CN102744064B - Catalyst and its preparation for nitrogen oxide in automobile exhaust processing - Google Patents

Catalyst and its preparation for nitrogen oxide in automobile exhaust processing Download PDF

Info

Publication number
CN102744064B
CN102744064B CN201210257069.3A CN201210257069A CN102744064B CN 102744064 B CN102744064 B CN 102744064B CN 201210257069 A CN201210257069 A CN 201210257069A CN 102744064 B CN102744064 B CN 102744064B
Authority
CN
China
Prior art keywords
catalyst
carrier
preparation
rare earth
aluminium
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Active
Application number
CN201210257069.3A
Other languages
Chinese (zh)
Other versions
CN102744064A (en
Inventor
王秀云
王瑞虎
洪茂椿
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Fujian Institute of Research on the Structure of Matter of CAS
Original Assignee
Fujian Institute of Research on the Structure of Matter of CAS
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Fujian Institute of Research on the Structure of Matter of CAS filed Critical Fujian Institute of Research on the Structure of Matter of CAS
Priority to CN201210257069.3A priority Critical patent/CN102744064B/en
Publication of CN102744064A publication Critical patent/CN102744064A/en
Application granted granted Critical
Publication of CN102744064B publication Critical patent/CN102744064B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Landscapes

  • Catalysts (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)

Abstract

The present invention is provided to the catalyst of nitrogen oxide in automobile exhaust processing and its preparation.For the catalyst using aluminium cerium zirconium as carrier, a small amount of noble metal is active metal, by the doping of rare earth element, improves the NO of catalystxConversion ratio and heat endurance.After the h of aging 100, its NO of described catalystxPurifying rate is held essentially constant, and undoped with catalyst its NOxPurifying rate reduces by more than 20%.

Description

Catalyst and its preparation for nitrogen oxide in automobile exhaust processing
Technical field
The invention belongs to nano-catalytic application, and in particular to a kind of rare earth doped aluminium-cerium-zirconium carrier application The NO in vehicle exhaustxPurification.
Background technology
In recent years, sharply increasing with automobile quantity, the tail gas of motor vehicle emission have become the main dirt of atmosphere pollution One of dye source, the NO in its compositionxSeriously endanger environment and the health of the public.China is at present to NOxPurification generally uses three First catalyst, very big due to being influenceed by engine air-fuel ratio, traditional three-way catalyst is to NOxClean-up effect and bad.Cause Under this lean-burn condition(Air-fuel ratio>1) NOxPurification is one of current challenging problem.Exhaust of lean-burn automotive at present The research of purification is concentrated mainly on NOxDirectly decompose, selective catalysis reduces and NOxStorage-reduction etc., wherein NOxStorage- Reduction technique is increasingly subject to pay attention to due to the plurality of advantages such as purification efficiency is high, temperature window is wide, operating cost is low.
NOxThe general principle of storage-reduction method is by NO under lean-burn conditionxAdsorption storage gets up, then in rich condition Under discharge, N is changed into by reducing agent2.Wherein Pt/Ba/Al2O3It is typical NOxStorage-reduction catalyzer, exist at present Japanese industrialized production.But the sulfur content in fuel on Japanese market is low, and some domestic sulfur contents in fuel are higher, easily It is that catalyst is poisoned, therefore Pt/Ba/Al2O3Catalyst is restricted in practical application at home.In addition, NOxStorage Deposit-heat endurance of reducing catalyst is also a pressing issues for being badly in need of solving, composition BaO and carrier are stored at high temperature Al2O3Or CeO2With reference to generation BaAlO4Or BaCeO3So as to inactivate.We have found that by the difference of rare earth element ion radius, enter Enter in aluminium-cerium-zirconium support crystal lattice, produce more oxygen vacancies, can effectively suppress BaAlO4Or BaCeO3Generation, so as to carry The heat endurance of high catalyst.There is presently no pertinent literature and patent to be reported this.
The content of the invention
High, the strong NO of stability the invention provides a kind of catalytic activityxCleaning catalyst.
The catalyst includes precious metals pt, Pd and the one kind or more in Rh of aluminium-cerium-zirconium carrier and load on this carrier Kind active component, alkali metal or alkaline-earth metal storage component, the aluminium-cerium-zirconium carrier are by Modified by Rare Earth Elements.
It is described to be used for NOxThe catalyst of purification, the carrier components include Al2O3、CeO2And ZrO2
It is described to be used for NOxThe catalyst of purification, aluminium-cerium that the catalyst uses-doping of zirconium carrier La, Y, Sm, Nd and Pr Deng rare earth element.Rare earth element accounts for the 1-10 % of aluminium-cerium-zirconium carrier quality(Calculated with La or Nd).It is preferred that 5%.
It is described to be used for NOxThe catalyst of purification, the noble metal of dipping is one or more in Pt, Pd and Rh.It is preferred that Pt.
Described NOxCleaning catalyst, active metal weight account for the 0.5-1 % of total catalyst weight.
Described NOxCleaning catalyst, the catalyst is using the alkaline earths such as Li, Na, K, Rb alkali metal or Mg, Ca, Ba, Sr gold One or more in category are auxiliary agent.It is preferred that Ba, K, wherein Ba, K mass fraction account for 16 % of carrier(Calculated with Ba).
The preparation method of described catalyst, include the synthesis of fresh sample, then be calcined by 500 °C -700 °C.
Its sintering temperature is preferably 550 °C.
By La, Y, Nd or Pr doping, NO is improvedxThe heat endurance of cleaning catalyst, in 350 °C of agings 100 Its activity keeps stable after h.
Brief description of the drawings
Fig. 1 is:Rare earth doped element La, Y, Nd and undoped with Pt/Ba/ACZ catalyst ns O change into NO2Activity.
Fig. 2 is:Rare earth doped element La, Y, Nd and undoped with Pt/Ba/ACZ catalyst ns OxConversion rate curve.
Fig. 3 is:Rare earth doped element La, Y, Nd and undoped with Pt/Ba/ACZ catalyst thermostabilization.
Embodiment
The present invention is used for NOxIt the catalyst of purification, can in granular form use, coating load can also be used as in entirety Integral catalyzer is formed on formula porous matrix.Monolithic porous matrix can be the ceramics such as cellular cordierite, mullite Matrix or other alloy substrates.
The NO of the present inventionxCleaning catalyst can be individually carried on a matrix, can also be with current three-element catalytic Agent mixing one multicomponent catalyst of composition.
More specifically the catalyst of the present invention is illustrated with reference to embodiment, but these embodiments are to the present invention's Scope is without any restrictions.
Embodiment 1
(1)The preparation of control sample:By Al (NO3)3 .6H2O, Ce (NO3)3 .6H2O and Zr (NO3)4 .5H2O wiring solution-formings, its Middle Al2O3:CeO2:ZrO2Mass percent be 67:22:11.Then 30 % H are added2O2As oxidant, NH is used3 .H2O It is 10 as precipitating reagent to pH, is washed by centrifugation, by H2PtCl6 .6H2O is distributed in above-mentioned slurries, aging, drying, 550 ° After C is calcined 4 h, by Ba (NO3)2It is impregnated into using incipient impregnation mode after being calcined on the carrier of gained, drying.Through 500 ° CH2/N2Gained catalyst is Pt/Ba/ Al after reduction2O3-Ce0.67Zr0.33O2Catalyst, it is designated as catalyst 1.
(2)Adulterate the preparation of lanthanum catalyst:By Al (NO3)3 .6H2O, Ce (NO3)3 .6H2O, Zr (NO3)4 .5H2O and La (NO3)3 .6H2O wiring solution-formings, wherein Al2O3:CeO2:ZrO2=67:22:11, add 30 % H2O2, La2O3For carrier quality 5%, with 30 % H2O2As oxidant, NH3 .H2O is precipitating reagent, and it is 10 to be precipitated to pH, is washed by centrifugation, will H2PtCl6 .6H2O is distributed in above-mentioned slurries, aging, drying, after 550 °C of 4 h of roasting, by Ba (NO3)2Using incipient impregnation Mode be impregnated into roasting after gained carrier on, drying.Through 500 °C of H2/N2Gained catalyst is Pt/Ba/ after reduction La2O3-Al2O3-Ce0.67Zr0.33O2Catalyst.It is designated as catalyst 2.
Embodiment 2
(1) preparation of control sample:By Al (NO3)3 .6H2O, Ce (NO3)3 .6H2O and Zr (NO3)4 .5H2O wiring solution-formings, its Middle Al2O3:CeO2:ZrO2Mass percent be 67:22:11.Then 30 % H are added2O2As oxidant, NH is used3 .H2O It is 10 as precipitating reagent to pH, is washed by centrifugation, by H2PtCl6 .6H2O is distributed in above-mentioned slurries, aging, drying, 550 ° After C is calcined 4 h, by Ba (NO3)2It is impregnated into using incipient impregnation mode after being calcined on the carrier of gained, drying.Through 500 ° CH2/N2Gained catalyst is Pt/Ba/ Al after reduction2O3-Ce0.67Zr0.33O2Catalyst, it is designated as catalyst 1.
(2) preparation of neodymium catalyst is adulterated:By Al (NO3)3 .6H2O, Ce (NO3)3 .6H2O, Zr (NO3)4 .5H2O and Nd (NO3)3 .6H2O wiring solution-formings, wherein Al2O3:CeO2:ZrO2Mass percent be 67:22:11, then add 30 % H2O2As oxidant, with NH3 .H2O is precipitating reagent, and it is 10 to be precipitated to pH, is washed by centrifugation, by H2PtCl6 .6H2O is distributed to In above-mentioned slurries, aging, drying, after 550 °C are calcined 4 h, by Ba (NO3)2After roasting being impregnated into using incipient impregnation mode On the carrier of gained.Drying.Through 500 °C of H2/N2Gained catalyst is Pt/Ba/Nd after reduction2O3-Al2O3- Ce0.67Zr0.33O2Catalyst.It is designated as catalyst 3.
The performance of embodiment catalyst is evaluated below
Catalyst is to NO under the different temperatures of test case 1x Conversion ratio
Embodiment 1-2 catalyst each 0.5 mL, the h of air speed 72 000 is respectively adopted-1, in continuous stream actuating miniature fixed bed Upper carry out NOxStorage and determination by reduction, NO in tail gasx Change in concentration passes through chemiluminescence NO-NO2-NOxAnalyzer detects (Thermo, 42i-HL).Reacting gas forms:500 ppm NO, 8Vol%O2, 8Vol%CO2, N2For Balance Air.Exist respectively Catalyst is determined under 200 °C, 250 °C, 300 °C, 350 °C, 400 °C to NOx Changing effect, test result is shown in Fig. 1, by taking 5 % rare earth elements (La or Nd) doped catalyst as an example, test result of the present invention is not limited to 5 % rare earth elements and mixed Miscellaneous catalyst.
It will be seen from figure 1 that described catalyst 2 and 3 has for the catalyst 1 undoped with rare earth element Higher NO-to-NO2Conversion ratio.At 350 °C, the NO-to-NO of catalyst 1,2 and 32Conversion ratio is respectively 33 %, 64 % With 43 %.
Figure it is seen that described catalyst 2 and 3 has for the catalyst 1 undoped with rare earth element Preferable NOxConversion ratio.T=350 °C, the NO of catalyst 2x It is converted into N2Conversion ratio be 98 %, the NO of catalyst 3x Conversion Rate is 94 %, and the NO of catalyst 1xConversion ratio is 83 %.In NO of 200 °C and 300 °C its catalyst 2 than catalyst 1xTurn Rate improves 20 more than %.
The catalyst 1-3 of test case 2 cycle life test
Reacting gas forms:500 ppm NO, 8 Vol%O2, 8 Vol%CO2, N2For Balance Air.Air speed is 72 000 h-1, continuously NO is being determined after the h of aging 100 in flowing fixed bed under 350 °CxThe stability ability of conversion ratio.Its result is shown in figure 3。
Fig. 3 catalyst 1 is in N2After 100 h are stabilized under atmosphere, NOx Conversion ratio reduces by 20 more than %, deactivation phenomenom occurs.
Fig. 3 catalyst 2 is in N2After 100 h are stabilized under atmosphere, NOx Conversion ratio is held essentially constant, and is not inactivated Phenomenon.
Fig. 3 catalyst 3 is in N2After 100 h are stabilized under atmosphere, NOx Conversion ratio also keeps not becoming substantially.
The representative embodiment of the present invention is the foregoing is only, it is every according to the modification done in scope of the present invention patent With change, it should all belong to covering scope of the invention.

Claims (8)

1. one kind is used for NOxThe catalyst of purification, it is characterized in that:The catalyst is by aluminium-cerium-zirconium carrier and loads on this carrier Precious metals pt and alkaline-earth metal storage component composition;Aluminium-cerium-zirconium the carrier is Al2O3、CeO2And ZrO2, it passes through rare earth Element is modified, one or more of the rare earth element in La, Y, Sm, Nd or Pr;The alkaline-earth metal be selected from Mg, Ca, One or more in Ba or Sr.
2. catalyst according to claim 1, it is characterised in that:The doping of the rare earth element accounts for aluminium-cerium-zirconium carrier The 1-10% of mass fraction.
3. catalyst as claimed in claim 1 or 2, it is characterised in that:Described alkaline-earth metal accounts for the 10- of total catalyst weight 16%.
4. catalyst according to claim 1 or 2, it is characterised in that:The Pt accounts for the 0.5-1% of total catalyst weight.
5. catalyst according to claim 1, it is characterised in that:The catalyst is Pt/Ba/La2O3-Al2O3- Ce0.67Zr0.33O2Or Pt/Ba/Nd2O3-Al2O3-Ce0.67Zr0.33O2
6. the preparation method of any one of the claim 1-5 catalyst, including:The synthesis of fresh sample, then by 500-700 DEG C Roasting.
7. the preparation method of catalyst according to claim 6, it is characterised in that:The sintering temperature is 550 DEG C.
8. the NO that any one of the claim 1-5 catalyst is used in vehicle exhaustxPurification.
CN201210257069.3A 2012-07-23 2012-07-23 Catalyst and its preparation for nitrogen oxide in automobile exhaust processing Active CN102744064B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201210257069.3A CN102744064B (en) 2012-07-23 2012-07-23 Catalyst and its preparation for nitrogen oxide in automobile exhaust processing

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201210257069.3A CN102744064B (en) 2012-07-23 2012-07-23 Catalyst and its preparation for nitrogen oxide in automobile exhaust processing

Publications (2)

Publication Number Publication Date
CN102744064A CN102744064A (en) 2012-10-24
CN102744064B true CN102744064B (en) 2017-12-12

Family

ID=47024760

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201210257069.3A Active CN102744064B (en) 2012-07-23 2012-07-23 Catalyst and its preparation for nitrogen oxide in automobile exhaust processing

Country Status (1)

Country Link
CN (1) CN102744064B (en)

Families Citing this family (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB2514177A (en) * 2013-05-17 2014-11-19 Johnson Matthey Plc Oxidation catalyst for a compression ignition engine
CN103551165A (en) * 2013-11-04 2014-02-05 中国科学院福建物质结构研究所 Transitional-element-doped nitrogen oxide purification catalyst as well as preparation method and application thereof
CN105709811B (en) * 2016-04-12 2017-11-07 青岛农业大学 A kind of Ag doping calcium and magnesium being used in motor exhaust is combined storage and reduction catalyst and its preparation method and application
JP2018171599A (en) * 2017-03-31 2018-11-08 トヨタ自動車株式会社 Catalyst for exhaust gas purification
CN114588901A (en) * 2022-03-30 2022-06-07 北京工业大学 NO oxidation catalyst for removing NOx from ship and preparation method thereof

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1053899A (en) * 1990-02-09 1991-08-21 底古萨股份公司 The catalyzer that is used for purification of exhaust gases of internal combustion engines
CN101428219A (en) * 2008-11-14 2009-05-13 中国科学院上海硅酸盐研究所 Oxynitride catalysis reductant in oxygen-enriched condition and preparation method thereof

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1053899A (en) * 1990-02-09 1991-08-21 底古萨股份公司 The catalyzer that is used for purification of exhaust gases of internal combustion engines
CN101428219A (en) * 2008-11-14 2009-05-13 中国科学院上海硅酸盐研究所 Oxynitride catalysis reductant in oxygen-enriched condition and preparation method thereof

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
铈基介孔低温氧化催化剂和钡基NOx储存还原催化剂研究;罗金勇;《中国博士学位论文全文数据库 工程科技I辑》;20101215(第12期);第五章 *
铈锆铝复合材料的性能研究;魏振玲;《中国优秀硕士学位论文全文数据库 工程科技I辑》;20080415(第04期);第四章 *

Also Published As

Publication number Publication date
CN102744064A (en) 2012-10-24

Similar Documents

Publication Publication Date Title
KR100196245B1 (en) Catalyst for purifying exhaust gases
CN103157470B (en) Ternary catalyst for automobile tail gas
WO2010010747A1 (en) Catalyst device for exhaust gas purification and method of purifying exhaust gas
RU2632877C2 (en) Trifunctional catalyst for use in vehicle exhaust gases and exhaust gas purification system
CN102744064B (en) Catalyst and its preparation for nitrogen oxide in automobile exhaust processing
US8506912B1 (en) Exhaust treatment system including a nickel-based catalyst
US6557342B2 (en) Exhaust gas purifying system
JP5218092B2 (en) Exhaust gas purification catalyst
WO1997037761A1 (en) Exhaust gas purifying catalyst and exhaust gas purifying method
US20100204036A1 (en) NOx PURIFYING CATALYST
EP3466535A1 (en) Gasoline engine exhaust gas purification three-way catalyst
CN102728383A (en) Preparation method of high temperature stable monolithic catalyst for purifying tail gas of automobile
JP2013072308A (en) Exhaust emission control device for internal combustion engine
CN102580764B (en) A kind of Catalysts and its preparation method for purifying nitrogen oxide
CN103495425B (en) NOx purification catalyst efficient and capable of being regenerated easily at low temperature
CN109589976B (en) Catalyst for diesel engine based on oxide composite main catalyst and preparation method thereof
KR20100037164A (en) Exhaust gas purifying catalyst
US8323579B2 (en) S storage catalyst and exhaust-gas converting apparatus
CN103551165A (en) Transitional-element-doped nitrogen oxide purification catalyst as well as preparation method and application thereof
CN109590016B (en) Catalyst for diesel engine based on modified hydrotalcite derived oxide and preparation method thereof
US10058851B2 (en) Use of mixed oxides as oxygen storage components
CN102744082A (en) NOx purification catalyst for automobile exhaust treatment, and preparation method thereof
CN104759281A (en) Preparation method of composite oxide catalyst used for purifying diesel engine
CN106622279A (en) NOx purification catalyst used for automobile exhaust gas treatment and preparation method thereof
JP5324414B2 (en) Exhaust purification catalyst

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant