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JPH0260374B2 - - Google Patents
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JPH0260374B2 - - Google Patents

Info

Publication number
JPH0260374B2
JPH0260374B2 JP59078664A JP7866484A JPH0260374B2 JP H0260374 B2 JPH0260374 B2 JP H0260374B2 JP 59078664 A JP59078664 A JP 59078664A JP 7866484 A JP7866484 A JP 7866484A JP H0260374 B2 JPH0260374 B2 JP H0260374B2
Authority
JP
Japan
Prior art keywords
catalyst
platinum
supported
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
JP59078664A
Other languages
Japanese (ja)
Other versions
JPS60222146A (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 JP59078664A priority Critical patent/JPS60222146A/en
Publication of JPS60222146A publication Critical patent/JPS60222146A/en
Publication of JPH0260374B2 publication Critical patent/JPH0260374B2/ja
Granted legal-status Critical Current

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D39/00Filtering material for liquid or gaseous fluids
    • B01D39/14Other self-supporting filtering material ; Other filtering material
    • B01D39/20Other self-supporting filtering material ; Other filtering material of inorganic material, e.g. asbestos paper, metallic filtering material of non-woven wires
    • B01D39/2027Metallic material
    • B01D39/2051Metallic foam
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F01MACHINES OR ENGINES IN GENERAL; ENGINE PLANTS IN GENERAL; STEAM ENGINES
    • F01NGAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR MACHINES OR ENGINES IN GENERAL; GAS-FLOW SILENCERS OR EXHAUST APPARATUS FOR INTERNAL-COMBUSTION ENGINES
    • F01N3/00Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust
    • F01N3/02Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for cooling, or for removing solid constituents of, exhaust
    • F01N3/021Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for cooling, or for removing solid constituents of, exhaust by means of filters
    • F01N3/033Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for cooling, or for removing solid constituents of, exhaust by means of filters in combination with other devices
    • F01N3/035Exhaust or silencing apparatus having means for purifying, rendering innocuous, or otherwise treating exhaust for cooling, or for removing solid constituents of, exhaust by means of filters in combination with other devices with catalytic reactors
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2239/00Aspects relating to filtering material for liquid or gaseous fluids
    • B01D2239/04Additives and treatments of the filtering material
    • B01D2239/0471Surface coating material
    • 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

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Geology (AREA)
  • Combustion & Propulsion (AREA)
  • Mechanical Engineering (AREA)
  • General Engineering & Computer Science (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)
  • Catalysts (AREA)

Description

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

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、圧損が上昇すればバーナーなどで蓄
積した微粒子を接続せしめて、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、頻瑣
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
ンジンに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撚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
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。一方白金属元素を
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
くはない。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、圧平衡温度を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は(b)群の白金族元素に対し極
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60〜90の範囲のとき、
しかも(a)群のタングステン酸塩の担持書が、8〜
120g/一担体、好ましくは10〜100g/一担
の範囲であり、(b)群の白金属元素の担持量が0.1
〜4.0g/一担体、好ましくは0.3〜3.0g/一
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、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
グス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 oranic 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―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、これらに限定されたも
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。 上記原料化合物は、酸化物、杉酸化物、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 市販のコージエライト発泡体(嵩密度0.35g/
cm3、空孔率87.5%、溶積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。 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。 次にタングステン酸塩カリウム(K2WO4
571.4g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Pt,Phの担持量は、それぞれ
0.90g/一担体、0.09g/一担体であり、
K2WO4の担持量は40g/一担体であつた。 出来上りのコート層の組成はアルミナ63.1重量
%、K2WO436.0重量%、Pt+Rh(Pt/Rh=10/
1)0.90重量%であつた。 実施例 2 Ptとして9.0gを含有するジニトロジアンミン
白金の硝酸溶媒と、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。 タングステン酸カリウム400gを水に溶解させ
800mlとした溶液に、該Pt,Rh含有アルミナ粉体
の全量を投入しよく混合した。150℃で5時間乾
燥後、500℃で2時間焼成してPt,Rh,K2WO4
を含有するアルミナ粉体をえた。 該粉体を湿式ミルで、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℃で3時間乾燥後750℃2時
間焼成した。 えられた出来上りのコート層の組成は、アルミ
ナ63.6重量%、K2WO435.5重量%、Pt+Rh(Pt/
Rh=10/1)0.90重量%であり、実施例1とほ
ぼ同組成であつた。 実施例 3 Ptとして9.0gを含有するジニトロジアンミン
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
溶解させ1とした。この両方の溶液を撹拌しな
がら混合しタングステン酸バリウムBaWO4の白
色沈殿物をえた。該沈殿物を過洗浄し、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0.9
g/一担体、0.09g/一担体であり、
BaWO4の担持量は47.3g/一担体であつた。
出来上りのコート層の組成はAl2O359.2重量%、
BaWo4、40重量%、Pt+Rh(Pt/Rh=10/1)
0.84重量%であつた。 実施例 4 実施例3でBaWo4の下記のタングステン酸塩
に替える、あるいは無機質基盤のAl2O3を他の無
機質基盤に替える、あるいはPt+Rhを他の白金
族金属に替える以外は同様な方法で実施例4―1
から実施例4―23までの触媒を調製した。えられ
た触媒の各成分の担持量(g/一担体)は第1
表の通りであつた。 実施例 5 実施例1においてタングステン酸カリウム
571.4gを使うかわりに、タングステン酸カリウ
ム285.7gと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)571.4gの
混合溶液を用いる以外は、全く同様の方法で触媒
を調製した。えられた触媒のPt,Rhの担持量は
それぞれ0.90g/一担体、0.09g/一担体、
K2WO4は21g/一担体、WO3は20g/一担
体であつた。出来上りのコート層の組成はアルミ
ナ 63.3重量%、K2Wo4 18.2重量%、WO3 17.6
重量%、Pt+Rh0.90重量%であつた。 実施例 6 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違いに
閉塞させ隔壁からのみガスを通過させるようにし
たいわゆる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。えられた触
媒のPt,Rhの担持量はそれぞれ0.90g/一担
体、0.09g/一担体であり、K2WO4は40g/
一担体であつた。出来上りコート層の組成はア
ルミナ63.0重量%、K2WO4 36.1重量%、Pt+Rh
0.90重量%であつた。 実施例 7 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,Rh,K2WO4をそれぞれ実施例1におけ
る順序で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
て同様に方法で触媒を調製し、Al2O3 70g/
一担体、K2WO4 40g/一担体をそれぞれ担持
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K2WO4を用いない以外は全
て同様な方法で、触媒を調製し、Al2O3 70g/
一担体、Pt+Rh(Pt/Rh=10/1)1.0g/
一担体を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 3 実施例1において最終の焼成温度を600℃に替
える以外は全て同様な方法で触媒を調製した。 実施例 8 実施例1〜7、比較例1〜3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、出口ガス
のSO2濃度を非分散型赤外分析型(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(%)=入口濃度SO2濃度(ppm)−出口S
O2濃度(ppm)/入口SO2濃度(ppm)×100 結果を次の第2表に示す。
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 consisting of solid carbon particles, sulfur-based particles such as sulfates, and liquid or solid high-molecular-weight hydrocarbon particles) in the exhaust gas of diesel engines has tended to become an environmental health problem. be. 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 particulates, and if the pressure drop increases, the particles may be accumulated in a burner, etc. One method is to regenerate the filter by connecting fine particles, and the other is to carry a catalyst substance on a carrier with this heat-resistant gas filter structure and perform over-operation as well as combustion operation to reduce the frequency of the 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 trivial 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 little ability to generate sulfate (SO 2 is further oxidized to SO 3 or sulfuric acid mist), and it is effective at igniting accumulated particulates within the temperatures found in normal engine running conditions. Although there is a demand for a catalyst with good performance for burning, the current situation is that no catalyst has been proposed that satisfactorily meets this condition. 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 Diesel engine exhaust gas purification characterized by dispersing and supporting tungstate and (b) at least one metal and/or oxide selected from the group of platinum group elements consisting of platinum, rhodium and palladium. Catalyst for use. (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,
The catalyst according to claim 1 or 2, which is a wire mesh, a metal foam, or a plugged ceramic honeycomb. (4) At least one of (a) A tungstate salt and (b) at least one metal and/or oxide selected from the group of platinum group elements consisting of platinum, rhodium, and palladium are dispersed and supported in the air at 700 to 1000
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 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 a catalyst that uses 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, forced regeneration from an external source is required frequently. It needs to be done expensively and lacks practicality. On the other hand, catalysts containing platinum metal elements 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 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 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, the tungstate of group (a) acts extremely closely on the platinum group elements of group (b), and It exhibits the effect of effectively suppressing the ability of the metal to generate sulfate. 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 60-90,
Moreover, the carrier number of group (a) tungstate is 8 to 8.
120g/one carrier, preferably in the range of 10 to 100g/one carrier, and the supported amount of group (b) platinum metal element is 0.1
It has been found that when the amount is in the range of ~4.0 g/carrier, preferably 0.3 to 3.0 g/carrier, the sulfate generation ability is suppressed the most and the combustion behavior of particulate matter is good. 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 oranic 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 to these. 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 compound containing at least one metal selected from the group of platinum group elements consisting of platinum, rhodium, and palladium, which is formed into a slurry and wash-coated on a metal foam (metal foam, plugged ceramic honeycomb) to form a support layer. is supported by an impregnating or dipping method in the form of a water-soluble or organic solvent (eg, alcohol) solution or dispersion, 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. The above raw material compounds include oxides, cedar oxides, 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 Commercially available cordierite foam (bulk density 0.35 g/
cm 3 , porosity 87.5%, voluminous 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. Next, the foam was immersed in mixed solution 2 of a dinitrodiammine platinum nitric acid solution containing 12.86 g of platinum (Pt) and a rhodium nitrate aqueous solution containing 1.286 g of rhodium (Rh), and the excess solution was shaken off. Cut and dry at 150℃ for 3 hours, then dry at 500℃ for 2 hours.
After firing for a period of time, a cordierite foam having an alumina coat layer containing platinum-rhodium was obtained. Then potassium tungstate (K 2 WO 4 )
The foam was immersed in an aqueous solution of 2 containing 571.4 g, and after shaking off the excess aqueous solution, it was heated at 150°C for 3
After drying for an hour, it was fired at 750°C for 2 hours. The supported amounts of Pt and Ph in the obtained catalyst are respectively
0.90g/one carrier, 0.09g/one carrier,
The amount of K 2 WO 4 supported was 40 g/carrier. The composition of the finished coating layer was 63.1% by weight of alumina, 36.0% by weight of K 2 WO 4 , and Pt+Rh (Pt/Rh=10/
1) It was 0.90% by weight. Example 2 700 g of alumina powder was added to 800 ml of a mixed solution of a dinitrodiammine platinum nitric acid solvent containing 9.0 g of Pt and an aqueous rhodium nitrate solution containing 0.9 g of Rh, mixed well, and dried at 150°C for 5 hours. After that, it was fired at 500°C for 2 hours to obtain alumina powder containing Pt and Rh. Dissolve 400g of potassium tungstate in water.
The entire amount of the Pt and Rh-containing alumina powder was added to the 800 ml solution and mixed well. After drying at 150℃ for 5 hours, baking at 500℃ for 2 hours to form Pt, Rh, K 2 WO 4
An alumina powder containing . The powder was made into a slurry using a wet mill, supported on a cordierite foam 1.7, and after shaking off the excess slurry, it was dried at 150°C for 3 hours and then fired at 750°C for 2 hours. The composition of the finished coating layer was 63.6% by weight of alumina, 35.5% by weight of K 2 WO 4 , and Pt+Rh (Pt/Rh).
Rh=10/1) 0.90% by weight, and had almost the same composition as Example 1. Example 3 700 g of alumina powder was added to 800 ml of a mixed solution of dinitrodiammine platinum nitric acid solution containing 9.0 g of Pt and rhodium nitrate aqueous solution containing 0.9 g of Rh, mixed well, and dried at 150°C for 5 hours. After that, it was fired 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 to obtain 1. Both solutions were mixed with stirring to obtain a white precipitate of barium tungstate BaWO 4 . The precipitate was superwashed and heated at 150°C.
The mixture was dried for 5 hours at 500°C and fired for 2 hours at 500°C. 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 coat layer containing Pt, Rh, and BaWO4 . The amount of Pt and Rh supported in the obtained catalyst was 0.9 each.
g/one carrier, 0.09g/one 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. Example 4 In the same manner as in Example 3 except that BaWo 4 was replaced with the following tungstate, or the inorganic base Al 2 O 3 was replaced with another inorganic base, or Pt + Rh was replaced with another platinum group metal. Example 4-1
The catalysts from Example 4-23 were prepared. The supported amount (g/carrier) of each component of the obtained catalyst was
It was as shown in the table. Example 5 Potassium tungstate in Example 1
A catalyst was prepared in exactly the same manner, except that instead of using 571.4 g, a mixed solution of 285.7 g of potassium tungstate and 571.4 g of an aqueous ammonium metatungstate solution (a solution containing 50% by weight as Wo 3 ) was used. The supported amounts of Pt and Rh in the obtained catalyst were 0.90g/one carrier, 0.09g/one carrier, respectively.
K 2 WO 4 was at 21 g/carrier and WO 3 at 20 g/carrier. The composition of the finished coating layer is 63.3% by weight of alumina, 18.2% by weight of K 2 Wo 4 , and 17.6% by weight of WO 3.
% by weight, Pt+Rh 0.90% by weight. Example 6 Exactly the same as in Example 1, except that the cordierite foam was replaced with a so-called plugged type honeycomb structure in which the adjacent holes on both end faces were alternately closed with a honeycomb structure to allow gas to pass only through the partition walls. The catalyst was prepared by the method. The supported amounts of Pt and Rh in the obtained catalyst were 0.90 g/carrier and 0.09 g/carrier, respectively, and K 2 WO 4 was 40 g/carrier.
It was a carrier. The composition of the finished coat layer is 63.0% by weight of alumina, 36.1% by weight of K 2 WO 4 , and Pt + Rh.
It was 0.90% by weight. Example 7 Commercially available alumina pellets (3 to 6 mmφ) 1.7
A catalyst was prepared by supporting Pt, Rh, and K 2 WO 4 in the order of Example 1 so as to have the composition of the finished coating 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 70 g of Al 2 O 3 /
A cordierite foam catalyst supporting one support and 40 g of K 2 WO 4 per support was obtained. Comparative Example 2 A catalyst was prepared in the same manner as in Example 1 except that K 2 WO 4 was not used, and 70 g of Al 2 O 3 /
One carrier, Pt+Rh (Pt/Rh=10/1) 1.0g/
Cordierite foam catalysts each carrying one support were obtained. Comparative Example 3 A catalyst was prepared in the same manner as in Example 1 except that the final calcination temperature was changed to 600°C. Example 8 The catalysts obtained in Examples 1 to 7 and Comparative Examples 1 to 3 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 change 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 increased due to the accumulation of fine particles and the pressure due to the combustion of fine particles. The temperature at which the drop is equal (Te) and the temperature at which ignition and combustion occur and the pressure drop rapidly decreases (Ti) were determined. In addition, the value of ΔP (mmHg/H) was determined by calculating the change in pressure drop over time when capturing fine particles at 2500 rpm and a torque of 4.0 Kg·m from a chart of the amount of change in pressure drop per hour. In addition, the conversion rate of SO 2 to SO 3 is determined by the exhaust gas temperature 600
Calculated in °C. The SO 2 conversion rate was determined by analyzing the SO 2 concentrations of the inlet gas and outlet gas using non-dispersive infrared analysis (NDIR method), and determining the SO 2 conversion rate (%) using the following calculation formula. SO 2 conversion rate (%) = Inlet concentration SO 2 concentration (ppm) - Outlet S
O 2 concentration (ppm)/inlet SO 2 concentration (ppm) x 100 The results are shown in Table 2 below.

【表】【table】

【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)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1
記載の触媒。 3 耐火性3次元構造体がセラミツクスフオー
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) It is characterized by dispersively supporting at least one tungstate and (b) at least one metal and/or oxide selected from the group of platinum group elements consisting of platinum, rhodium, and palladium. Catalyst for diesel engine exhaust gas purification. 2 Compounds selected from groups (a) and (b) in molar ratio
Claim 1 in which (a)/(b)=4 to 120
Catalysts as described. 3. The catalyst according to claim 1 or 2, wherein the refractory three-dimensional structure is a ceramic foam, wire mesh, metal foam, or 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 and (b) at least one metal and/or oxide selected from the group of platinum group elements consisting of platinum, rhodium, and palladium are dispersed and supported in air at a temperature in the range of 700 to 1000°C. A method for producing a catalyst for purifying diesel engine exhaust gas, which is characterized by heat treatment.
JP59078664A 1984-04-20 1984-04-20 Catalyst for purifying exhaust gas and its preparation Granted JPS60222146A (en)

Priority Applications (1)

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

Applications Claiming Priority (1)

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

Related Child Applications (1)

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

Publications (2)

Publication Number Publication Date
JPS60222146A JPS60222146A (en) 1985-11-06
JPH0260374B2 true JPH0260374B2 (en) 1990-12-17

Family

ID=13668126

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Link
JP (1) JPS60222146A (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0275342A (en) * 1988-09-13 1990-03-15 Cataler Kogyo Kk Catalyst for burning carbon fine particles
JP2001347168A (en) * 2000-06-06 2001-12-18 Toyota Motor Corp Exhaust gas purification catalyst
CN117769526A (en) * 2021-08-04 2024-03-26 三井金属矿业株式会社 Tungsten acid solution and its manufacturing method, tungsten oxide powder and its manufacturing method

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