JPH09225265A - Exhaust gas purification device - Google Patents

Exhaust gas purification device

Info

Publication number
JPH09225265A
JPH09225265A JP8036316A JP3631696A JPH09225265A JP H09225265 A JPH09225265 A JP H09225265A JP 8036316 A JP8036316 A JP 8036316A JP 3631696 A JP3631696 A JP 3631696A JP H09225265 A JPH09225265 A JP H09225265A
Authority
JP
Japan
Prior art keywords
exhaust gas
catalyst
zeolite
palladium
exhaust
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP8036316A
Other languages
Japanese (ja)
Inventor
Hiroyuki Kanesaka
浩行 金坂
Junji Ito
淳二 伊藤
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 JP8036316A priority Critical patent/JPH09225265A/en
Publication of JPH09225265A publication Critical patent/JPH09225265A/en
Pending legal-status Critical Current

Links

Classifications

    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F01MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
    • F01NGAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL-COMBUSTION ENGINES
    • F01N2240/00Combination or association of two or more different exhaust treating devices, or of at least one such device with an auxiliary device, not covered by indexing codes F01N2230/00 or F01N2250/00, one of the devices being
    • F01N2240/18Combination or association of two or more different exhaust treating devices, or of at least one such device with an auxiliary device, not covered by indexing codes F01N2230/00 or F01N2250/00, one of the devices being an adsorber or absorber
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F01MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
    • F01NGAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL-COMBUSTION ENGINES
    • F01N2570/00Exhaust treating apparatus eliminating, absorbing or adsorbing specific elements or compounds
    • F01N2570/12Hydrocarbons

Landscapes

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

Abstract

(57)【要約】 【課題】 エンジン始動時の排気ガスを充分に浄化する
ことができる排気ガス浄化装置を提供すること。 【解決手段】 内燃機関の始動時の排気ガス中浄化装置
において、排気流入側に活性アルミナを主成分とした無
機物にパラジウムの濃度として4wt%/g以上、15
wt%/g以下となるように担持した粉末を用い、かつ
パラジウム担持量が100g/cf以上、500g/c
f以下になるようにハニカム担体に塗布して理論空燃比
近傍で炭化水素、一酸化炭素、窒素酸化物を浄化する三
元触媒とした触媒Aを配置し、排気流出側にハニカム担
体に炭化水素の吸着に有効なゼオライトをコーティング
した吸着触媒Bを配置した。また、これらゼオライト層
上に貴金属成分として白金、ロジウム、パラジウムの組
み合わせからなる群から選ばれた触媒層を備えた。
(57) Abstract: [PROBLEMS] To provide an exhaust gas purifying device capable of sufficiently purifying exhaust gas when an engine is started. SOLUTION: In an exhaust gas purifying apparatus at the time of starting an internal combustion engine, the concentration of palladium in an inorganic substance containing activated alumina as a main component at the exhaust gas inflow side is 4 wt% / g or more.
Use powder supported so as to be less than wt% / g, and carry a palladium amount of 100 g / cf or more, 500 g / c
The catalyst A, which is a three-way catalyst for purifying hydrocarbons, carbon monoxide, and nitrogen oxides near the stoichiometric air-fuel ratio by coating the honeycomb carrier so as to be f or less, is arranged. The adsorption catalyst B coated with zeolite effective for adsorbing the above was placed. Further, a catalyst layer selected from the group consisting of a combination of platinum, rhodium and palladium as a noble metal component was provided on these zeolite layers.

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】 この発明は、内燃機関のの
エンジン始動時の排気ガスを浄化する排気ガス浄化装置
に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an exhaust gas purifying apparatus that purifies exhaust gas of an internal combustion engine when the engine is started.

【0002】[0002]

【従来の技術】 従来の炭化水素の吸着触媒を用いる排
気ガス浄化装置として、特願平5−319931号の明
細書に示される様に排気流入側に三元触媒をコーティン
グした触媒を配置し、排気流出側にゼオライトとしてモ
ルデナイト、USY、β一ゼオライト、ZSM5からな
る群から選ばれた少なくとも1種以上を用い、これらゼ
オライト層上に活性セリア/またはアルミナを主成分と
した粉末に触媒成分として白金、パラジウム、ロジウム
からなる群から選ばれた1種以上の貴金属を含む触媒層
を備えてなる吸着触媒を配置した排気ガス浄化装置が提
案されている。
As an exhaust gas purifying apparatus using a conventional hydrocarbon adsorption catalyst, a catalyst coated with a three-way catalyst is arranged on the exhaust inflow side as shown in the specification of Japanese Patent Application No. 5-319931. At least one selected from the group consisting of mordenite, USY, β-zeolite, and ZSM5 is used as a zeolite on the exhaust gas outflow side, and platinum is used as a catalyst component in a powder containing activated ceria / or alumina as a main component on these zeolite layers. An exhaust gas purifying apparatus has been proposed in which an adsorption catalyst having a catalyst layer containing one or more noble metals selected from the group consisting of palladium, rhodium and the like is arranged.

【0003】[0003]

【発明が解決しようとする課題】 しかしながら、この
ような排気ガス浄化装置では、 (1)排気流入側に用いる三元触媒の浄化性能が排気ガ
スが低い温度域で充分でないため、活性温度に達する前
に、排気流出側の炭化水素吸着触媒から炭化水素が脱離
してしまう。 (2)ゼオライト屑の上にコーティングする触媒層の浄
化性能が不十分なため、活性温度に達する前にゼオライ
ト層から炭化水素が脱離してしまう。等の問題があり、
エンジン始動時の排気ガスを充分に浄化できない。
However, in such an exhaust gas purification apparatus, (1) the purification performance of the three-way catalyst used on the exhaust inflow side reaches the activation temperature because the exhaust gas is not sufficient in a low temperature range. Before, hydrocarbons are desorbed from the hydrocarbon adsorption catalyst on the exhaust gas outflow side. (2) Hydrocarbons are desorbed from the zeolite layer before the activation temperature is reached because the purification performance of the catalyst layer coated on the zeolite waste is insufficient. There are problems such as
Exhaust gas at engine start cannot be purified sufficiently.

【0004】[0004]

【課題を解決するための手段】 このような従来の問題
点を解決するため、本発明の排気ガス浄化装置は、内燃
機関の排気系に炭化水素吸着材とその上流側に少なくと
も1個以上の三元触媒を備えた内燃機関の始動時の排気
ガス中浄化装置において、排気流入側に活性アルミナを
主成分とした無機物にパラジウムの濃度として4wt%
/g以上、15wt%/g以下となるように担持した粉
末を用い、かつパラジウム担持量が100g/cf以
上、500g/cf以下になるようにハニカム担体に塗
布して理論空燃比近傍で炭化水素、一酸化炭素、窒素酸
化物を浄化する三元触媒とした触媒Aを配置し、排気流
出側にハニカム担体に炭化水素の吸着に有効なゼオライ
トをコーティングした吸着触媒Bを配置した構成とし
た。なお、請求項2に記載のように、吸着触媒Bをゼオ
ライトとして、モルデナイト、Y、USY、β一ゼオラ
イト、ZSM−5からなる群から選ばれた少なくとも1
種以上を用い、これらゼオライト層上に貴金属成分とし
て白金およびロジウム、パラジウム、パラジウムおよび
ロジウム、白金およびパラジウムおよびロジウムの組み
合わせからなる群から選ばれた触媒層を備えた構成とし
てもよい。
In order to solve such a conventional problem, an exhaust gas purifying apparatus of the present invention has a hydrocarbon adsorbent in an exhaust system of an internal combustion engine and at least one or more hydrocarbon adsorbents upstream thereof. In an exhaust gas purifying apparatus at the time of starting an internal combustion engine equipped with a three-way catalyst, the concentration of palladium in the inorganic material containing activated alumina as a main component on the exhaust gas inflow side is 4 wt%
/ G or more and 15 wt% / g or less of the supported powder, and a palladium carrier amount of 100 g / cf or more and 500 g / cf or less applied to the honeycomb carrier to give a hydrocarbon near the theoretical air-fuel ratio. The catalyst A, which is a three-way catalyst for purifying carbon monoxide and nitrogen oxides, is arranged, and the adsorption catalyst B, which is a honeycomb carrier coated with zeolite effective for adsorbing hydrocarbons, is arranged on the exhaust gas outflow side. As described in claim 2, at least one selected from the group consisting of mordenite, Y, USY, β-zeolite and ZSM-5 with the adsorption catalyst B as zeolite.
A catalyst layer selected from the group consisting of platinum and rhodium, palladium, palladium and rhodium, platinum and a combination of palladium and rhodium may be provided as a noble metal component on these zeolite layers by using one or more species.

【0005】[0005]

【発明の実施例】 以下、この発明の実施例を示す。P
dを4wt%担持した活性アルミナ粉末1410g、活
性アルミナ590g、2%硝酸溶液2000gを磁性ポ
ットに仕込み、振動ミル装置で混合粉砕し、ウオッシュ
コートスラリーを製造した。このスラリーをコーディエ
ライト製モノリス担体(1.3L 400セル)に塗布
し、乾燥後、400℃で1時間、空気雰囲気中で仮焼成
した。このコーティング作業を塗布量が、焼成後に約2
00g/Lになるまで繰り返し、Pd担持量が160g
/cfとなるようにして、排気流入側の(触媒A1)を
得た。次に、H型USYゼオライト(SiO2 /Al2
3 =50)1000g、シリカゾル(固形分20%)
1000g、水1000gをボールミルポットに投入し
粉砕して得られたスラリーをコーディエライト製モノリ
ス担体(1.3L 400セル)に塗布し乾燥後、40
0℃で1時問、空気雰囲気中で仮焼成した。このコーテ
ィング作業を塗布量が、焼成後に約150g/Lになる
まで繰り返す。さらに、前記と同様にしてUSY層の上
にPd−アルミナ触媒層を100g/Lになるように塗
布し、乾燥後、400℃で1時間焼成を行ない、排気流
出側の(吸着触媒B1)を得た。排気流入側に触媒A
1、排気流出側に吸着触媒B1を組み合わせ、タンデム
型吸着触媒−1を得た。
Embodiments of the present invention will be described below. P
1410 g of activated alumina powder carrying 4 wt% of d, 590 g of activated alumina, and 2000 g of 2% nitric acid solution were charged in a magnetic pot and mixed and pulverized by a vibration mill device to produce a washcoat slurry. This slurry was applied to a cordierite monolith carrier (1.3 L 400 cells), dried, and then calcined at 400 ° C. for 1 hour in an air atmosphere. The coating amount is about 2 after firing.
Repeated until it became 00g / L, and the amount of Pd supported was 160g.
(Catalyst A1) on the exhaust gas inflow side was obtained such that the ratio became / cf. Next, H-type USY zeolite (SiO 2 / Al 2
O 3 = 50) 1000 g, silica sol (solid content 20%)
1000 g of water and 1000 g of water were put into a ball mill pot and pulverized to obtain a slurry, which was coated on a cordierite monolith carrier (1.3 L 400 cells) and dried.
It was calcined at 0 ° C. for 1 hour in an air atmosphere. This coating operation is repeated until the applied amount becomes about 150 g / L after firing. Further, in the same manner as above, a Pd-alumina catalyst layer was applied onto the USY layer so as to have a concentration of 100 g / L, dried and then calcined at 400 ° C. for 1 hour to remove (adsorption catalyst B1) on the exhaust gas outflow side. Obtained. Catalyst A on the exhaust inflow side
1. The adsorption catalyst B1 was combined with the exhaust gas outflow side to obtain a tandem type adsorption catalyst-1.

【0006】次に作用を説明する。本発明の排気ガス浄
化装置においては、排気流入側に活性アルミナを主成分
とした無機物にパラジウムの濃度として4wt%/g以
上、15wt%/g以下となるように担持した粉末を用
い、かつパラジウム担持量が80g/cf以上、500
g/cf以下になるようにハニカム担体に塗布して理論
空燃比近傍で炭化水素、一酸化炭素、窒素酸化物を浄化
する三元触媒とした触媒Aを配置し、排気流出側にハニ
カム担体に炭化水素の吸着に有効なゼオライトをコーテ
ィングした吸着触媒Bを配置し、さらに吸着触媒Bがゼ
オライトとしてモルデナイト、Y、USY、β一ゼオラ
イト、ZSM−5からなる群から選ばれた少なくとも1
種以上を用い、これらゼオライト層上に貴金属成分とし
て白金およびロジウム、パラジウム、パラジウムおよび
ロジウム、白金およびパラジウムおよびロジウムの組み
合わせからなる群から選ばれた触媒層を備えてなること
を特徴とする排気ガス浄化装置としている。
Next, the operation will be described. In the exhaust gas purifying apparatus of the present invention, a powder in which an inorganic material mainly composed of activated alumina is supported on the exhaust gas inflow side so that the concentration of palladium is 4 wt% / g or more and 15 wt% / g or less, and palladium is used. Carrying capacity 80g / cf or more, 500
A catalyst A, which is a three-way catalyst that is applied to the honeycomb carrier so as to be less than or equal to g / cf and purifies hydrocarbons, carbon monoxide, and nitrogen oxides near the stoichiometric air-fuel ratio, is arranged. An adsorption catalyst B coated with zeolite effective for adsorbing hydrocarbons is arranged, and the adsorption catalyst B is at least one selected from the group consisting of mordenite, Y, USY, β-zeolite and ZSM-5 as the zeolite.
Exhaust gas characterized by comprising a catalyst layer selected from the group consisting of platinum and rhodium, palladium, palladium and rhodium, a combination of platinum and palladium and rhodium as precious metal components on these zeolite layers using at least one species It is used as a purification device.

【0007】貴金属成分としてパラジウムは低温域での
酸化性能に優れているが、パラジウムを使っただけでは
必ずしも充分な低温域の酸化活性が得られない。そこ
で、パラジウムの担持濃度として4wt%以上とするこ
とで担持されたパラジウムの粒子径を、あらかじめ触媒
反応に適した粒子径にし、低温域の酸化性能を向上させ
ている。担持濃度が15wt%以上では、逆に担持した
Pdの粒子径が大きくなりすぎ、触媒反応の活性点が減
少し、充分な低温域での活性向上効果が得られない。
Palladium as a noble metal component is excellent in oxidation performance in a low temperature range, but it is not always possible to obtain sufficient oxidation activity in a low temperature range only by using palladium. Therefore, by setting the supported concentration of palladium to 4 wt% or more, the particle size of the supported palladium is set in advance to a particle size suitable for the catalytic reaction to improve the oxidation performance in the low temperature range. On the contrary, when the loading concentration is 15 wt% or more, the particle size of the loaded Pd becomes too large, the active sites of the catalytic reaction decrease, and the sufficient activity improving effect in the low temperature range cannot be obtained.

【0008】吸着触媒に用いるゼオライトとしては、排
気ガス中に含まれる炭化水素の径に対応した、Y、US
Y、モルデナイト、β−ゼオライト、ZSM5を用いる
ことができる。さらに、多種類の炭化水素を効率よく吸
着するために、細孔径の異なる2種以上のゼオライトを
混合することも可能である。
Zeolite used for the adsorption catalyst is Y, US, which corresponds to the diameter of hydrocarbon contained in the exhaust gas.
Y, mordenite, β-zeolite, ZSM5 can be used. Further, in order to efficiently adsorb many kinds of hydrocarbons, it is possible to mix two or more kinds of zeolites having different pore sizes.

【0009】各種ゼオライトは、H型でも充分な吸着能
力を有するが、Pd、Pt、Cu、Co、Ag等の金属
成分をイオン交換、含浸法、浸漬法等の通常の方法を用
いて担持することにより、炭化水素の吸着特性および脱
離特性をさらに向上させることができる。各担持量は任
意でよいが、例えば、0.1〜15wt%位が好まし
い。0.1wt%より少ないと、炭化水素の吸着特性お
よび脱離抑制効果が少なく、逆に15wt%を越えても
効果は変わらない。
Although various zeolites have sufficient adsorption ability even in the H type, they carry metal components such as Pd, Pt, Cu, Co and Ag by a usual method such as ion exchange, impregnation method and immersion method. As a result, the hydrocarbon adsorption and desorption characteristics can be further improved. Although each supported amount may be arbitrary, for example, about 0.1 to 15 wt% is preferable. If it is less than 0.1 wt%, the adsorption property of hydrocarbons and the desorption suppressing effect are small, and conversely, if it exceeds 15 wt%, the effect does not change.

【0010】さらにゼオライト層の上に白金およびロジ
ウム触媒、パラジウム触媒、パラジウムおよびロジウム
触媒、白金およびパラジウムおよびロジウム触媒等の三
元触媒層をコーティングすることで吸着材にて低温時に
吸着していた炭化水素が、排気温度が上昇することで脱
離してくる場合に浄化することができ、さらに排気温度
が充分に上昇した条件下では、上流側の三元触媒で充分
に浄化できなかった未浄化の排気ガス成分を浄化するこ
とができ、エンジン始動時に排気温度が低い条件下から
排気ガス成分を充分に浄化することができる。
Further, by coating the zeolite layer with a three-way catalyst layer of platinum and rhodium catalyst, palladium catalyst, palladium and rhodium catalyst, platinum and palladium and rhodium catalyst, etc. Hydrogen can be purified when it is desorbed when the exhaust temperature rises, and under the condition that the exhaust temperature rises sufficiently, the unpurified hydrogen that could not be sufficiently purified by the upstream three-way catalyst The exhaust gas component can be purified, and the exhaust gas component can be sufficiently purified from the condition that the exhaust temperature is low when the engine is started.

【0011】以下に、他の実施例を示す。 (実施例2)実施例1のPd担持濃度を4wt%の代わ
りに8wt%にし、塗布量を150g/Lとした以外は
実施例1と同様な排気ガス浄化装置とした。Pdを8w
t%担持した活性アルミナ粉末940g、活性アルミナ
1060g、2%硝酸溶液2000gを磁性ポットに仕
込み、振動ミル装置で混合粉砕し、ウオッシュコートス
ラリーを製造した。コーディエライト製モノリス担体
(1.3L 400セル)に塗布し、乾燥後、400℃
で1時間、空気雰囲気中で仮焼成した。このコーティン
グ作業を塗布量が、焼成後に約150g/Lになるまで
繰り返しPd担持量が160g/cfとなるようにし
て、排気流入側の(触媒A2)を得た。排気流入側に触
媒A2、排気流出側に吸着触媒B1を組み合わせ、タン
デム型吸着触媒ー2を得た。
Another embodiment will be described below. (Example 2) An exhaust gas purifying apparatus similar to that of Example 1 was adopted except that the concentration of Pd carried in Example 1 was changed to 8 wt% instead of 4 wt% and the coating amount was changed to 150 g / L. Pd 8w
A magnetic pot was charged with 940 g of activated alumina powder supporting t%, 1060 g of activated alumina and 2000 g of a 2% nitric acid solution, and the mixture was ground by a vibration mill device to produce a washcoat slurry. It is applied to a cordierite monolith carrier (1.3 L 400 cells), dried, and then 400 ° C.
Calcination for 1 hour in an air atmosphere. This coating operation was repeated until the applied amount became about 150 g / L after firing so that the Pd carrying amount became 160 g / cf to obtain (catalyst A2) on the exhaust gas inflow side. A catalyst A2 was combined with the exhaust inflow side and an adsorption catalyst B1 was combined with the exhaust outflow side to obtain a tandem type adsorption catalyst-2.

【0012】(実施例3)実施例1のPd担持濃度を4
wt%の代わりに12wt%にし塗布量を150g/L
とした以外は実施例1と同様な排気ガス浄化装置とし
た。Pdを12wt%担持した活性アルミナ粉末630
g、活性アルミナ1370g、2%硝酸溶液2000g
を磁性ポットに仕込み、振動ミル装置で混合粉砕し、ウ
オッシュコートスラリーを製造した。コーディエライト
製モノリス担体(1.3L 400セル)に塗布し、乾
燥後、400℃で1特間、空気雰囲気中で仮焼成した。
このコーティング作業を塗布量が、焼成後に約150g
/Lになるまで繰り返しPd担持量が160g/cfと
なるようにして、排気流入側の(触媒A3)を得た。排
気流入側に触媒A3、排気流出側に吸着触媒B1を組み
合わせ、タンデム型吸着触媒ー3を得た。
(Embodiment 3) The concentration of Pd supported in Embodiment 1 is set to 4
12 wt% instead of wt% and the coating amount is 150 g / L
Except for the above, the same exhaust gas purification device as in Example 1 was used. Activated alumina powder 630 carrying 12% by weight of Pd
g, activated alumina 1370 g, 2% nitric acid solution 2000 g
Was charged into a magnetic pot and mixed and pulverized with a vibration mill device to produce a wash coat slurry. It was applied to a cordierite monolith carrier (1.3 L 400 cells), dried, and then calcined at 400 ° C. for 1 special period in an air atmosphere.
The coating amount is about 150g after firing.
The amount of Pd carried was repeatedly set to 160 g / cf until it became / L to obtain (catalyst A3) on the exhaust gas inflow side. A catalyst A3 was combined with the exhaust inflow side and an adsorption catalyst B1 was combined with the exhaust outflow side to obtain a tandem type adsorption catalyst-3.

【0013】(実施例4)実施例1のPd担持濃度を4
wt%の代わりに8wt%にし、塗布量を150g/L
としPd担持量を240g/Lとした以外は実施例1と
同様な排気ガス浄化装置とした。Pdを8wt%担持し
た活性アルミナ粉末1410g、活性アルミナ590
g、2%硝酸溶液2000gを磁性ポットに仕込み、振
動ミル装置で混合粉砕し、ウオッシュコートスラリーを
製造した。コーディエライト製モノリス担体(1.3L
400セル)に塗布し、乾燥後、400℃で1時間、
空気雰囲気中で仮焼成した。このコーティング作業を塗
布量が、焼成後に約150g/Lになるまで繰り返しP
d担持量が240g/cfとなるようにして、排気流入
側の(触媒A4)を得た。排気流入側に触媒A4、排気
流出側に吸着触媒B1を組み合わせ、タンデム型吸着触
媒ー4を得た。
(Embodiment 4) The concentration of Pd supported in Embodiment 1 is set to 4
8 wt% instead of wt%, coating amount 150 g / L
The exhaust gas purifying apparatus was the same as in Example 1 except that the amount of Pd carried was 240 g / L. 1410 g of activated alumina powder carrying 8 wt% of Pd, activated alumina 590
g, a 2% nitric acid solution (2000 g) was charged into a magnetic pot and mixed and pulverized with a vibration mill device to produce a washcoat slurry. Cordierite monolith carrier (1.3L
400 cells) and dried, then at 400 ℃ for 1 hour,
It was calcined in an air atmosphere. This coating operation is repeated until the coating amount becomes about 150 g / L after firing.
The amount of ad supported was set to 240 g / cf to obtain (catalyst A4) on the exhaust gas inflow side. The catalyst A4 was combined with the exhaust inflow side and the adsorption catalyst B1 was combined with the exhaust outflow side to obtain a tandem type adsorption catalyst-4.

【0014】(実施例5)実施例1のPd担持濃度を4
wt%の代わりに8wt%にし塗布量を220g/Lと
しPd担持量を480g/Lとした以外は実施例1と同
様な排気ガス浄化装置とした。Pdを8wt%担持した
活性アルミナ粉末1920g、活性アルミナ80g、2
%硝酸溶液2000gを磁性ポットに仕込み、振動ミル
装置で混合粉砕し、ウオッシュコートスラリーを製造し
た。コーディエライト製モノリス担体(1.3L 40
0セル)に塗布し、乾燥後、400℃で1時間、空気雰
囲気中で仮焼成した。このコーティング作業を塗布量
が、焼成後に約220g/Lになるまで繰り返しPd担
持量が480g/cfとなるようにして、排気流入側の
触媒A5を得た。排気流入側に触媒A5、排気流出側に
吸着触媒B1を組み合わせ、タンデム型吸着触媒ー5)
を得た。
(Embodiment 5) The concentration of Pd supported in Embodiment 1 is set to 4
The exhaust gas purifying apparatus was the same as that of Example 1 except that the coating amount was 220 g / L and the Pd carrying amount was 480 g / L instead of 8 wt%. 1920g of activated alumina powder carrying 8wt% of Pd, 80g of activated alumina, 2
% Nitric acid solution (2000 g) was charged in a magnetic pot and mixed and pulverized by a vibration mill device to produce a washcoat slurry. Cordierite monolith carrier (1.3L 40
(0 cell), dried, and then calcined at 400 ° C. for 1 hour in an air atmosphere. This coating operation was repeated until the applied amount became about 220 g / L after firing, and the Pd loading amount was set to 480 g / cf, to obtain the catalyst A5 on the exhaust gas inflow side. The catalyst A5 is combined with the exhaust inflow side and the adsorption catalyst B1 is combined with the exhaust outflow side to form a tandem type adsorption catalyst-5).
I got

【0015】(実施例6)実施例1のUSYゼオライト
の代わりにUSYゼオライトとβゼオライトの混合物を
用いた以外は実施例1と同様な排気ガス浄化装置とし
た。H型USYゼオライト(SiO2 /Al23 =5
0)500g、H型βゼオライト(SiO2 /Al2
3 =100)500g、シリカゾル(固形分 20%)
1000g、水1000gをボールミルポットに投入し
粉砕して得られたスラリーをコーディエライト製モノリ
ス担体(1.3L 400セル)に塗布し乾燥後、40
0℃で1時間、空気雰囲気中で仮焼成した。このコーテ
ィング作業を塗布量が、焼成後に約150g/Lになる
まで繰り返す。さらに、実施例1と同方法でUSYとβ
ゼオライトの温合層の上にPd−アルミナ触媒層を10
0g/Lになるようにコートし、乾燥、400℃で1時
間焼成を行ない、排気流出側の(吸着触媒B2)を得
た。排気流入側に触媒A1、排気流出側に吸着触媒B2
を組み合わせ、タンデム型吸着触媒ー6を得た。
Example 6 An exhaust gas purifying apparatus similar to that of Example 1 was used except that a mixture of USY zeolite and β zeolite was used instead of the USY zeolite of Example 1. H-type USY zeolite (SiO 2 / Al 2 O 3 = 5
0) 500 g, H-type β zeolite (SiO 2 / Al 2 O
3 = 100) 500 g, silica sol (solid content 20%)
1000 g of water and 1000 g of water were put into a ball mill pot and pulverized to obtain a slurry, which was coated on a cordierite monolith carrier (1.3 L 400 cells) and dried.
Calcination was performed at 0 ° C. for 1 hour in an air atmosphere. This coating operation is repeated until the applied amount becomes about 150 g / L after firing. Further, USY and β were obtained by the same method as in Example 1.
A Pd-alumina catalyst layer was formed on the zeolite warming layer 10 times.
It was coated so as to be 0 g / L, dried and calcined at 400 ° C. for 1 hour to obtain (adsorption catalyst B2) on the exhaust gas outflow side. The catalyst A1 is on the exhaust inflow side, and the adsorption catalyst B2 is on the exhaust outflow side.
Were combined to obtain a tandem type adsorption catalyst-6.

【0016】(実施例7)実施例1のUSYゼオライト
の代わりにUSYゼオライトとβゼオライトとZSM5
の混合物を用いた以外は実施例1と同様な排気ガス浄化
装置とした。H型USYゼオライト(SiO2 /Al2
3 =50)200g、H型βゼオライト(SiO2
Al23 =100)400g、H型ZSM5ゼオライ
ト(SiO2 /Al23 =700)400g、シリカ
ゾル(固形分20%)1000g、水1000gをボー
ルミルポットに投入し粉砕して得られたスラリーをコー
ディエライト製モノリス担体(1.3L 400セル)
に塗布し乾燥後、400℃で1時問、空気雰囲気中で仮
焼成した。このコーティング作業を塗布量が、焼成後に
約150g/Lになるまで繰り返す。さらに、実施例1
と同方法でUSYとβゼオライトとZSM5の混合層の
上にPdーアルミナ触媒層を100g/Lになるように
コートし、乾燥、400℃で1時間焼成を行ない、排気
流出側の吸着触媒B3を得た。排気流入側に触媒A1、
排気流出側に吸着触媒B3を組み合わせ、タンデム型吸
着触媒ー7を得た。
(Example 7) Instead of the USY zeolite of Example 1, USY zeolite, β zeolite and ZSM5
An exhaust gas purifying apparatus similar to that in Example 1 was used except that the mixture of No. 1 was used. H-type USY zeolite (SiO 2 / Al 2
O 3 = 50) 200 g, H type β zeolite (SiO 2 /
Al 2 O 3 = 100) 400 g, H-type ZSM5 zeolite (SiO 2 / Al 2 O 3 = 700) 400 g, silica sol (solid content 20%) 1000 g, and water 1000 g were put into a ball mill pot and pulverized to obtain a slurry. Cordierite monolith carrier (1.3L 400 cells)
After being applied and dried, it was calcined at 400 ° C. for 1 hour in an air atmosphere. This coating operation is repeated until the applied amount becomes about 150 g / L after firing. Furthermore, Example 1
In the same manner as above, a Pd-alumina catalyst layer was coated on the mixed layer of USY, β-zeolite and ZSM5 so as to be 100 g / L, dried and calcined at 400 ° C. for 1 hour. Obtained. Catalyst A1 on the exhaust inflow side,
An adsorption catalyst B3 was combined with the exhaust gas outflow side to obtain a tandem type adsorption catalyst-7.

【0017】(実施例8)実施例1のUSYゼオライト
の代わりにβゼオライトとZSM5の組合物を用いた以
外は実施例1と同様な排気ガス浄化装置とした。H型β
ゼオライト(SiO2 /Al23 =100)500
g、H型ZSM5ゼオライト(SiO2 /Al23
700)500g、シリカゾル(固形分20%)100
0g、水1000gをボールミルポットに投入し粉砕し
て得られたスラリーをコーディエライト製モノリス担体
(1.3L 400セル)に塗布し乾燥後、400℃で
1時間、空気雰囲気中で仮焼成した。このコーティング
作業を塗布量が、焼成後に約150g/Lになるまで繰
り返す。さらに、実施例1と同方法でβゼオライトとZ
SM5の混合層の上にPdーアルミナ触媒層を100g
/Lになるようにコートし、乾燥、400℃で1時間焼
成を行ない、排気流出側の吸着触媒B4を得た。排気流
入側に触媒A1、排気流出側に吸着触媒B4を組み合わ
せ、タンデム型吸着触媒ー8を得た。
(Example 8) An exhaust gas purifying apparatus similar to that of Example 1 was used except that a combination of β zeolite and ZSM5 was used instead of the USY zeolite of Example 1. H type β
Zeolite (SiO 2 / Al 2 O 3 = 100) 500
g, H type ZSM5 zeolite (SiO 2 / Al 2 O 3 =
700) 500 g, silica sol (solid content 20%) 100
0 g and 1000 g of water were placed in a ball mill pot and pulverized to obtain a slurry, which was applied to a cordierite monolith carrier (1.3 L 400 cells), dried, and then calcined at 400 ° C. for 1 hour in an air atmosphere. . This coating operation is repeated until the applied amount becomes about 150 g / L after firing. Further, β zeolite and Z were prepared in the same manner as in Example 1.
100g of Pd-alumina catalyst layer on the mixed layer of SM5
/ L, and dried and baked at 400 ° C. for 1 hour to obtain an adsorption catalyst B4 on the exhaust gas outflow side. A catalyst A1 was combined with the exhaust inflow side and an adsorption catalyst B4 was combined with the exhaust outflow side to obtain a tandem type adsorption catalyst-8.

【0018】(実施例9)実施例1のUSYゼオライト
の代わりにβゼオライトとモルデナイトの混合物を用い
た以外は実施例1と同様な排気ガス浄化装置とした。H
型βゼオライト(SiO2 /Al203=100)50
0g、H型モルデナイト(SiO2 /Al203=20
0)500g、シリカゾル(固形分20%)1000
g、水1000gをボールミルポットに投人し粉砕して
得られたスラリーをコーディエライト製モノリス担体
(1.3L 400セル)に塗布し乾燥後、400℃で
1時間、空気雰囲気中で仮焼成した。このコーティング
作業を塗布量が、焼成後に約150g/Lになるまで繰
り返す。さらに、実施例1と同方法でβゼオライトとモ
ルデナイトの混合層の上にPdーアルミナ触媒層を10
0g/Lになるようにコートし、乾燥、400℃で1時
間焼成を行ない、排気流出側の吸着触媒B5を得た。排
気流入側に触媒A1、排気流出側に吸着触媒B5を組み
合わせ、タンデム型吸着触媒ー9を得た。
Example 9 An exhaust gas purifying apparatus similar to that of Example 1 was used except that a mixture of β zeolite and mordenite was used instead of the USY zeolite of Example 1. H
Type β zeolite (SiO 2 / Al203 = 100) 50
0 g, H-type mordenite (SiO 2 / Al203 = 20
0) 500 g, silica sol (solid content 20%) 1000
g, 1000 g of water was thrown into a ball mill pot and pulverized, and the resulting slurry was applied to a cordierite monolith carrier (1.3 L 400 cells), dried, and then calcined at 400 ° C. for 1 hour in an air atmosphere. did. This coating operation is repeated until the applied amount becomes about 150 g / L after firing. Further, in the same manner as in Example 1, 10 Pd-alumina catalyst layers were formed on the mixed layer of β zeolite and mordenite.
It was coated so as to be 0 g / L, dried and calcined at 400 ° C. for 1 hour to obtain an adsorption catalyst B5 on the exhaust gas outflow side. The catalyst A1 was combined with the exhaust inflow side and the adsorption catalyst B5 was combined with the exhaust outflow side to obtain a tandem type adsorption catalyst-9.

【0019】(実施例10)実施例8のβゼオライトと
ZSM5の混合物層の上のPd触媒層の代わりにPt/
Rh触媒層を用いた以外は実施例8と同様な排気ガス浄
化装置とした。実施例8と同方法でβゼオライトとZS
M5の混合物を塗布量が、焼成後に約150g/Lにな
るように塗布する。次に、Ptを2wt%担持した活性
アルミナ粉末1130g、Rhを3wt%担持した活性
アルミナ粉末80g、酸化セリウム550g、活性アル
ミナ240g、2%硝酸溶液2000gを磁性ポットに
仕込み、振動ミル装置で混合粉砕し、ウオッシュコート
スラリーを製造し、このスラリーを用いてβゼオライト
とZSM5の混合層の上に乾燥後の塗布量が100g/
Lになるようにコートし、乾燥、400℃で1時間焼成
を行ない、排気流出側の吸着触媒B6を得た。排気流入
側に触媒A1、排気流出側に吸着触媒B6を組み合わ
せ、タンデム型吸着触媒ー10を得た。
(Example 10) Pt / Pd was used instead of the Pd catalyst layer on the mixture layer of β zeolite and ZSM5 of Example 8.
An exhaust gas purification apparatus similar to that in Example 8 was used except that the Rh catalyst layer was used. In the same manner as in Example 8, β zeolite and ZS
The mixture of M5 is applied so that the applied amount will be about 150 g / L after firing. Next, 1130 g of activated alumina powder carrying 2 wt% of Pt, 80 g of activated alumina powder carrying 3 wt% of Rh, 550 g of cerium oxide, 240 g of activated alumina, 2000 g of 2% nitric acid solution were charged in a magnetic pot and mixed and ground with a vibration mill device. To produce a washcoat slurry, and using this slurry, the coating amount after drying on the mixed layer of β zeolite and ZSM5 is 100 g /
It was coated so as to be L, dried, and calcined at 400 ° C. for 1 hour to obtain an adsorption catalyst B6 on the exhaust gas outflow side. The catalyst A1 was combined with the exhaust inflow side and the adsorption catalyst B6 was combined with the exhaust outflow side to obtain a tandem type adsorption catalyst-10.

【0020】(実施例11)実施例8のβゼオライトと
ZSM5の混合物層の上のPd触媒層の代わりにPd/
Rh触媒層を用いた以外は実施例8と同様な排気ガス浄
化装置とした。実施例8と同方法でβゼオライトとZS
M5の混合物を塗布量が、焼成後に約150g/Lにな
るように塗布する。次に、Pdを4wt%担持した活性
アルミナ粉末1300g、Rhを3wt%担持した活性
アルミナ粉160g、酸化セリウム270g、活性アル
ミナ270g、2%硝酸溶液2000gを磁性ポットに
仕込み、振動ミル装置で混合粉砕しウオッシュコートス
ラリーを製造し、このスラリーを用いてβゼオライトと
ZSM5の混合層の上に乾燥後の塗布量が100g/L
になるようにコートし、乾燥、400℃で1時間焼成を
行ない、排気流出側の吸着触媒B7を得た。排気流入側
に触媒A1、排気流出側に吸着触媒B7を組み介わせ、
タンデム型吸着触媒ー11を得た。
Example 11 Pd / Pd was used instead of the Pd catalyst layer on the mixture layer of β zeolite and ZSM5 of Example 8.
An exhaust gas purification apparatus similar to that in Example 8 was used except that the Rh catalyst layer was used. In the same manner as in Example 8, β zeolite and ZS
The mixture of M5 is applied so that the applied amount will be about 150 g / L after firing. Next, 1300 g of activated alumina powder carrying 4 wt% of Pd, 160 g of activated alumina powder carrying 3 wt% of Rh, 270 g of cerium oxide, 270 g of activated alumina, 2000 g of 2% nitric acid solution were charged in a magnetic pot and mixed and pulverized with a vibration mill device. A washcoat slurry is produced, and the slurry is used to apply a coating amount of 100 g / L on a mixed layer of β zeolite and ZSM5 after drying.
To obtain an adsorption catalyst B7 on the exhaust gas outflow side. The catalyst A1 is installed on the exhaust inflow side, and the adsorption catalyst B7 is installed on the exhaust outflow side.
A tandem type adsorption catalyst-11 was obtained.

【0021】(実施例12)実施例8のβゼオライトと
ZSM5の混合物層の上のPd触媒層の代わりにPt/
Pd/Rh触媒層を用いた以外は、実施例8と同様な排
気ガス浄化装置とした。実施例8と同方法でβゼオライ
トとZSM5の混合物を塗布量か、焼成後に約150g
/Lになるように塗布する。次に、Pdを4wt%担持
した活性アルミナ粉末1180g、Rhを3wt%担持
した活性アルミナ粉末160g、Ptを2wt%担持し
た活性アルミナ粉末240g、酸化セリウム270g、
活性アルミナ150g、2%硝酸溶液2000gを磁性
ポットに仕込み、振動ミル装置で混合粉砕し、ウォッシ
ュコートスラリーを製造し、このスラリーを用いてβゼ
オライトとZSM5の混合層の上に乾燥後の塗布量か1
00g/Lになるようにコートし、乾燥、400℃で1
時間焼成を行ない、排気流出側の吸着触媒B8を得た。
排気流入側に触媒A1、排気流出側に吸着触媒B8を組
み合わせ、タンデム型吸着触媒ー12を得た。各実施例
に用いるゼオライトとしては、H型ゼオライト以外にP
t、Pd、Ag、Cu、Co等の金属を担持したゼオラ
イトを用いることができる。
(Example 12) Instead of the Pd catalyst layer on the mixture layer of β zeolite and ZSM5 of Example 8, Pt /
The same exhaust gas purification apparatus as in Example 8 was used except that the Pd / Rh catalyst layer was used. In the same manner as in Example 8, the coating amount of the mixture of β zeolite and ZSM5 was applied or about 150 g after firing.
/ L to apply. Next, 1180 g of activated alumina powder carrying 4 wt% of Pd, 160 g of activated alumina powder carrying 3 wt% of Rh, 240 g of activated alumina powder carrying 2 wt% of Pt, 270 g of cerium oxide,
150 g of activated alumina and 2000 g of 2% nitric acid solution were charged into a magnetic pot, mixed and pulverized by a vibration mill device to produce a wash coat slurry, and the slurry was used to apply a coating amount after drying on a mixed layer of β zeolite and ZSM5. Or 1
Coat to 00g / L, dry, 1 at 400 ℃
Firing was performed for an hour to obtain an adsorption catalyst B8 on the exhaust gas outflow side.
The catalyst A1 was combined with the exhaust inflow side and the adsorption catalyst B8 was combined with the exhaust outflow side to obtain a tandem type adsorption catalyst-12. As the zeolite used in each example, in addition to H-type zeolite, P
Zeolites supporting metals such as t, Pd, Ag, Cu and Co can be used.

【0022】(比較例1)Pdを2wt%担持した活性
アルミナ粉末1410g、活性アルミナ590g、2%
硝酸溶液2000gを磁性ポットに仕込み、振動ミル装
置で混合粉砕し、ウオッシュコートスラリーを製造し
た。コーディエライト製モノリス担体(1.3L 40
0セル)に塗布し、乾燥後、400℃で1時間、空気雰
囲気中で仮焼成した。このコーティング作業を塗布量
が、焼成後に約200g/Lになるまで繰り返しPd担
持量が80g/cfとなるようにして、排気流入側の触
媒A6を得た。排気流入側に触媒A6、排気流出側に吸
着触媒B1を組み合わせ、タンデム型吸着触媒ーR1を
得た。
Comparative Example 1 1410 g of activated alumina powder carrying 2 wt% of Pd, 590 g of activated alumina, 2%
A nitric acid solution (2000 g) was charged in a magnetic pot and mixed and pulverized by a vibration mill device to produce a washcoat slurry. Cordierite monolith carrier (1.3L 40
(0 cell), dried, and then calcined at 400 ° C. for 1 hour in an air atmosphere. This coating operation was repeated until the coating amount became about 200 g / L after firing, and the Pd loading amount was set to 80 g / cf to obtain the catalyst A6 on the exhaust gas inflow side. A catalyst A6 was combined with the exhaust inflow side and an adsorption catalyst B1 was combined with the exhaust outflow side to obtain a tandem type adsorption catalyst-R1.

【0023】(比較例2)H型USY(SiO2 /Al
23 =7)1000g、シリカゾル(固形分20%)
1000g、水1000gをボールミルポットに投入し
粉砕して得られたスラリーを、コーディエライト製モノ
リス担体(1.3L 400セル)に塗布し乾燥後、4
00℃で1時間、空気雰囲気中で仮焼成した。このコー
ティング作業を塗布量が、焼成後に約150g/Lにな
るまで繰り返し、吸着触媒B9を得た。排気流入側に触
媒A1、排気流出側に吸着触媒B9を組み合わせ、タン
デム型吸着触媒ーR2を得た。
COMPARATIVE EXAMPLE 2 H-type USY (SiO 2 / Al
2 O 3 = 7) 1000 g, silica sol (solid content 20%)
1000 g of water and 1000 g of water were put into a ball mill pot and pulverized to obtain a slurry, which was coated on a cordierite monolith carrier (1.3 L 400 cells) and dried, and then 4
It was calcined in an air atmosphere at 00 ° C. for 1 hour. This coating operation was repeated until the coating amount became about 150 g / L after firing, to obtain adsorption catalyst B9. The catalyst A1 was combined with the exhaust inflow side and the adsorption catalyst B9 was combined with the exhaust outflow side to obtain a tandem type adsorption catalyst-R2.

【0024】以上説明してきた、実施例1〜12、及び
比較例1、2の触媒仕様をまとめると、図1のようにな
る。
The catalyst specifications of Examples 1 to 12 and Comparative Examples 1 and 2 described above are summarized in FIG.

【0025】また、各実施例および比較例について下記
評価条件でHC浄化特性評価(FTP75 A−ba
g)を日産自動車(株)製車両(排気量 3L)を用い
て行なった。その結果を図2に示す。
Further, for each of the examples and comparative examples, the HC purification characteristic evaluation (FTP75 A-ba) was carried out under the following evaluation conditions.
g) was performed using a vehicle manufactured by Nissan Motor Co., Ltd. (displacement: 3 L). The result is shown in FIG.

【0026】性能評価条件 評価条件としては、エンジン始動時に排出されるHC浄
化能を評価するためAーbag 0〜125秒間のエミ
ッション低減率を測定した。
Performance Evaluation Conditions As the evaluation conditions, the emission reduction rate of A-bag for 0 to 125 seconds was measured in order to evaluate the HC purification ability discharged at engine start.

【0027】 ガス組成 エンジン始動時(0〜125秒) 芳香族44.4% パラフィン33.3% オレフィン22.3% 以上、本発明の実施例を詳述してきたが、具体的な構成
はこの実施例に限られるものではなく、本発明の要旨を
逸脱しない範囲における変更等があっても、本発明に含
まれる。
Gas composition At engine start (0 to 125 seconds) 44.4% aromatics 33.3% paraffins 22.3% olefins The embodiments of the present invention have been described in detail above. The present invention is not limited to the embodiments, and changes and the like within the scope of the present invention are included in the present invention.

【0028】[0028]

【発明の効果】 以上説明したように、本発明の内燃機
関の排気系に炭化水素吸着材とその上流側に少なくとも
1個以上の三元触媒を備えた内燃機関の始動時の排気ガ
ス浄化装置においては、排気流入側に活性アルミナを主
成分とした無機物にパラジウムの濃度として4wt%/
g以上、15wt%/g以下となるように担持した粉末
を用い、かつパラジウム担持量が100g/cf以上、
500g/cf以下になるようにハニカム担体に塗布し
て理論空燃比近傍で炭化水素、一酸化炭素、窒素酸化物
を浄化する三元触媒とした触媒Aを配置し、排気流出側
にハニカム担体に炭化水素の吸着に有効なゼオライトを
コーティングした吸着触媒Bを配置し、さらに、吸着触
媒Bがゼオライトとしてモルデナイト、Y、USY、β
一ゼオライト、ZSM‐5からなる群から選ばれた少な
くとも1種以上を用い、これらゼオライト層上に貴金属
成分として白金およびロジウム、パラジウム、パラジウ
ムおよびロジウム、白金およびパラジウムおよびロジウ
ムの組み合わせからなる群から選ばれた触媒層を備えて
なるこれらゼオライト層上に備えてなることを特徴とす
る排気ガス浄化装置とすることで、エンジン始動直後の
炭化水素の排出量を大幅に低減できる。
As described above, the exhaust gas purifying apparatus at the time of starting the internal combustion engine, which is provided with the hydrocarbon adsorbent in the exhaust system of the internal combustion engine of the present invention and at least one or more three-way catalyst upstream thereof. In the exhaust gas inflow side, the concentration of palladium in the inorganic material mainly composed of activated alumina was 4 wt% /
a powder supported so as to be not less than g and not more than 15 wt% / g, and the amount of palladium carried is not less than 100 g / cf,
A catalyst A, which is a three-way catalyst that is applied to a honeycomb carrier so as to be 500 g / cf or less and purifies hydrocarbons, carbon monoxide, and nitrogen oxides near the stoichiometric air-fuel ratio, is arranged. An adsorption catalyst B coated with zeolite effective for adsorption of hydrocarbons is arranged, and the adsorption catalyst B is used as zeolite for mordenite, Y, USY, β.
One zeolite, at least one selected from the group consisting of ZSM-5 is used, and platinum and rhodium as precious metal components on these zeolite layers are selected from the group consisting of platinum and a combination of palladium and rhodium. With the exhaust gas purifying device characterized by being provided on these zeolite layers provided with the above-mentioned catalyst layer, the emission amount of hydrocarbons immediately after the engine is started can be greatly reduced.

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

【図1】実施例1〜12及び比較例1,2の触媒仕様を
示す図である。
FIG. 1 is a diagram showing catalyst specifications of Examples 1 to 12 and Comparative Examples 1 and 2.

【図2】HC浄化特性評価条件を示す図である。FIG. 2 is a diagram showing conditions for evaluating HC purification characteristics.

【符号の説明】[Explanation of symbols]

なし None

───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 B01J 29/44 F01N 3/20 H F01N 3/20 3/22 321A 3/22 321 3/24 ZABE 3/24 ZAB B01D 53/36 ZAB ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI Technical indication location B01J 29/44 F01N 3/20 H F01N 3/20 3/22 321A 3/22 321 3/24 ZABE 3/24 ZAB B01D 53/36 ZAB

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 内燃機関の排気系に炭化水素吸着材とそ
の上流側に少なくとも1個以上の三元触媒を備えた内燃
機関の始動時の排気ガス浄化装置において、排気流入側
に活性アルミナを主成分とした無機物にパラジウムの濃
度として4wt%/g以上、15wt%/g以下となる
ように担持した粉末を用い、かつパラジウム担持量が1
00g/cf以上、500g/cf以下になるようにハ
ニカム担体に塗布して理論空燃比近傍で炭化水素、一酸
化炭素、窒素酸化物を浄化する三元触媒とした触媒Aを
配置し、排気流出側にハニカム担体に炭化水素の吸着に
有効なゼオライトをコーティングした吸着触媒Bを配置
したことを特徴とするエンジン始動時の排気ガス温度の
低温時に排出される排気ガスを浄化できる排気ガス浄化
装置。
1. In an exhaust gas purifying apparatus for starting an internal combustion engine, which comprises a hydrocarbon adsorbent in an exhaust system of the internal combustion engine and at least one three-way catalyst upstream thereof, activated alumina is provided on an exhaust inflow side. An inorganic substance used as a main component is a powder that is loaded so that the concentration of palladium is 4 wt% / g or more and 15 wt% / g or less, and the amount of palladium loaded is 1
The catalyst A, which is a three-way catalyst that is applied to the honeycomb carrier to remove hydrocarbons, carbon monoxide, and nitrogen oxides near the stoichiometric air-fuel ratio so as to be not less than 00 g / cf and not more than 500 g / cf, is arranged, and exhaust gas outflow An exhaust gas purifying device capable of purifying exhaust gas discharged at a low exhaust gas temperature at engine start-up, in which an adsorption catalyst B coated with zeolite effective for adsorbing hydrocarbons is arranged on the side.
【請求項2】 吸着触媒Bがゼオライトとしてモルデナ
イト、Y、USY、β一ゼオライト、ZSM−5からな
る群から選ばれた少なくとも1種以上を用い、これらゼ
オライト層上に貴金属成分として白金およびロジウム、
パラジウム、パラジウムおよびロジウム、白金およびパ
ラジウムおよびロジウムの組み合わせからなる群から選
ばれた触媒層を備えてなることを特徴とする請求項1記
載の排気ガス浄化装置。
2. The adsorption catalyst B uses at least one selected from the group consisting of mordenite, Y, USY, β-zeolite and ZSM-5 as zeolite, and platinum and rhodium as precious metal components on these zeolite layers.
The exhaust gas purifying apparatus according to claim 1, comprising a catalyst layer selected from the group consisting of palladium, palladium and rhodium, platinum and a combination of palladium and rhodium.
JP8036316A 1996-02-23 1996-02-23 Exhaust gas purification device Pending JPH09225265A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP8036316A JPH09225265A (en) 1996-02-23 1996-02-23 Exhaust gas purification device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP8036316A JPH09225265A (en) 1996-02-23 1996-02-23 Exhaust gas purification device

Publications (1)

Publication Number Publication Date
JPH09225265A true JPH09225265A (en) 1997-09-02

Family

ID=12466440

Family Applications (1)

Application Number Title Priority Date Filing Date
JP8036316A Pending JPH09225265A (en) 1996-02-23 1996-02-23 Exhaust gas purification device

Country Status (1)

Country Link
JP (1) JPH09225265A (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20020043091A (en) * 2000-12-01 2002-06-08 이계안 Closed Coupled Converter structure using metal catalystic
KR20030096889A (en) * 2002-06-18 2003-12-31 현대자동차주식회사 Catalyst for prevention of poison for automobile
KR100482872B1 (en) * 2001-12-14 2005-04-14 현대자동차주식회사 Apparatus for purifying
JP2006281127A (en) * 2005-04-01 2006-10-19 Ne Chemcat Corp Oxidation catalyst for exhaust gas purification, and exhaust gas purification system using the same
US7229596B2 (en) 1998-06-17 2007-06-12 Nissan Motor Co., Ltd. Exhaust emission control device
JP2012020276A (en) * 2010-01-04 2012-02-02 Toyota Motor Corp Catalyst for purifying exhaust gas

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US7229596B2 (en) 1998-06-17 2007-06-12 Nissan Motor Co., Ltd. Exhaust emission control device
KR20020043091A (en) * 2000-12-01 2002-06-08 이계안 Closed Coupled Converter structure using metal catalystic
KR100482872B1 (en) * 2001-12-14 2005-04-14 현대자동차주식회사 Apparatus for purifying
KR20030096889A (en) * 2002-06-18 2003-12-31 현대자동차주식회사 Catalyst for prevention of poison for automobile
JP2006281127A (en) * 2005-04-01 2006-10-19 Ne Chemcat Corp Oxidation catalyst for exhaust gas purification, and exhaust gas purification system using the same
WO2006109417A1 (en) * 2005-04-01 2006-10-19 N.E. Chemcat Corporation Oxidation catalyst for exhaust gas purification and exhaust gas purification system using the same
JP2012020276A (en) * 2010-01-04 2012-02-02 Toyota Motor Corp Catalyst for purifying exhaust gas

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