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JP2921130B2 - Exhaust gas purification catalyst - Google Patents
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JP2921130B2 - Exhaust gas purification catalyst - Google Patents

Exhaust gas purification catalyst

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Publication number
JP2921130B2
JP2921130B2 JP3005581A JP558191A JP2921130B2 JP 2921130 B2 JP2921130 B2 JP 2921130B2 JP 3005581 A JP3005581 A JP 3005581A JP 558191 A JP558191 A JP 558191A JP 2921130 B2 JP2921130 B2 JP 2921130B2
Authority
JP
Japan
Prior art keywords
catalyst
exhaust gas
zeolite
supported
activity
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Fee Related
Application number
JP3005581A
Other languages
Japanese (ja)
Other versions
JPH04243545A (en
Inventor
要次郎 入山
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
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Filing date
Publication date
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Priority to JP3005581A priority Critical patent/JP2921130B2/en
Publication of JPH04243545A publication Critical patent/JPH04243545A/en
Application granted granted Critical
Publication of JP2921130B2 publication Critical patent/JP2921130B2/en
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Expired - Fee Related legal-status Critical Current

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

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、自動車等の内燃機関や
硝酸製造工場などから排出される排気ガス中の窒素酸化
物を浄化する排気ガス浄化用触媒に関し、更に詳しくは
酸素過剰雰囲気下での耐久性に優れかつ NOx浄化活性の
高い温度域の広い排気ガス浄化用触媒に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an exhaust gas purifying catalyst for purifying nitrogen oxides in exhaust gas discharged from an internal combustion engine of a car or the like or a nitric acid production plant. The present invention relates to an exhaust gas purifying catalyst having excellent durability and high NOx purifying activity in a wide temperature range.

【0002】[0002]

【従来の技術】自動車等の内燃機関や硝酸製造工場など
から排出される排気ガス中には窒素酸化物 (NOx)等が含
まれているため、近年、排気ガス中の窒素酸化物の浄化
について種々の検討がなされている。従来、窒素酸化物
の浄化には還元性ガスの存在下に貴金属や金属の還元性
触媒を用いるのが主体であったが、近年、窒素酸化物を
酸化性ガスの存在下で浄化する触媒について種々研究さ
れている。ゼオライトは別名分子ふるいとも称されるよ
うに分子の大きさに匹敵する細孔を有し、吸着剤として
利用されるほか触媒として多くの反応に利用されてい
る。また Al2O3の負電荷を中和するために陽イオンを含
み、この陽イオンは水溶液中で他の陽イオンと容易に交
換されるためにイオン交換体としても利用されている。
ゼオライトはこの様な特徴を生かして近年自動車排ガス
浄化用触媒への利用が検討されている。例えばCuを担持
したゼオライト触媒が排気ガス浄化用触媒として知られ
ている(例えば特開昭60-97047号公報参照)。また特開
平1−135541号公報には、Pt,Pd,Rh,Ir又はRuから選
ばれる貴金属をイオン交換によりゼオライトに担持させ
た排気ガス浄化用触媒が開示されている。この触媒によ
れば燃料に対して酸素が過剰な、所謂リーン雰囲気下に
おける燃焼排気ガスに対しても NOx浄化性能に優れてい
る。
2. Description of the Related Art Exhaust gas discharged from internal combustion engines such as automobiles and nitric acid production plants contains nitrogen oxides (NOx). Various studies have been made. Conventionally, purification of nitrogen oxides has mainly involved the use of a noble metal or metal reducing catalyst in the presence of a reducing gas. Various studies have been made. Zeolite has pores comparable to the size of a molecule, also called a molecular sieve, and is used as an adsorbent and as a catalyst in many reactions. It also contains a cation to neutralize the negative charge of Al 2 O 3 , and this cation is used as an ion exchanger because it is easily exchanged with another cation in an aqueous solution.
Utilizing these characteristics, zeolite has recently been studied for use as a catalyst for purifying automobile exhaust gas. For example, a zeolite catalyst carrying Cu is known as an exhaust gas purifying catalyst (for example, see Japanese Patent Application Laid-Open No. 60-97047). JP-A-1-135541 discloses an exhaust gas purifying catalyst in which a noble metal selected from Pt, Pd, Rh, Ir or Ru is supported on zeolite by ion exchange. This catalyst is excellent in NOx purification performance even for combustion exhaust gas in a so-called lean atmosphere where oxygen is excessive with respect to fuel.

【0003】[0003]

【発明が解決しようとする課題】陽イオンとしてCuを担
持したCu担持ゼオライトは、Cuが NOxに対する高い吸着
能をもっているために、初期の触媒活性は優れているも
のの、例えば 600℃×5時間の触媒耐久試験後の劣化が
大きく、また低温(300℃以下) での NOx浄化率が低いと
いう問題があった。Cu担持ゼオライト触媒が耐久性に劣
るのは 600℃以上の高温ではCuがゼオライト中を移動し
て凝集し、触媒としての作用を失うためである。またCu
担持ゼオライト触媒が低温での活性が低いのは、低温で
は NOxが一部 NO2として存在し、Cu担持ゼオライト触媒
が NO2をN2 にまで還元することができないためであ
る。一方、Pt担持ゼオライト触媒は 300℃付近では高い
浄化能を持つが、 400℃以上では活性が落ち、有効な温
度域が狭いという問題がある。
The Cu-supported zeolite, which supports Cu as a cation, has excellent initial catalytic activity because Cu has a high adsorption capacity for NOx. There was a problem that deterioration after the catalyst durability test was large, and the NOx purification rate at low temperatures (300 ° C or lower) was low. The reason why the Cu-supported zeolite catalyst is inferior in durability is that at high temperatures of 600 ° C. or higher, Cu moves in the zeolite and aggregates, losing its catalytic effect. Also Cu
The activity of the supported zeolite catalyst at low temperatures is low because NOx is partially present as NO 2 at low temperatures, and the Cu-supported zeolite catalyst cannot reduce NO 2 to N 2 . On the other hand, the Pt-supported zeolite catalyst has a high purification ability at around 300 ° C., but has a problem that its activity is reduced at 400 ° C. or higher, and the effective temperature range is narrow.

【0004】従って、本発明は酸素過剰の希薄燃焼排気
ガス雰囲気下においても耐久性に優れかつ NOx浄化活性
の高い温度域の広い排気ガス浄化用触媒を開発すること
を目的とする。
Accordingly, an object of the present invention is to develop an exhaust gas purifying catalyst which has excellent durability even in a lean combustion exhaust gas atmosphere containing excess oxygen and has a wide temperature range with high NOx purifying activity.

【0005】[0005]

【課題を解決するための手段】本発明に従えば、Pt及び
Rhをゼオライトに担持させて成る排気ガス浄化用触媒に
おいて、担持Pt 100重量部に対するRhの担持量が 1.5〜
4.5重量部、好ましくは 1.8〜 4.2重量部である排気ガ
ス浄化用触媒が提供される。
According to the present invention, Pt and
In an exhaust gas purification catalyst in which Rh is supported on zeolite, the amount of supported Rh is 1.5 to 100 parts by weight of supported Pt.
An exhaust gas purifying catalyst is provided which is 4.5 parts by weight, preferably 1.8 to 4.2 parts by weight.

【0006】本発明に係る排気ガス浄化用触媒は、例え
ばゼオライトにPtとRhを各アンミン溶液でイオン交換す
ることによって担持することができ、従来のCu担持ゼオ
ライトと比較すると初期の触媒活性においては劣るもの
の、耐久後の劣化は小さく、特に耐久後の 300℃〜 400
℃での活性は上回っており、特に希薄燃焼エンジンの定
常運転時の排気温度が約 300℃程度であることを考慮す
れば実用上極めて有用である。
The exhaust gas purifying catalyst according to the present invention can be supported on zeolite, for example, by ion-exchange of Pt and Rh with each ammine solution. Compared with the conventional Cu-supported zeolite, the catalyst activity in the initial stage is lower. Although inferior, the deterioration after durability is small, especially 300 ℃ ~ 400 after durability.
The activity at ℃ is higher, and it is extremely useful in practice, especially considering that the exhaust gas temperature during steady operation of the lean burn engine is about 300 ℃.

【0007】本発明の最大の特徴は、PtとRhの担持量の
比をPt100重量部に対してRhを 1.5〜 4.5重量部、好ま
しくは 1.8〜 4.2重量部の範囲にすることによって、NO
x 浄化活性の高い温度域が拡大することである。本発者
らは従来Pt担持ゼオライト触媒やRh担持ゼオライト触媒
について研究開発をすすめて来たが、NOx 浄化活性の高
い温度領域が比較的狭い範囲にあるため、実用上問題が
あり、その範囲を如何にして広げていくかを検討してき
たが、PtとRhを前述した割合で担持させることによって
前記目的を達成することに成功した。
The most important feature of the present invention is that the ratio of the supported amount of Pt to Rh is in the range of 1.5 to 4.5 parts by weight, preferably 1.8 to 4.2 parts by weight, for 100 parts by weight of Pt.
x The expansion of the temperature range with high purification activity. The present inventors have been pursuing research and development on Pt-supported zeolite catalysts and Rh-supported zeolite catalysts.However, since the temperature range of high NOx purification activity is in a relatively narrow range, there is a problem in practical use. We have studied how to expand it, but succeeded in achieving the above object by supporting Pt and Rh in the above-mentioned ratio.

【0008】本発明において使用するゼオライトは、周
知の通り、SiO2及び Al2O3の四面体網状構造から構成さ
れ、個々の四面体構造はその隅を介して酸素の架橋によ
り互いに結合して通路及び空洞が貫通した網状構造を作
り、格子の負の電荷を有する交換点(強酸点)には交換
可能な陽イオンが導入されている。本発明において使用
するゼオライトのSiO2/Al2O3 のモル比は10〜 200が望
ましい。この比が10より少ないと 600℃以上の高温にお
いて熱安定性が悪くなり、またこの比が 200を超える
と、Al2O3 の量が減ってイオン交換点の減少、すなわち
触媒活性の低下を来たすことになる。熱劣化はアルミニ
ウム周辺の構造変化が主因と推定されるので、特に高温
での耐久性を確保したい場合にはSiO2/Al2O3 のモル比
を20以上としたゼオライトを用いるのが好ましい。特に
SiO2/Al2O3 のモル比が20〜 200であるZSM-5,Y又は
モルデナイト構造が望ましい。
The zeolite used in the present invention is, as is well known, composed of a tetrahedral network of SiO 2 and Al 2 O 3 , and the individual tetrahedral structures are bonded to each other through the corners by oxygen crosslinking. Exchangeable cations are introduced at the negatively charged exchange points (strong acid sites) of the lattice, with a network having channels and cavities penetrating therethrough. The molar ratio of the zeolite of SiO 2 / Al 2 O 3 for use in the present invention is from 10 to 200 is preferable. If this ratio is less than 10, thermal stability will be poor at high temperatures of 600 ° C or higher, and if this ratio exceeds 200, the amount of Al 2 O 3 will decrease and the ion exchange point will decrease, that is, the catalytic activity will decrease. Will come. Since thermal deterioration is presumed to be mainly caused by structural changes around aluminum, it is preferable to use zeolite with a molar ratio of SiO 2 / Al 2 O 3 of 20 or more, particularly when it is desired to ensure durability at high temperatures. Especially
A ZSM-5, Y or mordenite structure having a SiO 2 / Al 2 O 3 molar ratio of 20 to 200 is desirable.

【0009】ゼオライトへのPt及びRhの担持はイオン交
換または含浸法によって行うことができる。イオン交換
法、含浸法共に通常行われている方法を用いることがで
きる。例えばイオン交換法ではゼオライトの格子の負の
電荷を有するイオン交換点に導入されているNa+ やH+
等をPt及びRhイオンと交換する。イオン交換による担持
は例えば以下の工程によって行われる。即ち、Pt及びRh
のそれぞれのアンミンクロライドやアンミンヒドロキシ
ドなどの水溶液中にゼオライトを室温〜80℃で24〜48時
間浸漬するイオン交換工程と、これを 100〜 120℃の温
度で約10時間乾燥する乾燥工程と、 400℃〜 700℃で数
時間保持する焼成工程とからなる。なお、イオン交換時
のpHは8〜12が良い。
The loading of Pt and Rh on the zeolite can be carried out by ion exchange or impregnation. A method commonly used for both the ion exchange method and the impregnation method can be used. For example, in the ion-exchange method, Na + or H + introduced at the ion-exchange point having a negative charge on the zeolite lattice is used.
Are exchanged for Pt and Rh ions. Loading by ion exchange is performed, for example, by the following steps. That is, Pt and Rh
An ion exchange step of immersing the zeolite in an aqueous solution of each ammine chloride or ammine hydroxide at room temperature to 80 ° C for 24 to 48 hours, and a drying step of drying this at a temperature of 100 to 120 ° C for about 10 hours, And a baking step of holding at 400 ° C. to 700 ° C. for several hours. The pH at the time of ion exchange is preferably 8 to 12.

【0010】本発明に従ったPt/Rh担持ゼオライト触媒
はそのままで粒状、ペレット状、ハニカム状などの任意
の形状に成形して使用することができ、またコージェラ
イト、アルミナ、シリカ・アルミナ、スポジュメンなど
の任意の多孔質担体に担持して使用することもできる。
The Pt / Rh-supported zeolite catalyst according to the present invention can be used as it is in the form of granules, pellets, honeycombs, etc., and can be used as cordierite, alumina, silica-alumina, spodumene. It can also be used by supporting it on an arbitrary porous carrier.

【0011】本発明に係る排気ガス浄化用触媒は、通常
の方法によって浄化することができる。例えば反応器内
に前記触媒を配置し、その反応器内に排気ガスを導入し
て触媒と排気ガスを接触させて窒素酸化物を還元浄化
し、その後浄化された排気ガスを反応器より排出させる
ことにより実施することができる。浄化時の触媒層の反
応温度は例えば 200〜 800℃、好ましくは 250〜 550℃
において好適に実施することができる。また本発明に係
る浄化方法において、排気ガスを触媒層に導入する際空
間速度(SV)には特に制限はないが、例えば1万〜40万
/時間の範囲が望ましい。
The exhaust gas purifying catalyst according to the present invention can be purified by a usual method. For example, the catalyst is disposed in a reactor, exhaust gas is introduced into the reactor, the catalyst is contacted with the exhaust gas to reduce and purify nitrogen oxides, and then the purified exhaust gas is discharged from the reactor. Can be carried out. The reaction temperature of the catalyst layer during purification is, for example, 200 to 800 ° C, preferably 250 to 550 ° C.
Can be suitably implemented. In addition, in the purification method according to the present invention, the space velocity (SV) when introducing exhaust gas into the catalyst layer is not particularly limited, but is preferably in a range of, for example, 10,000 to 400,000 / hour.

【0012】[0012]

【作用】本発明に従って、Pt担持ゼオライト触媒にPt 1
00重量部に対しRhを 1.5〜 4.5重量部担持させることに
より、酸素過剰雰囲気下で耐久性に優れかつ 300℃〜 5
00℃という実用域で浄化活性の高い触媒が開発され、前
述の従来技術の問題点が解決される。
According to the present invention, Pt 1 supported on a Pt-supported zeolite catalyst.
By supporting 1.5 to 4.5 parts by weight of Rh with respect to 00 parts by weight, excellent durability and 300 ° C to 5
A catalyst having a high purification activity in the practical range of 00 ° C. has been developed, and the above-mentioned problems of the prior art are solved.

【0013】[0013]

【実施例】本発明に係る触媒を調製し、これらの触媒に
ついて、酸素過剰状態(リーン状態)のモデルガスを用
いて NOxに対する浄化活性を評価した。
EXAMPLES The catalysts according to the present invention were prepared, and the purification activity of these catalysts against NOx was evaluated using a model gas in an excess oxygen state (lean state).

【0014】例1 触媒調製 ゼオライトの一つであるNa型ZSM-5(SiO2/Al2O3 =3
9.4)(モービルオイル社製)粉末2価Ptアンミン溶液
及び3価Rhアンミン溶液を出発物質とした。前記ゼオラ
イトを2価Ptアンミン溶液及び3価Rhアンミン溶液の各
溶液中に浸漬し、24時間室温で攪拌した。その後、得ら
れた混合物を濾過し、イオン交換水で洗浄して不要なア
ニオンを除去し、 100℃で10時間乾燥後、空気中で温度
400℃で2時間焼成した。
Example 1 Catalyst Preparation One of the zeolites, Na type ZSM-5 (SiO 2 / Al 2 O 3 = 3)
9.4) (Mobile Oil Co., Ltd.) Powdered divalent Pt ammine solution and trivalent Rh ammine solution were used as starting materials. The zeolite was immersed in each of a divalent Pt ammine solution and a trivalent Rh ammine solution and stirred at room temperature for 24 hours. Then, the obtained mixture is filtered, washed with ion-exchanged water to remove unnecessary anions, dried at 100 ° C for 10 hours, and heated in air.
It was baked at 400 ° C. for 2 hours.

【0015】担持量分析 上で得られた触媒排気ガス浄化用触媒を原子吸光分析に
より分析した。結果は表1に示す。表1の担持量は触媒
100重量部に対する貴金属(Pt,Rh)の担持量である。
The catalyst for purifying the catalyst exhaust gas obtained in the analysis of the carried amount was analyzed by atomic absorption analysis. The results are shown in Table 1. The supported amount in Table 1 is the catalyst
The amount of noble metal (Pt, Rh) carried per 100 parts by weight.

【0016】触媒活性の評価 上で得られた触媒について、空燃比(A/F)=18のモ
デルガスを用い、触媒温度 200℃〜 600℃の範囲で耐久
試験処理後の NOx浄化率を測定した。なおサンプル量は
0.5gで触媒形状はペレット状である。なお、触媒の耐
久試験処理は空燃比(A/F)=18相当のモデルガス
(水蒸気10%を含む)雰囲気下に触媒を温度 600℃で5
時間曝して行った。
[0016] The catalyst obtained in the evaluation of the catalytic activity, using the air-fuel ratio (A / F) = 18 model gases, measuring the NOx purification ratio after the durability test treatment in the range of the catalyst temperature 200 ° C. ~ 600 ° C. did. The sample size is
At 0.5 g, the catalyst is in the form of a pellet. The durability test of the catalyst was carried out at a temperature of 600 ° C. in a model gas (including 10% water vapor) atmosphere having an air-fuel ratio (A / F) = 18.
Exposure was carried out.

【0017】実験結果 担持量と耐久試験後の NOx浄化率の関係を表1及び図1
〜3に示す。
Experimental Results The relationship between the carried amount and the NOx purification rate after the durability test is shown in Table 1 and FIG.
3 are shown.

【0018】[0018]

【表1】 [Table 1]

【0019】表1及び図1〜3の結果から明らかなよう
に、Pt・Rh/ゼオライトではPt/ゼオライト系触媒に比
べて、高い NOx浄化活性を示す温度域が、より高温側ま
で広がる傾向にあるが、Rhを更に加えていくと、逆に低
温側での触媒浄化活性が低下する。従ってPt担持ゼオラ
イト触媒にRhをRh/Pt= 1.8〜 4.2%(重量)となるよ
うに添加することによって高 NOx浄化活性を示す温度域
を著しく拡げることができた。
As is clear from the results shown in Table 1 and FIGS. 1 to 3, the temperature range showing high NOx purification activity in Pt.Rh / zeolite tends to spread to higher temperatures as compared with the Pt / zeolite catalyst. However, when Rh is further added, the catalyst purification activity on the low-temperature side decreases. Therefore, by adding Rh to the Pt-supported zeolite catalyst so that Rh / Pt becomes 1.8 to 4.2% (by weight), the temperature range showing high NOx purification activity could be remarkably expanded.

【0020】[0020]

【発明の効果】以上説明した通り、本発明に従えば、Pt
/Rh担持ゼオライト触媒において、Rhを担持Pt 100重量
部に対し 1.5〜 4.5重量部担持させることによって 600
℃×5時間の耐久試験処理後の浄化能にも優れかつ広い
温度域において良好な浄化活性を示す排気ガス浄化用触
媒が得られる。
As described above, according to the present invention, Pt
/ Rh is supported on a zeolite catalyst with 1.5 to 4.5 parts by weight of Rh per 100 parts by weight of supported Pt.
It is possible to obtain an exhaust gas purifying catalyst having excellent purifying ability after a durability test treatment at 5 ° C. × 5 hours and exhibiting good purifying activity in a wide temperature range.

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

【図1】300 ℃におけるRh/Pt(%)と NOx浄化率
(%)との関係を示すグラフ図である。
FIG. 1 is a graph showing a relationship between Rh / Pt (%) at 300 ° C. and a NOx purification rate (%).

【図2】400 ℃におけるRh/Pt(%)と NOx浄化率
(%)との関係を示すグラフ図である。
FIG. 2 is a graph showing a relationship between Rh / Pt (%) at 400 ° C. and a NOx purification rate (%).

【図3】500 ℃におけるRh/Pt(%)と NOx浄化率
(%)との関係を示すグラフ図である。
FIG. 3 is a graph showing the relationship between Rh / Pt (%) and NOx purification rate (%) at 500 ° C.

───────────────────────────────────────────────────── フロントページの続き (58)調査した分野(Int.Cl.6,DB名) B01J 21/00 - 38/74 B01D 53/86 - 53/88 ──────────────────────────────────────────────────続 き Continued on the front page (58) Field surveyed (Int.Cl. 6 , DB name) B01J 21/00-38/74 B01D 53/86-53/88

Claims (1)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 Pt及びRhをゼオライトに担持させて成る
排気ガス浄化用触媒において、担持Pt 100重量部に対す
るRhの担持量が1.5〜 4.5重量部であることを特徴とす
る排気ガス浄化用触媒。
1. An exhaust gas purifying catalyst comprising Pt and Rh supported on a zeolite, wherein the amount of Rh supported is 1.5 to 4.5 parts by weight based on 100 parts by weight of supported Pt. .
JP3005581A 1991-01-22 1991-01-22 Exhaust gas purification catalyst Expired - Fee Related JP2921130B2 (en)

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JP3498357B2 (en) * 1993-05-28 2004-02-16 マツダ株式会社 Method for producing exhaust gas purifying catalyst
JP3517973B2 (en) * 1993-09-30 2004-04-12 マツダ株式会社 Exhaust gas purifying catalyst, method for producing the exhaust gas purifying catalyst, and method for producing the exhaust gas purifying honeycomb catalyst

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