JPH0256247A - Exhaust purification catalyst - Google Patents

Exhaust purification catalyst

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Publication number
JPH0256247A
JPH0256247A JP63231178A JP23117888A JPH0256247A JP H0256247 A JPH0256247 A JP H0256247A JP 63231178 A JP63231178 A JP 63231178A JP 23117888 A JP23117888 A JP 23117888A JP H0256247 A JPH0256247 A JP H0256247A
Authority
JP
Japan
Prior art keywords
catalyst
layer
zeolite
catalyst layer
purification
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
JP63231178A
Other languages
Japanese (ja)
Inventor
Masataka Kawabata
昌隆 川端
Shinichi Matsumoto
伸一 松本
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.)
Toyota Motor Corp
Original Assignee
Toyota Motor Corp
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 Toyota Motor Corp filed Critical Toyota Motor Corp
Priority to JP63231178A priority Critical patent/JPH0256247A/en
Publication of JPH0256247A publication Critical patent/JPH0256247A/en
Pending legal-status Critical Current

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

Abstract

(57)【要約】本公報は電子出願前の出願データであるた
め要約のデータは記録されません。
(57) [Summary] This bulletin contains application data before electronic filing, so abstract data is not recorded.

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は、内燃機関の排気浄化用触媒に関し、なかでも
三元触媒と呼ばれる排気浄化用触媒に関する。
DETAILED DESCRIPTION OF THE INVENTION [Field of Industrial Application] The present invention relates to an exhaust purification catalyst for an internal combustion engine, and more particularly to an exhaust purification catalyst called a three-way catalyst.

この三元触媒は、たとえば、自動車用内燃機関の排気系
に取り付けられ、排気中の炭化水素、一酸化炭素および
窒素酸化物の三成分を、酸化性成分と還元性成分とが化
学量論的に等量に近い状態で同時に無害化するために利
用される。
This three-way catalyst is installed, for example, in the exhaust system of an automobile internal combustion engine, and converts the three components of exhaust gas, hydrocarbons, carbon monoxide, and nitrogen oxides, so that the oxidizing component and the reducing component are stoichiometric. It is used to simultaneously detoxify in nearly equal amounts.

〔従来の技術〕[Conventional technology]

近年、内燃機関の排気浄化に用いられる触媒は、酸化と
還元を同時に効率良く行う三元触媒が主流とされている
。この三元触媒は、たとえば、白金(Pt)、パラジウ
ム(Pd)、ロジウム(Rh)等の貴金属触媒をハニカ
ム断面をしたモノリス担体に担持して供される。モノリ
ス担体は、コージェライト等の熱膨張率が小さく、耐熱
性の高い材料が用いられ、モノリス担体に活性アルミナ
、ジルコニア等の高表面積を備えた多孔質材料をコーテ
イング後、貴金属触媒が担持される。貴金属触媒を担持
した三元触媒の具体例としては、たとえば、特公昭57
−20013にPt−Pd−Rh系の三元触媒が開示さ
れている。本例においては、被毒により性能低下を生じ
易いPdを内層に、Pt−Rhを外層に配して、さらに
性能の向上を図っている。
In recent years, three-way catalysts that efficiently perform oxidation and reduction have become mainstream as catalysts used for purifying exhaust gas from internal combustion engines. This three-way catalyst is provided by supporting a noble metal catalyst such as platinum (Pt), palladium (Pd), or rhodium (Rh) on a monolithic carrier having a honeycomb cross section. The monolith carrier is made of a material with a low coefficient of thermal expansion and high heat resistance, such as cordierite. After coating the monolith carrier with a porous material with a high surface area such as activated alumina or zirconia, the noble metal catalyst is supported. . As a specific example of a three-way catalyst supporting a precious metal catalyst, for example,
-20013 discloses a Pt-Pd-Rh based three-way catalyst. In this example, Pd, which tends to deteriorate performance due to poisoning, is placed in the inner layer and Pt-Rh is placed in the outer layer to further improve performance.

このような三元触媒は、理論空燃比の近傍において高い
酸化還元能を発揮するため、触媒に流入する排気は、で
きるだけ理論空燃比に近づくように制御されている;−
この制御は、触媒上流に設けた酸素濃度センサーで検出
される排気中の酸素濃度に応じて行われる。具体的には
、触媒上流の排気中における酸素濃度に応じて、内燃機
関の燃料供給量、吸入空気量、排気中への空気の供給量
等を調整することによって、排気を理論空燃比付近で一
定とすることが行われる。
Since such a three-way catalyst exhibits high redox ability near the stoichiometric air-fuel ratio, the exhaust gas flowing into the catalyst is controlled to be as close to the stoichiometric air-fuel ratio as possible;
This control is performed according to the oxygen concentration in the exhaust gas detected by an oxygen concentration sensor provided upstream of the catalyst. Specifically, by adjusting the amount of fuel supplied to the internal combustion engine, the amount of intake air, the amount of air supplied to the exhaust gas, etc. according to the oxygen concentration in the exhaust gas upstream of the catalyst, the exhaust gas is kept close to the stoichiometric air-fuel ratio. It is done to keep it constant.

〔発明が解決しようとする課題〕[Problem to be solved by the invention]

ところが、自動車用内燃機関の冷間始動時には供給燃料
を増量させるため、排気中の空燃比が小さくなる(空燃
比がリッチとなる)。すなわち、排気中の一酸化炭素、
炭化水素の量が増える上、低温であるため、三元触媒の
機能が十分に働かず、特にCo、HCの浄化率が低下す
る問題があった。
However, when an automobile internal combustion engine is cold started, the amount of supplied fuel is increased, so the air-fuel ratio in the exhaust gas becomes small (the air-fuel ratio becomes rich). i.e. carbon monoxide in the exhaust,
Since the amount of hydrocarbons increases and the temperature is low, the function of the three-way catalyst does not work sufficiently, and there is a problem that the purification rate of Co and HC in particular decreases.

したがって、本発明の目的は、冷間状態でがっ空燃比が
リッチの状態において、特に炭化水素の浄化活性の高い
三元触媒を提供することにある。
Therefore, an object of the present invention is to provide a three-way catalyst that has particularly high hydrocarbon purification activity in a cold state and a rich air-fuel ratio.

〔課題を解決するための手段〕 そこで、本発明の排気浄化用触媒は、触媒層を2N設け
、内層にゼオライトを配した三元触媒を特徴とする。
[Means for Solving the Problems] Therefore, the exhaust purification catalyst of the present invention is characterized by a three-way catalyst in which a 2N catalyst layer is provided and zeolite is arranged in the inner layer.

具体的には、本発明の構成は次の通りである。Specifically, the configuration of the present invention is as follows.

なお、参考までに第1図における符号を付しである。Note that the reference numerals in FIG. 1 are used for reference.

本発明は、内燃機関の排気中の炭化水素、一酸化炭素お
よび窒素酸化物を無害化するための触媒である。この触
媒は、担体(10)上にゼオライトを主成分とする第1
触媒層(12)とその上に酸化還元能を備えた貴金属触
媒を主成分とする第2触媒層(14)を設けてなる。
The present invention is a catalyst for detoxifying hydrocarbons, carbon monoxide, and nitrogen oxides in the exhaust gas of an internal combustion engine. This catalyst consists of a first catalyst containing zeolite as a main component on a carrier (10).
A catalyst layer (12) and a second catalyst layer (14) whose main component is a noble metal catalyst having redox ability are provided on the catalyst layer (12).

上述した本発明の構成において、担体は、一体型のいわ
ゆるモノリス担体や、粒状のペレット担体等を用いるこ
とが可能である。モノリス担体は、コーディエライト等
のセラミックスや、耐熱性金属薄板を積層したものを用
いることができる。ペレット担体は、アルミナ等のペレ
ットを使用することができる。
In the configuration of the present invention described above, it is possible to use a monolithic so-called monolithic carrier, a granular pellet carrier, or the like as the carrier. The monolith carrier may be made of ceramics such as cordierite or a laminate of heat-resistant thin metal plates. As the pellet carrier, pellets of alumina or the like can be used.

第1触媒層は、ゼオライトを主成分とする多孔質体層が
形成される。ゼオライトは、沸石とも呼ばれ、長石類又
は准長石類に類似した化学組成を有しており、一般式W
−Z−0zn−Hz O(ここで、Wは Na、、Ca
、、に、Ba又はSrであり、ZはSi+AfでSt/
Aj!>1)で示される含水珪酸塩である。そして、ゼ
オライトの内部構造は、カゴ状の空洞や、それらの空洞
を相互に連結する種々の口径のトンネル状の孔路等の間
隙からなり、その間隙の存在により、イオン交換能、吸
着能、分子ふるい能および触媒能を備えている。
The first catalyst layer is a porous layer containing zeolite as a main component. Zeolite, also called zeolite, has a chemical composition similar to feldspars or subfeldspars, and has the general formula W
-Z-0zn-Hz O (where W is Na, Ca
, , is Ba or Sr, Z is Si+Af and St/
Aj! It is a hydrous silicate represented by >1). The internal structure of zeolite consists of cage-shaped cavities and gaps such as tunnel-like pores of various diameters that interconnect these cavities. It has molecular sieving and catalytic abilities.

なお、第1触媒層には、ゼオライトの他にアルミナ、ジ
ルコニア、希土類酸化物等の耐熱性を有する酸化物を含
有してもよい。
Note that the first catalyst layer may contain heat-resistant oxides such as alumina, zirconia, and rare earth oxides in addition to zeolite.

また、第1触媒層には、Pt、Pd、Rh等の貴金属触
媒を担持してもよい。
Further, a noble metal catalyst such as Pt, Pd, Rh, etc. may be supported on the first catalyst layer.

また、第1触媒層には、Pt、Pd、Rh等の貴金属に
加えセリア(c e at ) 、ランタナ(La20
.)等の希土類酸化物を担持してもよい。
In addition to precious metals such as Pt, Pd, and Rh, the first catalyst layer contains ceria (ceat) and lanthana (La20).
.. ) may be supported.

第2触媒層は、第1触媒層の上にアルミナ等のコート層
を形成した後、このコート層にPt、Pd、Rh等の貴
金属触媒をその溶液で担持することにより形成される。
The second catalyst layer is formed by forming a coat layer of alumina or the like on the first catalyst layer, and then supporting a precious metal catalyst such as Pt, Pd, Rh or the like in a solution on this coat layer.

これら貴金属は、1種又は2種以上を用いることができ
、担持量は、0.1〜10g/l(担体1tlに対する
担持重量)とすることが好ましい。この場合、0.1g
/It未満では、三元触媒の効果が小さく、また、10
 g / 1を超えると、高価な貴金属触媒の担持量に
見合う三元触媒の効果が得られない。また、このコート
層には、セリア(ceoz)、ランタナ<La201)
等の希土類酸化物、酸化ジルコニウム等を含有すること
ができる。これにより、第2触媒層の耐熱性が高まり、
また、セリアを添加した場合には、その酸素ストレージ
能によって三元触媒のウィンドウ(理論空燃比を中心と
した三元浄化性能を維持できる空燃比の幅)を広くする
ことができる。
One type or two or more types of these noble metals can be used, and the amount supported is preferably 0.1 to 10 g/l (weight supported per 1 tl of carrier). In this case, 0.1g
/It, the effect of the three-way catalyst is small, and 10
If it exceeds g/1, the effect of the three-way catalyst that is commensurate with the amount of supported precious metal catalyst cannot be obtained. This coat layer also contains ceria (ceoz), lantana <La201)
It can contain rare earth oxides such as zirconium oxide, etc., and zirconium oxide. This increases the heat resistance of the second catalyst layer,
Furthermore, when ceria is added, the window of the three-way catalyst (the range of air-fuel ratios that can maintain three-way purification performance centered on the stoichiometric air-fuel ratio) can be widened due to its oxygen storage ability.

なお、この排気ガス浄化触媒は、排気温度3゜0〜80
0℃の温度が望ましく、そのときの排気流の空間速度(
S V)は、10000−1200o o h−’であ
ることが好ましい。
Note that this exhaust gas purification catalyst is suitable for exhaust gas temperatures of 3.0 to 80.
A temperature of 0°C is desirable, and the space velocity of the exhaust flow at that time (
SV) is preferably 10000-1200 o oh-'.

〔作用〕[Effect]

上述した本発明の排気浄化用触媒によれば、冷間状態で
空燃比がリッチの状態のとき、内層の第1触媒層(12
)において炭化水素が選択的にゼオライトに吸着される
。このため、触媒通過後の排気中のHCが減少する。機
関が暖機されると、排気ガスの温度が上昇して触媒の温
度も上がるため、第1触媒層(12)のゼオライトから
HCが徐々に脱離され、活性の高まった第2触媒層(1
4)においてHCSCoが酸化されるとともに、NOx
が還元され、無害化される。
According to the exhaust purification catalyst of the present invention described above, when the air-fuel ratio is rich in a cold state, the first catalyst layer (12
), hydrocarbons are selectively adsorbed onto the zeolite. Therefore, HC in the exhaust gas after passing through the catalyst is reduced. When the engine is warmed up, the temperature of the exhaust gas rises and the temperature of the catalyst also rises, so HC is gradually desorbed from the zeolite in the first catalyst layer (12), and the second catalyst layer (12) with increased activity is removed. 1
In 4), HCSCo is oxidized and NOx
is reduced and rendered harmless.

〔実施例〕〔Example〕

次に、第1図に基づき、本発明にかかる排気浄化用触媒
の実施例を比較例と併せて説明する。
Next, examples of the exhaust purification catalyst according to the present invention will be described together with comparative examples based on FIG.

第1図は、モノリス触媒の流路横断面の一部分を示す図
、そして、第2図は、実施例1.2、及び、比較例1.
2.3の触媒の入りガス温度とHCの浄化率の関係を示
すグラフ、そして、第3図は、実施例3.4.5、及び
、比較例4の触媒の入りガス温度とHCの浄化率の関係
を示すグラフである。
FIG. 1 is a diagram showing a part of the flow path cross section of the monolithic catalyst, and FIG.
2.3 is a graph showing the relationship between the gas temperature entering the catalyst and the purification rate of HC, and FIG. It is a graph showing the relationship between rates.

(実施例1) 第1図に示すように、触媒をコーティングする担体とし
て、コーディエライト製のハニカム型モノリス担体10
を用いた。モノリス担体10は、断面積で1平方インチ
当たり400個の断面正方形のセルを有する見掛は容量
が1.37!のものを用い、木簡処理後、ウォッシュコ
ートスラリー中に浸漬した。スラリーは、ゼオライト1
00重量部、シリカゾル80重量部とを水および硝酸と
ともにボールミリングして生成した。続いてスラリー中
からモノリスを引き上げ、圧縮空気をセル面に吹き付け
てセル中の過剰スラリーを吹き去り、乾燥(200℃)
して遊離水を除去した後、700℃で1時間焼成した。
(Example 1) As shown in FIG. 1, a honeycomb-shaped monolithic carrier 10 made of cordierite was used as a carrier to be coated with a catalyst.
was used. The monolithic carrier 10 has an apparent capacity of 1.37! with 400 square cross-sectional cells per square inch of cross-sectional area! After treating the wooden tablet, it was immersed in wash coat slurry. The slurry is zeolite 1
00 parts by weight of silica sol and 80 parts by weight of silica sol were ball milled together with water and nitric acid. Next, the monolith was pulled up from the slurry, compressed air was blown onto the cell surface to blow off the excess slurry in the cell, and it was dried (200°C).
After removing free water, it was calcined at 700°C for 1 hour.

この結果、モノリス担体10上に厚さ約25μmのゼオ
ライトコート層(第1触媒層)12が得られた。
As a result, a zeolite coat layer (first catalyst layer) 12 having a thickness of about 25 μm was obtained on the monolithic carrier 10.

このゼオライトコート層12を形成したモノリス担体1
0に承前処理を施した後、アルミナを主体とするウォッ
シュコートスラリー中にモノリス担体を浸漬し、ゼオラ
イトコート層12の形成時と同様に吹き払い、乾燥、浸
漬を行い、厚さ約25μmのアルミナコート層を得た。
Monolith carrier 1 on which this zeolite coat layer 12 is formed
After pre-treatment on the zeolite coating layer 12, the monolithic carrier is immersed in a wash coat slurry mainly composed of alumina, and then blown off, dried and immersed in the same manner as in the formation of the zeolite coat layer 12 to form alumina with a thickness of approximately 25 μm. A coat layer was obtained.

このウォッシュコートスラリーは、アルミナ100重量
部、硝酸アルミニウム水溶液14重量部とを水お、よび
硝酸とともにボールミリングして生成した。
This washcoat slurry was produced by ball milling 100 parts by weight of alumina and 14 parts by weight of an aluminum nitrate aqueous solution together with water and nitric acid.

続いて、アルミナコート層に、常法にしたがい、白金(
Pt)、ロジウム(Rh)とともにランタン(La)、
セリウム(Ce)を担持して第2触媒層14とした。こ
れらの成分の担持量は、担体11当たり、ptを1.5
g、Rhを0.3g、Laを0.03モル、Ceを0.
3モルであった。
Next, platinum (
Pt), lanthanum (La) along with rhodium (Rh),
The second catalyst layer 14 was prepared by supporting cerium (Ce). The amount of these components supported is 1.5 pt per 11 carriers.
g, Rh 0.3 g, La 0.03 mol, Ce 0.
It was 3 moles.

(実施例2) 本実施例は、第1触媒層であるゼオライトコ−1−層の
厚さを10μmとした以外は、実施例1と同様に触媒を
調整したものである。
(Example 2) In this example, the catalyst was prepared in the same manner as in Example 1, except that the thickness of the zeolite co-1 layer, which was the first catalyst layer, was 10 μm.

(比較例1) 本比較例は、実施例1における第2触媒層を形成せず、
第1触媒層であるゼオライトコート層の厚さを約50μ
mとしたものである。
(Comparative Example 1) In this comparative example, the second catalyst layer in Example 1 was not formed,
The thickness of the zeolite coat layer, which is the first catalyst layer, is approximately 50 μm.
m.

(比較例2) 本比較例は、実施例1における第1触媒層であルゼオラ
イトコート層を形成せず、第2触媒層の厚さを約50μ
mとしたものである。
(Comparative Example 2) In this comparative example, the first catalyst layer in Example 1 was not formed with a zeolite coat layer, and the thickness of the second catalyst layer was approximately 50 μm.
m.

(比較例3) 本比較例は、実施例1の貴金属触媒層をモノリス基体上
に形成する第1触媒層とし、ゼオライトコート層をその
上に形成する第2触媒層としたものである。
(Comparative Example 3) In this comparative example, the noble metal catalyst layer of Example 1 was used as the first catalyst layer formed on the monolith substrate, and the zeolite coat layer was used as the second catalyst layer formed thereon.

(評価結果l) 上述の実施例1.2および比較例1.2.3の浄化率の
測定を行い、評価した。
(Evaluation Results 1) The purification rates of Example 1.2 and Comparative Example 1.2.3 described above were measured and evaluated.

上述の触媒は、排気量1.6Nの4気筒エンジンの排気
系に装置して、触媒活性を調べた。排気量ガス温度は、
100℃から500℃まで変化させ、HC浄化率を測定
した。なお、空燃比(A/F)は、13.5の燃料過剰
(リッチバーン)とし、排気ガスの空間速度(S V)
は、約6万h−1であった。
The above-mentioned catalyst was installed in the exhaust system of a four-cylinder engine with a displacement of 1.6N, and the catalyst activity was examined. The exhaust gas temperature is
The temperature was varied from 100°C to 500°C, and the HC purification rate was measured. The air-fuel ratio (A/F) is 13.5 (rich burn), and the space velocity (S V) of exhaust gas is
was approximately 60,000 h-1.

第2図から明らかなように、本発明にかかる実施例1.
2の触媒は、冷間始動時等に見られる低温で燃料が過剰
の下で、低温領域(100〜200℃付近)から極めて
高いHC浄化率を示し、低温活性が優れていることが分
る。そして、入りガス温度の上昇につれて浄化性能の低
下が見られるが、さらに高温域では、高い浄化活性を示
している。低温領域から高温領域の間で一度浄化率が低
下するのは、200℃を超えてHCの脱離が起こってか
ら、酸化反応が活発化するまで、少しのズレを生じるこ
とによると考えられるが、その間の時間は僅かであり、
問題とはならない。
As is clear from FIG. 2, Example 1 according to the present invention.
Catalyst No. 2 shows an extremely high HC purification rate from the low temperature range (near 100 to 200 degrees Celsius) under conditions of excess fuel at low temperatures, such as during cold startup, indicating that it has excellent low-temperature activity. . Although purification performance decreases as the temperature of the entering gas increases, it shows high purification activity in higher temperature ranges. The reason why the purification rate once decreases between the low-temperature region and the high-temperature region is thought to be due to a slight deviation occurring after HC desorption occurs at a temperature exceeding 200°C until the oxidation reaction becomes active. , the time in between is short,
Not a problem.

(実施例3) 第1図に示すように、触媒をコーティングする担体とし
て、コーディエライト製のハニカム型モノリス担体lO
を用いた。モノリス担体10は、断面積で1平方インチ
当たり400個の断面正方形のセルを有する見掛は容量
が1,3I!のちのを用い、水前処理後、ウォッシュコ
ートスラリー中に浸漬した。スラリーは、ゼオライト1
00重量部、シリカゾル80重量部とを水および硝酸と
ともにボールミリングして生成した。続いてスラリー中
からモノリスを引き上げ、圧縮空気をセル面に吹き付け
てセル中の過剰スラリーを吹き去り、乾燥(200℃)
して遊離水を除去した後、700℃で1時間焼成した。
(Example 3) As shown in Fig. 1, a honeycomb-shaped monolithic carrier made of cordierite was used as a carrier for coating the catalyst.
was used. The monolithic carrier 10 has an apparent capacity of 1.3 I! with 400 square cross-sectional cells per square inch of cross-sectional area. After pretreatment with water, the sample was immersed in a washcoat slurry. The slurry is zeolite 1
00 parts by weight of silica sol and 80 parts by weight of silica sol were ball milled together with water and nitric acid. Next, the monolith was pulled up from the slurry, compressed air was blown onto the cell surface to blow off the excess slurry in the cell, and it was dried (200°C).
After removing free water, it was calcined at 700°C for 1 hour.

この結果、モノリス担体10上に厚さ約25μmのゼオ
ライトコート層(第1コート層)が得られた。
As a result, a zeolite coat layer (first coat layer) with a thickness of about 25 μm was obtained on the monolithic carrier 10.

上記コート層を水前処理後、ジニトロジアミン白金水溶
液に浸漬し、24時間放置して担体11当たり、0.7
5gのptをイオン交換した。
After the above coating layer was pretreated with water, it was immersed in a dinitrodiamine platinum aqueous solution and left to stand for 24 hours.
5 g of pt was ion exchanged.

その後、余分な水分を吹き払い250℃で1時間乾燥し
た後、塩化ロジウム水溶液に浸漬し、24時間放置して
担体1j!当たり0.15gのRhをイオン交換し、第
1触媒層12を形成した。
After that, excess water was blown off and dried at 250°C for 1 hour, and then immersed in an aqueous rhodium chloride solution and left for 24 hours to support 1j! The first catalyst layer 12 was formed by ion-exchanging 0.15 g of Rh per sample.

次に、アルミナを主体とするウォッシュコートスラリー
中にモノリス担体を浸漬し、ゼオライトコート層の形成
時と同様に吹き払い、乾燥、浸漬を行い、厚さ約25μ
mのアルミナコート層(第2コート層)を得た。このウ
ォッシュコートスラリーは、アルミナ100重量部、硝
酸アルミニウム水溶液14重量部とを水および硝酸とと
もにボールミリングして生成した。
Next, the monolithic carrier was immersed in a washcoat slurry mainly composed of alumina, and was blown off, dried, and immersed in the same manner as when forming the zeolite coat layer, to a thickness of approximately 25 μm.
An alumina coat layer (second coat layer) of m was obtained. This washcoat slurry was produced by ball milling 100 parts by weight of alumina and 14 parts by weight of an aluminum nitrate aqueous solution together with water and nitric acid.

続いて、アルミナコート層に、常法にしたがい、白金(
pt)、ロジウム(Rh)を担持して第2触媒層14と
した。これらの成分の担持量は、担体12当たり、Pt
を0.75g、Rhを0.15gであった。
Next, platinum (
pt) and rhodium (Rh) were supported to form the second catalyst layer 14. The supported amount of these components is Pt per 12 carriers.
was 0.75 g, and Rh was 0.15 g.

なお、第1触媒層、第2触媒層に担持された貴金属の総
和は、担体11当たり、Ptを1.5g、Rhを0.3
gであった。
The total amount of noble metals supported on the first catalyst layer and the second catalyst layer is 1.5 g of Pt and 0.3 g of Rh per carrier 11.
It was g.

次に、セリア(CeOz)水溶液中に上記担体を浸漬、
吹き払い、乾燥を行うことにより、担体11当たり、0
.3モルのCeをI旦持した。
Next, the above carrier is immersed in a ceria (CeOz) aqueous solution,
By blowing off and drying, 0 per carrier 11
.. 3 mol of Ce was held once.

(実施例4) 本実施例は、第1、第2触媒層に担持されているptを
Pdに置き変えた以外は、実施例3と同様に触媒を調整
したものである。
(Example 4) In this example, the catalyst was prepared in the same manner as in Example 3, except that Pd supported on the first and second catalyst layers was replaced with Pd.

(実施例5) 本実施例は、実施例3と同様であるが、Ce担持をしな
い触媒である。
(Example 5) This example is similar to Example 3, but the catalyst is not supported with Ce.

(比較例4) 本比較例は、実施例3における第1触媒層を形成セす、
第2触媒層の厚さを約50μmとし、Ptを1.5g、
Rhを0.3g、Ceを0.3モルとしたものである。
(Comparative Example 4) In this comparative example, the first catalyst layer in Example 3 was formed.
The thickness of the second catalyst layer was about 50 μm, Pt was 1.5 g,
Rh was set at 0.3 g and Ce was set at 0.3 mol.

(評価結果2) 上述の実施例3.4.5および比較例4の浄化率の測定
を行い、評価した。
(Evaluation Results 2) The purification rates of Examples 3.4.5 and Comparative Example 4 described above were measured and evaluated.

上述の触媒は、排気i1.6j!の4気筒エンジンの排
気系に装置して、触媒活性を調べた。排気人ガス温度は
、100℃から500℃まで変化させ、HC浄化率を測
定した。なお、空燃比(A/F)は、13.5の燃料過
剰(リッチバーン)とし、排気ガスの空間速度(S V
)は、約6万h−1であったO 第3図から明らかなように、本発明にかかる実施例3.
4.5の触媒は、冷間始動時等に見られる低温で燃料が
過剰の下で、低温領域(100−〜200℃付近)から
極めて高いHC浄化率を示し、低温活性が優れているこ
とが分る。
The above catalyst has an exhaust i1.6j! The device was installed in the exhaust system of a four-cylinder engine, and the catalyst activity was investigated. The exhaust gas temperature was varied from 100°C to 500°C, and the HC purification rate was measured. The air-fuel ratio (A/F) is 13.5 (rich burn), and the space velocity of exhaust gas (S V
) was about 60,000 h-1. As is clear from FIG. 3, Example 3.
The catalyst No. 4.5 shows an extremely high HC purification rate from the low temperature range (around 100-200°C) and has excellent low-temperature activity under conditions of excess fuel at low temperatures such as during cold startup. I understand.

そして、入りガス温度の上昇につれて浄化性能の低下が
見られるが、さらに高温域では、HC1C01NOxと
も高い浄化活性を示している。低温領域から高温領域の
間で一度浄化率が低下するのは、200℃を超えてHC
の脱離が起こってから、酸化反応が活発化するまで、少
しのズレを生じることによると考えられるが、その間の
時間は僅かであり、問題とはならない。
As the temperature of the incoming gas increases, the purification performance decreases, but in the higher temperature range, both HC1C01NOx show high purification activity. The purification rate decreases once between the low-temperature region and the high-temperature region when the temperature exceeds 200°C.
This is thought to be due to the fact that there is a slight lag between the time when desorption occurs and the time when the oxidation reaction becomes active, but the time period is so short that it does not pose a problem.

また、実施例3.4.5と比較例4において、COの浄
化率を比較した結果、入りガス温度が150°C140
0℃の時のそれぞれの浄化率は、比較例4では、0%、
86%であったのに対し、実施例3では、43%、87
%、実施例4では、40%、85%、実施例5では、1
0%、85%であり、実施例3.4.5によれば、CO
の低温活性も向上することが分かる。
In addition, as a result of comparing the CO purification rates in Example 3.4.5 and Comparative Example 4, it was found that the entering gas temperature was 150°C140°C.
The respective purification rates at 0°C are 0% and 0% in Comparative Example 4, respectively.
While it was 86%, in Example 3, it was 43% and 87%.
%, Example 4: 40%, 85%, Example 5: 1
0%, 85% and according to Example 3.4.5, CO
It can be seen that the low-temperature activity of is also improved.

また、希土類酸化物を添加した実施例3.4では、低温
時において、HCにCeの0□ストレージ効果を作用さ
せ、貴金属との酸化反応により、HCがCogへ変化し
無害化される。そして、この時発生する反応熱によって
、触媒反応を加速させるため、実施例5よりも低温活性
が向上する。
Furthermore, in Example 3.4 in which a rare earth oxide is added, the 0□ storage effect of Ce is applied to HC at low temperatures, and HC is converted to Cog and rendered harmless through an oxidation reaction with the noble metal. Since the reaction heat generated at this time accelerates the catalytic reaction, the low-temperature activity is improved compared to Example 5.

以上、本発明の特定の実施例について説明したが、本発
明は、この実施例に限定されるものではなく、特許請求
の範囲に記載の範囲内で種々の実施態様が包含されるも
のである。
Although specific embodiments of the present invention have been described above, the present invention is not limited to these embodiments, and includes various embodiments within the scope of the claims. .

〔発明の効果〕〔Effect of the invention〕

以上より、本発明の排気浄化用触媒によれば、触媒層を
2層設け、内層にゼオライトを配したので、冷間状態で
かつ空燃比がリンチの状態においても、炭化水素の浄化
活性の高い三元触媒が得られる。
As described above, according to the exhaust gas purification catalyst of the present invention, since two catalyst layers are provided and zeolite is arranged in the inner layer, the catalyst has high hydrocarbon purification activity even in a cold state and at a Lynch air-fuel ratio. A three-way catalyst is obtained.

また、この排気浄化触媒は、燃料の加速増量時において
排気中のHCが増加したときにも、ゼオライトがHCを
吸着し、−時的なHCの増加を防止することができる。
In addition, in this exhaust purification catalyst, even when HC in the exhaust gas increases during accelerated fuel increase, the zeolite adsorbs HC and can prevent a temporal increase in HC.

【図面の簡単な説明】[Brief explanation of the drawing]

第1図から第3図は、本発明にかかる排気浄化触媒の実
施例を説明するための図面であり、第1図は、モノリス
触媒の流路横断面の一部分を示す図、 そして、第2図は、実施例1.2、及び、比較例1.2
.3の触媒の入りガス温度とHCの浄化率の関係を示す
グラフである。 第3図は、実施例3.4.5、及び、比較例4の触媒の
入りガス温度とHCの浄化率の関係を示すグラフである
。 10−・−・−担体 12−−一−−−第1触媒層 14・−・−第2触媒層 出願人  トヨタ自動車株式会社 10TEジイジ=9 第2rA 実説例1 触媒人’) 77’ス逼度 第3図 1こ泡拶り3 吻蔓ギ入すカ゛ス温、t   c’
1 to 3 are drawings for explaining an embodiment of the exhaust purification catalyst according to the present invention, and FIG. The figure shows Example 1.2 and Comparative Example 1.2.
.. 3 is a graph showing the relationship between the gas temperature entering the catalyst and the HC purification rate of No. 3. FIG. 3 is a graph showing the relationship between the gas temperature entering the catalyst and the HC purification rate in Example 3.4.5 and Comparative Example 4. 10---Support 12--1--First catalyst layer 14--Second catalyst layer Applicant Toyota Motor Corporation 10TE Jiji = 9 2nd rA Demonstration example 1 Catalyst person') 77's Degree 3 Figure 1 Bubble Greeting 3 Temperature of the kiss that enters the snout, t c'

Claims (1)

【特許請求の範囲】[Claims] 内燃機関の排気中の炭化水素、一酸化炭素および窒素酸
化物を無害化するための触媒であって、担体上にゼオラ
イトを主成分とする第1触媒層とその上に酸化還元能を
備えた貴金属触媒を主成分とする第2触媒層を設けてな
ることを特徴とする排気浄化用触媒。
A catalyst for detoxifying hydrocarbons, carbon monoxide and nitrogen oxides in the exhaust gas of internal combustion engines, comprising a first catalyst layer mainly composed of zeolite on a carrier and a redox ability on the first catalyst layer. An exhaust purification catalyst characterized by being provided with a second catalyst layer containing a precious metal catalyst as a main component.
JP63231178A 1988-05-17 1988-09-14 Exhaust purification catalyst Pending JPH0256247A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP63231178A JPH0256247A (en) 1988-05-17 1988-09-14 Exhaust purification catalyst

Applications Claiming Priority (3)

Application Number Priority Date Filing Date Title
JP63-119728 1988-05-17
JP11972888 1988-05-17
JP63231178A JPH0256247A (en) 1988-05-17 1988-09-14 Exhaust purification catalyst

Publications (1)

Publication Number Publication Date
JPH0256247A true JPH0256247A (en) 1990-02-26

Family

ID=26457405

Family Applications (1)

Application Number Title Priority Date Filing Date
JP63231178A Pending JPH0256247A (en) 1988-05-17 1988-09-14 Exhaust purification catalyst

Country Status (1)

Country Link
JP (1) JPH0256247A (en)

Cited By (29)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5164350A (en) * 1990-11-09 1992-11-17 Ngk Insulators, Ltd. Catalyst composition for purification of exhaust gas, catalyst for purification of exhaust gas, and process for producing said catalyst
US5376610A (en) * 1992-04-15 1994-12-27 Nissan Motor Co., Ltd. Catalyst for exhaust gas purification and method for exhaust gas purification
US5662869A (en) * 1992-12-06 1997-09-02 Ngk Insulators, Ltd. Exhaust gas purification method and apparatus therefor
US6042797A (en) * 1997-07-02 2000-03-28 Tosoh Corporation Adsorbent for ethylene, method for adsorbing and removing ethylene and method for purifying an exhaust gas
US6047544A (en) * 1997-08-20 2000-04-11 Nissan Motor Co., Ltd. Engine exhaust gas purification catalyst and exhaust gas purifier
JP2000126603A (en) * 1998-10-20 2000-05-09 Nissan Motor Co Ltd Exhaust gas purification catalyst and method for producing the same
US6117400A (en) * 1997-06-03 2000-09-12 Honda Giken Kogyo Kabushiki Kaisha HC emission control member for exhaust gas
US6220018B1 (en) * 1998-06-01 2001-04-24 Nissan Motor Co., Ltd. Exhaust emission control device
US6444610B1 (en) 1999-07-15 2002-09-03 Nissan Motor Co., Ltd. Exhaust gas purifying catalyst
JP2002256934A (en) * 2001-02-27 2002-09-11 Mazda Motor Corp Engine exhaust purification device
JP2002320856A (en) * 2001-04-27 2002-11-05 Toyota Motor Corp Exhaust gas purification catalyst
US6503862B1 (en) 2000-02-01 2003-01-07 Nissan Motor Co., Ltd. Exhaust gas purifying catalyst
EP1308200A1 (en) 2001-11-01 2003-05-07 Nissan Motor Co., Ltd. Exhaust gas purifying catalyst
US6589901B2 (en) 2000-04-26 2003-07-08 Nissan Motor Co., Ltd. Exhaust gas purifying catalyst and method of producing same
US6641788B1 (en) 1997-07-02 2003-11-04 Tosoh Corporation Absorbent for a hydrocarbon, and exhaust gas-purifying catalyst
US6667018B2 (en) 1994-07-05 2003-12-23 Ngk Insulators, Ltd. Catalyst-adsorbent for purification of exhaust gases and method for purification of exhaust gases
US6729129B2 (en) 2001-10-25 2004-05-04 Nissan Motor Co., Ltd. Exhaust gas purifying system
US6869573B2 (en) * 1990-11-09 2005-03-22 Ngk Insulators, Ltd. Heater and catalytic converter
US7112550B2 (en) 2002-01-24 2006-09-26 Nissan Motor Co., Ltd. Exhaust gas purifying catalyst
US7163661B2 (en) 2001-06-18 2007-01-16 Nissan Motor Co., Ltd. Exhaust gas purifying system
US7265073B2 (en) 2003-04-17 2007-09-04 Ict Co., Ltd. Exhaust gas purifying catalyst and process for purifying exhaust gas
EP1839747A2 (en) 2006-03-16 2007-10-03 ICT Co., Ltd. Adsorbent for hydrocarbons, catalyst for exhaust gas purification and method for exhaust gas purification
US7442346B2 (en) 1993-12-20 2008-10-28 Nissan Motor Co., Ltd. Device for the purification of exhaust gas
JP2009011976A (en) * 2007-07-06 2009-01-22 Denso Corp Hexagonal cell honeycomb catalyst body and exhaust gas purification apparatus using the same
US8258075B2 (en) 2007-02-06 2012-09-04 Mitsubishi Heavy Industries, Ltd. Catalyst for treating exhaust gases, method for producing the same, and method for treating exhaust gases
WO2013118425A1 (en) 2012-02-07 2013-08-15 本田技研工業株式会社 Catalyst structure for treating exhaust gas
WO2014156676A1 (en) 2013-03-29 2014-10-02 三井金属鉱業株式会社 Catalyst structure for exhaust gas treatment
CN116532152A (en) * 2023-06-19 2023-08-04 大连海事大学 Cu-SAPO-34/cordierite monolithic catalyst and preparation method thereof
US20230294044A1 (en) * 2020-07-20 2023-09-21 Cataler Corporation Exhaust gas purification catalyst system

Citations (1)

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JPS5641303A (en) * 1979-09-14 1981-04-18 Tsubakimoto Chain Co Manufacture of sintered oil containing bearing and chain using the said bearing

Patent Citations (1)

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Publication number Priority date Publication date Assignee Title
JPS5641303A (en) * 1979-09-14 1981-04-18 Tsubakimoto Chain Co Manufacture of sintered oil containing bearing and chain using the said bearing

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US6309616B1 (en) 1977-11-26 2001-10-30 Tosoh Corporation Method for adsorbing and removing ethylene and method for purifying an exhaust gas
US6869573B2 (en) * 1990-11-09 2005-03-22 Ngk Insulators, Ltd. Heater and catalytic converter
US5164350A (en) * 1990-11-09 1992-11-17 Ngk Insulators, Ltd. Catalyst composition for purification of exhaust gas, catalyst for purification of exhaust gas, and process for producing said catalyst
US5376610A (en) * 1992-04-15 1994-12-27 Nissan Motor Co., Ltd. Catalyst for exhaust gas purification and method for exhaust gas purification
US5887422A (en) * 1992-12-06 1999-03-30 Ngk Insulators, Ltd. Exhaust gas purification method and apparatus therefor
US5662869A (en) * 1992-12-06 1997-09-02 Ngk Insulators, Ltd. Exhaust gas purification method and apparatus therefor
US7442346B2 (en) 1993-12-20 2008-10-28 Nissan Motor Co., Ltd. Device for the purification of exhaust gas
US7820123B2 (en) 1993-12-20 2010-10-26 Nissan Motor Co., Ltd. Device for the purification of exhaust gas
US6667018B2 (en) 1994-07-05 2003-12-23 Ngk Insulators, Ltd. Catalyst-adsorbent for purification of exhaust gases and method for purification of exhaust gases
US6117400A (en) * 1997-06-03 2000-09-12 Honda Giken Kogyo Kabushiki Kaisha HC emission control member for exhaust gas
US6641788B1 (en) 1997-07-02 2003-11-04 Tosoh Corporation Absorbent for a hydrocarbon, and exhaust gas-purifying catalyst
US6103208A (en) * 1997-07-02 2000-08-15 Tosoh Corporation Adsorbent for ethylene, method for adsorbing and removing ethylene and method for purifying an exhaust gas
US6042797A (en) * 1997-07-02 2000-03-28 Tosoh Corporation Adsorbent for ethylene, method for adsorbing and removing ethylene and method for purifying an exhaust gas
US6047544A (en) * 1997-08-20 2000-04-11 Nissan Motor Co., Ltd. Engine exhaust gas purification catalyst and exhaust gas purifier
US6220018B1 (en) * 1998-06-01 2001-04-24 Nissan Motor Co., Ltd. Exhaust emission control device
JP2000126603A (en) * 1998-10-20 2000-05-09 Nissan Motor Co Ltd Exhaust gas purification catalyst and method for producing the same
US6444610B1 (en) 1999-07-15 2002-09-03 Nissan Motor Co., Ltd. Exhaust gas purifying catalyst
US6503862B1 (en) 2000-02-01 2003-01-07 Nissan Motor Co., Ltd. Exhaust gas purifying catalyst
US6589901B2 (en) 2000-04-26 2003-07-08 Nissan Motor Co., Ltd. Exhaust gas purifying catalyst and method of producing same
JP2002256934A (en) * 2001-02-27 2002-09-11 Mazda Motor Corp Engine exhaust purification device
JP2002320856A (en) * 2001-04-27 2002-11-05 Toyota Motor Corp Exhaust gas purification catalyst
US7163661B2 (en) 2001-06-18 2007-01-16 Nissan Motor Co., Ltd. Exhaust gas purifying system
US6729129B2 (en) 2001-10-25 2004-05-04 Nissan Motor Co., Ltd. Exhaust gas purifying system
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US6967186B2 (en) 2001-11-01 2005-11-22 Nissan Motor Co., Ltd. Exhaust gas purifying catalyst
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US7112550B2 (en) 2002-01-24 2006-09-26 Nissan Motor Co., Ltd. Exhaust gas purifying catalyst
US7265073B2 (en) 2003-04-17 2007-09-04 Ict Co., Ltd. Exhaust gas purifying catalyst and process for purifying exhaust gas
US7981834B2 (en) 2006-03-16 2011-07-19 Ict Co., Ltd. Adsorbent for hydrocarbons, catalyst for exhaust gas purification and method for exhaust gas purification
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US8258075B2 (en) 2007-02-06 2012-09-04 Mitsubishi Heavy Industries, Ltd. Catalyst for treating exhaust gases, method for producing the same, and method for treating exhaust gases
US8501133B2 (en) 2007-02-06 2013-08-06 Mitsubishi Heavy Industries, Ltd. Catalyst for treating exhaust gases, method for producing the same, and method for treating exhaust gases
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WO2013118425A1 (en) 2012-02-07 2013-08-15 本田技研工業株式会社 Catalyst structure for treating exhaust gas
US9358524B2 (en) 2012-02-07 2016-06-07 Honda Motor Co., Ltd. Catalyst structure for treating exhaust gas
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US10576458B2 (en) 2013-03-29 2020-03-03 Mitsui Mining & Smelting Co., Ltd. Catalyst structure for exhaust gas treatment
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