JP3473245B2 - Exhaust gas purification catalyst - Google Patents

Exhaust gas purification catalyst

Info

Publication number
JP3473245B2
JP3473245B2 JP02777096A JP2777096A JP3473245B2 JP 3473245 B2 JP3473245 B2 JP 3473245B2 JP 02777096 A JP02777096 A JP 02777096A JP 2777096 A JP2777096 A JP 2777096A JP 3473245 B2 JP3473245 B2 JP 3473245B2
Authority
JP
Japan
Prior art keywords
catalyst
exhaust gas
zeolite
pores
total volume
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.)
Expired - Fee Related
Application number
JP02777096A
Other languages
Japanese (ja)
Other versions
JPH09220475A (en
Inventor
弘 赤間
浩行 金坂
真紀 上久保
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.)
Nissan Motor Co Ltd
Original Assignee
Nissan Motor Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Nissan Motor Co Ltd filed Critical Nissan Motor Co Ltd
Priority to JP02777096A priority Critical patent/JP3473245B2/en
Publication of JPH09220475A publication Critical patent/JPH09220475A/en
Application granted granted Critical
Publication of JP3473245B2 publication Critical patent/JP3473245B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A50/00TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/20Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters

Landscapes

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

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、排気ガス浄化用触
媒に関し、特に自動車エンジン等の内燃機関や各種燃焼
器等からの排気ガスの浄化効率に優れた排気ガス浄化用
触媒に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an exhaust gas purifying catalyst, and more particularly to an exhaust gas purifying catalyst having excellent purification efficiency of exhaust gas from an internal combustion engine such as an automobile engine and various combustors.

【0002】[0002]

【従来の技術】従来、自動車のエンジン等の排気ガスを
浄化するための触媒としては、三元触媒が幅広く用いら
れている。従来の三元触媒は、白金、パラジウム、ロジ
ウム等の貴金属成分およびセリウム成分等の各種成分を
含有したアルミナを主成分とする触媒が主流であり、エ
ンジンが理論空燃比の近傍で運転された場合の排気ガス
に対して高い浄化効率を示すものである。
2. Description of the Related Art Conventionally, three-way catalysts have been widely used as catalysts for purifying exhaust gas from automobile engines and the like. Conventional three-way catalysts mainly consist of catalysts containing alumina, which contains various components such as platinum, palladium, rhodium and other noble metals and cerium, and when the engine is operated near the stoichiometric air-fuel ratio. It shows a high purification efficiency for the exhaust gas.

【0003】一方、近年、燃費向上、二酸化炭素の排出
量削減の観点から、理論空燃比より高い空燃比において
も運転されるリーン・バーン・エンジンが注目されてい
る。かかるリーン・バーン・エンジンの排気ガス(リー
ン排気ガス)は、理論空燃比近傍でのみ運転する従来エ
ンジンの排気ガス(ストイキ排気ガス)に比較して、酸
素の含有率が高く、従来の三元触媒では窒素酸化物(N
Ox)の浄化が不十分となる。そこで、幅広い空燃比で
運転されるリーン・バーン・エンジンに適用可能な新触
媒が望まれていた。
On the other hand, in recent years, from the viewpoint of improving fuel efficiency and reducing carbon dioxide emissions, lean burn engines that are operated even at an air-fuel ratio higher than the stoichiometric air-fuel ratio have been receiving attention. The exhaust gas (lean exhaust gas) of such a lean burn engine has a higher oxygen content than the exhaust gas (stoichiometric exhaust gas) of a conventional engine that operates only in the vicinity of the stoichiometric air-fuel ratio. Nitrogen oxide (N
Ox) is insufficiently purified. Therefore, a new catalyst applicable to a lean burn engine that operates at a wide range of air-fuel ratios has been desired.

【0004】各種の金属成分を結晶性アルミノケイ酸塩
(以下、「ゼオライト」と称す)に担持して得られる金
属担持ゼオライト触媒(以下、「ゼオライト系触媒」と
称す)は、酸素含有率が高い排気ガス中(リーン排気ガ
ス)においても、炭化水素類(HC)が存在していれ
ば、NOxを比較的効率良く浄化できる能力があること
で注目されている。
A metal-supported zeolite catalyst (hereinafter referred to as "zeolite-based catalyst") obtained by supporting various metal components on crystalline aluminosilicate (hereinafter referred to as "zeolite") has a high oxygen content. Even in the exhaust gas (lean exhaust gas), if hydrocarbons (HC) are present, it is noted that NOx can be purified relatively efficiently.

【0005】この金属成分として銅(Cu)、コバルト
(Co)、銀(Ag)、ニッケル(Ni)、鉄(Fe)
等の遷移金属成分に加え、貴金属成分である白金(P
t)もその有効性が認められているが、特に銅(Cu)
を担持したCu−ゼオライト触媒は、NOx活性が高
く、高流速排気ガス条件下でも比較的優れたNOx浄化
性能を有しており、このため、自動車のような移動発生
源や定置型の自家発電用エンジン等からの排気ガス浄化
への適用が期待されている。
As the metal component, copper (Cu), cobalt (Co), silver (Ag), nickel (Ni), iron (Fe)
In addition to transition metal components such as platinum, platinum (P
t) is also known to be effective, but especially copper (Cu)
The Cu-zeolite catalyst supporting NO has a high NOx activity and has a relatively excellent NOx purification performance even under high-velocity exhaust gas conditions. Therefore, a mobile generation source such as an automobile or stationary private power generation is used. It is expected to be applied to the purification of exhaust gas from industrial engines.

【0006】しかし、ゼオライト系触媒のみでは、理論
空燃(ストイキ)から酸素過剰(リーン)の幅広い空燃
比で運転されるエンジンの排気ガスを十分に浄化するこ
とはできず、三元触媒との組合せが不可欠であった。こ
れは、ゼオライト系触媒は、ストイキ排気ガス中におけ
る炭化水素類(HC)、一酸化炭素(CO)、窒素酸化
物(NOx)の浄化性能が悪く、一方、酸素含有率の高
いリーン排気ガス中でもNOx浄化性能は優れているも
のの、HC,COを浄化する能力に劣るからである。
However, the zeolite catalyst alone cannot sufficiently purify the exhaust gas of an engine operated in a wide air-fuel ratio from stoichiometric air-fuel to stoichiometric oxygen excess (lean). The combination was essential. This is because the zeolite-based catalyst has a poor purification performance for hydrocarbons (HC), carbon monoxide (CO), and nitrogen oxides (NOx) in the stoichiometric exhaust gas, while in the lean exhaust gas with a high oxygen content. This is because the NOx purification performance is excellent, but the ability to purify HC and CO is inferior.

【0007】このため、ゼオライト系触媒と三元触媒と
を排気ガス流れ方向に対し直列に組み合わせる触媒シス
テムが考えられ、例えば、特開平1−139145号公
報には、排気ガス上流側に遷移金属を担持したゼオライ
ト触媒を、下流側に酸化触媒または三元触媒を配置する
ことが提案されている。
Therefore, a catalyst system in which a zeolite-based catalyst and a three-way catalyst are combined in series in the exhaust gas flow direction is conceivable. For example, in JP-A-1-139145, a transition metal is provided upstream of the exhaust gas. It has been proposed to arrange a supported zeolite catalyst on the downstream side of an oxidation catalyst or a three-way catalyst.

【0008】このような、排気ガスの上流側にゼオライ
ト系触媒を、下流側に三元触媒を配置する組み合わせ
は、ストイキからリーンに至る幅広い空燃比で運転する
リーン・バーン・エンジンの排気ガス浄化のためには有
効な触媒システムと考えられる。
Such a combination in which the zeolite-based catalyst is arranged on the upstream side of the exhaust gas and the three-way catalyst is arranged on the downstream side is exhaust gas purification of a lean burn engine operating at a wide air-fuel ratio from stoichiometric to lean. It is considered to be an effective catalyst system for.

【0009】[0009]

【発明が解決しようとする課題】しかしながら、上記従
来の排気ガス浄化触媒システムは、実際には排気ガス下
流側に設置した三元触媒の機能を十分に発揮させること
ができないという問題があった。その原因は明確ではな
いが、ゼオライト系触媒は、リーンからストイキ、スト
イキからリーンへと排気ガスの状態が切り換わる際に、
排気ガス中の一部のガス成分を一時的かつ選択的に捕捉
し、これが三元触媒入り口における排気ガス中の酸化性
ガス成分(NOx)と還元性ガス成分のバランスを崩
し、三元触媒の機能を低下させると概略的に考えられ
る。
However, the conventional exhaust gas purifying catalyst system described above has a problem that the function of the three-way catalyst installed on the downstream side of the exhaust gas cannot be fully exerted in practice. Although the cause is not clear, the zeolite-based catalyst, when the state of the exhaust gas switches from lean to stoichi, stoichi to lean,
Temporarily and selectively captures a part of the gas component in the exhaust gas, which disturbs the balance between the oxidizing gas component (NOx) and the reducing gas component in the exhaust gas at the inlet of the three-way catalyst, It is generally thought to reduce function.

【0010】従って、三元触媒の機能を低下させないた
めには、ゼオライト系触媒によるガス成分の捕捉力を弱
めることが必要である。そこで、本発明の目的は、三元
触媒の機能を低下させずに、ストイキからリーンに至る
幅広い空燃比で運転する自動車エンジンからの排気ガス
を効率良く浄化することができる排気ガス浄化用触媒を
提供するにある。
Therefore, in order not to deteriorate the function of the three-way catalyst, it is necessary to weaken the gas component capturing power of the zeolite-based catalyst. Therefore, an object of the present invention is to provide an exhaust gas purifying catalyst capable of efficiently purifying exhaust gas from an automobile engine operating at a wide air-fuel ratio from stoichiometric to lean without deteriorating the function of the three-way catalyst. To provide.

【0011】[0011]

【課題を解決するための手段】本発明者らは、上記課題
を解決するために研究した結果、ゼオライト系触媒の細
孔分布を特定することにより、ゼオライト系触媒による
特定のガス成分の捕捉力が変化することを見い出し、本
発明に到達した。
Means for Solving the Problems As a result of research to solve the above problems, the inventors of the present invention identified the pore distribution of a zeolite-based catalyst to determine the ability of the zeolite-based catalyst to capture a specific gas component. The present invention has been achieved by finding that

【0012】 本発明の排気ガス浄化用触媒は、4nm
以下の細孔直径を有する多孔質結晶性アルミノケイ酸塩
粒子間の細孔の全容積和が1〜100nmの細孔直径を
有する多孔質結晶性アルミノケイ酸塩粒子間の細孔の全
容積和の40%以上である多孔質結晶性アルミノケイ酸
塩を含むことを特徴とする。
The exhaust gas purifying catalyst of the present invention has a thickness of 4 nm.
Porous crystalline aluminosilicate having the following pore diameter
Comprising a porous than 40% is porous crystalline aluminosilicate of the total volume sum of the pores between the crystalline aluminosilicate particles total volume sum of the pores having a pore diameter of 1~100nm between particles It is characterized by

【0013】即ち、直径4〜100nmの細孔が特定ガ
ス成分の一時的かつ選択的な捕捉力を担っていると考え
られ、この細孔の割合を制御することにより、三元触媒
の機能低下を抑制することができるのである。特に好ま
しくは、直径4nm以下の径を有する細孔の容積和を、
直径1nm以上100nm以下の多孔質結晶性アルミノ
ケイ酸塩粒子間の細孔の容積総和の50%以上とする。
これにより効果的に三元触媒の機能低下を防止すること
ができるので好ましい。しかし、該細孔容積和の割合を
むやみに高めてもそれ以上に性能が向上しないことか
ら、該細孔容積和の割合のより好適な範囲は50〜85
%である。
That is, it is considered that the pores having a diameter of 4 to 100 nm play a temporary and selective trapping force for the specific gas component, and the function of the three-way catalyst is lowered by controlling the proportion of the pores. Can be suppressed. Particularly preferably, the volume sum of pores having a diameter of 4 nm or less is
Porous crystalline alumino with a diameter of 1 nm or more and 100 nm or less
It is 50% or more of the total volume of pores between silicate particles .
This is preferable because it can effectively prevent the functional deterioration of the three-way catalyst. However, even if the ratio of the pore volume sum is increased unnecessarily, the performance is not further improved. Therefore, the more preferable range of the pore volume sum ratio is 50 to 85.
%.

【0014】本発明のゼオライト系触媒と三元触媒の組
合せは、排気ガス上流側にゼオライト系触媒、下流側に
三元触媒という配置である。この配置を逆にするとリー
ン排気ガスのNOx浄化反応に必要な還元ガス成分がゼ
オライト系触媒に至る前に消費され、NOx浄化作用が
阻害される。
The combination of the zeolite-based catalyst and the three-way catalyst of the present invention is such that the zeolite-based catalyst is on the exhaust gas upstream side and the three-way catalyst is on the downstream side. If this arrangement is reversed, the reducing gas component necessary for the NOx purification reaction of the lean exhaust gas is consumed before reaching the zeolite catalyst, and the NOx purification action is hindered.

【0015】ゼオライト系触媒におけるゼオライトのS
iO2 /Al2 3 のモル比は20〜60の範囲が好ま
しい。SiO2 /Al2 3 のモル比が20未満になる
と、ゼオライトの熱安定性が不十分となり、触媒の耐熱
性や耐久性が低下する。逆に、モル比が60を超えると
活性金属成分の担持量が少なくなり、触媒活性が低下す
る。
Zeolite S in zeolite-based catalysts
The molar ratio of iO 2 / Al 2 O 3 is preferably in the range of 20-60. If the molar ratio of SiO 2 / Al 2 O 3 is less than 20, the thermal stability of the zeolite will be insufficient and the heat resistance and durability of the catalyst will decrease. On the contrary, when the molar ratio exceeds 60, the amount of the active metal component carried becomes small and the catalytic activity decreases.

【0016】本発明において用いられるゼオライトとし
ては、公知のゼオライトの中から適宜選択して使用する
ことができるが、特にペンタシジ型ゼオライトと称され
る群のものが有効である。このようなゼオライトとして
は、例えば、モルデナイト、フェリェライト、ZSM
5、ZSM11等があげられるが、特にZSM5が耐熱
性や耐久性の面から好ましい。
The zeolite used in the present invention can be appropriately selected from known zeolites and used, and those of the group called pentasidi type zeolite are particularly effective. Examples of such zeolites include mordenite, ferrierite, ZSM.
5, ZSM11 and the like can be mentioned, and ZSM5 is particularly preferable in terms of heat resistance and durability.

【0017】また、ゼオライトは、水熱処理、再合成な
どによって、結晶性を高めることにより安定化し、耐熱
性、耐久性の高い触媒が得られるので好ましい。
Zeolite is preferable because it can be stabilized by increasing crystallinity by hydrothermal treatment, resynthesis, etc., and a catalyst having high heat resistance and durability can be obtained.

【0018】本発明に用いられるゼオライトに担持する
金属成分としては、種々の遷移金属種が有効であるが、
特に、Cu,Co,Ag,Ni,Ptが好ましい。この
金属成分の原料としては、無機酸塩、酸化物、有機酸
塩、塩化物、炭酸塩、ナトリウム塩、アンモニウム塩、
アンミン錯化合物等の各種化合物を使用することがで
き、イオン交換法、含浸法等の通常用いられる方法で該
金属成分をゼオライトに担持することができる。さらに
は、金属原料を高温で蒸発させて気相担持する方法や、
物理的混合法による担持も有効である。
Various transition metal species are effective as the metal component supported on the zeolite used in the present invention.
In particular, Cu, Co, Ag, Ni and Pt are preferable. As the raw material of this metal component, inorganic acid salts, oxides, organic acid salts, chlorides, carbonates, sodium salts, ammonium salts,
Various compounds such as an ammine complex compound can be used, and the metal component can be supported on zeolite by a commonly used method such as an ion exchange method and an impregnation method. Furthermore, a method of evaporating a metal raw material at a high temperature to carry it in a vapor phase,
Supporting by a physical mixing method is also effective.

【0019】通常のイオン交換法、含浸法による場合に
は、金属原料は溶液で用いられることが多く、その溶液
には、酸あるいは塩基を添加して適当にpHを調節する
ことにより好ましい結果を与える場合もあるが、本発明
は担持法によって制限されるものではない。
In the case of the usual ion exchange method or impregnation method, the metal raw material is often used in the form of a solution, and an acid or a base is added to the solution to adjust the pH appropriately to obtain desirable results. In some cases, the present invention is not limited by the loading method.

【0020】ゼオライト系触媒の細孔径分布を制御する
方法としては、(1)ゼオライト粒子を湿式あるいは乾
式条件で粉砕し粒径制御する方法、(2)少なくとも6
00℃以上の高温で焼成して粒子を焼結する方法、
(3)各種酸化物の微粉末を混合する方法、(4)触媒
表面を各種酸化物でコーティングし粒径制御する方法等
がある。前記(3)および(4)の方法における各種酸
化物としては、可能な限り不活性で触媒性能に悪影響を
与えないものが好ましく、アルミナ(Al2 3 )、シ
リカ(SiO2 )、チタニア(TiO2 )、炭化珪素
(SiC)、窒化珪素(Si3 4 )等の微粉末が好適
に用いられる。上記方法は単独でも有効だが、上記
(1)〜(4)の方法を適当に組み合わせると、より一
層大きな効果が得られる。
As a method for controlling the pore size distribution of the zeolite-based catalyst, (1) a method of pulverizing zeolite particles under wet or dry conditions to control the particle size, (2) at least 6
A method of sintering particles by firing at a high temperature of 00 ° C. or higher,
(3) A method of mixing fine powders of various oxides, and (4) a method of controlling the particle size by coating the surface of the catalyst with various oxides. The various oxides used in the above methods (3) and (4) are preferably those that are as inert as possible and do not adversely affect the catalyst performance, such as alumina (Al 2 O 3 ), silica (SiO 2 ), titania ( Fine powders of TiO 2 ), silicon carbide (SiC), silicon nitride (Si 3 N 4 ) and the like are preferably used. The above method is effective alone, but if the methods (1) to (4) are appropriately combined, a greater effect can be obtained.

【0021】排気ガス流の下流側に配する触媒は、いわ
ゆる三元触媒の機能を有しており、耐火性無機物に貴金
属成分を担持することによって得られる。かかる触媒中
に含有される貴金属には、Pt,Pd,Rhから成る群
より選ばれる1種以上の元素が含まれる。また耐火性無
機物としては、アルミナ、シリカ、シリカ−アルミナ、
マグネシア、ジルコニア、チタニア等の一般的な触媒担
体を用いることができるが、これによって制限されるも
のではない。また、アルミナは比表面積が大きく、かつ
耐熱性に優れているため貴金属を高分散担持でき、より
少ない貴金属を有効に活用できるため好ましい触媒担体
である。
The catalyst disposed on the downstream side of the exhaust gas flow has a so-called three-way catalyst function, and is obtained by supporting a noble metal component on a refractory inorganic material. The noble metal contained in the catalyst contains at least one element selected from the group consisting of Pt, Pd, and Rh. Further, as the refractory inorganic material, alumina, silica, silica-alumina,
A general catalyst carrier such as magnesia, zirconia or titania can be used, but is not limited thereto. Alumina is a preferred catalyst carrier because it has a large specific surface area and is excellent in heat resistance, so that it can support precious metals in a highly dispersed manner and can effectively utilize less precious metals.

【0022】本発明の触媒はハニカム形状で使用するの
が好ましい。この場合、通常、ハニカム状の担体に本発
明のゼオライト系触媒を塗布して用いる。このハニカム
材料としては、一般にコージェライト質のものが広く用
いられているが、これに限定されるものではなく、金属
材料からなるハニカム担体も有効であり、また触媒粉末
そのものをハニカム状に成形することもできる。更に
は、触媒の形状をハニカム状とすることにより、触媒と
排気ガスとの接触面積が大きくなり、圧力損失も抑えら
れるため、振動があり、かつ限られた空間内で多量の排
気ガスを処理することが要求される自動車用触媒として
用いる場合に極めて有利となる。
The catalyst of the present invention is preferably used in the form of a honeycomb. In this case, usually, the zeolite-based catalyst of the present invention is applied to a honeycomb-shaped carrier for use. Generally, a cordierite material is widely used as the honeycomb material, but the material is not limited to this, and a honeycomb carrier made of a metal material is also effective, and the catalyst powder itself is formed into a honeycomb shape. You can also Furthermore, by making the shape of the catalyst honeycomb, the contact area between the catalyst and the exhaust gas is increased and pressure loss is also suppressed, so there is vibration and a large amount of exhaust gas is processed in a limited space. This is extremely advantageous when used as an automobile catalyst that is required to

【0023】[0023]

【実施例】以下、本発明を次の実施例及び比較例によっ
て更に詳述するが、本発明はこれによって限定されるも
のではない。実施例1 (1)ゼオライト系触媒 濃度0.1モルの硝酸銅水溶液にアンモニア水を滴下
し、pHを8.2とした。この溶液中にSiO2 /Al
2 3 モル比が約37のNH4 型ZSM5の粉末を添加
して良く攪拌し、次いで濾過することにより固液を分離
した。前記攪拌・濾過操作を3回繰り返すことにより、
Cuをイオン交換担持したZSM5ゼオライト触媒ケー
キを得た。このケーキを、乾燥機を用いて120℃で2
4時間以上乾燥し、次いで電気炉を用いて大気雰囲気下
630℃で8時間焼成することにより、Cuが4.6重
量%担持されたCu−ZSM5触媒粉を得た。
The present invention will be described in more detail below with reference to the following examples and comparative examples, but the present invention is not limited thereto. Example 1 (1) Aqueous ammonia was added dropwise to a copper nitrate aqueous solution having a zeolite catalyst concentration of 0.1 mol to adjust the pH to 8.2. SiO 2 / Al in this solution
The solid-liquid was separated by adding NH 4 type ZSM5 powder having a molar ratio of 2 O 3 of about 37, stirring well, and then filtering. By repeating the stirring and filtering operation three times,
A ZSM5 zeolite catalyst cake carrying Cu ion exchange was obtained. This cake is dried at 120 ° C. for 2 hours using a dryer.
It was dried for 4 hours or more and then calcined in an air atmosphere at 630 ° C. for 8 hours to obtain Cu-ZSM5 catalyst powder carrying 4.6% by weight of Cu.

【0024】このようにして得られたCu−ZSM5触
媒粉末とアルミゾル、シリカゾルおよび水とを磁性ボー
ルミルポットに入れ、6時間混合・粉砕してスラリー化
した。アルミナゾルおよびシリカゾルの添加量は、それ
ぞれAl2 3 、SiO2 として、吸着水を除いたCu
−ZSM5触媒粉に対して、8重量%、4重量%であっ
た。
The Cu-ZSM5 catalyst powder thus obtained, aluminum sol, silica sol and water were placed in a magnetic ball mill pot and mixed and pulverized for 6 hours to form a slurry. The addition amounts of alumina sol and silica sol were Al 2 O 3 and SiO 2 , respectively, and Cu excluding adsorbed water was used.
8% by weight and 4% by weight with respect to the ZSM5 catalyst powder.

【0025】得られたスラリーを、1平方インチ断面当
たり、約400個の流路を持つコージェライト製ハニカ
ム担体0.8Lに塗布し、150℃で熱風乾燥した後、
450℃で1時間焼成した。ハニカム担体へのCu−Z
SM5触媒粉のコート量は約150g/Lであった。該
ハニカム状触媒をコロイダルシリカ溶液中に浸し、次い
で乾燥機を用いて100℃で乾燥後、電気炉中500℃
で30分焼成し、本発明のハニカム状のCu−ZSM5
触媒を得た。コロイダルシリカの含浸担持量は、SiO
2 として6g/Lであった。
The obtained slurry was applied to 0.8 L of a cordierite honeycomb carrier having about 400 flow paths per 1 square inch cross section and dried with hot air at 150 ° C.
It was baked at 450 ° C. for 1 hour. Cu-Z on honeycomb carrier
The coating amount of the SM5 catalyst powder was about 150 g / L. The honeycomb catalyst is dipped in a colloidal silica solution and then dried at 100 ° C. using a dryer, and then 500 ° C. in an electric furnace.
For 30 minutes, and the honeycomb-shaped Cu-ZSM5 of the present invention
A catalyst was obtained. The amount of impregnated and supported colloidal silica is SiO.
2 was 6 g / L.

【0026】(2)三元触媒 γ−アルミナを主成分とする活性アルミナにジニトロジ
アンミンパラジウム水溶液を加え、含浸法でPdを担持
した後、乾燥機を用いて120℃で8時間乾燥し、空気
気流中450℃で2時間焼成し、Pdが1.4重量%担
持されたPd−活性アルミナを得た。このPd−活性ア
ルミナに酸化セリウム(CeO2 )、活性アルミナおよ
び硝酸酸性ベーマイトゾルを添加混合し、磁性ボールミ
ルポットで8時間粉砕してスラリーを得た。このスラリ
ーを上記ゼオライト系触媒と同様にしてハニカム担体
0.9Lにコーティングし、120℃で乾燥、400℃
で焼成した。該触媒のコート量は約100g/Lであっ
た。
(2) Three-way catalyst Dinitrodiamminepalladium aqueous solution was added to activated alumina containing γ-alumina as a main component, Pd was supported by the impregnation method, and then dried at 120 ° C. for 8 hours using a dryer, and then air was used. It was calcined in an air stream at 450 ° C. for 2 hours to obtain Pd-activated alumina carrying 1.4% by weight of Pd. Cerium oxide (CeO 2 ), activated alumina and nitric acid acidic boehmite sol were added to and mixed with this Pd-activated alumina, and pulverized in a magnetic ball mill pot for 8 hours to obtain a slurry. 0.9 L of the honeycomb carrier was coated with this slurry in the same manner as the above zeolite-based catalyst, dried at 120 ° C, and 400 ° C.
It was baked in. The coating amount of the catalyst was about 100 g / L.

【0027】次いで、活性アルミナに硝酸ロジウム水溶
液を加え、含浸法でPh担持した後、乾燥機を用いて1
20℃で8時間乾燥し、空気気流中450℃で2時間焼
成して、Rhが0.9重量%担持されたPh−活性アル
ミナを得た。このPh−活性アルミナに硝酸酸性ベーマ
イトゾルを添加混合し、磁性ボールミルポットで8時間
粉砕してスラリーを得た。このスラリーを上記Pd−活
性アルミナがコートされたハニカム上にコーティング
し、120℃での乾燥、400℃での焼成の工程を経て
三元触媒を得た。該Ph−活性アルミナのコート量は、
42g/Lであった。
Then, an aqueous rhodium nitrate solution was added to the activated alumina, and Ph was carried by the impregnation method, and then dried with a drier.
It was dried at 20 ° C. for 8 hours and calcined in an air stream at 450 ° C. for 2 hours to obtain Ph-activated alumina supporting 0.9% by weight of Rh. A nitric acid-acidic boehmite sol was added to and mixed with this Ph-activated alumina, and pulverized in a magnetic ball mill pot for 8 hours to obtain a slurry. The slurry was coated on the Pd-activated alumina-coated honeycomb, dried at 120 ° C., and calcined at 400 ° C. to obtain a three-way catalyst. The coating amount of the Ph-activated alumina is
It was 42 g / L.

【0028】上記のCu−ZSM5触媒と三元触媒を直
列に配置して触媒コンバーターに組み込み、〔0.8L
+0.9L〕=1.7Lのタンデム触媒(1)を得た。
The above Cu-ZSM5 catalyst and the three-way catalyst are arranged in series and installed in a catalytic converter, and [0.8L
+0.9 L] = 1.7 L of tandem catalyst (1) was obtained.

【0029】実施例2 実施例1において、Cu−ZSM5触媒をPt−ZSM
5触媒にかえた以外は、同様にしてタンデム触媒(2)
を得た。ただし、Pt−ZSM5触媒粉の製法は以下の
通りである。ジニトロジアンミン白金水溶液を用い、噴
霧含浸法でSiO2 /Al2 3 のモル比が約42のN
4 型ZSM5粉末に白金を担持した。これを乾燥機を
用いて、120℃で24時間以上乾燥し、次いで電気炉
を用い、大気雰囲気下700℃で6時間焼成する工程を
経て、Ptが1.1重量%担持されたPt−ZSM5触
媒粉を得た。このPt−ZSM5触媒粉を実施例1と同
様にしてハニカム担体にコーティングした。この際のコ
ージェライト担体へのコート量は約120g/Lであ
り、コロイダルシリカの含浸担持量は、実施例1と同様
にSiO2 として6g/Lであった。
Example 2 In Example 1, the Cu-ZSM5 catalyst was replaced by Pt-ZSM.
Tandem catalyst (2) in the same manner except that the catalyst was changed to 5
Got However, the method for producing the Pt-ZSM5 catalyst powder is as follows. Using a dinitrodiammine platinum aqueous solution, N 2 having a SiO 2 / Al 2 O 3 molar ratio of about 42 was obtained by a spray impregnation method.
H 4 type ZSM5 powder was loaded with platinum. This was dried using a dryer at 120 ° C. for 24 hours or more, and then baked in an electric furnace at 700 ° C. for 6 hours in an air atmosphere. A catalyst powder was obtained. This Pt-ZSM5 catalyst powder was coated on the honeycomb carrier in the same manner as in Example 1. At this time, the coating amount on the cordierite carrier was about 120 g / L, and the impregnated and supported amount of colloidal silica was 6 g / L as SiO 2 as in Example 1.

【0030】実施例3 実施例1において、Cu−ZSM5触媒粉の焼成を73
0℃で6時間とし、コロイダルシリカの含浸を行わなか
った以外は、同様にしてタンデム触媒(3)を得た。
Example 3 In Example 1, the Cu-ZSM5 catalyst powder was calcined at 73
A tandem catalyst (3) was obtained in the same manner except that the temperature was set to 0 ° C. for 6 hours and impregnation with colloidal silica was not performed.

【0031】実施例4 実施例1において、Cu−ZSM5触媒粉の焼成を68
0℃で6時間とし、コロイダルシリカの含浸担持量を4
g/Lとした以外は、同様にしてタンデム触媒(4)を
得た。
Example 4 In Example 1, the Cu-ZSM5 catalyst powder was calcined at 68
6 hours at 0 ° C, and impregnated and supported amount of colloidal silica is 4
A tandem catalyst (4) was obtained in the same manner except that g / L was used.

【0032】実施例5 実施例1において、Cu−ZSM5触媒粉の焼成を70
0℃で5時間とし、コロイダルシリカの含浸担持量を6
g/Lとした以外は、同様にしてタンデム触媒(5)を
得た。
Example 5 In Example 1, Cu-ZSM5 catalyst powder was calcined at 70
5 hours at 0 ° C, and impregnated and supported amount of colloidal silica is 6
A tandem catalyst (5) was obtained in the same manner except that g / L was used.

【0033】比較例1 実施例1において、Cu−ZSM5触媒粉の焼成を50
0℃で4時間とし、スラリー製造に際しては、シリカゾ
ルを加えずにアルミナゾルのみを添加した。その添加量
は、Al2 3 として、吸着水を除いたCu−ZSM5
触媒粉に対して12重量%であった。さらに、コロイダ
ルシリカゾル溶液を用いてのシリカ分の含浸担持を実施
しなかった以外は、実施例1と同様にしてハニカム状の
Cu−ZSM5触媒を得た。更に、実施例1と同様にし
てCu−ZSM5触媒と三元触媒を触媒コンバーターに
組み込んだ1.7L〔=0.8L+0.9L〕のタンデ
ム触媒(6)を得た。
Comparative Example 1 In Example 1, the Cu-ZSM5 catalyst powder was calcined at 50 times.
The temperature was set to 0 ° C. for 4 hours, and at the time of slurry production, only alumina sol was added without adding silica sol. The amount added as Al 2 O 3, Cu-ZSM5, excluding the adsorbed water
It was 12% by weight based on the catalyst powder. Further, a honeycomb-shaped Cu-ZSM5 catalyst was obtained in the same manner as in Example 1 except that impregnation and loading of the silica component using the colloidal silica sol solution was not carried out. Further, in the same manner as in Example 1, a 1.7 L [= 0.8 L + 0.9 L] tandem catalyst (6) in which a Cu-ZSM5 catalyst and a three-way catalyst were incorporated in a catalytic converter was obtained.

【0034】試験例 上記実施例1〜5及び比較例1で得られた排気ガス浄化
用触媒の細孔径分布と触媒性能を以下に示す方法により
検討した。
Test Example The pore size distribution and the catalytic performance of the exhaust gas purifying catalysts obtained in Examples 1 to 5 and Comparative Example 1 were examined by the following method.

【0035】金属成分を担持したゼオライト系触媒の細
孔径分布測定 装置;島津製作所(マイクロメリテックス)製 アサッ
プ2400形 測定方法;N2 ガス吸着による定容法 細孔分布データ解析;BJH法 サンプルの前処理方法;250℃で約15時間の脱気処
理(10-3トン以下) 解析データ;吸着側のデータから、細孔直径に対して積
算吸着細孔容積をプロットし、これから直径4nm以下
の細孔の容積和V4 と、直径1nm以上100nm以下
の細孔の容積総和V100 を求め、〔V4 /V100 〕×1
00(%)を算出した。その結果を表1に示す。
The fineness of a zeolite-based catalyst supporting a metal component
Pore size distribution measuring device; Shimadzu (Micromeritex) Asap 2400 measuring method; Constant volume method pore distribution data analysis by N 2 gas adsorption; BJH method sample pretreatment method; Degassing at 250 ° C for about 15 hours processing (10-3 tons or less) analysis data; from the adsorption side of the data, plots the cumulative adsorption pore volume against pore diameter, from which the volume sum V 4 of the following pore diameter 4 nm, a diameter 1nm or more 100nm The total volume V 100 of the following pores is calculated, and [V 4 / V 100 ] × 1
00 (%) was calculated. The results are shown in Table 1.

【0036】触媒性能試験例 直列6気筒2Lエンジンを搭載した車両の排気系に上記
実施例及び比較例のタンデム型触媒を各々装着し、A/
F=14.6(ストイキ)で40秒運転した後、A/F
=21(リーン)で20秒運転するA/F切り換え運転
モードを20回繰り返した。この切り換え運動時の排気
ガス中のHC,CO,NOxの浄化率を以下の式により
算出して、その結果を表1に示す。このモード切り換え
運転中の触媒入口平均温度は380℃であった。
Example of Catalyst Performance Test The tandem type catalysts of the above-mentioned Examples and Comparative Examples were mounted on the exhaust system of a vehicle equipped with an inline 6-cylinder 2L engine, respectively.
After driving for 40 seconds at F = 14.6 (stoichi), A / F
The A / F switching operation mode of 20 seconds at = 21 (lean) was repeated 20 times. The purification rates of HC, CO, and NOx in the exhaust gas during this switching movement were calculated by the following formulas, and the results are shown in Table 1. The catalyst inlet average temperature during the mode switching operation was 380 ° C.

【数1】 [Equation 1]

【0037】[0037]

【表1】 [Table 1]

【0038】[0038]

【発明の効果】本発明の自動車排気ガス浄化用触媒は、
ゼオライト系触媒の細孔分布を特定することにより、ゼ
オライト系触媒による特定のガス成分に対する補足力が
抑制できるため、三元触媒の機能を低下させずに、スト
イキからリーンに渡る幅広い空燃比で運転されるエンジ
ンの排気ガスが高効率で浄化可能となるため、環境汚染
が少なく、経済性(燃費)に優れた自動車を提供するこ
とができる。
The catalyst for purifying automobile exhaust gas of the present invention comprises:
By specifying the pore distribution of the zeolite-based catalyst, it is possible to suppress the ability of the zeolite-based catalyst to supplement a specific gas component, so that it can be operated over a wide range of air-fuel ratios from stoichiometric to lean without degrading the function of the three-way catalyst. Since the exhaust gas of the engine to be used can be purified with high efficiency, it is possible to provide a vehicle with less environmental pollution and excellent economy (fuel consumption).

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI F01N 3/10 F01N 3/28 301J 3/28 301 B01D 53/36 102H 102B 102C 104A (56)参考文献 特開 平1−135542(JP,A) 特開 平6−171915(JP,A) 特開 平4−27706(JP,A) 特開 平2−139040(JP,A) 特開 平1−139145(JP,A) (58)調査した分野(Int.Cl.7,DB名) B01J 21/00 - 38/74 B01D 53/86,53/94 F01N 3/10,3/28 ─────────────────────────────────────────────────── ─── Continuation of front page (51) Int.Cl. 7 Identification symbol FI F01N 3/10 F01N 3/28 301J 3/28 301 B01D 53/36 102H 102B 102C 104A (56) Reference JP-A-1-135542 (JP, A) JP-A-6-171915 (JP, A) JP-A-4-27706 (JP, A) JP-A-2-139040 (JP, A) JP-A-1-139145 (JP, A) (JP-A) 58) Fields investigated (Int.Cl. 7 , DB name) B01J 21/00-38/74 B01D 53 / 86,53 / 94 F01N 3 / 10,3 / 28

Claims (3)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 4nm以下の細孔直径を有する多孔質結
晶性アルミノケイ酸塩粒子間の細孔の全容積和が1〜1
00nmの細孔直径を有する多孔質結晶性アルミノケイ
酸塩粒子間の細孔の全容積和の40%以上である多孔質
結晶性アルミノケイ酸塩を含むことを特徴とする排気ガ
ス浄化用触媒。
1. A porous binder having a pore diameter of 4 nm or less.
The total volume of pores between crystalline aluminosilicate particles is 1 to 1
Porous crystalline aluminosilicate with a pore diameter of 00 nm
An exhaust gas purifying catalyst comprising a porous crystalline aluminosilicate which accounts for 40% or more of the total volume of pores between the acid salt particles .
【請求項2】 4nm以下の細孔直径を有する多孔質結
晶性アルミノケイ酸塩粒子間の細孔の全容積和が1〜1
00nmの細孔直径を有する多孔質結晶性アルミノケイ
酸塩粒子間の細孔の全容積和の40%以上である多孔質
結晶性アルミノケイ酸塩を含む触媒を排気ガス流の上流
側に配し、三元触媒を含む触媒を排気ガス流の下流側に
配してなることを特徴とする排気ガス浄化用触媒。
2. A porous binder having a pore diameter of 4 nm or less.
The total volume of pores between crystalline aluminosilicate particles is 1 to 1
Porous crystalline aluminosilicate with a pore diameter of 00 nm
A catalyst containing 40% or more of the total volume of the pores between the acid salt particles is placed upstream of the exhaust gas flow, and a catalyst containing the porous crystalline aluminosilicate is placed downstream of the exhaust gas flow. An exhaust gas purifying catalyst, which is arranged on the side.
【請求項3】 請求項1又は2に記載の排気ガス浄化用
触媒において、4nm以下の細孔直径を有する前記粒子
間の細孔の全容積和を、1〜100nmの細孔直径を有
する前記粒子間の細孔の全容積和の50%以上85%以
下とすることを特徴とする排気ガス浄化用触媒。
3. The exhaust gas purifying catalyst according to claim 1, wherein the particles have a pore diameter of 4 nm or less.
The total volume sum of the pores between the exhaust gas purifying catalyst, which comprises 50% or more than 85% of the total volume sum of the pores between the particles having a pore diameter of 1 to 100 nm.
JP02777096A 1996-02-15 1996-02-15 Exhaust gas purification catalyst Expired - Fee Related JP3473245B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP02777096A JP3473245B2 (en) 1996-02-15 1996-02-15 Exhaust gas purification catalyst

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP02777096A JP3473245B2 (en) 1996-02-15 1996-02-15 Exhaust gas purification catalyst

Publications (2)

Publication Number Publication Date
JPH09220475A JPH09220475A (en) 1997-08-26
JP3473245B2 true JP3473245B2 (en) 2003-12-02

Family

ID=12230224

Family Applications (1)

Application Number Title Priority Date Filing Date
JP02777096A Expired - Fee Related JP3473245B2 (en) 1996-02-15 1996-02-15 Exhaust gas purification catalyst

Country Status (1)

Country Link
JP (1) JP3473245B2 (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2014166623A (en) * 2013-01-31 2014-09-11 Daihatsu Motor Co Ltd Catalyst for exhaust gas purification

Also Published As

Publication number Publication date
JPH09220475A (en) 1997-08-26

Similar Documents

Publication Publication Date Title
US10260395B2 (en) Nitrous oxide removal catalysts for exhaust systems
JP2660411B2 (en) Method for reducing and removing nitrogen oxides in exhaust gas
US20080271441A1 (en) Exhaust gas purification catalyst for automobile, exhaust gas purification catalyst system and purifying process of exhaust gas
US6555081B2 (en) Method of the purification of the exhaust gas from a lean-burn engine using a catalyst
JPH10235192A (en) Exhaust gas purification catalyst
JP3479980B2 (en) Exhaust gas purification method and exhaust gas purification catalyst
JP4703818B2 (en) Exhaust gas purification catalyst and exhaust gas purification method
EP0935055A2 (en) Device for purifying oxygen rich exhaust gas
JPH0884911A (en) Catalyst for decomposing nitrogen oxides and method for purifying exhaust gas of diesel engine using the same
JPH11276907A (en) Exhaust gas purification catalyst and method for producing the same
JPH08281106A (en) Exhaust gas purification catalyst and method for producing the same
JPH11221466A (en) Exhaust gas purification catalyst and exhaust gas purification method
JPH10192713A (en) Exhaust gas purification catalyst and method of using the same
JP3835436B2 (en) Exhaust gas purification method and exhaust gas purification catalyst
JP3473245B2 (en) Exhaust gas purification catalyst
JP4501166B2 (en) Exhaust gas purification system
JPH10165819A (en) Exhaust gas purification catalyst and method of using the same
JPH11123331A (en) Exhaust gas purification catalyst
JP2006346605A (en) Exhaust gas purification filter and exhaust gas purification device for internal combustion engine
JP4106762B2 (en) Exhaust gas purification catalyst device and purification method
JPH10235199A (en) Exhaust gas purification catalyst
JPH0957066A (en) Exhaust gas purification catalyst
JP2000015104A (en) Exhaust gas purification catalyst and exhaust gas purification method
JP2001058131A (en) Exhaust gas purification catalyst
JP3477982B2 (en) Exhaust gas purification catalyst and exhaust gas purification method

Legal Events

Date Code Title Description
FPAY Renewal fee payment (event date is renewal date of database)

Free format text: PAYMENT UNTIL: 20080919

Year of fee payment: 5

LAPS Cancellation because of no payment of annual fees