JP2006198490A - Exhaust gas cleaning catalyst, its manufacturing method and exhaust gas cleaning method - Google Patents

Exhaust gas cleaning catalyst, its manufacturing method and exhaust gas cleaning method Download PDF

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JP2006198490A
JP2006198490A JP2005011079A JP2005011079A JP2006198490A JP 2006198490 A JP2006198490 A JP 2006198490A JP 2005011079 A JP2005011079 A JP 2005011079A JP 2005011079 A JP2005011079 A JP 2005011079A JP 2006198490 A JP2006198490 A JP 2006198490A
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exhaust gas
purifying catalyst
precursor
carrier
alloy particles
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JP4611038B2 (en
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Hideji Fujii
秀治 藤井
Masatoshi Katsuki
将利 勝木
Yasuhiko Tsuru
靖彦 水流
Katsumi Noji
勝己 野地
Akihiro Sawada
明宏 沢田
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Mitsubishi Heavy Industries Ltd
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Abstract

<P>PROBLEM TO BE SOLVED: To provide an exhaust gas cleaning catalyst capable of efficiently performing the decomposition treatment of nitrogen oxide over the whole temperature range of the exhaust gas discharged from a diesel engine or the like, its manufacturing method and an exhaust gas cleaning method. <P>SOLUTION: A solution, in which metal components are dissolved, is added to a precursor 111a in an amorphous state of a carrier 111 comprising an oxide to hold a plurality of the metal components 112a and 112b on the precursor 111a and this precursor 111a is heat-treated in a non-oxidizing atmosphere such as a nitrogen gas or the like and changed structurally to obtain the exhaust gas cleaning catalyst wherein alloy particles with a particle size of 100 nm or below composed of a solid solution of a plurality of the metal components 112a and 112b are supported on the carrier 111 comprising the oxide. <P>COPYRIGHT: (C)2006,JPO&NCIPI

Description

本発明は、ディーゼルエンジン等から排出される排ガス中の窒素酸化物を分解処理する排ガス浄化用触媒並びに排ガス浄化用触媒の製造方法及び排ガス浄化方法に関する。   The present invention relates to an exhaust gas purifying catalyst for decomposing nitrogen oxides in exhaust gas discharged from a diesel engine or the like, a method for producing an exhaust gas purifying catalyst, and an exhaust gas purifying method.

ディーゼルエンジン等から排出される排ガス中の窒素酸化物を分解処理する排ガス浄化用触媒としては、酸化チタン等の金属酸化物からなる担体にPt,Pd,Au,Rh,Ag,Ir等の金属粒子を単独又は組み合わせて担持させたものが用いられている。   As an exhaust gas purifying catalyst for decomposing nitrogen oxides in exhaust gas discharged from a diesel engine, etc., metal particles such as Pt, Pd, Au, Rh, Ag, Ir, etc. on a carrier made of a metal oxide such as titanium oxide. Are used alone or in combination.

このような排ガス浄化用触媒としては、例えば、担体に金属粒子を付着させた後、当該金属粒子と異なる種類の金属相を当該金属粒子の表面の一部を被覆するように当該金属粒子の表面に還元析出させたものが知られている(例えば、下記特許文献1,2等参照)。   As such an exhaust gas purifying catalyst, for example, after the metal particles are attached to the carrier, the surface of the metal particles is coated so that a part of the surface of the metal particles is coated with a different type of metal phase from the metal particles. In this regard, a product obtained by reducing and precipitating is known (for example, see Patent Documents 1 and 2 below).

特開平11−156193号公報JP-A-11-156193 特開平11−347424号公報JP-A-11-347424

ところで、ディーゼルエンジン等から排出される排ガスは、ディーゼルエンジン等の負荷具合により温度が幅広く変動する(約250〜450℃)。このため、ディーゼルエンジン等から排出される排ガス中の窒素酸化物を分解処理する排ガス浄化用触媒においては、当該ディーゼルエンジン等から排出される排ガスの温度領域全体にわたって効率よく作用できることが強く求められる。しかしながら、前述したような特許文献1,2等に記載されている排ガス浄化用触媒においては、上述したような幅広い温度領域全体にわたって窒素酸化物の分解処理を効率よく発現することができていなかった。   By the way, the temperature of exhaust gas discharged from a diesel engine or the like varies widely depending on the load condition of the diesel engine or the like (about 250 to 450 ° C.). For this reason, an exhaust gas purifying catalyst that decomposes nitrogen oxides in exhaust gas discharged from a diesel engine or the like is strongly required to be able to act efficiently over the entire temperature range of the exhaust gas discharged from the diesel engine or the like. However, in the exhaust gas purifying catalyst described in Patent Documents 1 and 2 and the like as described above, the decomposition treatment of nitrogen oxides could not be efficiently expressed over the wide temperature range as described above. .

このようなことから、本発明は、ディーゼルエンジン等から排出される排ガスの温度領域全体にわたって窒素酸化物の分解処理を効率よく発現することができる排ガス浄化用触媒並びにその製造方法及びその触媒を使用する排ガス浄化方法を提供することを目的とする。   Therefore, the present invention uses an exhaust gas purifying catalyst capable of efficiently expressing the decomposition treatment of nitrogen oxide over the entire temperature range of exhaust gas discharged from a diesel engine or the like, a method for producing the same, and a catalyst using the catalyst. An object of the present invention is to provide a method for purifying exhaust gas.

前述した課題を解決するための、本発明に係る排ガス浄化用触媒は、酸化物からなる担体と、前記担体に担持され、複数の金属成分を固溶させた合金粒子とを備え、前記合金粒子の粒径が100nm以下であることを特徴とする。   An exhaust gas purifying catalyst according to the present invention for solving the above-mentioned problems comprises a support made of an oxide, and alloy particles supported on the support and having a plurality of metal components dissolved therein, The particle size is 100 nm or less.

また、本発明に係る排ガス浄化用触媒は、上述において、前記担体が、TiO2,SiO2,Al23,ZrO2,CaO,MgO,SnO2,ZnOのうちの少なくとも二種以上の複合酸化物からなることを特徴とする。 In the exhaust gas purifying catalyst according to the present invention, the carrier is a composite of at least two of TiO 2 , SiO 2 , Al 2 O 3 , ZrO 2 , CaO, MgO, SnO 2 and ZnO. It consists of an oxide.

また、本発明に係る排ガス浄化用触媒は、上述において、前記合金粒子が、Pt,Ir,Pd,Rh,Ru,Au,Agのうちの少なくとも二種以上の固溶体であることを特徴とする。   The exhaust gas purifying catalyst according to the present invention is characterized in that, in the above, the alloy particles are solid solutions of at least two kinds of Pt, Ir, Pd, Rh, Ru, Au, and Ag.

また、本発明に係る排ガス浄化用触媒は、上述において、前記合金粒子が、少なくともIrを含む二種の金属成分の固溶体であると共に、10nm以上の粒径を有していることを特徴とする。   The exhaust gas purifying catalyst according to the present invention is characterized in that, in the above, the alloy particles are solid solutions of at least two kinds of metal components containing Ir and have a particle size of 10 nm or more. .

また、本発明に係る排ガス浄化用触媒は、上述において、前記合金粒子が、前記担体に対して0.1〜5wt%の割合で担持されていることを特徴とする。   The exhaust gas purifying catalyst according to the present invention is characterized in that, in the above, the alloy particles are supported at a ratio of 0.1 to 5 wt% with respect to the carrier.

他方、本発明に係る排ガス浄化用触媒の製造方法は、上述した本発明に係る排ガス浄化用触媒の製造方法であって、酸化物からなる前記担体のアモルファス状態の前駆体に、金属成分の溶解した溶液を含有させて当該前駆体に複数の金属成分を保持させた後、当該前駆体を非酸化雰囲気中で加熱処理して構造変化させることにより、酸化物からなる前記担体に、複数の前記金属成分を固溶させた前記合金粒子を担持させることを特徴とする。   On the other hand, the method for producing an exhaust gas purifying catalyst according to the present invention is the above-described method for producing an exhaust gas purifying catalyst according to the present invention, wherein a metal component is dissolved in an amorphous precursor of the carrier made of an oxide. The precursor is made to contain a plurality of metal components in the precursor, and then the precursor is heat-treated in a non-oxidizing atmosphere to change the structure. The alloy particles in which the metal component is dissolved are supported.

また、本発明に係る排ガス浄化用触媒の製造方法は、上述において、前記非酸化雰囲気が、還元性ガス及び不活性ガスの少なくとも一方からなることを特徴とする。   In the above-described method for producing an exhaust gas purifying catalyst according to the present invention, the non-oxidizing atmosphere includes at least one of a reducing gas and an inert gas.

また、本発明に係る排ガス浄化用触媒の製造方法は、上述において、前記非酸化雰囲気が、水蒸気を含有していることを特徴とする。   In the above-described method for producing an exhaust gas purifying catalyst according to the present invention, the non-oxidizing atmosphere contains water vapor.

さらに、本発明に係る排ガス浄化方法は、上述した本発明に係る排ガス浄化用触媒と排ガスとを接触させて当該排ガス中の窒素酸化物を分解処理することを特徴とする。   Furthermore, the exhaust gas purification method according to the present invention is characterized in that the exhaust gas purification catalyst according to the present invention and the exhaust gas are brought into contact with each other to decompose nitrogen oxides in the exhaust gas.

また、本発明に係る排ガス浄化方法は、上述において、前記排ガスが、ディーゼルエンジンから排出された250〜450℃の温度のガスであることを特徴とする。   The exhaust gas purification method according to the present invention is characterized in that, in the above, the exhaust gas is a gas having a temperature of 250 to 450 ° C. discharged from a diesel engine.

本発明に係る排ガス浄化用触媒によれば、粒径が100nm以下で複数の金属成分を固溶させた合金粒子を担体が担持したものなので、250〜450℃の広い温度領域全体にわたって窒素酸化物の分解処理を効率よく行うことができる。   According to the exhaust gas purifying catalyst of the present invention, since the carrier supports alloy particles having a particle size of 100 nm or less and in which a plurality of metal components are solid-solved, nitrogen oxides over a wide temperature range of 250 to 450 ° C. Can be efficiently performed.

また、本発明に係る排ガス浄化用触媒の製造方法によれば、本発明に係る排ガス浄化用触媒を容易に製造することができる。   Moreover, according to the method for producing an exhaust gas purifying catalyst according to the present invention, the exhaust gas purifying catalyst according to the present invention can be easily produced.

また、本発明に係る排ガス浄化方法によれば、負荷具合により温度が幅広く変動するディーゼルエンジン等からの排ガスであっても、当該排ガスの温度領域全体にわたって窒素酸化物を効率よく分解処理することができる。   In addition, according to the exhaust gas purification method of the present invention, nitrogen oxides can be efficiently decomposed over the entire temperature range of the exhaust gas, even if the exhaust gas is from a diesel engine whose temperature varies widely depending on the load condition. it can.

本発明に係る排ガス浄化用触媒並びに排ガス浄化用触媒の製造方法及び排ガス浄化方法の実施形態を図1,2に基づいて説明する。図1は、排ガス浄化用触媒の製造方法の手順を表わすフロー図、図2は、排ガス浄化用触媒の製造方法の説明図である。   An embodiment of an exhaust gas purifying catalyst, an exhaust gas purifying catalyst manufacturing method and an exhaust gas purifying method according to the present invention will be described with reference to FIGS. FIG. 1 is a flowchart showing the procedure of a method for producing an exhaust gas purification catalyst, and FIG. 2 is an explanatory diagram of the method for producing an exhaust gas purification catalyst.

本実施形態に係る排ガス浄化用触媒は、酸化物からなる担体と、担体に担持されて複数の金属成分を固溶させた合金粒子とを備え、合金粒子の粒径が100nm以下(より好ましくは50nm以下)となっているものである。   The exhaust gas purifying catalyst according to the present embodiment includes a support made of an oxide, and alloy particles supported on the support and having a plurality of metal components dissolved therein, and the alloy particles have a particle size of 100 nm or less (more preferably 50 nm or less).

ここで、上記合金粒子の粒径が、100nmを超えると、合金粒子の重量増加に対する表面積が少なくなり過ぎてしまい、流動する排ガス中の窒素酸化物を分解処理するにあたって十分な触媒機能を発現することができなくなってしまうため、適用することができない。   Here, if the particle size of the alloy particles exceeds 100 nm, the surface area for the increase in the weight of the alloy particles becomes too small, and a sufficient catalytic function is exhibited in decomposing nitrogen oxides in the flowing exhaust gas. Cannot be applied.

また、上記担体が、TiO2,SiO2,Al23,ZrO2,CaO,MgO,SnO2,ZnOのうちの少なくとも二種以上の複合酸化物からなると好ましく、特に、上記酸化物のうちの二種を組み合わせて、一方を5〜95mol%とし、他方を残りの割合とすると、安定した複合酸化物を得ることができるので好ましい。 The carrier is preferably composed of a composite oxide of at least two of TiO 2 , SiO 2 , Al 2 O 3 , ZrO 2 , CaO, MgO, SnO 2 and ZnO. It is preferable to combine the above two types so that one is in the range of 5 to 95 mol% and the other is in the remaining ratio because a stable composite oxide can be obtained.

さらに、TiO2とZrO2との組み合わせや(特に、45〜55mol%:45〜55mol%の割合の場合)、TiO2とSiO2との組み合わせ(特に、85〜95mol%:5〜15mol%の割合の場合)であると、複合化による酸点の増加が非常に大きくなり、脱硝性能を大きく向上できるため、非常に好ましい。 Further, a combination of TiO 2 and ZrO 2 (especially in the case of a ratio of 45 to 55 mol%: 45 to 55 mol%), a combination of TiO 2 and SiO 2 (especially 85 to 95 mol%: 5 to 15 mol%). In the case of the ratio), the increase in the acid point due to the combination becomes very large, and the denitration performance can be greatly improved, which is very preferable.

また、上記合金粒子が、Pt,Ir,Pd,Rh,Ru,Au,Agのうちの少なくとも二種以上の固溶体であると好ましく、特に、上記金属成分のうちの二種を組み合わせて、一方を20〜80wt%とし、他方を残りの割合とすると、安定した合金粒子を得ることができるので好ましい。   The alloy particles are preferably a solid solution of at least two of Pt, Ir, Pd, Rh, Ru, Au, and Ag. In particular, two of the metal components are combined and one of them is combined. It is preferable that the content is 20 to 80 wt% and the other is the remaining ratio because stable alloy particles can be obtained.

さらに、上記合金粒子が、少なくともIrを含む二種の金属成分の固溶体、例えば、IrとPtとの組み合わせや(特に、50〜80wt%:20〜50wt%の割合の場合)、IrとRhとの組み合わせ(特に、50〜80wt%:20〜50wt%の割合の場合)であると、350℃以上の高温での脱硝性能を大きく向上できるため、非常に好ましい。なお、Irを含む合金粒子の場合には、当該合金粒子の粒径が10nm以上であると、触媒活性が特に高くなるため、非常に好ましい。   Further, the alloy particles may be a solid solution of two kinds of metal components containing at least Ir, for example, a combination of Ir and Pt (especially in the case of 50 to 80 wt%: 20 to 50 wt%), Ir and Rh, The combination (particularly in the case of 50 to 80 wt%: 20 to 50 wt%) is very preferable because the denitration performance at a high temperature of 350 ° C. or higher can be greatly improved. In the case of alloy particles containing Ir, it is very preferable that the particle size of the alloy particles is 10 nm or more because the catalytic activity is particularly high.

また、上記合金粒子が、上記担体に対して0.1〜5wt%の割合で担持されていると好ましく、特に、1〜3wt%の割合であると非常に好ましい。なぜなら、担体に対する合金粒子の担持量が、0.1wt%未満であると、触媒としての機能を十分に発現することが難しくなり、5wt%を超えると、触媒作製の際に合金粒子の粒径が100nmを超える可能性が非常に高くなってしまうからである。   The alloy particles are preferably supported at a rate of 0.1 to 5 wt% with respect to the support, and particularly preferably at a rate of 1 to 3 wt%. This is because if the amount of the alloy particles supported on the support is less than 0.1 wt%, it is difficult to fully exhibit the function as a catalyst, and if it exceeds 5 wt%, the particle size of the alloy particles during catalyst preparation This is because the possibility of exceeding 100 nm becomes very high.

このような本実施形態に係る排ガス浄化用触媒の製造方法は、図1,2に示すように、酸化物からなる担体のアモルファス状態の前駆体111aを作製し(図1のS1、図2の(a))、複数の金属成分112a,112bの溶解した溶液を当該前駆体111aに含浸させて乾燥させることにより、前駆体111aに複数の金属成分112a,112b(粒径1nm以下)をそれぞれ保持させた後(図1のS2、図2の(b))、当該前駆体111aを非酸化雰囲気中で加熱処理して構造変化させることにより(図1のS3)、酸化物からなる担体111に、複数の前記金属成分112a,112bが固溶した合金粒子112(粒径100nm以下)を担持させた排ガス浄化用触媒110を容易に得ることができる(図2の(c))。   As shown in FIGS. 1 and 2, the manufacturing method of the exhaust gas purifying catalyst according to the present embodiment produces an amorphous precursor 111a of a carrier made of an oxide (S1 in FIG. 1, FIG. 2). (A)) A solution in which a plurality of metal components 112a and 112b are dissolved is impregnated in the precursor 111a and dried to hold the plurality of metal components 112a and 112b (particle size of 1 nm or less) in the precursor 111a. (S2 in FIG. 1, (b) in FIG. 2), the precursor 111a is heat-treated in a non-oxidizing atmosphere to change the structure (S3 in FIG. 1), thereby forming the oxide carrier 111. Further, it is possible to easily obtain the exhaust gas purifying catalyst 110 supporting the alloy particles 112 (particle size of 100 nm or less) in which the plurality of metal components 112a and 112b are solid-solved ((c) in FIG. 2).

ここで、上記担体の原料(前駆体の原料)としては、例えば、各種の塩化物や硝酸塩や硫酸塩等が挙げられる。具体的には、例えば、TiO2の場合には、TiCl4,TiOSO3等が挙げられ、SiO2の場合には、水ガラスやシリカゾル等が挙げられ、Al23の場合には、AlCl3等が挙げられ、ZrO2の場合には、ZrOCl2等が挙げられ、CaOの場合には、CaCl2,Ca(NO32等が挙げられ、MgOの場合には、MgCl2,Mg(NO32等が挙げられ、SnO2の場合には、SnCl2等が挙げられ、ZnOの場合には、ZnCl2等が挙げられる。 Here, examples of the raw material of the carrier (precursor raw material) include various chlorides, nitrates, sulfates, and the like. Specifically, for example, in the case of TiO 2 , TiCl 4 , TiOSO 3 and the like are mentioned, in the case of SiO 2 , water glass, silica sol and the like are mentioned, and in the case of Al 2 O 3 , AlCl 3 is mentioned. In the case of ZrO 2 , ZrOCl 2 and the like are mentioned. In the case of CaO, CaCl 2 and Ca (NO 3 ) 2 are mentioned, and in the case of MgO, MgCl 2 and Mg (NO 3 ) 2 and the like are mentioned. In the case of SnO 2 , SnCl 2 and the like are mentioned, and in the case of ZnO, ZnCl 2 and the like are mentioned.

これら原料を水中に所定の割合で混合溶解し、アンモニア水等を加えて撹拌することにより、これら原料の複合水酸化物と推察される沈殿物(担体のアモルファス状態の前駆体)が生成し、固液分離して固体分を乾燥させることにより、担体のアモルファス状態の前駆体を得ることができる。   By mixing and dissolving these raw materials in water at a predetermined ratio, adding ammonia water or the like and stirring, precipitates (amorphous precursor of the carrier) presumed to be composite hydroxides of these raw materials are generated, The precursor in the amorphous state of the carrier can be obtained by solid-liquid separation and drying the solid content.

また、上記金属成分の原料としては、例えば、各種の塩化物や硝酸塩やアンモニウム塩等が挙げられる。具体的には、例えば、Ptの場合には、H2PtCl6,Pt(NH34(OH)2等が挙げられ、Irの場合には、H2IrCl6,Ir(NH36Cl3等が挙げられ、Pdの場合には、H2PdCl4,Pd(NH32(NO22aq,Pd(NO3)等が挙げられ、Rhの場合には、H2RhCl6,Rh(NO33等が挙げられ、Ruの場合には、H2RuCl5,Ru(NO33等が挙げられ、Auの場合には、HAuCl4aq等が挙げられ、Agの場合には、AgNO3等が挙げられる。 Moreover, as a raw material of the said metal component, various chlorides, nitrate, ammonium salt etc. are mentioned, for example. Specifically, for example, in the case of Pt, H 2 PtCl 6 , Pt (NH 3 ) 4 (OH) 2 and the like can be mentioned, and in the case of Ir, H 2 IrCl 6 , Ir (NH 3 ) 6 Cl 3 and the like are mentioned. In the case of Pd, H 2 PdCl 4 , Pd (NH 3 ) 2 (NO 2 ) 2 aq, Pd (NO 3 ) and the like are mentioned. In the case of Rh, H 2 RhCl 6 , Rh (NO 3 ) 3 and the like. In the case of Ru, H 2 RuCl 5 , Ru (NO 3 ) 3 and the like are mentioned. In the case of Au, HAuCl 4 aq and the like are mentioned. In this case, AgNO 3 and the like can be mentioned.

これら原料を水中に所定の割合で混合溶解し、当該水溶液を前記前駆体に含浸させて当該前駆体を乾燥させることにより、当該前駆体に前記原料が保持され、これを加熱処理(予熱処理)することにより、前駆体に各金属成分(粒径1nm以下)を保持させることが容易にできる。   These raw materials are mixed and dissolved in water at a predetermined ratio, the precursor is impregnated with the aqueous solution, and the precursor is dried, whereby the precursor is held in the precursor, and this is subjected to heat treatment (pre-heat treatment). By doing, each metal component (particle size of 1 nm or less) can be easily held in the precursor.

なお、上記非酸化雰囲気とは、酸素ガスを含まないガス雰囲気のことであり、例えば、水素ガス等の還元性ガスや、窒素ガスやヘリウムガスやアルゴンガス等の不活性ガスや、これら還元性ガスと不活性ガスとの混合ガスや、これらガスに水蒸気を加えたもの等が挙げられる。   The non-oxidizing atmosphere is a gas atmosphere that does not contain oxygen gas. For example, a reducing gas such as hydrogen gas, an inert gas such as nitrogen gas, helium gas, or argon gas, or these reducing gases. Examples thereof include a mixed gas of a gas and an inert gas, and those obtained by adding water vapor to these gases.

このようにして製造される本実施形態に係る排ガス浄化用触媒においては、ディーゼルエンジン等から排出される排ガスと接触することにより、当該排ガス中の窒素酸化物を分解処理することができる。   In the exhaust gas purifying catalyst according to this embodiment manufactured as described above, the nitrogen oxide in the exhaust gas can be decomposed by contacting with the exhaust gas discharged from a diesel engine or the like.

このとき、ディーゼルエンジン等から排出される排ガスは、ディーゼルエンジン等の負荷具合により温度が幅広く変動するものの(約250〜450℃)、本実施形態に係る排ガス浄化用触媒においては、当該排ガスの温度領域(約250〜450℃)全体にわたって窒素酸化物を効率よく分解処理することができる。この理由を以下に説明する。   At this time, although the exhaust gas discharged from the diesel engine or the like varies widely in temperature depending on the load condition of the diesel engine or the like (about 250 to 450 ° C.), in the exhaust gas purifying catalyst according to the present embodiment, the temperature of the exhaust gas. Nitrogen oxide can be efficiently decomposed over the entire region (about 250 to 450 ° C.). The reason for this will be described below.

触媒活性を示す金属成分は、活性を発現する温度が元素の種類ごとに異なっている。このような活性発現温度が異なる複数種の金属成分を固溶化させた合金粒子においては、これら金属成分が相溶して異なる結晶構造となるため、その組成成分の各元素の活性発現温度と異なる温度で活性を発現するが、その活性発現温度幅はほとんど変化しないものと考えられていた。   The metal component exhibiting catalytic activity differs in temperature at which activity is manifested for each element type. In such alloy particles in which a plurality of types of metal components having different activity expression temperatures are solidified, these metal components are mixed together to have different crystal structures, and therefore differ from the activity expression temperature of each element of the composition component. Although the activity was expressed at the temperature, it was considered that the temperature range of the activity expression hardly changed.

ところが、本願発明者らが鋭意研究を行ったところ、活性発現温度が異なる複数種の金属成分を固溶化させた合金粒子においては、その合金粒子の組成成分の各元素の活性発現温度と異なる温度で活性を発現するばかりか、その活性発現温度幅が著しく増大するという知見を得ることができた。   However, when the inventors of the present application have conducted intensive research, in alloy particles in which a plurality of types of metal components having different activity expression temperatures are solid-solubilized, a temperature different from the activity expression temperature of each element of the composition component of the alloy particles. In addition to expressing the activity, it was possible to obtain the knowledge that the temperature range of the activity expression markedly increased.

よって、このように活性発現温度幅が著しく増大した合金成分を担体に担持させた触媒を、ディーゼルエンジン等から排出される排ガスのように温度が幅広く変動するガス中の窒素酸化物の分解処理に利用することにより、当該排ガスの温度領域(約250〜450℃)全体にわたって窒素酸化物を効率よく分解処理することが可能となるのである。   Therefore, the catalyst in which the alloy component whose activity expression temperature range is remarkably increased is supported on the carrier is used for the decomposition treatment of nitrogen oxide in the gas whose temperature fluctuates widely such as exhaust gas discharged from a diesel engine or the like. By using it, it becomes possible to efficiently decompose nitrogen oxides over the entire temperature range (about 250 to 450 ° C.) of the exhaust gas.

ところで、ディーゼルエンジン等から排出される排ガス中の窒素酸化物等を分解処理する触媒においては、比較的高速度で流動排出される排ガスと効率よく接触して窒素酸化物を分解処理しなければならないため、合金粒子が非常に大きな表面積、すなわち、非常に小さい粒径、具体的には100nm以下である必要がある。   By the way, in a catalyst that decomposes nitrogen oxides or the like in exhaust gas discharged from a diesel engine or the like, nitrogen oxides must be decomposed by efficiently contacting with exhaust gas flowing and discharged at a relatively high speed. Therefore, the alloy particles need to have a very large surface area, that is, a very small particle size, specifically, 100 nm or less.

しかしながら、100nm以下の非常に小さい粒径の合金粒子を作製することは非常に難しいのはもちろんのこと、100nm以下の粒径の合金粒子をたとえ作製したとしても、合金粒子を凝集させることなく担体にムラなく担持させることが極めて困難になってしまう。   However, it is very difficult to produce alloy particles having a very small particle size of 100 nm or less, and even if alloy particles having a particle size of 100 nm or less are produced, the carrier is not aggregated. It becomes extremely difficult to carry the film uniformly.

そこで、本願発明者らがさらに鋭意研究を行った結果、先ず、酸化物からなる担体のアモルファス状態の前駆体を作製し、金属成分の溶解した溶液を当該前駆体に含有させて複数の金属成分を保持させた後、当該前駆体を非酸化雰囲気中で加熱処理して構造変化させると、酸化物からなる担体に、複数の前記金属成分の固溶した100nm以下の粒径の合金粒子が担持された排ガス浄化用触媒を容易に得られることを見出したのである。   Therefore, as a result of further diligent research conducted by the inventors of the present application, first, an amorphous precursor of a support made of an oxide is prepared, and a solution in which a metal component is dissolved is contained in the precursor to thereby add a plurality of metal components. Then, when the precursor is heat-treated in a non-oxidizing atmosphere to change the structure, a plurality of alloy particles having a particle size of 100 nm or less in which a plurality of the metal components are dissolved are supported on the oxide support. It has been found that an exhaust gas purifying catalyst can be easily obtained.

このような製造方法により、酸化物からなる担体に、複数の金属成分の固溶した100nm以下の粒径の合金粒子を担持した排ガス浄化用触媒が容易に得られる理由は定かではないが、金属成分の溶解した溶液を前駆体に含有させることにより、前駆体に微小な金属成分(1nm以下)が保持され、この前駆体を構造変化させるように加熱処理すると、当該前駆体の分子構造の変移(結晶化)に伴って、当該金属成分が移動して、近傍に位置する金属成分と相溶して、適切な粒径(100nm以下)の合金粒子となるからではないか、と推察される。   The reason why an exhaust gas-purifying catalyst in which an alloy particle having a particle diameter of 100 nm or less in which a plurality of metal components are dissolved in a carrier made of an oxide is easily obtained by such a manufacturing method is not clear. By containing a solution in which a component is dissolved in the precursor, a minute metal component (1 nm or less) is retained in the precursor, and when the precursor is heat-treated to change the structure, the molecular structure of the precursor is changed. It is inferred that (with crystallization), the metal component moves and becomes compatible with the metal component located in the vicinity, resulting in alloy particles having an appropriate particle size (100 nm or less). .

また、上記加熱処理を酸化雰囲気(酸素ガスを含有する雰囲気)で行うと、合金粒子が生成せず、各金属成分が単に成長した各金属成分の粒子が生成するだけとなってしまう。この理由も定かではないが、上記加熱処理を酸化雰囲気(酸素ガスを含有する雰囲気)で行うと、各金属成分の表面に酸化被膜が形成されて、種類の異なる金属成分間での相溶性が著しく低下してしまうからではないか、と推察される。   Moreover, when the heat treatment is performed in an oxidizing atmosphere (an atmosphere containing oxygen gas), alloy particles are not generated, and only metal components particles in which each metal component is grown are generated. Although the reason for this is not clear, when the heat treatment is performed in an oxidizing atmosphere (an atmosphere containing oxygen gas), an oxide film is formed on the surface of each metal component, and compatibility between different types of metal components is increased. It is speculated that it may be significantly reduced.

したがって、本実施形態に係る排ガス浄化用触媒によれば、250〜450℃の広い温度領域全体にわたって窒素酸化物の分解処理を効率よく行うことができ、本実施形態に係る排ガス浄化用触媒の製造方法によれば、本実施形態に係る排ガス浄化用触媒を容易に製造することができ、本実施形態に係る排ガス浄化方法によれば、負荷具合により温度が幅広く変動するディーゼルエンジン等からの排ガスであっても、当該排ガスの温度領域全体にわたって窒素酸化物を効率よく分解処理することができるのである。   Therefore, according to the exhaust gas purifying catalyst according to the present embodiment, it is possible to efficiently perform the decomposition treatment of nitrogen oxide over the wide temperature range of 250 to 450 ° C., and manufacture of the exhaust gas purifying catalyst according to the present embodiment. According to the method, the exhaust gas purifying catalyst according to the present embodiment can be easily manufactured. According to the exhaust gas purifying method according to the present embodiment, exhaust gas from a diesel engine or the like whose temperature varies widely depending on the load condition. Even if it exists, a nitrogen oxide can be efficiently decomposed | disassembled over the whole temperature range of the said waste gas.

本発明に係る排ガス浄化用触媒並びに排ガス浄化用触媒の製造方法及び排ガス浄化方法の効果を確認するため、以下のような実験を行った。   In order to confirm the effects of the exhaust gas purifying catalyst, the exhaust gas purifying catalyst manufacturing method and the exhaust gas purifying method according to the present invention, the following experiments were conducted.

[A.触媒の製造]
〈試験体1〉
TiとZrとのモル比が50:50となるように、TiCl4水溶液とZrOCl2水溶液とを混合してアンモニア水溶液を加えて撹拌し、生成した沈殿物を濾別して乾燥(120℃×2時間)することにより、酸化物からなる担体のアモルファス状態の前駆体(TiO2−ZrO2の水酸化物)を作製する。
[A. Production of catalyst]
<Test body 1>
A TiCl 4 aqueous solution and a ZrOCl 2 aqueous solution are mixed so that the molar ratio of Ti and Zr is 50:50, an aqueous ammonia solution is added and stirred, and the resulting precipitate is filtered and dried (120 ° C. × 2 hours) ) To produce an amorphous precursor (TiO 2 —ZrO 2 hydroxide) of an oxide carrier.

続いて、担体の重量に対して、Irが1wt%、Ptが0.5wt%となる割合でH2IrCl6とH2PtCl6とを混合溶解した水溶液を上記前駆体に含浸させて乾燥(100℃×24時間)させることにより、上記前駆体にIr及びPtをそれぞれ保持させる。 Subsequently, the precursor is impregnated with an aqueous solution in which H 2 IrCl 6 and H 2 PtCl 6 are mixed and dissolved at a ratio of 1 wt% Ir and 0.5 wt% Pt with respect to the weight of the support and dried ( 100 ° C. × 24 hours), Ir and Pt are held in the precursor.

次に、上記前駆体を空気雰囲気中で予熱処理(500℃×5時間)することにより、残存する各種原料中の塩素分等の腐食性成分を先に除去した後、当該前駆体を非酸化雰囲気(10%H2O含有窒素ガス)中で加熱処理(750℃×6時間)することにより、当該前駆体を構造変化させて結晶化させて、排ガス浄化用触媒の試験体1(粒径0.5〜1mm)を得た。 Next, the precursor is pre-heated in an air atmosphere (500 ° C. × 5 hours) to first remove corrosive components such as chlorine in various remaining raw materials, and then the precursor is non-oxidized. By performing heat treatment (750 ° C. × 6 hours) in an atmosphere (nitrogen gas containing 10% H 2 O), the precursor is structurally changed to be crystallized, and an exhaust gas purifying catalyst specimen 1 (particle size) 0.5-1 mm).

〈試験体2〉
上記試験体1の製造方法において、加熱処理の非酸化雰囲気を変更(10%H2O+1%H2含有窒素ガス)する以外は上記試験体1の製造方法と同一の条件に基づいて試験体2を作製した。
<Specimen 2>
In the manufacturing method of the test body 1, the test body 2 is based on the same conditions as the manufacturing method of the test body 1 except that the non-oxidizing atmosphere of the heat treatment is changed (nitrogen gas containing 10% H 2 O + 1% H 2 ). Was made.

〈試験体3〉
上記試験体1の製造方法において、加熱処理の時間を変更(18時間)する以外は上記試験体1の製造方法と同一の条件に基づいて試験体3を作製した。
<Test body 3>
In the manufacturing method of the test body 1, the test body 3 was produced based on the same conditions as the manufacturing method of the test body 1 except that the heat treatment time was changed (18 hours).

〈試験体4〉
上記試験体1の製造方法において、加熱処理の非酸化雰囲気を変更(窒素ガスのみ)すると共に、加熱処理の温度及び時間を変更(800℃×5時間)する以外は上記試験体1の製造方法と同一の条件に基づいて試験体4を作製した。
<Test body 4>
In the manufacturing method of the test body 1, the non-oxidizing atmosphere of the heat treatment is changed (only nitrogen gas) and the temperature and time of the heat treatment are changed (800 ° C. × 5 hours). The test body 4 was produced based on the same conditions.

〈試験体5〉
上記試験体1の製造方法において、加熱処理の非酸化雰囲気を変更(窒素ガスのみ)すると共に、加熱処理の温度及び時間を変更(900℃×5時間)する以外は上記試験体1の製造方法と同一の条件に基づいて試験体5を作製した。
<Test body 5>
In the manufacturing method of the said test body 1, while changing the non-oxidizing atmosphere of heat processing (only nitrogen gas) and changing the temperature and time of heat processing (900 degreeC x 5 hours), the manufacturing method of the said test body 1 The test body 5 was produced based on the same conditions.

〈比較体1:Irのみ〉
上記試験体1の製造方法と同様にして、酸化物からなる担体のアモルファス状態の前駆体(TiO2−ZrO2の水酸化物)を作製した後、担体の重量に対して、Irが1wt%となる割合でH2IrCl6を溶解した水溶液を上記前駆体に含浸させて乾燥(100℃×24時間)させることにより、上記前駆体にIrを保持させる。以下、上記試験体1の製造方法と同様に操作することにより、排ガス浄化用触媒の比較体1を得た。
<Comparator 1: Ir only>
In the same manner as in the manufacturing method of the test body 1, an amorphous precursor of a support composed of an oxide (a hydroxide of TiO 2 —ZrO 2 ) was prepared, and then Ir was 1 wt% with respect to the weight of the support. The precursor is impregnated with an aqueous solution in which H 2 IrCl 6 is dissolved at a ratio to be dried and dried (100 ° C. × 24 hours), thereby holding Ir in the precursor. Hereinafter, the exhaust gas-purifying catalyst comparative body 1 was obtained by operating in the same manner as in the manufacturing method of the test body 1 described above.

〈比較体2:Ptのみ〉
上記試験体1の製造方法と同様にして、酸化物からなる担体のアモルファス状態の前駆体(TiO2−ZrO2の水酸化物)を作製した後、担体の重量に対して、Ptが2wt%となる割合でH2PtCl4を溶解した水溶液を上記前駆体に含浸させて乾燥(100℃×24時間)させることにより、上記前駆体にPtを保持させる。以下、上記試験体1の製造方法と同様に操作することにより、排ガス浄化用触媒の比較体2を得た。
<Comparator 2: Pt only>
In the same manner as in the manufacturing method of the test body 1, an amorphous precursor of a support made of an oxide (a hydroxide of TiO 2 —ZrO 2 ) was prepared, and then Pt was 2 wt% with respect to the weight of the support. The precursor is impregnated with an aqueous solution in which H 2 PtCl 4 is dissolved at a ratio to be dried and dried (100 ° C. × 24 hours), thereby holding Pt on the precursor. Thereafter, a comparative body 2 of an exhaust gas purifying catalyst was obtained by operating in the same manner as the manufacturing method of the test body 1 described above.

〈比較体3:酸化雰囲気下での加熱処理〉
上記試験体1の製造方法において、加熱処理を酸化雰囲気(大気)とする以外は上記試験体1の製造方法と同一の条件に基づいて比較体3を作製した。
<Comparator 3: Heat treatment under oxidizing atmosphere>
In the manufacturing method of the test body 1, a comparative body 3 was manufactured based on the same conditions as the manufacturing method of the test body 1 except that the heat treatment was performed in an oxidizing atmosphere (atmosphere).

〈比較体4:担体への金属成分直接保持〉
担体の重量に対して、Irが1wt%、Ptが0.5wt%となる割合でH2IrCl6とH2PtCl6とを混合溶解した水溶液をSiO2からなる担体(粒径0.5〜1mm)に含浸させて乾燥(100℃×24時間)させることにより、当該担体にIr及びPtをそれぞれ直接保持させる。以下、上記試験体1の製造方法と同様に操作することにより、排ガス浄化用触媒の比較体4を得た。
<Comparative body 4: Direct retention of metal components on the carrier>
An aqueous solution in which H 2 IrCl 6 and H 2 PtCl 6 are mixed and dissolved at a ratio of 1 wt% Ir and 0.5 wt% Pt with respect to the weight of the carrier is a carrier comprising SiO 2 (particle size 0.5 to 1 mm) and dried (100 ° C. × 24 hours) to directly hold Ir and Pt on the carrier. Thereafter, the exhaust gas purifying catalyst comparison body 4 was obtained by operating in the same manner as in the manufacturing method of the test body 1 described above.

〈比較体5:担体への合金粒子直接保持〉
担体の重量に対して、Irが1wt%、Ptが0.5wt%となる割合で金属Ir片と金属Pt片とを混合してアーク溶解して粉砕微粒化し、得られた合金粒子を水に分散させて、SiO2からなる担体(粒径0.5〜1mm)に含浸させて乾燥(100℃×24時間)させた後、大気中で加熱処理(500℃×2時間)することにより、当該担体にIr−Pt系の合金粒子を直接保持させた排ガス浄化用触媒の比較体5を得た。
<Comparator 5: Direct retention of alloy particles on carrier>
Metal Ir pieces and metal Pt pieces are mixed at a ratio of 1 wt% Ir and 0.5 wt% Pt with respect to the weight of the carrier, and arc-melted to pulverize and atomize the resulting alloy particles in water. After being dispersed, impregnated with a carrier made of SiO 2 (particle size 0.5 to 1 mm) and dried (100 ° C. × 24 hours), heat treatment in the atmosphere (500 ° C. × 2 hours) An exhaust gas purifying catalyst comparative body 5 in which Ir—Pt alloy particles were directly held on the carrier was obtained.

〈比較体6:特許文献1,2の記載に基づく触媒〉
担体の重量に対して、Irが1wt%となる割合でH2IrCl6を溶解した水溶液にTiO2からなる担体(粒径0.5〜1mm)を含浸させて乾燥(120℃×24時間)させた後、大気中で加熱処理(300℃×2時間)ことにより、当該担体にIrを担持させる。
<Comparator 6: Catalyst based on the description of Patent Documents 1 and 2>
An aqueous solution in which H 2 IrCl 6 is dissolved at a rate of 1 wt% of Ir with respect to the weight of the carrier is impregnated with a carrier made of TiO 2 (particle size 0.5 to 1 mm) and dried (120 ° C. × 24 hours) Then, Ir is supported on the carrier by heat treatment in the atmosphere (300 ° C. × 2 hours).

次に、上記担体をイオン交換水中に分散させ、当該担体の重量に対して、0.5wt%となる割合のPt(NO22(NH32を添加すると共に、Na2SO3・5H2O,Na2SO3,C67NaO6・H2Oを添加してpH調整して(pH=6.21)、撹拌(24時間)した後、濾過、水洗、乾燥(120℃×2時間)することにより、Ptを還元析出させ、続いて、大気中で加熱処理(500℃×2時間)することにより、Irの表面の一部にPtを積層した排ガス浄化用触媒の比較体6を得た。 Next, the carrier is dispersed in ion-exchanged water, Pt (NO 2 ) 2 (NH 3 ) 2 is added at a ratio of 0.5 wt% with respect to the weight of the carrier, and Na 2 SO 3. 5H 2 O, Na 2 SO 3 , C 6 H 7 NaO 6 .H 2 O was added to adjust the pH (pH = 6.21), the mixture was stirred (24 hours), filtered, washed with water, and dried (120 Of the exhaust gas purification catalyst in which Pt is laminated on part of the surface of Ir by heat-reducing in the atmosphere (500 ° C. × 2 hours). Comparative body 6 was obtained.

[B.実験方法]
〈a.活性成分の固溶合金化の有無及び平均粒径値〉
前記試験体1〜5及び比較体1〜6の活性成分の固溶合金化の有無及び平均粒径値をXRDでの測定結果に基づいて求めた。すなわち、XRDにより測定されたピーク位置に基づいて、面間隔(d(111))を求め、Ir及びPtの面間隔(文献値)とを比較して、その大きさや位置等から活性成分の固溶合金化の有無を求め、XRDにより測定されたピークの半値幅解析(Scherrerの式)によって活性成分の平均粒径値を求めた。なお、比較体5においては、作製した合金粒子を担体に担持させる前にXRDで測定して求めた。
[B. experimental method]
<A. Presence / absence of solid solution alloying of active ingredients and average particle size>
The presence / absence of solid solution alloying of the active components of the test bodies 1 to 5 and the comparative bodies 1 to 6 and the average particle size were determined based on the measurement results by XRD. That is, based on the peak position measured by XRD, the face spacing (d (111)) is obtained, and the face spacing (reference value) of Ir and Pt is compared, and the active ingredient is determined based on its size and position. The presence or absence of alloying was determined, and the average particle size value of the active component was determined by half-width analysis (Scherrer's formula) of the peak measured by XRD. In addition, in the comparative body 5, it measured and calculated | required by XRD before making the produced alloy particle carry | supported to a support | carrier.

〈b.脱硝率〉
上述したようにして製造した試験体1〜5及び比較体1〜6の各試料(2cm3)に対して、下記の組成の試験ガスを下記の条件で流通させながら所定の温度に加熱し、当該試料を流通した試験ガス中の窒素酸化物濃度を計測して、当該試料を流通させる前の試験ガス中の窒素酸化物濃度に基づいて、そのときの温度における脱硝率を求めた。
<B. Denitration rate>
For each sample (2 cm 3 ) of the test bodies 1 to 5 and the comparative bodies 1 to 6 manufactured as described above, a test gas having the following composition is heated to a predetermined temperature while circulating under the following conditions: The nitrogen oxide concentration in the test gas flowing through the sample was measured, and the denitration rate at the temperature at that time was determined based on the nitrogen oxide concentration in the test gas before flowing the sample.

《試験ガス組成》
・NO:900ppm
・SO2:900ppm
・C36:900ppm
・O2:15%
・H2O:5%
・N2:残
《Test gas composition》
・ NO: 900ppm
・ SO 2 : 900 ppm
・ C 3 H 6 : 900 ppm
・ O 2 : 15%
・ H 2 O: 5%
・ N 2 : Remaining

《試験ガス送給条件》
・GHSV:6500h-1
・AV:5.5Nm3/m2
《Test gas supply conditions》
・ GHSV: 6500h -1
・ AV: 5.5Nm 3 / m 2 h

[C.実験結果]
〈a.活性成分の固溶合金化の有無及び平均粒径値〉
上述したようにして求めた活性成分の固溶合金化の有無及び平均粒径値を下記の表1に示す
[C. Experimental result]
<A. Presence / absence of solid solution alloying of active ingredients and average particle size value>
Table 1 below shows the presence / absence of solid-solution alloying of the active ingredient and the average particle size determined as described above.

Figure 2006198490
Figure 2006198490

上記表1からわかるように、試験体1〜5においては、XRDの測定結果から求められた面間隔(d(111))がIr及びPtの面間隔(文献値)と明らかに異なることから、活性成分が固溶合金化していることが確認されると共に、平均粒径が10〜50nmの範囲内であることが確認された。   As can be seen from Table 1 above, in the test bodies 1 to 5, the interplanar spacing (d (111)) determined from the XRD measurement results is clearly different from the interplanar spacing of Ir and Pt (document values). It was confirmed that the active component was formed into a solid solution alloy and that the average particle size was in the range of 10 to 50 nm.

これに対し、比較体5においては、活性成分が固溶化した合金粒子ではあるものの、平均粒径をμmレベルにしかできず、比較体1〜4,6においては、活性成分の平均粒径が10〜50nmの範囲内であるものの、XRDの測定結果から求められた面間隔(d(111))がIr又はPtの面間隔(文献値)と略同じであることから、活性成分が固溶化した合金粒子とならずに存在していることが確認された。なお、比較体3,4,6において、Ptは、Irよりもピーク強度が非常に小さかったため計測することができなかった。   On the other hand, in the comparative body 5, although the active component is an alloy particle in which the active component is dissolved, the average particle diameter can only be at the μm level. In the comparative bodies 1 to 4, 6, the average particle diameter of the active ingredient is Although it is within the range of 10 to 50 nm, the surface distance (d (111)) determined from the XRD measurement results is substantially the same as the surface distance (document value) of Ir or Pt, so that the active ingredient is in solution. It was confirmed that they existed without becoming alloy particles. In Comparative Examples 3, 4, and 6, Pt could not be measured because the peak intensity was much smaller than Ir.

〈b.脱硝率〉
次に、脱硝率の測定実験結果を図3〜13に示す。
<B. Denitration rate>
Next, the measurement experiment results of the denitration rate are shown in FIGS.

これら図3〜13から明らかなように、試験体1〜5においては、250〜450℃の温度領域全体にわたって10%以上の脱硝率で窒素酸化物を分解処理できることが確認された。他方、比較体1〜6においては、250〜450℃の温度領域全体にわたって10%以上の脱硝率で窒素酸化物を分解処理できないことが確認された。   As is apparent from FIGS. 3 to 13, in the test bodies 1 to 5, it was confirmed that nitrogen oxides can be decomposed at a denitration rate of 10% or more over the entire temperature range of 250 to 450 ° C. On the other hand, in Comparative bodies 1 to 6, it was confirmed that nitrogen oxides could not be decomposed at a denitration rate of 10% or more over the entire temperature range of 250 to 450 ° C.

本発明に係る排ガス浄化用触媒は、250〜450℃の広い温度領域全体にわたって窒素酸化物の分解処理を効率よく行うことができ、本発明に係る排ガス浄化用触媒の製造方法は、本発明に係る排ガス浄化用触媒を容易に製造することができ、本発明に係る排ガス浄化方法は、負荷具合により温度が幅広く変動するディーゼルエンジン等からの排ガスであっても、当該排ガスの温度領域全体にわたって窒素酸化物を効率よく分解処理することができるので、本発明は、産業上、極めて有益に利用することができる。   The exhaust gas purifying catalyst according to the present invention can efficiently decompose nitrogen oxides over a wide temperature range of 250 to 450 ° C. The method for producing an exhaust gas purifying catalyst according to the present invention includes the present invention. Such an exhaust gas purifying catalyst can be easily manufactured, and the exhaust gas purifying method according to the present invention is capable of producing nitrogen over the entire temperature range of the exhaust gas, even if it is exhaust gas from a diesel engine whose temperature varies widely depending on the load condition. Since the oxide can be decomposed efficiently, the present invention can be used extremely beneficially industrially.

本発明に係る排ガス浄化用触媒の製造方法の実施形態の手順を表わすフロー図である。It is a flowchart showing the procedure of embodiment of the manufacturing method of the exhaust gas purification catalyst which concerns on this invention. 本発明に係る排ガス浄化用触媒の製造方法の実施形態の説明図である。It is explanatory drawing of embodiment of the manufacturing method of the catalyst for exhaust gas purification which concerns on this invention. 試験体1における温度と脱硝率との関係を表わすグラフである。3 is a graph showing the relationship between the temperature and the denitration rate in the test body 1. 試験体2における温度と脱硝率との関係を表わすグラフである。4 is a graph showing the relationship between the temperature and the denitration rate in the test body 2. 試験体3における温度と脱硝率との関係を表わすグラフである。3 is a graph showing the relationship between the temperature and the denitration rate in the test body 3. 試験体4における温度と脱硝率との関係を表わすグラフである。3 is a graph showing the relationship between the temperature and the denitration rate in the test body 4. 試験体5における温度と脱硝率との関係を表わすグラフである。4 is a graph showing the relationship between the temperature and the denitration rate in the test body 5. 比較体1における温度と脱硝率との関係を表わすグラフである。3 is a graph showing the relationship between the temperature and the denitration rate in the comparative body 1. 比較体2における温度と脱硝率との関係を表わすグラフである。4 is a graph showing the relationship between the temperature and the denitration rate in comparative body 2. 比較体3における温度と脱硝率との関係を表わすグラフである。5 is a graph showing the relationship between the temperature and the denitration rate in the comparative body 3. 比較体4における温度と脱硝率との関係を表わすグラフである。4 is a graph showing the relationship between the temperature and the denitration rate in the comparative body 4. 比較体5における温度と脱硝率との関係を表わすグラフである。5 is a graph showing the relationship between the temperature and the denitration rate in the comparative body 5. 比較体6における温度と脱硝率との関係を表わすグラフである。7 is a graph showing the relationship between the temperature and the denitration rate in the comparative body 6.

符号の説明Explanation of symbols

110 排ガス浄化用触媒
111 担体
111a 前駆体
112 合金粒子
112a,112b 金属成分
110 exhaust gas purifying catalyst 111 support 111a precursor 112 alloy particles 112a and 112b metal components

Claims (10)

酸化物からなる担体と、
前記担体に担持され、複数の金属成分を固溶させた合金粒子と
を備え、
前記合金粒子の粒径が100nm以下である
ことを特徴とする排ガス浄化用触媒。
A support made of an oxide;
An alloy particle supported on the carrier and having a plurality of metal components dissolved therein,
A catalyst for exhaust gas purification, wherein the alloy particles have a particle size of 100 nm or less.
請求項1において、
前記担体が、TiO2,SiO2,Al23,ZrO2,CaO,MgO,SnO2,ZnOのうちの少なくとも二種以上の複合酸化物からなる
ことを特徴とする排ガス浄化用触媒。
In claim 1,
Wherein said carrier, TiO 2, SiO 2, Al 2 O 3, ZrO 2, CaO, MgO, exhaust gas-purifying catalyst characterized by comprising a SnO 2, at least two or more composite oxides of ZnO.
請求項1において、
前記合金粒子が、Pt,Ir,Pd,Rh,Ru,Au,Agのうちの少なくとも二種以上の固溶体である
ことを特徴とする排ガス浄化用触媒。
In claim 1,
The catalyst for exhaust gas purification, wherein the alloy particles are at least two kinds of solid solutions of Pt, Ir, Pd, Rh, Ru, Au, and Ag.
請求項3において、
前記合金粒子が、少なくともIrを含む二種の金属成分の固溶体であると共に、10nm以上の粒径を有している
ことを特徴とする排ガス浄化用触媒。
In claim 3,
The exhaust gas purifying catalyst, wherein the alloy particles are a solid solution of two kinds of metal components containing at least Ir and have a particle size of 10 nm or more.
請求項1において、
前記合金粒子が、前記担体に対して0.1〜5wt%の割合で担持されている
ことを特徴とする排ガス浄化用触媒。
In claim 1,
The exhaust gas purifying catalyst, wherein the alloy particles are supported at a ratio of 0.1 to 5 wt% with respect to the carrier.
請求項1から請求項5のいずれかの排ガス浄化用触媒の製造方法であって、
酸化物からなる前記担体のアモルファス状態の前駆体に、金属成分の溶解した溶液を含有させて当該前駆体に複数の金属成分を保持させた後、当該前駆体を非酸化雰囲気中で加熱処理して構造変化させることにより、酸化物からなる前記担体に、複数の前記金属成分を固溶させた前記合金粒子を担持させる
ことを特徴とする排ガス浄化用触媒の製造方法。
A method for producing an exhaust gas purifying catalyst according to any one of claims 1 to 5,
The amorphous precursor of the carrier made of an oxide contains a solution in which a metal component is dissolved, and the precursor is held with a plurality of metal components, and then the precursor is heat-treated in a non-oxidizing atmosphere. The method for producing an exhaust gas purifying catalyst is characterized in that the alloy particles in which a plurality of the metal components are dissolved are supported on the support made of oxide by changing the structure.
請求項6において、
前記非酸化雰囲気が、還元性ガス及び不活性ガスの少なくとも一方からなる
ことを特徴とする排ガス浄化用触媒の製造方法。
In claim 6,
The method for producing an exhaust gas purifying catalyst, wherein the non-oxidizing atmosphere comprises at least one of a reducing gas and an inert gas.
請求項6において、
前記非酸化雰囲気が、水蒸気を含有している
ことを特徴とする排ガス浄化用触媒の製造方法。
In claim 6,
The method for producing an exhaust gas purifying catalyst, wherein the non-oxidizing atmosphere contains water vapor.
請求項1から請求項5のいずれかの排ガス浄化用触媒と排ガスとを接触させて当該排ガス中の窒素酸化物を分解処理する
ことを特徴とする排ガス浄化方法。
An exhaust gas purification method comprising decomposing a nitrogen oxide in the exhaust gas by bringing the exhaust gas purification catalyst according to any one of claims 1 to 5 into contact with the exhaust gas.
請求項9において、
前記排ガスが、ディーゼルエンジンから排出された250〜450℃の温度のガスである
ことを特徴とする排ガス浄化方法。
In claim 9,
The exhaust gas is a gas having a temperature of 250 to 450 ° C discharged from a diesel engine.
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WO2012120711A1 (en) 2011-03-04 2012-09-13 トヨタ自動車株式会社 Metal particles, catalyst for exhaust gas purification containing same, and production method therefor
US9115621B2 (en) 2011-03-04 2015-08-25 Toyota Jidosha Kabushiki Kaisha Metal particles, exhaust gas purifying catalyst comprising metal particles, and methods for producing them
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