JP2001149757A - Exhaust gas purifying catalyst - Google Patents

Exhaust gas purifying catalyst

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Publication number
JP2001149757A
JP2001149757A JP33823899A JP33823899A JP2001149757A JP 2001149757 A JP2001149757 A JP 2001149757A JP 33823899 A JP33823899 A JP 33823899A JP 33823899 A JP33823899 A JP 33823899A JP 2001149757 A JP2001149757 A JP 2001149757A
Authority
JP
Japan
Prior art keywords
catalyst
oxide powder
exhaust gas
powder
cerium oxide
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.)
Granted
Application number
JP33823899A
Other languages
Japanese (ja)
Other versions
JP4368991B2 (en
Inventor
Kiyotaka Hayashi
清高 林
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.)
Cataler Corp
Original Assignee
Cataler Corp
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Filing date
Publication date
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Priority to JP33823899A priority Critical patent/JP4368991B2/en
Publication of JP2001149757A publication Critical patent/JP2001149757A/en
Application granted granted Critical
Publication of JP4368991B2 publication Critical patent/JP4368991B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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Abstract

PROBLEM TO BE SOLVED: To provide a high temperature NOx occlusion/reduction type exhaust gas purifying catalyst exhibiting catalytic activity even at high temperature use and exhibiting an effective purifying action while suppressing the sintering of noble metal. SOLUTION: In the NOx occlusion/reduction type exhaust gas purifying catalyst having a carrier and a catalyst retaining layer formed on the carrier, the catalyst retaining layer is composed of alumina powder to which a noble metal is previously deposited, titanium oxide powder, the cerium oxide powder to which a noble metal is deposited and at least one kind of NOx occluding alkali metal salts and alkaline earth metal salts supported on the alumina powder, the titanium oxide powder and the cerium oxide powder, and at least one king of the alkali metal salts and the alkaline earth metal salts is deposited in the state dissolved in the slurry aqueous solution in which the alumina powder, the titanium oxide powder and the cerium oxide powder are disperesed.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、排ガス浄化用触媒
に関するもので、自動車などの内燃機関から排出される
排ガス中に含まれる特にNOxを吸蔵還元性を高めると
同時に硫黄による被毒性を低減させたNOx吸蔵還元型
の排ガス浄化用触媒に係るものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an exhaust gas purifying catalyst, and more particularly to a method for increasing the occlusion and reduction of NOx contained in exhaust gas discharged from an internal combustion engine of an automobile or the like and reducing the toxicity of sulfur. The present invention relates to a NOx storage reduction type exhaust gas purifying catalyst.

【0002】[0002]

【従来の技術】従来、窒素酸化物吸蔵型排ガス浄化触媒
は、窒素酸化物を含む排ガスを酸素過剰雰囲気(リーン
条件)下に触媒に接触させて、窒素酸化物をバリウム
や、バリウムとアルミニウムの複合酸化物に吸蔵させ、
これに還元剤を噴射するなどの方法により、排ガスを還
元雰囲気(リッチ条件)とし、触媒に吸蔵されている窒
素酸化物を窒素に還元されることが知られている(例え
ば特開平10−314593号公報)。
2. Description of the Related Art Conventionally, a nitrogen oxide storage type exhaust gas purifying catalyst is prepared by bringing an exhaust gas containing nitrogen oxide into contact with the catalyst under an oxygen-excess atmosphere (lean condition) to convert the nitrogen oxide into barium or a mixture of barium and aluminum. Occluded in the composite oxide,
It is known that the exhaust gas is reduced to a reducing atmosphere (rich condition) by a method such as injection of a reducing agent, and the nitrogen oxides stored in the catalyst are reduced to nitrogen (for example, Japanese Patent Application Laid-Open No. 10-314593). No.).

【0003】また、特開平6−142458号公報に
は、炭化水素と窒素酸化物を同時に浄化する触媒とし
て、多孔質からなる担体に白金およびパラジウムの少な
くとも1種の貴金属、バリウム並びにアルカリ金属、
鉄、ニッケル、コバルトおよびマグネシウムの群から選
ばれた少なくとも1種の金属を担持した排ガス浄化用触
媒が開示されている。
Japanese Patent Application Laid-Open No. 6-142458 discloses a catalyst for simultaneously purifying hydrocarbons and nitrogen oxides, which comprises a porous carrier comprising at least one of platinum and palladium, at least one noble metal, barium and an alkali metal.
An exhaust gas purifying catalyst supporting at least one metal selected from the group consisting of iron, nickel, cobalt and magnesium is disclosed.

【0004】しかし、上記の触媒では、触媒金属と触媒
活性物質との分散状態が均一とならず、必ずしも十分な
浄化性能を発揮できない場合がある。すなわち、触媒金
属が凝集して粒状化したり、触媒金属の補助作用をする
触媒活性物質が触媒金属の近傍に存在せず想定される浄
化性能が発現しない場合があった。
[0004] However, in the above-mentioned catalyst, the dispersion state of the catalytic metal and the catalytically active substance is not uniform, so that sufficient purification performance may not always be exhibited. That is, the catalytic metal may be aggregated and granulated, or a catalytically active substance that assists the catalytic metal may not be present in the vicinity of the catalytic metal, and the expected purification performance may not be exhibited.

【0005】上記のNOx吸蔵還元型触媒では、熱劣化
が著しく熱履歴により浄化性のが低下するのでこの点を
改良した触媒が望まれている。
[0005] In the above-mentioned NOx occlusion reduction type catalyst, thermal degradation is remarkable, and purifying performance is degraded due to heat history. Therefore, a catalyst which improves this point is desired.

【0006】アルカリもしくはアルカリ土類金属をNO
x吸蔵材として触媒中に含有していると、高温で貴金属
のシンタリングが起こり、また、リーン雰囲気で触媒を
高温で使用すると貴金属のシンタリングが大きくなる不
具合がある。
When the alkali or alkaline earth metal is converted to NO
When x is contained in the catalyst as an occlusion material, sintering of the noble metal occurs at a high temperature, and sintering of the noble metal increases when the catalyst is used at a high temperature in a lean atmosphere.

【0007】[0007]

【発明が解決しようとする課題】本発明は上記の事情に
鑑みてなされたもので、高温での使用においても触媒活
性を示し貴金属がシンタリングを起こしたり、NOx吸
蔵材が飛散するのを抑えて有効な浄化作用を示す高温N
Ox吸蔵還元型の排ガス浄化用触媒を提案することを課
題とする。
SUMMARY OF THE INVENTION The present invention has been made in view of the above circumstances, and exhibits catalytic activity even when used at a high temperature to prevent sintering of precious metals and scattering of NOx storage materials. Temperature N showing effective and effective purifying action
It is an object to propose an Ox storage reduction type exhaust gas purifying catalyst.

【0008】[0008]

【課題を解決するための手段】本発明者は、上記の課題
を解決するために触媒活性を示す貴金属のシンタリング
を抑え、かつ窒素酸化物を吸蔵する吸蔵材の飛散を抑制
することを鋭意検討した結果、本発明を完成したもので
ある。
Means for Solving the Problems In order to solve the above-mentioned problems, the present inventor has sought to suppress the sintering of a noble metal exhibiting catalytic activity and to suppress the scattering of a storage material for storing nitrogen oxides. As a result of the study, the present invention has been completed.

【0009】本発明の排ガス浄化用触媒は、担体と前記
担体上に形成された触媒保持層とを持つNOx吸蔵還元
型触媒であって、前記触媒保持層は、予め貴金属が担持
されたアルミナ粉末と、酸化チタン粉末と、貴金属が担
持されたセリウム酸化物粉末と、該アルミナ粉末、該酸
化チタン粉末、該セリウム酸化物とに担持されたNOx
吸蔵性のアルカリ金属塩、アルカリ土類金属塩の少なく
とも1種とからなり、該アルカリ金属塩、アルカリ土類
金属塩の少なくとも1種は該アルミナ粉末、該酸化チタ
ン粉末、該セリウム酸化物が分散したスラリー水溶液に
溶解した状態で担持されたものであることを特徴とす
る。
The exhaust gas purifying catalyst of the present invention is a NOx storage reduction catalyst having a carrier and a catalyst holding layer formed on the carrier, wherein the catalyst holding layer is made of an alumina powder pre-loaded with a noble metal. , A titanium oxide powder, a cerium oxide powder supporting a noble metal, the alumina powder, the titanium oxide powder, and NOx supported on the cerium oxide.
It comprises at least one of an occluding alkali metal salt and an alkaline earth metal salt, and at least one of the alkali metal salt and the alkaline earth metal salt contains the alumina powder, the titanium oxide powder and the cerium oxide dispersed therein. Characterized by being carried in a state of being dissolved in the slurry aqueous solution.

【0010】前記触媒保持層は、該アルミナ粉末、該酸
化チタン粉末、該セリウム酸化物およびNOx吸蔵性の
該アルカリ金属塩、アルカリ土類金属塩の少なくとも1
種が、スラリー中で機械的に強制粉砕混合され各構成成
分が均一に分散していることが好ましい。
[0010] The catalyst holding layer comprises at least one of the alumina powder, the titanium oxide powder, the cerium oxide and the alkali metal salt or alkaline earth metal salt having NOx storage properties.
It is preferred that the seeds be mechanically comminuted and mixed in the slurry so that each component is uniformly dispersed.

【0011】前記アルミナ粉末に担持された貴金属は、
白金およびロジウムであることが好ましい。
The noble metal supported on the alumina powder is
Preference is given to platinum and rhodium.

【0012】前記セリウムを含む酸化物粉末に担持され
た貴金属は、白金であることが好ましい。
The noble metal supported on the cerium-containing oxide powder is preferably platinum.

【0013】前記セリウム酸化物は、セリウム酸化物あ
るいはジルコニウムとの複合酸化物であることが好まし
い。
The cerium oxide is preferably a cerium oxide or a composite oxide with zirconium.

【0014】前記NOx吸蔵性のアルカリ金属、アルカ
リ土類金属塩は、バリウム、マグネシウム、リチウム、
ナトリウム、カリウムであることが好ましい。
The NOx-storing alkali metal and alkaline earth metal salts include barium, magnesium, lithium,
Preferably, they are sodium and potassium.

【0015】[0015]

【発明の実施の形態】本発明の排ガス浄化用触媒は、リ
ーンバーンエンジンのリーン雰囲気時にNOxを吸蔵し
てストイキもしくはリッチ雰囲気時に吸蔵したNOxを
還元するタイプの触媒である。
DESCRIPTION OF THE PREFERRED EMBODIMENTS The exhaust gas purifying catalyst of the present invention is a type of catalyst that stores NOx in a lean burn engine in a lean atmosphere and reduces the stored NOx in a stoichiometric or rich atmosphere.

【0016】リーン雰囲気時にNOx吸蔵材のアルカリ
金属、アルカリ土類金属塩の少なくとも1種を貴金属を
担持したアルミナ粉末、酸化チタン粉末、貴金属を担持
したセリウム酸化物と共に触媒保持層に均一に分散させ
ることで、リッチ雰囲気時に触媒が吸蔵したNOxを容
易に還元する構成である。
In a lean atmosphere, at least one of alkali metal and alkaline earth metal salts of the NOx storage material is uniformly dispersed in the catalyst holding layer together with alumina powder, titanium oxide powder carrying noble metal, and cerium oxide carrying noble metal. Thus, the configuration is such that the NOx stored by the catalyst is easily reduced in the rich atmosphere.

【0017】貴金属が予めアルミナ粉末、セリウム酸化
物粉末に担持されていることで触媒保持層に均一に分散
され貴金属どうしのシンタリングが抑制できる。また、
NOx吸蔵材も触媒保持層に均一に高分散されているの
で、高温の排ガスが導入されても、NOx吸蔵材の移動
・飛散を抑制することができる。また、高分散状態の予
め貴金属を担持させセリウム酸化物粉末と、高分散状態
のNOx吸蔵材によりストイキもしくはリッチ雰囲気で
のNOxの還元反応を促進させ、吸蔵したの還元性を高
めることができる。さらに、酸化チタン粉末の存在によ
り硫黄による触媒の被毒が再生され触媒の浄化性能を長
期間保持することができる。この結果、高温での触媒の
性能を保持することができ、耐劣化性能が向上できる。
Since the noble metal is previously supported on the alumina powder and the cerium oxide powder, the noble metal is uniformly dispersed in the catalyst holding layer, and sintering between the noble metals can be suppressed. Also,
Since the NOx storage material is also uniformly and highly dispersed in the catalyst holding layer, the movement and scattering of the NOx storage material can be suppressed even when high-temperature exhaust gas is introduced. In addition, the reduction reaction of NOx in a stoichiometric or rich atmosphere can be promoted by the cerium oxide powder preloaded with a noble metal in a highly dispersed state and the NOx occluding material in a highly dispersed state, so that the occlusion reducibility can be enhanced. Further, the poisoning of the catalyst by sulfur is regenerated by the presence of the titanium oxide powder, and the purification performance of the catalyst can be maintained for a long time. As a result, the performance of the catalyst at a high temperature can be maintained, and the deterioration resistance performance can be improved.

【0018】上記の各粉末成分は、NOx吸蔵材の溶解
液とで形成されるスラリーで機械的に強制粉砕混合によ
り均一に混合される。好ましくはスラリーをミリング処
理などで混合することで粉末の粒径を揃えてかつ貴金属
を機械的に粉末粒子に均一に固着させた後、担体上にコ
ートされ触媒保持層が形成される。その結果、各構成成
分は、単にそれぞれコートないしは浸漬によって担持し
た場合とは異なり触媒保持層全体に均一に分散し、特に
貴金属の移動を抑制された触媒担持層が形成できる。
Each of the above-mentioned powder components is uniformly mixed mechanically by forced pulverization and mixing with a slurry formed with a solution of the NOx storage material. Preferably, the slurry is mixed by milling or the like to make the powder particle size uniform and the noble metal is mechanically fixed to the powder particles uniformly, and then coated on the carrier to form a catalyst holding layer. As a result, each component is dispersed uniformly throughout the catalyst holding layer, unlike a case where each component is simply supported by coating or dipping, and a catalyst supporting layer in which migration of noble metals is particularly suppressed can be formed.

【0019】触媒の貴金属は、アルミナ粉末に担持させ
ることで触媒の耐熱性が保持される。貴金属のアルミナ
への担持量は、0.5〜10重量%の程度であることが
触媒の活性を保つ上で好ましい。貴金属としては、白
金、ロジウムの少なくとも1種が用いられる。白金とロ
ジウムの両者を併用するときはPt/Rh=3/1〜1
00/1の範囲が浄化効率を高めるために好ましい。
The noble metal of the catalyst is supported on alumina powder to maintain the heat resistance of the catalyst. The amount of the noble metal supported on alumina is preferably about 0.5 to 10% by weight to maintain the activity of the catalyst. As the noble metal, at least one of platinum and rhodium is used. When both platinum and rhodium are used in combination, Pt / Rh = 3/1 to 1
The range of 00/1 is preferable for increasing the purification efficiency.

【0020】本発明の排ガス浄化用触媒は、酸化チタン
粉末を配合することで耐硫黄性を向上させることができ
る。酸化チタン粉末の配合量はTi/Al=1/9〜2
/1の範囲が好ましい。酸化チタン粉末の量が多くなる
と触媒の耐熱性が低下するので好ましくない。酸化チタ
ン粉末は、単独または、セリウム酸化物粉末と同時にス
ラリー添加して混合しても良い。
The exhaust gas purifying catalyst of the present invention can improve sulfur resistance by blending titanium oxide powder. The amount of the titanium oxide powder is Ti / Al = 1/9 to 2
/ 1 is preferred. If the amount of the titanium oxide powder is too large, the heat resistance of the catalyst decreases, which is not preferable. The titanium oxide powder may be added alone or mixed with the cerium oxide powder by slurry addition.

【0021】セリウム酸化物粉末は予め貴金属を担持し
てスラリーに添加して混合させる。セリウム酸化物粉末
は、ジルコニウムと複合酸化物を形成したものを用いる
ことができる。セリウム複合酸化物としてはCe/Zr
(好ましい比率は4/1〜1/1である)等が利用でき
る。セリウム酸化物粉末に担持させる貴金属としては白
金が好ましい。白金を担持したセリウム酸化物粉末によ
り浄化触媒は、リッチパルスの再生性を向上させ、触媒
の耐久性を向上させることができる。
The cerium oxide powder previously supports a noble metal and is added to and mixed with the slurry. As the cerium oxide powder, a composite oxide formed with zirconium can be used. Ce / Zr as cerium composite oxide
(Preferable ratio is 4/1 to 1/1) and the like. Platinum is preferred as the noble metal supported on the cerium oxide powder. With the cerium oxide powder supporting platinum, the purification catalyst can improve the reproducibility of the rich pulse and improve the durability of the catalyst.

【0022】セリウム酸化物粉末に担持させる貴金属の
量は、5〜50mg/gの範囲であることが性能上好ま
しい。
The amount of the noble metal supported on the cerium oxide powder is preferably in the range of 5 to 50 mg / g in terms of performance.

【0023】NOx吸蔵材はアルカリ金属塩、アルカリ
土類金属塩の水溶液が利用できる。アルカリ金属塩、ア
ルカリ金属塩の少なくとも1種としては、バリウム、マ
グネシウム、リチウム、ナトリウム、カリウムの塩(例
えば炭酸塩、硝酸塩、塩酸塩、硫酸塩、水酸化物、酢酸
塩)等が利用でき、特にリチウムとカリウムの混合溶液
を用いるのが好ましい。このアルカリ金属塩の水溶液は
スラリー中で上記の貴金属を担持したアルミナ粉末、酸
化チタン粉末、セリウム酸化物粉末と共に混合されて、
均一に粉末が担持される。
As the NOx storage material, an aqueous solution of an alkali metal salt or an alkaline earth metal salt can be used. As at least one of alkali metal salts and alkali metal salts, barium, magnesium, lithium, sodium, potassium salts (eg, carbonate, nitrate, hydrochloride, sulfate, hydroxide, acetate) and the like can be used. In particular, a mixed solution of lithium and potassium is preferably used. The aqueous solution of the alkali metal salt is mixed with the alumina powder, the titanium oxide powder, and the cerium oxide powder supporting the noble metal in the slurry,
The powder is uniformly loaded.

【0024】NOxの吸蔵材の量は、触媒保持層中に
0.01〜0.5mol/g存在するのが好ましい。
The amount of the NOx occluding material is preferably 0.01 to 0.5 mol / g in the catalyst holding layer.

【0025】貴金属を上記の様に予めアルミナ粉末、セ
リウム酸化物粉末上に担持させておくことにより、後か
ら触媒保持層を貴金属の溶解液やNOx吸蔵材の溶解液
に浸漬担持した場合よりも触媒保持層に均一に分散させ
ることができ、触媒としての耐久性を高めることができ
る。
By pre-loading the noble metal on the alumina powder or cerium oxide powder as described above, the catalyst holding layer is later immersed and supported in a noble metal solution or NOx storage material solution. The catalyst can be uniformly dispersed in the catalyst holding layer, and the durability as a catalyst can be enhanced.

【0026】なお、貴金属の上記のアルミナ粉末および
セリウム酸化物粉末への担持は、通常の方法が利用でき
る。すなわち、貴金属塩の所定濃度の溶解水溶液等に上
記の各粉末を浸漬して十分混合して乾固焼成して得られ
る。
The noble metal can be supported on the alumina powder and the cerium oxide powder by an ordinary method. That is, it is obtained by immersing each of the above-mentioned powders in an aqueous solution of a predetermined concentration of a noble metal salt or the like, mixing them sufficiently, and baking to dryness.

【0027】本発明において、アルミナ粉末、酸化チタ
ン粉末、セリウム酸化物粉末の配合割合は4:1:1で
あることが好ましい。またNOx吸蔵材の量は、上記の
粉末に対し100重量部に対して0.05〜0.5mol
の量の範囲であることが浄化性能および触媒の耐久性を
高める上で好ましい。
In the present invention, the mixing ratio of alumina powder, titanium oxide powder and cerium oxide powder is preferably 4: 1: 1. The amount of the NOx occluding material is 0.05 to 0.5 mol based on 100 parts by weight of the above powder.
Is preferable in order to enhance the purification performance and the durability of the catalyst.

【0028】[0028]

【実施例】以下、実施例により具体的に説明する。The present invention will be specifically described below with reference to examples.

【0029】(実施例1)ジニトロジアミン白金溶液
(Ptとしての溶解量:1.5g)と硝酸ロジウム溶液
(Rhとしての溶解量:0.1g)との混合溶液にアル
ミナ粉末100g(粒径0.01〜10μm)を加えて
アルミナに貴金属を担持した後、溶媒を蒸発乾固させて
170℃で焼成して所定量の貴金属を担持したアルミナ
粉末を作製した。
Example 1 A mixture of a dinitrodiamine platinum solution (dissolved amount as Pt: 1.5 g) and a rhodium nitrate solution (dissolved amount as Rh: 0.1 g) was mixed with 100 g of alumina powder (particle size 0). Then, the solvent was evaporated to dryness and calcined at 170 ° C. to produce an alumina powder carrying a predetermined amount of the noble metal.

【0030】セリウムとジルコニウムの複合酸化物粉末
(Ce:Zr=5:1atom比)100gをジニトロジア
ミン白金溶液(Ptとしての溶解量:2g)と混合して
乾燥させて生成したPt担持セリウムとジルコニウムの
複合酸化粉末40gと、酸化チタン粉末40gを加
え、さらにNOx吸蔵材のカリウム塩(酢酸塩)20g
とリチウム塩(硝酸塩)10gを溶解した水溶液200
mlを加えて混合してスラリー状とした。このスラリーの
粒度を平均約5μmに調整するために、ボールミル等で
ミリングしてスラリーを調製した。得られたスラリーを
コージライトなどでできているモノリス担体にコートし
て実施例1の触媒を作製した。
Pt-supported cerium and zirconium formed by mixing and drying 100 g of a composite oxide powder of cerium and zirconium (Ce: Zr = 5: 1 atom ratio) (dissolved amount as Pt: 2 g) a composite oxide powder 40g of titanium oxide powder 40g addition, further potassium salt of NOx-absorbing material (acetate) 20 g
And an aqueous solution 200 in which 10 g of lithium salt (nitrate) are dissolved
ml was added and mixed to form a slurry. In order to adjust the average particle size of the slurry to about 5 μm, the slurry was prepared by milling with a ball mill or the like. The resulting slurry was coated on a monolithic carrier made of cordierite or the like to prepare a catalyst of Example 1.

【0031】(実施例2)実施例1でのNOx吸蔵材の
リチウム塩を酢酸バリウムに代えた以外は、実施例1と
同様にして実施例2の触媒を調製した。
(Example 2) A catalyst of Example 2 was prepared in the same manner as in Example 1, except that the lithium salt of the NOx storage material in Example 1 was changed to barium acetate.

【0032】(比較例1)アルミナ100g、チタニア
40gおよびセリウム複合酸化物粉末(実施例1と同
じ)40gをスラリーとしてモノリス担体にコートして
担持層を形成した。この担持層の表面付近に貴金属触媒
のPt/Rhを2/0.1mgの溶液を浸漬担持し、さ
らに実施例1と同じ濃度のNOx吸蔵材の溶液をコート
して比較例1の触媒を得た。
Comparative Example 1 A monolith carrier was coated as a slurry with 100 g of alumina, 40 g of titania, and 40 g of cerium composite oxide powder (same as in Example 1) to form a support layer. A 2 / 0.1 mg solution of a noble metal catalyst, Pt / Rh, was immersed and supported near the surface of the support layer, and was further coated with a solution of a NOx storage material having the same concentration as in Example 1 to obtain a catalyst of Comparative Example 1. Was.

【0033】(比較例2)実施例1において、セリウム
複合酸化物粉末はPtを予め担持してないものを用いた
以外は、実施例1と同様の操作により比較例2の触媒を
作製した。
Comparative Example 2 A catalyst of Comparative Example 2 was prepared in the same manner as in Example 1, except that the cerium composite oxide powder did not previously support Pt.

【0034】(比較例3)実施例1において、NOx吸
蔵材はスラリー中で混合するのでなく他のアルミナ粉末
およびセリウム複合酸化物粉末をモノリス担体にコート
して形成した担持層に後から浸漬法により担持して比較
例3の触媒を作製した。 (触媒の評価)実施例1〜2及び比較例1〜3で得られ
た触媒の排ガス浄化性能は、以下の方法で評価した。
(Comparative Example 3) In Example 1, the NOx occluding material was not mixed in the slurry but instead was immersed in a carrier layer formed by coating another alumina powder and a cerium composite oxide powder on a monolith carrier. To produce a catalyst of Comparative Example 3. (Evaluation of catalyst) The exhaust gas purification performance of the catalysts obtained in Examples 1-2 and Comparative Examples 1-3 was evaluated by the following method.

【0035】排気量4Lのエンジンで800℃×50時
間ストイキF/B(フィードバック)雰囲気で耐久を実
施した結果を表1および図1に示した。評価はトヨタ製
カリーナバン車輌で測定した。評価モードは、欧州での
車輌評価モードで、最後にある高速走行を疑似したモー
ドパターンのECEモードで実施し、EUDC部の排出
値で効果を判定した。
Table 1 and FIG. 1 show the results of endurance tests performed in a stoichiometric F / B (feedback) atmosphere at 800 ° C. for 50 hours using an engine having a displacement of 4 L. Evaluation was measured with a carina van made by Toyota. The evaluation mode was a vehicle evaluation mode in Europe, in which the last high-speed running was performed in an ECE mode with a simulated mode pattern, and the effect was determined based on the emission value of the EUDC unit.

【0036】[0036]

【表1】 [Table 1]

【0037】図1および表1に示したように、実施例1
のNOx浄化性能は比較例1の貴金属を触媒保持層の表
面に浸漬担持させたものに比べて優れていることが分か
る。
As shown in FIG. 1 and Table 1, the first embodiment
It can be seen that the NOx purification performance of Example 2 is superior to that of Comparative Example 1 in which the noble metal was immersed and supported on the surface of the catalyst holding layer.

【0038】上記の条件(800℃×50時間ストイキ
F/B雰囲気)での耐熱試験後のPtの粒径を調べた結
果を表2および図2に示した。(測定方法はX線回折で
得たPtピークの半価幅より算出)。
Table 2 and FIG. 2 show the results of examining the particle size of Pt after the heat resistance test under the above conditions (800 ° C. × 50 hour stoichiometric F / B atmosphere). (The measurement method was calculated from the half width of the Pt peak obtained by X-ray diffraction).

【0039】[0039]

【表2】 [Table 2]

【0040】図2に示したように本発明の貴金属を担持
酸化物粉末中に均一に分散させた実施例1は、貴金属を
担持酸化物粉末の表面にコートした比較例1の場合と比
較して耐熱試験後においてPtの粒径が小さく貴金属の
シンタリングを抑制していることが分かる。
As shown in FIG. 2, Example 1 in which the noble metal of the present invention was uniformly dispersed in the supported oxide powder was compared with Comparative Example 1 in which the surface of the noble metal was coated on the supported oxide powder. Thus, it can be seen that the Pt particle size is small after the heat resistance test and the sintering of the noble metal is suppressed.

【0041】また、耐久試験条件を800−700℃×
20時間、リッチ(1min)−リーン(4min)サイクル
雰囲気で行った際のEUDC−NOxエミッション値を
図3および表3に、貴金属のPtの粒径を図4および表
4に示した。
The durability test conditions were set at 800-700 ° C. ×
FIG. 3 and Table 3 show EUDC-NOx emission values when subjected to a rich (1 min) -lean (4 min) cycle atmosphere for 20 hours, and FIG. 4 and Table 4 show the Pt particle size of the noble metal.

【0042】[0042]

【表3】 [Table 3]

【0043】[0043]

【表4】 [Table 4]

【0044】リッチ(1min)−リーン(4min)サイク
ル雰囲気での耐久試験後においても本発明の実施例1で
は比較例1よりNOxの排出量が少なく、Pt粒径も比
較例1よりも小さい。したがって、貴金属が担体酸化物
粉末中に均一高分散していることの効果を示しおり、そ
のため触媒の高温での耐久性が向上していることを示し
ている。
Even after the durability test in a rich (1 min) -lean (4 min) cycle atmosphere, Example 1 of the present invention has a smaller NOx emission and a smaller Pt particle size than Comparative Example 1 in Comparative Example 1. Therefore, the effect of the noble metal being uniformly and highly dispersed in the carrier oxide powder is shown, which indicates that the durability of the catalyst at high temperatures is improved.

【0045】図5には、排気量4Lのエンジンで800
−700℃×20時間、リッチ(1min)−リーン(4m
in)サイクル雰囲気で行った際のEUDC−NOxエミ
ッション値を示した。
FIG. 5 shows an 800-liter engine with a displacement of 4 liters.
-700 ° C x 20 hours, rich (1min)-lean (4m
in) EUDC-NOx emission values when performed in a cycle atmosphere.

【0046】[0046]

【表5】 [Table 5]

【0047】Pt−Ceの担持部位を同一にしている実
施例1、2は、Ceに直接Ptを担持していない比較例
1、2に比べてNOx排出量が少なくなっていることが
分かる。
It can be seen that Examples 1 and 2 in which the Pt-Ce loading sites are the same have lower NOx emissions than Comparative Examples 1 and 2 in which Pt is not directly loaded on Ce.

【0048】図6および表6には、実施例1と比較例3
について排気量4Lのエンジンで800−700℃×2
0時間、リッチ(1min)−リーン(4min)サイクル雰
囲気で行った際の10.15モードでのNOxとHCの
エミッション値を示した。
FIG. 6 and Table 6 show Example 1 and Comparative Example 3.
About 800-700 ° C x 2 with 4L engine
The emission values of NOx and HC in the 10.15 mode when the operation was performed in a rich (1 min) -lean (4 min) cycle atmosphere for 0 hour are shown.

【0049】NOx吸蔵材を高分散化することで、比較
例3のコート層に後からNOx吸蔵材を担持した比較例
3の触媒と比較して排出量が少なく耐熱性能が向上して
いることが分かる。
By making the NOx storage material highly dispersed, the emission amount is smaller and the heat resistance is improved as compared with the catalyst of Comparative Example 3 in which the NOx storage material is later loaded on the coat layer of Comparative Example 3. I understand.

【0050】[0050]

【表6】 [Table 6]

【0051】図7は600℃、700℃、800℃、9
00℃の各温度で5時間熱処理した後の触媒中に残存し
ているNOx吸蔵材の量を示した。(X線回折法で測定
した)実施例1では800℃における吸蔵材のカリウム
の飛散量が比較例1および比較例3に比べて特に少なく
飛散を抑制していることが分かる。つまりNOx吸蔵材
を高分散化することで、吸蔵材の飛散を抑え、触媒の性
能を向上させることが確認できる。
FIG. 7 shows 600 ° C., 700 ° C., 800 ° C., 9
The amount of the NOx storage material remaining in the catalyst after the heat treatment at each temperature of 00 ° C. for 5 hours is shown. In Example 1 (measured by the X-ray diffraction method), it can be seen that the scattering amount of potassium in the storage material at 800 ° C. was particularly small as compared with Comparative Examples 1 and 3, and the scattering was suppressed. In other words, it can be confirmed that by making the NOx storage material highly dispersed, scattering of the storage material is suppressed and the performance of the catalyst is improved.

【0052】[0052]

【表7】 [Table 7]

【0053】[0053]

【発明の効果】上述したように、本発明の排ガス浄化用
触媒は、触媒金属の貴金属をアルミナ粉末、セリウム粉
末予め担持してNOx吸蔵材と共に触媒保持層に均一に
高分散させたので、貴金属のシンタリングが防止できる
と共に、高温でのNOx吸蔵材の飛散か防止できる。そ
の結果、排ガス浄化用触媒の耐熱性が向上できる。
As described above, in the exhaust gas purifying catalyst of the present invention, the noble metal of the catalyst metal is pre-loaded with alumina powder and cerium powder and uniformly dispersed in the catalyst holding layer together with the NOx storage material. Sintering can be prevented, and scattering of the NOx storage material at high temperatures can be prevented. As a result, the heat resistance of the exhaust gas purifying catalyst can be improved.

【0054】さらに、セリウム酸化物粉末に貴金属を担
持させたことにより、ストイキもしくはリッチ雰囲気で
の還元反応を促進させて、吸蔵したNOxの還元性を高
め、均一に分散した酸化チタン粉末が硫黄による触媒の
被毒を再生するので触媒の耐久性が向上できる。
Further, by supporting the noble metal on the cerium oxide powder, the reduction reaction in a stoichiometric or rich atmosphere is promoted to enhance the reducibility of the stored NOx, and the uniformly dispersed titanium oxide powder is formed by sulfur. Since the poisoning of the catalyst is regenerated, the durability of the catalyst can be improved.

【図面の簡単な説明】[Brief description of the drawings]

【図1】実施例1および比較例1の触媒の800℃50
時間の耐熱試験後のNOxの排出量を示す棒グラフであ
る。
FIG. 1 shows the catalysts of Example 1 and Comparative Example 1 at 800 ° C. 50
It is a bar graph which shows the discharge amount of NOx after the heat resistance test of time.

【図2】実施例1および比較例1の触媒の800℃50
時間の耐熱試験後の触媒貴金属Ptの粒径を示すグラフ
である。
FIG. 2 shows the catalysts of Example 1 and Comparative Example 1 at 800 ° C. 50
It is a graph which shows the particle size of the catalyst noble metal Pt after the heat resistance test of time.

【図3】実施例1および比較例1の触媒の800℃−7
00℃20時間のリッチ−リーンサイクルでの耐熱試験
後のNOxの排出量を示す棒グラフである。
FIG. 3 shows 800 ° C.-7 of the catalysts of Example 1 and Comparative Example 1.
It is a bar graph which shows the NOx discharge amount after the heat test in the rich-lean cycle of 00 degreeC 20 hours.

【図4】実施例1および比較例1の触媒の800℃−7
00℃20時間のリッチ−リーンサイクルでの耐熱試験
後のNOxの触媒貴金属Ptの粒径を示す棒グラフであ
る。
FIG. 4 shows a temperature of 800 ° C.-7 of the catalysts of Example 1 and Comparative Example 1.
It is a bar graph which shows the particle size of catalytic noble metal Pt of NOx after the heat test in a rich-lean cycle of 00 ° C for 20 hours.

【図5】実施例1、実施例2、比較例1、比較例2での
Pt−Ceの担持部位の違いによるNOx排出量を示す
棒グラフである。
FIG. 5 is a bar graph showing NOx emission amounts according to differences in Pt—Ce carrying sites in Example 1, Example 2, Comparative Example 1, and Comparative Example 2.

【図6】実施例1および比較例3の800℃−700℃
20時間のリッチ−リーンサイクルでの耐熱試験後の、
10.15モードでのNOxとHCの排出量を示す棒グ
ラフである。
FIG. 6: 800 ° C. to 700 ° C. in Example 1 and Comparative Example 3
After a heat test in a 20-hour rich-lean cycle,
It is a bar graph which shows the emission amount of NOx and HC in 10.15 mode.

【図7】実施例2、比較例1および比較例3の触媒入り
ガス温度とNOx吸蔵材の飛散量との関係を示すグラフ
である。
FIG. 7 is a graph showing the relationship between the catalyst-containing gas temperature and the amount of NOx storage material scattered in Example 2, Comparative Examples 1 and 3.

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Claims (6)

【特許請求の範囲】[Claims] 【請求項1】担体と前記担体上に形成された触媒保持層
とを持つNOx吸蔵還元型触媒であって、 前記触媒保持層は、予め貴金属が担持されたアルミナ粉
末と、酸化チタン粉末と、貴金属が担持されたセリウム
酸化物粉末と、該アルミナ粉末、該酸化チタン粉末、該
セリウム酸化物とに担持されたNOx吸蔵性のアルカリ
金属塩、アルカリ土類金属塩の少なくとも1種とからな
り、該アルカリ金属塩、アルカリ土類金属塩の少なくと
も1種は該アルミナ粉末、該酸化チタン粉末、該セリウ
ム酸化物が分散したスラリー水溶液に溶解した状態で担
持されたものであることを特徴とする排ガス浄化用触
媒。
1. A NOx occlusion reduction type catalyst having a carrier and a catalyst holding layer formed on the carrier, wherein the catalyst holding layer comprises alumina powder on which a noble metal is previously supported, titanium oxide powder, A cerium oxide powder carrying a noble metal, and the alumina powder, the titanium oxide powder, at least one of an alkali metal salt of NOx storage ability and an alkaline earth metal salt carried on the cerium oxide, An exhaust gas characterized in that at least one of the alkali metal salt and the alkaline earth metal salt is supported in a state of being dissolved in an aqueous slurry solution in which the alumina powder, the titanium oxide powder, and the cerium oxide are dispersed. Purification catalyst.
【請求項2】前記触媒保持層は、該アルミナ粉末、該酸
化チタン粉末、該セリウム酸化物およびNOx吸蔵性の
該アルカリ金属塩、アルカリ土類金属塩の少なくとも1
種が、スラリー中で機械的に強制粉砕混合され各構成成
分が均一に分散している請求項1に記載の排ガス浄化用
触媒。
2. The catalyst holding layer comprises at least one of the alumina powder, the titanium oxide powder, the cerium oxide, and the alkali metal salt or alkaline earth metal salt having NOx storage properties.
2. The exhaust gas purifying catalyst according to claim 1, wherein the seeds are mechanically comminuted and mixed in a slurry, and each component is uniformly dispersed.
【請求項3】前記アルミナ粉末に担持された貴金属は、
白金およびロジウムである請求項1に記載の排ガス浄化
用触媒。
3. The noble metal supported on the alumina powder,
The exhaust gas purifying catalyst according to claim 1, which is platinum and rhodium.
【請求項4】前記セリウム酸化物に担持された貴金属
は、白金である請求項1に記載の排ガス浄化用触媒。
4. The exhaust gas purifying catalyst according to claim 1, wherein the noble metal supported on the cerium oxide is platinum.
【請求項5】前記セリウム酸化物は、セリウム酸化物あ
るいはジルコニウムとの複合酸化物である請求項1に記
載の排ガス浄化用触媒。
5. The exhaust gas purifying catalyst according to claim 1, wherein the cerium oxide is a composite oxide with cerium oxide or zirconium.
【請求項6】前記NOx吸蔵性のアルカリ金属、アルカ
リ土類金属塩の少なくとも1種は、バリウム、マグネシ
ウム、リチウム、ナトリウム、カリウムである請求項1
に記載の排ガス浄化用触媒。
6. The NOx-storing alkali metal or alkaline earth metal salt of at least one of barium, magnesium, lithium, sodium and potassium.
An exhaust gas purifying catalyst according to claim 1.
JP33823899A 1999-11-29 1999-11-29 Exhaust gas purification catalyst Expired - Fee Related JP4368991B2 (en)

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Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002361094A (en) * 2001-06-08 2002-12-17 Mitsubishi Motors Corp Catalyst for cleaning exhaust gas
JP2006095474A (en) * 2004-09-30 2006-04-13 Matsushita Electric Ind Co Ltd Exhaust gas cleaning material
WO2011030831A1 (en) * 2009-09-10 2011-03-17 株式会社 キャタラー Catalyst for exhaust gas purification

Cited By (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002361094A (en) * 2001-06-08 2002-12-17 Mitsubishi Motors Corp Catalyst for cleaning exhaust gas
JP4645786B2 (en) * 2001-06-08 2011-03-09 三菱自動車工業株式会社 Exhaust gas purification catalyst
JP2006095474A (en) * 2004-09-30 2006-04-13 Matsushita Electric Ind Co Ltd Exhaust gas cleaning material
JP4687057B2 (en) * 2004-09-30 2011-05-25 パナソニック株式会社 Exhaust gas purification material
WO2011030831A1 (en) * 2009-09-10 2011-03-17 株式会社 キャタラー Catalyst for exhaust gas purification
CN102481548A (en) * 2009-09-10 2012-05-30 株式会社科特拉 Catalyst For Exhaust Gas Purification
US20120149557A1 (en) * 2009-09-10 2012-06-14 Sho Hoshino Exhaust gas-purifying catalyst
JPWO2011030831A1 (en) * 2009-09-10 2013-02-07 株式会社キャタラー Exhaust gas purification catalyst
US8569198B2 (en) 2009-09-10 2013-10-29 Cataler Corporation Exhaust gas-purifying catalyst
JP5690736B2 (en) * 2009-09-10 2015-03-25 株式会社キャタラー Exhaust gas purification catalyst and method for producing the same
CN102481548B (en) * 2009-09-10 2015-09-16 株式会社科特拉 Exhaust gas purification catalyst

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