JP3154602B2 - Exhaust gas purification method - Google Patents
Exhaust gas purification methodInfo
- Publication number
- JP3154602B2 JP3154602B2 JP26609693A JP26609693A JP3154602B2 JP 3154602 B2 JP3154602 B2 JP 3154602B2 JP 26609693 A JP26609693 A JP 26609693A JP 26609693 A JP26609693 A JP 26609693A JP 3154602 B2 JP3154602 B2 JP 3154602B2
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- JP
- Japan
- Prior art keywords
- exhaust gas
- catalyst
- group
- gasoline
- kerosene
- Prior art date
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- Exhaust Gas Treatment By Means Of Catalyst (AREA)
- Catalysts (AREA)
- Industrial Gases (AREA)
Description
【0001】[0001]
【産業上の利用分野】本発明は窒素酸化物(以下、NO
xと略す)、一酸化炭素(CO)、炭化水素(以下、H
Cと略す)を含有する排気ガスを浄化する方法に関す
る。The present invention relates to a nitrogen oxide (hereinafter referred to as NO
x), carbon monoxide (CO), hydrocarbons (hereinafter H
C) (hereinafter abbreviated as C).
【0002】[0002]
【従来の技術】自動車等の排ガス処理においては、排ガ
ス中のCO、HCを利用して触媒を用いて理論空燃比付
近の極めて狭い範囲でNOxを浄化しているのが一般的
である。しかし、リーンバーンガソリンエンジン又はデ
ィーゼルエンジンの排ガス処理においては、排ガス中に
酸素が過剰に存在するため、これまでの触媒では全く脱
硝作用を示さない。最近、酸素過剰雰囲気でNOxを浄
化できる触媒として、コバルト又は銅を含有した結晶性
シリケート触媒が高性能を有する触媒として脚光をあび
ている。しかし、これらの触媒は反応初期においては十
分な性能を有するが熱や排ガス中のスチーム、SO2 に
よる触媒劣化が問題点として生じている。2. Description of the Related Art In the treatment of exhaust gas from automobiles and the like, it is general to purify NOx in a very narrow range near the stoichiometric air-fuel ratio using a catalyst by utilizing CO and HC in the exhaust gas. However, in the exhaust gas treatment of a lean burn gasoline engine or a diesel engine, since the exhaust gas contains excessive oxygen, the conventional catalysts do not show any denitration action. Recently, as a catalyst capable of purifying NOx in an oxygen-excess atmosphere, a crystalline silicate catalyst containing cobalt or copper has been spotlighted as a catalyst having high performance. However, these catalysts have a sufficient performance in the early stage of the reaction, but the deterioration of the catalyst due to heat, steam in the exhaust gas, or SO 2 has occurred as a problem.
【0003】これまで、本発明者らは上記不具合を克服
する触媒を鋭意検討してきたところ、イリジウムを担持
した触媒が、耐久性を有する高活性な触媒であることを
見い出している(特願平5−26369、特願平5−1
00698、特願平5−228382など参照)。ただ
し、ディーゼルエンジンから排出されるNOxを浄化す
る場合、排ガス中のHC濃度が薄いため、これらの触媒
を用いても十分な脱硝率を得るには至っていない。The inventors of the present invention have intensively studied catalysts that can overcome the above-mentioned problems, and have found that iridium-supported catalysts are highly durable and highly active catalysts (Japanese Patent Application No. Hei 10-26139). 5-26369, Japanese Patent Application 5-1
00698, Japanese Patent Application No. 5-228382, etc.). However, when purifying NOx exhausted from a diesel engine, a sufficient denitration rate has not yet been obtained even with the use of these catalysts because the HC concentration in the exhaust gas is low.
【0004】[0004]
【発明が解決しようとする課題】そこで、本発明者ら
は、上記問題点を克服するため、燃料として用いる軽
油、灯油及びガソリンを添加し、排ガス中の炭化水素濃
度を高め効率的に脱硝を行う方法を見い出した。さらに
好ましくは添加する燃料を熱分解又は触媒分解により触
媒が有効に作用するオレフィン又は芳香族類を多く含有
する炭化水素に変換したものを添加することにより、よ
り高効率にて脱硝を行うことを見い出した。Therefore, in order to overcome the above-mentioned problems, the present inventors have added light oil, kerosene and gasoline used as fuel to increase the hydrocarbon concentration in the exhaust gas and efficiently perform denitration. I found a way to do it. More preferably, denitration is performed with higher efficiency by adding the fuel to be added to a hydrocarbon containing a large amount of olefins or aromatics in which the catalyst effectively acts by thermal cracking or catalytic cracking. I found it.
【0005】本発明は上記知見によって完成されたもの
であって、本発明は次の第1〜第3発明を含むものであ
る。 (1)窒素酸化物、一酸化炭素及び炭化水素を含有する
排気ガス中の窒素酸化物を還元物とともに触媒に接触さ
せて窒素酸化物を窒素に還元する方法において、前記触
媒が一般式 (1±0.8)R2 O・(aM2 O3 ・bM′O・cAl2 O3 )・ySiO2 (但し、上記式中、Rはアルカリ金属イオン及び/又は
水素イオン、MはVIII族元素、希土類元素、チタン、バ
ナジウム、クロム、ニオブ、アンチモン及びガリウムよ
りなる群から選ばれた少なくとも1種以上の元素イオ
ン、M′はマグネシウム、カルシウム、ストロンチウ
ム、バリウムのアルカリ土類金属イオン、a≧0、20
>b>0、a+c=1、3000>y>11)なる化学
式を有し、表Aに示すX線回折パターンを有する結晶性
シリケートよりなる担体に活性金属としてイリジウムを
担持したイリジウム触媒であり、前記還元物が灯油、軽
油及びガソリンよりなる群から選ばれた1種以上の炭化
水素系燃料油であることを特徴とする排気ガスの浄化方
法。(第1発明)The present invention has been completed based on the above findings, and the present invention includes the following first to third inventions. (1) A method for reducing nitrogen oxides into nitrogen by bringing the nitrogen oxides in the exhaust gas containing nitrogen oxides, carbon monoxide and hydrocarbons into contact with a catalyst together with a reductant, wherein the catalyst has the general formula (1) ± 0.8) R 2 O. (aM 2 O 3 .bM'O.cAl 2 O 3 ) .ySiO 2 (where R is an alkali metal ion and / or hydrogen ion, and M is a group VIII element , A rare earth element, at least one element ion selected from the group consisting of titanium, vanadium, chromium, niobium, antimony and gallium, M 'is an alkaline earth metal ion of magnesium, calcium, strontium, barium, a ≧ 0 , 20
>B> 0 , a + c = 1, 3000>y> 11) is an iridium catalyst in which iridium is supported as an active metal on a support made of a crystalline silicate having an X-ray diffraction pattern shown in Table A, A method for purifying exhaust gas, wherein the reduced product is at least one hydrocarbon fuel oil selected from the group consisting of kerosene, light oil and gasoline. (First invention)
【0006】(2)前記還元物が灯油、軽油及びガソリ
ンよりなる群より選ばれた1種以上の炭化水素系燃料油
を熱分解してなるオレフィン類、芳香族炭化水素に富む
ガスであることを特徴とする上記(1)の排気ガスの浄
化方法。(第2発明) (3)前記還元物が灯油、軽油及びガソリンよりなる群
より選ばれた1種以上の炭化水素系燃料油を触媒分解し
てなるオレフィン類、芳香族炭化水素に富むガスである
ことを特徴とする上記(1)の排気ガスの浄化方法。
(第3発明) (2) The reduced product is kerosene, light oil or gasoline
At least one hydrocarbon fuel oil selected from the group consisting of
Rich in olefins and aromatic hydrocarbons obtained by thermal decomposition of
The exhaust gas purifying apparatus of (1), which is a gas.
Method. (2nd invention) (3) A group in which the reductant comprises kerosene, light oil and gasoline
Catalytically decomposes one or more hydrocarbon fuel oils selected from
Is a gas rich in olefins and aromatic hydrocarbons
(1) The method for purifying exhaust gas according to the above (1).
(Third invention)
【0007】第1発明における結晶性シリケートは下記
表Aに示すX線回折パターンを有する。 The crystalline silicate according to the first invention is as follows:
It has the X-ray diffraction pattern shown in Table A.
【0008】[0008]
【表2】 [Table 2]
【0009】第1発明における結晶性シリケートにイリ
ジウムを担持する方法としては、該結晶性シリケートを
イリジウム塩溶液に浸漬し、イオン交換法又は含浸法に
よって担持することができる。担持するイリジウムは
0.002wt%以上で十分に活性が発現し、好ましく
は0.02wt%以上で高い活性を有する。 In the first invention, the crystalline silicate is
As a method for supporting the indium, the crystalline silicate
Immersion in iridium salt solution, ion exchange method or impregnation method
Therefore, it can be carried. The supported iridium is
At 0.002 wt% or more, sufficient activity is exhibited, and
Has high activity at 0.02 wt% or more.
【0010】第2発明における灯油、軽油及びガソリン
よりなる群より選ばれた1種以上の炭化水素燃料油の熱
分解法は、これらの炭化水素燃料油を約800℃に保っ
た管式加熱炉に0.6〜1.3秒の滞留時間にて供給す
ることによって行うことができる。また、還元性雰囲気
となるため、不活性な反応管、例えば石英管を用いるこ
とが好ましい。この際、コーク類の副生を防ぐため、ス
チームを同時に供給することもできる。[0010] In the second invention , the method for pyrolyzing one or more hydrocarbon fuel oils selected from the group consisting of kerosene, light oil and gasoline comprises a tubular heating furnace in which these hydrocarbon fuel oils are maintained at about 800 ° C. At a residence time of 0.6 to 1.3 seconds. In addition, since the atmosphere becomes a reducing atmosphere, it is preferable to use an inert reaction tube, for example, a quartz tube. At this time, steam can be supplied at the same time to prevent by-products of coke.
【0011】第3発明における上記炭化水素燃料油の触
媒分解法は、触媒としてGa又はZnを各々0.1〜3
0wt%担持した結晶性シリケートを用いて、滞留時間
としてLHSV:1h-1、温度:約500℃の条件で行
うことができる。In the third aspect of the present invention, the method for decomposing a hydrocarbon fuel oil may comprise the steps of:
Using a crystalline silicate loaded with 0 wt%, it can be carried out under the conditions of LHSV: 1 h -1 and residence time: about 500 ° C.
【0012】[0012]
【作用】イリジウムを担持した触媒を用いて、NOx、
CO、HCを含有する排ガスを浄化する浄化反応式は下
記のとおりである。Function: Using a catalyst supporting iridium, NOx,
The purification reaction formula for purifying the exhaust gas containing CO and HC is as follows.
【0013】[0013]
【化1】 *1)炭化水素(HC)の例としてC3 H6 を代表とし
て示した。 *2)含酸素炭化水素の例としてCH2 Oを代表として
示した。 上記反応式において、(1)はHCの活性化、(2)は
HCの燃焼、(3)は脱硝反応、(4)はCOの燃焼を
示している。Embedded image * 1) C 3 H 6 is shown as a representative example of hydrocarbon (HC). * 2) CH 2 O is shown as a representative example of the oxygen-containing hydrocarbon. In the above reaction formula, (1) indicates activation of HC, (2) indicates combustion of HC, (3) indicates denitration reaction, and (4) indicates combustion of CO.
【0014】イリジウムを担持した触媒はC2 H4 、C
3 H6 等のオレフィン類及びベンゼン、トルエン等の芳
香族類が効率的に上記CH2 O(含酸素炭化水素)を形
成し、脱硝反応(3)を選択的に進行させる作用を有す
る。そのため、NOxの還元剤として軽油、灯油、ガソ
リンよりなる群より選ばれた1種以上の炭化水素燃料油
をそのまま添加するよりも、オレフィン分や芳香族分が
多い炭化水素に変換して添加する方が効率的に脱硝を行
うことができる。The catalyst supporting iridium is C 2 H 4 , C
Olefins such as 3 H 6 and aromatics such as benzene and toluene efficiently form the above-mentioned CH 2 O (oxygen-containing hydrocarbon), and have a function of selectively proceeding the denitration reaction (3). Therefore, rather than adding one or more hydrocarbon fuel oils selected from the group consisting of light oil, kerosene, and gasoline as a NOx reducing agent, they are converted into hydrocarbons having a high olefin content or aromatic content and added. Denitration can be performed more efficiently.
【0015】[0015]
【実施例】以下に実施例を示し、本発明を具体的に説明
するが、本発明は下記実施例に制限されるものではな
い。 (実施例1) 〇 触媒1の調製 水ガラス1号(SiO2 :30%):5616gを水:
5429gに溶解し、この溶液を溶液Aとする。一方、
水:4175gに硫酸アルミニウム:718.9g、塩
化第二鉄:110g、酢酸カルシウム:47.2g、塩
化ナトリウム:262g、濃塩酸:2020gを溶解
し、この溶液を溶液Bとする。溶液Aと溶液Bを一定割
合で供給し、沈殿を生成させ、十分攪拌してpH=8.
0のスラリを得る。このスラリを20リットルのオート
クレーブに仕込み、さらにテトラプロピルアンモニウム
ブロマイドを500g添加し、160℃にて72時間水
熱合成を行い、合成後水洗して乾燥させ、さらに500
℃、3時間焼成させ結晶性シリケート1を得る。この結
晶性シリケート1は酸化物のモル比で(結晶水を省く)
下記の組成式で表され、結晶構造はX線回折で前記表A
にて表示されるものである。 0.5Na2 O・0.5H2 O〔0.8Al2 O3 ・
0.2Fe2 O3 ・0.25CaO〕・25SiO2 上記結晶性シリケート1を4NのNH4 Cl水溶液40
℃に3時間攪拌してNH4 イオン交換を実施した。イオ
ン交換後洗浄して100℃、24時間乾燥させた後、4
00℃、3時間焼成してH型の結晶性シリケート1を得
た。EXAMPLES The present invention will be described below in detail with reference to Examples, but the present invention is not limited to the following Examples. (Example 1) の Preparation of catalyst 1 Water glass No. 1 (SiO 2 : 30%): 5616 g of water:
The solution was dissolved in 5429 g, and this solution was designated as solution A. on the other hand,
Aluminum sulfate: 718.9 g, ferric chloride: 110 g, calcium acetate: 47.2 g, sodium chloride: 262 g, and concentrated hydrochloric acid: 2020 g are dissolved in water: 4175 g. Solution A and solution B are supplied at a constant rate to form a precipitate, and the mixture is sufficiently stirred to obtain a pH of 8.
Get a slurry of zero. This slurry was charged into a 20-liter autoclave, and 500 g of tetrapropylammonium bromide was further added. Hydrothermal synthesis was performed at 160 ° C. for 72 hours.
C. for 3 hours to obtain crystalline silicate 1. This crystalline silicate 1 has a molar ratio of oxides (the crystallization water is omitted).
The crystal structure is represented by the following composition formula, and the crystal structure is determined by X-ray diffraction.
It is displayed in. 0.5Na 2 O.0.5H 2 O [0.8Al 2 O 3.
0.2Fe 2 O 3 .0.25 CaO] .25 SiO 2 The above crystalline silicate 1 was treated with a 4N NH 4 Cl aqueous solution 40
The mixture was stirred at 3 ° C. for 3 hours to carry out NH 4 ion exchange. After ion exchange washing and drying at 100 ° C. for 24 hours, 4
The resultant was fired at 00 ° C. for 3 hours to obtain H-type crystalline silicate 1.
【0016】〇 触媒化 次に、上記100部のH型の結晶性シリケート1に対し
て、バインダとしてアルミナゾル:3部、シリカゾル:
55部(SiO2 :20%)及び水:200部加え、充
分攪拌を行いウォッシュコート用スラリとした。次にコ
ージェライト用モノリス基材(400セルの格子目)を
上記スラリに浸漬し、取り出した後、余分なスラリを吹
きはらい200℃で乾燥させた。コート量は基材1リッ
トルあたり200g担持し、このコート物をハニカムコ
ート物1とする。次に、塩化イリジウム(IrCl4 ・
H2 O:2.88g/200cc、H2O)に上記ハニ
カムコート物を浸漬し1時間含浸した後、基材の壁の付
着した液をふきとり200℃で乾燥させた。次いで50
0℃で窒素雰囲気で12時間パージ処理を行い、ハニカ
ム触媒1を得た。(2) Catalysis Next, 3 parts of alumina sol and 3 parts of silica sol were used as binders for the above 100 parts of H-type crystalline silicate 1.
55 parts (SiO 2 : 20%) and 200 parts of water were added and sufficiently stirred to obtain a slurry for wash coating. Next, a monolith base material for cordierite (a grid of 400 cells) was immersed in the slurry, taken out, and then sprayed with excess slurry and dried at 200 ° C. The coating amount is 200 g per 1 liter of the base material. Next, iridium chloride (IrCl 4.
H 2 O: 2.88g / 200cc, it was immersed impregnated 1 hour the honeycomb coating material in H 2 O), dried at 200 ° C. wiping the adhered liquid walls of the substrate. Then 50
A purging treatment was performed at 0 ° C. in a nitrogen atmosphere for 12 hours to obtain a honeycomb catalyst 1.
【0017】〇 触媒2〜15の調製 上記ハニカム触媒1の調製での結晶性シリケート1の合
成法において、塩化第二鉄の代わりに塩化コバルト、塩
化ルテニウム、塩化ロジウム、塩化ランタン、塩化セリ
ウム、塩化チタン、塩化バナジウム、塩化クロム、塩化
アンチモン、塩化ガリウム及び塩化ニオブを各々酸化物
換算でFe2 O3 と同じモル数だけ添加した以外は結晶
性シリケート1と同様の操作を繰り返して結晶性シリケ
ート2〜12を調製した。これらの結晶性シリケートの
結晶構造はX線回折で前記表Aに表示されるものであ
り、その組成は酸化物のモル比(脱水された形態)で表
わして0.5NaO2 ・0.5H2 O・(0.2M2 O
3 ・0.8Al2 O3 ・0.25CaO)・25SiO
2 である。ここでMはCo,Ru,Rh,La,Ce,
Ti,V,Cr,Sb,Ga,Nbである。(2) Preparation of Catalysts 2 to 15 In the method for synthesizing the crystalline silicate 1 in the above preparation of the honeycomb catalyst 1, instead of ferric chloride, cobalt chloride, ruthenium chloride, rhodium chloride, lanthanum chloride, cerium chloride, chloride The same operation as that of crystalline silicate 1 was repeated except that titanium, vanadium chloride, chromium chloride, antimony chloride, gallium chloride, and niobium chloride were each added in the same mole number as Fe 2 O 3 in terms of oxide. ~ 12 were prepared. The crystal structures of these crystalline silicates are shown in Table A above by X-ray diffraction, and their compositions are expressed in terms of the molar ratio of oxides (dehydrated form) to 0.5NaO 2 .0.5H 2 O ・ (0.2M 2 O
3・ 0.8Al 2 O 3・ 0.25CaO) ・ 25SiO
2 Where M is Co, Ru, Rh, La, Ce,
Ti, V, Cr, Sb, Ga, Nb.
【0018】さらに、結晶性シリケート1の合成法にお
いて、酢酸カルシウムの代わりに酢酸マグネシウム、酢
酸ストロンチウム、酢酸バリウムを各々酸化物換算でC
aOと同じモル数だけ添加した以外は結晶性シリケート
1と同様の操作を繰り返して結晶性シリケート13〜1
5を調製した。これらの結晶性シリケートの結晶構造は
X線回折で前記表Aに表示されるものであり、その組成
は酸化物のモル比(脱水された形態)で表わして0.5
Na2 O・0.5H2 O・(0.2Fe2 O3・0.8
Al2 O3 ・0.25MeO)・25SiO2 である。
ここでMeはMg,Sr,Baである。Further, in the method for synthesizing the crystalline silicate 1, magnesium acetate, strontium acetate, and barium acetate are used in place of calcium acetate in terms of oxides, respectively.
The same operation as that of the crystalline silicate 1 was repeated except that the same mole number as that of the aO was added, and the crystalline silicates 13 to 1 were added.
5 was prepared. The crystal structures of these crystalline silicates are shown in Table A above by X-ray diffraction, and their compositions are expressed in terms of a molar ratio of oxides (dehydrated form) of 0.5.
Na 2 O · 0.5H 2 O · (0.2Fe 2 O 3 · 0.8
Al 2 O 3 · 0.25MeO) · 25SiO 2 .
Here, Me is Mg, Sr, and Ba.
【0019】上記結晶性シリケート2〜15を用いてハ
ニカム触媒1と同様の方法でH型の結晶性シリケート2
〜15を得、このシリケートをさらにハニカム触媒1の
調製と同様の工程にてコージェライトモノリス基材にコ
ートしてハニカムコート物2〜15を得た。次に塩化イ
リジウム水溶液に浸漬しハニカム触媒1と同様の処理に
てハニカム触媒2〜15を得た。以上のハニカム触媒1
〜15の性状を下記表Bにまとめて示す。Using the above crystalline silicates 2 to 15, the H-type crystalline silicate 2 is produced in the same manner as the honeycomb catalyst 1.
To 15 were obtained, and this silicate was further coated on a cordierite monolith substrate in the same step as in the preparation of the honeycomb catalyst 1 to obtain honeycomb coated products 2 to 15. Next, it was immersed in an iridium chloride aqueous solution, and honeycomb catalysts 2 to 15 were obtained in the same manner as the honeycomb catalyst 1. The above honeycomb catalyst 1
Table 15 below summarizes the properties of Nos. To 15.
【0020】[0020]
【表3】 [Table 3]
【0021】[0021]
【0022】[0022]
【0023】○ 燃料分解触媒Aの調製 結晶性シリケート100gとZn(NO3 )2 ・6H2
O:297.4gを5リットルの蒸留水に添加し70℃
に保温した後、攪拌を24時間行ってイオン交換を行っ
た。イオン交換後ろ過、洗浄を行った後、200℃で乾
燥を行いZn:2.3wt%担持結晶性シリケートを調
製した。この触媒をハニカム触媒1の触媒化と同様の方
法にてハニカムを行い燃料分解触媒Aを得た。Preparation of Fuel Decomposition Catalyst A 100 g of crystalline silicate and Zn (NO 3 ) 2 .6H 2
O: 297.4 g was added to 5 liters of distilled water, and 70 ° C.
Then, the mixture was stirred for 24 hours to perform ion exchange. After ion exchange, filtration and washing were performed, followed by drying at 200 ° C. to prepare a crystalline silicate supporting Zn: 2.3 wt%. This catalyst was subjected to honeycomb treatment in the same manner as that for the honeycomb catalyst 1 to obtain a fuel decomposition catalyst A.
【0024】○ NOx分解試験 ハニカム触媒1を用いて、ディーゼルエンジン模擬排ガ
ス中のNOx除去試験を実施した。試験条件は下記のと
おりである。 ハニカム触媒の形状:15mm×15mm×60mm
(144セル数) 13.5cc ガス量 945Nl/h、GHSV:70,000h-1 温 度:300,400,500℃ ガス組成 NO:500ppm、CO:500ppm、C2 H4 :
700ppm(C1 換算:1400ppm)、CO2 :
6%、H2 O:6%、O2 :10%、SO2 :15pp
m 上記試験条件(Run1)で実施したハニカム触媒1の
脱硝活性結果を後記表Cに示す。NOx Decomposition Test Using the honeycomb catalyst 1, a test for removing NOx from the simulated exhaust gas of a diesel engine was performed. The test conditions are as follows. Shape of honeycomb catalyst: 15 mm x 15 mm x 60 mm
(144 cells) 13.5 cc Gas amount 945 Nl / h, GHSV: 70,000 h -1 Temperature: 300, 400, 500 ° C Gas composition NO: 500 ppm, CO: 500 ppm, C 2 H 4 :
700 ppm (C 1 terms: 1400ppm), CO 2:
6%, H 2 O: 6 %, O 2: 10%, SO 2: 15pp
m The results of the denitration activity of the honeycomb catalyst 1 performed under the above test conditions (Run 1) are shown in Table C below.
【0025】次に、燃料として用いて軽油を気化させ
て、上記ガス組成にC1 換算で3000ppm(C2 H
4 +軽油:計C1 換算4400ppm)添加してハニカ
ム触媒1の活性評価試験を行い(Run2)、その時の
脱硝活性を後記表Cに併せて示す。Next, to vaporize diesel fuel used as a fuel, a C 1 terms of the gas composition 3000 ppm (C 2 H
4 + gas oil: total C 1 Convert 4400 ppm) performs the activity evaluation test of the honeycomb catalyst 1 was added (Run2), are also shown denitration activity at that time in the following Table C.
【0026】さらに、上記軽油を前記燃料分解触媒Aを
用いて、下記条件にて分解させた後、分解炭化水素を触
媒へ供給させた。 燃料分解触媒Aの形状:5mm×10mm×60mm
(32セル数)3cc 軽油供給量:3cc/h、LHSX:1h-1 触媒温度 :500℃Further, the light oil was cracked using the fuel cracking catalyst A under the following conditions, and cracked hydrocarbons were supplied to the catalyst. Shape of fuel cracking catalyst A: 5 mm x 10 mm x 60 mm
(32 cells) 3 cc Light oil supply: 3 cc / h, LHSX: 1 h -1 Catalyst temperature: 500 ° C.
【0027】上記条件にて軽油を分解した際の炭化水素
組成は下記の通りである。 C2 H4 :15%、C3 H6 :10%、C4 H8 :5
%、ベンゼン:20%、トルエン:15%、キシレン:
5%、その他の炭化水素:30% 上記分解ガスをハニカム触媒1へ添加した際(Run
3)の脱硝活性結果を後記表Cに併せて示す。The hydrocarbon composition when gas oil is cracked under the above conditions is as follows. C 2 H 4: 15%, C 3 H 6: 10%, C 4 H 8: 5
%, Benzene: 20%, toluene: 15%, xylene:
5%, other hydrocarbons: 30% When the above cracked gas was added to the honeycomb catalyst 1 (Run
The denitration activity result of 3) is also shown in Table C below.
【0028】(実施例2) ○ 軽油の熱分解装置 実施例1の燃料分解触媒Aを用いる代わりに、熱分解法
による軽油の分解を実施した。内径6mmφの石英管を
電気炉にて800℃に加熱する。軽油を加熱石英管にて
マイクロポンプを用いて滞留時間1秒を保つように瞬時
に供給して熱分解を行う。熱分解によるガス組成は下記
の通りである。 C2 H4 :25%、C3 H1:20%、C4 H8 :5
%、ベンゼン:5%、トルエン:5%、その他の炭化水
素:40% なお、上記熱分解ガスは実施例1と同様に軽油をC1 換
算で3000ppm(C2 H4 +軽油:計C1 換算44
00ppm)でハニカム触媒1へ供給して活性評価試験
を実施し(Run4)、脱硝活性結果を下記表Cに併せ
て示す。(Example 2) 装置 Gas oil thermal cracking device Instead of using the fuel cracking catalyst A of Example 1, gas oil was cracked by a thermal cracking method. A quartz tube having an inner diameter of 6 mmφ is heated to 800 ° C. in an electric furnace. Light oil is supplied instantaneously in a heated quartz tube using a micropump so as to maintain a residence time of 1 second to perform thermal decomposition. The gas composition by the thermal decomposition is as follows. C 2 H 4: 25%, C 3 H1: 20%, C 4 H 8: 5
% Benzene: 5%, toluene: 5%, other hydrocarbons: 40% Note, 3000ppm (C 2 H 4 + gas oil the pyrolysis gases with C 1 converts the light oil in the same manner as in Example 1: Total C 1 Conversion 44
(00 ppm) to the honeycomb catalyst 1 to perform an activity evaluation test (Run 4). The results of the denitration activity are also shown in Table C below.
【0029】[0029]
【表4】 [Table 4]
【0030】(実施例3) 触媒2〜15においてもハニカム触媒1と同様に実施例
1,2に示したRun1〜4の試験を実施例1,2と同
一の方法にて脱硝活性評価を実施した。400℃におけ
る脱硝評価結果を表Dに示す。(Example 3) In Catalysts 2 to 15 , the tests of Runs 1 to 4 shown in Examples 1 and 2 were carried out in the same manner as in Honeycomb Catalyst 1 to evaluate the denitration activity in the same manner as in Examples 1 and 2. did. Table D shows the denitration evaluation results at 400 ° C.
【0031】[0031]
【表5】 [Table 5]
【0032】以上実施例1,2及び3に示すようにイリ
ジウムを含有した触媒に炭化水素燃料を添加することに
より脱硝活性の向上が認められ、さらに燃料を触媒分解
法及び熱分解法によりオレフィン、芳香族分が多い炭化
水素に変換して添加することにより、より著しい脱硝活
性の向上を確認した。さらに、上記方法により500時
間の耐久試験を連続的に実施したところ触媒性能に変化
はなく、安定な性能を維持できることを確認した。また
本発明で使用するハニカム触媒1は脱硝の他にCO、C
Hの燃焼除去も可能であるため燃料の添加が未燃CHの
排出を生じさせる心配はない。As shown in Examples 1, 2 and 3, the addition of hydrocarbon fuel to the catalyst containing iridium showed an improvement in the denitration activity. Further, the fuel was subjected to catalytic decomposition and thermal decomposition to produce olefins and olefins. It was confirmed that the conversion to a hydrocarbon containing a large amount of aromatics was added and the remarkable improvement in the denitration activity was achieved. Furthermore, when a 500-hour durability test was continuously performed by the above method, it was confirmed that there was no change in the catalyst performance and that stable performance could be maintained. In addition, the honeycomb catalyst 1 used in the present invention has CO, C
Since H can be removed by burning, there is no concern that the addition of fuel causes emission of unburned CH.
【0033】[0033]
【発明の効果】以上、説明したとおり、本発明による排
気ガス浄化方法は高い脱硝性能を安定に維持することを
可能にし、ディーゼルエンジン等の高酸素濃度、低炭化
水素濃度排ガス中での脱硝を効率よく行なうことが可能
である。As described above, the exhaust gas purifying method according to the present invention makes it possible to stably maintain high denitration performance, and to perform denitration in exhaust gas with high oxygen concentration and low hydrocarbon concentration such as diesel engine. It can be performed efficiently.
───────────────────────────────────────────────────── フロントページの続き (56)参考文献 特開 平5−245386(JP,A) 特開 昭51−35667(JP,A) 特開 平5−192539(JP,A) 特開 平5−212246(JP,A) (58)調査した分野(Int.Cl.7,DB名) B01J 21/00 - 37/36 ──────────────────────────────────────────────────続 き Continuation of the front page (56) References JP-A-5-245386 (JP, A) JP-A-51-35667 (JP, A) JP-A-5-192539 (JP, A) JP-A-5-92539 212246 (JP, A) (58) Field surveyed (Int. Cl. 7 , DB name) B01J 21/00-37/36
Claims (3)
含有する排気ガス中の窒素酸化物を還元物とともに触媒
に接触させて窒素酸化物を窒素に還元する方法におい
て、前記触媒が一般式 (1±0.8)R2 O・(aM2 O3 ・bM′O・cAl2 O3 )・ySiO2 (但し、上記式中、Rはアルカリ金属イオン及び/又は
水素イオン、MはVIII族元素、希土類元素、チタン、バ
ナジウム、クロム、ニオブ、アンチモン及びガリウムよ
りなる群から選ばれた少なくとも1種以上の元素イオ
ン、M′はマグネシウム、カルシウム、ストロンチウ
ム、バリウムのアルカリ土類金属イオン、a≧0、20
>b>0、a+c=1、3000>y>11)なる化学
式を有し、表Aに示すX線回折パターンを有する結晶性
シリケートよりなる担体に活性金属としてイリジウムを
担持したイリジウム触媒であり、前記還元物が灯油、軽
油及びガソリンよりなる群から選ばれた1種以上の炭化
水素系燃料油であることを特徴とする排気ガスの浄化方
法。 【表1】 1. A method for reducing nitrogen oxides into nitrogen by bringing the nitrogen oxides in an exhaust gas containing nitrogen oxides, carbon monoxide and hydrocarbons into contact with a catalyst together with a reductant, wherein the catalyst has a general formula (1 ± 0.8) R 2 O. (aM 2 O 3 .bM'O.cAl 2 O 3 ) .ySiO 2 (where R is an alkali metal ion and / or hydrogen ion, M is VIII Group element, rare earth element, at least one or more element ions selected from the group consisting of titanium, vanadium, chromium, niobium, antimony and gallium, M 'is an alkaline earth metal ion of magnesium, calcium, strontium, barium, a ≧ 0, 20
>B> 0 , a + c = 1, 3000>y> 11) is an iridium catalyst in which iridium is supported as an active metal on a support made of a crystalline silicate having an X-ray diffraction pattern shown in Table A, A method for purifying exhaust gas, wherein the reduced product is at least one hydrocarbon fuel oil selected from the group consisting of kerosene, light oil and gasoline. [Table 1]
りなる群より選ばれた1種以上の炭化水素系燃料油を熱
分解してなるオレフィン類、芳香族炭化水素に富むガス
であることを特徴とする請求項1記載の排気ガスの浄化
方法。 2. The method according to claim 1, wherein the reduced product is kerosene, light oil or gasoline.
Heat at least one hydrocarbon fuel oil selected from the group consisting of
Decomposed olefins and aromatic hydrocarbon-rich gas
The exhaust gas purification according to claim 1, characterized in that:
Method.
りなる群より選ばれた1種以上の炭化水素系燃料油を触
媒分解してなるオレフィン類、芳香族炭化水素に富むガ
スであることを特徴とする請求項1記載の排気ガスの浄
化方法。 3. The method according to claim 1, wherein the reduced product is kerosene, light oil or gasoline.
At least one hydrocarbon fuel oil selected from the group consisting of
Gases rich in olefins and aromatic hydrocarbons
The exhaust gas purification according to claim 1, wherein
Method.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP26609693A JP3154602B2 (en) | 1993-10-25 | 1993-10-25 | Exhaust gas purification method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP26609693A JP3154602B2 (en) | 1993-10-25 | 1993-10-25 | Exhaust gas purification method |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH07116470A JPH07116470A (en) | 1995-05-09 |
| JP3154602B2 true JP3154602B2 (en) | 2001-04-09 |
Family
ID=17426268
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP26609693A Expired - Lifetime JP3154602B2 (en) | 1993-10-25 | 1993-10-25 | Exhaust gas purification method |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP3154602B2 (en) |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| KR100379714B1 (en) * | 2000-04-10 | 2003-04-10 | 주식회사 얼라이브텍 | Harmful Material Removers Used For Removing Sulfur Oxides, Nitrogen Oxides And Aromatic Halogen Compounds Among Flue Gases |
-
1993
- 1993-10-25 JP JP26609693A patent/JP3154602B2/en not_active Expired - Lifetime
Also Published As
| Publication number | Publication date |
|---|---|
| JPH07116470A (en) | 1995-05-09 |
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