JPH1157484A - Exhaust gas cleaning catalyst and its use - Google Patents
Exhaust gas cleaning catalyst and its useInfo
- Publication number
- JPH1157484A JPH1157484A JP9214330A JP21433097A JPH1157484A JP H1157484 A JPH1157484 A JP H1157484A JP 9214330 A JP9214330 A JP 9214330A JP 21433097 A JP21433097 A JP 21433097A JP H1157484 A JPH1157484 A JP H1157484A
- Authority
- JP
- Japan
- Prior art keywords
- catalyst
- exhaust gas
- alumina
- noble metal
- gas purifying
- 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.)
- Withdrawn
Links
- 239000003054 catalyst Substances 0.000 title claims abstract description 87
- 238000004140 cleaning Methods 0.000 title abstract 7
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 claims abstract description 25
- BASFCYQUMIYNBI-UHFFFAOYSA-N platinum Chemical compound [Pt] BASFCYQUMIYNBI-UHFFFAOYSA-N 0.000 claims abstract description 25
- 229910000510 noble metal Inorganic materials 0.000 claims abstract description 17
- KDLHZDBZIXYQEI-UHFFFAOYSA-N Palladium Chemical compound [Pd] KDLHZDBZIXYQEI-UHFFFAOYSA-N 0.000 claims abstract description 15
- 238000000746 purification Methods 0.000 claims abstract description 14
- 238000000034 method Methods 0.000 claims abstract description 12
- 239000010948 rhodium Substances 0.000 claims abstract description 12
- 239000002245 particle Substances 0.000 claims abstract description 9
- 229910052697 platinum Inorganic materials 0.000 claims abstract description 9
- 229910052703 rhodium Inorganic materials 0.000 claims abstract description 9
- 239000011148 porous material Substances 0.000 claims abstract description 8
- 239000000446 fuel Substances 0.000 claims abstract description 7
- 229910052763 palladium Inorganic materials 0.000 claims abstract description 7
- 229910052741 iridium Inorganic materials 0.000 claims abstract description 6
- GKOZUEZYRPOHIO-UHFFFAOYSA-N iridium atom Chemical compound [Ir] GKOZUEZYRPOHIO-UHFFFAOYSA-N 0.000 claims abstract description 6
- MHOVAHRLVXNVSD-UHFFFAOYSA-N rhodium atom Chemical compound [Rh] MHOVAHRLVXNVSD-UHFFFAOYSA-N 0.000 claims abstract description 6
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 claims description 29
- 229910021536 Zeolite Inorganic materials 0.000 claims description 28
- 239000010457 zeolite Substances 0.000 claims description 28
- 230000000694 effects Effects 0.000 abstract description 16
- 239000007789 gas Substances 0.000 description 40
- 239000000843 powder Substances 0.000 description 25
- 239000007864 aqueous solution Substances 0.000 description 11
- 239000002002 slurry Substances 0.000 description 11
- 238000006243 chemical reaction Methods 0.000 description 8
- 238000011156 evaluation Methods 0.000 description 7
- 230000000052 comparative effect Effects 0.000 description 6
- 239000007788 liquid Substances 0.000 description 6
- 230000002776 aggregation Effects 0.000 description 4
- 229910052878 cordierite Inorganic materials 0.000 description 4
- 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 4
- 239000010410 layer Substances 0.000 description 4
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 4
- 229910002651 NO3 Inorganic materials 0.000 description 3
- NHNBFGGVMKEFGY-UHFFFAOYSA-N Nitrate Chemical compound [O-][N+]([O-])=O NHNBFGGVMKEFGY-UHFFFAOYSA-N 0.000 description 3
- 238000010521 absorption reaction Methods 0.000 description 3
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 3
- 238000010298 pulverizing process Methods 0.000 description 3
- RMAQACBXLXPBSY-UHFFFAOYSA-N silicic acid Chemical compound O[Si](O)(O)O RMAQACBXLXPBSY-UHFFFAOYSA-N 0.000 description 3
- 239000007787 solid Substances 0.000 description 3
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 2
- 238000005054 agglomeration Methods 0.000 description 2
- 238000004220 aggregation Methods 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- 229910002091 carbon monoxide Inorganic materials 0.000 description 2
- 230000003197 catalytic effect Effects 0.000 description 2
- 238000009792 diffusion process Methods 0.000 description 2
- 238000006073 displacement reaction Methods 0.000 description 2
- 229930195733 hydrocarbon Natural products 0.000 description 2
- 150000002430 hydrocarbons Chemical class 0.000 description 2
- 238000005342 ion exchange Methods 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 239000002994 raw material Substances 0.000 description 2
- 238000001179 sorption measurement Methods 0.000 description 2
- 239000000758 substrate Substances 0.000 description 2
- 229910052684 Cerium Inorganic materials 0.000 description 1
- 229910052779 Neodymium Inorganic materials 0.000 description 1
- 229910052772 Samarium Inorganic materials 0.000 description 1
- QCWXUUIWCKQGHC-UHFFFAOYSA-N Zirconium Chemical compound [Zr] QCWXUUIWCKQGHC-UHFFFAOYSA-N 0.000 description 1
- 150000001242 acetic acid derivatives Chemical class 0.000 description 1
- 150000003863 ammonium salts Chemical class 0.000 description 1
- 229910052788 barium Inorganic materials 0.000 description 1
- DSAJWYNOEDNPEQ-UHFFFAOYSA-N barium atom Chemical compound [Ba] DSAJWYNOEDNPEQ-UHFFFAOYSA-N 0.000 description 1
- 238000001354 calcination Methods 0.000 description 1
- 150000004649 carbonic acid derivatives Chemical class 0.000 description 1
- 239000000969 carrier Substances 0.000 description 1
- 230000015556 catabolic process Effects 0.000 description 1
- 239000000919 ceramic Substances 0.000 description 1
- ZMIGMASIKSOYAM-UHFFFAOYSA-N cerium Chemical compound [Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce][Ce] ZMIGMASIKSOYAM-UHFFFAOYSA-N 0.000 description 1
- 239000011248 coating agent Substances 0.000 description 1
- 239000011247 coating layer Substances 0.000 description 1
- 238000000576 coating method Methods 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 238000006731 degradation reaction Methods 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 238000001704 evaporation Methods 0.000 description 1
- 230000008020 evaporation Effects 0.000 description 1
- 229910001657 ferrierite group Inorganic materials 0.000 description 1
- 150000004820 halides Chemical class 0.000 description 1
- 238000005470 impregnation Methods 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 229910052746 lanthanum Inorganic materials 0.000 description 1
- FZLIPJUXYLNCLC-UHFFFAOYSA-N lanthanum atom Chemical compound [La] FZLIPJUXYLNCLC-UHFFFAOYSA-N 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 239000007769 metal material Substances 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 239000002808 molecular sieve Substances 0.000 description 1
- QEFYFXOXNSNQGX-UHFFFAOYSA-N neodymium atom Chemical compound [Nd] QEFYFXOXNSNQGX-UHFFFAOYSA-N 0.000 description 1
- 150000002823 nitrates Chemical class 0.000 description 1
- 239000003208 petroleum Substances 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 229910052761 rare earth metal Inorganic materials 0.000 description 1
- 239000011819 refractory material Substances 0.000 description 1
- KZUNJOHGWZRPMI-UHFFFAOYSA-N samarium atom Chemical compound [Sm] KZUNJOHGWZRPMI-UHFFFAOYSA-N 0.000 description 1
- URGAHOPLAPQHLN-UHFFFAOYSA-N sodium aluminosilicate Chemical compound [Na+].[Al+3].[O-][Si]([O-])=O.[O-][Si]([O-])=O URGAHOPLAPQHLN-UHFFFAOYSA-N 0.000 description 1
- 229910001220 stainless steel Inorganic materials 0.000 description 1
- 229910052712 strontium Inorganic materials 0.000 description 1
- CIOAGBVUUVVLOB-UHFFFAOYSA-N strontium atom Chemical compound [Sr] CIOAGBVUUVVLOB-UHFFFAOYSA-N 0.000 description 1
- 238000010792 warming Methods 0.000 description 1
- 229910052726 zirconium Inorganic materials 0.000 description 1
Landscapes
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
- Catalysts (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は、ガソリン自動車、
ディーゼル自動車等の内燃機関から排出される排気ガス
中の炭化水素(HC)、一酸化炭素(CO)および窒素
酸化物(NOx )を浄化する排気ガス浄化用触媒及びそ
の使用方法に関し、特に酸素過剰雰囲気下でのNOx の
浄化性能に優れる排気ガス浄化用触媒及びその使用方法
に関する。[0001] The present invention relates to a gasoline-powered vehicle,
The present invention relates to an exhaust gas purifying catalyst for purifying hydrocarbons (HC), carbon monoxide (CO) and nitrogen oxides (NO x ) in exhaust gas discharged from an internal combustion engine such as a diesel vehicle and a method of using the same, and particularly to oxygen. exhaust gas purifying catalyst excellent in purification performance of the NO x under rich atmosphere and the use thereof.
【0002】[0002]
【従来の技術】近年、石油資源の枯渇問題および地球温
暖化問題の関点から、低燃費自動車の実現が期待されて
おり、特にガソリン自動車に対しては希薄燃焼自動車の
開発が望まれている。希薄燃焼自動車においては、希薄
燃焼走行時の排気ガス雰囲気は、理論空燃状態(以下、
「ストイキ状態」と称す)に比べて酸素過剰雰囲気(以
下、「リーン雰囲気」と称す)となる。リーン雰囲気に
おいて、従来の三元触媒を適応させた場合には、過剰な
酸素の影響からNOx 浄化作用が不十分となるという問
題があった。このためリーン雰囲気下においてもNOx
を浄化できる触媒の開発が望まれていた。2. Description of the Related Art In recent years, in view of the problem of depletion of petroleum resources and the problem of global warming, realization of low fuel consumption vehicles is expected, and development of lean burn vehicles is particularly desired for gasoline vehicles. . In lean-burn vehicles, the exhaust gas atmosphere during lean-burn operation is based on the theoretical air-fuel condition
An oxygen-excess atmosphere (hereinafter, referred to as a “lean atmosphere”) as compared to “stoichiometric state”. In a lean atmosphere, when adapted to a conventional three-way catalyst, NO x purification action from the effects of excess oxygen is disadvantageously insufficient. For this reason, NO x
There has been a demand for the development of a catalyst that can purify methane.
【0003】従来より、リーン雰囲気下におけるNOx
浄化性能を向上させる触媒は種々提案されており、例え
ば特開平1−135541号公報には、Pt等の貴金属
をゼオライトに担持した触媒が提案されている。Conventionally, NO x in a lean atmosphere has been
Various catalysts for improving the purification performance have been proposed. For example, JP-A-1-135541 proposes a catalyst in which a noble metal such as Pt is supported on zeolite.
【0004】前記排気ガス浄化用触媒中におけるゼオラ
イトは、ゼオライトの有する分子ふるいの性質が活性種
である貴金属上へのガスの吸着に影響を及ぼし、NOx
浄化反応を促進するものである。しかしながら、上記従
来のNOx 浄化触媒は、担持基材として用いるゼオライ
トが熱や水蒸気によって劣化しやすいことから、高温耐
久後の浄化性能が不十分となるという問題があった。[0004] The zeolite contained in the exhaust gas purifying catalyst has a molecular sieve characteristic of the zeolite which affects the adsorption of gas on a noble metal which is an active species, and NO x
It promotes a purification reaction. However, the conventional of the NO x purification catalyst, the zeolite used as carrier substrates from the susceptible to degradation by heat and water vapor, there is a problem that the purification performance after high-temperature durability becomes insufficient.
【0005】[0005]
【発明が解決しようとする課題】従って、請求項1〜2
記載の発明の目的は、従来の触媒では十分な活性を示さ
なかったリーン雰囲気下におけるNOx 浄化性能を向上
させることができ、特に高温耐久後においても優れたN
Ox 浄化性能を有する排気ガス浄化用触媒を提供するに
ある。SUMMARY OF THE INVENTION
An object of the described invention is to improve the NO x purification performance in a lean atmosphere, which did not show sufficient activity with the conventional catalyst, and to achieve an excellent N 2 even after high temperature durability.
An object of the present invention is to provide an exhaust gas purifying catalyst having O x purifying performance.
【0006】また、請求項3〜4記載の発明の目的は、
本発明の排気ガス浄化用触媒のそのNOx 浄化作用が特
に有効に発現できる排気ガス浄化用触媒の使用方法を提
供するにある。[0006] The object of the invention according to claims 3 and 4 is as follows.
It is to provide the use of an exhaust gas purifying catalyst that the NO x purification action of the exhaust gas purifying catalyst can be particularly effectively the expression of the present invention.
【0007】[0007]
【課題を解決するための手段】請求項1記載の排気ガス
浄化用触媒は、白金、パラジウム、ロジウム及びイリジ
ウムから成る群より選択された少なくとも一種の貴金属
を担持したゼオライトと、アルミナとを含み、該貴金属
担持ゼオライトは触媒1Lあたり30〜200g、アル
ミナは触媒1Lあたり30〜200gの量で含まれ、該
アルミナの粒径は平均粒径で1〜30μm、細孔容積が
0.1〜1.0cc/g、比表面積が50〜500m2
/gであることを特徴とする。According to a first aspect of the present invention, there is provided an exhaust gas purifying catalyst comprising zeolite carrying at least one noble metal selected from the group consisting of platinum, palladium, rhodium and iridium; and alumina. The noble metal-supported zeolite is contained in an amount of 30 to 200 g per liter of the catalyst, and alumina is contained in an amount of 30 to 200 g per liter of the catalyst. The average particle diameter of the alumina is 1 to 30 μm, and the pore volume is 0.1 to 1. 0 cc / g, specific surface area 50-500 m 2
/ G.
【0008】請求項2記載の排気ガス浄化用触媒は、白
金、パラジウム、ロジウム及びイリジウムから成る群よ
り選択された少なくとも1種の貴金属の担持量が、触媒
1Lあたり0.1〜10gであることを特徴とする。[0008] In the exhaust gas purifying catalyst according to the present invention, the carried amount of at least one noble metal selected from the group consisting of platinum, palladium, rhodium and iridium is 0.1 to 10 g per liter of the catalyst. It is characterized by.
【0009】請求項3記載の排気ガス浄化用触媒の使用
方法は、上記本発明の排気ガス浄化用触媒を空燃比がス
トイキオメトリーと、15〜50の範囲とを繰り返すリ
ーンバーンエンジン車に使用することを特徴とする。According to a third aspect of the present invention, the exhaust gas purifying catalyst of the present invention is used for a lean burn engine vehicle in which the air-fuel ratio repeats stoichiometry and a range of 15 to 50. It is characterized by doing.
【0010】請求項4記載の排気ガス浄化用触媒の使用
方法は、上記本発明の排気ガス浄化用触媒をディーゼル
エンジン車に使用することを特徴とする。A method of using an exhaust gas purifying catalyst according to a fourth aspect is characterized in that the exhaust gas purifying catalyst of the present invention is used for a diesel engine vehicle.
【0011】本発明の排気ガス浄化用触媒中の貴金属に
は、白金、パラジウム、ロジウム及びイリジウムから成
る群より選ばれる少なくとも1種が用いられる。例えば
PtとRh、PdとRh、PtとId、Pdのみ等の種
々の組み合わせが可能である。前記貴金属の含有量は、
NOx 吸収能と三元触媒性能が十分に得られれば特に限
定されないが、0.1gより少ないと十分な三元性能が
得られず、10gより多く使用しても有意な特性向上は
みられない点から、本発明の排気ガス浄化用触媒1Lあ
たり0.1〜10gが好ましい。As the noble metal in the exhaust gas purifying catalyst of the present invention, at least one selected from the group consisting of platinum, palladium, rhodium and iridium is used. For example, various combinations such as Pt and Rh, Pd and Rh, Pt and Id, and Pd alone are possible. The content of the noble metal is
Although absorption of NO x performance and three-way catalyst performance is not particularly limited as long enough to give less than 0.1g and not sufficient ternary performance is obtained, even significant improving characteristics by using more than 10g is seen In view of this, 0.1 to 10 g is preferable per 1 L of the exhaust gas purifying catalyst of the present invention.
【0012】上記貴金属を担持するための基材であるゼ
オライトは、編目状立体構造のものであれば特に限定さ
れず、例えばペンタシル型ゼオライト、Y型ゼオライ
ト、モルデナイト、フェリエライト等が望ましい。ゼオ
ライトの使用量は本発明の触媒1L当たり、30〜20
0gであり、30gより少ないとゼオライトの有する貴
金属へのガス吸着状態を好適化するという作用が十分に
得られず、200gより多く使用しても有意な増量効果
が得られない。The zeolite as a substrate for supporting the noble metal is not particularly limited as long as it has a knitted three-dimensional structure. For example, pentasil-type zeolite, Y-type zeolite, mordenite, ferrierite and the like are desirable. The amount of zeolite used is 30 to 20 per liter of the catalyst of the present invention.
If the amount is less than 0 g, the effect of optimizing the gas adsorption state on the noble metal of the zeolite cannot be sufficiently obtained, and even if the amount is more than 200 g, a significant effect of increasing the amount cannot be obtained.
【0013】アルミナは、平均粒径が1〜30μm、細
孔容積が0.1〜1.0cc/g、比表面積が10〜5
00m2 /gであれば特に限定されず、種々のものを用
いることができる。平均粒径が1μm未満の場合には層
密度が高くなりガス拡散が十分なものとならず、また、
30μmを超えるとゼオライトとアルミナとの接触面が
不足し、アルミナの有する粒凝集抑制効果が十分に得ら
れない。また、細孔容積ならびに比表面積が上記範囲未
満の場合にはゼオライトとアルミナとの接触面が十分な
ものとならず、また上記範囲を超えても有意な向上効果
は得られない。Alumina has an average particle size of 1 to 30 μm, a pore volume of 0.1 to 1.0 cc / g, and a specific surface area of 10 to 5 μm.
There is no particular limitation as long as it is 00 m 2 / g, and various types can be used. If the average particle size is less than 1 μm, the layer density increases and gas diffusion is not sufficient,
If it exceeds 30 μm, the contact surface between zeolite and alumina becomes insufficient, and the effect of alumina to suppress the aggregation of particles cannot be sufficiently obtained. If the pore volume and specific surface area are less than the above ranges, the contact surface between zeolite and alumina will not be sufficient, and if it exceeds the above ranges, no significant improvement effect will be obtained.
【0014】アルミナの使用量は触媒1L当たり、30
〜200gであり、30gより少ないと、アルミナの有
する粒凝集抑制効果が十分に得られず、また200gよ
り多く使用しても有意な増量効果が得られない。The amount of alumina used is 30 per liter of the catalyst.
When the amount is less than 30 g, the effect of suppressing the aggregation of alumina cannot be sufficiently obtained, and even when the amount is more than 200 g, a significant effect of increasing the amount cannot be obtained.
【0015】上記ゼオライト又はアルミナの耐熱比表面
積を高めるために、これらに希土類元素やジルコニウム
を添加することもできる。In order to increase the heat resistant specific surface area of the above-mentioned zeolite or alumina, a rare earth element or zirconium can be added thereto.
【0016】このように本発明の排気ガス浄化用触媒
は、貴金属担持ゼオライトとアルミナとを含むことによ
り、高温耐久後においても高いNOx 浄化性能を得るこ
とが可能となっている。これは、貴金属担持ゼオライト
の粒凝集がアルミナを混合することで抑制され、活性種
である貴金属が高分散状態に保たれること、また粒凝集
が抑えられることで触媒層中でのガス拡散が確保できる
ことによる。The exhaust gas purifying catalyst of the present invention as described above, by including a noble metal loaded zeolite and alumina, it is possible to obtain high the NO x purification performance even after high-temperature durability. This is because the agglomeration of the noble metal-supported zeolite is suppressed by mixing the alumina, the noble metal, which is the active species, is kept in a highly dispersed state, and gas diffusion in the catalyst layer is suppressed by suppressing the agglomeration. It depends on what you can secure.
【0017】上記本発明の排気ガス浄化用触媒は、特
に、空燃比がストイキオメトリーと、15〜50の範囲
とを繰り返すリーンバーンエンジン車、及びディーゼル
エンジン車に使用することができる。このような使用方
法とすることにより、NOx 吸収・放出のサイクルが極
めて有効に成立し、特に効率の良いNOx 浄化が可能と
なる。The exhaust gas purifying catalyst of the present invention can be used especially for lean-burn engine vehicles and diesel engine vehicles in which the air-fuel ratio repeats stoichiometry and a range of 15 to 50. Such With usage, NO x absorption and release cycle is established very effectively, thereby enabling particularly efficient the NO x purification.
【0018】本発明に用いる触媒調製用貴金属原料化合
物としては、硝酸塩、炭酸塩、アンモニウム塩、酢酸
塩、ハロゲン化物、酸化物等を組み合わせて使用するこ
とができるが、特に水溶性の塩を使用することが触媒性
能を向上させる観点から好ましい。貴金属の担持法とし
ては特殊な方法に限定されず、成分の著しい偏在を伴わ
ない限り、公知の蒸発乾固法、沈殿法、含浸法、イオン
交換法等の種々の方法を用いることができる。ゼオライ
トへの担持には、貴金属の分散性確保の点からイオン交
換法が望ましい。As the noble metal raw material compound for preparing a catalyst used in the present invention, nitrates, carbonates, ammonium salts, acetates, halides, oxides and the like can be used in combination. Is preferable from the viewpoint of improving the catalyst performance. The method for supporting the noble metal is not limited to a special method, and various methods such as a well-known evaporation and drying method, a precipitation method, an impregnation method, and an ion exchange method can be used as long as the components are not significantly unevenly distributed. For the support on the zeolite, the ion exchange method is desirable from the viewpoint of ensuring the dispersibility of the noble metal.
【0019】本発明で用いる触媒調製用原料には、その
上記作用を妨げる量でなければ微量の不純物を含んでも
構わず、例えばバリウム中に含まれるストロンチウム
や、セリウム中に含まれるランタン、ネオジウム、サマ
リウム等である。The raw material for preparing a catalyst used in the present invention may contain a trace amount of impurities as long as it does not interfere with the above-mentioned action. For example, strontium contained in barium, lanthanum, neodymium contained in cerium, And samarium.
【0020】このようにして得られる本発明に用いる、
貴金属担持ゼオライトと、アルミナとを粉砕してスラリ
ーとし、触媒担体にコートして、400〜900℃の温
度で焼成することにより、本発明の排気ガス浄化用触媒
を得ることができる。In the present invention thus obtained,
The catalyst for purifying exhaust gas of the present invention can be obtained by pulverizing a noble metal-supported zeolite and alumina to form a slurry, coating the slurry on a catalyst carrier, and calcining the catalyst at a temperature of 400 to 900 ° C.
【0021】触媒担体としては、公知の触媒担体の中か
ら適宜選択して使用することができ、例えば耐火性材料
からなるモノリス構造を有するハニカム担体やメタル担
体等が挙げられる。この触媒担体の形状は、特に制限さ
れないが、通常はハニカム形状で使用することが好まし
く、このハニカム材料としては、一般に例えばセラミッ
クス等のコージェライト質のものが多く用いられるが、
フェライト系ステンレス等の金属材料からなるハニカム
を用いることも可能であり、更には触媒粉末そのものを
ハニカム形状に成形しても良い。触媒の形状をハニカム
状とすることにより、触媒と排気ガスの触媒面積が大き
くなり、圧力損失も抑えられるため自動車用等として用
いる場合に極めて有利である。The catalyst carrier can be appropriately selected from known catalyst carriers, and includes, for example, a honeycomb carrier and a metal carrier having a monolith structure made of a refractory material. Although the shape of the catalyst carrier is not particularly limited, it is usually preferable to use a honeycomb shape. As the honeycomb material, cordierite materials such as ceramics are generally used.
It is also possible to use a honeycomb made of a metal material such as a ferritic stainless steel, and further, the catalyst powder itself may be formed into a honeycomb shape. By making the shape of the catalyst into a honeycomb shape, the area of the catalyst and the exhaust gas becomes large, and the pressure loss can be suppressed.
【0022】[0022]
【実施例】以下、本発明を実施例及び比較例により説明
する。実施例1 ZSM5型ゼオライトにジニトロジアンミンPt水溶液
を含浸し、乾燥後400℃で1時間焼成して、Pt担持
ゼオライト粉末(粉末A)を得た。この粉末AのPt濃
度は3.0重量%であった。The present invention will be described below with reference to examples and comparative examples. Example 1 ZSM5 type zeolite was impregnated with an aqueous solution of dinitrodiammine Pt, dried and calcined at 400 ° C. for 1 hour to obtain a Pt-supported zeolite powder (powder A). The Pt concentration of this powder A was 3.0% by weight.
【0023】上記粉末Aを426g、粉砕後の平均粒径
が10μm、細孔容積0.3cc/g、比表面積150
m2 /gの活性アルミナ粉末(粉末B)を426g、シ
リカゾル(固形分20%)を240g、水710gを磁
性ボールミルに投入し、混合粉砕してスラリー液を得
た。このスラリー液をコーディエライト質モノリス担体
(1.0L、400セル)に付着させ、空気流にてセル
内の余剰のスラリーを取り除いて130℃で乾燥した
後、400℃で1時間焼成し、コート層重量150g/
L−担体の本発明の排気ガス浄化用触媒を得た。426 g of the powder A, the average particle size after pulverization is 10 μm, the pore volume is 0.3 cc / g, and the specific surface area is 150
426 g of m 2 / g activated alumina powder (powder B), 240 g of silica sol (solid content: 20%), and 710 g of water were charged into a magnetic ball mill and mixed and pulverized to obtain a slurry liquid. This slurry liquid was adhered to a cordierite-based monolithic carrier (1.0 L, 400 cells), excess slurry in the cells was removed by air flow, dried at 130 ° C., and calcined at 400 ° C. for 1 hour. Coating layer weight 150g /
An exhaust gas purifying catalyst of the present invention, which is an L-carrier, was obtained.
【0024】実施例2 実施例1におけるジニトロジアンミンPt水溶液の代わ
りに硝酸Rh水溶液を用いる以外は、実施例1と同様の
方法で、本発明の排気ガス浄化用触媒を得た。 Example 2 An exhaust gas purifying catalyst of the present invention was obtained in the same manner as in Example 1 except that an aqueous solution of Rh nitrate was used instead of the aqueous solution of dinitrodiammine Pt in Example 1.
【0025】実施例3 実施例1におけるジニトロジアンミンPt水溶液の代わ
りに硝酸Pd水溶液を用いる以外は、実施例1と同様の
方法で、本発明の排気ガス浄化用触媒を得た。 Example 3 An exhaust gas purifying catalyst of the present invention was obtained in the same manner as in Example 1 except that an aqueous solution of Pd nitrate was used instead of the aqueous solution of dinitrodiammine Pt in Example 1.
【0026】実施例4 実施例1におけるジニトロジアンミンPt水溶液の代わ
りに塩化Ir水溶液を用いる以外は、実施例1と同様の
方法で、本発明の排気ガス浄化用触媒を得た。 Example 4 An exhaust gas purifying catalyst of the present invention was obtained in the same manner as in Example 1 except that an aqueous solution of IrCl was used instead of the aqueous solution of dinitrodiammine Pt in Example 1.
【0027】実施例5 ZSM5型ゼオライトにジニトロジアンミンPt水溶液
を含浸し、乾燥後400℃で1時間焼成して、Pt担持
濃度2重量%のPt担持ゼオライト粉末(粉末C)を得
た。 Example 5 ZSM5 type zeolite was impregnated with an aqueous solution of dinitrodiammine Pt, dried and calcined at 400 ° C. for 1 hour to obtain a Pt-supported zeolite powder (powder C) having a Pt-supporting concentration of 2% by weight.
【0028】上記粉末Cを606g、実施例1で得られ
た粉末Bを246g、シリカゾル(固形分20%)を2
40g、水710gを磁性ボールミルに投入し、混合粉
砕してスラリー液を得た。このスラリー液をコーディエ
ライト質モノリス担体(1.0L、400セル)に付着
させ、空気流にてセル内の余剰のスラリーを取り除いて
130℃で乾燥した後、400℃で1時間焼成し、コー
ト層重量150g/L−担体の本発明の排気ガス浄化用
触媒を得た。606 g of the powder C, 246 g of the powder B obtained in Example 1, and 2 parts of silica sol (solid content: 20%).
40 g and 710 g of water were charged into a magnetic ball mill and mixed and pulverized to obtain a slurry liquid. This slurry liquid was adhered to a cordierite-based monolithic carrier (1.0 L, 400 cells), excess slurry in the cells was removed by air flow, dried at 130 ° C., and calcined at 400 ° C. for 1 hour. An exhaust gas purifying catalyst of the present invention having a coat layer weight of 150 g / L-carrier was obtained.
【0029】実施例6 ZSM5型ゼオライトにジニトロジアンミンPt水溶液
を含浸し、乾燥後400℃で1時間焼成して、Pt担持
濃度5重量%のPt担持ゼオライト粉末(粉末D)を得
た。 Example 6 ZSM5 type zeolite was impregnated with an aqueous solution of dinitrodiammine Pt, dried and calcined at 400 ° C. for 1 hour to obtain a Pt-supported zeolite powder (powder D) having a Pt-supporting concentration of 5% by weight.
【0030】上記粉末Dを246g、実施例1で得られ
た粉末Bを606g、シリカゾル(固形分20%)を2
40g、水710gを磁性ボールミルに投入し、混合粉
砕してスラリー液を得た。このスラリー液をコーディエ
ライト質モノリス担体(1.0L、400セル)に付着
させ、空気流にてセル内の余剰のスラリーを取り除いて
130℃で乾燥した後、400℃で1時間焼成し、コー
ト層重量150g/L−担体の本発明の排気ガス浄化用
触媒を得た。246 g of the powder D, 606 g of the powder B obtained in Example 1, and 2 parts of silica sol (solid content: 20%)
40 g and 710 g of water were charged into a magnetic ball mill and mixed and pulverized to obtain a slurry liquid. This slurry liquid was adhered to a cordierite-based monolithic carrier (1.0 L, 400 cells), excess slurry in the cells was removed by air flow, dried at 130 ° C., and calcined at 400 ° C. for 1 hour. An exhaust gas purifying catalyst of the present invention having a coat layer weight of 150 g / L-carrier was obtained.
【0031】実施例7 実施例1におけるアルミナの代わりに、平均粒径5μ
m、細孔容積0.8cc/g、比表面積210m2 /g
のアルミナ粉末(粉末E)を用いる以外は実施例1と同
様の方法で、本発明の排気ガス浄化用触媒を得た。 Example 7 Instead of alumina in Example 1, the average particle size was 5 μm.
m, pore volume 0.8 cc / g, specific surface area 210 m 2 / g
Except that the alumina powder (powder E) was used, an exhaust gas purifying catalyst of the present invention was obtained in the same manner as in Example 1.
【0032】実施例8 ZSM5型ゼオライトにジニトロジアンミンPt水溶液
及び硝酸Rh水溶液を含浸し、乾燥後400℃で1時間
焼成して、Pt及びRh担持ゼオライト粉末(粉末F)
を得た。この粉末FのPt濃度は3.0重量%、Rh濃
度は3.0重量%であった。実施例1における粉末Aの
代わりに上記粉末Fを用いる以外は実施例1と同様の方
法で、排気ガス浄化用触媒を得た。 Example 8 ZSM5 type zeolite was impregnated with an aqueous solution of dinitrodiammine Pt and an aqueous solution of Rh nitrate, dried and calcined at 400 ° C. for 1 hour to obtain a zeolite powder carrying Pt and Rh (powder F).
I got The powder F had a Pt concentration of 3.0% by weight and an Rh concentration of 3.0% by weight. An exhaust gas purifying catalyst was obtained in the same manner as in Example 1 except that the powder F was used instead of the powder A in Example 1.
【0033】比較例1 実施例1における活性アルミナの代わりにZSM5型ゼ
オライト粉末を用いる以外は実施例1と同様の方法で、
排気ガス浄化用触媒を得た。 Comparative Example 1 The procedure of Example 1 was repeated, except that ZSM5 type zeolite powder was used instead of activated alumina.
An exhaust gas purifying catalyst was obtained.
【0034】比較例2 実施例1における活性アルミナの代わりに、粉砕後の平
均粒径が35μm、細孔容積が0.05cc/g、比表
面積が40m2 /gのアルミナ粉末(粉末C)を用いる
以外は実施例1と同様の方法で、排気ガス浄化用触媒を
得た。 Comparative Example 2 Instead of activated alumina in Example 1, alumina powder (powder C) having an average particle size after pulverization of 35 μm, a pore volume of 0.05 cc / g and a specific surface area of 40 m 2 / g was used. An exhaust gas purifying catalyst was obtained in the same manner as in Example 1 except that the catalyst was used.
【0035】前記実施例1〜8及び比較例1〜2で得ら
れた排気ガス浄化用触媒の触媒組成を表1に示す。Table 1 shows the catalyst compositions of the exhaust gas purifying catalysts obtained in Examples 1 to 8 and Comparative Examples 1 and 2.
【0036】[0036]
【表1】 [Table 1]
【0037】試験例 前記実施例1〜8及び比較例1〜2で得られた排気ガス
浄化用触媒について、以下の条件で初期及び耐久後の触
媒活性評価を行った。活性評価には、自動車の排気ガス
を模したモデルガスを用いる自動評価装置を用いた。 Test Examples The exhaust gas purifying catalysts obtained in Examples 1 to 8 and Comparative Examples 1 and 2 were evaluated for initial and endurance catalytic activities under the following conditions. For the activity evaluation, an automatic evaluation device using a model gas simulating the exhaust gas of an automobile was used.
【0038】耐久条件 エンジン4400ccの排気系に触媒を装着し、触媒入
口温度600℃で、50時間運転して耐久を行った。 Endurance conditions A catalyst was attached to the exhaust system of a 4400 cc engine, and operation was performed at a catalyst inlet temperature of 600 ° C. for 50 hours to endurance.
【0039】評価条件1 触媒活性評価は、排気量2000ccのガソリンエンジ
ンの排気系に各触媒を装着し、触媒入口温度を300℃
とし、A/F=14.6(ストイキ状態)で60秒間、
その後A/F=22(リーン雰囲気)で30秒間、次い
で、A/F=50(リーン雰囲気)で30秒間の運転を
1サイクル行ない、各々平均転化率を測定し、このA/
F=14.6(ストイキ状態)の場合の平均転化率とA
/F=22(リーン雰囲気)の場合の平均転化率と、A
/F=50(リーン雰囲気)の場合の平均転化率とを平
均してトータル転化率とした。 Evaluation condition 1 The catalyst activity was evaluated by mounting each catalyst in the exhaust system of a gasoline engine with a displacement of 2000 cc and setting the catalyst inlet temperature to 300 ° C.
A / F = 14.6 (stoichiometric state) for 60 seconds,
Thereafter, operation was performed for one cycle at A / F = 22 (lean atmosphere) for 30 seconds, then at A / F = 50 (lean atmosphere) for 30 seconds, and the average conversion was measured.
Average conversion rate and A when F = 14.6 (stoichiometric state)
/ F = 22 (lean atmosphere) and average conversion
The average conversion when / F = 50 (lean atmosphere) was averaged to obtain the total conversion.
【0040】評価条件2 排気量2000ccのディーゼルエンジンの排気系に各
触媒を装着し、触媒入口温度を150〜450℃まで3
0分かけて昇温し、その際のNOx の最高転化率を求め
た。 Evaluation condition 2 Each catalyst was mounted on the exhaust system of a diesel engine with a displacement of 2000 cc, and the catalyst inlet temperature was raised from 150 to 450 ° C.
The temperature was raised over a period of 0 min, was determined the highest conversion rate of the NO x at that time.
【0041】上記評価条件1及び2の評価を初期及び耐
久後に各々行ない、触媒活性評価値を以下の式により決
定した。The evaluation conditions 1 and 2 were evaluated at the initial stage and after the endurance, respectively, and the catalyst activity evaluation value was determined by the following equation.
【数1】 (Equation 1)
【0042】トータル転化率として得られた触媒活性評
価結果を表2に示す。比較例に比べて実施例は、触媒活
性が高く、後述する本発明の効果を確認することができ
た。Table 2 shows the results of the catalyst activity evaluation obtained as the total conversion. The catalytic activity of the example was higher than that of the comparative example, and the effect of the present invention described later could be confirmed.
【0043】[0043]
【表2】 [Table 2]
【0044】[0044]
【発明の効果】請求項1〜2記載の排気ガス浄化用触媒
は、従来の触媒では十分な活性を示さなかったリーン雰
囲気下におけるNOx 浄化性能を向上させ、更に熱耐久
後においても優れたNOx 浄化性能を示すことができ
る。Effects of the Invention claim 1-2 exhaust gas purifying catalyst described in the prior art catalysts to improve the NO x purification performance in the lean atmosphere that did not exhibit sufficient activity, excellent further after thermal endurance the NO x purification performance can exhibit.
【0045】請求項3〜4記載の排気ガス浄化用触媒の
使用方法においては、上記本発明の排気ガス浄化用触媒
の有効なNOx 吸収、放出サイクルを特に効率良く発現
させることができる。[0045] In the use of the catalyst for purifying exhaust gases according to claim 3-4, wherein the effective absorption of NO x of the exhaust gas purifying catalyst of the present invention, it is possible to particularly effectively express release cycle.
フロントページの続き (51)Int.Cl.6 識別記号 FI B01D 53/36 104A Continued on the front page (51) Int.Cl. 6 Identification code FI B01D 53/36 104A
Claims (4)
ウムから成る群より選択された少なくとも一種の貴金属
を担持したゼオライトと、アルミナとを含み、該貴金属
担持ゼオライトは触媒1Lあたり30〜200g、アル
ミナは触媒1Lあたり30〜200gの量で含まれ、該
アルミナの粒径は平均粒径で1〜30μm、細孔容積が
0.1〜1.0cc/g、比表面積が50〜500m2
/gであることを特徴とする排気ガス浄化用触媒。1. A zeolite supporting at least one noble metal selected from the group consisting of platinum, palladium, rhodium and iridium, and alumina, wherein the noble metal-supported zeolite is 30 to 200 g per liter of catalyst and alumina is 1 liter of catalyst. In an amount of 30 to 200 g per unit, the average particle size of the alumina is 1 to 30 μm, the pore volume is 0.1 to 1.0 cc / g, and the specific surface area is 50 to 500 m 2.
/ G, the catalyst for purifying exhaust gas.
ウムから成る群より選択された少なくとも1種の貴金属
の担持量は、触媒1Lあたり0.1〜10gであること
を特徴とする請求項1記載の排気ガス浄化用触媒。2. The exhaust gas according to claim 1, wherein the carried amount of at least one noble metal selected from the group consisting of platinum, palladium, rhodium and iridium is 0.1 to 10 g per liter of the catalyst. Gas purification catalyst.
媒を、空燃比がストイキオメトリーと、15〜50の範
囲とを繰り返すリーンバーンエンジン車に使用すること
を特徴とする排気ガス浄化用触媒の使用方法。3. The exhaust gas purifying catalyst according to claim 1, wherein the exhaust gas purifying catalyst is used in a lean burn engine vehicle in which an air-fuel ratio alternates between stoichiometry and 15 to 50. How to use catalyst for
ディーゼルエンジン車に使用することを特徴とする排気
ガス浄化用触媒の使用方法。4. The exhaust gas purifying catalyst according to claim 1,
A method for using an exhaust gas purifying catalyst, which is used for a diesel engine vehicle.
Priority Applications (1)
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JP9214330A JPH1157484A (en) | 1997-08-08 | 1997-08-08 | Exhaust gas cleaning catalyst and its use |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP9214330A JPH1157484A (en) | 1997-08-08 | 1997-08-08 | Exhaust gas cleaning catalyst and its use |
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Publication Number | Publication Date |
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JPH1157484A true JPH1157484A (en) | 1999-03-02 |
Family
ID=16653975
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Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH11123330A (en) * | 1997-08-20 | 1999-05-11 | Hino Motors Ltd | Exhaust gas cleaning catalyst and manufacture thereof |
JP2002045701A (en) * | 2000-08-08 | 2002-02-12 | Cataler Corp | Catalyst for purifying exhaust gas |
-
1997
- 1997-08-08 JP JP9214330A patent/JPH1157484A/en not_active Withdrawn
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH11123330A (en) * | 1997-08-20 | 1999-05-11 | Hino Motors Ltd | Exhaust gas cleaning catalyst and manufacture thereof |
JP2002045701A (en) * | 2000-08-08 | 2002-02-12 | Cataler Corp | Catalyst for purifying exhaust gas |
JP4642978B2 (en) * | 2000-08-08 | 2011-03-02 | 株式会社キャタラー | Exhaust gas purification catalyst |
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