JPH03213149A - Manufacture of nitrogen oxide decomposing catalyst - Google Patents
Manufacture of nitrogen oxide decomposing catalystInfo
- Publication number
- JPH03213149A JPH03213149A JP2004898A JP489890A JPH03213149A JP H03213149 A JPH03213149 A JP H03213149A JP 2004898 A JP2004898 A JP 2004898A JP 489890 A JP489890 A JP 489890A JP H03213149 A JPH03213149 A JP H03213149A
- Authority
- JP
- Japan
- Prior art keywords
- zeolite
- copper
- solution
- catalyst
- present
- 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.)
- Granted
Links
- 239000003054 catalyst Substances 0.000 title claims abstract description 32
- MWUXSHHQAYIFBG-UHFFFAOYSA-N Nitric oxide Chemical compound O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 title claims abstract description 28
- 238000004519 manufacturing process Methods 0.000 title claims description 7
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 claims abstract description 32
- 239000010457 zeolite Substances 0.000 claims abstract description 32
- 229910021536 Zeolite Inorganic materials 0.000 claims abstract description 31
- 239000000243 solution Substances 0.000 claims abstract description 13
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 claims abstract description 12
- 229910052802 copper Inorganic materials 0.000 claims abstract description 12
- 239000010949 copper Substances 0.000 claims abstract description 12
- 229910001860 alkaline earth metal hydroxide Inorganic materials 0.000 claims abstract description 8
- 239000005749 Copper compound Substances 0.000 claims abstract description 7
- 150000001880 copper compounds Chemical class 0.000 claims abstract description 7
- 239000007864 aqueous solution Substances 0.000 claims abstract description 6
- 238000000354 decomposition reaction Methods 0.000 claims description 4
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 abstract description 15
- 238000000034 method Methods 0.000 abstract description 15
- 229910021529 ammonia Inorganic materials 0.000 abstract description 7
- 230000000694 effects Effects 0.000 abstract description 7
- 229910052751 metal Inorganic materials 0.000 abstract description 5
- 239000002184 metal Substances 0.000 abstract description 5
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 abstract description 3
- 239000000920 calcium hydroxide Substances 0.000 abstract description 3
- 229910001861 calcium hydroxide Inorganic materials 0.000 abstract description 3
- VTHJTEIRLNZDEV-UHFFFAOYSA-L magnesium dihydroxide Chemical compound [OH-].[OH-].[Mg+2] VTHJTEIRLNZDEV-UHFFFAOYSA-L 0.000 abstract description 3
- 239000000347 magnesium hydroxide Substances 0.000 abstract description 3
- 229910001862 magnesium hydroxide Inorganic materials 0.000 abstract description 3
- 229910052680 mordenite Inorganic materials 0.000 abstract description 3
- 239000006185 dispersion Substances 0.000 abstract 3
- 229910000365 copper sulfate Inorganic materials 0.000 abstract 1
- ARUVKPQLZAKDPS-UHFFFAOYSA-L copper(II) sulfate Chemical compound [Cu+2].[O-][S+2]([O-])([O-])[O-] ARUVKPQLZAKDPS-UHFFFAOYSA-L 0.000 abstract 1
- 239000007789 gas Substances 0.000 description 10
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 4
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 4
- 239000000203 mixture Substances 0.000 description 4
- 239000001301 oxygen Substances 0.000 description 4
- 229910052760 oxygen Inorganic materials 0.000 description 4
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 4
- 238000006243 chemical reaction Methods 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 2
- BYFGZMCJNACEKR-UHFFFAOYSA-N aluminium(i) oxide Chemical compound [Al]O[Al] BYFGZMCJNACEKR-UHFFFAOYSA-N 0.000 description 2
- RQPZNWPYLFFXCP-UHFFFAOYSA-L barium dihydroxide Chemical compound [OH-].[OH-].[Ba+2] RQPZNWPYLFFXCP-UHFFFAOYSA-L 0.000 description 2
- 229910001863 barium hydroxide Inorganic materials 0.000 description 2
- 150000001768 cations Chemical class 0.000 description 2
- 239000003638 chemical reducing agent Substances 0.000 description 2
- XTVVROIMIGLXTD-UHFFFAOYSA-N copper(II) nitrate Chemical compound [Cu+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O XTVVROIMIGLXTD-UHFFFAOYSA-N 0.000 description 2
- 238000001035 drying Methods 0.000 description 2
- 229930014626 natural product Natural products 0.000 description 2
- 239000002245 particle Substances 0.000 description 2
- 150000003839 salts Chemical class 0.000 description 2
- 229920006395 saturated elastomer Polymers 0.000 description 2
- 239000000377 silicon dioxide Substances 0.000 description 2
- 239000002912 waste gas Substances 0.000 description 2
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 1
- TWRXJAOTZQYOKJ-UHFFFAOYSA-L Magnesium chloride Chemical compound [Mg+2].[Cl-].[Cl-] TWRXJAOTZQYOKJ-UHFFFAOYSA-L 0.000 description 1
- ODUCDPQEXGNKDN-UHFFFAOYSA-N Nitrogen oxide(NO) Natural products O=N ODUCDPQEXGNKDN-UHFFFAOYSA-N 0.000 description 1
- 238000002441 X-ray diffraction Methods 0.000 description 1
- 239000000809 air pollutant Substances 0.000 description 1
- 231100001243 air pollutant Toxicity 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 229910000323 aluminium silicate Inorganic materials 0.000 description 1
- 238000004458 analytical method Methods 0.000 description 1
- 230000003872 anastomosis Effects 0.000 description 1
- 238000001479 atomic absorption spectroscopy Methods 0.000 description 1
- 239000011230 binding agent Substances 0.000 description 1
- 238000003421 catalytic decomposition reaction Methods 0.000 description 1
- 238000010531 catalytic reduction reaction Methods 0.000 description 1
- 238000005119 centrifugation Methods 0.000 description 1
- 239000004927 clay Substances 0.000 description 1
- 229910052570 clay Inorganic materials 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 239000013078 crystal Substances 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 229910052675 erionite Inorganic materials 0.000 description 1
- 238000011156 evaluation Methods 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 238000009472 formulation Methods 0.000 description 1
- 238000004817 gas chromatography Methods 0.000 description 1
- 150000003840 hydrochlorides Chemical class 0.000 description 1
- 239000001257 hydrogen Substances 0.000 description 1
- 229910052739 hydrogen Inorganic materials 0.000 description 1
- 238000001027 hydrothermal synthesis Methods 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-M hydroxide Chemical compound [OH-] XLYOFNOQVPJJNP-UHFFFAOYSA-M 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 229910052809 inorganic oxide Inorganic materials 0.000 description 1
- 238000005342 ion exchange Methods 0.000 description 1
- 239000000395 magnesium oxide Substances 0.000 description 1
- CPLXHLVBOLITMK-UHFFFAOYSA-N magnesium oxide Inorganic materials [Mg]=O CPLXHLVBOLITMK-UHFFFAOYSA-N 0.000 description 1
- AXZKOIWUVFPNLO-UHFFFAOYSA-N magnesium;oxygen(2-) Chemical compound [O-2].[Mg+2] AXZKOIWUVFPNLO-UHFFFAOYSA-N 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 150000002739 metals Chemical class 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 150000002823 nitrates Chemical class 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 238000002360 preparation method Methods 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 239000012047 saturated solution Substances 0.000 description 1
- UUCCCPNEFXQJEL-UHFFFAOYSA-L strontium dihydroxide Chemical compound [OH-].[OH-].[Sr+2] UUCCCPNEFXQJEL-UHFFFAOYSA-L 0.000 description 1
- 229910001866 strontium hydroxide Inorganic materials 0.000 description 1
- 150000003467 sulfuric acid derivatives Chemical class 0.000 description 1
Landscapes
- Catalysts (AREA)
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
Abstract
Description
【発明の詳細な説明】
[産業上の利用分野コ
本発明は窒素酸化物を含むガスから、それを分解によっ
て除去する触媒の製造法に関するものであり、さらに詳
しくは一酸化窒素を分解するゼオライト系の触媒の製造
法に関するものである。Detailed Description of the Invention [Field of Industrial Application] The present invention relates to a method for producing a catalyst that removes nitrogen oxides from a gas by decomposition, and more specifically relates to a method for producing a catalyst that removes nitrogen oxides from a gas by decomposition. The present invention relates to a method for producing a catalyst of this type.
[従来技術]
環境保全の観点から、大気汚染物質の除去は大きな社会
的な課題である。とりわけ産業活動の拡大に伴う燃焼廃
ガスの浄化は、現在の緊急課題である。固定発生源であ
る工場や、移動発生源である自動車から排出されるガス
中に含まれる窒素酸化物は、光化学スモッグの原因と言
われ人体に留置なガスである。特に−酸化窒素(No)
は除去がむずかしく、検討課題となっている。[Prior Art] From the perspective of environmental conservation, the removal of air pollutants is a major social issue. In particular, purification of combustion waste gas accompanying the expansion of industrial activities is a current urgent issue. Nitrogen oxides contained in gases emitted from factories, which are fixed sources, and automobiles, which are mobile sources, are said to be the cause of photochemical smog, and are gases that remain in the human body. Especially - Nitrogen oxide (No)
It is difficult to remove and is an issue to be considered.
これまでにもいくつかの方法が考えられている。例えば
接触還元法と呼ばれる方法は、アンモニアや水素などの
還元剤を用い触媒上で、NOをN2とN20にして除去
する方法である。しかしながら還元剤を利用するため、
その回収や漏れの対策が必要で、規模が大きな固定発生
源については有利だが、自動車のような発生源には適さ
ない。一方、排気ガスが還元性ガスであるガソリンエン
ジンの廃ガス浄化には、これまでに多くの触媒が開発さ
れて、一般に使用されている。しかしながらこれらの触
媒は、酸素共存下では用いることができない。Several methods have been considered so far. For example, a method called catalytic reduction method is a method of removing NO by converting it into N2 and N20 on a catalyst using a reducing agent such as ammonia or hydrogen. However, since a reducing agent is used,
It is advantageous for large-scale stationary sources that require measures to recover and prevent leakage, but is not suitable for sources such as automobiles. On the other hand, many catalysts have been developed and are commonly used to purify the exhaust gas of gasoline engines whose exhaust gas is a reducing gas. However, these catalysts cannot be used in the coexistence of oxygen.
ところで、NOの接触分解、すなわちNOを直接N2と
02に分解する法は、排気ガスを触媒層に通ずるだけで
すみ極めて簡便なため利用範囲は広い。これについても
従来より触媒が見いだされている。p、、c、1c、系
触媒がNOの分解活性に効果があるが、いずれも生成す
る酸素によって被毒を受けると言う問題があった。通常
ディーゼルエンジンの廃ガスは酸素を含むため、これま
での触媒では対応できず、新規な触媒の開発が望まれて
いる。By the way, the catalytic decomposition of NO, that is, the method of directly decomposing NO into N2 and O2, is extremely simple and can be used in a wide range of applications because it only requires passing exhaust gas through a catalyst layer. Catalysts have been found for this as well. Although p-, c-, and 1c-based catalysts are effective in reducing NO decomposition activity, they all have the problem of being poisoned by the produced oxygen. Diesel engine waste gas usually contains oxygen, which cannot be handled by conventional catalysts, and the development of new catalysts is desired.
[発明が解決しようとする課題] 前記の問題に対していくつかの触媒が提案されている。[Problem to be solved by the invention] Several catalysts have been proposed to address the above problems.
たとえば、特開昭60−125250号公報では銅を含
む特異なゼオライトが、酸素を含む系でNOの分解に効
果があることが開示されている。また銅を含むペロブス
カイトが有効であることもケミストリーレター誌(CH
EMI 5T−RY LETTER)の1988年の
1797〜1800ページに記載されている。とりわけ
調合をゼオライトは優れた性質を持つが、銅を導入する
際イオン交換では長時間必要である。しかしながら最近
、特開平1−9E3011号公帽にアンモニアを用いて
容易に担持する方法が開示された。For example, JP-A-60-125250 discloses that a special zeolite containing copper is effective in decomposing NO in a system containing oxygen. Chemistry Letters (CH
EMI 5T-RY LETTER), 1988, pages 1797-1800. In particular, zeolite has excellent properties when it comes to formulation, but ion exchange requires a long time when introducing copper. However, recently, Japanese Patent Application Laid-Open No. 1-9E3011 discloses a method of easily supporting the particles using ammonia.
しかしながらアンモニアは臭気が強く、取り扱いに手間
がかかるという欠点があり、またアンモニアを用いると
触媒の前処理においてアンモニアガスが発生するという
問題があった。However, ammonia has the disadvantage that it has a strong odor and is time-consuming to handle, and when ammonia is used, there is a problem that ammonia gas is generated during pretreatment of the catalyst.
そこで以上の問題点を解決するため、ゼオライトに銅を
短時間でかつ所定量導入でき、しかも前処理においてア
ンモニアの発生がなく、高活性な触媒の調製法を開発す
る必要がある。Therefore, in order to solve the above problems, it is necessary to develop a method for preparing a highly active catalyst that can introduce a predetermined amount of copper into zeolite in a short time and does not generate ammonia during pretreatment.
[課題を解決する手段]
本発明は前記の問題点を解決するための方法に関するも
のである。すなわち、本発明は、ゼオライトを銅化合物
の水溶液に分散し、その中にアルカリ土類金属の水酸化
物溶液を添加し、pHを少なくとも6.0に調整するこ
とで該ゼオライトに銅を担持することを特徴とする窒素
酸化物の分解触媒の製造方法に関する。[Means for Solving the Problems] The present invention relates to a method for solving the above problems. That is, the present invention disperses zeolite in an aqueous solution of a copper compound, adds an alkaline earth metal hydroxide solution therein, and adjusts the pH to at least 6.0 to support copper on the zeolite. The present invention relates to a method for producing a catalyst for decomposing nitrogen oxides, characterized in that:
本発明で用いられるゼオライトとは結晶性アルミノ珪酸
塩であり、組成は次の式で表わされる。The zeolite used in the present invention is a crystalline aluminosilicate, and its composition is represented by the following formula.
XM2/II O”A1203 ” YS io2”
ZH20(nは陽イオンMの原子価、Xは0.8〜2.
0の範囲の数、yは2.0以上の数、2は0以上の数で
ある。)
ゼオライトの基本構造は5i1A110が規則正しく三
次元に結合したもので、単位構造の違いにより、種々の
構造をとる。ゼオライトには多くの種類が知られている
が、X線回折によって特徴ずけられ、その結晶構造によ
り名称が異なる。例えば天然品として、モルデナイト、
エリオナイト、シャバサイトなど、合成品としてはA型
、X型、Y型、ZSM−5などが挙げられる。XM2/II O"A1203" YS io2"
ZH20 (n is the valence of the cation M, X is 0.8-2.
A number in the range of 0, y is a number greater than or equal to 2.0, and 2 is a number greater than or equal to 0. ) The basic structure of zeolite is that 5i1A110 is regularly bonded in three dimensions, and it takes on various structures depending on the difference in the unit structure. Many types of zeolite are known, but they are characterized by X-ray diffraction and have different names depending on their crystal structure. For example, as a natural product, mordenite,
Examples of synthetic products such as erionite and chabasite include A type, X type, Y type, and ZSM-5.
一般にゼオライトの合成品は、適当なシリカ源、アルミ
ナ源、アルカリ源を混合し、100〜250℃程度の水
熱条件下で結晶化させることで容易に得られる。また前
記の混合物にテンプレートと呼ばれるを機物を添加して
、水熱合成によって得られる。Generally, a synthetic product of zeolite can be easily obtained by mixing a suitable silica source, alumina source, and alkali source and crystallizing the mixture under hydrothermal conditions at about 100 to 250°C. It can also be obtained by hydrothermal synthesis by adding a material called a template to the above mixture.
本発明で用いられるゼオライト類は特に限定しない。天
然品、合成品どちらでもかまわないが、前者では不純物
を含み精製に手間がかかることから、合成品が好ましく
用いられる。Zeolites used in the present invention are not particularly limited. Either natural products or synthetic products may be used, but synthetic products are preferably used because the former contain impurities and require time and effort to purify.
本発明で用いられるゼオライトはY型、モルデナイト型
、ZSM−5が好ましく、更に好ましくはZSM−5で
ある。The zeolite used in the present invention is preferably Y type, mordenite type, or ZSM-5, and more preferably ZSM-5.
本発明で用いられるゼオライトの5iOz/A1□03
モル比は2.0以上、好ましくは2〜t、ooo、さら
に好ましくは20〜200である。5iOz/A1□03 of zeolite used in the present invention
The molar ratio is 2.0 or more, preferably 2-t, ooo, more preferably 20-200.
本発明で用いる銅化合物の水溶液とは、銅化合物を溶か
しこんだ溶液のことで、化合物はどのような形でもかま
わない。例えば、硫酸塩、塩酸塩、硝酸塩、育機酸塩、
金属の複合塩などがある。金属種としてはカチオンを生
成するものが好ましい。銅化合物の濃度は0.1〜10
0g/lが好ましく、さらに0.5〜50g/lが好ま
しい。The aqueous solution of a copper compound used in the present invention is a solution in which a copper compound is dissolved, and the compound may be in any form. For example, sulfates, hydrochlorides, nitrates, ionic salts,
There are also complex metal salts. As the metal species, those that generate cations are preferred. The concentration of copper compounds is 0.1-10
0 g/l is preferable, and 0.5 to 50 g/l is more preferable.
本発明で用いられるアルカリ土類金属の水酸化物として
は、水酸化マグネシウム、水酸化カルシウム、水酸化ス
トロンチウム、水酸化バリウムが好ましい。As the alkaline earth metal hydroxide used in the present invention, magnesium hydroxide, calcium hydroxide, strontium hydroxide, and barium hydroxide are preferable.
なお、アルカリ土類金属水酸化物溶液の作り方は、該水
酸化物を水に溶かしても良いし、該金属の酸化物を水に
溶かして得ることもできる。Note that the alkaline earth metal hydroxide solution may be prepared by dissolving the hydroxide in water, or by dissolving the oxide of the metal in water.
本発明において、アルカリ土類金属水酸化物溶液の添加
量は所定のpHになるように添加すればよい。本発明で
はpHの範囲は少なくとも6.0で、好ましくは6.0
〜13.0で、特に好ましくは1)Hが7.0〜10.
0に調整することである。pHが6.0未清だと銅担持
量が少なく、触媒としての活性が低い。In the present invention, the alkaline earth metal hydroxide solution may be added in an amount such that a predetermined pH is achieved. In the present invention the pH range is at least 6.0, preferably 6.0.
~13.0, particularly preferably 1) H is 7.0~10.
It is to adjust it to 0. When the pH is 6.0, the amount of copper supported is small and the activity as a catalyst is low.
本発明ではpHを調整後にゼオライトを回収するが、そ
の方法は公知の方法でもよく、通常行われる濾過や遠心
分離が好ましい。In the present invention, the zeolite is recovered after adjusting the pH, but the method may be any known method, and commonly used filtration or centrifugation is preferred.
本発明では回収したゼオライトは乾燥してもよい。乾燥
は室温でもよく、また常圧あるいは減圧でもよい。例え
ば50°C以上で5〜24時間乾燥を行なう。さらにゼ
オライトは100〜600℃、好ましくは300〜50
0℃の温度で8〜24時間、好ましくは8〜16時間焼
成してもよい。In the present invention, the recovered zeolite may be dried. Drying may be performed at room temperature, or under normal pressure or reduced pressure. For example, drying is performed at 50° C. or higher for 5 to 24 hours. Furthermore, the zeolite is heated at a temperature of 100 to 600°C, preferably 300 to 50°C.
It may be baked at a temperature of 0° C. for 8 to 24 hours, preferably 8 to 16 hours.
本発明において、ゼオライトの銅の含有量は少なくとも
0.5wt%が好ましく、さらに、好ましくは少なくと
も1.0wt%で、特に、2.0〜5.0wt%が好ま
しい。In the present invention, the copper content of the zeolite is preferably at least 0.5 wt%, more preferably at least 1.0 wt%, particularly preferably 2.0 to 5.0 wt%.
本発明の触媒の工業的な使用方法は、シリカ・アルミナ
等の無機酸化物や粘土をバインダーとして混合し、球状
、柱状、ハニカム状等の適当な形の触媒にして反応装置
に充填する。またゼオライトを銅導入前に成型しておき
、その扱銅を導入する方法であってもよい。いずれにし
ても特に限定されるものではない。In an industrial method of using the catalyst of the present invention, an inorganic oxide such as silica or alumina or clay is mixed as a binder, and the catalyst is formed into a suitable shape such as spherical, columnar, or honeycomb shape, and is filled into a reaction apparatus. Alternatively, a method may be adopted in which zeolite is molded before copper is introduced, and the copper is then introduced. In any case, it is not particularly limited.
本発明の触媒を使用する温度は500〜850℃の範囲
が好ましく、さらに550〜800℃が好ましい。また
本触媒と窒素酸化吻合を処理ガスとの接触時間は限定さ
れるものではない。The temperature at which the catalyst of the present invention is used is preferably in the range of 500 to 850°C, more preferably 550 to 800°C. Further, the contact time between the present catalyst and the treatment gas for nitrogen oxidation anastomosis is not limited.
[実施例コ 次に、実施例によって本発明を更に詳しく述べる。[Example code] Next, the present invention will be described in more detail with reference to Examples.
実」L例」!ヱj−
8iO3/Al2O,のモル比が約50のZSM−5ゼ
オライト3.0gを、0.5gのの硝酸銅を含む500
m1の溶液に分散し、水酸化バリウムの飽和水溶液を少
量ずつ滴下して所定のpHに調整した。その後、ゼオラ
イトを濾過しイオン交換水で充分洗浄した。得られたゼ
オライトを減圧乾燥して触媒A−Eを得た。Actually "L example"! 3.0 g of ZSM-5 zeolite with a molar ratio of 8iO3/Al2O of about 50 was added to 500 g of ZSM-5 zeolite containing 0.5 g of copper nitrate.
ml solution, and a saturated aqueous solution of barium hydroxide was added dropwise little by little to adjust the pH to a predetermined value. Thereafter, the zeolite was filtered and thoroughly washed with ion-exchanged water. The obtained zeolite was dried under reduced pressure to obtain catalysts A-E.
比」L例」−
pHを4.0に調整する他は実施例と同様に行った。こ
のようにして触媒Fを得た。Ratio "Example L" - The same procedure as in Example was carried out except that the pH was adjusted to 4.0. Catalyst F was thus obtained.
比Jし医2工
実施例と同じゼオライトを用い、0.5gの硝酸銅を含
む500m1の溶液に分散し、20時間撹拌した。その
後、ゼオライトを鑓過しイオン交換水で充分洗浄した。Using the same zeolite as in the Example, it was dispersed in 500 ml of a solution containing 0.5 g of copper nitrate, and stirred for 20 hours. Thereafter, the zeolite was filtered and thoroughly washed with ion-exchanged water.
得られたゼオライトを減圧乾燥して触媒Gを得た。The obtained zeolite was dried under reduced pressure to obtain catalyst G.
実JJL亀:1−
水酸化カルシウムの飽和水溶液つくり実施例1と同じ方
法でpHを8.0に調整し、触媒Hを得た。Real JJL Turtle: 1- Preparation of a saturated aqueous solution of calcium hydroxide The pH was adjusted to 8.0 in the same manner as in Example 1, and Catalyst H was obtained.
さらに酸化マグネシウムの飽和溶液を調整し、それをマ
グネシウムの水酸化物溶液として実施例工と同じ方法で
、pHを8.0に調整して触媒Iを得た。Furthermore, a saturated solution of magnesium oxide was prepared, and this solution was used as a magnesium hydroxide solution, and the pH was adjusted to 8.0 in the same manner as in the example, to obtain catalyst I.
評1例−
前記で得られた触媒を500℃で焼成し、それを原子吸
光法で銅の担持量を求めた。Evaluation Example 1 - The catalyst obtained above was calcined at 500°C, and the amount of copper supported was determined by atomic absorption spectrometry.
また触媒を打錠成型の後、砕いて粒径をそろえたもので
反応評価を行った。すなわち、触媒1゜0gを流通式の
反応器にいれて、Heを流しながら徐々に昇温して50
0℃にした。そこで−酸化窒素500ppmを含むHe
を50m1/minの割合で流し、生成物をガスクロマ
トグラフィーで分析した。なお分析値は、反応後2.0
時間を経過したものである。In addition, after the catalyst was compressed into tablets, it was crushed to have a uniform particle size, and the reaction was evaluated. That is, 1.0 g of catalyst was placed in a flow reactor, and the temperature was gradually raised while He was flowing.
The temperature was set to 0°C. So - He containing 500 ppm nitrogen oxide
was flowed at a rate of 50 ml/min, and the products were analyzed by gas chromatography. The analysis value is 2.0 after the reaction.
It is something that has passed over time.
結果を第1表、第2表にまとめる。The results are summarized in Tables 1 and 2.
第1表に示すように、本発明の方法によって銅の担持量
が多く、また活性の高い触媒が得られることが分かる。As shown in Table 1, it can be seen that by the method of the present invention, a catalyst with a large amount of copper supported and a high activity can be obtained.
第1表
第2表
第2表にあるように、いろいろなアルカリ土類金属の水
酸化物溶液が利用できることが分かる。As shown in Table 1 and Table 2, it can be seen that various alkaline earth metal hydroxide solutions can be used.
[発明の効果コ
以上に示した本発明の方法によって、ゼオライトに金属
を短時間で容易に、かつ所定量導入でき、しかも前処理
においてアンモニアの発生力ない。また得られた触媒の
活性は高く、−酸化窒素の濃度が低いガスからも、
効率よく一酸化窒素を
除去できる。[Effects of the Invention] By the method of the present invention described above, metals can be easily introduced into zeolite in a predetermined amount in a short time, and there is no generation of ammonia in the pretreatment. Furthermore, the resulting catalyst has high activity and can efficiently remove nitrogen monoxide even from gases with low concentrations of nitrogen oxide.
Claims (1)
にアルカリ土類金属の水酸化物溶液を添加し、pHを少
なくとも6.0に調整することで該ゼオライトに銅を担
持することを特徴とする窒素酸化物の分解触媒の製造方
法。(1) Copper is supported on the zeolite by dispersing the zeolite in an aqueous solution of a copper compound, adding an alkaline earth metal hydroxide solution therein, and adjusting the pH to at least 6.0. A method for producing a nitrogen oxide decomposition catalyst.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2004898A JP2892410B2 (en) | 1990-01-12 | 1990-01-12 | Method for producing nitrogen oxide decomposition catalyst |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2004898A JP2892410B2 (en) | 1990-01-12 | 1990-01-12 | Method for producing nitrogen oxide decomposition catalyst |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH03213149A true JPH03213149A (en) | 1991-09-18 |
| JP2892410B2 JP2892410B2 (en) | 1999-05-17 |
Family
ID=11596492
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP2004898A Expired - Fee Related JP2892410B2 (en) | 1990-01-12 | 1990-01-12 | Method for producing nitrogen oxide decomposition catalyst |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP2892410B2 (en) |
Family Cites Families (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| EP1442745A1 (en) | 1993-10-07 | 2004-08-04 | Euro-Celtique | Orally administrable opioid formulations having extended duration of effect |
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1990
- 1990-01-12 JP JP2004898A patent/JP2892410B2/en not_active Expired - Fee Related
Also Published As
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|---|---|
| JP2892410B2 (en) | 1999-05-17 |
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