to as “DPF”) is installed in the exhaust gas passage of the internal combustion engine, Generally, PM in exhaust gas is collected and removed.
- PM regeneration since the PM collected in the DPF gradually accumulates, regeneration (hereinafter referred to as “PM regeneration”) is performed periodically or by detecting a decrease in the performance of the DPF and burning and removing the PM collected in the DPF. ”).
- PM regeneration operation is usually performed by heating the DPF while supplying a reducing agent such as hydrocarbon (HC) to the DPF.
- a reducing agent such as hydrocarbon (HC)
- Ash is generated when the engine oil mixed in the cylinder of the engine burns, and the generated ash particles are covered with PM in the DPF.
- the ash particles covered with PM are exposed to high temperature conditions during the PM regeneration operation in the DPF, and the PM covering the ash particles is burned and removed.
- Ash deposition occurs because the ash particles are agglomerated and increased in size by further applying heat to the ash particles from which the PM has been burned and removed.
- the improvement to the conventional DPF and the improvement to the regeneration operation of the DPF are intended to improve the collection efficiency of the DPF and improve the performance of the PM regeneration operation, and not to the accumulation of ash.
- an invention disclosed in Patent Document 1 for example, there is an invention disclosed in Patent Document 1, and Patent Document 1 shows a configuration of a DPF capable of burning PM at a relatively low temperature. Yes.
- the structure of the DPF disclosed in Patent Document 1 is characterized in that, in the DPF and the exhaust gas purification method using the DPF, a catalyst made of a solid superacid having an active metal supported on the DPF is held on the filter surface. is there.
- Patent Document 1 reduces the combustion temperature of PM with a solid super strong acid carrying an active metal, and regenerates DPF at a lower temperature than before, preferably continuously, and CO, HC, NO, NO 2 can be removed at the same time.
- Patent Document 1 is intended to improve the performance of the PM regeneration operation, and does not correspond to the accumulation of ash. If the use of the DPF is continued, the PM regeneration operation is performed. However, this does not solve the problem that the pressure loss of the DPF gradually increases, and unless the PM regeneration temperature is gradually increased, sufficient regeneration cannot be performed and the fuel consumption deteriorates.
- Patent Document 2 which is selected from platinum, palladium and rhodium as a catalyst for a diesel engine exhaust gas purification device.
- SOF Solid Organic Fraction
- unburned hydrocarbons, etc. contained in particulate matter in diesel engine exhaust gas from a low temperature range.
- the invention of Patent Document 2 aims at an effect similar to the invention of Patent Document 1 and does not relate to DPF.
- JP 2006-289175 A Japanese Patent Laid-Open No. 10-033985
- the present invention provides an exhaust emission control device for an internal combustion engine that can suppress accumulation of ash on the DPF and suppress an increase in pressure loss, an increase in PM regeneration temperature, and a decrease in fuel consumption over a long period of time. It is aimed.
- the present invention provides a configuration in which the ash deposited on the DPF is discharged with a reduced particle size, and the DPF is regenerated (hereinafter referred to as “ash regeneration”). It is an object of the present invention to provide an epoch-making DPF that has an advantageous effect of suppressing an increase in temperature and a decrease in fuel consumption.
- the accumulated ash can be discharged with a reduced particle size.
- a DPF that is smaller than the conventional DPF can be used from the beginning of the installation of the DPF. Not only cost reduction, but also energy cost of PM regeneration operation can be reduced.
- the fact that a small DPF can be used means that the space for mounting the DPF on the vehicle can be reduced, and the weight of the vehicle on which the DPF is mounted can be reduced.
- the inventor of the present application studied the problem of ash accumulation inside the DPF, analyzed the cause of ash accumulation, and the main components of ash were calcium (Ca) contained in engine oil and SOx in exhaust gas. It was found that ash is ion-bonded, CaSO 4 is the main component, and Ca salt has a high melting point, so that in the exhaust gas, ash flows into the DPF as a solid and aggregates to increase the particle size.
- Ca calcium
- the inventors of the present application have confirmed by experiments that the size of ash is on the order of submicrons, and that the ash slips through the DPF when the ash size is reduced to the order of nanomicrons.
- Ca ions associated with stronger acid than SO 3 on the surface of the DPF is different from the stronger acid than SO 3 on the surface of the DPF, if a stronger acid is present in the atmosphere It was confirmed by an experiment that it binds to a stronger acid in the atmosphere, is released from the DPF, and passes through the DPF to be discharged.
- the particle size will be submicron.
- CaSO 4 deposited in the DPF turned into, in a reducing atmosphere becomes CaSO 3 SO 4 is reduced in CaSO 4
- Ca ions CaSO 3 is bonded with the acid on the surface of the DPF, on the surface of the DPF Disperse in atomic form.
- SO 4 is present in the atmosphere, the Ca on the surface of the DPF combines with the SO 4 in the atmosphere and becomes sub-nanometer-sized CaSO 4 and is released from the DPF.
- the exhaust gas atmosphere is a stoichiometric or rich atmosphere, it is the above-described reducing atmosphere, and when it is a lean atmosphere, the lean atmosphere contains SO 4 . Therefore, if control for making the atmosphere stoichiometric or rich and control for making the lean atmosphere next are performed on the above-mentioned DPF, ash Ca ions deposited on the DPF in the stoichiometric or rich atmosphere are converted to DPF. Then, in a lean atmosphere, Ca on the surface of the DPF is combined with SO 4 in the lean atmosphere and released from the DPF, and the fine particle size is reduced to a sub-nanometer size. CaSO 4 is converted to pass through the DPF and discharged.
- the first CaSO 4 having a large particle size of submicron and deposited on the DPF is finally released again from the DPF as CaSO 4.
- No. 4 is reduced in size to a sub-nanometer size and passes through the DPF and is discharged.
- PM accumulated in the DPF is burned and removed by performing the PM regeneration operation before performing the ash regeneration operation. Therefore, CaSO 4 having a large particle size that has been buried in PM is exposed to a reducing atmosphere, and the ash that has been reduced to CaSO 3 becomes solid acid on the surface of the DPF. The ash regeneration operation effectively proceeds.
- an exhaust purification device for an internal combustion engine in which a DPF is disposed in an exhaust system of the internal combustion engine, wherein the DPF is a DPF whose surface is coated with a solid acid,
- the acid strength is larger than the acid strength of SO 3 and smaller than the acid strength of SO 4
- an ash regeneration operation control that removes ash accumulated in the DPF.
- the control for increasing the temperature and the control of the air-fuel ratio of the atmosphere in the DPF, and the control of the air-fuel ratio of the atmosphere in the DPF is performed before the control for increasing the temperature of the DPF.
- an exhaust gas purification apparatus for an internal combustion engine which is controlled to change to an atmosphere and then to an air-fuel ratio lean atmosphere, and performs PM regeneration operation before performing ash regeneration operation.
- the PM regeneration operation is performed before the ash regeneration operation. Therefore, CaSO 4 having a large particle size that has been buried in PM is exposed to a reducing atmosphere, and the ash that has been reduced to CaSO 3 becomes solid acid on the surface of the DPF.
- the ash regeneration operation following the PM regeneration operation effectively proceeds.
- an exhaust gas purification apparatus for an internal combustion engine is provided in which ash is completely removed and an increase in pressure loss, an increase in PM regeneration temperature, and a decrease in fuel consumption can be suppressed over a long period of time.
- the ash regeneration operation proceeds effectively, the ash is completely removed in the ash regeneration operation, and the pressure loss increases, the PM regeneration temperature increases, and the fuel consumption decreases over a long period of time.
- This provides an effect of providing an exhaust gas purification device for an internal combustion engine that can suppress the above-described problem.
- FIG. 1 is a diagram illustrating contact of ash with a solid acid in an embodiment in which the present invention is applied to a DPF of the present invention.
- FIG. 2 is a diagram for explaining the presence state of ash before the present invention is carried out on the DPF of the present invention.
- FIG. 3 is a diagram illustrating contact of ash with a solid acid in another embodiment in which the present invention is applied to the DPF of the present invention.
- FIG. 4 is a diagram for explaining similarities and differences between a regeneration (hereinafter referred to as “S regeneration”) operation condition and an ash regeneration operation condition of a sulfur-poisoned NOx storage reduction catalyst (hereinafter referred to as “NSR”).
- S regeneration hereinafter referred to as “S regeneration”
- NSR sulfur-poisoned NOx storage reduction catalyst
- A is a figure explaining the atmosphere in S reproduction
- (b) is a figure
- FIG. 2 is a diagram for explaining the presence state of ash before the present invention is carried out on the DPF of the present invention.
- the ash is buried in the PM deposited in the DPF as shown in FIG. Therefore, even trying to ash reproduced in this state, in order to CaSO 4 deposited in the DPF with large grain size to the size of the sub-micron can not be in contact with a reducing atmosphere, SO 4 of CaSO 4 is reduced Not.
- the ash reduced to CaSO 3 cannot contact the solid acid on the surface of the DPF. Therefore, the ash cannot be decomposed as it is.
- FIG. 1 is a diagram illustrating contact of ash with a solid acid in an embodiment in which the present invention is applied to a DPF of the present invention.
- the state in which the solid acid is coated on the surface of the DPF will be described in detail.
- the carrier 61 is distributed on the DPF substrate 5, and the acid points 62 of the solid acid are scattered on the carrier 61.
- the ash Ca ions reduced to CaSO 3 in the reducing atmosphere are bonded to the acid sites 62 of the solid acid and dispersed atomically on the surface of the DPF.
- the CaSO 4 having a large particle size that was buried in the PM is exposed to a reducing atmosphere.
- the ash Ca ions reduced to CaSO 3 can bind to the acid sites 62 of the solid acid on the surface of the DPF. Therefore, the ash regeneration operation following the PM regeneration operation effectively proceeds.
- FIG. 4 illustrates, as an example, similarities and differences between the NSR S regeneration operation condition and the ash regeneration operation condition when the NSR and the DPF are separately installed and a DPR is provided downstream of the NSR.
- (A) is a figure explaining the atmosphere in S reproduction
- (b) is a figure explaining the atmosphere in ash reproduction
- the state of the NSR entrance is indicated by IN, and the state of the NSR exit is indicated by OUT. That is, OUT represents the state of the DPR entrance.
- Reference numeral 20 denotes a reducing agent, and (a) indicates that the reducing agent 20 is injected.
- the conditions for the S regeneration are that the temperature is 600 ° C. or higher, the air-fuel ratio is rich, and the presence of a reducing agent is essential.
- the control trigger is the S accumulation amount.
- the conditions for the ash regeneration are that the temperature is 600 ° C. or higher and that the atmosphere is a reducing atmosphere, and if it is an oxygen-free atmosphere, a reducing agent may be present but it is not necessary.
- the control trigger is the ash deposition amount.
- the PM regeneration condition requires that the temperature is 600 ° C. or higher, the air-fuel ratio is lean, and no reducing agent is required.
- the control trigger is the PM accumulation amount.
- FIG. FIG. 5 exemplifies the required timings for PM regeneration, ash regeneration, and S regeneration with respect to the travel distance.
- Circle marks indicate the necessary timings, which are implemented among the circle marks. Things are painted black.
- P is PM regeneration
- A is ash regeneration
- S is S regeneration.
- PM regeneration is first performed, and then S regeneration is performed.
- PM regeneration is first performed, and then ash regeneration is performed.
- all trigger timings of PM regeneration, ash regeneration, and S regeneration coincide with each other. In this case, PM regeneration is performed first, and then S regeneration is performed. The ash is removed from the DPF by the S regeneration operation without performing the ash regeneration control.
- FIG. 3 is a diagram illustrating contact of ash with a solid acid in another embodiment in which the present invention is applied to the DPF of the present invention. That is, in the present invention, when performing PM regeneration operation before performing ash regeneration operation, CaSO 4 having a large particle size that was buried in PM is exposed to a reducing atmosphere, Further, the ash reduced to CaSO 3 comes into contact with the acid sites 62 of the solid acid on the surface of the DPF, but as shown in FIG. 3, the ash is exposed to a reducing atmosphere, and the ash If it comes into contact with the acid point 62 of the solid acid, PM may remain without completely removing PM, and the ash regeneration operation following the PM regeneration operation effectively proceeds.
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Abstract
Description
本発明は、内燃機関の排気浄化装置に関する。 The present invention relates to an exhaust purification device for an internal combustion engine.
内燃機関の排気ガス中の粒子状物質(以下「PM」という)の粒子数を低減するためには、内燃機関の排気ガス通路にディーゼルパティキュレートフィルタ(以下「DPF」という)を設置して、排気中のPMを捕集、除去することが一般に行われている。 In order to reduce the number of particles of particulate matter (hereinafter referred to as “PM”) in the exhaust gas of the internal combustion engine, a diesel particulate filter (hereinafter referred to as “DPF”) is installed in the exhaust gas passage of the internal combustion engine, Generally, PM in exhaust gas is collected and removed.
この場合、DPF内に捕集されたPMは次第に堆積していくので、定期的に或いはDPFの性能低下を検知して、DPF内に捕集されたPMを燃焼除去する再生(以下「PM再生」という)運転を行う。 In this case, since the PM collected in the DPF gradually accumulates, regeneration (hereinafter referred to as “PM regeneration”) is performed periodically or by detecting a decrease in the performance of the DPF and burning and removing the PM collected in the DPF. ”).
PM再生運転は、通常、DPFに還元剤、例えばハイドロカーボン(HC)等、を供給しつつ、DPFを加熱することによって行われる。 PM regeneration operation is usually performed by heating the DPF while supplying a reducing agent such as hydrocarbon (HC) to the DPF.
DPFによって排気中のPMを捕集し、DPF内に捕集されたPMを燃焼除去するPM再生運転を行う構成に対しては、その性能向上やコスト低減のため、従来から様々な改良が提案されている。 Various improvements have been proposed to improve the performance and reduce the cost of the PM regeneration operation that collects PM in the exhaust gas using the DPF and burns and removes the PM collected in the DPF. Has been.
しかし、従来のDPFにおいては、DPFの使用を継続していると、PM再生運転を行っても、次第にDPFの圧力損失が増加し、また、PM再生温度を次第に増加させなければ十分な再生が行われなくなる、という問題があり、燃費が悪化する。この問題は、DPF内部にアッシュが堆積することが原因である。 However, in the conventional DPF, if the use of the DPF is continued, even if the PM regeneration operation is performed, the pressure loss of the DPF gradually increases, and if the PM regeneration temperature is not gradually increased, sufficient regeneration is achieved. There is a problem that it will not be performed, and fuel consumption deteriorates. This problem is caused by the accumulation of ash inside the DPF.
アッシュは、エンジンのシリンダー内部に混入したエンジンオイルが燃焼することにより生成し、生成したアッシュ粒子は、DPF内でPMに覆われる。PMに覆われたアッシュ粒子は、DPF内でPM再生運転時の高温条件に晒され、アッシュ粒子を覆っていたPMが燃焼除去される。アッシュの堆積は、このPMが燃焼除去されたアッシュ粒子に、更に熱が加わることによって、アッシュ粒子が凝集し、大粒径化するために発生するものである。 Ash is generated when the engine oil mixed in the cylinder of the engine burns, and the generated ash particles are covered with PM in the DPF. The ash particles covered with PM are exposed to high temperature conditions during the PM regeneration operation in the DPF, and the PM covering the ash particles is burned and removed. Ash deposition occurs because the ash particles are agglomerated and increased in size by further applying heat to the ash particles from which the PM has been burned and removed.
しかし、このようなアッシュの堆積に対しては、今まで有効な解決手段がなく、DPFにアッシュが堆積することによる影響を極力小さくするために、例えば、あらかじめ大容量のDPFを設置しておくという対策がとられていた。 However, there is no effective solution to the accumulation of ash so far, and in order to minimize the influence of the accumulation of ash on the DPF, for example, a large-capacity DPF is installed in advance. Measures were taken.
すなわち、従来のDPFに対する改良や、DPFの再生運転に対する改良は、DPFの捕集効率の改善や、PM再生運転の性能向上を目的とするものであり、アッシュの堆積に対するものではない。PM再生運転の性能向上を目的とするものとしては、例えば特許文献1に示された発明があり、特許文献1には、比較的低温でPMを燃焼させることができるDPFの構成が示されている。 That is, the improvement to the conventional DPF and the improvement to the regeneration operation of the DPF are intended to improve the collection efficiency of the DPF and improve the performance of the PM regeneration operation, and not to the accumulation of ash. As an object for improving the performance of the PM regeneration operation, for example, there is an invention disclosed in Patent Document 1, and Patent Document 1 shows a configuration of a DPF capable of burning PM at a relatively low temperature. Yes.
特許文献1に示されたDPFの構成は、DPF及びこれを用いた排ガス浄化方法において、DPFに活性金属を担持した固体超強酸からなる触媒を、フィルタ表面に保持することを特徴とするものである。 The structure of the DPF disclosed in Patent Document 1 is characterized in that, in the DPF and the exhaust gas purification method using the DPF, a catalyst made of a solid superacid having an active metal supported on the DPF is held on the filter surface. is there.
すなわち、特許文献1の発明は、活性金属を担持した固体超強酸により、PMの燃焼温度を低下させ、従来よりも低温でDPFを、できれば連続的に再生すると共に、CO、HC、NO、NO2をも同時に除去することができるというものである。 That is, the invention of Patent Document 1 reduces the combustion temperature of PM with a solid super strong acid carrying an active metal, and regenerates DPF at a lower temperature than before, preferably continuously, and CO, HC, NO, NO 2 can be removed at the same time.
したがって、特許文献1の発明は、PM再生運転の性能向上を目的としたものであり、アッシュの堆積に対応するものではなく、DPFの使用を継続していると、PM再生運転を行っても、次第にDPFの圧力損失が増加し、また、PM再生温度を次第に増加させなければ十分な再生が行われなくなり、燃費が悪化する、という問題を解決するものではない。 Therefore, the invention of Patent Document 1 is intended to improve the performance of the PM regeneration operation, and does not correspond to the accumulation of ash. If the use of the DPF is continued, the PM regeneration operation is performed. However, this does not solve the problem that the pressure loss of the DPF gradually increases, and unless the PM regeneration temperature is gradually increased, sufficient regeneration cannot be performed and the fuel consumption deteriorates.
また、特許文献1の発明に類似する触媒構成を開示したものとして、特許文献2の発明があるが、特許文献2には、ディーゼルエンジン排ガス浄化装置用触媒として、白金、パラジウム及びロジウムから選ばれる少なくとも1種の貴金属と、固体の超強酸とを有する触媒を利用すると、ディーゼルエンジン排ガス中の微粒子物質に含まれるSOF(Soluble Organic Fraction)や未燃焼炭化水素などを低温域から浄化することができ、高温域においても二酸化硫黄の酸化抑制効果を示すと記載されており、特許文献2の発明は、特許文献1の発明と類似する効果を狙ったものであり、また、DPFに関するものではない。したがって、DPFへのアッシュの堆積に対応するものではなく、DPFの使用を継続していると、PM再生運転を行っても、次第にDPFの圧力損失が増加し、また、PM再生温度を次第に増加させなければ十分な再生が行われなくなり、燃費が悪化する、という問題を解決するものではない。 Further, as a disclosure of a catalyst structure similar to the invention of Patent Document 1, there is an invention of Patent Document 2, which is selected from platinum, palladium and rhodium as a catalyst for a diesel engine exhaust gas purification device. By using a catalyst having at least one kind of noble metal and a solid super strong acid, it is possible to purify SOF (Soluable Organic Fraction), unburned hydrocarbons, etc. contained in particulate matter in diesel engine exhaust gas from a low temperature range. Further, it is described that the effect of suppressing oxidation of sulfur dioxide is exhibited even in a high temperature range, and the invention of Patent Document 2 aims at an effect similar to the invention of Patent Document 1 and does not relate to DPF. Therefore, it does not correspond to the accumulation of ash on the DPF. If the use of the DPF is continued, the pressure loss of the DPF gradually increases and the PM regeneration temperature gradually increases even if the PM regeneration operation is performed. If this is not done, it will not solve the problem that sufficient regeneration will not be performed and fuel consumption will deteriorate.
本発明は、DPFへのアッシュの堆積を抑制し、長期にわたって圧損の増加や、PM再生温度の増加、また、燃費の低下を抑制することができる、内燃機関の排気浄化装置を提供することを目的としている。 The present invention provides an exhaust emission control device for an internal combustion engine that can suppress accumulation of ash on the DPF and suppress an increase in pressure loss, an increase in PM regeneration temperature, and a decrease in fuel consumption over a long period of time. It is aimed.
すなわち、本発明は、DPFに堆積したアッシュを細粒径化して排出し、DPFを再生(以下「アッシュ再生」という)する構成を提供し、この構成により、長期にわたって圧損の増加や、PM再生温度の増加、また、燃費の低下を抑制することができる、という有利な効果を奏する、画期的なDPFを提供するものである。 That is, the present invention provides a configuration in which the ash deposited on the DPF is discharged with a reduced particle size, and the DPF is regenerated (hereinafter referred to as “ash regeneration”). It is an object of the present invention to provide an epoch-making DPF that has an advantageous effect of suppressing an increase in temperature and a decrease in fuel consumption.
本発明によれば、堆積したアッシュを細粒径化させて排出することができるので、更に付随する効果として、DPFの設置当初から従来よりも小型のDPFを使用することができ、DPFの製造コストの低減のみならず、PM再生運転のエネルギーコストを低減することもできる。また、小型のDPFを使用することができるということは、DPFの車両への搭載スペースを低減することができ、当該DPFを搭載した車両の重量を低減することができるということである。 According to the present invention, the accumulated ash can be discharged with a reduced particle size. As a further effect, a DPF that is smaller than the conventional DPF can be used from the beginning of the installation of the DPF. Not only cost reduction, but also energy cost of PM regeneration operation can be reduced. In addition, the fact that a small DPF can be used means that the space for mounting the DPF on the vehicle can be reduced, and the weight of the vehicle on which the DPF is mounted can be reduced.
本願の発明者は、DPF内部へのアッシュの堆積の問題を研究し、アッシュの堆積原因を分析して、アッシュの主成分が、エンジンオイル中に含まれるカルシウム(Ca)と排気中のSOxとがイオン結合した、CaSO4が主体であり、Ca塩は融点が高いため、排気中ではアッシュが固体としてDPFに流入し、凝集して、大粒径化するという知見を得た。 The inventor of the present application studied the problem of ash accumulation inside the DPF, analyzed the cause of ash accumulation, and the main components of ash were calcium (Ca) contained in engine oil and SOx in exhaust gas. It was found that ash is ion-bonded, CaSO 4 is the main component, and Ca salt has a high melting point, so that in the exhaust gas, ash flows into the DPF as a solid and aggregates to increase the particle size.
更に、本願の発明者は、アッシュの大きさはサブミクロンのオーダーであり、これをナノミクロンのオーダーまで細粒径化すると、アッシュがDPFをすり抜けることを、実験により確認した。 Furthermore, the inventors of the present application have confirmed by experiments that the size of ash is on the order of submicrons, and that the ash slips through the DPF when the ash size is reduced to the order of nanomicrons.
更に、本願の発明者は、サブミクロンの大きさに大粒径化したCaSO4を、還元雰囲気におくと、CaSO4のSO4が還元されてSO3となり、Caとの結合が弱まること、及び、このときDPFの表面上にSO3よりも強い酸が存在すると、CaSO3のCaとSO3との結合が切断され、CaイオンがDPFの表面上のSO3よりも強い酸の上に原子状に分散して結合するということを、実験により確認した。 Furthermore, the inventors of the present application, a CaSO 4 that large grain size to the size of submicron, when placed in a reducing atmosphere, it becomes SO 3 SO 4 of CaSO 4 is reduced, the bond between Ca weakened, At this time, if an acid stronger than SO 3 is present on the surface of the DPF, the bond between Ca and SO 3 in the CaSO 3 is cleaved, and the Ca ions are stronger than the SO 3 on the surface of the DPF. It was confirmed by experiments that the atoms were dispersed and bonded in an atomic form.
更に、本願の発明者は、DPFの表面上のSO3よりも強い酸と結合したCaイオンは、DPFの表面上のSO3よりも強い酸と比べて、更に強い酸が雰囲気中に存在すると、雰囲気中の更に強い酸と結合して、DPFから放出され、DPFをすり抜けて排出されるというということを、実験により確認した。 Furthermore, the inventors of the present application, Ca ions associated with stronger acid than SO 3 on the surface of the DPF is different from the stronger acid than SO 3 on the surface of the DPF, if a stronger acid is present in the atmosphere It was confirmed by an experiment that it binds to a stronger acid in the atmosphere, is released from the DPF, and passes through the DPF to be discharged.
以上を整理すると、DPFの表面上のSO3よりも強い酸として、この酸の酸強度を、SO3よりも強くSO4よりも弱い酸強度とすれば、サブミクロンの大きさに大粒径化してDPF内に堆積したCaSO4は、還元雰囲気において、CaSO4のSO4が還元されてCaSO3となり、CaSO3のCaイオンが、DPFの表面上の酸と結合し、DPFの表面上に原子状に分散する。次に、雰囲気中にSO4を存在させれば、DPFの表面上のCaは、雰囲気中のSO4と結合して、サブナノメートルの大きさのCaSO4となってDPFから放出される。 To summarize the above, if the acid strength of this acid is stronger than SO 3 on the surface of the DPF and the acid strength of this acid is stronger than SO 3 and weaker than SO 4 , the particle size will be submicron. CaSO 4 deposited in the DPF turned into, in a reducing atmosphere, becomes CaSO 3 SO 4 is reduced in CaSO 4, Ca ions CaSO 3 is bonded with the acid on the surface of the DPF, on the surface of the DPF Disperse in atomic form. Next, if SO 4 is present in the atmosphere, the Ca on the surface of the DPF combines with the SO 4 in the atmosphere and becomes sub-nanometer-sized CaSO 4 and is released from the DPF.
排気ガスの雰囲気が、ストイキ又はリッチ雰囲気である場合には、上述の還元雰囲気であり、リーン雰囲気である場合には、リーン雰囲気にはSO4が含まれている。そこで、上述のDPFに対して、雰囲気をストイキ又はリッチ雰囲気にする制御と、次にリーン雰囲気にする制御と、を行えば、ストイキ又はリッチ雰囲気において、DPFに堆積したアッシュのCaイオンが、DPFの表面上に原子状に分散し、次に次にリーン雰囲気において、DPFの表面上のCaが、リーン雰囲気中のSO4と結合してDPFから放出され、サブナノメートルの大きさに細粒径化したCaSO4となってDPFをすり抜け、排出される。 When the exhaust gas atmosphere is a stoichiometric or rich atmosphere, it is the above-described reducing atmosphere, and when it is a lean atmosphere, the lean atmosphere contains SO 4 . Therefore, if control for making the atmosphere stoichiometric or rich and control for making the lean atmosphere next are performed on the above-mentioned DPF, ash Ca ions deposited on the DPF in the stoichiometric or rich atmosphere are converted to DPF. Then, in a lean atmosphere, Ca on the surface of the DPF is combined with SO 4 in the lean atmosphere and released from the DPF, and the fine particle size is reduced to a sub-nanometer size. CaSO 4 is converted to pass through the DPF and discharged.
すなわち、以上の過程では、最初の、サブミクロンの大きさに大粒径化してDPFに堆積したCaSO4が、最終的に、再びCaSO4となってDPFから放出されるが、放出されるCaSO4は、サブナノメートルの大きさに細粒径化されており、DPFをすり抜けて排出される。 That is, in the above process, the first CaSO 4 having a large particle size of submicron and deposited on the DPF is finally released again from the DPF as CaSO 4. No. 4 is reduced in size to a sub-nanometer size and passes through the DPF and is discharged.
ところで、以上のアッシュ再生運転を行う場合、通常、アッシュは、DPF内に堆積したPMの中に埋没した状態にある。したがって、この状態でアッシュ再生を行おうとしても、サブミクロンの大きさに大粒径化してDPF内に堆積したCaSO4が還元雰囲気と接触することができないために、CaSO4のSO4が還元されない。或いは、還元されてCaSO3となったアッシュも、DPFの表面上の固体酸に接触することができない。したがって、アッシュを分解することができないという問題がある。 By the way, when performing the above ash reproduction | regeneration operation | movement, the ash is normally in the state buried in PM deposited in DPF. Therefore, even trying to ash reproduced in this state, in order to CaSO 4 deposited in the DPF with large grain size to the size of the sub-micron can not be in contact with a reducing atmosphere, SO 4 of CaSO 4 is reduced Not. Alternatively, the ash reduced to CaSO 3 cannot contact the solid acid on the surface of the DPF. Therefore, there is a problem that the ash cannot be decomposed.
本発明は、この問題を解決するために、アッシュ再生運転を行うに先立ち、PM再生運転を行うことによって、DPF内に堆積したPMを燃焼させ、除去するものである。したがって、PMの中に埋没した状態にあった大粒径化したCaSO4が、還元雰囲気に晒されるようになり、また、還元されてCaSO3となったアッシュが、DPFの表面上の固体酸に接触するようになり、アッシュ再生運転が、効果的に進行する。 In order to solve this problem, in the present invention, PM accumulated in the DPF is burned and removed by performing the PM regeneration operation before performing the ash regeneration operation. Therefore, CaSO 4 having a large particle size that has been buried in PM is exposed to a reducing atmosphere, and the ash that has been reduced to CaSO 3 becomes solid acid on the surface of the DPF. The ash regeneration operation effectively proceeds.
請求項1に記載の発明によれば、内燃機関の排気系にDPFを配置した、内燃機関の排気浄化装置であって、DPFが、表面上に固体酸をコーティングしたDPFであり、固体酸の酸強度が、SO3の酸強度よりも大きくSO4の酸強度よりも小さく、更に、DPF内に堆積したアッシュを除去する、アッシュ再生運転の制御を備え、アッシュ再生運転の制御が、DPFの温度を上昇させる制御と、DPF内の雰囲気の空燃比の制御と、を備え、DPF内の雰囲気の空燃比の制御が、DPFの温度を上昇させる制御の間に、先にストイキ又は空燃比リッチ雰囲気とし、次に空燃比リーン雰囲気に変化させる制御であり、アッシュ再生運転を行う前に、PM再生運転を行うことを特徴とする、内燃機関の排気浄化装置が提供される。 According to the first aspect of the present invention, there is provided an exhaust purification device for an internal combustion engine in which a DPF is disposed in an exhaust system of the internal combustion engine, wherein the DPF is a DPF whose surface is coated with a solid acid, The acid strength is larger than the acid strength of SO 3 and smaller than the acid strength of SO 4 , and further includes an ash regeneration operation control that removes ash accumulated in the DPF. The control for increasing the temperature and the control of the air-fuel ratio of the atmosphere in the DPF, and the control of the air-fuel ratio of the atmosphere in the DPF is performed before the control for increasing the temperature of the DPF. Provided is an exhaust gas purification apparatus for an internal combustion engine, which is controlled to change to an atmosphere and then to an air-fuel ratio lean atmosphere, and performs PM regeneration operation before performing ash regeneration operation.
すなわち、請求項1の発明では、アッシュ再生運転を行う前に、PM再生運転を行う。したがって、PMの中に埋没した状態にあった大粒径化したCaSO4が、還元雰囲気に晒されるようになり、また、還元されてCaSO3となったアッシュが、DPFの表面上の固体酸に接触するようになり、PM再生運転に続くアッシュ再生運転が、効果的に進行する。この結果、アッシュが完全に除去され、長期にわたって圧損の増加や、PM再生温度の増加、また、燃費の低下を抑制することができる、内燃機関の排気浄化装置が提供される。 That is, according to the first aspect of the present invention, the PM regeneration operation is performed before the ash regeneration operation. Therefore, CaSO 4 having a large particle size that has been buried in PM is exposed to a reducing atmosphere, and the ash that has been reduced to CaSO 3 becomes solid acid on the surface of the DPF. The ash regeneration operation following the PM regeneration operation effectively proceeds. As a result, an exhaust gas purification apparatus for an internal combustion engine is provided in which ash is completely removed and an increase in pressure loss, an increase in PM regeneration temperature, and a decrease in fuel consumption can be suppressed over a long period of time.
請求項1に記載の発明によれば、アッシュ再生運転が効果的に進行し、アッシュ再生運転においてアッシュが完全に除去され、長期にわたって圧損の増加や、PM再生温度の増加、また、燃費の低下を抑制することができる、内燃機関の排気浄化装置を提供するという効果を奏する。 According to the first aspect of the present invention, the ash regeneration operation proceeds effectively, the ash is completely removed in the ash regeneration operation, and the pressure loss increases, the PM regeneration temperature increases, and the fuel consumption decreases over a long period of time. This provides an effect of providing an exhaust gas purification device for an internal combustion engine that can suppress the above-described problem.
図1は、本発明を、本発明のDPFに適用した実施形態における、アッシュの、固体酸への接触を説明する図である。
図2は、本発明を、本発明のDPFに対して実施する前の、アッシュの存在状態を説明する図である。
図3は、本発明を、本発明のDPFに対して適用した、別の実施形態における、アッシュの、固体酸への接触を説明する図である。
図4は、硫黄被毒したNOx吸蔵還元触媒(以下「NSR」という)の再生(以下「S再生」という)運転条件とアッシュ再生運転条件との類似点と相違点とを説明する図であり、(a)は、S再生における雰囲気を説明する図であり、(b)は、アッシュ再生における雰囲気を説明する図である。
図5は、本発明のアッシュ再生の、PM再生及びS再生とのタイミングを説明する図である。
FIG. 1 is a diagram illustrating contact of ash with a solid acid in an embodiment in which the present invention is applied to a DPF of the present invention.
FIG. 2 is a diagram for explaining the presence state of ash before the present invention is carried out on the DPF of the present invention.
FIG. 3 is a diagram illustrating contact of ash with a solid acid in another embodiment in which the present invention is applied to the DPF of the present invention.
FIG. 4 is a diagram for explaining similarities and differences between a regeneration (hereinafter referred to as “S regeneration”) operation condition and an ash regeneration operation condition of a sulfur-poisoned NOx storage reduction catalyst (hereinafter referred to as “NSR”). (A) is a figure explaining the atmosphere in S reproduction | regeneration, (b) is a figure explaining the atmosphere in ash reproduction | regeneration.
FIG. 5 is a diagram for explaining the timing of PM regeneration and S regeneration of ash regeneration according to the present invention.
以下、添付図面を用いて本発明の実施形態について説明する。なお、複数の添付図面において、同一又は相当する部材には、同一の符号を付している。 Hereinafter, embodiments of the present invention will be described with reference to the accompanying drawings. In the plurality of accompanying drawings, the same or corresponding members are denoted by the same reference numerals.
図2は、本発明を、本発明のDPFに対して実施する前の、アッシュの存在状態を説明する図である。通常、アッシュは、図2のように、DPF内に堆積したPMの中に埋没した状態にある。したがって、この状態でアッシュ再生を行おうとしても、サブミクロンの大きさに大粒径化してDPF内に堆積したCaSO4が還元雰囲気と接触することができないために、CaSO4のSO4が還元されない。或いは、還元されてCaSO3となったアッシュも、DPFの表面上の固体酸に接触することができない。したがって、このままでは、アッシュを分解することができない。 FIG. 2 is a diagram for explaining the presence state of ash before the present invention is carried out on the DPF of the present invention. Usually, the ash is buried in the PM deposited in the DPF as shown in FIG. Therefore, even trying to ash reproduced in this state, in order to CaSO 4 deposited in the DPF with large grain size to the size of the sub-micron can not be in contact with a reducing atmosphere, SO 4 of CaSO 4 is reduced Not. Alternatively, the ash reduced to CaSO 3 cannot contact the solid acid on the surface of the DPF. Therefore, the ash cannot be decomposed as it is.
図1は、本発明を、本発明のDPFに適用した実施形態における、アッシュの、固体酸への接触を説明する図である。DPFの表面上に固体酸をコーティングした状態を、詳細に説明すると、DPF基材5の上に担体61が分布し、担体61の上に、固体酸の酸点62が点在している。還元雰囲気中で還元されてCaSO3となったアッシュのCaイオンは、固体酸の酸点62と結合して、DPFの表面上に原子状に分散する。
FIG. 1 is a diagram illustrating contact of ash with a solid acid in an embodiment in which the present invention is applied to a DPF of the present invention. The state in which the solid acid is coated on the surface of the DPF will be described in detail. The
したがって、本発明において、アッシュ再生運転を行う前にPM再生運転を行うと、図1に示すように、PMの中に埋没した状態にあった大粒径化したCaSO4が、還元雰囲気に晒されるようになり、また、還元されてCaSO3となったアッシュのCaイオンが、DPFの表面上の固体酸の酸点62と結合することができる。したがって、PM再生運転に続くアッシュ再生運転が、効果的に進行する。
Therefore, in the present invention, when the PM regeneration operation is performed before the ash regeneration operation, as shown in FIG. 1, the CaSO 4 having a large particle size that was buried in the PM is exposed to a reducing atmosphere. In addition, the ash Ca ions reduced to CaSO 3 can bind to the
図4は、例として、NSRとDPFとを分離して設置し、NSRの下流にDPRを備えた場合において、NSRのS再生運転条件とアッシュ再生運転条件との類似点と相違点とを説明する図であり、(a)は、S再生における雰囲気を説明する図であり、(b)は、アッシュ再生における雰囲気を説明する図である。NSRの入口の状態をINで示し、NSRの出口の状態をOUTで表す。すなわち、OUTは、DPRの入口の状態を表している。符号20は還元剤であり、(a)では還元剤20を注入することを示している。
FIG. 4 illustrates, as an example, similarities and differences between the NSR S regeneration operation condition and the ash regeneration operation condition when the NSR and the DPF are separately installed and a DPR is provided downstream of the NSR. (A) is a figure explaining the atmosphere in S reproduction | regeneration, (b) is a figure explaining the atmosphere in ash reproduction | regeneration. The state of the NSR entrance is indicated by IN, and the state of the NSR exit is indicated by OUT. That is, OUT represents the state of the DPR entrance.
すなわち、S再生の条件は、温度は600℃以上であり、かつ、空燃比がリッチであることが必要であり、還元剤の存在が必須である。制御トリガーは、S堆積量である。 That is, the conditions for the S regeneration are that the temperature is 600 ° C. or higher, the air-fuel ratio is rich, and the presence of a reducing agent is essential. The control trigger is the S accumulation amount.
一方、アッシュ再生の条件は、温度は600℃以上であり、かつ、還元雰囲気であることが必要であり、無酸素雰囲気であれば、還元剤はあってもよいが必要ではない。制御トリガーは、アッシュ堆積量である。 On the other hand, the conditions for the ash regeneration are that the temperature is 600 ° C. or higher and that the atmosphere is a reducing atmosphere, and if it is an oxygen-free atmosphere, a reducing agent may be present but it is not necessary. The control trigger is the ash deposition amount.
したがって、アッシュ再生の条件とS再生の条件とを比較すると、アッシュ再生とS再生のトリガータイミングが一致する場合には、S再生を実施して、アッシュ再生を省略することができる。 Therefore, when the ash playback condition and the S playback condition are compared, if the ash playback and the S playback trigger timing match, the S playback can be performed and the ash playback can be omitted.
なお、PM再生条件は、温度は600℃以上であり、かつ、空燃比がリーンであることが必要であり、還元剤は必要ない。制御トリガーは、PM堆積量である。 Note that the PM regeneration condition requires that the temperature is 600 ° C. or higher, the air-fuel ratio is lean, and no reducing agent is required. The control trigger is the PM accumulation amount.
これらの制御タイミングの関係の一例を、図5に示す。図5は、PM再生と、アッシュ再生と、S再生と、のそれぞれの必要なタイミングを、走行距離に対して例示したものであり、丸印が必要なタイミングを表し、丸印のうち実施するものを黒く塗りつぶしてある。PはPM再生、Aはアッシュ再生、SはS再生である。図5のIで示したタイミングでは、まずPM再生を行い、次にS再生を行う。図5のIIで示したタイミングでは、まずPM再生を行い、次にアッシュ再生を行う。図5のIIIで示したタイミングでは、PM再生と、アッシュ再生と、S再生と、の全てのトリガータイミングが一致しているが、この場合は、まずPM再生を行い、次にS再生を行えばよく、アッシュ再生制御は行わなくても、アッシュは、S再生運転によってDPFから除去される。 An example of the relationship between these control timings is shown in FIG. FIG. 5 exemplifies the required timings for PM regeneration, ash regeneration, and S regeneration with respect to the travel distance. Circle marks indicate the necessary timings, which are implemented among the circle marks. Things are painted black. P is PM regeneration, A is ash regeneration, and S is S regeneration. At the timing indicated by I in FIG. 5, PM regeneration is first performed, and then S regeneration is performed. At the timing indicated by II in FIG. 5, PM regeneration is first performed, and then ash regeneration is performed. At the timing indicated by III in FIG. 5, all trigger timings of PM regeneration, ash regeneration, and S regeneration coincide with each other. In this case, PM regeneration is performed first, and then S regeneration is performed. The ash is removed from the DPF by the S regeneration operation without performing the ash regeneration control.
図3は、本発明を、本発明のDPFに対して適用した別の実施形態における、アッシュの、固体酸への接触を説明する図である。すなわち、本発明において、アッシュ再生運転を行う前に、PM再生運転を行った場合、PMの中に埋没した状態にあった大粒径化したCaSO4が、還元雰囲気に晒されるようになり、また、還元されてCaSO3となったアッシュが、DPFの表面上の固体酸の酸点62に接触するようになるが、図3に示すように、アッシュが還元雰囲気に晒され、また、アッシュが固体酸の酸点62と接触すれば、PMを完全に除去しない状態で、PMが残存していてもよく、PM再生運転に続くアッシュ再生運転が、効果的に進行する。
FIG. 3 is a diagram illustrating contact of ash with a solid acid in another embodiment in which the present invention is applied to the DPF of the present invention. That is, in the present invention, when performing PM regeneration operation before performing ash regeneration operation, CaSO 4 having a large particle size that was buried in PM is exposed to a reducing atmosphere, Further, the ash reduced to CaSO 3 comes into contact with the
1 内燃機関
2 DPF
3 アッシュ
4 細粒径化粒子
5 DPF基材
6 固体酸
10 PM
20 還元剤
61 担体
62 固体酸点
A アッシュ再生
P PM再生
S S再生
1 Internal combustion engine 2 DPF
3 Ash 4
20 Reducing
Claims (1)
前記DPFが、表面上に固体酸をコーティングしたDPFであり、
前記固体酸の酸強度が、SO3の酸強度よりも大きくSO4の酸強度よりも小さく、
更に、前記DPF内に堆積したアッシュを除去する、アッシュ再生運転の制御を備え、
前記アッシュ再生運転の制御が、
DPFの温度を上昇させる制御と、
DPF内の雰囲気の空燃比の制御と、を備え、
前記DPF内の雰囲気の空燃比の制御が、前記DPFの温度を上昇させる制御の間に、先にストイキ又は空燃比リッチ雰囲気とし、次に空燃比リーン雰囲気に変化させる制御であり、
前記アッシュ再生運転を行う前に、PM再生運転を行うことを特徴とする、
内燃機関の排気浄化装置。 An exhaust purification device for an internal combustion engine in which a DPF is disposed in an exhaust system of the internal combustion engine,
The DPF is a DPF having a surface coated with a solid acid,
The acid strength of the solid acid is greater than the acid strength of SO 3 and less than the acid strength of SO 4 ;
Furthermore, the ash regeneration operation control for removing the ash accumulated in the DPF is provided,
The control of the ash regeneration operation is
Control to increase the temperature of the DPF;
An air-fuel ratio control of the atmosphere in the DPF,
The control of the air-fuel ratio of the atmosphere in the DPF is a control for changing the atmosphere to the stoichiometric or air-fuel ratio rich atmosphere first and then changing to the air-fuel ratio lean atmosphere during the control to increase the temperature of the DPF.
Before performing the ash regeneration operation, PM regeneration operation is performed,
An exhaust purification device for an internal combustion engine.
Priority Applications (26)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| PCT/JP2011/065648 WO2013005342A1 (en) | 2011-07-01 | 2011-07-01 | Exhaust purification device for internal combustion engine |
| CN201280031473.7A CN103619441B (en) | 2011-07-01 | 2012-06-29 | Exhaust purification system for internal combustion engine |
| CN201280032271.4A CN103635245B (en) | 2011-07-01 | 2012-06-29 | Particulate filter |
| PCT/JP2012/067406 WO2013005851A2 (en) | 2011-07-01 | 2012-06-29 | Exhaust Purification System for Internal Combustion Engine |
| US14/126,947 US9057298B2 (en) | 2011-07-01 | 2012-06-29 | Exhaust purification system for internal combustion engine |
| JP2013555657A JP2014520227A (en) | 2011-07-01 | 2012-06-29 | Exhaust gas purification device for internal combustion engine |
| US14/126,904 US9011569B2 (en) | 2011-07-01 | 2012-06-29 | Particulate filter |
| PCT/JP2012/067404 WO2013005849A1 (en) | 2011-07-01 | 2012-06-29 | Exhaust Purification System for Internal Combustion Engine |
| JP2013555681A JP5626487B2 (en) | 2011-07-01 | 2012-06-29 | Particulate filter |
| JP2014514345A JP2014520229A (en) | 2011-07-01 | 2012-06-29 | Exhaust gas purification device for internal combustion engine |
| EP12741115.5A EP2726176A2 (en) | 2011-07-01 | 2012-06-29 | Exhaust purification system for internal combustion engine |
| EP12738239.8A EP2726172B1 (en) | 2011-07-01 | 2012-06-29 | Particulate filter |
| US14/127,355 US9080480B2 (en) | 2011-07-01 | 2012-06-29 | Exhaust purification system for internal combustion engine |
| PCT/JP2012/067405 WO2013005850A2 (en) | 2011-07-01 | 2012-06-29 | Exhaust Purification System for Internal Combustion Engine |
| PCT/JP2012/067407 WO2013005852A1 (en) | 2011-07-01 | 2012-06-29 | Particulate Filter |
| CN201280031454.4A CN103619439B (en) | 2011-07-01 | 2012-06-29 | For the emission control system of internal combustion engine |
| JP2013555656A JP5655961B2 (en) | 2011-07-01 | 2012-06-29 | Exhaust gas purification device for internal combustion engine |
| JP2013535609A JP5494893B2 (en) | 2011-07-01 | 2012-06-29 | How to remove ash from particulate filters |
| CN201280031461.4A CN103619440B (en) | 2011-07-01 | 2012-06-29 | Exhaust purification system for internal combustion engine |
| US14/110,811 US8778053B2 (en) | 2011-07-01 | 2012-06-29 | Method of removing ash from particulate filter |
| EP12738240.6A EP2726173B1 (en) | 2011-07-01 | 2012-06-29 | Method of removing ash from particulate filter |
| CN201280030742.8A CN103619438B (en) | 2011-07-01 | 2012-06-29 | Method of removing ash from particulate filter |
| PCT/JP2012/067408 WO2013005853A2 (en) | 2011-07-01 | 2012-06-29 | Method of Removing Ash from Particulate Filter |
| US14/126,997 US9057299B2 (en) | 2011-07-01 | 2012-06-29 | Exhaust purification system for internal combustion engine |
| EP12741116.3A EP2726177B1 (en) | 2011-07-01 | 2012-06-29 | Exhaust purification system for internal combustion engine |
| EP12741114.8A EP2726175B1 (en) | 2011-07-01 | 2012-06-29 | Exhaust Purification System for Internal Combustion Engine |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
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| PCT/JP2011/065648 WO2013005342A1 (en) | 2011-07-01 | 2011-07-01 | Exhaust purification device for internal combustion engine |
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Citations (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH1054268A (en) * | 1996-08-08 | 1998-02-24 | Toyota Motor Corp | Diesel engine exhaust purification system |
| JP2004513771A (en) * | 2001-05-16 | 2004-05-13 | ケイエイチ ケミカルズ カンパニー、リミテッド | Catalyst for purification of diesel engine exhaust gas |
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| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH1054268A (en) * | 1996-08-08 | 1998-02-24 | Toyota Motor Corp | Diesel engine exhaust purification system |
| JP2004513771A (en) * | 2001-05-16 | 2004-05-13 | ケイエイチ ケミカルズ カンパニー、リミテッド | Catalyst for purification of diesel engine exhaust gas |
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