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JPH0464735B2 - - Google Patents
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JPH0464735B2 - - Google Patents

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Publication number
JPH0464735B2
JPH0464735B2 JP59036255A JP3625584A JPH0464735B2 JP H0464735 B2 JPH0464735 B2 JP H0464735B2 JP 59036255 A JP59036255 A JP 59036255A JP 3625584 A JP3625584 A JP 3625584A JP H0464735 B2 JPH0464735 B2 JP H0464735B2
Authority
JP
Japan
Prior art keywords
catalyst
supported
foam
group
exhaust gas
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 - Lifetime
Application number
JP59036255A
Other languages
Japanese (ja)
Other versions
JPS60183037A (en
Inventor
Kenji Ueda
Yasuo Ikeda
Koichi Saito
Kyoshi Yonehara
Tetsutsugu Ono
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.)
Nippon Shokubai Co Ltd
Original Assignee
Nippon Shokubai 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 Nippon Shokubai Co Ltd filed Critical Nippon Shokubai Co Ltd
Priority to JP59036255A priority Critical patent/JPS60183037A/en
Publication of JPS60183037A publication Critical patent/JPS60183037A/en
Publication of JPH0464735B2 publication Critical patent/JPH0464735B2/ja
Granted legal-status Critical Current

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  • Exhaust Gas Treatment By Means Of Catalyst (AREA)

Description

【発明の詳細な説明】[Detailed description of the invention]

本発明はデーイゼルエンジンからの排ガス浄化
用触媒およびその製法に関する。詳しく述べると
本発明はデイーゼルエンジン排ガス中に存在する
炭素系微粒子を燃焼せしめて除去する性能にすぐ
れたデイーゼルエンジン排ガス浄化用触媒および
その製法に関するものである。 近年デイーゼルエンジン排気ガス中の微粒子状
物質(主として固体状炭素微粒子、硫酸塩など硫
黄微粒子、そして、液状ないし固体上の高分子量
炭化水素微粒子などよりなる)が環境衛生上問題
化する傾向にある。これら微粒子はその粒子径が
ほとんど1ミクロン以下であり、大気中に浮遊し
やすく呼吸により人体内に取り込まれやすいため
である。したがつてこれら微粒子のデイーゼルエ
ンジンからの排出規制を厳しくしていく方向で検
討が進められている。 ところで、これらの微粒子の除去方法として
は、大別して以下の2つの方法がある。1つは耐
熱性ガスフイルター(セラミツクフオーム、ワイ
ヤーメツシユ、金属発泡体、目封じタイプのセラ
ミツクハニカムなど)を用いて排ガスを過して
微粒子を補捉し、圧損が上昇すればバーナーなど
で蓄積した微粒子を燃焼せしめて、フイルターを
再生する方法と、他はこの耐熱性ガスフイルター
構造を持つ担体に触媒物質を担持させ過操作と
ともに、燃焼操作も行なわせて、上記燃焼再生の
頻度を少なくするとか、再生の必要のないほどに
触媒の燃焼活性を高める方法である。 前者の場合、微粒子の除去効果を高めれば高め
るほど圧損上昇が早く再生頻度も多くなり、煩瑣
であり経済的にも著しく不利となるであろう。そ
れにくらべて後者の方法は、デイーゼルエンジン
排気ガスの排出条件(ガス組成および温度)にお
いて触媒活性を維持しうる触媒物質が採用される
ならばはるかに優れた方法と考えられる。 しかしながらデイーゼルエンジンの排気ガス温
度はガソリンエンジンの場合と比較して格段に低
く、しかも燃料として軽油を用いるために該排ガ
ス中にはSO2量も多い。したがつてサルフエート
(SO2がさらに酸化されてSO3や硫酸ミストとな
つたもの)生成能がほとんどなく、かつ通常のエ
ンジンの走行条件下でえられる温度内で蓄積した
微粒子も良好に着火燃焼させる性能の触媒が要求
されるにもかかわらず、今迄この条件に十分に適
合する触媒は提案されていないのが現状である。 本発明はこの要求を満足せしめる触媒を提供す
ることを目的とする。具体的には通常の市中走行
時にえられるデイーゼルエンジン排気ガス温度範
囲で微粒子の燃料挙動が良く圧損上昇がゆるやか
でかつ所定の排ガス温度に達したり、すみやかに
燃焼再生が起るデイーゼルエンジン排ガス浄化用
触媒を提供することを目的とする。 すなわち、本発明は以下の如く特定される。 (1) ガスフイルター機能を有する耐火性3次元構
造体上に担持せしめられた多孔性無機質基般上
に、あるいはペレツト状に成型せしめられてな
る多孔性無機質基盤上に、(a)モリブデン酸バリ
ウムおよびモリブデン酸ランタンよりなる群か
ら選ばれた少なくとも1種と(b)白金、ロジウム
およびパラジウムよりなる群から選ばれた少な
くとも1種の金属の化合物とを分散担持せしめ
てなることを特徴とするデイーゼルエンジン排
ガス浄化用触媒。 (2) (a)および(b)群から選ばれた化合物が、モル比
で(a)/(b)=5〜90の範囲である上記1記載の触
媒。 (3) 耐火性3次元構造体がセラミツクフオーム、
ワイヤメツシユ、金属発泡体または目封じ型の
セラミツクハニカムである上記1または2記載
の触媒。 (4) ガスフイルター機能を有する耐火性3次元構
造体上に担持せしめられた多孔性無機質基般上
に、あるいはペレツト状に成型せしめられてな
る多孔性無機質基盤上に、(a)モリブデン酸バリ
ウムおよびモリブデン酸ランタンよりなる群か
ら選ばれた少なくとも1種と(b)白金、ロジウム
およびパラジウムよりなる群から選ばれた少な
くとも1種の金属の化合物とを分散担持せし
め、これを空気中700〜1000℃の範囲の温度で
熱処理することを特徴とするデイーゼルエンジ
ン排ガス浄化用触媒の製法。 本発明者らはデーイゼルエンジンからの排ガス
温度が格段に低く、市中走行時排ガス温度はマン
ホールド出口でも450℃に達しないことから350℃
以下でも炭素系微粒子の燃焼挙動が良く、圧平衝
温度(微粒子の蓄積による圧力上昇と微粒子の燃
焼による圧力降下とが等しくなる温度)が330〜
350℃と低く、蓄積微粒子が400℃以下で燃焼開始
して圧損が急激に下がる触媒でかつサルフエート
の生成が450℃でもほぼ認められない特性を有す
る触媒系を見出した。 通常、卑金属だけを用いた触媒では微粒子の燃
焼挙動は、所定の温度に達するまでは、圧損上昇
が早く、通常の走行条件下で該再生温度に達しな
い場合は、外部からの強制再生を頻度高く行なう
必要があり実用性に欠けている。一方貴金属の添
加した触媒の場合、一酸化炭素(CO)、炭化水素
類(HC)の酸化性能を具備しているが同時に
SO2の酸化も起り、サルフエートが生成し好まし
くない。しかし、低温領域でも微粒子の燃え易い
成分が一部燃えるため圧損上昇はゆるやかであ
り、圧平衝温度も卑金属だけを用いた場合よりも
低い。 本発明は上記の欠点を補い、かつ各触媒成分の
持つ利点を損なうことのない触媒組成物を提供す
るものである。 また、通常モリブデンは飛散性が高く、活性劣
化が起りやすいとされているが、本発明者らは上
記(a)成分がモリブデンの飛散を抑制しかつ微粒子
状物質の燃焼挙動が良好でしか貴金属を有するサ
ルフエート生成能を著しく抑制する効果のあるこ
とを見い出し、本発明を完成したものである。 本発明者らの知見によると無機質基盤上に分散
担持せしめられた上記触媒成分において(a)群のモ
リブデン酸バリウムあるいはモリブデン酸ランタ
ンは(b)群の貴金属に対し極めて密接に作用し、元
来貴金属が具備するサルフエート生成能を有効に
抑える効果を発揮する。とくに最終焼成が700〜
1000℃という高温で行なわれてなる触媒において
効果が十分に発揮される。 しかもその共存する割合が(a)/(b)のモル比で5
〜90の範囲、好ましくは8〜60の範囲のとき、し
かも(a)群のモリブデン酸バリウムまたはモリブデ
ン酸ランタンと担持量が8〜120g/−担体、
好ましくは10〜100g/−担体であり、(b)群の
貴金属の担持量が0.1〜4.0g/−担体、好まし
くは0.3〜3.0g/−担体の範囲のときサルフエ
ート生成能が最も抑制され、しかも微粒子状物質
の燃焼挙動が良好であることが知見されたのであ
る。 本発明においては上記のモリブデン酸塩が特定
されるものであるが、他のモリブデン酸金属塩、
たとえばモリブデン酸カリウム、モリブデン酸リ
チウム、モリブデン酸バナジウム等はモリブデン
の飛散性が高く好ましくないことが認められ、ま
たモリブデン酸ストロンチウム、モリブデン酸コ
バルト等についても微粒子物質の燃焼挙動が良く
ないことが認められた。 本発明が使用する無機質基盤とは通常担体基盤
として用いられるアルミナ、シリカ、チタニア、
ジルコニア、シリカ−アルミナ、アルミナ−ジル
コニア、アルミナ−チタニア、シリカ−チタニ
ア、シリカ−ジルコニア、チタニア−ジルコニア
等が好適に用いられるが、これらに限定されるも
のではない。 本発明にかかる触媒の調製法を具体的に示すと
以下の如くである。1例として、上記無機質基盤
をガスフイルター構造を有する3次元構造体(た
とえば、セラミツクフオーム、ワイヤーメツシ
ユ、金属発泡体、目封じタイプのセラミツクハニ
カム)にスラリー化してウオツシユコートして担
持層を形成せしめ、白金、ロジウム、パラジウム
よりなり群から選ばれた少なくとも1種の金属を
含む化合物を、水溶性ないし有機溶媒(アルコー
ルなど)性の溶液または分散液の形で含浸または
浸漬法により担持させ乾燥あるいは乾燥後300〜
500℃で焼成する。次いでモリブデンの水溶性な
いし有機溶媒可溶性塩を含浸担持させ乾燥後、
300〜500℃で焼成する。この焼成物にバリウムの
水溶性ないし有機溶媒可溶性塩またはランタンの
水溶性ないし有機溶媒可溶性を含浸担持させ乾燥
後、700〜1000℃で1〜5時間焼成する。 上記化合物は酸化物、水酸化物、硝酸塩、炭酸
塩、リン酸塩、硫酸塩、ハロゲン化物、金属酸塩
などの無機化合物ないし酢酸塩、ギ酸塩などのカ
ルボン酸塩や錯化合物などの有機化合物のなかか
ら適宜選択されるが水やアルコール性有機溶媒に
溶解しやすいものの使用が好ましい。 また、該触媒成分の担持順序を変えても差しつ
かえない。 さらに、あらかじめ無機質基盤形成物と各触媒
成分群とを混合処理し、これをウオツシユコート
し乾燥し、焼成して完成触媒とする方法も採用で
き、これらの折衷方法も適宜採用される。 触媒形態としては、上記三次元構造体に限定さ
れることなく、無機質基盤として示したもののペ
レツト状のものに該触媒成分の担持しても良い。 以下実施例および比較列を示した本発明をさら
に詳しく説明する。 実施例 1 市販のコージエライト発泡体(嵩密度0.35g/
cm3、空孔率87.5%、容積1.7)にアルミナ粉末
1Kgを湿式ミルを用いてスラリー化して担持し、
余分なスラリーを振り切つて150℃で3時間乾燥
後、500℃で2時間焼成してアムミナコート層を
有するコージエライト発泡体をえた。 次に白金(Pt)として12.86gを含有するジニ
トロジアンミン白金の硝酸溶液とロジウム(Rh)
として1.286gを含有する硝酸ロジウム水溶液の
混合溶液2に、該発泡体を浸漬し、余分な溶液
を振り切つて150℃で3時間乾燥後500℃で2時間
焼成し、白金−ロジウムを含有するアルミナコー
ト層を有するコージエライト発泡体をえた。 次にパラモリブデン酸アンモニウム350.6gを
含有する水溶液2に該発泡体を浸漬し、余分な
水溶液を振り切つて150℃で3時間乾燥後500℃で
2時間焼成して、モリブデン(Mo)−Pt−Rhを
含有するアルミナコート層を有するコージエライ
ト発泡体をえた。 次いで、酢酸バリウム507.2gを含む水溶液2
は該発泡体を浸漬し、余分な水溶液を振り切つ
て150℃3時間乾燥後、750℃2時間焼成してモリ
ブデン酸バリウム(BaMoO4)を形成せしめ、
BaMoO4、Pt、Rhを含有するアルミナコート層
を有するコージエライト発泡体をえた。 この時のPt、Rhの担持量をそれぞれ0.90g/
−担体、0.09g/−担体であり、BaMoO4
担持量は41.3g/−担体であつた。 出来上りのコート層の組成はアルミナ62.3重量
%、BaMoO436.8重量%、Pt+Rh(Pt/Rt=10/
1)0.89重量%であつた。 実施例 2 パラモリブデン酸アンモニウム353gを2の
イオン交換水に溶解させ、あらかじめ塩化バリウ
ム41.65gを2のイオン交換水に溶解させた水
溶液中にかくはんしながら投入して、生成した沈
殿を過洗浄し150℃で5時間乾燥し、500℃で2
時間焼成して約530gのBaMoO4の粉末をえた。 この粉末472gとアルミナ粉末800gをボールミ
ルで十分混合し、次いで湿式ミルでスラリー化し
てコージエライト発泡体1.7に担持し、余分な
スラリーの振り切つて150℃3時間乾燥後500℃2
時間焼成して、BaMoO4を含有するアルミナコ
ート層を有するコージエライト発泡体をえた。次
いで実施例1に順じた方法で、Pt、Rhを担持し
150℃2時間乾燥後750℃で2時間焼成した。 この時の出来上りのコート層の組成は実施例1
とほぼ同組成であつた。 実施例 3 実施例1において、酢酸バリウムの替りに硝酸
ランタムLa(NO33・6H2Oの水溶液を用いる以
外は全て同じ方法で触媒を調製しAl2O370g/
−担体、モリブデン酸ランタン〔La2(MoO43
35.1g/−担体、PtおよびRhの担持量はそれ
ぞれ0.90g/−担体、0.09g/−担体であつ
た。 出来上りのコート層の組成はAl2O366.0重量%、
La2(MoO4333.1重量%、Pt+Rh(Pt/Rh=10/
1)0.94重量%であつた。 実施例 4 実施例2において、Ptを用いる替りにPdを用
いる以外は全て同じ方法で触媒を調製した。出来
上りコート層の組成は、Al2O362.3重量%、
BaMoO436.8重量%、Pd+Rh(Pd/Rh=10/1)
0.89重量%であつた。 実施例 5 実施例1においてコージエライト発泡体をハニ
カム構造体で両端面の隣接する各孔を互いに違い
に閉塞させ隔璧からのみガスを通過させるように
した目封じタイプのハニカムに替える以外は全く
同様の方法で、触媒を調製した。 実施例 6 市販のアルミナペレツト(3〜6mmφ)1.7
に実施例1の出来上りのコート層の組成になるよ
うにPt、Rt、BaMoO4を担持して触媒を調製し
た。 比較例 1 実施例1においてPt、Rhを用いない以外は全
て同じ方法で触媒を調製し、Al2O370g/−担
体、BaMoO441.3g/−担体それぞれ担持した
コージエライト発泡体触媒をえた。 比較例 2 実施例1において、酢酸バリウムを用いない以
外は全て同じ方法で触媒を調製し、Al2O370g/
−担体、MoO320g/−担体、Pt0.90g/
−担体、Rh0.09g/−担体それぞれ担持した
コージエライト発泡体をえた。 比較例 3 実施例1において、酢酸バリウムの替りに硝酸
カリウムを用いる以外は全て同じ方法で触媒を調
製し、Al2O370g/−担体、K2MoO433.1g/
−担体、Pt0.90g/−担体、Rh0.09g/−
担体それぞれ担持したコージエライト発泡体をえ
た。 比較例 4 実施例1において、パラモリブデン酸アンモニ
ウムの替りにモリブデン酸カリウムを用いた酢酸
バリウムを用いない以外は全て同じ方法で触媒を
調製し比較例3と同じ組成の触媒をえた。 比較例 5 実施例1において最終の焼成温度を600℃に替
える以外は全て同じ方法で触媒を調製した。 実施例 7 実施例1〜6、比較例1〜5でえられた触媒に
ついて、排気量2300c.c.、4気筒デイーゼルエンジ
ンを用いて触媒の評価試験を行なつた。エンジン
回転数2500rpm、トルク4.0Kg・mの条件で微粒
子の捕捉約2時間を行ない、次いで、トルクを
0.5Kg・m間隔で5分毎に上昇させて、触媒層の
圧損変化連続的に記録し、微粒子が触媒上で排ガ
ス温度上昇に伴ない、微粒子の蓄積による圧力上
昇と微粒子の燃焼による圧力降下とが等しくなる
温度(Te)と着火燃焼し、圧損が急激に下降す
る温度(Ti)を求めた。また2500rpm、トルク
4.0Kg・mで微粒子を捕捉する場合の圧損の経時
変化を1時間あたりの圧損変化量をチヤートから
計算して△P(mmHg/H)の値を求めた。 又、SO2のSO3への転化率を排ガス温度450℃
で求めた。SO2の転化率は入口ガス、出口ガスの
SO2濃度を非分散型赤外分析計(NDIR法)で分
析し、次の算出式よりSO2の転化率(%)を求め
た。 SO2転化率(%)=入口SO2濃度(ppm)−出口SO2濃度(
ppm)/入口SO2濃度(ppm)×100 結果を次の表−1に示す。 次に各触媒について2500rpm、トルク14Kg・m
の条件で排ガス温度620℃で20時間曝露(エージ
ング)したものについて上記テストと同様にSO2
転化率およびTe、Tiを求めかつテスト済みの触
媒のMo残存率を蛍光X線分析で求めた。結果を
表−2に示す。
The present invention relates to a catalyst for purifying exhaust gas from a diesel engine and a method for producing the same. Specifically, the present invention relates to a catalyst for purifying diesel engine exhaust gas that has excellent performance in burning and removing carbon-based particulates present in diesel engine exhaust gas, and a method for producing the catalyst. In recent years, particulate matter (mainly composed of solid carbon particles, sulfur particles such as sulfates, and liquid or solid high molecular weight hydrocarbon particles) in diesel engine exhaust gas has become a problem in terms of environmental health. This is because most of these fine particles have particle diameters of 1 micron or less and are easily suspended in the atmosphere and easily taken into the human body through breathing. Therefore, studies are underway to tighten regulations on the emission of these particulates from diesel engines. By the way, methods for removing these fine particles can be broadly classified into the following two methods. One is to use a heat-resistant gas filter (ceramic foam, wire mesh, metal foam, sealed ceramic honeycomb, etc.) to pass through the exhaust gas and capture fine particles, and if the pressure drop increases, they will accumulate in a burner, etc. There is a method of regenerating the filter by burning the fine particles, and another method is to carry a catalyst substance on a carrier having this heat-resistant gas filter structure and perform a combustion operation as well as an over-operation to reduce the frequency of the above-mentioned combustion regeneration. This is a method of increasing the combustion activity of the catalyst to such an extent that regeneration is not necessary. In the former case, the higher the particle removal effect, the faster the pressure drop will rise and the more frequently the regeneration will occur, which will be cumbersome and economically disadvantageous. In comparison, the latter method is considered to be a much better method if a catalytic material that can maintain catalytic activity under the exhaust conditions (gas composition and temperature) of diesel engine exhaust gas is employed. However, the exhaust gas temperature of a diesel engine is much lower than that of a gasoline engine, and since light oil is used as fuel, the amount of SO 2 in the exhaust gas is also large. Therefore, it has almost no ability to generate sulfate (SO 2 is further oxidized to SO 3 or sulfuric acid mist), and even the accumulated particulates can be ignited and combusted well within the temperature obtained under normal engine running conditions. Although there is a demand for a catalyst with performance that satisfies this requirement, the current situation is that no catalyst has been proposed that satisfactorily meets this requirement. The object of the present invention is to provide a catalyst that satisfies this requirement. Specifically, we aim to purify diesel engine exhaust gas in a diesel engine exhaust gas temperature range that occurs during normal city driving, in which the fuel behavior of fine particles is good, the pressure drop rises slowly, the specified exhaust gas temperature is reached, and combustion regeneration occurs quickly. The purpose is to provide a catalyst for That is, the present invention is specified as follows. (1) On a porous inorganic substrate supported on a refractory three-dimensional structure having a gas filter function, or on a porous inorganic substrate formed into a pellet, (a) barium molybdate and (b) a compound of at least one metal selected from the group consisting of platinum, rhodium and palladium. Catalyst for engine exhaust gas purification. (2) The catalyst according to the above item 1, wherein the compound selected from groups (a) and (b) has a molar ratio of (a)/(b) = 5 to 90. (3) The fire-resistant three-dimensional structure is ceramic foam,
3. The catalyst according to 1 or 2 above, which is a wire mesh, a metal foam, or a plugged ceramic honeycomb. (4) (a) barium molybdate on a porous inorganic base supported on a refractory three-dimensional structure having a gas filter function, or on a porous inorganic base formed into a pellet shape; and (b) at least one metal compound selected from the group consisting of platinum, rhodium, and palladium, and (b) a compound of at least one metal selected from the group consisting of platinum, rhodium, and palladium. A method for producing a catalyst for purifying diesel engine exhaust gas, which is characterized by heat treatment at a temperature in the range of °C. The present inventors found that the exhaust gas temperature from a diesel engine is extremely low, and the exhaust gas temperature during city driving does not reach 450℃ even at the manhold exit, so it is 350℃.
The combustion behavior of carbon-based fine particles is good even below, and the applanation temperature (the temperature at which the pressure increase due to accumulation of fine particles is equal to the pressure drop due to combustion of fine particles) is 330~
We have found a catalyst system that has characteristics such that the temperature is as low as 350℃, the combustion of accumulated particulates starts below 400℃, and the pressure drop decreases rapidly, and the formation of sulfate is hardly observed even at 450℃. Normally, with catalysts that use only base metals, the combustion behavior of fine particles is such that the pressure drop increases quickly until a predetermined temperature is reached, and if the regeneration temperature is not reached under normal running conditions, external forced regeneration is required frequently. It needs to be done expensively and lacks practicality. On the other hand, catalysts containing precious metals have the ability to oxidize carbon monoxide (CO) and hydrocarbons (HC), but at the same time
Oxidation of SO 2 also occurs, producing sulfate, which is undesirable. However, even in the low temperature range, the combustible components of the fine particles are partially combusted, so the increase in pressure drop is gradual, and the applanation temperature is also lower than when only base metals are used. The present invention provides a catalyst composition that compensates for the above-mentioned drawbacks and does not impair the advantages of each catalyst component. Furthermore, although it is generally believed that molybdenum has high scattering properties and is prone to activity deterioration, the present inventors believe that component (a) can suppress the scattering of molybdenum and have good combustion behavior for fine particulate matter. The present invention has been completed based on the discovery that the sulfate-producing ability of the sulfate-generating ability of the sulfate-producing compound is significantly suppressed. According to the findings of the present inventors, in the above catalyst component dispersedly supported on an inorganic substrate, barium molybdate or lanthanum molybdate of group (a) acts extremely closely on the noble metal of group (b), and It exhibits the effect of effectively suppressing the sulfate generation ability of precious metals. Especially the final firing is 700~
The effect is fully demonstrated in catalysts that are processed at a high temperature of 1000°C. Moreover, the ratio of their coexistence is 5 in the molar ratio of (a)/(b).
90, preferably 8 to 60, and the supported amount of barium molybdate or lanthanum molybdate of group (a) is 8 to 120 g/- carrier,
Preferably it is 10 to 100 g/-carrier, and when the amount of noble metal of group (b) supported is in the range of 0.1-4.0 g/-carrier, preferably 0.3-3.0 g/-carrier, the sulfate-forming ability is most suppressed, Moreover, it was discovered that the combustion behavior of particulate matter is good. In the present invention, the above-mentioned molybdate is specified, but other molybdate metal salts,
For example, it has been recognized that potassium molybdate, lithium molybdate, vanadium molybdate, etc. are undesirable due to the high scattering of molybdenum, and it has also been recognized that strontium molybdate, cobalt molybdate, etc. have poor combustion behavior of particulate matter. Ta. The inorganic bases used in the present invention include alumina, silica, titania, which are usually used as carrier bases,
Zirconia, silica-alumina, alumina-zirconia, alumina-titania, silica-titania, silica-zirconia, titania-zirconia and the like are preferably used, but are not limited thereto. The specific method for preparing the catalyst according to the present invention is as follows. As an example, the above-mentioned inorganic substrate is slurried into a three-dimensional structure having a gas filter structure (for example, ceramic foam, wire mesh, metal foam, sealed type ceramic honeycomb) and coated with wash to form a support layer. A compound containing at least one metal selected from the group consisting of platinum, rhodium, and palladium is supported in the form of a water-soluble or organic solvent (alcohol etc.) solution or dispersion by an impregnation or dipping method. Dry or after drying 300~
Fire at 500℃. Next, a water-soluble or organic solvent-soluble salt of molybdenum is impregnated and supported, and after drying,
Bake at 300-500℃. The fired product is impregnated with a water-soluble or organic solvent-soluble salt of barium or a water-soluble or organic solvent-soluble salt of lanthanum, dried, and then fired at 700 to 1000°C for 1 to 5 hours. The above compounds include inorganic compounds such as oxides, hydroxides, nitrates, carbonates, phosphates, sulfates, halides, and metal salts, and organic compounds such as carboxylates and complex compounds such as acetates and formates. It is preferable to use one that is easily soluble in water or an alcoholic organic solvent. Furthermore, the order in which the catalyst components are supported may be changed. Furthermore, it is also possible to adopt a method in which the inorganic base material and each catalyst component group are mixed in advance, and then washed, dried, and calcined to obtain a finished catalyst, and a compromise between these methods can also be adopted as appropriate. The form of the catalyst is not limited to the three-dimensional structure described above, but the catalyst component may be supported on a pellet-like structure shown as an inorganic base. The present invention will be described in more detail below with examples and comparative columns. Example 1 Commercially available cordierite foam (bulk density 0.35 g/
cm 3 , porosity 87.5%, volume 1.7), 1 kg of alumina powder is slurried and supported using a wet mill,
After shaking off the excess slurry and drying at 150°C for 3 hours, the product was fired at 500°C for 2 hours to obtain a cordierite foam having an ammina coat layer. Next, a nitric acid solution of dinitrodiammine platinum containing 12.86 g as platinum (Pt) and rhodium (Rh)
The foam was immersed in mixed solution 2 of an aqueous rhodium nitrate solution containing 1.286 g of rhodium, the excess solution was shaken off, and the foam was dried at 150°C for 3 hours and then fired at 500°C for 2 hours to form a foam containing platinum-rhodium. A cordierite foam with an alumina coat layer was obtained. Next, the foam was immersed in aqueous solution 2 containing 350.6 g of ammonium paramolybdate, the excess aqueous solution was shaken off, and the foam was dried at 150°C for 3 hours and then fired at 500°C for 2 hours to produce molybdenum (Mo)-Pt. A cordierite foam with an alumina coat layer containing -Rh was obtained. Next, aqueous solution 2 containing 507.2 g of barium acetate
The foam was immersed, the excess aqueous solution was shaken off, the foam was dried at 150°C for 3 hours, and then fired at 750°C for 2 hours to form barium molybdate (BaMoO 4 ).
A cordierite foam with an alumina coat layer containing BaMoO 4 , Pt, and Rh was obtained. The amount of Pt and Rh supported at this time was 0.90g/0.90g/
- carrier, 0.09 g/- carrier, and the amount of BaMoO 4 supported was 41.3 g/- carrier. The composition of the finished coating layer was 62.3% by weight of alumina, 36.8% by weight of BaMoO 4 , and Pt+Rh (Pt/Rt=10/
1) It was 0.89% by weight. Example 2 353 g of ammonium paramolybdate was dissolved in the ion-exchanged water from step 2, and added while stirring into an aqueous solution in which 41.65 g of barium chloride had been previously dissolved in the ion-exchanged water from step 2, and the precipitate formed was overwashed. Dry at 150℃ for 5 hours, then dry at 500℃ for 2 hours.
About 530g of BaMoO 4 powder was obtained by firing for a time. 472g of this powder and 800g of alumina powder were thoroughly mixed in a ball mill, then slurried in a wet mill, supported on cordierite foam 1.7, excess slurry was shaken off, dried at 150℃ for 3 hours, and then dried at 500℃ for 3 hours.
After firing for a period of time, a cordierite foam with an alumina coat layer containing BaMoO 4 was obtained. Next, Pt and Rh were supported by a method according to Example 1.
After drying at 150°C for 2 hours, it was fired at 750°C for 2 hours. The composition of the finished coat layer at this time is Example 1
The composition was almost the same. Example 3 A catalyst was prepared in the same manner as in Example 1 except that an aqueous solution of lantum nitrate La(NO 3 ) 3.6H 2 O was used instead of barium acetate .
-Support, lanthanum molybdate [La 2 (MoO 4 ) 3 ]
The supported amounts of Pt and Rh were 35.1 g/-carrier and 0.90 g/-carrier and 0.09 g/-carrier, respectively. The composition of the finished coating layer is Al 2 O 3 66.0% by weight,
La 2 (MoO 4 ) 3 33.1% by weight, Pt + Rh (Pt/Rh=10/
1) It was 0.94% by weight. Example 4 A catalyst was prepared in the same manner as in Example 2 except that Pd was used instead of Pt. The composition of the finished coat layer is 62.3% by weight of Al 2 O 3 ;
BaMoO 4 36.8% by weight, Pd+Rh (Pd/Rh=10/1)
It was 0.89% by weight. Example 5 Exactly the same as in Example 1 except that the cordierite foam was replaced with a sealed type honeycomb structure in which the adjacent holes on both end faces were closed differently to allow gas to pass through only through the partitions. A catalyst was prepared by the method described in . Example 6 Commercially available alumina pellets (3 to 6 mmφ) 1.7
A catalyst was prepared by supporting Pt, Rt, and BaMoO 4 so as to have the composition of the finished coat layer of Example 1. Comparative Example 1 A catalyst was prepared in the same manner as in Example 1 except that Pt and Rh were not used, and a cordierite foam catalyst was obtained in which 70 g/- of Al 2 O 3 and 41.3 g/- of BaMoO 4 were supported. Comparative Example 2 A catalyst was prepared in the same manner as in Example 1 except that barium acetate was not used, and 70 g of Al 2 O 3 /
-Support, MoO 3 20g/-Support, Pt0.90g/
A cordierite foam was obtained in which each of the -carrier and Rh0.09g/-carrier was supported. Comparative Example 3 A catalyst was prepared in the same manner as in Example 1 except that potassium nitrate was used instead of barium acetate, and Al 2 O 3 70 g/- support and K 2 MoO 4 33.1 g/
-Support, Pt0.90g/-Support, Rh0.09g/-
Cordierite foams each supported on a carrier were obtained. Comparative Example 4 A catalyst was prepared in the same manner as in Example 1 except that potassium molybdate was used instead of ammonium paramolybdate and barium acetate was not used, and a catalyst having the same composition as Comparative Example 3 was obtained. Comparative Example 5 A catalyst was prepared in the same manner as in Example 1 except that the final calcination temperature was changed to 600°C. Example 7 The catalysts obtained in Examples 1 to 6 and Comparative Examples 1 to 5 were evaluated using a 4-cylinder diesel engine with a displacement of 2300 c.c. Particulate capture was carried out for approximately 2 hours under the conditions of engine rotation speed 2500 rpm and torque 4.0 kg・m, and then the torque was
The pressure drop in the catalyst layer was continuously recorded by increasing the pressure at 0.5 kg/m intervals every 5 minutes, and as the exhaust gas temperature rose on the catalyst, the pressure increase due to the accumulation of fine particles and the pressure drop due to combustion of the fine particles were measured. The temperature (Te) at which these are equal to the temperature (Ti) at which ignition and combustion occur and the pressure drop rapidly decreases was determined. Also 2500rpm, torque
The value of ΔP (mmHg/H) was determined by calculating the change in pressure drop per hour from a chart when capturing fine particles at 4.0 kg·m. In addition, the conversion rate of SO 2 to SO 3 was determined at an exhaust gas temperature of 450℃.
I asked for it. The conversion rate of SO 2 is determined by the inlet gas and outlet gas.
The SO 2 concentration was analyzed using a non-dispersive infrared analyzer (NDIR method), and the conversion rate (%) of SO 2 was determined using the following formula. SO 2 conversion rate (%) = Inlet SO 2 concentration (ppm) − Outlet SO 2 concentration (
ppm)/Inlet SO 2 concentration (ppm) x 100 The results are shown in Table 1 below. Next, for each catalyst, 2500 rpm, torque 14 Kg・m
Similar to the above test, SO 2
The conversion rate, Te, and Ti were determined, and the Mo residual rate of the tested catalyst was determined by fluorescent X-ray analysis. The results are shown in Table-2.

【表】【table】

【表】【table】

【表】【table】

Claims (1)

【特許請求の範囲】 1 ガスフイルター機能を有する耐火性3次元構
造体上に担持せしめられた多孔性無機質基盤上
に、あるいはペレツト状に成型せしめられてなる
多孔性無機質基盤上に、(a)モリブデン酸バリウム
およびモリブデン酸ランタンよりなる群から選ば
れた少なくとも1種と(b)白金、ロジウムおよびパ
ラジウムよりなる群から選ばれた少なくとも1種
の金属の化合物とを分散担持せしめてなることを
特徴とするデイーゼルエンジン排ガス浄化用触
媒。 2 (a)および(b)群から選ばれた化合物が、モル比
で(a)/(b)=5〜90の範囲である特許請求の範囲第
1項記載の触媒。 3 耐火性3次元構造体がセラミツクフオーム、
ワイヤメツシユ、金属発泡体または目封じ型のセ
ラミツクハニカムである特許請求の範囲第1また
は2記載の触媒。 4 ガスフイルター機能を有する耐火性3次元構
造体上に担持せしめられた多孔性無機質基般上
に、あるいはペレツト状に成型せしめられてなる
多孔性無機質基盤上に、(a)モリブデン酸バリウム
およびモリブデン酸ランタンよりなる群から選ば
れた少なくとも1種と(b)白金、ロジウムおよびパ
ラジウムよりなる群から選ばれた少なくとも1種
の金属の化合物とを分散担持せしめ、これを空気
中700〜1000℃の範囲の温度で熱処理することを
特徴とするデイーゼルエンジン排ガス浄化用触媒
の製法。
[Scope of Claims] 1. On a porous inorganic base supported on a refractory three-dimensional structure having a gas filter function, or on a porous inorganic base formed into a pellet, (a) (b) a compound of at least one metal selected from the group consisting of barium molybdate and lanthanum molybdate; and (b) at least one metal selected from the group consisting of platinum, rhodium, and palladium. A catalyst for purifying diesel engine exhaust gas. 2. The catalyst according to claim 1, wherein the compounds selected from groups (a) and (b) have a molar ratio of (a)/(b)=5 to 90. 3 The fire-resistant three-dimensional structure is ceramic foam,
The catalyst according to claim 1 or 2, which is a wire mesh, a metal foam, or a plugged ceramic honeycomb. 4. (a) Barium molybdate and molybdenum are placed on a porous inorganic base supported on a refractory three-dimensional structure having a gas filter function, or on a porous inorganic base formed into a pellet. A compound of at least one metal selected from the group consisting of lanthanum acid and (b) at least one metal selected from the group consisting of platinum, rhodium, and palladium is dispersed and supported in the air at 700 to 1000°C. A method for producing a catalyst for purifying diesel engine exhaust gas, which is characterized by heat treatment at a temperature within a range.
JP59036255A 1984-02-29 1984-02-29 Exhaust gas purifying catalyst and its preparation Granted JPS60183037A (en)

Priority Applications (1)

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JP59036255A JPS60183037A (en) 1984-02-29 1984-02-29 Exhaust gas purifying catalyst and its preparation

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Application Number Priority Date Filing Date Title
JP59036255A JPS60183037A (en) 1984-02-29 1984-02-29 Exhaust gas purifying catalyst and its preparation

Publications (2)

Publication Number Publication Date
JPS60183037A JPS60183037A (en) 1985-09-18
JPH0464735B2 true JPH0464735B2 (en) 1992-10-15

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Country Link
JP (1) JPS60183037A (en)

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2001347168A (en) * 2000-06-06 2001-12-18 Toyota Motor Corp Exhaust gas purification catalyst
CN110124640B (en) * 2019-04-19 2020-05-19 华中科技大学 Composites of Lanthanum Molybdate and Ferromagnetic Materials and Their Preparation and Application in Adsorption and Phosphorus Removal

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