JPH05168860A - Purifying method of exhaust gas - Google Patents

Purifying method of exhaust gas

Info

Publication number
JPH05168860A
JPH05168860A JP3344781A JP34478191A JPH05168860A JP H05168860 A JPH05168860 A JP H05168860A JP 3344781 A JP3344781 A JP 3344781A JP 34478191 A JP34478191 A JP 34478191A JP H05168860 A JPH05168860 A JP H05168860A
Authority
JP
Japan
Prior art keywords
exhaust gas
catalyst
nox
lanthanum
porous carrier
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
JP3344781A
Other languages
Japanese (ja)
Inventor
Kenji Kato
健治 加藤
Tokuta Inoue
悳太 井上
Hidetaka Nohira
英隆 野平
Kiyoshi Nakanishi
清 中西
Satoru Iguchi
哲 井口
Tetsuo Kihara
哲郎 木原
Hideaki Muraki
秀昭 村木
Mariko Adachi
真理子 安達
Shiyuuji Tateishi
修士 立石
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 JP3344781A priority Critical patent/JPH05168860A/en
Publication of JPH05168860A publication Critical patent/JPH05168860A/en
Pending legal-status Critical Current

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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

Abstract

PURPOSE:To efficiently purify NOX in exhaust gas together with CO and hydrocarbons(HC) by bringing the exhaust gas of oxygen-excess atmosphere into contact with a catalyst of platinum and lanthanum deposited on a porous carrier. CONSTITUTION:A catalyst of platinum and lanthanum as a rare earth metal deposited on a porous carrier is used as a catalyst which simultaneously effects oxidization of CO and HC and reduction of NOX in the exhaust gas from an automobile on which a lean-burn engine is mounted. The porous carrier is alumina, zeolite, zirconia, silica alumina, silica, etc., which carries lanthanum by 0.05-1.0mol/L. By bringing the exhaust gas of oxygen-excess atmosphere into contact with this catalyst, NOX, NO and HC in the exhaust gas can be purified both in a normal driving state and in a transition state.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は排気ガス浄化方法に関
し、更に詳しくは、酸素過剰の排気ガス、即ち排気ガス
中に含まれる一酸化炭素、水素及び炭化水素等の還元性
物質を完全に酸化させるのに必要な酸素量よりも過剰な
量の酸素が含まれている排気ガス中の窒素酸化物(NO
x)を効率よく浄化する方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for purifying exhaust gas, and more particularly to a method for completely oxidizing exhaust gas in excess of oxygen, that is, reducing substances such as carbon monoxide, hydrogen and hydrocarbons contained in the exhaust gas. Nitrogen oxides (NO) in exhaust gas containing oxygen in excess of the oxygen required to
x) is efficiently purified.

【0002】[0002]

【従来の技術】従来、自動車の排気ガス浄化用触媒とし
て排気ガス中の一酸化炭素(CO)及び炭化水素(H
C)の酸化と、窒素酸化物(NOx)の還元とを同時に
行なって排気ガスを浄化する排気ガス浄化用三元触媒が
数多く知られている。このような触媒としては、例えば
コージェライトなどの耐火性担体にγ−アルミナスラリ
ーを塗布、焼成し、Pd、Pt、Rhなどの貴金属を担
持させたものが典型的である。
2. Description of the Related Art Conventionally, carbon monoxide (CO) and hydrocarbons (H) in exhaust gas have been used as catalysts for purifying exhaust gas of automobiles.
Many exhaust gas purification three-way catalysts that purify exhaust gas by simultaneously oxidizing C) and reducing nitrogen oxides (NOx) are known. As such a catalyst, for example, a refractory carrier such as cordierite is typically coated with γ-alumina slurry and baked to carry a noble metal such as Pd, Pt, or Rh.

【0003】ところで、前記排気ガス浄化用触媒の性能
はエンジンの設定空燃比によって大きく左右され、希薄
混合気、つまり空燃比の大きいリーン側では燃焼後の排
気ガス中の酸素量が多くなり、酸化作用が活発に、還元
作用が不活発になる。逆に空燃比の小さいリッチ側では
燃焼後の排気ガス中の酸素量が少なくなり、酸化作用が
不活発に、還元作用が活発になる。一方、近年、自動車
の低燃費化の要請に応えて通常走行時になるべく酸素過
剰の混合気で燃焼させるリーン側での運転が行なわれて
おり、リーン側でも充分にNOxを浄化できる触媒が望
まれていた。
By the way, the performance of the exhaust gas purifying catalyst is largely influenced by the set air-fuel ratio of the engine, and on the lean side where the air-fuel ratio is lean, that is, on the lean side where the air-fuel ratio is large, the amount of oxygen in the exhaust gas after combustion increases and the oxidation The action becomes active, and the reducing action becomes inactive. On the other hand, on the rich side where the air-fuel ratio is small, the amount of oxygen in the exhaust gas after combustion becomes small, the oxidation action becomes inactive, and the reducing action becomes active. On the other hand, in recent years, in response to the demand for low fuel consumption of automobiles, lean-side operation in which combustion is performed with an oxygen-rich mixture as much as possible during normal driving is performed, and a catalyst capable of sufficiently purifying NOx is also desired on the lean side. Was there.

【0004】かかる状況下に酸素過剰雰囲気下の自動車
排気ガス浄化用触媒として、一酸化炭素(CO)及び炭
化水素(HC)の酸化と、窒素酸化物(NOx)の還元
を同時に行なう触媒が種々提案されている。このような
触媒として、例えばアルミナに白金を担持したPt/Al
2O3 触媒が提案されている。しかしながら、酸素過剰雰
囲気下において、この触媒は白金の担持量を増加しても
NOx浄化率は高々30〜40%程度(触媒入側温度 275
℃、A/F=22)で実用上十分な浄化率とはいえなかっ
た。
Under such circumstances, various catalysts for purifying automobile exhaust gas in an oxygen-excess atmosphere include catalysts that simultaneously oxidize carbon monoxide (CO) and hydrocarbons (HC) and reduce nitrogen oxides (NOx). Proposed. As such a catalyst, for example, Pt / Al in which platinum is supported on alumina
2 O 3 catalysts have been proposed. However, in an oxygen-excessive atmosphere, the NOx purification rate of this catalyst is at most about 30-40% (catalyst inlet temperature 275
At a temperature of A and F of 22), the purification rate was not sufficient for practical use.

【0005】[0005]

【発明が解決しようとする課題】自動車の走行中のエン
ジンから排出される排気ガス組成は、理論A/F値近傍
からオーバーリーンのA/F値(約23)までの範囲内で
頻繁に変化する。従って、本発明は、前記した従来技術
の問題点を排除し、上記した実際の自動車等の走行状態
(A/F値の過渡の連続)において、排気ガス中のNO
x、CO及びHCを効率よく浄化することができる排気
ガス浄化方法を提供することを目的とする。
The composition of the exhaust gas emitted from the engine while the automobile is running frequently changes within the range from near the theoretical A / F value to the over lean A / F value (about 23). To do. Therefore, the present invention eliminates the above-mentioned problems of the prior art, and eliminates NO in exhaust gas in the above-described actual traveling state of an automobile or the like (continuous A / F value transition).
It is an object of the present invention to provide an exhaust gas purification method capable of efficiently purifying x, CO and HC.

【0006】[0006]

【課題を解決するための手段】本発明に従えば、酸素過
剰の排気ガスを多孔質担体に白金とランタンとを担持し
てなる触媒と接触させて排気ガス中の窒素酸化物を浄化
することを特徴とする排気ガス浄化方法が提供される。
以下に説明するように、本発明の排気ガス浄化方法を用
いることにより、希薄燃焼エンジンを搭載した車両から
排出される排気ガス中のCO、HC及びNOxを、定常
走行時(例えば40km/hr) 及び過渡状態(市街地走行模
擬状態)のいずれにおいても高効率で浄化することがで
きる。
According to the present invention, exhaust gas in excess of oxygen is brought into contact with a catalyst having platinum and lanthanum supported on a porous carrier to purify nitrogen oxides in the exhaust gas. An exhaust gas purification method is provided.
As will be described below, by using the exhaust gas purification method of the present invention, CO, HC and NOx contained in exhaust gas discharged from a vehicle equipped with a lean burn engine can be steadily run (for example, 40 km / hr). Also, it is possible to purify with high efficiency in both the transient state (simulated urban driving state).

【0007】本発明方法においては活性金属として白金
(Pt)とランタン(La)を用い、これらを多孔質担
体に担持させて使用する。本発明において用いることの
できる多孔質担体としてはアルミナ、ゼオライト、ジル
コニア、シリカアルミナ、シリカ等がある。これらの多
孔質担体の種類及び物性については特に限定はなく、従
来から触媒用として使用されていた任意の多孔質担体を
使用することができる。また、これらの多孔質担体はコ
ージェライト、耐熱金属合金等からなるモノリスにコー
トして用いても良い。
In the method of the present invention, platinum (Pt) and lanthanum (La) are used as active metals, and these are used by being supported on a porous carrier. Examples of the porous carrier that can be used in the present invention include alumina, zeolite, zirconia, silica alumina, silica and the like. The type and physical properties of these porous carriers are not particularly limited, and any porous carrier conventionally used for catalysts can be used. Further, these porous carriers may be used by coating them on a monolith made of cordierite, heat-resistant metal alloy or the like.

【0008】本発明に従えば、前記した多孔質担体に白
金及び希土類金属としてランタンを担持した触媒を使用
する。これらの金属の担持量には特に限定はないが、実
質的に有効なNOx浄化率を達成するために、好ましく
はランタンの担持量は0.05〜1.0mol/L、後述するNO
x吸着能力を最大限に活用するために、更に好ましくは
0.1〜0.4mol/Lであり、白金の担持量は、有効なNO
x浄化率を達成するために好ましくは 0.1〜10g/L、
NOxの還元能力を最大限に活用するために、特に好ま
しくは 0.5〜7g/Lである。
According to the present invention, a catalyst in which platinum and lanthanum as a rare earth metal are supported on the above-mentioned porous carrier is used. The supported amount of these metals is not particularly limited, but in order to achieve a substantially effective NOx purification rate, the supported amount of lanthanum is preferably 0.05 to 1.0 mol / L, NO described later.
x In order to maximize the adsorption capacity, it is more preferable
0.1 to 0.4 mol / L, and the amount of platinum supported is effective NO
x in order to achieve a purification rate of 0.1-10 g / L,
It is particularly preferably 0.5 to 7 g / L in order to maximize the reducing ability of NOx.

【0009】本発明において使用する排気ガス浄化用触
媒の製造方法については特に限定はなく、従来の一般的
方法に準ずることができる。例えば常法に従って調製し
たアルミナその他の多孔質担体を例えば硝酸ランタンな
どのランタン化合物の水溶液又はランタン化合物を含む
アルミナスラリー中に浸漬し、乾燥焼成(例えば温度60
0 〜 700℃)して多孔質担体にLaを担持させ、更にこ
れをジニトロジアミン白金、塩化白金酸などの白金化合
物の水溶液に浸漬して乾燥焼成(例えば温度 200〜 500
℃)して製造することができる。
The method for producing the exhaust gas purifying catalyst used in the present invention is not particularly limited and can be based on the conventional general method. For example, alumina or other porous carrier prepared according to a conventional method is immersed in an aqueous solution of a lanthanum compound such as lanthanum nitrate or an alumina slurry containing a lanthanum compound, and dried and calcined (for example, at a temperature of 60
(0 to 700 ° C.) to allow La to be carried on the porous carrier, which is further immersed in an aqueous solution of a platinum compound such as dinitrodiamine platinum or chloroplatinic acid and dried and baked (for example, at a temperature of 200 to 500).
℃) and can be manufactured.

【0010】本発明に係る排気ガス浄化方法において排
気ガスを浄化するにあたっては、希薄燃焼エンジンの排
気通路において触媒を設置する場所には特に限定はない
が、例えば車両の床下、スタート触媒または三元触媒の
下流側の床下などに配置するのが好ましい。
In purifying the exhaust gas in the exhaust gas purifying method according to the present invention, the place where the catalyst is installed in the exhaust passage of the lean burn engine is not particularly limited. For example, under the floor of the vehicle, start catalyst or three-way catalyst. It is preferably arranged under the floor on the downstream side of the catalyst.

【0011】本発明に係る浄化方法において、排気ガス
を触媒層に導入する空間速度(SV)には特に制限はな
いが、例えば 300,000〜10,000hr-1の範囲が好ましく、
また触媒層温度にも特に制限はないが 200〜 500℃が好
ましい。
In the purification method according to the present invention, the space velocity (SV) for introducing the exhaust gas into the catalyst layer is not particularly limited, but is preferably in the range of 300,000 to 10,000 hr -1 , for example.
The temperature of the catalyst layer is also not particularly limited, but is preferably 200 to 500 ° C.

【0012】[0012]

【作用】本発明に従って、ランタンと白金とを多孔質担
体に担持した触媒を用い、これを希薄燃焼する内燃機関
の排気通路に設置すると、以下の実施例にも示すよう
に、車両走行時に、CO、HC及びNOxを高効率で浄
化できる。
According to the present invention, when a catalyst in which lanthanum and platinum are supported on a porous carrier is used and is installed in the exhaust passage of an internal combustion engine which burns lean, as shown in the following examples, when the vehicle is running, CO, HC and NOx can be purified with high efficiency.

【0013】本発明による触媒の構成は、例えばアルミ
ナなどの多孔質担体の表面に酸化ランタン(La2O3) が覆
い、その上に白金が担持されており、かかる構成の触媒
は車両走行時のエンジン排出ガスの組成変化に対して次
のように作用するものと想定する。
The structure of the catalyst according to the present invention is such that lanthanum oxide (La 2 O 3 ) is covered on the surface of a porous carrier such as alumina, and platinum is carried thereon, and the catalyst having such a structure is used when the vehicle is running. It is assumed that the following changes will act on the composition change of the engine exhaust gas.

【0014】車両停止時:A/Fは理論A/F近傍で排
気ガス中にはNOxが少ない。触媒上では酸化ランタン
に吸着されていたNOxがPtに移動(逆スピルオーバ
ー)し、排気ガス中の還元ガス(CO、H2 、HC)と
反応し、NOxはN2 に還元される。このとき、還元ガ
スも浄化される。酸化ランタンに吸着されたNOxが無
くなれば、Pt上に還元ガスが吸着される。
When the vehicle is stopped: The A / F is near the theoretical A / F and the exhaust gas contains little NOx. NOx adsorbed on lanthanum oxide on the catalyst moves to Pt (reverse spillover) and reacts with the reducing gas (CO, H 2 , HC) in the exhaust gas, and NOx is reduced to N 2 . At this time, the reducing gas is also purified. When the NOx adsorbed on the lanthanum oxide disappears, the reducing gas is adsorbed on Pt.

【0015】車両加速時:A/Fは理論A/F近傍から
リーン(A/F=23)まで連続的に変化し、排気ガス中
にNOxが多量に存在するようになる。触媒上では排気
ガス中のNOxがPtに吸着した還元ガスによりN2
還元される。このとき、還元ガスも浄化される。
During vehicle acceleration: The A / F continuously changes from near the theoretical A / F to lean (A / F = 23), and a large amount of NOx exists in the exhaust gas. On the catalyst, NOx in the exhaust gas is reduced to N 2 by the reducing gas adsorbed on Pt. At this time, the reducing gas is also purified.

【0016】定常走行時:A/Fはリーン(A/F=2
3)状態で、排気ガス中のNOxは加速時より少なく、
HCは多めとなり、NOxはHCによりN2 に還元され
る。このとき、HCも浄化される。また、反応しないN
Oxは担体上の酸化ランタンに吸着される。
During steady running: A / F is lean (A / F = 2
In the 3) state, NOx in the exhaust gas is less than during acceleration,
HC is increased and NOx is reduced to N 2 by HC. At this time, HC is also purified. Also, N does not react
Ox is adsorbed on lanthanum oxide on the support.

【0017】減速時:A/Fはオートマティック(A/
T)車では理論A/F近傍であり、マニュアル(M/
T)車では酸化雰囲気(燃料カット)となり、排気ガス
中のNOxは少ない。触媒上ではA/T車の場合は車両
停止時と同じ状態になり、M/T車の場合にはNOxは
酸化ランタンに吸着保持される。
During deceleration: A / F is automatic (A / F
T) is near theoretical A / F, and manual (M /
The T) vehicle has an oxidizing atmosphere (fuel cut), and the amount of NOx in the exhaust gas is small. On the catalyst, in the case of the A / T vehicle, the state is the same as when the vehicle is stopped, and in the case of the M / T vehicle, NOx is adsorbed and retained by lanthanum oxide.

【0018】[0018]

【実施例】以下、実施例に従って、本発明を更に詳しく
説明するが、本発明の範囲をこれらの実施例に限定する
ものでないことはいうまでもない。以下の例において
「部」は特にことわらない限り「重量部」を示す。
EXAMPLES The present invention will be described in more detail below with reference to Examples, but it goes without saying that the scope of the present invention is not limited to these Examples. In the following examples, "parts" means "parts by weight" unless otherwise specified.

【0019】実施例1 担持量の異なるPt/酸化ランタン/アルミナのモノリ
ス触媒を調製し、NOx浄化活性を比較した。 a) アルミナ・スラリーの調製 アルミナ粉末 100部に、アルミナゾル (アルミナ含有率
10重量%) 70部、40重量%硝酸アルミニウム水溶液15部
および水30部を加えて攪拌混合し、コーテイング用スラ
リーを調製した。
Example 1 Pt / lanthanum oxide / alumina monolith catalysts having different loadings were prepared and their NOx purification activities were compared. a) Preparation of alumina slurry To 100 parts of alumina powder, alumina sol (alumina content rate)
10 parts by weight) 70 parts, 15 parts by weight of 40% by weight aluminum nitrate aqueous solution and 30 parts of water were added and mixed with stirring to prepare a coating slurry.

【0020】b) コーテイング及び焼成 コージェライト製モノリス状ハニカム担体を水に浸漬
し、余分な水を吹き払った後、上記a)で得られたスラリ
ーに浸漬し、取りだした後、余分なスラリーを吹き払
い、温度80℃で20分間乾燥し、更にこれを 600℃で1時
間焼成した。アルミナのコート量はモノリスの体積1リ
ットル当たり 120gであった。
B) Coating and firing A monolithic honeycomb carrier made of cordierite is immersed in water to blow off excess water, then immersed in the slurry obtained in the above a) and taken out, and then the excess slurry is removed. It was blown off, dried at a temperature of 80 ° C. for 20 minutes, and then calcined at 600 ° C. for 1 hour. The coated amount of alumina was 120 g per 1 liter volume of the monolith.

【0021】表1に示すLa担持量が得られるように調
製した所定濃度の硝酸ランタン水溶液に前記アルミナコ
ートハニカム担体を浸漬し、乾燥後、600 ℃で1時間焼
成し、表1の触媒No.1〜12に示したLa担持量の触媒
を得た。
The alumina-coated honeycomb carrier was immersed in an aqueous solution of lanthanum nitrate having a predetermined concentration prepared so as to obtain the amount of La shown in Table 1, dried, and calcined at 600 ° C. for 1 hour. Catalysts with La loadings shown in 1 to 12 were obtained.

【0022】c) Ptの担持 上記のようにして得られたLa担持モノリスを、表1に
示すPt担持量が得られるように調製した所定濃度のジ
ニトロジアミン白金の水溶液に浸漬し、表1の触媒No.
1〜12に示したPtの担持量を持つ触媒を調製した。比
較触媒としてLaを担持しないNo.13〜15の触媒も上記
実施例に準じた方法で併せ調製した。
C) Support of Pt The La-supported monolith obtained as described above was immersed in an aqueous solution of dinitrodiamine platinum having a predetermined concentration prepared so as to obtain the amount of supported Pt shown in Table 1, and Catalyst No.
Catalysts having Pt loadings shown in 1 to 12 were prepared. As comparative catalysts, catalysts of Nos. 13 to 15 which did not carry La were also prepared in the same manner as in the above-mentioned examples.

【0023】 表1:調製触媒 ────────────────────────── 担 持 量 触媒No. La(mol/L) Pt(g/L) 1 0.04 2.0 2 0.1 2.0 3 0.2 2.0 4 0.7 2.0 5 1.2 2.0 6 1.5 2.0 7 0.2 0.2 8 0.2 0.5 9 0.2 1.0 10 0.2 5.0 11 0.2 7.5 12 0.2 12.0 13 0.0 0.2 14 0.0 2.0 15 0.0 7.5 ───────────────────────── Table 1: Preparation catalyst ────────────────────────────────── Supported catalyst No. La (mol / L) Pt (g / L) 1 0.04 2.0 2 0.1 2.0 3 0.2 2.0 4 0.7 2.0 5 1.2 2.0 6 1.5 2.0 7 0.2 0.2 8 0.2 0.5 9 0.2 1.0 10 0.2 5.0 11 0.2 7.5 12 0.2 12.0 13 0.0 0.2 14 0.0 2.0 15 0.0 7.5 ─── ──────────────────────

【0024】評価 上記触媒の浄化性能を下記条件で評価した。 a) 定常活性 希薄燃焼エンジン(1.6リットル) の排気通路に上記No.
1〜15の各々の触媒(1.3リットル) を排気マニフォール
ドの下流 1.6mの位置に設置し、エンジンをA/F=22
で運転し、触媒の入り口側の温度が 275℃になるように
エンジンの出力を調整した。そしてこの条件下における
CO、HC及びNOxの浄化率を触媒前後のガス濃度を
排気ガス分析計で測定することにより調べた。結果を表
2に示す。
Evaluation The purification performance of the above catalyst was evaluated under the following conditions. a) Steady activation The above-mentioned No.
Each catalyst 1 to 15 (1.3 liters) was installed at a position 1.6 m downstream of the exhaust manifold, and the engine was set to A / F = 22.
The engine output was adjusted so that the temperature on the inlet side of the catalyst would be 275 ° C. Then, the purification rates of CO, HC and NOx under these conditions were examined by measuring the gas concentrations before and after the catalyst with an exhaust gas analyzer. The results are shown in Table 2.

【0025】 表 2 ─────────────────────────── 浄 化 率 (%) 触媒No. NOx HC CO 1 37 84 85 2 39 85 86 3 40 85 85 4 39 86 88 5 32 84 86 6 30 83 85 7 25 80 79 8 30 84 81 9 40 86 85 10 43 86 87 11 43 86 85 12 43 86 86 13* 15 76 75 14* 30 82 80 15* 35 85 82 ─────────────────────────── *:比較例 Table 2 ─────────────────────────── Purification rate (%) Catalyst No. NOx HC CO 1 37 84 85 2 39 85 86 3 40 85 85 4 39 86 88 5 32 84 86 6 30 83 85 7 25 80 79 8 30 84 81 9 40 86 85 10 43 86 87 11 43 86 85 12 43 86 86 13 * 15 76 75 14 * 30 82 80 15 * 35 85 82 ─────────────────────────── * : Comparative example

【0026】b) A/F変化における活性(過渡活性) 希薄燃焼エンジンをA/F=14.5(ストイキ)とA/F
=18(リーン)とを6分周期で変化させた。A/F=1
4.5と18とにおけるエンジンの触媒入り口側の排気ガス
温度はそれぞれ 250℃と 275℃であった。また、その時
のスロットル開度はA/F=14.5の時に全閉、A/F=
18の時にマニフォールド負圧 400mmHgであった。実験結
果は、排気分析計により触媒入り口側のNOx排出量と
触媒通過後のNOx排出量とを測定し、その両者の差よ
り減少したNOxの量を求め、ガス量で換算した後、N
Ox浄化率とした。その結果を表3に示す。
B) Activity in A / F change (transient activity) A / F = 14.5 (stoichi) and A / F in a lean burn engine.
= 18 (lean) was changed in a 6-minute cycle. A / F = 1
The exhaust gas temperatures on the catalyst inlet side of the engine at 4.5 and 18 were 250 ° C and 275 ° C, respectively. The throttle opening at that time is fully closed when A / F = 14.5, A / F =
At 18, the manifold negative pressure was 400 mmHg. The experimental results were obtained by measuring the NOx emission amount at the catalyst inlet side and the NOx emission amount after passing through the catalyst with an exhaust gas analyzer, and obtaining the NOx amount reduced from the difference between the two, and converting it into a gas amount, then N
It was defined as the Ox purification rate. The results are shown in Table 3.

【0027】 表 3 ─────────────────── 触媒No. NOx浄化率(%) 1 84 2 92 3 89 4 85 5 76 6 70 7 68 8 85 9 87 10 91 11 92 12 92 13* 53 14* 75 15* 81 ─────────────────── *:比較例 Table 3 ─────────────────── Catalyst No. NOx purification rate (%) 1 84 2 92 3 89 4 85 5 76 6 70 7 68 8 85 9 87 10 91 11 92 12 92 13 * 53 14 * 75 15 * 81 ─────────────────── * : Comparative example

【0028】上記結果から本発明による触媒および方法
は希薄燃焼エンジンを搭載した車両から排出されるNO
x、CO及びHCを効率よく浄化することが明らかであ
る。特に、Laの担持量0.05〜1.0mol/L、Ptの担持
量 0.5〜 7.0g/Lが好ましい。
From the above results, the catalyst and method according to the present invention are NO emitted from vehicles equipped with lean burn engines.
It is clear that x, CO and HC are efficiently purified. In particular, the La loading amount of 0.05 to 1.0 mol / L and the Pt loading amount of 0.5 to 7.0 g / L are preferable.

【0029】[0029]

【発明の効果】実際の運転において、自動車は加減速を
繰り返して使用されるのが現状である。かかる状況下に
排出される排気ガスに対し、本発明によれば、Ptの電
子状態を酸化ランタンによりコントロールすることによ
り、HCとNOxとの反応活性を向上させることがで
き、更に、酸化ランタンのNOx吸着特性を利用し、加
減速におけるNOx浄化率を大きく向上させることがで
きる。この結果、酸素過剰の排気ガス中のCO及びHC
を十分に浄化したもとで、同排気ガス中の窒素酸化物を
効率良く浄化することができる。
In the actual driving, the automobile is currently used by repeatedly accelerating and decelerating. According to the present invention, by controlling the electronic state of Pt by lanthanum oxide with respect to the exhaust gas discharged under such a condition, the reaction activity of HC and NOx can be improved. By utilizing the NOx adsorption characteristic, the NOx purification rate during acceleration / deceleration can be greatly improved. As a result, CO and HC in exhaust gas with excess oxygen
The nitrogen oxides in the exhaust gas can be efficiently purified under sufficient purification.

───────────────────────────────────────────────────── フロントページの続き (72)発明者 中西 清 愛知県豊田市トヨタ町1番地 トヨタ自動 車株式会社内 (72)発明者 井口 哲 愛知県豊田市トヨタ町1番地 トヨタ自動 車株式会社内 (72)発明者 木原 哲郎 愛知県豊田市トヨタ町1番地 トヨタ自動 車株式会社内 (72)発明者 村木 秀昭 愛知県愛知郡長久手町大字長湫字横道41番 地の1 株式会社豊田中央研究所内 (72)発明者 安達 真理子 愛知県愛知郡長久手町大字長湫字横道41番 地の1 株式会社豊田中央研究所内 (72)発明者 立石 修士 静岡県小笠郡大東町千浜7800番地 キャタ ラー工業株式会社内 ─────────────────────────────────────────────────── ─── Continuation of the front page (72) Inventor Kiyoshi Nakanishi 1st Toyota-cho, Toyota-shi, Aichi Prefecture Toyota Motor Co., Ltd. (72) Inventor Satoshi Iguchi 1st Toyota-cho, Toyota-shi, Aichi Toyota Motor Co., Ltd. ( 72) Inventor Tetsuro Kihara 1 Toyota Town, Toyota City, Aichi Prefecture, Toyota Motor Co., Ltd. (72) Inventor Hideaki Muraki 41, Nagakute Town, Nagakute Town, Aichi County, Aichi Prefecture 1 Toyota Central Research Institute Co., Ltd. (72 ) Inventor Mariko Adachi No. 41, Yokocho, Nagakute-machi, Aichi-gun, Aichi Prefecture, 1 Yokouchi Central Research Co., Ltd. (72) Inventor, Master Tateishi 7800, Chihama, Oto-gun, Shizuoka Prefecture, Cataler Industry

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 酸素過剰の排気ガスを多孔質担体に白金
とランタンとを担持してなる触媒と接触させて排気ガス
中の窒素酸化物を浄化することを特徴とする排気ガス浄
化方法。
1. A method for purifying exhaust gas, which comprises purifying nitrogen oxides in exhaust gas by bringing the exhaust gas in excess of oxygen into contact with a catalyst having platinum and lanthanum supported on a porous carrier.
JP3344781A 1991-12-26 1991-12-26 Purifying method of exhaust gas Pending JPH05168860A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP3344781A JPH05168860A (en) 1991-12-26 1991-12-26 Purifying method of exhaust gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP3344781A JPH05168860A (en) 1991-12-26 1991-12-26 Purifying method of exhaust gas

Publications (1)

Publication Number Publication Date
JPH05168860A true JPH05168860A (en) 1993-07-02

Family

ID=18371936

Family Applications (1)

Application Number Title Priority Date Filing Date
JP3344781A Pending JPH05168860A (en) 1991-12-26 1991-12-26 Purifying method of exhaust gas

Country Status (1)

Country Link
JP (1) JPH05168860A (en)

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US5762892A (en) * 1994-07-12 1998-06-09 Cataler Industrial Co., Ltd. Process for purifying exhaust gases
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