WO2008066197A1 - Appareil de purification de gaz d'échappement - Google Patents
Appareil de purification de gaz d'échappement Download PDFInfo
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- WO2008066197A1 WO2008066197A1 PCT/JP2007/073322 JP2007073322W WO2008066197A1 WO 2008066197 A1 WO2008066197 A1 WO 2008066197A1 JP 2007073322 W JP2007073322 W JP 2007073322W WO 2008066197 A1 WO2008066197 A1 WO 2008066197A1
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- exhaust gas
- storage
- catalyst
- occlusion
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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
- F01N3/0814—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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- 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
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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
- B01D53/9413—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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- 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
- B01D53/9481—Catalyst preceded by an adsorption device without catalytic function for temporary storage of contaminants, e.g. during cold start
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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
- B01D53/9481—Catalyst preceded by an adsorption device without catalytic function for temporary storage of contaminants, e.g. during cold start
- B01D53/949—Catalyst preceded by an adsorption device without catalytic function for temporary storage of contaminants, e.g. during cold start for storing sulfur oxides
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J23/00—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
- B01J23/38—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals
- B01J23/54—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of noble metals combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
- B01J23/56—Platinum group metals
- B01J23/58—Platinum group metals with alkali- or alkaline earth metals
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J37/00—Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
- B01J37/02—Impregnation, coating or precipitation
- B01J37/024—Multiple impregnation or coating
- B01J37/0242—Coating followed by impregnation
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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
- F01N3/10—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
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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
- F01N3/10—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
- F01N3/24—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
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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
- B01D2255/20—Metals or compounds thereof
- B01D2255/204—Alkaline earth metals
- B01D2255/2042—Barium
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/20—Metals or compounds thereof
- B01D2255/204—Alkaline earth metals
- B01D2255/2047—Magnesium
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/20—Metals or compounds thereof
- B01D2255/206—Rare earth metals
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/20—Metals or compounds thereof
- B01D2255/207—Transition metals
- B01D2255/20707—Titanium
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/20—Metals or compounds thereof
- B01D2255/207—Transition metals
- B01D2255/20715—Zirconium
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/20—Metals or compounds thereof
- B01D2255/209—Other metals
- B01D2255/2092—Aluminium
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2255/00—Catalysts
- B01D2255/50—Zeolites
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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
- B01D2255/92—Dimensions
- B01D2255/9207—Specific surface
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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
- F01N2570/04—Sulfur or sulfur oxides
Definitions
- the present invention relates to an exhaust gas purification device that purifies exhaust gas discharged from an internal combustion engine such as an automobile. About.
- a NO storage reduction catalyst supporting a NO storage material selected from alkali metals, alkaline earth metals and rare earth elements together with noble metals is known. ing.
- this NO storage reduction catalyst By using this NO storage reduction catalyst and controlling the composition of the gas mixture so that it becomes a steep to rich atmosphere in the middle of a lean atmosphere, the oxidation of HC and CO and the reduction of NO can proceed efficiently. High purification performance can be obtained.
- a general NO storage reduction catalyst has a problem that the NO storage amount in a low temperature region is insufficient.
- the exhaust gas contains SO generated by combustion of sulfur (S) contained in the fuel, which is oxidized by the catalytic metal in an oxygen-excess atmosphere to become so. And that is
- the water vapor contained in the exhaust gas easily turns into sulfurous acid or sulfuric acid, which reacts with the NO storage material to produce sulfite and sulfate, so that the NO storage material is poisoned and deteriorated. It was.
- porous carriers such as alumina have the property of being able to occlude SO, so there is a problem that the above-described sulfur poisoning is promoted.
- Japanese Patent Application Laid-Open No. 2002-0111347 describes an SO storage material containing a composite oxide composed of a rare earth element and an aluminum oxide, and this SO storage material is disposed on the upstream side of the NO storage reduction catalyst. It is described to do.
- JP-A-2001-113172 proposes an exhaust gas purification catalyst in which a barrier layer for suppressing the diffusion of SO is provided on the upper layer of the NO storage reduction catalyst layer.
- the noria layer is made of an inorganic oxide carrying a noble metal and a transition metal.
- the noble metal oxidizes S in a lean atmosphere in the lean layer, and the generated SO is firmly captured by the transition metal, so that SO diffuses into the lower NO storage reduction catalyst layer. Is suppressed.
- the noble metal of the barrier layer reduces SO in a stoichiometric to rich atmosphere, the bond between the transition metal and SO is broken, and SO is released from the barrier layer. Therefore, the SO storage capacity of the barrier layer is not saturated.
- the sulfur oxide cover of the downstream NO storage reduction catalyst is provided. You can power the poison.
- Occlusion of SO also means that NO is occluded, so there may be an advantage that the amount of NO occlusion increases in the low temperature range.
- Patent Document 1 JP 2001-113172 A
- Patent Document 2 Japanese Patent Laid-Open No. 2002-0111347
- the present invention has been made in view of the above circumstances, and increases the SO storage amount of the storage catalyst arranged upstream of the ⁇ storage reduction catalyst and also increases the NO storage amount in the low temperature range. This is a problem to be solved.
- an exhaust gas purification comprising: an occlusion catalyst that occludes NO and SO; an NO occlusion reduction catalyst that is disposed on the exhaust gas downstream side of the occlusion catalyst; A device,
- the storage catalyst is the storage catalyst
- a carrier substrate having a specific surface area of 30 m 2 / g or more;
- the coating powder consists of a carrier powder composed of at least one kind and a precious metal that occludes NO and SO.
- the carrier base material also contains the occlusion material!
- the storage catalyst is A10, CeO, ZrO, TiO, and
- a support substrate made of at least one selected from 2 3 2 2 2 oleite and having a specific surface area of 30 m 2 / g or more is used. Since this carrier base material has a large specific surface area, the amount of the occlusion material that occludes NO and SO increases remarkably, and the SO occlusion amount and the NO occlusion amount in a low temperature range increase remarkably. In addition, since the carrier base material made of such a material does not easily react with the storage material that stores NO and SO, there is no problem that the strength of the carrier base material decreases.
- FIG. 1 is an explanatory view showing an exhaust gas purifying apparatus according to an embodiment of the present invention.
- FIG. 2 is a bar graph showing NO storage amount.
- FIG. 3 is a bar graph showing the amount of stored sulfur. Explanation of symbols
- the exhaust gas purifying apparatus of the present invention comprises an occlusion catalyst that occludes NO and SO, and an NO occlusion reduction catalyst arranged on the exhaust gas downstream side of the occlusion catalyst.
- the NO storage reduction catalyst is selected from a porous oxide support, a noble metal supported on the porous oxide support, an alkali metal, an alkaline earth metal and a rare earth element, and a NO supported on the porous oxide support.
- An occlusion material and a force-configured conventional one can be used.
- porous oxide carrier used for the NO storage reduction catalyst alumina, silica, silica, alumina, titania, zeolite and the like can be used. One of these can be used! /, And multiple types can be mixed and used. Of these, highly active ⁇ -alumina is preferably used.
- Examples of the noble metal used in the NO storage reduction catalyst include Pt, Rh, Pd, Ir and the like.
- the amount of noble metal supported is preferably 0 • l to 10 g per liter of the catalyst. If it is less than this, the purification activity is insufficient, and if it is supported more than this, the effect is saturated and the cost becomes high.
- the amount of the NO storage material supported on the NO storage reduction catalyst is preferably in the range of 0.01 to 2 moles per liter of the catalyst. If the loading amount is less than this range, the NO storage capacity decreases, so the NO purification capacity decreases, and if it exceeds this range, the precious metal is covered with the NO storage material and the activity decreases.
- Examples of the alkali metal include lithium, sodium, potassium, and cesium.
- Examples of alkaline earth metals include group 2A elements of barium, beryllium, magnesium, calcium, and strontium.
- Examples of rare earth elements include scandium, yttrium, lanthanum, cerium, praseodymium, neodymium, dysprosium, ytterbium, and the like.
- the storage catalyst that characterizes the present invention includes a carrier substrate, a coat layer formed on the surface of the carrier substrate, and force.
- the carrier substrate is selected from A10, CeO, ZrO, TiO and zeolite. And a specific surface area of 30 m 2 / g or more. If the specific surface area is less than 30 m 2 / g, the amount of occlusion of the occlusion material becomes insufficient, the amount of SO occlusion decreases, and the amount of NO occlusion in the low temperature region also decreases, which is not preferable. It is particularly desirable that the specific surface area of the carrier substrate is 50 m 2 / g or more! /.
- A10 or ZrO is particularly preferable as the material for the carrier substrate.
- A10 is preferred because it has a remarkably high specific surface area.
- ZrO has a high basicity, so it absorbs SO.
- Zeolite is also a preferred material for reasons described below.
- the coating layer is at least one selected from A10, CeO, ZrO, TiO and zeolite
- the carrier powder is formed by supporting a storage material for storing NO and SO and a noble metal.
- A10 or ZrO is particularly preferred for the same reason as above.
- the amount of the coat layer formed is preferably 100 g or more, preferably 150 g or more, per liter of the storage catalyst. If the amount of coating layer formed is small, the storage amount of NO and SO decreases.
- the occlusion material that occludes NO and SO is desirably at least one selected from alkali metals and alkaline earth metals. Of these, Mg or Ba having high basicity and excellent stability is preferred.
- an alkali metal oxide or an alkaline earth metal oxide has a high ability to occlude NO and SO, but on the other hand, it is difficult to release the occluded NO and SO. For this reason, the temperature at which NO and SO are released becomes high, and when used in the low to medium temperature range, the storage amount of NO and SO becomes saturated, and it becomes difficult to store more NO and SO. There is. If a carrier material such as zeolitic and zeolitic is used as an occlusion material in which alkali metal or alkaline earth metal is ion-exchange-supported, the temperature at which the occluded NO and SO are released is lowered, and the exhaust gas temperature in the low to medium temperature range is reduced. Even so, it is possible to repeatedly store and release NO and SO.
- ZrO added with an alkali metal or alkaline earth metal is different from other occlusion materials.
- Oxidizing activity is expressed by ⁇ , Fe ⁇ , etc., and NO or SO in exhaust gas is oxidized.
- alkali metal or alkaline earth metal is not clear, but alkali metal or alkaline earth metal is dissolved in the ZrO lattice to dissolve the alkali metal
- Lukari earth metal and ZrO are compounded, which modifies the ZrO surface and newly absorbs it.
- the storage material has different temperatures for storing NO and SO depending on its type. Therefore, it is also preferable to use multiple types of occlusion materials with different temperatures that indicate the maximum occlusion amount! For example, if a low-temperature type occlusion material that efficiently stores NO and SO at a low temperature is arranged on the most upstream side, and an intermediate temperature type occlusion material that efficiently occludes NO and SO is arranged on the downstream side, NO. Since SO and SO are gradually stored from the upstream side where the storage temperature is low, NO and SO can be stored in a wide temperature range from a low temperature range to a high temperature range. Further, since the exhaust gas is heated by the heat generated by the storage of NO and SO, there is an effect that the downstream storage material or the NO storage reduction catalyst is activated early.
- a zeolite carrying a rare earth element such as Ce a zeolite carrying an alkali metal, an alkaline earth metal or a transition metal
- a zeolite carrying an alkali metal, an alkaline earth metal or a transition metal examples include those carrying a noble metal on ZrO and those carrying a transition metal such as Co 0.
- Examples are those carrying a metal and an alkali metal or alkaline earth metal.
- Zeolite has pores comparable to the size of the molecule, also called a molecular sieve, and is used not only as an occlusion material but also as a catalyst in many reactions. It also contains a cation to neutralize the negative charge of the main component, A10,
- At least one metal selected from alkali metals and alkaline earth metals can be ion-exchanged and supported in an extremely highly dispersed state.
- the ion exchange-supported metal element is supported on the zeolite with extremely high dispersion. NO and SO oxidation activity at low temperatures where activity is extremely high
- zeolite such as ferrierite, ZSM-5, mordenite, and Y-type zeolite can be used.
- ZSM-5 and mordenite are excellent in ion exchange capacity, so it is desirable to select and use them.
- a NO storage / reduction catalyst is arranged downstream of the storage material in which at least one metal element selected from alkali metals, alkaline earth metals, and rare earth elements is ion-exchange-supported in zeolite, NO can be used even at low temperatures. Is already NO, so even if there is NO that could not be occluded by the occlusion material, it will be occluded by the downstream NO occlusion reduction catalyst. As a result, the NO storage capacity at low temperatures is improved and the NO purification capacity is improved.
- the coat layer further carries a noble metal.
- the noble metal include Pt, Rh, Pd, Ir and the like. Among them, Pt having a high oxidation activity is particularly preferable.
- the amount of noble metal supported is preferably 0.5 to 2.0 g per liter of the storage catalyst. If it is less than this, the storage performance of NO and SO will be insufficient, and if it is supported more than this, the effect will be saturated and it will be expensive.
- the shape of the support substrate in the occlusion catalyst may be a pellet shape, a foam shape, a straight-ported single honeycomb shape, a wall flow honeycomb shape, or the like.
- the coating layer is formed on the surface of the carrier substrate that comes into contact with the exhaust gas.
- the support base material of the occlusion catalyst in, for example, a straight flow type honeycomb shape, a powder made of at least one selected from A10, CeO, ZrO, TiO and zeolite is used.
- the slurry can be made into a highly viscous slurry together with the inner and fired after extrusion. And to form a coating layer on the surface of the carrier substrate, A10, CeO, ZrO, T Comparison of powder with at least one selected from iO and zeolite together with binder
- the slurry is made into a slurry with low physical viscosity, sucked and then dried and fired after being put into the carrier substrate, and then impregnated with a solution in which the noble metal compound is dissolved and a solution in which the compound containing the occlusion material element is dissolved in order, followed by drying and firing. do it.
- a solution in which a compound containing an occlusion material element such as nitrate is dissolved is used. Since we want to increase the amount of occlusion material as much as possible, it is desirable that the concentration of the compound containing the occlusion material element in the solution be a saturation concentration! /. In addition, since it is desirable to carry a large amount in one treatment, it is particularly desirable that the water absorption amount in a state where the coat layer is formed is at least 150 g per liter of the catalyst, preferably 200 g or more.
- the storage base material of the storage catalyst also contains the storage material described above. This further increases the storage amount of N 0 and SO.
- the above-mentioned loading method includes a certain amount of occlusion material on the carrier substrate, it is desirable to mix occlusion material powders such as MgO and BaO in the slurry used for the production of the carrier substrate. In this case, if the mixing amount of the occlusion material powder is increased, the strength of the carrier substrate may be reduced, and the specific surface area may be less than 30 m 2 / g.
- the NO purification reaction in the NO storage reduction catalyst includes a first step in which NO in the exhaust gas is oxidized to NO in a lean atmosphere, a second step in which NO is stored in the NO storage element, and a stoichiometric reaction. It is known to comprise a third step of reducing NO released from NO storage elements on the catalyst in a rich atmosphere. Therefore, in order for the NO purification reaction to proceed smoothly, each of these steps must proceed smoothly.
- the exhaust gas purifying apparatus of the present invention has a configuration in which the storage catalyst is arranged upstream of the exhaust gas upstream of the NO storage reduction catalyst.
- the storage material contained in the storage catalyst is easy to store NO. Stores NO even at low temperatures. Therefore, in the low temperature range, exhaust gas containing almost no NO is supplied to the NO storage reduction catalyst, so almost no NO is emitted.
- the exhaust gas temperature rises the stored NO is desorbed from the storage material and flows into the NO storage reduction catalyst. Since the NO storage reduction catalyst is already at the activation temperature, the reaction in the first step is smooth. NO is efficiently reduced and purified. With such a mechanism, according to the exhaust gas purification apparatus of the present invention, it is possible to secure a high NO purification rate from low temperature to high temperature with the force S.
- FIG. 1 shows an exhaust gas purification apparatus of this example.
- a catalyst converter 2 is disposed in the exhaust gas passage of the engine 1.
- the storage catalyst 3 is disposed on the upstream side
- the NO storage reduction catalyst 4 is disposed on the downstream side of the storage catalyst 3.
- the storage catalyst 3 and the NO storage reduction catalyst 4 are both honeycomb catalysts having a straight flow structure.
- the storage catalyst 3 includes a straight flow type honeycomb substrate 30 formed by ⁇ -A10 force, and
- the honeycomb substrate 30 has a volume of 2 L, 600 cells / in 2 , and a specific surface area of 100 m 2 / g.
- the coat layer 31 is formed in an amount of 150 g per liter of the honeycomb substrate 30.
- the coat layer 31 is formed by wash-coating a slurry mainly containing ⁇ - ⁇ 10 powder.
- the honeycomb substrate 30 carries 2.0 g of Pt per liter of the honeycomb substrate 30 and 2.5 mol of MgO per liter of the honeycomb substrate 30.
- wash coating, drying and firing were performed to form an alumina coating layer.
- the alumina coat layer was impregnated with a predetermined amount of Pt chemical solution having a predetermined concentration, and baked to carry Pt.
- a maximum amount of magnesium nitrate aqueous solution saturated aqueous solution
- the amount of MgO supported was 100 g per liter of the honeycomb substrate 30.
- the NO storage reduction catalyst 4 is composed of a straight flow type honeycomb substrate 40 formed of cordierite, a coat layer 41 formed on the cell wall surface, and force.
- the honeycomb substrate 40 has a volume of 3 L, 400 cells / in 2 , and a specific surface area of 100 m 2 / g.
- Coat layer 41 is a honeycomb 150 g is formed per liter of the base material 40.
- the coat layer 41 is composed of ⁇ -A1 0 powder and Pt, K, and Ba supported on the ⁇ -A1 0 powder.
- the 1 liter of honeycomb substrate 40 carries 2 g of Pt, 0.1 mol of K, and 0.1 mol of Ba.
- ⁇ - A1 0 powder instead of ⁇ - A1 0 powder: MgO powder
- the honeycomb substrate has the same shape as that of Example 1, and its specific surface area is 100 m 2 / g.
- an alumina coat layer similar to that in Example 1 was formed.
- the alumina coat layer was formed in an amount of 150 g per liter of the two-cam base material.
- Pt and MgO were supported on the alumina coat layer in the same manner as in Example 1 except that the concentration of the magnesium nitrate aqueous solution was different.
- the amounts of Pt and MgO supported were the same as in Example 1.
- 1.0 mol / L was supported on the honeycomb substrate and 1.5 mol / L was supported on the coat layer.
- the obtained storage catalyst was arranged on the upstream side, and the NO storage reduction catalyst 4 similar to that of Example 1 was arranged on the downstream side, whereby the exhaust gas purification apparatus of Example 2 was obtained.
- honeycomb base material of the storage catalyst 3 it is formed from cordierite powder instead of ⁇ - ⁇ 10 powder.
- the honeycomb substrate has the same shape as in Example 1, and the specific surface area is 0.1 to lm 2 / g. Using this honeycomb substrate, the same alumina coat layer as in Example 1 was formed. The alumina coat layer was formed in an amount of 150 g per liter of the honeycomb substrate.
- the supported amount of Pt was the same as in Example 1, but the supported amount of MgO was 1.0 mol / L, which was less than in Example 1. It was.
- the obtained storage catalyst was arranged on the upstream side, and the NO storage reduction catalyst 4 similar to that in Example 1 was arranged on the downstream side, whereby the exhaust gas purification apparatus of Comparative Example 1 was obtained.
- the honeycomb base material of the storage catalyst 3 is formed of cordierite powder instead of ⁇ - ⁇ 10 powder. What was made was used.
- the honeycomb substrate has the same shape as in Example 1, and the specific surface area is 0.1 to lm 2 / g.
- the same alumina coat layer as in Example 1 was formed.
- the alumina coat layer was formed in an amount of 150 g per liter of the honeycomb substrate.
- Pt and MgO were supported on the alumina coat layer in the same manner as in Example 1
- the supported amount of Pt was the same as in Example 1, but the supported amount of MgO was 1.25 mol / L, which was less than Example 1. It was.
- Fig. 3 shows the results of measuring the amount of sulfur stored when passing 90g of model gas as sulfur per liter of honeycomb substrate.
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- Biomedical Technology (AREA)
- Analytical Chemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Organic Chemistry (AREA)
- General Engineering & Computer Science (AREA)
- Mechanical Engineering (AREA)
- Toxicology (AREA)
- Catalysts (AREA)
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
- Exhaust Gas After Treatment (AREA)
Description
Claims
Priority Applications (5)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
BRPI0720791-3A BRPI0720791B1 (pt) | 2006-12-01 | 2007-12-03 | Aparelho de conversão de gás de escapamento |
EP07832942A EP2103341A4 (en) | 2006-12-01 | 2007-12-03 | APPARATUS FOR PURIFYING EXHAUST GAS |
CN2007800444496A CN101547734B (zh) | 2006-12-01 | 2007-12-03 | 排气净化装置 |
US12/516,813 US8128881B2 (en) | 2006-12-01 | 2007-12-03 | Exhaust-gas converting apparatus |
KR1020097010187A KR101159901B1 (ko) | 2006-12-01 | 2007-12-03 | 배기 가스 정화 장치 |
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2006325756A JP4327837B2 (ja) | 2006-12-01 | 2006-12-01 | 排ガス浄化装置 |
JP2006-325756 | 2006-12-01 |
Publications (1)
Publication Number | Publication Date |
---|---|
WO2008066197A1 true WO2008066197A1 (fr) | 2008-06-05 |
Family
ID=39467978
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
PCT/JP2007/073322 WO2008066197A1 (fr) | 2006-12-01 | 2007-12-03 | Appareil de purification de gaz d'échappement |
Country Status (8)
Country | Link |
---|---|
US (1) | US8128881B2 (ja) |
EP (1) | EP2103341A4 (ja) |
JP (1) | JP4327837B2 (ja) |
KR (1) | KR101159901B1 (ja) |
CN (1) | CN101547734B (ja) |
BR (1) | BRPI0720791B1 (ja) |
RU (1) | RU2408415C1 (ja) |
WO (1) | WO2008066197A1 (ja) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2016178299A1 (ja) * | 2015-05-07 | 2016-11-10 | 株式会社デンソー | 内燃機関の排気浄化装置 |
Families Citing this family (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
EP2236194A1 (en) * | 2009-03-31 | 2010-10-06 | Ibiden Co., Ltd. | Honeycomb structure |
KR101159756B1 (ko) * | 2010-05-18 | 2012-06-25 | 한국기계연구원 | 금속폼 필터를 구비한 질소산화물 흡장촉매장치 |
JP5168411B2 (ja) * | 2010-12-06 | 2013-03-21 | トヨタ自動車株式会社 | 内燃機関の排気浄化装置 |
KR101629910B1 (ko) * | 2014-09-24 | 2016-06-14 | 주식회사 태강 | 폐석탄재를 이용한 복합 탈취제 제조방법 |
JP6278008B2 (ja) * | 2015-07-17 | 2018-02-14 | トヨタ自動車株式会社 | 排ガス浄化触媒 |
JP2018171599A (ja) * | 2017-03-31 | 2018-11-08 | トヨタ自動車株式会社 | 排ガス浄化触媒 |
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JP2001113172A (ja) | 1999-10-15 | 2001-04-24 | Toyota Motor Corp | 排気ガス浄化用触媒 |
JP2001116172A (ja) | 1999-10-15 | 2001-04-27 | Takada Seisakusho:Kk | 組立て式管体 |
JP2002011347A (ja) | 2000-06-28 | 2002-01-15 | Toyota Central Res & Dev Lab Inc | SOx吸収材及びそれを用いた排ガス浄化用触媒と排ガス浄化方法 |
JP2002095967A (ja) * | 2000-09-25 | 2002-04-02 | Toyota Motor Corp | 排ガス浄化用触媒 |
JP2004230241A (ja) * | 2003-01-29 | 2004-08-19 | Nissan Motor Co Ltd | 排気ガス浄化触媒及びその製造方法 |
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JPS57117326A (en) * | 1981-01-12 | 1982-07-21 | Toyota Motor Corp | Filter for exhaust gas of internal-combustion engine |
RU2029107C1 (ru) | 1991-02-19 | 1995-02-20 | Республиканский инженерно-технический центр порошковой металлургии | Каталитический нейтрализатор отработавших газов двигателя внутреннего сгорания |
EP0685258A4 (en) | 1993-12-21 | 1996-05-15 | Toray Industries | MATERIAL WITH SELECTIVE ADSORPTION PROPERTIES FOR INORGANIC MATERIALS AND THEIR PRODUCTION METHOD. |
JPH0889803A (ja) | 1994-09-28 | 1996-04-09 | Isuzu Motors Ltd | 窒素酸化物接触還元用触媒 |
JPH08103651A (ja) | 1994-10-05 | 1996-04-23 | Mitsubishi Heavy Ind Ltd | 低濃度窒素酸化物用吸着材 |
JP3636384B2 (ja) | 1994-12-12 | 2005-04-06 | 川崎重工業株式会社 | 自動車塗装システム |
US6471924B1 (en) * | 1995-07-12 | 2002-10-29 | Engelhard Corporation | Method and apparatus for NOx abatement in lean gaseous streams |
DE19714536A1 (de) | 1997-04-09 | 1998-10-15 | Degussa | Autoabgaskatalysator |
EP0899002A2 (en) | 1997-08-26 | 1999-03-03 | General Motors Corporation | Promoted three-way catalyst and process for lean NOx reduction |
DE19847008A1 (de) * | 1998-10-13 | 2000-04-20 | Degussa | Stickoxid-Speicherkatalysator |
JP2003521363A (ja) | 1998-11-13 | 2003-07-15 | エンゲルハード・コーポレーシヨン | 排気ガス放出を減少させる触媒および方法 |
US20020048542A1 (en) * | 1999-04-02 | 2002-04-25 | Michel Deeba | Catalytic trap and methods of making and using the same |
EP1319436B1 (en) | 2000-09-08 | 2009-04-15 | Ngk Insulators, Ltd. | Method for producing catalyst body and carrier having alumina carried thereon |
JP2002113077A (ja) | 2000-10-06 | 2002-04-16 | Shimakawa Seisakusho:Kk | 脱臭装置および脱臭方法 |
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JP4495574B2 (ja) | 2004-11-22 | 2010-07-07 | 株式会社日立国際電気 | 放送システムにおける放送素材のプレビュー方法 |
-
2006
- 2006-12-01 JP JP2006325756A patent/JP4327837B2/ja not_active Expired - Fee Related
-
2007
- 2007-12-03 WO PCT/JP2007/073322 patent/WO2008066197A1/ja active Application Filing
- 2007-12-03 US US12/516,813 patent/US8128881B2/en not_active Expired - Fee Related
- 2007-12-03 BR BRPI0720791-3A patent/BRPI0720791B1/pt not_active IP Right Cessation
- 2007-12-03 EP EP07832942A patent/EP2103341A4/en not_active Withdrawn
- 2007-12-03 RU RU2009120456/05A patent/RU2408415C1/ru not_active IP Right Cessation
- 2007-12-03 CN CN2007800444496A patent/CN101547734B/zh not_active Expired - Fee Related
- 2007-12-03 KR KR1020097010187A patent/KR101159901B1/ko active IP Right Grant
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JP2001113172A (ja) | 1999-10-15 | 2001-04-24 | Toyota Motor Corp | 排気ガス浄化用触媒 |
JP2001116172A (ja) | 1999-10-15 | 2001-04-27 | Takada Seisakusho:Kk | 組立て式管体 |
JP2002011347A (ja) | 2000-06-28 | 2002-01-15 | Toyota Central Res & Dev Lab Inc | SOx吸収材及びそれを用いた排ガス浄化用触媒と排ガス浄化方法 |
JP2002095967A (ja) * | 2000-09-25 | 2002-04-02 | Toyota Motor Corp | 排ガス浄化用触媒 |
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Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2016178299A1 (ja) * | 2015-05-07 | 2016-11-10 | 株式会社デンソー | 内燃機関の排気浄化装置 |
JP2016211410A (ja) * | 2015-05-07 | 2016-12-15 | 株式会社デンソー | 内燃機関の排気浄化装置 |
Also Published As
Publication number | Publication date |
---|---|
KR101159901B1 (ko) | 2012-06-25 |
JP4327837B2 (ja) | 2009-09-09 |
US20100034712A1 (en) | 2010-02-11 |
US8128881B2 (en) | 2012-03-06 |
CN101547734B (zh) | 2012-09-05 |
EP2103341A1 (en) | 2009-09-23 |
BRPI0720791B1 (pt) | 2018-02-06 |
BRPI0720791A2 (pt) | 2014-03-11 |
CN101547734A (zh) | 2009-09-30 |
KR20090075728A (ko) | 2009-07-08 |
JP2008136941A (ja) | 2008-06-19 |
RU2408415C1 (ru) | 2011-01-10 |
EP2103341A4 (en) | 2011-06-15 |
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