JPH06226052A - Method for removing nox - Google Patents
Method for removing noxInfo
- Publication number
- JPH06226052A JPH06226052A JP5013580A JP1358093A JPH06226052A JP H06226052 A JPH06226052 A JP H06226052A JP 5013580 A JP5013580 A JP 5013580A JP 1358093 A JP1358093 A JP 1358093A JP H06226052 A JPH06226052 A JP H06226052A
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- zro
- tio
- nox
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Abstract
Description
【0001】[0001]
【産業上の利用分野】本発明は窒素酸化物(以後、NO
xと略称)を浄化する方法に関するものである。The present invention relates to nitrogen oxides (hereinafter referred to as NO
x) (abbreviated as x).
【0002】[0002]
【従来の技術】排ガス及び汚染空気中のNOx除去法と
しては吸着法、酸化吸収法、接触還元法などがあるが、
後処理不要の接触還元法が経済的、技術的にも有利とさ
れている。接触還元法の中でボイラ排ガス中のNOxは
アンモニア等の還元ガスを加える選択的還元法が主流で
あり、自動車排ガス中のNOx除去は共存するH2 ,C
O,炭化水素の還元性ガスによる非選択的還元法が主流
である。2. Description of the Related Art As methods for removing NOx in exhaust gas and polluted air, there are adsorption method, oxidation absorption method, catalytic reduction method, etc.
The catalytic reduction method, which requires no post-treatment, is considered to be economically and technically advantageous. In the catalytic reduction method, NOx in the boiler exhaust gas is predominantly a selective reduction method in which a reducing gas such as ammonia is added, and NOx in the vehicle exhaust gas is coexistent with H 2 and C 2 .
The non-selective reduction method using reducing gas of O and hydrocarbon is the mainstream.
【0003】一方、近年、窒素酸化物の直接分解触媒に
関する研究が鋭意実施されており、Pt/Al2 O3 ,
LaSrCoOx(ペロブスカイト構造),Al
2 O3 ,Cu−ZSM−5等の触媒が報告されている。
しかし、いずれの触媒とも、反応速度が遅く、H2 O,
O2 等の共存ガスにより、活性が低下する問題点を有す
る。On the other hand, in recent years, research on a direct decomposition catalyst of nitrogen oxides has been earnestly conducted, and Pt / Al 2 O 3 ,
LaSrCoOx (perovskite structure), Al
Catalysts such as 2 O 3 and Cu-ZSM-5 have been reported.
However, the reaction rate of each of the catalysts is slow, and H 2 O,
There is a problem that activity decreases due to coexisting gas such as O 2 .
【0004】又、本発明者らは酸化物のモル比で表わし
て下記式1の組成を有し、かつ結晶構造がX線回折にて
後記表Aの回折パターンを有する結晶性シリケートに
銅、ニッケル、コバルト、鉄、クロム、亜鉛、マンガン
を担持した触媒が高活性であることを見い出している
が、実用化に到るまでの反応速度は有していない。 (1±0.6)R2 O・〔aM2 O3 ・bAl2 O3 ・cMeO〕・ySiO2 ・・・(式1) (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族金属、希土類金属、チタン、バナジウ
ム、クロム、ニオブ、アンチモン、ガリウムからなる群
から選ばれた1種以上の金属、Meはアルカリ土類金
属、a≧0,b≧0,c≧0,a+b=1,y/c>1
2,y>12)The present inventors have also reported that the crystalline silicate has a composition represented by the following formula 1 in terms of a molar ratio of oxides and has a crystal structure of X-ray diffraction having a diffraction pattern shown in the following Table A. It has been found that a catalyst supporting nickel, cobalt, iron, chromium, zinc and manganese has high activity, but it does not have a reaction rate until it is put to practical use. (1 ± 0.6) R 2 O · [aM 2 O 3 · bAl 2 O 3 · cMeO] · ySiO 2 (Equation 1) (wherein R is an alkali metal ion and / or a hydrogen ion, M is at least one metal selected from the group consisting of Group VIII metals, rare earth metals, titanium, vanadium, chromium, niobium, antimony and gallium, Me is an alkaline earth metal, a ≧ 0, b ≧ 0, c ≧ 0, a + b = 1, y / c> 1
2, y> 12)
【0005】[0005]
【表1】 W : 弱 M : 中級 S : 強 VS : 非常に強 (X線源:Cu) I0 は最も強いピーク強度でI/I0 は相対強度[Table 1] W: Weak M: Intermediate S: Strong VS: Very strong (X-ray source: Cu) I 0 is the strongest peak intensity and I / I 0 is the relative intensity
【0006】[0006]
【発明が解決しようとする課題】ボイラ排ガス中のNO
x除去で用いられる触媒は通常V−W/TiO2 系であ
り、還元剤はアンモニアが用いられているが高価であ
り、安全面に十分な注意を払う必要があるため代替の還
元剤を望まれている。又、自動車排ガス中のNOx除去
では、通常、Pt−Rh/Al2 O3 系である三元触媒
(排ガス中の炭化水素,一酸化炭素,NOxの3物質を
同時に除去する触媒で空燃比14.6前後でのみNOx
除去を実施しているが、リーンバーンガソリンエンジン
やディーゼルエンジン等の高O2 濃度排ガス中では三元
触媒によるNOx除去は不可能である。[Problems to be Solved by the Invention] NO in boiler exhaust gas
The catalyst used for x removal is usually a V-W / TiO 2 system, and ammonia is used as the reducing agent, but it is expensive and it is necessary to pay sufficient attention to safety, so an alternative reducing agent is desired. It is rare. In addition, in the removal of NOx from automobile exhaust gas, a Pt—Rh / Al 2 O 3 -based three-way catalyst (a catalyst that simultaneously removes hydrocarbons, carbon monoxide, and NOx in exhaust gas at the same time as an air-fuel ratio of 14 NOx only around 6
Although they are being removed, it is impossible to remove NOx with a three-way catalyst in exhaust gas with a high O 2 concentration such as lean burn gasoline engine and diesel engine.
【0007】又、地下トンネルや駐車場等の公共の場で
の希薄NOxの除去方法としては、PSA法により希薄
NOxを吸着濃縮し、さらに濃縮NOxを触媒による直
接分解法が提案されているが、O2 ,H2 Oの共存ガス
が存在するため、NOx除去のためには多量の触媒量が
必要となる不具合が生じている。As a method for removing lean NOx in public places such as underground tunnels and parking lots, a method has been proposed in which lean NOx is adsorbed and concentrated by the PSA method, and further concentrated NOx is directly decomposed by a catalyst. , O 2 and H 2 O are present as coexisting gas, which causes a problem that a large amount of catalyst is required to remove NOx.
【0008】本発明は上記技術水準に鑑み、従来法にお
けるような不具合のないNOxの除去方法を提供しよう
とするものである。In view of the above-mentioned state of the art, the present invention intends to provide a method for removing NOx which does not have the problem of the conventional method.
【0009】[0009]
【課題を解決するための手段】本発明者らは前記した結
晶性シリケート触媒の有効的な利用方法を鋭意検討した
結果、ボイラ排ガス(NO:約500ppm、O2 :約
10%、H2 O:約10%)中のNOx除去には該触媒
を用いてアンモニアの代わりに有機物が有効な還元剤と
して作用することを確認すると共に、組成式にて、Al
2 O3 ,ZrO 2 、TiO2 又はSiO2 のような酸化
物、Al2 O3 ・TiO2 ,Al2 O3・ZrO2 ,Z
rO2 ・TiO2 又はSiO2 ・Al2 O3 のような複
合酸化物、Y型ゼオライト、モルデナイト、L型ゼオラ
イト、クリノプチロライト、フェリエライト、ZSM−
5型ゼオライト又はA型ゼオライトのようなゼオライ
ト、さらに、SO4 /ZrO2 、SO4 /ZrO2 ・A
l2 O3 、SO4 /ZrO2・TiO2 又はSO4 /T
iO2 のような固体酸触媒(固体超強酸触媒)も上記結
晶性シリケート触媒と同様に有機物の存在により有効に
窒素酸化物が浄化できることを確認した。Means for Solving the Problems The present inventors have made the aforementioned conclusions.
Diligent study on effective utilization of crystalline silicate catalyst
As a result, boiler exhaust gas (NO: about 500 ppm, O2:about
10%, H2O: about 10%) for removing NOx in the catalyst
Instead of ammonia as an effective reducing agent using
It is confirmed that it works, and in the composition formula, Al
2O3, ZrO 2, TiO2Or SiO2Oxidation like
Thing, Al2O3・ TiO2, Al2O3・ ZrO2, Z
rO2・ TiO2Or SiO2・ Al2O3Like
Compound oxide, Y-type zeolite, mordenite, L-type Zeora
Ito, clinoptilolite, ferrierite, ZSM-
Zeoli, such as type 5 zeolite or type A zeolite
And further SOFour/ ZrO2, SOFour/ ZrO2・ A
l2O3, SOFour/ ZrO2・ TiO2Or SOFour/ T
iO2Solid acid catalysts (solid super strong acid catalysts) such as
Effective in the presence of organic substances, similar to crystalline silicate catalysts
It was confirmed that nitrogen oxides could be purified.
【0010】さらに、添加する有機物としては、エタ
ン、プロパン、ブタン、ペンタン、ヘキサンのパラフィ
ン類、エチレン、プロピレン、ブテンのオレフィン類、
アセチレン、ブタジエンのジエン類、メタノール、エタ
ノール、プロパノール、ブタノールのアルコール類、ベ
ンゼン、トルエン、キシレンの芳香族類、アセトン、メ
チルエチルケトンのケトン類、ジメチルエーテル、ジエ
チルエーテルのエーテル類、酢酸、ギ酸のカルボン酸
類、ホルムアルデヒド、アセトアルデヒドのアルデヒド
類、ギ酸メチルからなる群から選ばれた少なくとも1種
の物質又はガソリン、灯油、軽油などの混合物燃料がい
ずれも有効な還元剤として窒素酸化物の浄化反応に有効
であることを確認した。Furthermore, as organic substances to be added, paraffins of ethane, propane, butane, pentane, hexane, olefins of ethylene, propylene, butene,
Acetylene, butadiene dienes, methanol, ethanol, propanol, butanol alcohols, benzene, toluene, xylene aromatics, acetone, methyl ethyl ketone ketones, dimethyl ether, diethyl ether ethers, acetic acid, formic acid carboxylic acids, At least one substance selected from the group consisting of formaldehyde, acetaldehyde aldehydes, and methyl formate or a mixed fuel such as gasoline, kerosene, and light oil is effective as a reducing agent in the nitrogen oxide purification reaction. It was confirmed.
【0011】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 (1)窒素酸化物を含有する排ガスに有機物を添加し、
温度100〜800℃の条件下において、下記触媒群の
一種の触媒と接触させることを特徴とする排ガス中の窒
素酸化物の浄化方法。 脱水された状態において酸化物のモル比で表わし
て、(1±0.6)R2 O・〔aM2 O3 ・bAl2 O
3 ・cMeO〕・ySiO2(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族金属、希
土類金属、チタン、バナジウム、クロム、ニオブ、アン
チモン、ガリウムからなる群から選ばれた1種以上の金
属、Meはアルカリ土類金属、a≧0,b≧0,c≧
0,a+b=1,y/c>12,y>12)の化学式を
有し、かつ本文で詳記する表Aで示されるX線パターン
を有する結晶性シリケートに銅、コバルト、ニッケル、
鉄、クロム、亜鉛、マンガンよりなる群から選ばれた1
種以上の金属を担持した触媒 組成式で表わして、Al2 O3 、ZrO2 、TiO
2 又はSiO2 の酸化物並びにAl2 O3 ・TiO2 、
Al2 O3 ・ZrO2 、ZrO2 ・TiO2 又はSiO
2 ・Al2 O3 の複合酸化物よりなる群から選ばれた1
種以上の酸化物又は複合酸化物よりなる触媒 Y型ゼオライト、モルデナイト、L型ゼオライト、
クリノプチロライト、フェリエライト、ZSM−5型ゼ
オライト、A型ゼオライトよりなる群から選ばれた1種
以上のゼオライトよりなる触媒 SO4 /ZrO2 、SO4 /ZrO2 ・Al
2 O3 、SO4 /ZrO2 ・TiO2 、SO4 /TiO
2 よりなる群から選ばれた1種以上の固体超強酸よりな
る触媒。 (2)添加する有機物がエタン、プロパン、ブタン、ペ
ンタン、ヘキサンのパラフィン類、エチレン、プロピレ
ン、ブテンのオレフィン類、アセチレン、ブタジエンの
ジエン類、メタノール、エタノール、プロパノール、ブ
タノールのアルコール類、ベンゼン、トルエン、キシレ
ンの芳香族類、アセトン、メチルエチルケトンのケトン
類、ジメチルエーテル、ジエチルエーテルのエーテル
類、酢酸、ギ酸のカルボン酸類、ホルムアルデヒド、ア
セトアルデヒドのアルデヒド類、ギ酸メチルからなる群
から選ばれた少なくとも1種の物質又はガソリン、灯
油、軽油などの混合物燃料であることを特徴とする上記
(1)記載の窒素酸化物の浄化方法。である。The present invention has been completed based on the above findings. (1) An organic substance is added to exhaust gas containing nitrogen oxides,
A method for purifying nitrogen oxides in exhaust gas, which comprises contacting the catalyst with a catalyst of the following catalyst group under the condition of a temperature of 100 to 800 ° C. Expressed as a molar ratio of oxides in the dehydrated state, (1 ± 0.6) R 2 O. [aM 2 O 3 .bAl 2 O
3 · cMeO] · ySiO 2 (wherein R is an alkali metal ion and / or a hydrogen ion, M is a group VIII metal, a rare earth metal, titanium, vanadium, chromium, niobium, antimony, or gallium. One or more metals, Me is an alkaline earth metal, a ≧ 0, b ≧ 0, c ≧
0, a + b = 1, y / c> 12, y> 12), and copper, cobalt, nickel, a crystalline silicate having an X-ray pattern shown in Table A described in detail herein.
1 selected from the group consisting of iron, chromium, zinc and manganese
A catalyst supporting one or more metals. Al 2 O 3 , ZrO 2 , TiO
2 or SiO 2 oxide and Al 2 O 3 TiO 2 ,
Al 2 O 3 · ZrO 2 , ZrO 2 · TiO 2 or SiO
1 selected from the group consisting of 2 -Al 2 O 3 complex oxides
Catalyst composed of one or more kinds of oxides or composite oxides Y-type zeolite, mordenite, L-type zeolite,
Catalyst made of one or more kinds of zeolite selected from the group consisting of clinoptilolite, ferrierite, ZSM-5 type zeolite and A type zeolite SO 4 / ZrO 2 , SO 4 / ZrO 2 .Al
2 O 3 , SO 4 / ZrO 2 · TiO 2 , SO 4 / TiO
A catalyst comprising one or more solid superacids selected from the group consisting of 2 . (2) Organic substances added include ethane, propane, butane, pentane, hexane paraffins, ethylene, propylene, butene olefins, acetylene, butadiene dienes, methanol, ethanol, propanol, butanol alcohols, benzene, toluene. , At least one substance selected from the group consisting of xylene aromatics, acetone, methyl ethyl ketone ketones, dimethyl ether, diethyl ether ethers, acetic acid, formic acid carboxylic acids, formaldehyde, acetaldehyde aldehydes, and methyl formate. Alternatively, the method for purifying nitrogen oxides according to (1) above, which is a mixed fuel such as gasoline, kerosene, or light oil. Is.
【0012】[0012]
【作用】リーンバーンエンジン排ガス(O2 濃度1〜1
0%)中のNOx除去に該触媒が有効に作用することも
明らかとなり、排ガス中の有機物が還元剤として有効に
働く。さらに、排ガス中の有機物が少ない場合、定置型
エンジンでは連続的に、移動型エンジンでは還元剤の濃
度に応じて有機物を供給すれば、所定のNOx除去性能
を有することが判明した。又、ディーゼルエンジンもガ
ソリンエンジンと同様に、排ガス中に還元剤の濃度に応
じて有機物を添加することにより所定のNOx除去性能
を有することを確認している。[Function] Lean burn engine exhaust gas (O 2 concentration 1 to 1
It was also clarified that the catalyst effectively acts on the removal of NOx in (0%), and the organic matter in the exhaust gas acts effectively as a reducing agent. Further, it has been found that when the exhaust gas contains a small amount of organic matter, the stationary engine has continuous NOx removal performance if the organic engine is supplied continuously according to the concentration of the reducing agent. Also, it has been confirmed that the diesel engine has a predetermined NOx removal performance by adding an organic substance to the exhaust gas in accordance with the concentration of the reducing agent, as in the gasoline engine.
【0013】なお、いずれの触媒、いずれの還元剤とも
作用する温度は100〜800℃と広範囲であり、共存
するガス(SOx,H2 O,O2 等)の影響も少ない。The temperature at which any catalyst and any reducing agent act is in a wide range of 100 to 800 ° C., and the influence of coexisting gases (SOx, H 2 O, O 2 etc.) is small.
【0014】上記触媒(結晶性シリケート系、固体酸
系)はNOx除去に用いる場合、NOxの直接分解(2
NO→N2 +O2 )反応に有効に働くが、有機物が存在
する場合、系内に存在するO2 により有機物が活性化さ
れ、活性有機化合物が生成すると考えられる。炭化水素
のC3 H6 を例に採って示すと反応式は下記のようにな
ると考えられる。 C3 H6 + 3/2O2 → 3CH2 O・(これが活性有機化合物と想定)(a) CH2 O・+O2 → CO2 +H2 O ・・・・・・・ (b) CH2 O・+2NO→ N2 +CO2 +H2 O ・・・・・・・ (c)When the above catalyst (crystalline silicate type, solid acid type) is used for removing NOx, the direct decomposition of NOx (2
Although it works effectively for the NO → N 2 + O 2 ) reaction, it is considered that when organic matter is present, the organic matter is activated by O 2 present in the system to produce an active organic compound. Taking C 3 H 6 which is a hydrocarbon as an example, the reaction formula is considered to be as follows. C 3 H 6 + 3 / 2O 2 → 3CH 2 O · (this is assumed to be an active organic compound) (a) CH 2 O · + O 2 → CO 2 + H 2 O ··· (b) CH 2 O・ + 2NO → N 2 + CO 2 + H 2 O ・ ・ ・ ・ ・ ・ (c)
【0015】[0015]
(例1) (触媒調製)本発明の一実施例にて用いる結晶性シリケ
ートは脱水された状態でNa2 O・0.5Al2 O3 ・
0.5Fe2 O3 ・0.1CaO・25SiO2 で表わ
され、前記表Aに示す結晶構造を有するものを使用し
た。なお、この結晶性シリケートは以下のように調製し
た。(Example 1) (Catalyst preparation) The crystalline silicate used in one example of the present invention is Na 2 O · 0.5Al 2 O 3 · in a dehydrated state.
Represented by 0.5Fe 2 O 3 · 0.1CaO · 25SiO 2, were used those having a crystal structure shown in Table A. The crystalline silicate was prepared as follows.
【0016】水ガラス3号を水に溶解し溶液Aとする。
また硫酸第二鉄、硫酸アルミニウム、酢酸カルシウムを
水に溶解して溶液Bとする。なお、溶液A、溶液Bの仕
込みモル数は36Na2 O・〔0.5Fe2 O3 ・0.
5Al2 O3 ・0.1CaO〕・25SiO2 ・160
0H2 Oのように調製し、溶液Aと溶液Bを等量ずつ別
の容器に滴下しゲルを生成させる。中和によって生成し
た上記スラリーゲルに硫酸を適当量添加し、ゲルのpH
を9に合わせる。その後、有機窒素化合物として、テト
ラプロピルアンモニウムブロマイドをFe2 O3 とAl
2 O3 合計モル数の10倍加え、上記スラリとよく混合
し、3リットルのステンレスオートクレーブにはり込
む。このスラリを300rpmにて攪拌しながら、16
0℃3日間反応させた。冷却後、固形分をろ過し、洗浄
水のpHが7になるまで充分水洗し、110℃で12時
間乾燥し、550℃で3時間焼成し結晶性シリケート1
を得た。該結晶性シリケートを0.04モル濃度酢酸水
液にて銅イオン交換を20℃、48時間連続して実施
し、イオン交換後、垂涎、乾燥し粉末触媒1を調製し
た。担持Cu量は0.70mmolであった。この粉末
触媒1にバインダーとしてアルミナゾル、シリカゾル、
水を加えて混合攪拌し、ウォッシュコート用スラリを調
製した。このスラリにコージェライトモノリス基材を浸
漬させ、余分なスラリを吹き払い、ハニカム触媒1を調
製した。Water glass No. 3 is dissolved in water to prepare a solution A.
Further, ferric sulfate, aluminum sulfate, and calcium acetate are dissolved in water to obtain solution B. The molar numbers of the solutions A and B charged were 36Na 2 O. [0.5Fe 2 O 3 .0.
5Al 2 O 3 · 0.1CaO] · 25SiO 2 · 160
It is prepared as 0H 2 O, and the solution A and the solution B are dropped in equal amounts in different containers to form a gel. Add an appropriate amount of sulfuric acid to the above-mentioned slurry gel produced by neutralization, and adjust the pH of the gel.
To 9. Then, tetrapropylammonium bromide as an organic nitrogen compound was mixed with Fe 2 O 3 and Al.
Add 10 times the total number of moles of 2 O 3, mix well with the above slurry, and place in a 3 liter stainless steel autoclave. While stirring this slurry at 300 rpm,
The reaction was carried out at 0 ° C for 3 days. After cooling, the solid content is filtered, washed thoroughly with water until the pH of the wash water reaches 7, dried at 110 ° C. for 12 hours, and calcined at 550 ° C. for 3 hours to obtain crystalline silicate 1.
Got The crystalline silicate was continuously subjected to copper ion exchange with a 0.04 molar aqueous solution of acetic acid at 20 ° C. for 48 hours, and after the ion exchange, was dripped and dried to prepare a powder catalyst 1. The amount of supported Cu was 0.70 mmol. Alumina sol, silica sol, and
Water was added and mixed and stirred to prepare a slurry for washcoat. A cordierite monolith substrate was dipped in this slurry and the excess slurry was blown off to prepare a honeycomb catalyst 1.
【0017】(活性評価)ハニカム触媒1を用いてディ
ーゼル排ガスの脱硝試験として下記模擬ガスにて活性評
価試験を実施した。 〇温 度 : 350℃,450℃ 〇GHSV : 30000h-1 〇ガス組成 : NO:400ppm,O2 :8%,C
O2 :10%,H2 O:10%,残N2 触媒の前段に還元剤としてC2 H5 OHを1000pp
m(C1 換算で2000ppm)均一に上記模擬ガスに
供給して脱硝反応を実施した。活性評価結果を後記表B
に示す。(Activity evaluation) Using the honeycomb catalyst 1, an activity evaluation test was carried out as a denitration test of diesel exhaust gas with the following simulated gas. ○ Temperature: 350 ℃, 450 ℃ ○ GHSV: 30000h -1 ○ Gas composition: NO: 400ppm, O 2 : 8%, C
O 2 : 10%, H 2 O 10%, 1000 pp of C 2 H 5 OH as a reducing agent before the remaining N 2 catalyst.
m (2000 ppm in terms of C 1 ) was uniformly supplied to the above simulated gas to carry out the denitration reaction. The activity evaluation results are shown in Table B below.
Shown in.
【0018】(例2)結晶性シリケートの調合時におい
て、例1と同様に硫酸第二鉄の代わりに、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、塩化ニオブ、塩化アンチモン、塩化ガリウムを各々
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2,3,4,5,6,7,8,9,10,
11,12を調製した。(Example 2) In preparing a crystalline silicate, cobalt chloride, ruthenium chloride, rhodium chloride, lanthanum chloride, cerium chloride, titanium chloride, vanadium chloride and chloride were used instead of ferric sulfate in the same manner as in Example 1. The same operations as those for the crystalline silicate 1 were repeated except that chromium, niobium chloride, antimony chloride, and gallium chloride were added in the same mole number as Fe 2 O 3 in terms of oxide. 5, 6, 7, 8, 9, 10,
11, 12 were prepared.
【0019】又例1と同様に結晶性シリケート調合時に
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
4,15を調製した。In the same manner as in Example 1, magnesium acetate, strontium acetate, and barium acetate were used as oxides instead of calcium acetate in the preparation of the crystalline silicate, respectively.
The same operations as those for the crystalline silicate 1 were repeated except that the same number of moles as aO was added, and the crystalline silicates 13, 1
4,15 were prepared.
【0020】これらの結晶性シリケートを例1と同様の
方法で粉末触媒化し、粉末触媒2〜15を得、さらに例
1と同様にハニカム触媒化し、ハニカム触媒2〜15を
調製した。These crystalline silicates were powder-catalyzed in the same manner as in Example 1 to obtain powder catalysts 2 to 15, and further honeycomb-catalyzed in the same manner as in Example 1 to prepare honeycomb catalysts 2 to 15.
【0021】この例2で得たハニカム触媒2〜15を例
1の活性評価条件と同じ条件で評価した結果を、後記表
Bに併せて示す。The results of evaluation of the honeycomb catalysts 2 to 15 obtained in Example 2 under the same conditions as the activity evaluation conditions of Example 1 are also shown in Table B below.
【0022】(例3)結晶性シリケート1を用いて塩化
コバルト、塩化ニッケル、塩化第二鉄、硝酸クロム、塩
化亜銅、塩化マンガンの各0.04M水溶液にてイオン
交換を60℃、48時間連続して実施し、イオン交換
後、水洗、乾燥し粉末触媒16〜21を得た。さらに例
1と同様に粉末触媒16〜21をハニカム化しハニカム
触媒16〜21を得た。(Example 3) Using crystalline silicate 1, ion exchange was carried out with 0.04 M aqueous solution of each of cobalt chloride, nickel chloride, ferric chloride, chromium nitrate, cuprous chloride and manganese chloride at 60 ° C for 48 hours. It was carried out continuously, after ion exchange, washed with water and dried to obtain powder catalysts 16 to 21. Further, in the same manner as in Example 1, the powder catalysts 16 to 21 were made into honeycomb to obtain honeycomb catalysts 16 to 21.
【0023】この例3で得たハニカム触媒16〜21を
例1の活性評価条件と同じ条件で評価した結果を下記表
Bに併せて示す。The results of evaluation of the honeycomb catalysts 16 to 21 obtained in Example 3 under the same conditions as the activity evaluation conditions of Example 1 are also shown in Table B below.
【0024】[0024]
【表2】 [Table 2]
【0025】[0025]
【表3】 [Table 3]
【0026】(例4)組成式にてAl2 O3 (γ型),
ZrO2 ,TiO2 (アナターゼ型),SiO2 の酸化
物、Al2 O3 ・TiO2 ,Al2 O3 ・ZrO2 ,Z
rO2 ・TiO2 ,SiO2 ・Al2 O3 の複合酸化
物、Y型ゼオライト(SiO2 /Al2O3 :6)、モ
ルデナイト(SiO2 /Al2 O3 :15)、L型ゼオ
ライト(SiO2 /Al2 O3 :6)、クリノプチロラ
イト(SiO2 /Al2 O3 :5)、フェリエライト
(SiO2 /Al2 O3 :5)、ZSM−5型ゼオライ
ト(SiO2 /Al2 O3 :35)、A型ゼオライト
(SiO2 /Al2 O3 :1)のゼオライト(全てH
型)、さらにSO4 /ZrO2 ,SO4 /ZrO2 ・A
l 2 O3 ,SO4 /ZrO2 ・TiO2 ,SO4 /Ti
O2 の固体超強酸を用いてこれらの触媒を例1と同様に
ハニカム化し、ハニカム触媒22〜40を得た。(Example 4) Al in the composition formula2O3(Γ type),
ZrO2, TiO2(Anatase type), SiO2Oxidation of
Thing, Al2O3・ TiO2, Al2O3・ ZrO2, Z
rO2・ TiO2, SiO2・ Al2O3Complex oxidation of
Thing, Y-type zeolite (SiO2/ Al2O3: 6), Mo
Rudenite (SiO2/ Al2O3: 15), L-type Zeo
Light (SiO2/ Al2O3: 6), Clinoptilola
Ito (SiO2/ Al2O3: 5), Ferrierite
(SiO2/ Al2O3: 5), ZSM-5 type Zeoli
To (SiO2/ Al2O3: 35), type A zeolite
(SiO2/ Al2O3: 1) zeolite (all H
Type), and SOFour/ ZrO2, SOFour/ ZrO2・ A
l 2O3, SOFour/ ZrO2・ TiO2, SOFour/ Ti
O2These catalysts were prepared as in Example 1 using the solid superacids of
Honeycombing was performed to obtain honeycomb catalysts 22 to 40.
【0027】例4で得られたハニカム触媒22〜40を
例1の活性評価条件と同じ条件で評価した結果を下記表
Cに併せて示す。The results of evaluation of the honeycomb catalysts 22 to 40 obtained in Example 4 under the same conditions as the activity evaluation conditions of Example 1 are also shown in Table C below.
【0028】表Cの結果より上記触媒を用いることによ
り、高酸素濃度下においてもC2 H 5 OHを添加するこ
とにより効率的にNOxが浄化できることが判明した。From the results in Table C, it is possible to use the above catalyst.
C, even under high oxygen concentration2H FiveAdd OH
It was found that NOx can be efficiently purified by.
【0029】[0029]
【表4】 [Table 4]
【0030】(例5)ハニカム触媒1を用いて還元剤と
して下記炭化水素を添加して例1と同様の活性評価条件
にて実施した。還元剤はエタン、プロパン、ブタン、ペ
ンタン、ヘキサン、プロピレン、ブテン、アセチレン、
ブタジエン、メタノール、エチレン、エタノール、プロ
パノール、ブタノール、ベンゼン、トルエン、キシレ
ン、アセトン、メチルエチルケトン、ジメチルエーテ
ル、ジエチルエーテル、酢酸、ギ酸、ホルムアルデヒ
ド、アセトアルデヒド、ギ酸メチル、ガソリン、灯油、
軽油さらに各々C1 換算で2000ppm添加した。活
性評価結果を表Dに示す。Example 5 Using honeycomb catalyst 1, the following hydrocarbon was added as a reducing agent and the same activity evaluation conditions as in Example 1 were used. The reducing agent is ethane, propane, butane, pentane, hexane, propylene, butene, acetylene,
Butadiene, methanol, ethylene, ethanol, propanol, butanol, benzene, toluene, xylene, acetone, methyl ethyl ketone, dimethyl ether, diethyl ether, acetic acid, formic acid, formaldehyde, acetaldehyde, methyl formate, gasoline, kerosene,
Light oil was further added at 2000 ppm in terms of C 1 . The results of activity evaluation are shown in Table D.
【0031】表Dに示すように上記還元剤を添加するこ
とにより、高酸素濃度下においても効率的にNOxが浄
化できることが判明した。なお、ハニカム触媒1以外の
ハニカム触媒2〜21及び22〜40においてもハニカ
ム触媒1と同様に効率的にNOx浄化できることを確認
している。As shown in Table D, it was found that NOx can be efficiently purified even under a high oxygen concentration by adding the reducing agent. It has been confirmed that the honeycomb catalysts 2 to 21 and 22 to 40 other than the honeycomb catalyst 1 can also efficiently purify NOx as with the honeycomb catalyst 1.
【0032】[0032]
【表5】 [Table 5]
【0033】[0033]
【発明の効果】本発明により実施例にて示すように窒素
酸化物を含有する排ガスに有機物を添加して触媒と接触
させることにより、排ガス中の窒素酸化物が有効に浄化
されることがわかった。EFFECTS OF THE INVENTION According to the present invention, it was found that nitrogen oxide in exhaust gas can be effectively purified by adding an organic substance to the exhaust gas containing nitrogen oxide and bringing it into contact with a catalyst as shown in Examples. It was
Claims (2)
添加し、温度100〜800℃の条件下において、下記
触媒群の一種の触媒と接触させることを特徴とする排ガ
ス中の窒素酸化物の浄化方法。 脱水された状態において酸化物のモル比で表わし
て、(1±0.6)R2 O・〔aM2 O3 ・bAl2 O
3 ・cMeO〕・ySiO2(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族金属、希
土類金属、チタン、バナジウム、クロム、ニオブ、アン
チモン、ガリウムからなる群から選ばれた1種以上の金
属、Meはアルカリ土類金属、a≧0,b≧0,c≧
0,a+b=1,y/c>12,y>12)の化学式を
有し、かつ本文で詳記する表Aで示されるX線パターン
を有する結晶性シリケートに銅、コバルト、ニッケル、
鉄、クロム、亜鉛、マンガンよりなる群から選ばれた1
種以上の金属を担持した触媒 組成式で表わして、Al2 O3 、ZrO2 、TiO
2 又はSiO2 の酸化物並びにAl2 O3 ・TiO2 、
Al2 O3 ・ZrO2 、ZrO2 ・TiO2 又はSiO
2 ・Al2 O3 の複合酸化物よりなる群から選ばれた1
種以上の酸化物又は複合酸化物よりなる触媒 Y型ゼオライト、モルデナイト、L型ゼオライト、
クリノプチロライト、フェリエライト、ZSM−5型ゼ
オライト、A型ゼオライトよりなる群から選ばれた1種
以上のゼオライトよりなる触媒 SO4 /ZrO2 、SO4 /ZrO2 ・Al
2 O3 、SO4 /ZrO2 ・TiO2 、SO4 /TiO
2 よりなる群から選ばれた1種以上の固体超強酸よりな
る触媒。1. An organic substance is added to an exhaust gas containing nitrogen oxides, and the organic substance is brought into contact with a catalyst of the following catalyst group under the condition of a temperature of 100 to 800 ° C. Purification method. Expressed as a molar ratio of oxides in the dehydrated state, (1 ± 0.6) R 2 O. [aM 2 O 3 .bAl 2 O
3 · cMeO] · ySiO 2 (wherein R is an alkali metal ion and / or a hydrogen ion, M is a group VIII metal, a rare earth metal, titanium, vanadium, chromium, niobium, antimony, or gallium. One or more metals, Me is an alkaline earth metal, a ≧ 0, b ≧ 0, c ≧
0, a + b = 1, y / c> 12, y> 12), and copper, cobalt, nickel, a crystalline silicate having an X-ray pattern shown in Table A described in detail herein.
1 selected from the group consisting of iron, chromium, zinc and manganese
A catalyst supporting one or more metals. Al 2 O 3 , ZrO 2 , TiO
2 or SiO 2 oxide and Al 2 O 3 TiO 2 ,
Al 2 O 3 · ZrO 2 , ZrO 2 · TiO 2 or SiO
1 selected from the group consisting of 2 -Al 2 O 3 complex oxides
Catalyst composed of one or more kinds of oxides or composite oxides Y-type zeolite, mordenite, L-type zeolite,
Catalyst made of one or more kinds of zeolite selected from the group consisting of clinoptilolite, ferrierite, ZSM-5 type zeolite and A type zeolite SO 4 / ZrO 2 , SO 4 / ZrO 2 .Al
2 O 3 , SO 4 / ZrO 2 · TiO 2 , SO 4 / TiO
A catalyst comprising one or more solid superacids selected from the group consisting of 2 .
タン、ペンタン、ヘキサンのパラフィン類、エチレン、
プロピレン、ブテンのオレフィン類、アセチレン、ブタ
ジエンのジエン類、メタノール、エタノール、プロパノ
ール、ブタノールのアルコール類、ベンゼン、トルエ
ン、キシレンの芳香族類、アセトン、メチルエチルケト
ンのケトン類、ジメチルエーテル、ジエチルエーテルの
エーテル類、酢酸、ギ酸のカルボン酸類、ホルムアルデ
ヒド、アセトアルデヒドのアルデヒド類、ギ酸メチルか
らなる群から選ばれた少なくとも1種の物質又はガソリ
ン、灯油、軽油などの混合物燃料であることを特徴とす
る請求項1記載の窒素酸化物の浄化方法。2. The organic matter added is ethane, propane, butane, pentane, hexane paraffins, ethylene,
Propylene, butene olefins, acetylene, butadiene dienes, methanol, ethanol, propanol, butanol alcohols, benzene, toluene, xylene aromatics, acetone, methyl ethyl ketone ketones, dimethyl ether, diethyl ether ethers, The at least one substance selected from the group consisting of acetic acid, carboxylic acids of formic acid, formaldehyde, aldehydes of acetaldehyde, and methyl formate, or a mixed fuel of gasoline, kerosene, light oil, etc. Method for purifying nitrogen oxides.
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JP01358093A JP3276191B2 (en) | 1993-01-29 | 1993-01-29 | Nitrogen oxide purification method |
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Cited By (13)
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WO1996022828A1 (en) * | 1995-01-25 | 1996-08-01 | Gaz Metropolitain And Company, Limited Partnership | Selective catalytic reduction of nitrogen oxides |
AU698950B2 (en) * | 1995-01-25 | 1998-11-12 | Gaz Metropolitain And Company, Limited Partnership | Selective catalytic reduction of nitrogen oxides |
US6023165A (en) * | 1992-09-28 | 2000-02-08 | Fonar Corporation | Nuclear magnetic resonance apparatus and methods of use and facilities for incorporating the same |
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US6576587B2 (en) | 2001-03-13 | 2003-06-10 | Delphi Technologies, Inc. | High surface area lean NOx catalyst |
US6624113B2 (en) | 2001-03-13 | 2003-09-23 | Delphi Technologies, Inc. | Alkali metal/alkaline earth lean NOx catalyst |
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US6023165A (en) * | 1992-09-28 | 2000-02-08 | Fonar Corporation | Nuclear magnetic resonance apparatus and methods of use and facilities for incorporating the same |
US6075364A (en) * | 1992-09-28 | 2000-06-13 | Fonar Corporation | Nuclear magnetic resonance apparatus and methods of use and facilities for incorporating the same |
US6150820A (en) * | 1992-09-28 | 2000-11-21 | Fonar Corporation | Nuclear magnetic resonance apparatus and methods of use and facilities for incorporating the same |
WO1996022828A1 (en) * | 1995-01-25 | 1996-08-01 | Gaz Metropolitain And Company, Limited Partnership | Selective catalytic reduction of nitrogen oxides |
US5612010A (en) * | 1995-01-25 | 1997-03-18 | Gas Metropolitain & Company, Limited | Selective catalytic reduction of nitrogen oxides |
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US6879157B1 (en) | 2000-11-22 | 2005-04-12 | Fonar Corporation | Ferromagnetic frame with laminated carbon steel |
US6670296B2 (en) | 2001-01-11 | 2003-12-30 | Delphi Technologies, Inc. | Alumina/zeolite lean NOx catalyst |
US6624113B2 (en) | 2001-03-13 | 2003-09-23 | Delphi Technologies, Inc. | Alkali metal/alkaline earth lean NOx catalyst |
US6576587B2 (en) | 2001-03-13 | 2003-06-10 | Delphi Technologies, Inc. | High surface area lean NOx catalyst |
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US6455463B1 (en) | 2001-03-13 | 2002-09-24 | Delphi Technologies, Inc. | Alkaline earth/transition metal lean NOx catalyst |
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