JPH0575457B2 - - Google Patents

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Publication number
JPH0575457B2
JPH0575457B2 JP2154036A JP15403690A JPH0575457B2 JP H0575457 B2 JPH0575457 B2 JP H0575457B2 JP 2154036 A JP2154036 A JP 2154036A JP 15403690 A JP15403690 A JP 15403690A JP H0575457 B2 JPH0575457 B2 JP H0575457B2
Authority
JP
Japan
Prior art keywords
catalyst
supported
platinum
exhaust gas
inorganic base
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
JP2154036A
Other languages
Japanese (ja)
Other versions
JPH03114539A (en
Inventor
Yasuo Ikeda
Kenji Ueda
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 JP2154036A priority Critical patent/JPH03114539A/en
Publication of JPH03114539A publication Critical patent/JPH03114539A/en
Publication of JPH0575457B2 publication Critical patent/JPH0575457B2/ja
Granted legal-status Critical Current

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Classifications

    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F02COMBUSTION ENGINES; HOT-GAS OR COMBUSTION-PRODUCT ENGINE PLANTS
    • F02BINTERNAL-COMBUSTION PISTON ENGINES; COMBUSTION ENGINES IN GENERAL
    • F02B3/00Engines characterised by air compression and subsequent fuel addition
    • F02B3/06Engines characterised by air compression and subsequent fuel addition with compression ignition

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

Description

【発明の詳細な説明】 本発明はデイー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の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
硫黄系微粒子、そして、液状まないし固体上の高
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
子を捕捉し、圧損を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が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
微粒子を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、今までこの条件に十分に
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
囲で微粒子の燃焼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ら、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)少なくとも1種の
タングステン酸塩と、(b)白金、ロジウムおよび
パラジウムからなる白金族元素の群から選ばれ
た少なくとも1種の金属および/または酸化物
と、(c)モリブデン酸バリウムとを分散担持せし
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)=4〜120の範囲である特許請求の範囲
第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特許請求の範囲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)少なくとも1種の
タングステン酸塩と、(b)白金、ロジウムおよび
パラジウムからなる白金族元素の群から選ばれ
た少なくとも1種の金属および/または酸化物
と、(c)モリブデン酸バリウムとを分散担持せし
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。 以下本発明にかかる触媒の到達しえた効果につ
いて、さらに具体的に説明する。 本発明者らは上記によつてデイーゼルエンジン
からの排ガス温度が格段に低く、市中走行時排ガ
ス温度はマニホールド出口でも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、圧平衡温度(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600℃でも5%以下と非
常に少ないすぐれた特性を有する触媒系を見い出
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。一方白金族元素
を添加した触媒の場合、一酸化炭素(CO)、炭化
水素類(HC)の酸化性能は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中の燃え
易い成分が一部燃えるため圧損上昇はゆるやかで
あり、圧平衡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。 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
のタングステン酸塩および(c)群のモリブデン酸バ
リウムは(b)群の白金族元素に対して極めて密接に
作用し、元来該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
媒においてその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4
〜120の範囲、好ましくは6〜90の範囲のとき、
しかも(a)群のタングステン酸塩の担持量が、8〜
120g/l−担体、好ましくは10〜100g/−担
体の範囲であり、(b)群の白金属元素の担持量が
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。そしてまた(c)
群のモリブデン酸バリウムを8〜120g/−担
体、好ましくは10〜100g/−担体の範囲で組
合せることにより、さらに微粒子状物質の燃焼性
能が良くなることが知見されたのである。 本発明において、タングステン酸塩とは、リチ
ウム、ナトリウム、カリウム、セシウム、マグネ
シウム、カルシウム、ストロンチウム、バリウ
ム、ランタン、セリウム、鉄、コバルト、ニツケ
ル、銅、銀、ビスマス、錫、鉛などの金属のタン
グテン酸塩を意味する。 (a)/(b)のモル比が4より小さい範囲では、サル
フエートの生成の抑制効果が悪くなり、600℃の
デイーゼル排ガスの条件下で10%以上のSO2
SO3への転換率を示す。(a)/(b)のモル比が120よ
り大きい範囲では、低温(300℃以下)での微粒
子の燃焼性能が悪くなり、単位時間あたりの圧損
上昇が大きくなり、白金族元素の特質である低温
における「SOF(soluble organic fraction)」の
燃焼性能を妨害して好ましくない。 また(a)および(b)成分担持後の焼成温度を700℃
以下で行なつた場合は、SO2のSO3の転換率が高
くなる傾向が見られ、1000℃以上で焼成を行なつ
た場合は、自己再生温度(微粒子の燃焼による触
媒層の圧損降下が見られる温度)が高くなり好ま
しくない。 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、シリカーアルミナ、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、パラジウム等
の白金族元素よりなる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(たとえばアルコール)性の溶液または分散液
の形で含浸または浸潰法により担持させ、乾燥あ
るいは乾燥後300〜500℃で焼成する。次いでタン
グステ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。次いで
先に述べたタングステン酸塩を形成する金属
(Li,Na,K,Cs,Mg,Ca,Sr,Ba,La,
Ce,Fe,Co,Ni,Cu,Ag,Bi,Sn,Pb)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700〜1000℃で1〜5時間焼成する。そして
さらにモリブデン酸バリウムが生成するように水
溶性化合物の形で各化合物を含浸担持させて触媒
上にこれらモリブデン酸塩を分散形成せしめた後
700〜1000℃で焼成してもよい。 上記原料化合物は、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、あらかじめタングステン酸塩を
調製し粉砕したものと、無機質基盤形成物に白金
族金属を含有せしめた粉体とを湿式ミル等を用い
て混合スラリー化してウオツシユコートし乾燥後
700〜1000℃で焼成し触媒を完成してもよい。ま
た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3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を担持しても良い。 以下実施例および比較例を示し本発明をさらに
詳しく説明する。 実施例 1 パラモリブデン酸アンモニウム353gを2の
水に溶解させ、あらかじめ塩化バリウム416.5g
を2の水に溶解させた水溶液中に攪拌しながら
投入し、生成した沈澱を過洗浄し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。 Ptとして9.0gを含有するジニトロジアミン白
金の硝酸溶液と、Rhとして0.9gを含有する硝酸
ロジウム水溶液の混合溶液800mlにアルミナ粉体
700gを投入し、よく混合し、150℃で5時間乾燥
後、500℃で2時間焼成し、Pt,Rhを含有するア
ルミナ粉体をえた。 市販のメタタングステン酸アンモニウム水溶液
〔WO3として50重量%含有溶液、日本無機化学工
業(株)製)を853g採り、これを水で1に希釈し
た。別に酢酸バリウムBa(C2H3O22を470g採り
水に溶解させ1とした。この両方の溶液を攪拌
しながら混合しタングステン酸バリウムBaWO4
の白色沈澱物をえた。該沈澱物を過洗浄し、
150℃で5時間乾燥し、500℃で2時間焼成した。 得られたBaWO4粉末472.6gおよび該BoMoO4
の粉末208.1gと、上記Pt,Rhを含有するアルミ
ナ粉体710gとをボールミルで充分混合し、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、余分なスリラーを振り切つて
から150℃で3時間乾燥後750℃で2時間焼成し
て、Pt,Rh,BaMoO4,BaWO4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。 えられた触媒のPt,Rhの担持量は、それぞれ
0.9g/−担体、0.09g/−担体であり、
BaMoO4の担持量は20.8g/−担体、BaWO4
の担持量は47.3g/−担体であつた。出来上り
のコート層の組成はAl2O350.3重量%、BaMoO4
14.9重量%、BaWO434.0重量%、Pt+Rh(Pt/
Rh=10/1)0.72重量%であつた。 比較例 1 Ptとして9.0gを含有するジニトロジアミン白
金の硝酸溶液と、Rhとして0.9gを含有する硝酸
ロジウム水溶液の混合溶液800mlにアルミナ粉体
700gを投入しよく混合し、150℃で5時間乾燥
後、500℃で2時間焼成し、Pt,Rhを含有するア
ルミナ粉体をえた。 市販のメタタングステン酸アンモニウム水溶液
〔WO3として50重量%含有溶液、日本無機化学工
業(株)製〕を853g採り、これを水で1に希釈し
た。別に酢酸バリウムBa(C2H3O22を470g採り
水に溶解させ1とした。この両方の溶液を攪拌
しながら混合しタングステン酸バリウムBaWO4
の白色沈澱物をえた。該沈澱物を過洗浄し、
150℃で5時間乾燥し、500℃で2時間焼成した。 該BaWO4の粉末472.6gと上記のPt,Rhを含
有するアルミナ粉体710gとをボールミルで充分
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を
振り切つてから150℃3時間乾燥後750℃で2時間
焼成してPt,Rh,BaWO4を含有するアルミナコ
ード層を有するコージエライト発泡体をえた。 えられた触媒はPt,Rhの担持量はそれぞれ0.9
g/−担体、0.09g/−担体であり、
BaWO4の担持量は47.3g/−担体であつた。
出来上りのコート層の組成はAl2O359.2重量%、
BaWO440重量%、Pt+Rh(Pt/Rh=10/1)
0.84重量%であつた。 比較例 2 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時間焼成してアルミナコート層を
有するコージエライト発泡体をえた。アルミナ担
持量は、70.1g/−担体であつた。 次にタングステン酸カリウム(K2WO4)571.4
gを含有する2の水溶液に該発泡体を浸漬し、
余分な水溶液を振り切つてから150℃で3時間乾
燥後、750℃で2時間焼成した。 えられた触媒のK2WO4の担持量は40g/−
担体であつた。 出来上りのコート層の組成はアルミナ63.7重量
%、K2WO436.3重量%であつた。 実施例 2 実施例1、比較例1〜2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0.5
Kg・m間隔で5分毎に上昇させて、触媒層の圧損
変化を連続的に記録し、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ΔP
(mmHg/H)の値を求めた。 また、SO2のSO3への転化率を排ガス温度600
℃で求めた。SO2の転化率は入口ガスし、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 結果を第1表に示す。 【表】
DETAILED DESCRIPTION OF THE INVENTION 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-based particles such as sulfates, and high molecular weight hydrocarbon particles in liquid or solid form) in the exhaust gas of diesel engines has become a problem in terms of environmental health. It is in. 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, the methods for removing these fine particles are as follows:
There are two main methods as follows. 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. There is a method of regenerating the filter by burning the particulates, and another method is to carry a catalyst material on a carrier with 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 is, the higher the pressure drop will be and the faster the frequency of regeneration will be, which will be troublesome 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 it can effectively ignite and burn accumulated particulates within the temperature that can be 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, diesel engine exhaust gas purification has good combustion behavior of particulates within the diesel engine exhaust gas temperature range found during normal city driving, with a gradual rise in pressure drop, and where combustion regeneration occurs promptly when a predetermined exhaust gas temperature is reached. The purpose is to provide a catalyst for That is, the present invention is specified as follows. (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) at least one kind of tungstate, (b) at least one metal and/or oxide selected from the group of platinum group elements consisting of platinum, rhodium and palladium, and (c) barium molybdate are dispersed and supported. A diesel engine exhaust gas purification catalyst featuring: (2) Compounds selected from groups (a) and (b) in molar ratio
The catalyst according to claim 1, wherein (a)/(b)=4 to 120. (3) The fire-resistant three-dimensional structure is ceramic foam,
3. The catalyst according to claim 1, which is a wire mesh, a metal foam, or a plugged ceramic honeycomb. (4) At least one of (a) A tungstate salt, (b) at least one metal and/or oxide selected from the group of platinum group elements consisting of platinum, rhodium, and palladium, and (c) barium molybdate are dispersed and supported. A method for producing a catalyst for purifying diesel engine exhaust gas, which is characterized by heat treatment in air at a temperature in the range of 700 to 1000°C. The effects achieved by the catalyst according to the present invention will be explained in more detail below. As a result of the above, the present inventors found that the exhaust gas temperature from the diesel engine is extremely low, and the exhaust gas temperature during city driving does not reach 450°C even at the manifold outlet, so the combustion behavior of carbon-based particulates is good even below 350°C. The pressure equilibrium temperature (the temperature at which the pressure rise due to the accumulation of fine particles is equal to the pressure drop due to combustion of fine particles) is low at 330 to 350℃, and the accumulated fine particles are at 400℃.
We have discovered a catalyst system that has excellent properties, such as a catalyst that starts combustion at a temperature of 600 degrees Celsius, and has very low sulfate production of 5% or less even at 600 degrees Celsius. 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, in the case of a catalyst containing a platinum group element, although it has the ability to oxidize carbon monoxide (CO) and hydrocarbons (HC), it also oxidizes SO 2 and produces sulfate, which is not desirable. However, even in the low temperature range, some of the combustible components in the fine particles burn, so the pressure drop increases slowly, and the pressure equilibrium 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. According to the findings of the present inventors, in the above catalyst component dispersedly supported on an inorganic substrate, tungstate of group (a) and barium molybdate of group (c) are combined with platinum group elements of group (b). It acts extremely closely against the metal, and exhibits the effect of effectively suppressing the sulfate-generating ability that the metal originally has. In particular, the effect is fully exhibited in catalysts whose final calcination is carried out at a high temperature of 700 to 1000°C. Moreover, the proportion of their coexistence is 4 in the molar ratio of (a)/(b).
When in the range of ~120, preferably in the range of 6 to 90,
Moreover, the supported amount of tungstate of group (a) is 8 to 8.
120g/l-carrier, preferably in the range of 10-100g/l-carrier, and the amount of supported platinum metal element of group (b) is
0.1-4.0g/- carrier, preferably 0.3-3.0g/
- It was found that the sulfate generation ability was suppressed the most when the carrier was in the range, and the combustion behavior of particulate matter was good. And again (c)
It has been found that the combustion performance of particulate matter is further improved by combining barium molybdate of the group in the range of 8 to 120 g/-carrier, preferably 10-100 g/-carrier. In the present invention, tungstate refers to tungstate of metals such as lithium, sodium, potassium, cesium, magnesium, calcium, strontium, barium, lanthanum, cerium, iron, cobalt, nickel, copper, silver, bismuth, tin, and lead. means acid salt. If the molar ratio of (a)/(b) is less than 4, the effect of suppressing sulfate formation will be poor, and under the condition of diesel exhaust gas at 600°C, more than 10% of SO 2 will be produced.
Shows the conversion rate to SO 3 . If the molar ratio of (a)/(b) is greater than 120, the combustion performance of fine particles at low temperatures (below 300°C) will deteriorate, and the pressure drop per unit time will increase, which is a characteristic of platinum group elements. This is undesirable because it interferes with the combustion performance of SOF (soluble organic fraction) at low temperatures. In addition, the firing temperature after supporting components (a) and (b) was set to 700℃.
When firing at temperatures below 1,000°C, there is a tendency for the conversion rate of SO 2 to SO 3 to increase, and when firing at temperatures above 1000°C, the self-regeneration temperature (pressure drop in the catalyst layer due to combustion of particulates decreases). temperature) becomes high, which is undesirable. 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 inorganic base may be formed into a three-dimensional structure having a gas filter structure (for example, ceramic foam, wire mesh, etc.).
A support layer is formed by slurrying a metal foam (metal foam, plugged ceramic honeycomb) and washing-coating it, and contains at least one metal selected from the group consisting of platinum group elements such as platinum, rhodium, and palladium. The compound is supported in the form of an aqueous or organic solvent (for example, alcohol) solution or dispersion by an impregnation or soaking method, and dried or fired at 300 to 500°C after drying. Next, a water-soluble or organic solvent-soluble salt of tungsten is impregnated and supported, dried and then fired at 300 to 500°C. Next, the metals (Li, Na, K, Cs, Mg, Ca, Sr, Ba, La,
A water-soluble or organic solvent-soluble salt of Ce, Fe, Co, Ni, Cu, Ag, Bi, Sn, Pb) is impregnated and supported, and after drying, it is fired at 700 to 1000°C for 1 to 5 hours. Then, each compound is impregnated and supported in the form of a water-soluble compound to form barium molybdate, and these molybdates are dispersed and formed on the catalyst.
It may be fired at 700-1000°C. The above raw material compounds include oxides, hydroxides, nitrates, carbonates, phosphates, sulfates, halides,
It is appropriately selected from inorganic compounds such as metal salts, carboxylic acid salts such as acetate and formate, and organic compounds such as complex compounds, and it is preferable to use compounds that are easily soluble in water or alcoholic organic solvents. Furthermore, the order in which the catalyst components are supported may be changed. Furthermore, the tungstate prepared and ground in advance and the powder containing the platinum group metal in the inorganic base material are mixed into a slurry using a wet mill, wash coated, and dried.
The catalyst may be completed by firing at 700 to 1000°C. A compromise between these methods may 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. EXAMPLES The present invention will be explained in more detail below with reference to Examples and Comparative Examples. Example 1 353 g of ammonium paramolybdate was dissolved in water from step 2, and 416.5 g of barium chloride was added in advance.
was poured into an aqueous solution of step 2 with stirring, the resulting precipitate was overwashed, dried at 150℃ for 5 hours, and calcined at 500℃ for 2 hours to obtain about 530g of
I got BaMoO 4 powder. Add alumina powder to 800ml of a mixed solution of dinitrodiamine platinum nitric acid solution containing 9.0g as Pt and rhodium nitrate aqueous solution containing 0.9g as Rh.
700 g was added, mixed well, dried at 150°C for 5 hours, and then calcined at 500°C for 2 hours to obtain alumina powder containing Pt and Rh. 853 g of a commercially available ammonium metatungstate aqueous solution (solution containing 50% by weight as WO 3 , manufactured by Japan Inorganic Chemical Industry Co., Ltd.) was taken and diluted to 1 with water. Separately, 470 g of barium acetate Ba(C 2 H 3 O 2 ) 2 was taken and dissolved in water to obtain 1. Mix both solutions with stirring and add barium tungstate BaWO 4
A white precipitate was obtained. The precipitate is overwashed,
It was dried at 150°C for 5 hours and fired at 500°C for 2 hours. 472.6 g of the obtained BaWO 4 powder and the BoMoO 4
208.1 g of powder and 710 g of alumina powder containing Pt and Rh are thoroughly mixed in a ball mill, then slurried in a wet mill, supported on cordierite foam 1.7, and after shaking off excess slurry, heated at 150°C. After drying for 3 hours at 750° C., it was fired for 2 hours to obtain a cordierite foam having an alumina coat layer containing Pt, Rh, BaMoO 4 and BaWO 4 . The supported amounts of Pt and Rh in the obtained catalyst are respectively
0.9g/-carrier, 0.09g/-carrier,
The amount of BaMoO 4 supported is 20.8g/− carrier, BaWO 4
The amount supported was 47.3 g/-carrier. The composition of the finished coating layer is 50.3% by weight of Al 2 O 3 and BaMoO 4
14.9% by weight, BaWO 4 34.0% by weight, Pt+Rh (Pt/
Rh=10/1) was 0.72% by weight. Comparative Example 1 Alumina powder was added to 800 ml of a mixed solution of dinitrodiamine platinum nitric acid solution containing 9.0 g as Pt and rhodium nitrate aqueous solution containing 0.9 g as Rh.
700 g was added, mixed well, dried at 150°C for 5 hours, and then calcined at 500°C for 2 hours to obtain alumina powder containing Pt and Rh. 853 g of a commercially available ammonium metatungstate aqueous solution (solution containing 50% by weight as WO 3 , manufactured by Japan Inorganic Chemical Industry Co., Ltd.) was taken and diluted to 1 with water. Separately, 470 g of barium acetate Ba(C 2 H 3 O 2 ) 2 was taken and dissolved in water to obtain 1. Mix both solutions with stirring and add barium tungstate BaWO 4
A white precipitate was obtained. The precipitate is overwashed,
It was dried at 150°C for 5 hours and fired at 500°C for 2 hours. 472.6 g of the BaWO 4 powder and 710 g of the above alumina powder containing Pt and Rh were thoroughly mixed in a ball mill, then slurried in a wet mill, supported on cordierite foam 1.7, and the excess slurry was shaken off. After drying at 150°C for 3 hours, it was fired at 750°C for 2 hours to obtain a cordierite foam having an alumina cord layer containing Pt, Rh, and BaWO4 . The amount of supported Pt and Rh in the obtained catalyst was 0.9 each.
g/- carrier, 0.09 g/- carrier,
The amount of BaWO 4 supported was 47.3 g/-carrier.
The composition of the finished coating layer is Al 2 O 3 59.2% by weight,
BaWO 4 40% by weight, Pt+Rh (Pt/Rh=10/1)
It was 0.84% by weight. Comparative Example 2 Commercially available cordierite foam (bulk density 0.35g/
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, it was fired at 500°C for 2 hours to obtain a cordierite foam having an alumina coat layer. The amount of alumina supported was 70.1 g/-carrier. Next, potassium tungstate (K 2 WO 4 ) 571.4
immersing the foam in an aqueous solution of 2 containing g;
After shaking off the excess aqueous solution, it was dried at 150°C for 3 hours, and then baked at 750°C for 2 hours. The amount of K 2 WO 4 supported on the obtained catalyst was 40 g/-
It was a carrier. The composition of the finished coat layer was 63.7% by weight of alumina and 36.3% by weight of K 2 WO 4 . Example 2 A catalyst evaluation test was conducted on the catalysts obtained in Example 1 and Comparative Examples 1 and 2 using a 4-cylinder diesel engine with a displacement of 2300 c.c. Particulate capture was carried out for approximately 2 hours at an engine speed of 2500 rpm and a torque of 4.0 kg・m, and then the torque was reduced to 0.5 kg/m.
The change in pressure drop in the catalyst layer is continuously recorded by raising the pressure at Kg/m intervals every 5 minutes, and as the exhaust gas temperature rises on the catalyst, the pressure rises due to the accumulation of particles and the pressure drops due to combustion of the particles. The temperature at which Te becomes equal to the temperature at which ignition and combustion occur and the pressure drop rapidly decreases
I asked for Ti. In addition, when capturing particulates at 2500 rpm and a torque of 4.0 kg・m, the change in pressure drop over time is calculated from the chart by calculating the change in pressure drop per hour by ΔP.
The value of (mmHg/H) was determined. In addition, the conversion rate of SO 2 to SO 3 is determined by the exhaust gas temperature 600
Calculated in °C. The conversion rate of SO 2 is measured using the inlet gas, and the SO 2 concentration of the outlet gas is measured using a non-dispersive infrared analyzer (NDIR method).
The conversion rate (%) of SO 2 was determined using the following calculation formula. SO2 conversion rate (%) = Inlet SO2 concentration (ppm) - Outlet SO2
Concentration (ppm)/Inlet SO 2 concentration (ppm) x 100 The results are shown in Table 1. 【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)少なくとも1種のタン
グステン酸塩と、(b)白金、ロジウムおよびパラジ
ウムからなる白金族元素の群から選ばれた少なく
とも1種の金属および/または酸化物と、(c)モリ
ブデン酸バリウム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)群から選ばれたモル比で(a)/(b)=
4〜120の範囲である特許請求の範囲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特許請求の範囲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)少なくとも1種のタン
グステン酸塩と、(b)白金、ロジウムおよびパラジ
ウムからなる白金族元素の群から選ばれた少なく
とも1種の金属および/または酸化物と、(c)モリ
ブデン酸バリウム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) Distributed support of at least one tungstate, (b) at least one metal and/or oxide selected from the group of platinum group elements consisting of platinum, rhodium, and palladium, and (c) barium molybdate. A catalyst for purifying diesel engine exhaust gas that is characterized by the following characteristics: 2 (a)/(b)= molar ratio selected from groups (a) and (b)
The catalyst according to claim 1, having a molecular weight ranging from 4 to 120. 3 The fire-resistant three-dimensional structure is ceramic foam,
3. The catalyst according to claim 1, which is a wire mesh, a metal foam, or a plugged ceramic honeycomb. 4. 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) at least one type of tungstic acid. A salt, (b) at least one metal and/or oxide selected from the group of platinum group elements consisting of platinum, rhodium, and palladium, and (c) barium molybdate are dispersed and supported in the air. 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 700°C to 1000°C.
JP2154036A 1990-06-14 1990-06-14 Catalyst for exhaust gas cleaning and its preparation Granted JPH03114539A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2154036A JPH03114539A (en) 1990-06-14 1990-06-14 Catalyst for exhaust gas cleaning and its preparation

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2154036A JPH03114539A (en) 1990-06-14 1990-06-14 Catalyst for exhaust gas cleaning and its preparation

Related Parent Applications (1)

Application Number Title Priority Date Filing Date
JP59078664A Division JPS60222146A (en) 1984-04-20 1984-04-20 Catalyst for purifying exhaust gas and its preparation

Publications (2)

Publication Number Publication Date
JPH03114539A JPH03114539A (en) 1991-05-15
JPH0575457B2 true JPH0575457B2 (en) 1993-10-20

Family

ID=15575512

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2154036A Granted JPH03114539A (en) 1990-06-14 1990-06-14 Catalyst for exhaust gas cleaning and its preparation

Country Status (1)

Country Link
JP (1) JPH03114539A (en)

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP4024251B2 (en) * 2005-02-02 2007-12-19 市村 富久代 Charge transfer catalyst, redox functional material using the catalyst, and charge transfer catalyst-containing material

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JPH03114539A (en) 1991-05-15

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