JPH04193348A - Catalyst for purification of exhaust gas - Google Patents
Catalyst for purification of exhaust gasInfo
- Publication number
- JPH04193348A JPH04193348A JP2321296A JP32129690A JPH04193348A JP H04193348 A JPH04193348 A JP H04193348A JP 2321296 A JP2321296 A JP 2321296A JP 32129690 A JP32129690 A JP 32129690A JP H04193348 A JPH04193348 A JP H04193348A
- Authority
- JP
- Japan
- Prior art keywords
- catalyst
- exhaust gas
- titanosilicate
- purification
- nitrogen oxides
- 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.)
- Pending
Links
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- Exhaust Gas Treatment By Means Of Catalyst (AREA)
- Catalysts (AREA)
Abstract
Description
【発明の詳細な説明】
〔産業上の利用分野〕
本発明は、自動車等の内燃機関や硝酸製造工場などの化
学工場から排出される排気ガス中の窒素酸化物を浄化す
る触媒に関する。DETAILED DESCRIPTION OF THE INVENTION [Field of Industrial Application] The present invention relates to a catalyst for purifying nitrogen oxides in exhaust gas discharged from internal combustion engines such as automobiles and chemical plants such as nitric acid manufacturing plants.
自動車等の内燃機関や硝酸製造工場などから排出される
排気ガス中には、窒素酸化物(NOx)等が含まれてい
るため、近年、排気ガス中の窒素酸化物の浄化について
種々の検討がなされている。Exhaust gas emitted from internal combustion engines such as automobiles and nitric acid manufacturing plants contains nitrogen oxides (NOx), etc. In recent years, various studies have been conducted on purifying nitrogen oxides from exhaust gas. being done.
従来、窒素酸化物の浄化には還元性ガスの存在下に貴金
属や金属の還元性触媒を用いるのが主体で、窒素酸化物
を酸化性ガスの存在下で浄化する触媒は殆ど知られてい
ない。Conventionally, the purification of nitrogen oxides has mainly been carried out using reducing catalysts made of noble metals or metals in the presence of reducing gases, but there are almost no known catalysts that purify nitrogen oxides in the presence of oxidizing gases. .
ペンタシル型ゼオライトZSM−5のアルミニウムを結
晶合成の段階でチタンに置換したチタノシリケートが、
オレフィンの芳香族化等低級オレフィンの芳香族化触媒
として有用であることが報告されている(触媒Vo1.
2B 、No、2.1986) 、しかし、排気ガス中
のNOx等の浄化にこの触媒の適用を示唆する記載は全
く認められない。Titanosilicate is made by substituting aluminum of pentasil type zeolite ZSM-5 with titanium at the stage of crystal synthesis.
It has been reported that it is useful as a catalyst for aromatizing lower olefins, such as aromatizing olefins (Catalyst Vol.
2B, No. 2.1986), however, there is no description suggesting the application of this catalyst to the purification of NOx, etc. in exhaust gas.
また、近年のガソリンエンジンにおいては、低燃費化や
排出炭酸ガスの低減の目的で希薄燃焼させることが必要
となってきている。しかしながら、この希薄燃焼ガソリ
ンエンジンの排気ガスは酸素過剰雰囲気であるため従来
の三元触媒(排気ガス中の窒素酸化物、−酸化炭素及び
炭化水素の有害三成分を除去する触媒)は使用できず、
有害成分を除去する方法は実用化されていない。Furthermore, in recent years, gasoline engines have become required to perform lean combustion in order to improve fuel efficiency and reduce carbon dioxide emissions. However, because the exhaust gas from this lean-burn gasoline engine is in an oxygen-rich atmosphere, conventional three-way catalysts (catalysts that remove the three harmful components of nitrogen oxides, carbon oxides, and hydrocarbons in the exhaust gas) cannot be used. ,
No method has been put into practical use to remove harmful components.
このような酸素過剰の排気ガスから、特に窒素酸化物を
除去する方法としては、アンモニア等の還元剤を添加す
る方法、窒素酸化物をアルカリに吸収させて除去する方
法等も知られているが、これらの方法は移動発生源であ
る自動車等に用いるには有効な方法ではなく、その適用
が限定されている。There are known methods for removing nitrogen oxides from such oxygen-excess exhaust gas, including adding a reducing agent such as ammonia and removing nitrogen oxides by absorbing them in alkali. However, these methods are not effective for use in moving sources such as automobiles, and their application is limited.
従って、本発明は前述のような従来技術の問題点を解決
し、自動車等の内燃機関などから排出される排気ガスか
ら、窒素酸化物、−酸化炭素及び炭化水素を同時に除去
する排気ガス浄化触媒を提供することを目的とする。Therefore, the present invention solves the problems of the prior art as described above, and provides an exhaust gas purification catalyst that simultaneously removes nitrogen oxides, carbon oxides, and hydrocarbons from exhaust gas discharged from internal combustion engines of automobiles, etc. The purpose is to provide
〔課題を解決するための手段]
本発明に従えば、先ず、組成式(r):Mn(Tt、、
5Lb−no+qz) + 16HzO(r )(式中
、Mはナトリウムまたはカリウムイオンを表し、n〈2
7である)で示される結晶性のチタノシリケートに白金
、銅及びコバルトの中から選ばれた少なくとも一種の金
属を担持せしめてなる、主として排気ガス中の窒素酸化
物を除去する触媒が提供される。[Means for Solving the Problems] According to the present invention, first, compositional formula (r): Mn(Tt, ,
5Lb-no+qz) + 16HzO(r) (where M represents sodium or potassium ion, and n<2
There is provided a catalyst which mainly removes nitrogen oxides from exhaust gas, which is made by supporting at least one metal selected from platinum, copper and cobalt on the crystalline titanosilicate shown in item 7). Ru.
本発明に係る排気ガス浄化触媒は、前述の如く、公知の
ゼオライト(アルミノシリケート ZSM−5モービル
オイル社製)とは異なり、チタン原子をシリケート骨格
中に組み込んだ構造を有する前記組成式(1)で表され
る結晶性物質にPt、Cu及び/又はCoを担持させて
なる触媒である。As mentioned above, the exhaust gas purification catalyst according to the present invention differs from the known zeolite (aluminosilicate ZSM-5 manufactured by Mobil Oil Co., Ltd.) in that it has the composition formula (1) having a structure in which titanium atoms are incorporated into the silicate skeleton. This is a catalyst made by supporting Pt, Cu and/or Co on a crystalline substance represented by:
結晶性のチタノシリケート触媒にPt、Cu及び/又は
COを担持させる方法としては、例えば金属塩水溶液中
に鉄シリケートを混入、攪拌する通常のイオン交換法を
あげることができる。An example of a method for supporting Pt, Cu and/or CO on a crystalline titanosilicate catalyst is the usual ion exchange method in which iron silicate is mixed into an aqueous metal salt solution and stirred.
前記組成式(I)で表される結晶性のチタノシリケート
触媒は、所定のケイ酸塩である水ガラスとチタンイオン
等とを水熱合成することにより容易に得ることができる
。このチタノシリケート中のS i / T i原子比
は15以上であることが好ましく、更に好ましくは25
〜100である。また担持するPt、Cu及び/又はC
oはチタノシリケート重量当り1.0重量%以上である
のが好ましく、2〜7重量%であるのが更に好ましい。The crystalline titanosilicate catalyst represented by the compositional formula (I) can be easily obtained by hydrothermally synthesizing water glass, which is a predetermined silicate, and titanium ions. The S i /T i atomic ratio in this titanosilicate is preferably 15 or more, more preferably 25
~100. Also supported Pt, Cu and/or C
o is preferably 1.0% by weight or more, more preferably 2 to 7% by weight, based on the weight of titanosilicate.
本発明によれば、炭化水素と窒素酸化物とを含有する酸
化性排気ガスを前記浄化触媒と接触させることによって
酸化性排気ガス中の窒素酸化物を浄化することができる
。According to the present invention, nitrogen oxides in the oxidizing exhaust gas can be purified by bringing the oxidizing exhaust gas containing hydrocarbons and nitrogen oxides into contact with the purification catalyst.
ここで「酸化性排気ガスJとは、排気ガス中に含まれる
一酸化炭素、水素及び炭化水素等の還元性物質を完全に
酸化して水と炭酸ガスに変換するに必要な酸素量よりも
過剰な量の酸素が含まれている排気ガスをいい、例えば
、自動車等の内燃機関から排出される排気ガスの場合に
は、空燃費(A/F)が大きい状態(燃料のリーン領域
)で排出される排気ガスである。Here, ``Oxidizing exhaust gas J'' refers to the amount of oxygen that is greater than the amount of oxygen required to completely oxidize reducing substances such as carbon monoxide, hydrogen, and hydrocarbons contained in exhaust gas and convert them into water and carbon dioxide gas. Refers to exhaust gas that contains an excessive amount of oxygen. For example, in the case of exhaust gas emitted from internal combustion engines such as automobiles, it is the case when the air/fuel ratio (A/F) is high (fuel lean region). This is exhaust gas that is emitted.
本発明に係る前記金属担持チタノシリケート触媒は、排
気ガス中の炭化水素と酸素との反応よりも炭化水素と窒
素酸化物との反応を優先的に促進させて窒素酸化物を浄
化する。従って、排気ガス中の炭化水素と窒素酸化物と
を浄化することができる。The metal-supported titanosilicate catalyst according to the present invention purifies nitrogen oxides by promoting the reaction between hydrocarbons and nitrogen oxides more preferentially than the reaction between hydrocarbons and oxygen in exhaust gas. Therefore, hydrocarbons and nitrogen oxides in the exhaust gas can be purified.
浄化される排気ガス中に存在する炭化水素としては、通
常の排気ガス中に残存する炭化水素でよいが、前記の窒
素酸化物と炭化水素との反応をおこなうのに不十分な場
合には、外部より炭化水素を補充すればよい。炭化水素
の必要量としては、100〜10,000ppm (
CHaに換算した場合の濃度として)の範囲が好ましい
。The hydrocarbons present in the exhaust gas to be purified may be the hydrocarbons remaining in normal exhaust gas, but if the hydrocarbons are insufficient to carry out the reaction between the nitrogen oxides and the hydrocarbons, Hydrocarbons can be replenished from the outside. The required amount of hydrocarbons is 100 to 10,000 ppm (
(as the concentration when converted to CHa) is preferable.
本発明に係る浄化方法は、通常、反応器内に前記金属担
持チタノシリケート触媒を配置し、その反応器内に排気
ガスを導入して金属担持チタノシリケート触媒と排気ガ
スとを接触させて窒素酸化物を還元浄化し、その後浄化
された排気ガスを反応器より排出させることにより実施
する。また、本発明の浄化方法において公知の浄化触媒
と併用することにより、さらに浄化効果を高めることも
できる。The purification method according to the present invention usually involves arranging the metal-supported titanosilicate catalyst in a reactor and introducing exhaust gas into the reactor to bring the metal-supported titanosilicate catalyst into contact with the exhaust gas. This is carried out by reducing and purifying nitrogen oxides and then discharging the purified exhaust gas from the reactor. Further, in the purification method of the present invention, the purification effect can be further enhanced by using a known purification catalyst together.
本発明において、浄化時の触媒層の反応温度としては、
耐久性及び触媒の活性の点から、200〜800 ’C
の範囲の温度が望ましい。この触媒層の温度が800°
Cを超えると触媒の耐久性が低下するおそれがあるため
好ましくない。また、200°C未満であると浄化が不
十分となり好ましくない。また本発明に係る浄化方法に
おいて、排気ガスを触媒層に導入する空間速度(SV)
には特に制限はないが、例えば、1.000〜500.
000/時間の範囲が活性を維持するために望ましい。In the present invention, the reaction temperature of the catalyst layer during purification is as follows:
From the viewpoint of durability and catalytic activity, 200-800'C
A temperature in the range of . The temperature of this catalyst layer is 800°
If it exceeds C, the durability of the catalyst may deteriorate, which is not preferable. Further, if the temperature is less than 200°C, purification will be insufficient, which is not preferable. In addition, in the purification method according to the present invention, the space velocity (SV) at which exhaust gas is introduced into the catalyst layer
There is no particular limit to the value, for example, 1.000 to 500.
A range of 0.000/hour is desirable to maintain activity.
本発明に係る前記した特定の金属(即ちPt、Cu及び
/又はCo)を含有する担持チタノシリケート触媒は、
シリケート骨格中にチタン原子を組み込んだ結晶性の構
造を有しているため、前記特定の金属をアルミナに担持
したものやチタンをシリケートにイオン交換で担持して
形成したものに比較して、窒素酸化物の浄化に優れた性
能を有している。The supported titanosilicate catalyst containing the above-described specific metal (i.e., Pt, Cu and/or Co) according to the present invention is
Because it has a crystalline structure with titanium atoms incorporated in the silicate skeleton, compared to those formed by supporting the above-mentioned specific metal on alumina or supporting titanium on silicate by ion exchange, it has a lower nitrogen content. It has excellent performance in purifying oxides.
この金属担持チタノシリケート触媒に、少なくとも炭化
水素と窒素酸化物とを含む酸化性排気ガスを接触させる
と、排気ガス中の窒素酸化物を高能率で窒素ガスに還元
して排気ガスを浄化することができる。When this metal-supported titanosilicate catalyst is brought into contact with oxidizing exhaust gas containing at least hydrocarbons and nitrogen oxides, the nitrogen oxides in the exhaust gas are reduced to nitrogen gas with high efficiency and the exhaust gas is purified. be able to.
また、この金属担持チタノシリケート触媒は、600°
Cで5時間加熱する耐久試験後においても排気ガスの浄
化性能を有し、通常の排気ガス用触媒として使用するこ
とができる。In addition, this metal-supported titanosilicate catalyst
Even after a durability test of heating with C for 5 hours, it still has exhaust gas purification performance and can be used as a normal exhaust gas catalyst.
本発明に係る排気ガスの浄化方法は、前記した特定の金
属担持チタノシリケート触媒を炭化水素と窒素酸化物と
を含有する酸化性排気ガスと接触させて窒素酸化物を浄
化する。この酸化性排気ガスは、−酸化炭素、水素及び
炭化水素等の還元性物質を完全に酸化して水と炭酸ガス
に変換するに必要な酸素量よりも過剰な量の酸素が含ま
れた状態である。The method for purifying exhaust gas according to the present invention purifies nitrogen oxides by bringing the specific metal-supported titanosilicate catalyst described above into contact with oxidizing exhaust gas containing hydrocarbons and nitrogen oxides. This oxidizing exhaust gas - contains an amount of oxygen in excess of that required to completely oxidize reducing substances such as carbon oxides, hydrogen and hydrocarbons, converting them into water and carbon dioxide. It is.
本発明に係るPt5Cu及び/又はCo担持チタタノシ
リケート触媒は、炭化水素と酸素との反応に優先して炭
化水素と窒素酸化物とを反応させ、窒素酸化物を還元し
て窒素ガスとする。その後炭化水素が酸素と反応して炭
酸ガスに転化する。かくして酸化性排気ガス中の窒素酸
化物を浄化することができる。The Pt5Cu and/or Co-supported titanosilicate catalyst according to the present invention reacts hydrocarbons and nitrogen oxides preferentially to the reaction between hydrocarbons and oxygen, and reduces the nitrogen oxides to produce nitrogen gas. The hydrocarbons then react with oxygen and are converted to carbon dioxide. In this way, nitrogen oxides in the oxidizing exhaust gas can be purified.
以下実施例により本発明を具体的に説明するが、本発明
を以下の実施例に限定するものでないことはいうまでも
ない。EXAMPLES The present invention will be specifically explained below with reference to Examples, but it goes without saying that the present invention is not limited to the following Examples.
髭よ
〔触媒の調製〕
S i / T iの原子比が25のpt担持チタノシ
リケート触媒を、以下のようにして調製した。Beard [Catalyst Preparation] A pt-supported titanosilicate catalyst having an atomic ratio of S i /T i of 25 was prepared as follows.
A液:硫酸チタン(IV)
(Ti (SOa) z・4HJ ) 3.3
9 gHzO85,Og
B液:水ガラス
(Si(h 35〜38重量%) 50.0g
HzO50,Og
C液:硫酸(〉85重量%) 15.Og
D液:テトラプロピルアンモニウムヒドロキサイド((
C3H?)、NOF! (20〜25重量%))30.
0 g
の4種の溶液を調製した。A liquid: Titanium sulfate (IV) (Ti (SOa) z・4HJ) 3.3
9 gHzO85, Og Liquid B: Water glass (Si (h 35-38% by weight) 50.0g
HzO50, Og Solution C: Sulfuric acid (>85% by weight) 15. Og
Solution D: Tetrapropylammonium hydroxide ((
C3H? ), NOF! (20-25% by weight))30.
Four solutions of 0 g were prepared.
前記A液を200−のビーカーに入れ、室温下でpHを
2.5〜3.5に保ち、激しく攪拌しながら、B液及び
C液を滴下して混合した。この混合液にD液を混入し約
3時間攪拌し、得られた混合液をオートクレーブに移し
、攪拌をおこなわずに、1°C/分の昇温速度で180
°Cまで加熱昇温させ、その後0.25°C/分の昇温
速度で210°Cまで加熱昇温させた後、210°Cで
60時間保持した。冷却後、生成物を洗浄し、120℃
で乾燥した。次いで、窒素流通下550″Cで15時間
焼成した後、空気流通下550°Cで5時間焼成した。The above-mentioned solution A was placed in a 200-mm beaker, the pH was maintained at 2.5 to 3.5 at room temperature, and solutions B and C were added dropwise and mixed while stirring vigorously. Solution D was mixed into this mixed solution and stirred for about 3 hours, and the resulting mixed solution was transferred to an autoclave and heated to 180 °C at a heating rate of 1°C/min without stirring.
The temperature was raised to 210°C by heating at a heating rate of 0.25°C/min, and then held at 210°C for 60 hours. After cooling, the product was washed and heated to 120°C.
It was dried. Next, it was fired at 550°C under nitrogen flow for 15 hours, and then at 550°C under air flow for 5 hours.
続いてこの焼成体を濃度INのNLNO:+溶液に3時
間浸漬して、アンモニウム型に変換した。その後、室温
で水洗した後、100°Cで乾燥し、さらに空気中50
0″Cで1時間焼成してチタノシリケートを得た。チタ
ンの含有量は2.74重量%であった。Subsequently, this fired body was immersed in an NLNO:+ solution at a concentration of IN for 3 hours to convert it into an ammonium type. After that, after washing with water at room temperature, drying at 100°C, and then 50°C in air.
A titanosilicate was obtained by firing at 0''C for 1 hour.The content of titanium was 2.74% by weight.
このアンモニウム型チタノシリケートを0.2M/lの
Ptアミン水溶液に3時間浸漬してPtイオン交換した
後、室温で水洗し、100°Cで乾燥し、さらに空気中
で350°Cで3時間焼成してPt1B持チタノシリケ
ート触媒Aを得た。This ammonium type titanosilicate was immersed in a 0.2 M/l Pt amine aqueous solution for 3 hours to exchange Pt ions, washed with water at room temperature, dried at 100°C, and then heated in air at 350°C for 3 hours. The Pt1B-bearing titanosilicate catalyst A was obtained by firing.
イオン交換については、pHが高く、水溶液温度も高い
方が交換量が向上する。Regarding ion exchange, the higher the pH and the higher the temperature of the aqueous solution, the higher the amount of exchange.
上で得たPt担持チタノシリケート触媒のPt含有量は
7.44重量%であった。The Pt content of the Pt-supported titanosilicate catalyst obtained above was 7.44% by weight.
比較用触媒として、活性アルミナに1.2重量%Ptを
担持した触媒B及び前記の方法で調製したアンモニウム
型チタ7ノシリケート触媒Cを用いた。As comparative catalysts, catalyst B in which 1.2% by weight of Pt was supported on activated alumina and ammonium type titanosilicate catalyst C prepared by the method described above were used.
上で得たpt担担持チタノシリケート触媒色比較用触媒
B及びCとの触媒性能を比較した。Catalyst performance was compared with the pt-supported titanosilicate catalyst color comparison catalysts B and C obtained above.
それぞれフレッシュおよび600°Cで5時間耐久試験
後、自動車の排気ガスを模擬した下記組成並びに条件の
ガスと接触させて浄化性能を比較した。After a fresh and 5-hour durability test at 600°C, the purification performance was compared by contacting with a gas having the composition and conditions shown below, which simulates automobile exhaust gas.
ガス組成:
HC(炭化水素):0.08%、co:o、i1%、0
2:4.30%、NO:0.10%、N2:o、03%
、C02:11.9%、N20:2.3%、N2 :
8t、2%、SV(触媒層へのガスを導入する空間速度
):420.000/時間、
触媒層の温度:250°C1300°C及び400°C
に於ける初期浄化率を表1に示し、耐久試験後の浄化率
を表2に示す。Gas composition: HC (hydrocarbon): 0.08%, co: o, i1%, 0
2:4.30%, NO:0.10%, N2:o, 03%
, C02: 11.9%, N20: 2.3%, N2:
8t, 2%, SV (space velocity for introducing gas into the catalyst layer): 420,000/hour, temperature of the catalyst layer: 250°C, 1300°C and 400°C
Table 1 shows the initial purification rate in the test, and Table 2 shows the purification rate after the durability test.
表1及び2に示したように、本発明に係る触媒Aは比較
例触媒B及びCに比べて数倍から士数倍の窒素酸化物を
浄化を示した。また炭化水素及び−酸化炭素の浄化性能
においても優れていた。As shown in Tables 1 and 2, Catalyst A according to the present invention purified nitrogen oxides several times to several times as much as Comparative Example Catalysts B and C. It was also excellent in purifying performance for hydrocarbons and carbon oxides.
以下余白
1 亘゛ ° %
貫I
〔触媒の調製]
Si/Tiの原子比が25のCu担持チタノシリケート
触媒を、以下のようにして調製した。The following margin is 1 ゛ ° % (I) [Catalyst Preparation] A Cu-supported titanosilicate catalyst having an Si/Ti atomic ratio of 25 was prepared as follows.
例1の方法で調製したアンモニウム型チタノシリケート
を0.2M#2酢酸銅水溶液に3時間浸漬してCuイオ
ン交換した後、室温で水洗し、100°Cで乾燥し、さ
らに空気中で350°Cで3時間焼成してCu担持チタ
ノシリケート触媒りを得た。The ammonium-type titanosilicate prepared by the method of Example 1 was immersed in a 0.2M #2 copper acetate aqueous solution for 3 hours to exchange Cu ions, washed with water at room temperature, dried at 100°C, and further heated in air for 350°C. It was calcined at °C for 3 hours to obtain a Cu-supported titanosilicate catalyst.
酢酸銅によるCuイオン交換については、pHが高く、
水溶液温度も高い方が交換量が向上する。For Cu ion exchange with copper acetate, the pH is high;
The higher the temperature of the aqueous solution, the better the exchange rate.
上で得たCu担持チタノシリケート触媒のCυ含有量は
3.64重量%であった。The Cυ content of the Cu-supported titanosilicate catalyst obtained above was 3.64% by weight.
比較用触媒として、活性アルミナに1.2重量%Cuを
担持した触媒E及び前記の方法で調製したアンモニウム
型チタノシリケート触媒Fを用いた。As comparative catalysts, Catalyst E in which 1.2% by weight of Cu was supported on activated alumina and Ammonium titanosilicate Catalyst F prepared by the method described above were used.
[浄化性能評価〕
前記で得たCu担持チタノシリケート触媒りと比較用触
媒E及びFとの触媒性能を比較した。[Evaluation of purification performance] The catalytic performance of the Cu-supported titanosilicate catalyst obtained above and comparative catalysts E and F were compared.
それぞれフレッシュおよび600’Cで5時間耐久試験
後、自動車の排気ガスを模擬した下記組成並びに条件の
ガスに接触させて浄化性能を比較した。After a fresh and 5-hour durability test at 600'C, each sample was brought into contact with a gas having the following composition and conditions that simulated automobile exhaust gas, and the purification performance was compared.
ガス組成:
HC(炭化水素):o、o8%、co:o、i1%、0
□: 4.30%、NO:0.10%、H2:0.03
%、COx : 11.9%、H2O:2.3%、Nz
:81.2%、SV(触媒層へのガスを導入する空間速
度)=420.000/時間、
触媒層の温度=400°C1500°C及び600°C
に於ける初期浄化率を表3に示し、耐久試験後の浄化率
を表4に示す。Gas composition: HC (hydrocarbon): o, o8%, co: o, i1%, 0
□: 4.30%, NO: 0.10%, H2: 0.03
%, COx: 11.9%, H2O: 2.3%, Nz
:81.2%, SV (space velocity for introducing gas into the catalyst layer) = 420,000/hour, temperature of the catalyst layer = 400°C, 1500°C and 600°C
Table 3 shows the initial purification rate, and Table 4 shows the purification rate after the durability test.
表3及び4に示したように、本発明に係る触媒りは比較
例触媒E及びFに比べて数倍から十数倍の窒素酸化物を
浄化を示した。また炭化水素及び−酸化炭素の浄化性能
においても優れていた。更に、貴金属担持チタノチリケ
ート触媒よりも高温側での性能向上が認められた。As shown in Tables 3 and 4, the catalyst according to the present invention purified nitrogen oxides several times to more than ten times as much as Comparative Example Catalysts E and F. It was also excellent in purifying performance for hydrocarbons and carbon oxides. Furthermore, improved performance at high temperatures was observed compared to the noble metal-supported titanosilicate catalyst.
以下余白
倒」−
〔触媒の調製〕
Si/Tiの原子比が25のCo担持チタノシリケート
触媒を、以下のようにして調製した。The following blanks are left out. [Preparation of Catalyst] A Co-supported titanosilicate catalyst having an Si/Ti atomic ratio of 25 was prepared as follows.
例1の方法で調製したアンモニウム型チタノシリケート
を0.2M#!酢酸コバルト水溶液に3時間浸漬してC
oイオン交換した後、室温で水洗し、100°Cで乾燥
し、更に空気中で350°Cで3時間焼成してCO担持
チタノシリケート触媒Gを得た。Ammonium type titanosilicate prepared by the method of Example 1 was added to 0.2M#! C by immersion in cobalt acetate aqueous solution for 3 hours
After ion exchange, the product was washed with water at room temperature, dried at 100°C, and further calcined in air at 350°C for 3 hours to obtain CO-supported titanosilicate catalyst G.
上で得たCo担持チタノシリケート触媒のCO含有量は
3.2重量%であった。The CO content of the Co-supported titanosilicate catalyst obtained above was 3.2% by weight.
比較用触媒として、前記の方法で調製したアンモニウム
型チタノシリケート触媒Hを用いた。As a comparative catalyst, ammonium titanosilicate catalyst H prepared by the method described above was used.
前記で得たCo担担持チタノシリケート触媒色比較用触
媒Hとの触媒性能を比較した。The catalyst performance was compared with the Co-supported titanosilicate catalyst color comparison catalyst H obtained above.
それぞれフレッシュ及び600°Cで5時間耐久試験後
、自動車の排気ガスを模擬した下記組成並びに条件のガ
スに接触させて浄化性能を比較した。After a fresh and 5-hour durability test at 600°C, the samples were brought into contact with a gas having the composition and conditions shown below, which simulates automobile exhaust gas, and their purification performance was compared.
ガス組成:
HC:C炭化水素):0.08%、Co:0.11%、
ORr4.30%、NO:0.10%、H,:0.03
%、CO□ : 11.9%、H,0:2.3%、N、
:81.2%、SV(触媒層へのガスを導入する空
間速度):420.000/時間、
触媒層の温度:500°C1600°C及び700°C
に於ける初期浄化率を表5に示し、耐久試験後の浄化率
を表6に示す。Gas composition: HC:C hydrocarbon): 0.08%, Co: 0.11%,
ORr4.30%, NO:0.10%, H:0.03
%, CO□: 11.9%, H, 0: 2.3%, N,
: 81.2%, SV (space velocity for introducing gas into the catalyst layer): 420,000/hour, Temperature of the catalyst layer: 500°C, 1600°C and 700°C
Table 5 shows the initial purification rate in the test, and Table 6 shows the purification rate after the durability test.
表5及び6に示したように、本発明に係る触媒Gは比較
例触媒Hに比べて数倍から士数倍の窒素酸化物を浄化を
示した。また炭化水素及び−酸化炭素の浄化性能におい
ても優れていた。更に、貴金属担持チタノシリケート触
媒よりも高温側での性能向上が認められた。As shown in Tables 5 and 6, Catalyst G according to the present invention purified nitrogen oxides several times to several times as much as Comparative Example Catalyst H. It was also excellent in purifying performance for hydrocarbons and carbon oxides. Furthermore, improved performance at high temperatures was observed compared to the noble metal-supported titanosilicate catalyst.
以下余白
〔発明の効果〕
以下説明したように、本発明によれば、前記した特定の
組成を有する結晶性チタノシリケートにPt、Cu及び
/又はCoを担持した触媒を用いることによって、酸素
過剰雰囲気下において排気ガス中の炭化水素、−酸化炭
素及び窒素酸化物を同時に除去でき、また600°CX
5時間の耐久試験後においても実用的に受は入れること
のできる浄化性能を有する。Blank space below [Effects of the Invention] As explained below, according to the present invention, by using a catalyst in which Pt, Cu and/or Co is supported on crystalline titanosilicate having the above-mentioned specific composition, oxygen excess can be achieved. Hydrocarbons, carbon oxides, and nitrogen oxides in exhaust gas can be removed simultaneously in an atmosphere, and even at 600°C
Even after a 5-hour durability test, it has a purification performance that is practically acceptable.
本発明に係るPt、Cu及び/又はCo担持チタノシリ
ケート触媒は、粒状、ペレット状、ハニカム状等その浄
化時の構造は問わない。The Pt, Cu and/or Co-supported titanosilicate catalyst according to the present invention may have any structure during purification, such as granular, pellet, or honeycomb shapes.
なお、自動車等の内燃機関のみならず、硝酸製造工場、
各種燃焼設備などの窒素酸化物を含有する排気ガスの浄
化に利用することができる。In addition to internal combustion engines such as automobiles, nitric acid manufacturing plants,
It can be used to purify exhaust gas containing nitrogen oxides from various combustion equipment.
Claims (1)
)・16H_2O( I )(式中、Mはナトリウムまた
はカリウムイオンを表し、n<27である)で示される
結晶性チタノシリケートに白金、銅及びコバルトの中か
ら選ばれた少なくとも一種の金属を担持せしめてなるこ
とを特徴とする、主として排気ガス中の窒素酸化物を除
去する排気ガス浄化触媒。[Claims] 1. Composition formula: M_n(Ti_nSi_9_6_-_nO_1_9_2
)・16H_2O(I) (wherein M represents a sodium or potassium ion, and n<27) is added with at least one metal selected from platinum, copper, and cobalt. An exhaust gas purification catalyst that mainly removes nitrogen oxides from exhaust gas, characterized by being supported on the catalyst.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2321296A JPH04193348A (en) | 1990-11-27 | 1990-11-27 | Catalyst for purification of exhaust gas |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2321296A JPH04193348A (en) | 1990-11-27 | 1990-11-27 | Catalyst for purification of exhaust gas |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH04193348A true JPH04193348A (en) | 1992-07-13 |
Family
ID=18130992
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP2321296A Pending JPH04193348A (en) | 1990-11-27 | 1990-11-27 | Catalyst for purification of exhaust gas |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH04193348A (en) |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN108722477A (en) * | 2018-06-06 | 2018-11-02 | 中国科学院过程工程研究所 | A kind of alkali resistant poisoning high-efficiency denitration catalyst and its preparation method and application |
| JP2024545017A (en) * | 2021-12-20 | 2024-12-05 | ジョンソン、マッセイ、パブリック、リミテッド、カンパニー | Catalytic materials for treating exhaust gases produced by natural gas engines |
-
1990
- 1990-11-27 JP JP2321296A patent/JPH04193348A/en active Pending
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN108722477A (en) * | 2018-06-06 | 2018-11-02 | 中国科学院过程工程研究所 | A kind of alkali resistant poisoning high-efficiency denitration catalyst and its preparation method and application |
| JP2024545017A (en) * | 2021-12-20 | 2024-12-05 | ジョンソン、マッセイ、パブリック、リミテッド、カンパニー | Catalytic materials for treating exhaust gases produced by natural gas engines |
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