JPH0871424A - Exhaust gas purification catalyst - Google Patents
Exhaust gas purification catalystInfo
- Publication number
- JPH0871424A JPH0871424A JP6211548A JP21154894A JPH0871424A JP H0871424 A JPH0871424 A JP H0871424A JP 6211548 A JP6211548 A JP 6211548A JP 21154894 A JP21154894 A JP 21154894A JP H0871424 A JPH0871424 A JP H0871424A
- Authority
- JP
- Japan
- Prior art keywords
- porous carrier
- exhaust gas
- powder
- nickel
- zeolite
- 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.)
- Pending
Links
- 239000003054 catalyst Substances 0.000 title claims description 53
- 238000000746 purification Methods 0.000 title description 14
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 claims abstract description 67
- 229910052759 nickel Inorganic materials 0.000 claims abstract description 32
- 239000011973 solid acid Substances 0.000 claims abstract description 13
- 229910000510 noble metal Inorganic materials 0.000 claims abstract description 12
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical group O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 claims description 31
- 229910021536 Zeolite Inorganic materials 0.000 claims description 30
- 239000010457 zeolite Substances 0.000 claims description 30
- 229910000420 cerium oxide Inorganic materials 0.000 claims description 10
- BMMGVYCKOGBVEV-UHFFFAOYSA-N oxo(oxoceriooxy)cerium Chemical compound [Ce]=O.O=[Ce]=O BMMGVYCKOGBVEV-UHFFFAOYSA-N 0.000 claims description 10
- 239000010970 precious metal Substances 0.000 claims description 6
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 abstract description 54
- 229910021529 ammonia Inorganic materials 0.000 abstract description 27
- 230000000694 effects Effects 0.000 abstract description 13
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 abstract description 8
- 239000001257 hydrogen Substances 0.000 abstract description 3
- 229910052739 hydrogen Inorganic materials 0.000 abstract description 3
- 229910052757 nitrogen Inorganic materials 0.000 abstract description 3
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 abstract description 2
- 239000000843 powder Substances 0.000 description 54
- 239000007789 gas Substances 0.000 description 50
- MWUXSHHQAYIFBG-UHFFFAOYSA-N Nitric oxide Chemical compound O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 36
- PNEYBMLMFCGWSK-UHFFFAOYSA-N Alumina Chemical compound [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 27
- 230000000052 comparative effect Effects 0.000 description 27
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 14
- 239000004215 Carbon black (E152) Substances 0.000 description 11
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 11
- 229910002091 carbon monoxide Inorganic materials 0.000 description 11
- 229930195733 hydrocarbon Natural products 0.000 description 11
- 150000002430 hydrocarbons Chemical class 0.000 description 11
- KDLHZDBZIXYQEI-UHFFFAOYSA-N palladium Substances [Pd] KDLHZDBZIXYQEI-UHFFFAOYSA-N 0.000 description 10
- BASFCYQUMIYNBI-UHFFFAOYSA-N platinum Substances [Pt] BASFCYQUMIYNBI-UHFFFAOYSA-N 0.000 description 10
- 239000000446 fuel Substances 0.000 description 8
- 238000000034 method Methods 0.000 description 8
- 238000002156 mixing Methods 0.000 description 8
- 239000007864 aqueous solution Substances 0.000 description 7
- 238000004519 manufacturing process Methods 0.000 description 7
- 239000000377 silicon dioxide Substances 0.000 description 7
- 239000000203 mixture Substances 0.000 description 6
- 239000002002 slurry Substances 0.000 description 6
- 239000000758 substrate Substances 0.000 description 6
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 5
- 239000001301 oxygen Substances 0.000 description 5
- 229910052760 oxygen Inorganic materials 0.000 description 5
- 239000008188 pellet Substances 0.000 description 5
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 4
- MCMNRKCIXSYSNV-UHFFFAOYSA-N Zirconium dioxide Chemical compound O=[Zr]=O MCMNRKCIXSYSNV-UHFFFAOYSA-N 0.000 description 4
- KBJMLQFLOWQJNF-UHFFFAOYSA-N nickel(ii) nitrate Chemical compound [Ni+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O KBJMLQFLOWQJNF-UHFFFAOYSA-N 0.000 description 4
- 229910052763 palladium Inorganic materials 0.000 description 4
- 238000006722 reduction reaction Methods 0.000 description 4
- 229910052703 rhodium Inorganic materials 0.000 description 4
- 239000010948 rhodium Substances 0.000 description 4
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical compound O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 description 3
- 229910052788 barium Inorganic materials 0.000 description 3
- DSAJWYNOEDNPEQ-UHFFFAOYSA-N barium atom Chemical compound [Ba] DSAJWYNOEDNPEQ-UHFFFAOYSA-N 0.000 description 3
- 239000011248 coating agent Substances 0.000 description 3
- 238000000576 coating method Methods 0.000 description 3
- 238000010304 firing Methods 0.000 description 3
- 229910052697 platinum Inorganic materials 0.000 description 3
- 229920006395 saturated elastomer Polymers 0.000 description 3
- 239000000243 solution Substances 0.000 description 3
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 description 2
- 230000002378 acidificating effect Effects 0.000 description 2
- 229910052783 alkali metal Chemical group 0.000 description 2
- 150000001340 alkali metals Chemical group 0.000 description 2
- 229910052784 alkaline earth metal Inorganic materials 0.000 description 2
- 150000001342 alkaline earth metals Chemical class 0.000 description 2
- 230000003197 catalytic effect Effects 0.000 description 2
- 229910017052 cobalt Inorganic materials 0.000 description 2
- 239000010941 cobalt Substances 0.000 description 2
- GUTLYIVDDKVIGB-UHFFFAOYSA-N cobalt atom Chemical compound [Co] GUTLYIVDDKVIGB-UHFFFAOYSA-N 0.000 description 2
- 229910052802 copper Inorganic materials 0.000 description 2
- 239000010949 copper Substances 0.000 description 2
- 229910001873 dinitrogen Inorganic materials 0.000 description 2
- 238000007598 dipping method Methods 0.000 description 2
- 238000011156 evaluation Methods 0.000 description 2
- 238000007654 immersion Methods 0.000 description 2
- 229910052809 inorganic oxide Inorganic materials 0.000 description 2
- 229910052742 iron Inorganic materials 0.000 description 2
- 229910052746 lanthanum Inorganic materials 0.000 description 2
- FZLIPJUXYLNCLC-UHFFFAOYSA-N lanthanum atom Chemical compound [La] FZLIPJUXYLNCLC-UHFFFAOYSA-N 0.000 description 2
- 229910000480 nickel oxide Inorganic materials 0.000 description 2
- 230000001590 oxidative effect Effects 0.000 description 2
- GNRSAWUEBMWBQH-UHFFFAOYSA-N oxonickel Chemical compound [Ni]=O GNRSAWUEBMWBQH-UHFFFAOYSA-N 0.000 description 2
- 229910052761 rare earth metal Inorganic materials 0.000 description 2
- MHOVAHRLVXNVSD-UHFFFAOYSA-N rhodium atom Chemical compound [Rh] MHOVAHRLVXNVSD-UHFFFAOYSA-N 0.000 description 2
- 238000001179 sorption measurement Methods 0.000 description 2
- 229910018072 Al 2 O 3 Inorganic materials 0.000 description 1
- 229910052684 Cerium Inorganic materials 0.000 description 1
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 description 1
- 229910004298 SiO 2 Inorganic materials 0.000 description 1
- FCUFAHVIZMPWGD-UHFFFAOYSA-N [O-][N+](=O)[Pt](N)(N)[N+]([O-])=O Chemical compound [O-][N+](=O)[Pt](N)(N)[N+]([O-])=O FCUFAHVIZMPWGD-UHFFFAOYSA-N 0.000 description 1
- 239000002250 absorbent Substances 0.000 description 1
- 230000002745 absorbent Effects 0.000 description 1
- 239000006096 absorbing agent Substances 0.000 description 1
- 230000001133 acceleration Effects 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 230000002411 adverse Effects 0.000 description 1
- 229910052782 aluminium Inorganic materials 0.000 description 1
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 1
- ITHZDDVSAWDQPZ-UHFFFAOYSA-L barium acetate Chemical compound [Ba+2].CC([O-])=O.CC([O-])=O ITHZDDVSAWDQPZ-UHFFFAOYSA-L 0.000 description 1
- 238000001354 calcination Methods 0.000 description 1
- 239000000969 carrier Substances 0.000 description 1
- CETPSERCERDGAM-UHFFFAOYSA-N ceric oxide Chemical compound O=[Ce]=O CETPSERCERDGAM-UHFFFAOYSA-N 0.000 description 1
- GWXLDORMOJMVQZ-UHFFFAOYSA-N cerium Chemical compound [Ce] GWXLDORMOJMVQZ-UHFFFAOYSA-N 0.000 description 1
- 229910000422 cerium(IV) oxide Inorganic materials 0.000 description 1
- UFMZWBIQTDUYBN-UHFFFAOYSA-N cobalt dinitrate Chemical compound [Co+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O UFMZWBIQTDUYBN-UHFFFAOYSA-N 0.000 description 1
- 229910001981 cobalt nitrate Inorganic materials 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- XTVVROIMIGLXTD-UHFFFAOYSA-N copper(II) nitrate Chemical compound [Cu+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O XTVVROIMIGLXTD-UHFFFAOYSA-N 0.000 description 1
- 229910052878 cordierite Inorganic materials 0.000 description 1
- JSKIRARMQDRGJZ-UHFFFAOYSA-N dimagnesium dioxido-bis[(1-oxido-3-oxo-2,4,6,8,9-pentaoxa-1,3-disila-5,7-dialuminabicyclo[3.3.1]nonan-7-yl)oxy]silane Chemical compound [Mg++].[Mg++].[O-][Si]([O-])(O[Al]1O[Al]2O[Si](=O)O[Si]([O-])(O1)O2)O[Al]1O[Al]2O[Si](=O)O[Si]([O-])(O1)O2 JSKIRARMQDRGJZ-UHFFFAOYSA-N 0.000 description 1
- 229910052675 erionite Inorganic materials 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 239000010419 fine particle Substances 0.000 description 1
- 125000004435 hydrogen atom Chemical group [H]* 0.000 description 1
- 229910010272 inorganic material Inorganic materials 0.000 description 1
- 239000011147 inorganic material Substances 0.000 description 1
- 229910052500 inorganic mineral Inorganic materials 0.000 description 1
- MVFCKEFYUDZOCX-UHFFFAOYSA-N iron(2+);dinitrate Chemical compound [Fe+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O MVFCKEFYUDZOCX-UHFFFAOYSA-N 0.000 description 1
- NZPIUJUFIFZSPW-UHFFFAOYSA-H lanthanum carbonate Chemical compound [La+3].[La+3].[O-]C([O-])=O.[O-]C([O-])=O.[O-]C([O-])=O NZPIUJUFIFZSPW-UHFFFAOYSA-H 0.000 description 1
- 239000000395 magnesium oxide Substances 0.000 description 1
- CPLXHLVBOLITMK-UHFFFAOYSA-N magnesium oxide Inorganic materials [Mg]=O CPLXHLVBOLITMK-UHFFFAOYSA-N 0.000 description 1
- 229910044991 metal oxide Inorganic materials 0.000 description 1
- 150000004706 metal oxides Chemical class 0.000 description 1
- 239000011707 mineral Substances 0.000 description 1
- 239000011812 mixed powder Substances 0.000 description 1
- 229910000069 nitrogen hydride Inorganic materials 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- GPNDARIEYHPYAY-UHFFFAOYSA-N palladium(ii) nitrate Chemical compound [Pd+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O GPNDARIEYHPYAY-UHFFFAOYSA-N 0.000 description 1
- 239000011148 porous material Substances 0.000 description 1
- 238000011144 upstream manufacturing Methods 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 1
- 229910001868 water Inorganic materials 0.000 description 1
- RUDFQVOCFDJEEF-UHFFFAOYSA-N yttrium(III) oxide Inorganic materials [O-2].[O-2].[O-2].[Y+3].[Y+3] RUDFQVOCFDJEEF-UHFFFAOYSA-N 0.000 description 1
Landscapes
- Catalysts (AREA)
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
Abstract
(57)【要約】
【目的】三元活性は従来と同等に維持しつつ、アンモニ
アの排出を抑制する。
【構成】互いに近傍に配置された第1多孔質担体及び固
体酸点をもつ第2多孔質担体と、少なくとも第1多孔質
担体に担持された貴金属と、第2多孔質担体に担持され
た少なくともニッケルと、からなることを特徴とする。
第1多孔質担体で生成したアンモニアは第2多孔質担体
の固体酸点に選択的に吸着され、近傍に存在するニッケ
ルによって窒素と水素に分解される。(57) [Summary] [Purpose] To suppress the emission of ammonia while maintaining the same ternary activity as before. A first porous carrier and a second porous carrier having solid acid points, which are arranged in the vicinity of each other, at least a noble metal supported on the first porous carrier, and at least a second porous carrier supported on the second porous carrier. It is characterized by being composed of nickel.
Ammonia generated on the first porous carrier is selectively adsorbed on the solid acid points of the second porous carrier and decomposed into nitrogen and hydrogen by nickel existing in the vicinity.
Description
【0001】[0001]
【産業上の利用分野】本発明は、自動車等の内燃機関か
ら排出される排ガス中に含まれる、炭化水素(HC)、
一酸化炭素(CO)、窒素酸化物(NOx)の三成分を
同時に浄化できる排ガス浄化用触媒に関し、さらに詳し
くは、NOxを還元浄化する際に発生する可能性のある
アンモニア(NH3 )をも同時に浄化できる排ガス浄化
用触媒に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to hydrocarbon (HC) contained in exhaust gas discharged from an internal combustion engine of an automobile,
The present invention relates to an exhaust gas purifying catalyst capable of purifying three components of carbon monoxide (CO) and nitrogen oxide (NOx) at the same time. More specifically, it also includes ammonia (NH 3 ) which may be generated during reduction purification of NOx. The present invention relates to an exhaust gas purification catalyst that can be purified at the same time.
【0002】[0002]
【従来の技術】従来より、自動車の排ガス浄化用触媒と
して、CO及びHCの酸化とNOxの還元とを同時に行
って排ガスを浄化する三元触媒が用いられている。この
ような三元触媒としては、例えばコージェライトなどの
耐熱性担体基材にγ−アルミナからなる多孔質の担体層
を形成し、その担体層にPt,Pd,Rhなどの貴金属
触媒を担持させたものが広く知られている。2. Description of the Related Art Conventionally, a three-way catalyst for purifying exhaust gas by simultaneously oxidizing CO and HC and reducing NOx has been used as a catalyst for purifying exhaust gas of automobiles. As such a three-way catalyst, for example, a porous carrier layer made of γ-alumina is formed on a heat resistant carrier substrate such as cordierite, and a precious metal catalyst such as Pt, Pd, Rh is supported on the carrier layer. Things are widely known.
【0003】例えば特開平2−107334号公報に
は、アルミニウム,セリウム,ニッケル及びバリウムの
金属酸化物からなる担体と、その担体に担持されたP
t,Pd及びRhの少なくとも一種と、からなる排ガス
浄化用触媒が開示されている。この排ガス浄化用触媒に
よれば、排ガス中のCO,HC及びNOxの浄化ととも
に、硫化水素(H2 S)の排出を阻止することができ
る。For example, Japanese Patent Laid-Open No. 2-107334 discloses a carrier made of a metal oxide of aluminum, cerium, nickel and barium, and P supported on the carrier.
An exhaust gas purification catalyst comprising at least one of t, Pd and Rh is disclosed. According to this exhaust gas purifying catalyst, it is possible to purify CO, HC and NOx in the exhaust gas and prevent the emission of hydrogen sulfide (H 2 S).
【0004】[0004]
【発明が解決しようとする課題】ところで従来の三元触
媒の使用に際しては、エンジンと排ガス処理系に酸素セ
ンサを含んだシステムが構築され、そのシステムは空燃
比(A/F)を化学量論点(ストイキ)近傍に制御して
排ガス中のCO,HC及びNOxを同時に浄化できるよ
うに設計されている。すなわち、酸素センサにより排ガ
ス中の酸素濃度を検出し、その検出値によりエンジンを
フィードバック制御することで、空燃比を常に化学量論
点近傍に制御できる仕組みになっている。By the way, when using the conventional three-way catalyst, a system including an oxygen sensor in the engine and the exhaust gas treatment system is constructed, and the system has an air-fuel ratio (A / F) as a stoichiometric point. It is designed so that CO, HC and NOx in the exhaust gas can be simultaneously purified by controlling the vicinity of (stoichiometric). That is, by detecting the oxygen concentration in the exhaust gas with an oxygen sensor and feedback-controlling the engine based on the detected value, the air-fuel ratio can always be controlled near the stoichiometric point.
【0005】ところが、市街地走行における頻繁な加速
・減速の繰り返しなど、エンジンの運転条件の変動によ
り空燃比が化学量論点からずれる場合がある。そして空
燃比(A/F)が化学量論点より大きい場合(リーン)
には、酸素が充分含まれるため排ガス組成は酸化性雰囲
気となり、空燃比(A/F)が化学量論点より小さい場
合(リッチ)には、燃料中のHCやCOが多く排ガス組
成は還元性雰囲気となる。However, there are cases where the air-fuel ratio deviates from the stoichiometric point due to fluctuations in engine operating conditions such as frequent repeated acceleration / deceleration during urban driving. And when the air-fuel ratio (A / F) is larger than the stoichiometric point (lean)
Contains a sufficient amount of oxygen, the exhaust gas composition becomes an oxidizing atmosphere, and when the air-fuel ratio (A / F) is smaller than the stoichiometric point (rich), HC and CO in the fuel are large and the exhaust gas composition is reducing. It becomes an atmosphere.
【0006】そして特に還元性雰囲気の著しい排ガスが
三元触媒に導入されると、排ガス中のNOxは還元され
るもののN2 とはならず、アンモニア(NH3 )が生成
して排出される恐れがあった。本発明はこのような事情
に鑑みてなされたものであり、三元活性は従来と同等に
維持しつつ、アンモニアの生成及び排出を抑制すること
を目的とする。When the exhaust gas having a remarkably reducing atmosphere is introduced into the three-way catalyst, NOx in the exhaust gas is reduced but does not become N 2 and ammonia (NH 3 ) may be produced and discharged. was there. The present invention has been made in view of such circumstances, and an object thereof is to suppress the production and discharge of ammonia while maintaining the ternary activity equivalent to that of the conventional one.
【0007】[0007]
【課題を解決するための手段】上記課題を解決する本発
明の排ガス浄化用触媒は、互いに近傍に配置された第1
多孔質担体及び固体酸点をもつ第2多孔質担体と、少な
くとも第1多孔質担体に担持された貴金属と、第2多孔
質担体に担持された少なくともニッケルと、からなるこ
とを特徴とする。The exhaust gas-purifying catalyst of the present invention for solving the above-mentioned problems is a first catalyst disposed in the vicinity of each other.
It is characterized by comprising a porous carrier and a second porous carrier having a solid acid point, a noble metal supported on at least the first porous carrier, and at least nickel supported on the second porous carrier.
【0008】また第2発明の排ガス浄化用触媒は、少な
くとも第1多孔質担体にはさらにセリウム酸化物が担持
されていることを特徴とする。第3発明の排ガス浄化用
触媒は、第2多孔質担体はゼオライトであることを特徴
とする。さらに第4発明の排ガス浄化用触媒は、固体酸
点を有する多孔質担体に貴金属とニッケルとが担持され
てなることを特徴とする。The exhaust gas purifying catalyst of the second invention is characterized in that at least the first porous carrier further carries cerium oxide. The exhaust gas-purifying catalyst of the third invention is characterized in that the second porous carrier is zeolite. Furthermore, the exhaust gas purifying catalyst of the fourth invention is characterized in that a precious metal and nickel are supported on a porous carrier having solid acid points.
【0009】[0009]
【作用】本第1〜第3発明の排ガス浄化用触媒では、少
なくとも第1多孔質担体に担持された貴金属の三元活性
により、排ガス中のCO及びHCが従来と同様に酸化浄
化されるとともに、NOxが還元浄化される。そして排
ガス組成が著しい還元性雰囲気にある場合には、NOx
が窒素ガス(N2 )とならずアンモニア(NH3 )が生
成する場合がある。しかし本発明の排ガス浄化用触媒で
は、アンモニアは第2多孔質担体の固体酸点に選択的に
吸着され、同じく第2多孔質担体に担持され近傍に存在
するニッケルによって窒素と水素に分解されるため、ア
ンモニアの排出が抑制される。In the exhaust gas purifying catalysts of the first to third inventions, CO and HC in the exhaust gas are oxidized and purified in the same manner as in the conventional case by at least the ternary activity of the noble metal supported on the first porous carrier. , NOx is reduced and purified. When the exhaust gas composition is in a remarkably reducing atmosphere, NOx
May not be nitrogen gas (N 2 ) and ammonia (NH 3 ) may be generated. However, in the exhaust gas purifying catalyst of the present invention, ammonia is selectively adsorbed on the solid acid points of the second porous carrier, and is decomposed into nitrogen and hydrogen by nickel which is also carried on the second porous carrier and is present in the vicinity. Therefore, the emission of ammonia is suppressed.
【0010】さらにセリウム酸化物が担持されている場
合には、セリウム酸化物は酸素を一時的に貯留する性質
をもつため、排ガス組成の雰囲気変動が緩和されて著し
い還元性雰囲気となるのが防止されるため、アンモニア
の生成自体が抑制される。そして第2多孔質担体がゼオ
ライトである場合には、均質な固体酸点が単位体積当た
りに多数存在するので、アンモニアを吸着する能力に特
に優れアンモニアの排出が一層抑制される。Further, when the cerium oxide is supported, the cerium oxide has a property of temporarily storing oxygen, so that it is possible to prevent the atmosphere variation of the exhaust gas composition from being relieved to form a remarkably reducing atmosphere. Therefore, the production of ammonia itself is suppressed. When the second porous carrier is zeolite, a large number of homogeneous solid acid points are present per unit volume, so that the ability to adsorb ammonia is particularly excellent and the emission of ammonia is further suppressed.
【0011】本第4発明の排ガス浄化用触媒では、固体
酸点を有する多孔質担体に貴金属とニッケルとが担持さ
れている。このため貴金属の三元活性により、排ガス中
のCO及びHCが従来と同様に酸化浄化されるととも
に、アンモニアが生成した場合には、そのアンモニアは
固体酸点に選択的に吸着され、貴金属近傍に存在するニ
ッケルによって効率良く窒素と水とに分解されるため、
アンモニアの排出が抑制される。In the exhaust gas purifying catalyst according to the fourth aspect of the present invention, the noble metal and nickel are supported on the porous carrier having solid acid points. Therefore, due to the ternary activity of the precious metal, CO and HC in the exhaust gas are oxidatively purified as in the conventional case, and when ammonia is produced, the ammonia is selectively adsorbed to the solid acid point and is near the precious metal. Since the existing nickel is efficiently decomposed into nitrogen and water,
Ammonia emission is suppressed.
【0012】[0012]
(発明の具体例)本第1〜第3発明において、第1多孔
質担体としては、アルミナ、シリカ、チタニア、ジルコ
ニアなどの高比表面積を有する耐火性無機酸化物が挙げ
られる。特に、高耐熱性で高比表面積の活性アルミナが
望ましい。Specific Examples of the Invention In the first to third inventions, examples of the first porous carrier include refractory inorganic oxides having a high specific surface area such as alumina, silica, titania, and zirconia. In particular, activated alumina having high heat resistance and high specific surface area is desirable.
【0013】本第1〜第4発明において、貴金属として
は、白金(Pt)、パラジウム(Pd)、ロジウム(R
h)の少なくとも一種が用いられる。この貴金属の担持
量は、第1多孔質担体に対して0.1重量%以上であ
り、好ましくは0.5〜20重量%である。貴金属の担
持量が0.1重量%より少ないと、CO及びHCの酸化
反応が低下するとともに、特に低温側におけるNOxの
還元反応が低下するので好ましくない。また20重量%
を超えて担持すると、効果が飽和して高価となる。In the first to fourth inventions, platinum (Pt), palladium (Pd), rhodium (R
At least one of h) is used. The amount of the noble metal supported is 0.1% by weight or more, preferably 0.5 to 20% by weight, based on the first porous carrier. When the supported amount of the noble metal is less than 0.1% by weight, the oxidation reaction of CO and HC is reduced, and the reduction reaction of NOx is reduced particularly on the low temperature side, which is not preferable. 20% by weight
If it is carried over, the effect is saturated and the cost becomes high.
【0014】本第1〜第3発明における固体酸点を有す
る第2多孔質担体及び本第4発明における固体酸点を有
する多孔質担体とは、ブレンステッド酸性(プロトンを
放つ)あるいはルイス酸性(電子対を受け取る)を有す
る無機酸化物をいい、例えばゼオライト、シリカ・アル
ミナ、シリカ・チタニア、シリカ・マグネシア、あるい
はゼオライト型無機物としてSAPO(シリコアルミノ
フォスフェート)などが例示される。中でもゼオライト
が特に好ましい。The second porous carrier having a solid acid point in the first to third inventions and the porous carrier having a solid acid point in the fourth invention are Bronsted acidic (proton releasing) or Lewis acidic ( An inorganic oxide having an electron pair) is included, and examples thereof include zeolite, silica-alumina, silica-titania, silica-magnesia, and zeolite-type inorganic materials such as SAPO (silicoaluminophosphate). Of these, zeolite is particularly preferable.
【0015】ゼオライトは一般式 Mx ・(Al
2 O3 )x ・(SiO2 )Y(Mは水素又はアルカリ金
属等)で示される特異な細孔構造を有する鉱物の総称で
あり、中でも耐熱性を有するシリカが多いものでシリカ
/アルミナ比(y/x)が10〜1000程度のものが
特に望ましい。シリカ/アルミナ比がこの範囲を外れる
と、固体酸点が少なくなったり酸強度が弱くなるため、
アンモニア吸着能が低下してアンモニアが排出され易く
なる。シリカ/アルミナ比(y/x)が10〜1000
程度のゼオライトとしては、ゼオライトβ,ZSM−5
などのペンタシル型ゼオライト、モルデナイト、エリオ
ナイト/オフレタイトなどが挙げられる。Zeolite has the general formula M x · (Al
2 O 3 ) x · (SiO 2 ) Y (M is hydrogen or alkali metal etc.) is a general term for minerals having a unique pore structure. Among them, there are many heat-resistant silicas and the silica / alumina ratio is high. It is particularly desirable that (y / x) is about 10 to 1000. If the silica / alumina ratio is out of this range, the number of solid acid points will decrease and the acid strength will decrease.
Ammonia adsorption capacity is lowered and ammonia is easily discharged. Silica / alumina ratio (y / x) is 10 to 1000
Zeolite β, ZSM-5
Examples include pentasil-type zeolite, mordenite, erionite / offretite, and the like.
【0016】本第1〜第3発明において第2多孔質担体
に担持されるニッケル又は本第4発明において多孔質担
体に担持されるニッケルの担持量は、触媒1L当たり
0.01〜1.0モルの範囲が望ましい。ニッケルの担
持量が0.01モル/Lより少ないとアンモニアの排出
を抑制することが困難となり、0.1モル/Lより多く
担持しても効果が飽和し高価になるだけである。The amount of nickel supported on the second porous carrier in the first to third inventions or nickel supported on the porous carrier in the fourth inventions is 0.01 to 1.0 per 1 L of the catalyst. A molar range is desirable. When the amount of nickel supported is less than 0.01 mol / L, it becomes difficult to suppress the emission of ammonia, and even when more than 0.1 mol / L is supported, the effect is saturated and the cost becomes high.
【0017】なお、第2多孔質担体には、ニッケルの他
に白金、ロジウム、パラジウムなどの貴金属がさらに担
持されていてもよい。また本第1〜第3発明の排ガス浄
化用触媒では、セリウム酸化物が少なくとも第1多孔質
担体に含有されていることが望ましく、本第4発明の排
ガス浄化用触媒では多孔質担体にさらにセリウム酸化物
が担持されていることが望ましい。このセリウム酸化物
の含有量は特に制限されないが、触媒1L当たり0.0
1〜3.0モルの範囲が適当である。0.01モル/L
より少ないと含有した効果が得られず、3.0モル/L
より多く含有しても、効果が飽和するとともに多孔質担
体量が相対的に少なくなって悪影響が現れる。In addition to nickel, the second porous carrier may further carry a noble metal such as platinum, rhodium or palladium. Further, in the exhaust gas purifying catalysts of the first to third inventions, it is desirable that at least the first porous carrier contains cerium oxide, and in the exhaust gas purifying catalyst of the fourth invention, the porous carrier further contains cerium oxide. It is desirable that the oxide is supported. The content of this cerium oxide is not particularly limited, but is 0.0 per 1 L of the catalyst.
A range of 1 to 3.0 mol is suitable. 0.01 mol / L
If it is less, the effect of inclusion cannot be obtained and 3.0 mol / L
Even if it is contained in a larger amount, the effect will be saturated and the amount of the porous carrier will be relatively small, resulting in an adverse effect.
【0018】また、本第1〜第3発明において、第1多
孔質担体と第2多孔質担体とは近傍に配置されている。
近傍とは、第1多孔質担体で発生したアンモニアを第2
多孔質担体で吸着・浄化するのを妨げないような距離を
いう。両担体の配置の形態としては、例えば、排ガス流
路前段に第1多孔質担体を、後段に第2多孔質担体を配
置する方法、あるいは、担体基材に第2多孔質担体を塗
布し、その第2多孔質担体層表面に第1多孔質担体をさ
らに塗布して配置する方法などが挙げられる。少なくと
も第1多孔質担体が第2多孔質担体より排ガス流路上流
側にあれば、特に限定されない。In the first to third inventions, the first porous carrier and the second porous carrier are arranged in the vicinity.
The vicinity means that the ammonia generated in the first porous carrier is the second
A distance that does not prevent adsorption and purification with a porous carrier. As the arrangement of both carriers, for example, a method of arranging the first porous carrier in the front stage of the exhaust gas flow channel and the second porous carrier in the rear stage, or applying the second porous carrier to the carrier substrate, Examples include a method in which the first porous carrier is further applied and arranged on the surface of the second porous carrier layer. There is no particular limitation as long as at least the first porous carrier is on the upstream side of the exhaust gas flow path with respect to the second porous carrier.
【0019】なお、特に好ましい配置形態として、第1
多孔質担体及び第2多孔質担体がそれぞれ微細な粒子で
均一に混合して配置されているのがよい。この場合に
は、第1多孔質担体で発生したアンモニアが第2多孔質
担体で最も効率良く吸着・浄化されるからである。本第
1〜第4発明の排ガス浄化用触媒には、さらにアルカリ
金属、アルカリ土類金属あるいは希土類元素などのNO
x吸収材を含有することも好ましい。これによりNOx
の浄化性能が一層向上する。またジルコニアやイットリ
アを含ませれば、セリウム酸化物の耐熱性を一層向上さ
せることができる。As a particularly preferable arrangement form, the first
It is preferable that the porous carrier and the second porous carrier are uniformly mixed and arranged with fine particles. This is because in this case, the ammonia generated in the first porous carrier is adsorbed and purified most efficiently in the second porous carrier. The exhaust gas purifying catalysts of the first to fourth inventions further include NO such as alkali metal, alkaline earth metal or rare earth element.
It is also preferable to contain x absorber. As a result, NOx
The purification performance of is further improved. If zirconia or yttria is included, the heat resistance of cerium oxide can be further improved.
【0020】本第1〜第3発明の排ガス浄化用触媒を製
造するには、浸漬法などで予めニッケルを担持した第2
多孔質担体と第1多孔質担体及び貴金属をスラリーとし
てモノリス基材などに被覆し焼成する方法、予めニッケ
ルを担持した第2多孔質担体と第1多孔質担体をスラリ
ー化してモノリス基材などに被覆し焼成した後に貴金属
を浸漬法で担持する方法、などの方法がある。In order to produce the exhaust gas purifying catalysts of the first to third inventions, the second catalyst preliminarily loaded with nickel by an immersion method or the like is used.
A method of coating a porous carrier, a first porous carrier, and a noble metal on a monolith substrate as a slurry and firing the slurry, or a slurry of the second porous carrier and the first porous carrier carrying nickel in advance to form a monolith substrate, etc. There is a method of supporting a noble metal by a dipping method after coating and firing.
【0021】本第4発明の排ガス浄化用触媒を製造する
には、浸漬法などでニッケルを担持した多孔質担体及び
貴金属をスラリーとしてモノリス基材などに被覆し焼成
する方法、ニッケルを担持した多孔質担体をスラリー化
してモノリス基材などに被覆し焼成した後に貴金属を浸
漬法で担持する方法、などの方法がある。以下、実施例
により具体的に説明する。 (実施例1)γ−アルミナ粉末120gに対し、炭酸ラ
ンタン粉末0.1モル、セリウム酸化物粉末0.3モル
を混合した混合粉末を、Pdが3g含まれた硝酸パラジ
ウム水溶液に浸漬し、蒸発乾固した後110℃で1昼夜
乾燥し、さらに大気中600℃で3時間焼成処理を施し
た。得られたPd担持粉末を0.2モルの酢酸バリウム
を溶解させた水溶液に浸漬し、蒸発乾固した後110℃
で1昼夜乾燥し、さらに大気中600℃で3時間焼成処
理を施して、Pd/バリウム/セリア/ランタン/アル
ミナからなる第1粉末を調製した。In order to produce the exhaust gas purifying catalyst of the fourth aspect of the present invention, a porous carrier supporting nickel by a dipping method or the like, a method of coating a monolith substrate or the like with a slurry of a noble metal as a slurry, and firing it, a porous supporting nickel There is a method in which a porous carrier is made into a slurry, coated on a monolith substrate, etc., baked, and then a precious metal is supported by an immersion method. Hereinafter, a specific description will be given with reference to examples. (Example 1) 120 g of γ-alumina powder was mixed with 0.1 mol of lanthanum carbonate powder and 0.3 mol of cerium oxide powder, and the mixed powder was immersed in an aqueous palladium nitrate solution containing 3 g of Pd and evaporated. After being dried and solidified, it was dried at 110 ° C. for one day, and further subjected to baking treatment at 600 ° C. for 3 hours in the atmosphere. The obtained Pd-supported powder was immersed in an aqueous solution in which 0.2 mol of barium acetate was dissolved, evaporated to dryness, and then 110 ° C.
After being dried for 1 day and 2 days, and further subjected to a calcination treatment in the atmosphere at 600 ° C. for 3 hours, a first powder composed of Pd / barium / ceria / lanthanum / alumina was prepared.
【0022】この第1粉末は、第1多孔質担体としての
γ−アルミナに貴金属としてPdが担持され、さらにセ
リウム酸化物を含んでいる。そしてさらにNOx吸収剤
としての希土類元素であるランタンとアルカリ土類金属
であるバリウムを含んでいる。一方、所定濃度の硝酸ニ
ッケル水溶液に市販のH型ZSM−5ゼオライト(シリ
カ/アルミナ比=40)50gを浸漬させ、その後60
0℃で3時間焼成処理することで、ニッケルを10重量
%担持した第2粉末を調製した。この第2粉末は、第2
多孔質担体としてのゼオライトにニッケルが担持された
構成である。The first powder has γ-alumina as the first porous carrier on which Pd is carried as a noble metal and further contains cerium oxide. Further, it contains lanthanum which is a rare earth element as an NOx absorbent and barium which is an alkaline earth metal. On the other hand, 50 g of a commercially available H-type ZSM-5 zeolite (silica / alumina ratio = 40) was immersed in an aqueous nickel nitrate solution of a predetermined concentration, and then 60
A second powder carrying 10% by weight of nickel was prepared by performing a baking treatment at 0 ° C. for 3 hours. This second powder is the second
This is a structure in which nickel is supported on zeolite as a porous carrier.
【0023】次に、第1粉末と第2粉末を混合し、圧粉
成形した後0.5〜1mmのペレット状にして、実施例
1の排ガス浄化用触媒を調製した。第1粉末と第2粉末
の混合割合は、アルミナ120gに対してニッケルが
0.1モルとなる比率である。 (比較例1)実施例1で調製した第1粉末のみを圧粉成
形した後ペレット状として、比較例1の排ガス浄化用触
媒とした。当然ながらニッケルは含まれていない。 (比較例2)実施例1で調製した第1粉末に市販の酸化
ニッケル粉末を所定量混合した粉末を圧粉成型した後ペ
レット状として、比較例2の排ガス浄化用触媒とした。
酸化ニッケル粉末の混合割合は、実施例1と同様にアル
ミナ120gに対してニッケルが0.1モルとなる比率
である。 (比較例3)ゼオライトの代わりにシリカ粉末を用いて
第2粉末を調製したこと以外は実施例1と同様にして、
比較例3の排ガス浄化用触媒を調製した。第1粉末とシ
リカ/ニッケルよりなる第2粉末の混合割合は、実施例
1と同様にアルミナ120gに対してニッケルが0.1
モルとなる比率である。 (比較例4)ゼオライトの代わりにアルミナ粉末を用い
て第2粉末を調製したこと以外は実施例1と同様にし
て、比較例4の排ガス浄化用触媒を調製した。第1粉末
とアルミナ/ニッケルよりなる第2粉末の混合割合は、
実施例1と同様に第1粉末のアルミナ120gに対して
ニッケルが0.1モルとなる比率である。 (実施例2)γ−アルミナ粉末を所定濃度のジニトロジ
アミノ白金水溶液に浸漬し、蒸発乾固した後110℃で
1昼夜乾燥し、さらに大気中600℃で3時間焼成処理
を施して、Pt/アルミナからなる第1粉末を調製し
た。Ptの担持量は4.0重量%である。Next, the first powder and the second powder were mixed, pressed and molded into pellets of 0.5 to 1 mm to prepare an exhaust gas purifying catalyst of Example 1. The mixing ratio of the first powder and the second powder is such that nickel is 0.1 mol with respect to 120 g of alumina. (Comparative Example 1) Only the first powder prepared in Example 1 was compacted into a pellet and used as an exhaust gas purifying catalyst of Comparative Example 1. Of course, nickel is not included. (Comparative Example 2) A powder obtained by mixing a predetermined amount of commercially available nickel oxide powder with the first powder prepared in Example 1 was compacted and formed into pellets to obtain an exhaust gas purifying catalyst of Comparative Example 2.
The mixing ratio of the nickel oxide powder is a ratio in which nickel is 0.1 mol with respect to 120 g of alumina as in Example 1. (Comparative Example 3) In the same manner as in Example 1 except that silica powder was used instead of zeolite to prepare the second powder,
An exhaust gas purifying catalyst of Comparative Example 3 was prepared. The mixing ratio of the first powder and the second powder composed of silica / nickel is, as in Example 1, 120 g of alumina and 0.1% of nickel.
It is the ratio of molar. (Comparative Example 4) An exhaust gas purifying catalyst of Comparative Example 4 was prepared in the same manner as in Example 1 except that the second powder was prepared by using alumina powder instead of zeolite. The mixing ratio of the first powder and the second powder of alumina / nickel is
As in Example 1, the ratio is such that nickel is 0.1 mol with respect to 120 g of the first powder alumina. (Example 2) γ-alumina powder was immersed in an aqueous dinitrodiaminoplatinum solution having a predetermined concentration, evaporated to dryness, dried at 110 ° C. for one day and then calcined in the atmosphere at 600 ° C. for 3 hours to obtain Pt / A first powder made of alumina was prepared. The supported amount of Pt is 4.0% by weight.
【0024】一方、実施例1と同様にして第2粉末を調
製した。ゼオライトへのニッケルの担持量は、ゼオライ
ト96gに対して金属ニッケル換算で2gの割合とし
た。そして第1粉末と第2粉末を、重量比でゼオライト
/アルミナ=4/1となる割合で混合し、実施例1と同
様にしてペレット状の実施例2の排ガス浄化用触媒を調
製した。 (実施例3)第2粉末におけるニッケルとゼオライトの
比率が、重量比でニッケル/ゼオライト=5/96であ
ること以外は実施例2と同様にして、実施例3の排ガス
浄化用触媒を調製した。 (比較例5)実施例2と同様のPt/アルミナからなる
第1粉末とゼオライトのみからなる第2粉末とを混合し
圧粉成型した後ペレット状として、比較例5の排ガス浄
化用触媒とした。第1粉末と第2粉末の混合割合は、重
量比でゼオライト/アルミナ=4/1である。 (比較例6)実施例2と同様のPt/アルミナからなる
第1粉末とアルミナのみからなる第2粉末とを混合し圧
粉成型した後ペレット状として、比較例6の排ガス浄化
用触媒とした。第1粉末と第2粉末の混合割合は、重量
比で4/1である。 (比較例7)硝酸ニッケル水溶液の代わりに硝酸鉄水溶
液を用いたこと以外は実施例1と同様にして第2粉末を
調製し、実施例2と同様の第1粉末とともに圧粉成型し
た後ペレット状として、比較例7の排ガス浄化用触媒と
した。なおゼオライトへの鉄の担持割合は、重量比で鉄
/ゼオライト=2/96であり、第1粉末と第2粉末の
混合割合は、重量比でゼオライト/アルミナ=4/1で
ある。 (比較例8)硝酸ニッケル水溶液の代わりに硝酸銅水溶
液を用いたこと以外は実施例1と同様にして第2粉末を
調製し、実施例2と同様の第1粉末とともに圧粉成型し
た後ペレット状として、比較例8の排ガス浄化用触媒と
した。なおゼオライトへの銅の担持割合は、重量比で銅
/ゼオライト=2/96であり、第1粉末と第2粉末の
混合割合は、重量比でゼオライト/アルミナ=4/1で
ある。 (比較例9)硝酸ニッケル水溶液の代わりに硝酸コバル
ト水溶液を用いたこと以外は実施例1と同様にして第2
粉末を調製し、実施例2と同様の第1粉末とともに圧粉
成型した後ペレット状として、比較例9の排ガス浄化用
触媒とした。なおゼオライトへのコバルトの担持割合
は、重量比でコバルト/ゼオライト=2/96であり、
第1粉末と第2粉末の混合割合は、重量比でゼオライト
/アルミナ=4/1である。 (評価試験1)実施例1と比較例1〜4の各触媒につい
て、固定床流通型反応装置を用い以下の条件にて排気モ
デルガスの浄化性能を測定した。On the other hand, a second powder was prepared in the same manner as in Example 1. The amount of nickel supported on the zeolite was 2 g in terms of metallic nickel with respect to 96 g of zeolite. Then, the first powder and the second powder were mixed in a weight ratio of zeolite / alumina = 4/1, and a pellet-shaped exhaust gas purifying catalyst of Example 2 was prepared in the same manner as in Example 1. (Example 3) An exhaust gas purifying catalyst of Example 3 was prepared in the same manner as in Example 2 except that the weight ratio of nickel to zeolite in the second powder was nickel / zeolite = 5/96. . (Comparative Example 5) A first powder made of Pt / alumina as in Example 2 and a second powder made of only zeolite were mixed and compacted into a pellet, which was used as an exhaust gas purifying catalyst of Comparative Example 5. . The mixing ratio of the first powder and the second powder is zeolite / alumina = 4/1 by weight. (Comparative Example 6) The same Pt / alumina powder as in Example 2 and a second powder made of alumina alone were mixed and compacted into a pellet, which was used as the exhaust gas purifying catalyst of Comparative Example 6. . The mixing ratio of the first powder and the second powder is 4/1 by weight. (Comparative Example 7) A second powder was prepared in the same manner as in Example 1 except that an iron nitrate aqueous solution was used instead of the nickel nitrate aqueous solution, and the second powder was compacted together with the first powder as in Example 2 and then pelletized. As a condition, the exhaust gas-purifying catalyst of Comparative Example 7 was used. The weight ratio of iron supported on the zeolite was iron / zeolite = 2/96, and the weight ratio of the first powder and the second powder was zeolite / alumina = 4/1. (Comparative Example 8) A second powder was prepared in the same manner as in Example 1 except that a copper nitrate aqueous solution was used in place of the nickel nitrate aqueous solution, and the second powder was compacted together with the same first powder as in Example 2 and then pelletized. As a condition, the exhaust gas-purifying catalyst of Comparative Example 8 was used. The weight ratio of copper supported on the zeolite was copper / zeolite = 2/96, and the weight ratio of the first powder and the second powder was zeolite / alumina = 4/1. (Comparative Example 9) Second example similar to Example 1 except that an aqueous solution of cobalt nitrate was used instead of the aqueous solution of nickel nitrate.
A powder was prepared, pressed and molded with the same first powder as in Example 2, and then pelletized to obtain an exhaust gas purifying catalyst of Comparative Example 9. The ratio of cobalt supported on the zeolite was cobalt / zeolite = 2/96 by weight,
The mixing ratio of the first powder and the second powder is zeolite / alumina = 4/1 by weight. (Evaluation Test 1) With respect to each of the catalysts of Example 1 and Comparative Examples 1 to 4, the purification performance of the exhaust model gas was measured under the following conditions using a fixed bed flow reactor.
【0025】排気モデルガス温度:300℃ 空間速度(SV) :5万/hr 空燃比 :λ=0.96(A/F=14.0
相当) なお、λ=0.96の排気モデルガス組成は、表1に示
すとおりである。Exhaust model gas temperature: 300 ° C. space velocity (SV): 50,000 / hr air-fuel ratio: λ = 0.96 (A / F = 14.0)
Equivalent) Note that the exhaust model gas composition of λ = 0.96 is as shown in Table 1.
【0026】[0026]
【表1】 浄化性能は、NO,CO及びHCの浄化率を測定すると
ともに、排出されたアンモニアの量をそれぞれ測定し比
較例1の触媒のアンモニア排出量を基準としてアンモニ
ア低減率を算出した。それぞれの結果を表2に示す。[Table 1] Regarding the purification performance, the purification rates of NO, CO, and HC were measured, the amounts of ammonia discharged were measured, and the ammonia reduction rate was calculated based on the ammonia emissions of the catalyst of Comparative Example 1. The respective results are shown in Table 2.
【0027】[0027]
【表2】 表2より、実施例1の排ガス浄化用触媒は比較例と同等
の三元触媒活性をもち、しかも比較例に比べてアンモニ
ア低減率が著しく高いことがわかる。これはゼオライト
にニッケルを担持した第2粉末をもつことに起因してい
ることが明らかであり、ゼオライトとニッケルの共存に
よる効果であることが明らかである。 (評価試験2)また、実施例2〜3及び比較例5〜9の
各触媒について、固定床流通型反応装置を用い以下の条
件にて排気モデルガスの浄化性能を測定した。[Table 2] From Table 2, it can be seen that the exhaust gas-purifying catalyst of Example 1 has the same three-way catalytic activity as that of the comparative example, and the ammonia reduction rate is remarkably higher than that of the comparative example. It is clear that this is due to the fact that the zeolite has the second powder in which nickel is supported, and it is clear that this is an effect due to the coexistence of zeolite and nickel. (Evaluation Test 2) With respect to each of the catalysts of Examples 2 to 3 and Comparative Examples 5 to 9, the exhaust model gas purification performance was measured under the following conditions using a fixed bed flow reactor.
【0028】排気モデルガス温度:400℃ 空間速度(SV) :5万/hr 空燃比 :λ=0.98(A/F=14.3
相当) なお、λ=0.98の排気モデルガス組成は、表3に示
すとおりである。Exhaust model gas temperature: 400 ° C. Space velocity (SV): 50,000 / hr Air-fuel ratio: λ = 0.98 (A / F = 14.3)
Equivalent) Note that the exhaust model gas composition of λ = 0.98 is as shown in Table 3.
【0029】[0029]
【表3】 浄化性能は、NO,CO及びHCの浄化率を測定すると
ともに、排出されたアンモニアの量と窒素ガスの量を測
定してそれぞれの生成率を算出した。それぞれの結果を
図1及び図2に示す。なお、各触媒の構成を表4に示
す。[Table 3] As for the purification performance, the production rates of NO, CO and HC were measured, and the production rates were calculated by measuring the amounts of discharged ammonia and nitrogen gas. The respective results are shown in FIGS. 1 and 2. The constitution of each catalyst is shown in Table 4.
【0030】[0030]
【表4】 図1より、λ=0.98という還元性雰囲気において
も、実施例の各触媒は比較例に勝るとも劣らない三元触
媒活性を有していることが明らかである。また図2よ
り、λ=0.98という還元性雰囲気においても、実施
例の触媒は比較例に比べてN2 生成率が高くかつNH3
生成率が低くなっており、これはゼオライトにNiを担
持したことによる効果であることが明らかである。また
実施例2の方が実施例1より良い結果を示し、この実験
の範囲であればNiが多い方が良いことも分かる。[Table 4] From FIG. 1, it is clear that even in a reducing atmosphere of λ = 0.98, each catalyst of Examples has a three-way catalytic activity comparable to that of Comparative Examples. Further, from FIG. 2, even in the reducing atmosphere of λ = 0.98, the catalyst of the example has a higher N 2 production rate and NH 3 production than the comparative example.
The production rate is low, and it is clear that this is the effect of supporting Ni on the zeolite. In addition, Example 2 shows better results than Example 1, and it can be seen that the larger the amount of Ni, the better in the range of this experiment.
【0031】[0031]
【発明の効果】すなわち本発明の排ガス浄化用触媒によ
れば、従来と同等の三元浄化活性を維持しつつ、還元性
雰囲気の排ガスを浄化する際におけるアンモニアの生成
を防止できるとともに、万一アンモニアが生成しても吸
着・分解して浄化されるので、アンモニアの排出が抑制
される。[Effects of the Invention] That is, according to the catalyst for purifying exhaust gas of the present invention, it is possible to prevent generation of ammonia when purifying exhaust gas in a reducing atmosphere while maintaining the same three-way purification activity as conventional ones. Even if ammonia is produced, it is adsorbed / decomposed and purified, so that the emission of ammonia is suppressed.
【図1】実施例と比較例の排ガス浄化用触媒の浄化率を
示す棒グラフである。FIG. 1 is a bar graph showing purification rates of exhaust gas-purifying catalysts of Examples and Comparative Examples.
【図2】実施例と比較例の排ガス浄化用触媒の、NO浄
化率とNH3 及びN 2 の生成率を示す棒グラフである。FIG. 2 shows NO purification of exhaust gas purifying catalysts of Examples and Comparative Examples.
Rate and NH3And N 23 is a bar graph showing the generation rate of.
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 B01D 53/36 104 A ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI technical display location B01D 53/36 104 A
Claims (4)
及び固体酸点をもつ第2多孔質担体と、少なくとも該第
1多孔質担体に担持された貴金属と、該第2多孔質担体
に担持された少なくともニッケルと、からなることを特
徴とする排ガス浄化用触媒。1. A first porous carrier and a second porous carrier having solid acid points, which are disposed in the vicinity of each other, a noble metal supported on at least the first porous carrier, and the second porous carrier. An exhaust gas-purifying catalyst comprising at least nickel supported.
リウム酸化物が担持されていることを特徴とする請求項
1記載の排ガス浄化用触媒。2. The exhaust gas-purifying catalyst according to claim 1, wherein at least the first porous carrier further carries cerium oxide.
項1記載の排ガス浄化用触媒。3. The exhaust gas purifying catalyst according to claim 1, wherein the second porous carrier is zeolite.
ニッケルとが担持されてなることを特徴とする排ガス浄
化用触媒。4. An exhaust gas purifying catalyst, characterized in that a precious metal and nickel are supported on a porous carrier having solid acid points.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP6211548A JPH0871424A (en) | 1994-09-05 | 1994-09-05 | Exhaust gas purification catalyst |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP6211548A JPH0871424A (en) | 1994-09-05 | 1994-09-05 | Exhaust gas purification catalyst |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH0871424A true JPH0871424A (en) | 1996-03-19 |
Family
ID=16607648
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP6211548A Pending JPH0871424A (en) | 1994-09-05 | 1994-09-05 | Exhaust gas purification catalyst |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0871424A (en) |
Cited By (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO1998047605A1 (en) * | 1997-04-23 | 1998-10-29 | Toyota Jidosha Kabushiki Kaisha | Exhaust gas purification method and exhaust gas purification catalyst |
| JP2002045701A (en) * | 2000-08-08 | 2002-02-12 | Cataler Corp | Catalyst for purifying exhaust gas |
| WO2009041028A1 (en) * | 2007-09-27 | 2009-04-02 | Yamaha Hatsudoki Kabushiki Kaisha | Straddle riding-type vehicle |
| JP2010284640A (en) * | 2009-05-12 | 2010-12-24 | Central Res Inst Of Electric Power Ind | Ammonia decomposition catalyst |
| KR20140035982A (en) * | 2011-06-01 | 2014-03-24 | 존슨 맛쎄이 퍼블릭 리미티드 컴파니 | Cold start catalyst and its use in exhaust systems |
-
1994
- 1994-09-05 JP JP6211548A patent/JPH0871424A/en active Pending
Cited By (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO1998047605A1 (en) * | 1997-04-23 | 1998-10-29 | Toyota Jidosha Kabushiki Kaisha | Exhaust gas purification method and exhaust gas purification catalyst |
| US6191061B1 (en) | 1997-04-23 | 2001-02-20 | Toyota Jidosha Kabushiki Kaisha | Method of purifying exhaust gas and catalyst for purifying exhaust gas |
| JP2002045701A (en) * | 2000-08-08 | 2002-02-12 | Cataler Corp | Catalyst for purifying exhaust gas |
| WO2009041028A1 (en) * | 2007-09-27 | 2009-04-02 | Yamaha Hatsudoki Kabushiki Kaisha | Straddle riding-type vehicle |
| JP2010284640A (en) * | 2009-05-12 | 2010-12-24 | Central Res Inst Of Electric Power Ind | Ammonia decomposition catalyst |
| KR20140035982A (en) * | 2011-06-01 | 2014-03-24 | 존슨 맛쎄이 퍼블릭 리미티드 컴파니 | Cold start catalyst and its use in exhaust systems |
| JP2014519975A (en) * | 2011-06-01 | 2014-08-21 | ジョンソン、マッセイ、パブリック、リミテッド、カンパニー | Cold start catalyst and its use in exhaust systems |
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