JPH0442063B2 - - Google Patents
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- JPH0442063B2 JPH0442063B2 JP58184559A JP18455983A JPH0442063B2 JP H0442063 B2 JPH0442063 B2 JP H0442063B2 JP 58184559 A JP58184559 A JP 58184559A JP 18455983 A JP18455983 A JP 18455983A JP H0442063 B2 JPH0442063 B2 JP H0442063B2
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- oxide
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- metals
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- Filtering Of Dispersed Particles In Gases (AREA)
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
Description
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
進められている。
ところで、こられ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
子を補足し、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得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
時に得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、(a)銅、マンガン、モリブデン、鉛、鉄、コ
バルト、バナジウムおよび銀よりなる群から選
ばれた少なくとも1種の金属の酸化物と(b)ナト
リウム、カリウムおよびセシウムよりなる群か
ら選ばれた少なくとも1種の金属の酸化物とさ
らに(c)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種の金属とから
なり、かつ(a)および(b)群で示される酸化物が、
それらの金属の原子比で(a)/(b)=0.25〜9.0の
範囲であり、(b)および(c)群で示される酸化物及
び金属が、それらの金属の原子比で(b)/(c)=4
〜80の範囲で分散担持せしめてなる排ガス浄化
用触媒。
(2) 完成触媒1当り多孔性無機質基盤が酸化物
として5〜250g、(a)群で示される酸化物が2
〜100g、(b)群で示される酸化物が2〜100g、
さらに(c)群で示される金属が0.1〜4.0gの範囲
含有せしめられてなる特許請求の範囲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、ワイヤーメツシユ、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、(a)銅、マンガン、モリブデン、鉛、鉄、コ
バルト、バナジウムおよび銀よりなる群から選
ばれた少なくとも1種の金属を含む化合物と(b)
ナトリウム、カリウムおよびセシウムよりなる
群から選ばれた少なくとも1種の金属を含む化
合物とさらに(c)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
属を含む化合物とからなり、かつ(a)および(b)群
で示される化合物が、それらの金属の原子比で
(a)/(b)=0.25〜9.0の範囲であり、(b)および(c)
群で示される化合物が、それらの金属の原子比
で(b)/(c)=4〜80の範囲で分散担持せしめ、こ
れを700〜1000℃の範囲の温度で熱処理するこ
とにより、(a)および(b)の化合物については酸化
物、(c)の化合物については金属とすることを特
徴とする排ガス浄化用触媒の製法。
本発明者らは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450℃でもほぼ認められない特性を有す
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。一方貴金属を添
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、(b)群
のアルカリ金属は(c)群の貴金属に対し極めて密接
に作用し、元来具有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。もちろん(b)群のアル
カリ金属にも(a)群金属と同様の微粒子の燃焼性能
を認めている。とくにアルカリ金属と貴金属との
担持焼成が700〜1000℃という高温で行なわれる
とき、効果が十分に発揮される。しかもその共存
する割合がアルカリ金属/貴金属(モル比)で4
〜80の範囲、好ましくは8〜50の範囲のときサル
フエート生成能が最も抑制されることが知見され
たのである。
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。まず上記無機質基盤をガスフ
イルター型構造を有する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、銅、マンガン、モリブデン、鉛、
鉄、コバルト、バナジウム、銀よりなる群から選
ばれた少なくとも1種の金属を含む化合物、カリ
ウム、セシウム、ナトリウム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さらに白
金、ロジウム、パラジウムよりなる群から選ばれ
た少なくとも1種の金属を含む化合物を、水性な
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
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、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。
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
アルミナ粉末1Kg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
ジウム水溶液を添加して充分混合し150℃で3時
間乾燥後500℃で2時間焼成し、粉砕してPt、Rh
を含有するアルミナ粉末を得た。
該粉体を湿式ミルを用いてスラリー化して担持
し、市販のコージエライト発泡体(嵩密度0.35
g/cm3、空孔率87.5%、容積1.7)に浸漬担持
し、余分なスラリーを振り切つて、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
ライト発泡体を得た。
次に硝酸鉛265gと硝酸セシウム124.4gをイオ
ン交換水に溶解させ2とした。これに該発泡体
を浸漬し余分な溶液を振り切つて、150℃で3時
間乾燥後750℃で2時間焼成した。
この時のPt、Rhの担持量は0.90g/−担体、
0.09g/−担体、鉛、セシウムの担持量は酸化
物換算でそれぞれ20g/−担体、10g/−担
体であつた。出来上りのコート層の組成はアルミ
ナ69.3重量%、PbO19.8重量%、Cs2O9.9重量%、
Pt+Rh(Pt/Rh=10/1)0.99重量%であつた。
実施例 2
チタンをTiO2として959g含む四塩化チタン10
重量%の水溶液に、ケイ素をSiO2として180.2g
含有するスノーテツクス−0(20重量%含有品)
と28%アンモニウム水、約3.9の混合溶液を攪
拌下添加し、生成したケーキを過水洗し150℃
で5時間乾燥後500℃で2時間焼成した。該焼成
品を粉砕して、TiO2/SiO2モル比8/2のチタ
ニア−シリカ粉体をえた。表面積は160m2/gで
あつた。
次に、硝酸銅Cu(NO3)2・3H2O868gと硝酸カ
リウムKNO3307g、Ptとして12.86gを含有する
塩化白金酸水溶液とRhとして1.286gを含有する
塩化ロジウム水溶液を混合して約1の溶液とし
て、これに上記チタニア−シリカ粉体1Kgを混合
して、均一に分散させた。150℃3時間乾燥後、
500℃で2時間焼成して粉砕しCuO、K2O、Pt、
Rhを含有するチタニア−シリカ粉体をえた。
該粉体1Kgを湿式ミルでスラリー化して1.7
容量のコージエライト発泡体に浸漬担持し、余分
なスラリーを取り除いた後、150℃で3時間乾燥
し、800℃で2時間焼成した。
この時のチタニア−シリカの担持量は、70g/
−担体で、Pt、Rhの担持量はそれぞれ0.90
g/−担体、0.09g/−担体であり、銅およ
びカリウムは酸化物換算でそれぞれ20g/−担
体、10g/−担体であつた。
出来上りのコート層の組成はチタニア−シリカ
69.3重量%、CuO19.8重量%、K2O9.9重量%、Pt
+Rh(Pt/Rh=10/1)0.99重量%であつた。
実施例 3
触媒3−a、3−b、3−c、3−e、3−
g、3−j、3−m及び3−nについては、実施
例1に準じた方法、3−d、3−f、3−h、3
−i、3−k及び3−lについては、実施例2に
準じた方法で下記の触媒組成のコート層を有する
コージエライト発泡体からなる触媒をえた。
( )内数字は各成分の担持量(g/−担
体)を示す。
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 in diesel engine exhaust gas (mainly consisting of solid carbon particles, sulfur-based particles such as sulfates, and high molecular weight hydrocarbon particles in liquid or solid form) has tended to become an environmental health problem. . 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, efforts are being made to tighten regulations on the emission of these particulates from diesel engines. By the way, as a method for removing these fine particles,
There are two main methods as follows. One is to use a heat-resistant gas filter (ceramic foam, wire mesh, metal foam, sealed type ceramic honeycomb, etc.) to pass through the exhaust gas and capture fine particles, and if the pressure drop increases, the particles may be accumulated in a burner, etc. One method is to burn the fine particles to regenerate the filter, 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 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 it can effectively ignite and burn accumulated particulates 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, diesel engine exhaust gas purification has good combustion behavior of particulates within the diesel engine exhaust gas temperature range obtained 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, (a) selected from the group consisting of copper, manganese, molybdenum, lead, iron, cobalt, vanadium and silver; (b) an oxide of at least one metal selected from the group consisting of sodium, potassium and cesium; and (c) an oxide of at least one metal selected from the group consisting of platinum, rhodium and palladium. and at least one metal and represented by groups (a) and (b),
The atomic ratio of these metals is in the range of (a)/(b) = 0.25 to 9.0, and the oxides and metals shown in groups (b) and (c) have an atomic ratio of (b) /(c)=4
A catalyst for exhaust gas purification that is dispersedly supported in the range of ~80%. (2) The porous inorganic substrate contains 5 to 250 g of oxide per finished catalyst, and the oxide of group (a) contains 2
~100g, 2~100g of oxides shown in group (b),
The catalyst according to claim 1, further comprising 0.1 to 4.0 g of a metal represented by group (c). (3) The catalyst according to claim 1 or 2, wherein the refractory three-dimensional structure is a ceramic foam, a wire mesh, a metal foam, or a sealed ceramic honeycomb. (4) On a porous inorganic base supported on a refractory three-dimensional structure having a gas filter function, (a) a material selected from the group consisting of copper, manganese, molybdenum, lead, iron, cobalt, vanadium and silver; (b) a compound containing at least one metal;
(c) a compound containing at least one metal selected from the group consisting of sodium, potassium and cesium; and (c) a compound containing at least one metal selected from the group consisting of platinum, rhodium and palladium; The compounds shown in groups (a) and (b) are
(a)/(b)=0.25 to 9.0, and (b) and (c)
By dispersing and supporting the compounds represented by the group in an atomic ratio of metals (b)/(c) in the range of 4 to 80, and heat-treating this at a temperature in the range of 700 to 1000°C, (a ) and (b) are oxides, and (c) is a metal. 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 pressure equilibrium 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 discovered a catalyst system that has the characteristics of a catalyst that is as low as 350°C, starts combustion of accumulated particulates below 400°C, and rapidly reduces pressure drop, and has the characteristics that almost no sulfate formation is observed even at 450°C. 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, 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-mentioned catalyst component dispersed and supported on an inorganic substrate, the alkali metal of group (b) acts extremely closely on the noble metal of group (c), and the sulfate that originally contains Demonstrates the effect of effectively suppressing generation capacity. Of course, group (b) alkali metals have the same fine particle combustion performance as group (a) metals. In particular, the effect is fully exhibited when supporting and firing alkali metals and noble metals is carried out at a high temperature of 700 to 1000°C. Moreover, the coexistence ratio of alkali metals/noble metals (molar ratio) is 4.
It has been found that the sulfate-forming ability is most suppressed in the range of 80 to 80, preferably 8 to 50. 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. First, the above-mentioned inorganic base is formed into a three-dimensional structure having a gas filter type structure (e.g., ceramic foam, wire mesh, metal foam, sealed type ceramic honeycomb).
The slurry is made into a slurry and coated with wash to form a support layer.
Compounds containing at least one metal selected from the group consisting of iron, cobalt, vanadium, and silver, compounds containing at least one metal selected from the group consisting of potassium, cesium, and sodium, and further platinum, rhodium, and palladium. A compound containing at least one metal selected from the group consisting of at least one metal is supported in the form of an aqueous or organic solvent (alcohol etc.) solution or dispersion by an impregnation or dipping method. 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. Although it is appropriately selected from among these, it is preferable to use one that is easily soluble in water or an alcoholic organic solvent. It is also possible to adopt a method in which the inorganic base material and each catalyst component group are mixed in advance, and this is washed coated, dried, and fired to form a finished catalyst.
These compromise methods may also be adopted as appropriate. Hereinafter, the present invention will be explained in more detail by showing Examples and Comparative Examples. Example 1 1 kg of alumina powder contains 12.86 g of platinum (Pt)
A nitric acid solution of dinitrodiammine platinum containing Pt and a rhodium nitrate aqueous solution containing 1.286 g of rhodium (Rh) were added and mixed thoroughly, dried at 150°C for 3 hours, fired at 500°C for 2 hours, and crushed to obtain Pt, Rh
An alumina powder containing . The powder was made into a slurry using a wet mill and supported on a commercially available cordierite foam (bulk density 0.35
g/cm 3 , porosity 87.5%, volume 1.7), and the excess slurry was shaken off to obtain a cordierite foam having an alumina coat layer containing platinum-rhodium. Next, 265 g of lead nitrate and 124.4 g of cesium nitrate were dissolved in ion exchange water to obtain 2. The foam was immersed in this, the excess solution was shaken off, and the foam was dried at 150°C for 3 hours and then baked at 750°C for 2 hours. At this time, the supported amount of Pt and Rh was 0.90g/− carrier,
The supported amounts of 0.09 g/-carrier, lead, and cesium were 20 g/-carrier and 10 g/-carrier, respectively, in terms of oxides. The composition of the finished coating layer is 69.3% by weight of alumina, 19.8% by weight of PbO, 9.9% by weight of Cs 2 O,
Pt+Rh (Pt/Rh=10/1) was 0.99% by weight. Example 2 Titanium tetrachloride 10 containing 959g of titanium as TiO 2
180.2 g of silicon as SiO 2 in a wt% aqueous solution
Contains Snowtex-0 (product containing 20% by weight)
A mixed solution of about 3.9% and 28% ammonium water was added under stirring, and the resulting cake was washed with water and heated to 150°C.
After drying for 5 hours at 500°C, it was fired for 2 hours. The fired product was pulverized to obtain titania-silica powder with a TiO 2 /SiO 2 molar ratio of 8/2. The surface area was 160 m 2 /g. Next, 868 g of copper nitrate Cu ( NO 3 ) 2.3H 2 O, 307 g of potassium nitrate KNO 3 , a chloroplatinic acid aqueous solution containing 12.86 g as Pt, and a rhodium chloride aqueous solution containing 1.286 g as Rh were mixed to give about 1. To this solution, 1 kg of the titania-silica powder was mixed and uniformly dispersed. After drying at 150℃ for 3 hours,
Sintered at 500℃ for 2 hours and crushed to produce CuO, K 2 O, Pt,
Titania-silica powder containing Rh was obtained. 1 kg of the powder is made into a slurry using a wet mill to make a slurry of 1.7 kg.
The slurry was dipped and supported on a capacity cordierite foam, and after removing excess slurry, it was dried at 150°C for 3 hours and fired at 800°C for 2 hours. The amount of titania-silica supported at this time was 70g/
-The amount of Pt and Rh supported on the carrier is 0.90 each.
g/-carrier and 0.09 g/-carrier, and copper and potassium were 20 g/-carrier and 10 g/-carrier, respectively, in terms of oxides. The composition of the finished coating layer is titania-silica.
69.3 wt%, CuO19.8 wt%, K2O9.9 wt%, Pt
+Rh (Pt/Rh=10/1) was 0.99% by weight. Example 3 Catalysts 3-a, 3-b, 3-c, 3-e, 3-
For g, 3-j, 3-m and 3-n, the method according to Example 1, 3-d, 3-f, 3-h, 3
For -i, 3-k and 3-l, catalysts made of cordierite foam having a coat layer having the following catalyst composition were obtained in the same manner as in Example 2. The numbers in parentheses indicate the amount of each component supported (g/-carrier).
【表】
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、PbO20g/−担体、Cs210g/−担体、
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においてセシ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、PbO20g/−担体、Pt0.90g/−担体、
Rh0.09g/−担体、担持したコージエライト
発泡体をえた。
比較例 3
実施例2において、硝酸銅を用いない以外は全
て同じ方法で触媒を調製し、チタニア−シリカ70
g/−担体、K2O10g/−担体、Pt0.90g/
−担体、Rh0.09g/−担体、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 4
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
にした目封じタイプのハニカムに替える以外は、
全く同様の本法で触媒を調製した。
実施例 5
実施例1〜4、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
0.5Kg・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(Te)と着火燃焼し、圧損が急激に加工
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。
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に転化率(%)を求め
た。
SO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。
実施例1〜3、比較例1〜3で得られた触媒の
(a)/(b)値、(b)/(c)値を表2に示す。[Table] Comparative Example 1 Except for not using Pt and Rh in Example 1,
All catalysts were prepared in the same way, Al 2 O 3 70g/-
Support, PbO20g/-support, Cs 2 10g/-support,
A supported cordierite foam catalyst was obtained. Comparative Example 2 A catalyst was prepared in the same manner as in Example 1 except that cesium was not used, and 70 g of Al 2 O 3 /- support, 20 g of PbO /- support, 0.90 g of Pt /- support,
Rh0.09g/- carrier, supported cordierite foam was obtained. Comparative Example 3 A catalyst was prepared in the same manner as in Example 2 except that copper nitrate was not used, and titania-silica 70
g/- carrier, K 2 O 10 g/- carrier, Pt 0.90 g/
- Carrier, Rh 0.09 g/- Carrier, supported cordierite foam was obtained. Comparative Example 4 A catalyst was prepared in the same manner as in Example 1 except that the final calcination temperature was changed to 600°C. Example 4 In Example 1, except that the cordierite foam was replaced with a sealed type honeycomb structure in which adjacent holes on both end faces were alternately closed with a honeycomb structure to allow gas to pass only from the partition wall.
A catalyst was prepared using exactly the same method. Example 5 The catalysts obtained in Examples 1 to 4 and Comparative Examples 1 to 2 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 increases (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 was determined at an exhaust gas temperature of 450°C. 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 (%) to SO 2 was determined using the following calculation formula. SO 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. The catalysts obtained in Examples 1 to 3 and Comparative Examples 1 to 3
Table 2 shows the (a)/(b) values and (b)/(c) values.
【表】【table】
【表】【table】
【表】【table】
【表】【table】
Claims (1)
造体上に担持せしめられた多孔性無機質基盤上
に、(a)銅、マンガン、モリブデン、鉛、鉄、コバ
ルト、バナジウムおよび銀よりなる群から選ばれ
た少なくとも1種の金属の酸化物と(b)ナトリウ
ム、カリウムおよびセシウムよりなる群から選ば
れた少なくとも1種の金属の酸化物とさらに(c)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種の金属とからなり、かつ(a)
および(b)群で示される酸化物が、それらの金属の
原子比で(a)/(b)=0.25〜9.0の範囲であり、(b)お
よび(c)群で示される酸化物及び金属が、それらの
金属の原子比で(b)/(c)=4〜80の範囲で分散担持
せしめてなる排ガス浄化用触媒。 2 完成触媒1当り多孔性無機質基盤が酸化物
として5〜250g、(a)群で示される酸化物が2〜
100g、(b)群で示される酸化物が2〜100g、さら
に(c)群で示される金属が0.1〜4.0gの範囲含有せ
しめられてなる特許請求の範囲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、ワイヤーメツシユ、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、(a)銅、マンガン、モリブデン、鉛、鉄、コバ
ルト、バナジウムおよび銀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と(b)ナトリ
ウム、カリウムおよびセシウムよりなる群から選
ばれた少なくとも1種の金属を含む化合物とさら
に(c)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種の金属を含む化合物
とからなり、かつ(a)および(b)群で示される化合物
が、それらの金属の原子比で(a)/(b)=0.25〜9.0
の範囲であり、(b)および(c)群で示される化合物
が、それらの金属の原子比で(b)/(c)=4〜80の範
囲で分散担持せしめ、これを700〜1000℃の範囲
の温度で熱処理することにより、(a)および(b)の化
合物については酸化物、(c)の化合物については金
属とすることを特徴とする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, (a) a material made of copper, manganese, molybdenum, lead, iron, cobalt, vanadium, and silver; (b) an oxide of at least one metal selected from the group consisting of sodium, potassium and cesium; and (c) platinum, rhodium and palladium. at least one metal selected from the group, and (a)
The oxides and metals shown in groups (b) and (c) have an atomic ratio of (a)/(b) = 0.25 to 9.0. A catalyst for exhaust gas purification is prepared by dispersing and supporting these metals in an atomic ratio of (b)/(c)=4 to 80. 2. The porous inorganic base contains 5 to 250 g of oxide per finished catalyst, and the oxide of group (a) contains 2 to 250 g of oxide.
2. The catalyst according to claim 1, which contains 100 g of the oxide of group (b), 2 to 100 g of the oxide of group (b), and 0.1 to 4.0 g of the metal of group (c). 3. Claim 1, wherein the fire-resistant three-dimensional structure is ceramic foam, wire mesh, metal foam, or sealed ceramic honeycomb.
or the catalyst described in 2. 4. On a porous inorganic base supported on a refractory three-dimensional structure having a gas filter function, (a) a material selected from the group consisting of copper, manganese, molybdenum, lead, iron, cobalt, vanadium and silver; (b) a compound containing at least one metal selected from the group consisting of sodium, potassium, and cesium; and (c) at least one selected from the group consisting of platinum, rhodium, and palladium. and a compound containing one kind of metal, and the compound represented by groups (a) and (b) has an atomic ratio of those metals (a)/(b)=0.25 to 9.0.
The compounds shown in groups (b) and (c) are dispersed and supported at an atomic ratio of (b)/(c) = 4 to 80, and this is carried out at 700 to 1000°C. A method for producing a catalyst for exhaust gas purification, characterized in that the compounds (a) and (b) are converted into oxides, and the compound (c) is converted into metals by heat treatment at a temperature in the range of .
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP58184559A JPS6078640A (en) | 1983-10-04 | 1983-10-04 | Catalyst for purifying exhaust gas and preparation thereof |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP58184559A JPS6078640A (en) | 1983-10-04 | 1983-10-04 | Catalyst for purifying exhaust gas and preparation thereof |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS6078640A JPS6078640A (en) | 1985-05-04 |
| JPH0442063B2 true JPH0442063B2 (en) | 1992-07-10 |
Family
ID=16155320
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP58184559A Granted JPS6078640A (en) | 1983-10-04 | 1983-10-04 | Catalyst for purifying exhaust gas and preparation thereof |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS6078640A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO2010058834A1 (en) | 2008-11-21 | 2010-05-27 | 日産自動車株式会社 | Particulate substance removing material, particulate substance removing filter catalyst using particulate substance removing material, and method for regenerating particulate substance removing filter catalyst |
Families Citing this family (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS62140647A (en) * | 1985-12-13 | 1987-06-24 | Bridgestone Corp | Catalyst for purifying exhaust gas |
| JPH0621539B2 (en) * | 1986-12-04 | 1994-03-23 | キヤタラ−工業株式会社 | Patty unit for burning catalyst filter |
| JPH067920B2 (en) * | 1987-03-31 | 1994-02-02 | 株式会社リケン | Exhaust gas purification material and exhaust gas purification method |
| US5888924A (en) * | 1996-08-07 | 1999-03-30 | Goal Line Enviromental Technologies Llc | Pollutant removal from air in closed spaces |
| JP4639455B2 (en) * | 2000-10-02 | 2011-02-23 | パナソニック株式会社 | Exhaust gas purification material |
| DE102004058780A1 (en) * | 2004-12-07 | 2006-06-08 | Robert Bosch Gmbh | Catalyst for the oxidation of carbonaceous particles and apparatus for purifying gas mixtures containing them |
| JP2014168764A (en) * | 2013-03-05 | 2014-09-18 | Toyota Central R&D Labs Inc | Oxidation catalyst for diesel exhaust gas and purification method of diesel exhaust gas using the same |
Family Cites Families (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS58174236A (en) * | 1982-04-05 | 1983-10-13 | Bridgestone Corp | Catalyst for removing particulate matter in waste gas |
-
1983
- 1983-10-04 JP JP58184559A patent/JPS6078640A/en active Granted
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO2010058834A1 (en) | 2008-11-21 | 2010-05-27 | 日産自動車株式会社 | Particulate substance removing material, particulate substance removing filter catalyst using particulate substance removing material, and method for regenerating particulate substance removing filter catalyst |
| US9222382B2 (en) | 2008-11-21 | 2015-12-29 | Nissan Motor Co., Ltd. | Particulate matter purifying material, filter catalyst for purifying particulate matter using particulate matter purifying material, and method of regenerating filter catalyst for purifying particulate matter |
Also Published As
| Publication number | Publication date |
|---|---|
| JPS6078640A (en) | 1985-05-04 |
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