CN106661984B - Exhaust system with modified poor NOX trap - Google Patents

Exhaust system with modified poor NOX trap Download PDF

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Publication number
CN106661984B
CN106661984B CN201580042915.1A CN201580042915A CN106661984B CN 106661984 B CN106661984 B CN 106661984B CN 201580042915 A CN201580042915 A CN 201580042915A CN 106661984 B CN106661984 B CN 106661984B
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metal
exhaust system
zeolite
modification
trap
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CN106661984A (en
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D·斯瓦洛
S·里德
P·菲利普斯
J·维利
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Johnson Matthey PLC
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Johnson Matthey PLC
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Priority claimed from PCT/IB2015/056016 external-priority patent/WO2016024193A1/en
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Abstract

It discloses a kind of for handling the exhaust system of engine exhaust gas.The system includes modified poor NOxTrap (LNT), urea injection system and ammonia-selective catalytic reduction catalysts.The LNT of the modification includes first layer and the second layer.First layer includes NOxAbsorbent component and one or more platinums group metal.The second layer includes diesel oxidation catalyst area and NO zoneofoxidation.The diesel oxidation catalyst area includes platinum group metal, zeolite and optional alkaline-earth metal.The NO zoneofoxidation includes platinum group metal and carrier.The LNT of the modification is being below about 200 DEG C of temperature storage NOxIt is discharged with the temperature at greater than about 200 DEG C.Also disclose the method for the LNT and the LNT using the modification of the modification.

Description

With modified poor NOxThe exhaust system of trap
Invention field
The present invention relates to a kind of exhaust systems for handling engine exhaust gas, and the method for processing engine exhaust gas.
Background of invention
Internal combustion engine generates the exhaust gas containing multiple pollutant, including nitrogen oxides (" NOx"), carbon monoxide and unburned Hydrocarbon, this is the theme of government regulation.Emission control system is widely used in reducing amount of these pollutant emissions into atmosphere, Once and typically their operation temperatures (typically 200 DEG C and higher) for having reached them, then realize very high efficiency. But these systems are relatively inefficient when being lower than their operation temperature (" cold start-up " phase).
For example, application is applied to meet the selective catalytic reduction (SCR) for being currently based on urea of Euro 6b discharge standard It is required that adding that can measure urea and being used to convert NOxBefore, the temperature at urea metering point of addition is greater than about 180℃.The NO lower than 180 DEG C is difficult to realize using current systemxConversion, and following Europe and Code of Federal Regulations will be emphasized Low temperature NOxStorage and conversion.This is realized by heat protocol at present, but this is with CO2The ill-effect of discharge.
Due to even tightened up countries and regions regulation reduces can be from diesel engine or the pollutant of gasoline exhaust Amount, so reduce the cold start-up phase during emission just becoming a significant challenge.Therefore, lasting research and development reduce cold start-up The NO discharged in conditioning processxHorizontal method.
For example, PCT international application WO2008/047170 discloses a kind of system, wherein from the NO of lean exhaust gasxLow In 200 DEG C of temperature adsorption, then it is being higher than 200 DEG C of thermal desorptions.It is said that NOxAdsorbent is by palladium and cerium oxide or contains cerium It is formed with the mixed oxide or composite oxides of other at least one transition metal.
U.S.Application Publication 2011/0005200 teaches a kind of catalyst system, by by ammonia-selective catalysis also Original (" NH3- SCR ") catalyst preparation object is placed in poor NOxTrap downstream, to remove deammoniation simultaneously and improve net NOxConversion ratio.It is said that NH3SCR catalyst is adsorbed on poor NOxThe ammonia generated in rich pulse process in trap.The ammonia of storage then with the poor NO in upstreamxTrap discharge NOxReaction, this improves NOxConversion ratio, while consuming the ammonia of storage.
PCT international application WO2004/076829 discloses a kind of waste gas cleaning system, and it includes be arranged in SCR catalyst The NO of upstreamxStore catalyst.The NOxStoring catalyst includes at least one alkali metal, alkaline-earth metal or rare earth metal, is used At least one platinum group metal (Pt, Pd, Rh or Ir) coats or activates.It is said that a kind of particularly preferred NOxStore catalyst packet Oxidation-containing cerium is used platinum and is coated as the other platinum of the oxidation catalyst on the carrier based on aluminium oxide.EP1027919 Disclose a kind of NOxSorbent material, it includes porous carrier materials for example aluminium oxide, zeolite, zirconium oxide, titanium dioxide and/ Or lanthana, and the noble metal (Pt, Pd and/or Rh) of at least 0.1 weight %.Example is the platinum loaded on alumina.
Using any automotive system and method, need to obtain further improvement in exhaust treatment system, especially In cold start conditions.It has been found that a kind of system, the NO during the cold start-up phase can be reducedxDischarge, while keeping good Good CO oxidation activity and show the resistance to inactivation due to caused by sulphation.
Summary of the invention
The present invention is a kind of exhaust system for handling engine exhaust gas.The system includes modified poor NOxTrap (LNT), urine Plain injected system and ammonia-selective catalytic reduction (NH3- SCR) catalyst.The LNT of the modification includes first layer and the second layer.The One layer includes NOxAbsorbent component and one or more platinums group metal.The second layer includes that diesel oxidation catalyst area and NO are aoxidized Area.The diesel oxidation catalyst area includes platinum group metal, zeolite and optional alkaline-earth metal.The NO zoneofoxidation includes platinum family gold Category and carrier.The LNT of the modification is being below about 200 DEG C of temperature storage NOx, discharged in greater than about 200 DEG C of temperature.The present invention It further include the method for the LNT and the LNT using the modification of the modification.
Detailed description of the invention
Fig. 1 shows the accumulation NO from the Engine Block Test for the LNT for using the modificationx
Fig. 2 shows the NO of the modification of LNT2/NOxConcentration ratio, the LNT include diesel oxidation catalyst area and are including NOx NO zoneofoxidation on the first layer of adsorbent.
Specific embodiment
The present invention is a kind of exhaust system for handling engine exhaust gas.The system includes modified poor NOxTrap (LNT).It is poor NOxTrap is well known in the art.Poor NOxTrap is typically designed to adsorb NO under poor exhaust conditionsx, discharged under the conditions of richness The NO of absorptionx, and the NO of reduction releasexTo form N2
LNT typically comprises NOxStorage component, oxidation component and reduction components.The NOxStorage component preferably comprises alkaline earth Metal (such as barium, calcium, strontium and magnesium), alkali metal (such as potassium, sodium, lithium and caesium), rare earth metal (such as lanthanum, yttrium, praseodymium and neodymium) or A combination thereof.The metal typically exists in the form of an oxide.Typically, oxidative function is played comprising platinum, is played comprising rhodium Restoring function.These components are included on one or more carriers.
Oxidation/reduction catalyst and NOxStorage component is preferably supported on carrier material such as inorganic oxide, to be formed For the LNT in exhaust system.
The LNT of modification of the invention is designed to the function different from known LNT, this is them preferably through designing Be below about 200 DEG C of temperature storage NOx, in the NO of greater than about 200 DEG C of temperature release storagex.Discharge the NO of storagexIt can To be carried out by heat, or can also be carried out by richness purging.
The LNT of the modification includes first layer and the second layer.First layer includes NOxAbsorbent component and one or more platinum families Metal.The NOxAbsorbent component preferably comprises alkaline-earth metal, alkali metal, rare earth metal and its mixture.The alkaline-earth metal is preferred It is barium, calcium, strontium or magnesium.The alkali metal is preferably potassium, sodium, lithium or caesium.The rare earth metal is preferably lanthanum, yttrium, praseodymium or neodymium.Most preferably Ground, the NOxAbsorbent component includes barium.
If used, then or mixtures thereof alkaline-earth metal, alkali metal, rare earth metal can preferably be carried on inorganic oxide On object.The inorganic oxide material preferably contains ceria material or magnesia-alumina.It is preferred that this contains ceria material It is or mixtures thereof ceria, ceria-zirconia, ceria-zirconia-aluminium oxide.It is highly preferred that this contains dioxy Changing cerium material is ceria, specifically particulate cerium oxide.The magnesia-alumina is preferably spinelle, magnesia-oxygen Change aluminium mixed-metal oxides, hydrotalcite or hydrotalcite sample material and its combination of two or more.It is highly preferred that the oxidation Magnesium-alumina supports are spinelles.
The alkaline-earth metal, alkali metal or rare earth component can be carried on the inorganic oxide by any of means On object material, addition manner is not considered particularly critical.For example, can be by dipping, absorption, ion exchange, initial wetting, heavy Barium compound (such as barium acetate) is added to containing in ceria material by shallow lake etc..Preferably, first layer includes at least 2.5 weights Measure the barium of %.
The platinum group metal is preferably or mixtures thereof platinum, palladium, rhodium.Particularly preferred platinum and palladium.
Preferably, first layer also includes carrier.The carrier is preferably the oxide of the race of the 2nd, 3,4,5,13 and 14 element. Most preferably, the carrier be aluminium oxide, silica, titanium dioxide, zirconium oxide, magnesia, niobium oxide, tantalum oxide, molybdenum oxide, Tungsten oxide, the arbitrarily mixed oxide of two or more or composite oxides and its mixture.
The preferred preferred surface area of carrier is 10-1500m2/ g, pore volume is 0.1-4mL/g and aperture is about 10- 1000 angstroms.Particularly preferred surface area is greater than 80m2The high surface area carrier of/g.
The second layer includes diesel oxidation catalyst area and NO zoneofoxidation.The diesel oxidation catalyst area include platinum group metal, Zeolite and optional alkaline-earth metal.The optional alkaline-earth metal is preferably magnesium, calcium, strontium or barium;More preferably barium.The platinum group metal Preferably include platinum and palladium.Preferably, the Pd:Pt ratio in the diesel oxidation catalyst area is 0.25-1.
The zeolite can be any natural or synthetic zeolite, and preferably comprise aluminium, silicon and/or phosphorus.The zeolite is typical Ground has SiO4、AlO4And/or PO4Three-dimensional arrangement, combined by shared oxygen atom, but be also possible to two-dimensional structure. The zeolite skeleton is typically anion, is balanced by charge compensation cation, the charge compensation cation allusion quotation It is type alkali and alkaline earth metal ions element (such as Na, K, Mg, Ca, Sr and Ba), ammonium ion and proton.
Preferably, aluminosilicate zeolites, the aluminate or phosphate zeolite, gold which is selected from aluminosilicate zeolites, metal replaces Belong to the silicoaluminophosphate zeolite that the aluminate or phosphate zeolite, silicoaluminophosphate zeolite or metal replaced replaces.
Particularly preferably with following framework types zeolite: ACO, AEI, AEN, AFN, AFT, AFX, ANA, APC, APD, ATT、CDO、CHA、DDR、DFT、 EAB、EDI、EPI、ERI、GIS、GOO、IHW、ITE、ITW、LEV、KFI、 MER、MON、 NSI、OWE、PAU、PHI、RHO、RTH、SAT、SAV、 SIV、THO、TSC、UEI、UFI、VNI、YUG、ZON、MFI、FER、 MWW, EUO, CON, BEA, FAU, MOR and EMT and its two or more any mixture or commensal.Most preferably, The framework types of the zeolite are AEI, CHA, LEV, BEA (such as β zeolite), FAU (such as zeolite Y) or MFI (such as ZSM- 5)。
The diesel oxidation catalyst can also preferably comprise manganese.
The diesel oxidation catalyst area preferably also includes inorganic oxide carrier.The inorganic oxide carrier preferably comprises 2, the oxide of 3,4,5,13 and 14 race's elements.Most preferably, which is aluminium oxide or silica-doped carrying alumina Body.
The NO zoneofoxidation includes platinum group metal and carrier.The platinum group metal preferably includes platinum and palladium.Preferably, which aoxidizes Pd:Pt ratio in area is 0-0.25.
The carrier is preferably aluminium oxide, silica, containing ceria material, titanium dioxide, zirconium oxide, magnesia, oxygen Change niobium, tantalum oxide, molybdenum oxide, tungsten oxide, the arbitrarily mixed oxide of two or more or composite oxides (such as dioxy SiClx-aluminium oxide, magnesia-alumina) and its mixture.This contains ceria material and is preferably ceria, titanium dioxide Or mixtures thereof cerium-zirconium oxide, ceria-zirconia-aluminium oxide,;It is highly preferred that it is oxidation that this, which contains ceria material, Cerium, especially particulate cerium oxide.The mixture of particularly preferred carrier such as aluminium oxide and ceria.
The NO zoneofoxidation can also preferably comprise manganese.
The NO zoneofoxidation may include alkali or alkaline earth metal such as barium, but can also substantially free of alkali metal or Alkaline earth metal component.Substantially free indicates that no alkali or alkaline earth metal is intentionally added to NO zoneofoxidation.Preferably, Substantially free indicates that NO zoneofoxidation includes the alkali or alkaline earth metal less than 0.1 weight %, more preferably less than 0.05 weight The alkali or alkaline earth metal for measuring %, most preferably without alkali or alkaline earth metal.
The LNT of the modification preferably comprises substrate.The substrate is preferably ceramic bases or metallic substrates.The ceramic bases can be with It is made of any suitable refractory material, the refractory material such as aluminium oxide, silica, titanium dioxide, ceria, oxidation Zirconium, magnesia, zeolite, silicon nitride, silicon carbide, zirconium silicate, magnesium silicate, aluminosilicate and metal aluminosilicates (such as cordierite And spodumene) or its two or more any mixture or mixed oxide.Particularly preferred cordierite, magnesium alumino metasilicate Salt and silicon carbide.
The metallic substrates can be made of any suitable metal, and the metal especially heating resisting metal and metal alloy are for example Titanium and stainless steel and Alfer, the Alfer contain iron, nickel, chromium and/or aluminium and other trace metals.
The substrate is preferably flow type substrate or filter base.Most preferably, which is flow type substrate.Specifically Ground, which is flow type material all in one piece, preferably has honeycomb body structure, has and extends axially through the substrate and run through Many small, parallel thin-walled channels that the substrate extends.
The channel cross-section of the substrate can be any shape, it is preferred that be square, sinusoidal, triangle, rectangle, Hexagon, trapezoidal, round or ellipse.
When being added to the substrate, the NO of the modificationxThe layer of trap can arrange in any order on this substrate, but excellent First layer is selected to be located in the substrate, the second layer is located on first layer.The diesel oxidation catalyst area of the second layer is preferably placed in Then the upstream of the NO zoneofoxidation contacts the NO zoneofoxidation so that exhaust gas contacts the diesel oxidation catalyst area first.
The NO of modification of the inventionxTrap can be prepared by method commonly known in the art.Preferably, the NOxTrap is logical It crosses that two layers is deposited in the substrate using carrier coating (washcoat) program and prepares.
Preferably, the whole length of the substrate is coated with first layer slurry, so that the of carrier coating (washcoat) One layer of whole surface for covering the substrate.The a part of the length of the substrate from front end is coated with the diesel oxidation catalyst Area, and the rest part of base length is coated with the NO zoneofoxidation.
The LNT of the modification of the invention is being below about 200 DEG C of temperature storage NOx, discharged in greater than about 200 DEG C of temperature The NO of storagex
The exhaust system of the invention also includes ammonia-selective catalytic reduction (NH3- SCR) catalyst.The NH3- SCR catalysis Agent may include any of NH3SCR catalyst is well known in the art.NH3SCR catalyst be by with nitrification Object (such as ammonia or urea) is reacted NOxIt is reduced into N2Catalyst.
Preferably, the NH3SCR catalyst includes vanadium oxide-titanium deoxide catalyst, vanadium oxide-tungsten oxide-titanium dioxide Titanium catalyst or metal/zeolite.Metal/the zeolite catalyst includes metal and zeolite.Preferred metal includes iron and copper.
The zeolite can be any natural or synthetic zeolite, preferably comprise aluminium, silicon and/or phosphorus.The zeolite typically has There is SiO4、AlO4And/or PO4Three-dimensional arrangement, combined by shared oxygen atom, but be also possible to two-dimensional structure.
The zeolite skeleton is typically anion, is balanced by charge compensation cation, the charge compensation Cation is typically alkali and alkaline earth metal ions element (such as Na, K, Mg, Ca, Sr and Ba), ammonium ion and proton.
Preferably, aluminosilicate zeolites, the aluminate or phosphate zeolite, gold which is selected from aluminosilicate zeolites, metal replaces Belong to the silicoaluminophosphate zeolite that the aluminate or phosphate zeolite, silicoaluminophosphate zeolite or metal replaced replaces.
Particularly preferably with following framework types zeolite: ACO, AEI, AEN, AFN, AFT, AFX, ANA, APC, APD, ATT、CDO、CHA、DDR、DFT、 EAB、EDI、EPI、ERI、GIS、GOO、IHW、ITE、ITW、LEV、KFI、 MER、MON、 NSI、OWE、PAU、PHI、RHO、RTH、SAT、SAV、 SIV、THO、TSC、UEI、UFI、VNI、YUG、ZON、MFI、FER、 MWW, EUO, CON, BEA, FAU, MOR and EMT and its two or more any mixture or commensal.Most preferably, The framework types of the zeolite are AEI, CHA, LEV, BEA (such as β zeolite) or FER (such as ferrierite).
The NH3SCR catalyst is preferably applied in ceramics or metallic substrates, as described above.The substrate is typically through designing There is provided the channel that many vehicle exhausts are passed through, and the surface in the channel will be preferably coated with the NH3SCR catalyst.
For the NH3The substrate of SCR catalyst can be filter base or flow type substrate.Preferably, the NH3-SCR Catalyst is coated on filter, is referred to as ammonia-selective catalytic reduction filter (NH3-SCRF).SCRF is single substrate Device, a combination thereof NH3The function of-SCR and particulate filter.They are used to restore the NO of internal combustion enginexAnd particle emission.
System of the invention further includes urea injection system.The urea injection system preferably comprises urea injector, It introduces urea into the NH3In the waste gas stream in SCR catalyst upstream and the downstream LNT of the modification.The urea injection system will It is preferred that being made of nozzle, to generate the urea liquid droplet of sharp outline.The droplet size is preferably smaller than 500 microns to allow fastly Speed evaporation and urea decompose.The syringe pressure and pump rate will be so that effectively mix in the waste gas stream.
The urea injection system also preferably by urea slot, feed-line and will be used to that urea liquid to be avoided to freeze possible Heating system composition.
Preferably, which injects urea in greater than about 180 DEG C of temperature.
The invention also includes a kind of methods for handling engine exhaust gas.This method includes making the exhaust gas by above-mentioned modification LNT.The LNT of the modification removes nitrogen oxides (NO in the temperature below about 200 DEG C from the exhaust gasx), and greater than about 200 DEG C of temperature discharges the NOx.In greater than about 180 DEG C of temperature, urea injects in the exhaust gas in the downstream LNT of the modification, and And make containing the NO discharged from the LNT of the modificationxPass through NH with the exhaust gas of urea3- SCR catalyst.The NO of the releasexPass through ammonia (being generated by urea) and NOxIn the NH3It is reacted in SCR catalyst and is converted to nitrogen.The NO of the releasexIt is in low-temperature storage in this On modified LNT, then in the NO of higher temperature releasex, and further include by the NH3SCR catalyst is without storage NOx
Preferably, the LNT of the modification periodically passes through rich desulfurized step.Sulphur compound is for the modification present in fuel LNT can be harmful, because the oxidation of sulphur compound generates the oxysulfide in the exhaust gas.In the LNT, sulfur dioxide can be with It is oxidized to sulfur trioxide on platinum group metal, and forms surface sulfate (such as barium monoxide or carbonic acid on the surface LNT Barium reacts to form barium sulfate with sulfur trioxide).These sulfate are more more stable than nitrate, and need higher temperature (> 500 DEG C) carry out desulfurization.If the LNT of the modification has low barium content, lower desulfurization temperature can be useful.
In rich desulfurization, the LNT of the modification is typically in enriched air: passing through greater than about 500 DEG C of temperature in fuel ratio environment Degree, to complete desulfurization.The desulfurization preferably increases delivery temperature by injecting after fuel to carry out.Desulfurization program may include list A, lasting is rich in phase or a series of short rich pulses.
Following embodiment only illustrates the present invention.Those skilled in the art will recognize that many variations in purport and power of the invention In the range of sharp claim.
Embodiment 1: modified LNT is prepared
Modified LNT 1A
By NO of the flow type cordierite substrates material all in one piece comprising two layers of 400 holes/square inch (cpsi)xAdsorbent is urged Agent formulation is coated.Lower layer's carrier coating includes Pt, Pd, 28% Ce/ magnesium-aluminate spinel and 66% dioxy Change cerium (95% total CeO 2 supporting amount includes particulate cerium oxide, contains 7% Ba).The carrier coating uses Method disclosed in WO99/47260 is coated on original substrate material all in one piece, then dry in 100 DEG C of forced ventilation drying machine It 30 minutes, is then calcined 2 hours at 500 DEG C.
Preparation is by slurrying and is ground to d90Second slurry of < 20 microns of aluminium oxide composition, is then added suitable solvable Property platinum and palladium salt and particulate cerium oxide generate 50% aluminium oxide and 50% particulate cerium oxide.Second slurry is passed through Lower layer through calcining is administered to by exit passageway.By this it is partially dried and 500 DEG C calcine.
Preparation is by slurrying in water and is ground to d90The third of < 20 microns of silica-doped alumina powder composition Slurry.Barium acetate is added in the slurry, suitable soluble platinum and palladium salt are then added.Then the slurry stirs 30 minutes It is homogenized, adds β zeolite then to generate 81% silica-doped aluminium oxide and 19% β zeolite.By third slurry The lower layer through calcining is administered to via access road.By this it is partially dried and 500 DEG C calcine, to generate 89g/ft3Pt and 30g/ft3Total PGM load capacity of Pd.
Compare LNT 2
By NO of the flow type cordierite substrates material all in one piece comprising single layer of 400 holes/square inch (cpsi)xAdsorbent is urged Agent formulation is coated, this layer includes the particulate cerium oxide of Pt, Pd, Ce/ magnesium-aluminate spinel, Ba coating, and packet Containing 33% Ce/ magnesium-aluminate spinel, 61% ceria, (93% total CeO 2 supporting amount includes granular dioxy Change cerium, contain 7% Ba) and 113g/ft3Pt and Pd.The carrier coating is applied using method disclosed in WO99/47260 It is layed on original substrate material all in one piece, it is then 30 minutes dry in 100 DEG C of forced ventilation drying machine, it is then small in 500 DEG C of calcinings 2 When.
Embodiment 2: Engine Block Test
By modified LNT 1A and comparison LNT 2 (1.4L catalyst volume) 800 DEG C hydrothermal aging 5 hours.Each LNT Using low pressure exhaust gas recycling (EGR) on 1.6L engine, preconditioned by 4 NEDC periods of operation, the NEDC period 5s richness purging with the λ 0.95 when 100kph cruises.Then it is evaluated on 2.2L engine with NEDC drive cycle.? Without using rich purging in evaluation procedure.
The results show that the LNT 1A of the modification stores the NO of about 0.5g at most about 200 DEG Cx, then from 200 DEG C to 300 DEG C of almost hot NO for releasing storagex, this shows that the LNT of modification of the invention can be used in NH3SCR system.Fig. 2 The LNT 1A design of display, the modification makes rear LNT NO2/NOxThan increasing 20-40%, the 5-20% shape of this and comparison LNT 2 In contrast with.Table 1 describes the exhaust pipe CO discharge using the LNT 1A of the modification, which show considerably higher CO conversion ratio and For the greatly modified stability of the oxidative deactivation of 4 NEDC without richness purging.Table 2 describes the LNT using the modification The exhaust pipe HC of 1A is discharged, and which show considerably higher HC conversion ratios.
1 exhaust pipe CO of table discharge
2 exhaust pipe HC of table discharge

Claims (20)

1. the exhaust system for handling engine exhaust gas, it includes modified poor NOxTrap, urea injection system and ammonia-selectivity Catalytic reduction catalysts, the wherein poor NO of the modificationxTrap is being lower than 200 DEG C of temperature storage NOxBe higher than 200 DEG C of temperature Discharge the NO of storagex, the poor NO of the modificationxTrap includes:
(a) first layer, it includes NOxAbsorbent component and one or more platinums group metal, the wherein NOxAbsorbent component includes Alkaline-earth metal, alkali metal, rare earth metal and its mixture;With
(b) second layer, it includes: the diesel oxidation catalyst area comprising platinum group metal, zeolite and optional alkaline-earth metal;And packet The NO zoneofoxidation of platinum group metal and carrier.
2. exhaust system according to claim 1, wherein the urea injection system injects urine in the temperature higher than 180 DEG C Element.
3. exhaust system according to claim 1, wherein the alkaline-earth metal, alkali metal, rare earth metal and its mixture are negative It is loaded on inorganic oxide material.
4. exhaust system according to claim 3, wherein the inorganic oxide material is containing ceria material or oxidation Magnesium-aluminium oxide.
5. exhaust system according to claim 4, wherein the magnesia-alumina is magnesium-aluminate spinel.
6. exhaust system according to claim 1 or 2, the wherein NOxAbsorbent component includes barium.
7. exhaust system according to claim 1 or 2, wherein one or more platinums group metal of first layer be selected from palladium, Platinum, rhodium and its mixture.
8. exhaust system according to claim 1 or 2, wherein the zeolite in the diesel oxidation catalyst area is selected from sending down the fishbone Frame type: AEI, CHA, LEV, BEA, FAU and MFI.
9. exhaust system according to claim 1 or 2, wherein the diesel oxidation catalyst area further includes: including oxygen Change the inorganic oxide carrier of aluminium or silica-doped aluminium oxide.
10. exhaust system according to claim 1 or 2, wherein the carrier of the NO zoneofoxidation includes aluminium oxide and dioxy Change cerium.
11. exhaust system according to claim 1 or 2, wherein the NO zoneofoxidation further includes manganese.
12. exhaust system according to claim 1 or 2, wherein ammonia-the selective catalytic reduction catalysts are selected from oxidation Vanadium-titanium deoxide catalyst, vanadium oxide-tungsten oxide-titanium deoxide catalyst and metal/zeolite.
13. exhaust system according to claim 12, wherein metal/the zeolite includes the metal selected from iron or copper, and choosing From the zeolite of following framework types: AEI, CHA, LEV, BEA or FER.
14. exhaust system according to claim 12, wherein metal/the zeolite includes metal and the β boiling selected from iron or copper Stone.
15. exhaust system according to claim 12, wherein metal/the zeolite includes metal and magnesium selected from iron or copper Alkali zeolite.
16. exhaust system according to claim 1 or 2, wherein ammonia-the selective catalytic reduction catalysts are ammonia-selections Property catalysis reduction filter.
17. exhaust system according to claim 16, wherein the ammonia-selective catalytic reduction filter includes to have ammonia- The filter of selective catalytic reduction catalysts, the ammonia-selective catalytic reduction catalysts are selected from: vanadium oxide-titanium dioxide is urged Agent, vanadium oxide-tungsten oxide-titanium deoxide catalyst and metal/zeolite.
18. modified poor NOxTrap, it includes:
(a) first layer, it includes NOxAbsorbent component and one or more platinums group metal, the wherein NOxAbsorbent component includes Alkaline-earth metal, alkali metal, rare earth metal and its mixture;With
(b) second layer, it includes: the diesel oxidation catalyst area comprising platinum group metal, zeolite and optional alkaline-earth metal;And packet The NO zoneofoxidation of platinum group metal and carrier.
19. the method for handling vehicle internal combustion engine exhaust gas comprising:
(a) make poor NO of the exhaust gas Jing Guo modification according to claim 18 in the temperature lower than 200 DEG CxTrap removes this Nitrogen oxides (NO in exhaust gasx), and the NO is discharged in the temperature higher than 200 DEG Cx
(b) it is being higher than 180 DEG C of temperature, in the poor NO of the modificationxTrap downstream introduces urea into the exhaust gas;With
(c) make containing the poor NO from the modificationxThe NO of trap releasexExhaust gas with urea is by ammonia-selective catalytic reduction catalysis Agent, by the NOxIt is converted to nitrogen.
20. further comprising according to the method for claim 19, the poor NO for periodically making the modificationxTrap is in enriched air: fuel By the temperature higher than 500 DEG C in the environment of ratio, to remove accumulation in the poor NO of the modificationxSulphur on trap.
CN201580042915.1A 2014-08-12 2015-08-07 Exhaust system with modified poor NOX trap Active CN106661984B (en)

Applications Claiming Priority (3)

Application Number Priority Date Filing Date Title
US201462036184P 2014-08-12 2014-08-12
US62/036,184 2014-08-12
PCT/IB2015/056016 WO2016024193A1 (en) 2014-08-12 2015-08-07 Exhaust system with a modified lean noxtrap

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CN106661984A CN106661984A (en) 2017-05-10
CN106661984B true CN106661984B (en) 2019-07-16

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Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20040004376A (en) * 2000-09-16 2004-01-13 존슨 맛쎄이 퍼블릭 리미티드 컴파니 Nox-trap
JP3861489B2 (en) * 1998-01-30 2006-12-20 マツダ株式会社 Exhaust gas purification catalyst and method for producing the same
CN102089066A (en) * 2008-06-27 2011-06-08 巴斯夫公司 NOx adsorber catalyst with superior low temperature performance
CN102387851A (en) * 2009-04-03 2012-03-21 巴斯夫公司 Emissions treatment system with ammonia-generating and SCR catalysts
CN103089380A (en) * 2011-11-07 2013-05-08 通用汽车环球科技运作有限责任公司 Electronically heated nox adsorber catalyst
KR20130058988A (en) * 2011-11-28 2013-06-05 현대자동차주식회사 Lnt for engine

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP3861489B2 (en) * 1998-01-30 2006-12-20 マツダ株式会社 Exhaust gas purification catalyst and method for producing the same
KR20040004376A (en) * 2000-09-16 2004-01-13 존슨 맛쎄이 퍼블릭 리미티드 컴파니 Nox-trap
CN102089066A (en) * 2008-06-27 2011-06-08 巴斯夫公司 NOx adsorber catalyst with superior low temperature performance
CN102387851A (en) * 2009-04-03 2012-03-21 巴斯夫公司 Emissions treatment system with ammonia-generating and SCR catalysts
CN103089380A (en) * 2011-11-07 2013-05-08 通用汽车环球科技运作有限责任公司 Electronically heated nox adsorber catalyst
KR20130058988A (en) * 2011-11-28 2013-06-05 현대자동차주식회사 Lnt for engine

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