JP2000157872A - Halogen-containing organic compound-decomposing catalyst, production thereof, and waste gas treatment method - Google Patents

Halogen-containing organic compound-decomposing catalyst, production thereof, and waste gas treatment method

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Publication number
JP2000157872A
JP2000157872A JP10337767A JP33776798A JP2000157872A JP 2000157872 A JP2000157872 A JP 2000157872A JP 10337767 A JP10337767 A JP 10337767A JP 33776798 A JP33776798 A JP 33776798A JP 2000157872 A JP2000157872 A JP 2000157872A
Authority
JP
Japan
Prior art keywords
catalyst
halogen
component
organic compound
containing organic
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
Application number
JP10337767A
Other languages
Japanese (ja)
Other versions
JP3762121B2 (en
Inventor
Masatoshi Fujisawa
雅敏 藤澤
Yasuyoshi Kato
泰良 加藤
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Mitsubishi Power Ltd
Original Assignee
Babcock Hitachi KK
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Babcock Hitachi KK filed Critical Babcock Hitachi KK
Priority to JP33776798A priority Critical patent/JP3762121B2/en
Publication of JP2000157872A publication Critical patent/JP2000157872A/en
Application granted granted Critical
Publication of JP3762121B2 publication Critical patent/JP3762121B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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Abstract

PROBLEM TO BE SOLVED: To decompose halogen-containing organic compounds at high efficiency for a long duration by preventing deterioration of catalytic activity by deliquescent components. SOLUTION: This halogen-containing organic compound-decomposing catalyst comprises a component having a function of oxidizing and decomposing halogen- containing organic compounds, and a coating formed on the component has a coating containing an organic porous component, a mixture coating containing an organic porous component and an inorganic oxide particle or a mixture coating containing an organic porous component and a catalyst component particle formed thereon. The method for producing the halogen-containing organic compound decomposition catalyst comprises applying at least one type of slurries or emulsions containing components selected from an organic porous component, a mixture containing an organic porous component and an inorganic oxide particle, and a mixture containing an organic porous component and a catalyst component particle to the surface of a halogen-containing organic compound decomposition catalyst and forming a porous coating by drying the resultant halogen-containing organic compound decomposition catalyst.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明はハロゲン含有有機化
合物分解触媒およびその製法ならびに排ガス処理方法に
関し、さらに詳しくはアルカリ金属、アルカリ土類金属
などの潮解性成分を含む排ガス(特にゴミ焼却炉排ガ
ス)中のダイオキシンなどのハロゲン含有有機化合物
を、長期にわたり効率よく浄化するのに好適なハロゲン
含有有機化合物分解触媒およびその製法ならびに排ガス
処理方法に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a catalyst for decomposing a halogen-containing organic compound, a method for producing the same, and an exhaust gas treatment method, and more particularly, to an exhaust gas containing a deliquescent component such as an alkali metal or an alkaline earth metal (particularly, an exhaust gas from a garbage incinerator). TECHNICAL FIELD The present invention relates to a halogen-containing organic compound decomposition catalyst suitable for efficiently purifying a halogen-containing organic compound such as dioxin for a long period of time, a production method thereof, and an exhaust gas treatment method.

【0002】[0002]

【従来の技術】ゴミ焼却炉などから排出されるハロゲン
化芳香族化合物、特にポリ塩化ジベンゾジオキシンやポ
リ塩化ジベンゾフランなどの一般にダイオキシン類と言
われる物質は非常に毒性が高く、近年、ダイオキシン類
の発ガン性が深刻な問題となり、厚生省の新ガイドライ
ンにより厳しい排出規制がなされている。
2. Description of the Related Art Halogenated aromatic compounds discharged from refuse incinerators and the like, particularly substances generally called dioxins, such as polychlorinated dibenzodioxins and polychlorinated dibenzofurans, are extremely toxic. Cancer has become a serious problem, and new emission guidelines have been strictly regulated by the Ministry of Health and Welfare.

【0003】ダイオキシン類の浄化用触媒および浄化方
法については多くの研究がなされている。例えば、特開
平5−245343号公報には、Ti、Si、Zr、A
lおよびVから選択されVを必ず含むA成分と、Pt、
Pd、Ru、Mn、Cu、CrおよびFeからなる群か
ら選択されるB成分とを含んだ触媒を用いて、温度範囲
150〜450℃、空間速度20,000 h-1以下、か
つ触媒表面面積1m2当たりのガス量100m3/Hr( at te
mp )の条件で浄化する方法が提案されている。また特開
平4−284849号公報には、酸性ゼオライトまたは
酸性ゼオライトに遷移金属を担持および/またはイオン
交換して得られる触媒を用いる浄化方法が提案され、さ
らに特開平4−503772号公報には、酸化チタン
型、酸化鉄型またはゼオライト型などの脱硝触媒または
変性脱硝触媒で、特に酸化チタン型の場合、チタン含有
量が70重量%以上で供与体として酸化タングステン、
酸化モリブデンおよび/または酸化バナジウムを含む触
媒を、150〜500℃の温度で酸化性条件の下に処理
を行う浄化方法が提案されている。
Many studies have been made on dioxin purifying catalysts and purifying methods. For example, JP-A-5-245343 discloses that Ti, Si, Zr, A
A component selected from l and V and containing V, Pt,
Using a catalyst containing a B component selected from the group consisting of Pd, Ru, Mn, Cu, Cr and Fe, a temperature range of 150 to 450 ° C., a space velocity of 20,000 h −1 or less, and a catalyst surface area 1 m 2 per gas volume 100m 3 / Hr (at te
A method for purifying under the condition of mp) has been proposed. JP-A-4-284849 proposes a purification method using an acidic zeolite or a catalyst obtained by carrying and / or ion-exchanging a transition metal on an acidic zeolite. Further, JP-A-4-503772 discloses a purification method. A denitration catalyst or a modified denitration catalyst such as a titanium oxide type, an iron oxide type or a zeolite type, particularly, in the case of a titanium oxide type, having a titanium content of 70% by weight or more and tungsten oxide as a donor,
A purification method has been proposed in which a catalyst containing molybdenum oxide and / or vanadium oxide is treated under an oxidizing condition at a temperature of 150 to 500 ° C.

【0004】しかしながら、上記の方法に用いられる触
媒は、潮解性成分を含む排ガス処理において、触媒活性
の低下が著しいという欠点があった。例えば、ゴミ焼却
炉から排出される排ガスなどに多く含まれるアルカリ金
属、アルカリ土類金属などの潮解性の高い成分を含む排
ガスを、上記ハロゲン含有有機化合物を分解する触媒で
処理すると、アルカリ塩類がダストとともに触媒表面に
付着し、さらに排ガス中の水分を吸収してアルカリ塩類
の潮解が生じる。潮解したアルカリ塩類は、触媒粒子間
から触媒内部へとしみこんで触媒内の細孔を閉塞すると
ともに、触媒成分と反応して活性点を変質させるため、
触媒の活性を著しく低下させる。この現象は、特に起動
停止時における触媒層温度の昇温・降温時に生じる凝縮
により促進される。そこで、潮解性成分の触媒内部への
進入による触媒活性の低下を防ぐ手段として、起動停止
時においても触媒層を高温に維持して潮解を防ぐなどの
対策がとられているが、設備費およびランニングコスト
が非常に高くなるという問題があった。
[0004] However, the catalyst used in the above method has a drawback that the catalytic activity is remarkably reduced in the treatment of exhaust gas containing a deliquescent component. For example, when an exhaust gas containing a highly deliquescent component such as an alkali metal and an alkaline earth metal, which is contained in a large amount in an exhaust gas discharged from a garbage incinerator, is treated with a catalyst that decomposes the halogen-containing organic compound, alkali salts are removed. It adheres to the catalyst surface together with the dust, and further absorbs the moisture in the exhaust gas to cause deliquescence of the alkali salts. The deliquescent alkali salts infiltrate into the inside of the catalyst from between the catalyst particles, block the pores in the catalyst, and react with the catalyst components to alter the active site,
Significantly reduces the activity of the catalyst. This phenomenon is promoted by condensation that occurs when the temperature of the catalyst layer rises and falls particularly when the startup and shutdown are performed. Therefore, measures have been taken to prevent the deliquescent component from entering the inside of the catalyst, thereby reducing catalyst activity, such as maintaining the catalyst layer at a high temperature even during startup and stopping to prevent deliquescent. There was a problem that the running cost became very high.

【0005】[0005]

【発明が解決しようとする課題】本発明の課題は、上記
従来技術の問題点を解決し、潮解性成分による触媒活性
の低下を防止し、ハロゲン含有有機化合物の分解を長期
間効率よく行うことができるハロゲン含有有機化合物分
解触媒およびその製法ならびに排ガス処理方法を提供す
ることにある。
SUMMARY OF THE INVENTION An object of the present invention is to solve the above-mentioned problems of the prior art, to prevent a decrease in catalytic activity due to a deliquescent component, and to efficiently decompose a halogen-containing organic compound for a long period of time. It is an object of the present invention to provide a halogen-containing organic compound decomposing catalyst, a method for producing the same, and an exhaust gas treatment method.

【0006】[0006]

【課題を解決するための手段】本発明者らは上記課題に
ついて鋭意研究した結果、ハロゲン含有有機化合物を酸
化分解する機能を有する成分の表面に、有機多孔性成分
の皮膜を形成して撥水性を持たせ、潮解性成分の触媒内
部への進入を妨げることにより、上記課題が達成できる
ことを見いだし、本発明に到達したものである。すなわ
ち、本願で特許請求される発明は以下のとおりである。
Means for Solving the Problems The present inventors have conducted intensive studies on the above-mentioned problems, and as a result, have formed a film of an organic porous component on the surface of a component having a function of oxidatively decomposing a halogen-containing organic compound, thereby obtaining water repellency. To prevent the deliquescent component from entering the inside of the catalyst, thereby achieving the above object, and arrived at the present invention. That is, the invention claimed in the present application is as follows.

【0007】(1)ハロゲン含有有機化合物を酸化分解
する機能を有する成分の表面に、有機多孔性成分皮膜、
有機多孔性成分と無機酸化物粒子の混合皮膜または有機
多孔性成分と触媒成分粒子の混合皮膜を形成したことを
特徴とするハロゲン含有有機化合物分解触媒。 (2)前記触媒が、Ti、Zr、SiおよびAlの少な
くとも一種の金属酸化物と、V、MoおよびWの少なく
とも一種の金属酸化物とを含有することを特徴とする
(1)記載のハロゲン含有有機化合物分解触媒。 (3)前記触媒が、活性成分としてPt、Pd、Ru、
RhおよびIrの少なくとも一種の貴金属系成分を含有
することを特徴とする(1)記載のハロゲン含有有機化
合物分解触媒。 (4)前記触媒が、活性成分としてCr、Mn、Fe、
Co、NiおよびCuの少なくとも一種の遷移金属系成
分を含有することを特徴とする(1)記載のハロゲン含
有有機化合物分解触媒。
(1) An organic porous component film, which has a function of oxidizing and decomposing a halogen-containing organic compound,
A halogen-containing organic compound decomposition catalyst, wherein a mixed film of an organic porous component and inorganic oxide particles or a mixed film of an organic porous component and catalyst component particles is formed. (2) The halogen according to (1), wherein the catalyst contains at least one metal oxide of Ti, Zr, Si and Al and at least one metal oxide of V, Mo and W. Containing organic compound decomposition catalyst. (3) The catalyst comprises Pt, Pd, Ru,
The catalyst for decomposing a halogen-containing organic compound according to (1), comprising at least one noble metal component of Rh and Ir. (4) The catalyst comprises Cr, Mn, Fe,
The halogen-containing organic compound decomposition catalyst according to (1), further comprising at least one transition metal component of Co, Ni, and Cu.

【0008】(5)前記有機多孔性成分が、フッ素樹
脂、アクリル樹脂、ポリアミド樹脂およびシリコン樹脂
の少なくとも一種を含むことを特徴とする(1)〜
(4)のいずれかに記載のハロゲン含有有機化合物分解
触媒。 (6)有機多孔性成分、有機多孔性成分と無機酸化物粒
子の混合物および有機多孔性成分と触媒成分粒子の混合
物からなる群から選ばれた少なくとも一種のスラリーま
たはエマルジョンを、ハロゲン含有有機化合物分解触媒
の表面に塗布した後、乾燥させて多孔性皮膜を形成する
ことを特徴とするハロゲン含有有機化合物分解触媒の製
法。 (7)潮解成分を含む排ガスを上記(1)〜(6)のい
ずれかに記載の触媒と120〜350℃の温度で接触さ
せてハロゲン含有有機化合物を分解することを特徴とす
る排ガス処理方法。
(5) The organic porous component contains at least one of a fluorine resin, an acrylic resin, a polyamide resin and a silicone resin.
The catalyst for decomposing a halogen-containing organic compound according to any of (4). (6) decomposing at least one slurry or emulsion selected from the group consisting of an organic porous component, a mixture of an organic porous component and inorganic oxide particles, and a mixture of an organic porous component and catalyst component particles into a halogen-containing organic compound; A method for producing a halogen-containing organic compound decomposition catalyst, which is applied to the surface of a catalyst and then dried to form a porous film. (7) An exhaust gas treatment method comprising decomposing a halogen-containing organic compound by bringing an exhaust gas containing a deliquescent component into contact with the catalyst according to any of (1) to (6) at a temperature of 120 to 350 ° C. .

【0009】[0009]

【作用】本発明による触媒の表面には有機多孔性成分を
含む皮膜が形成されており、該有機多孔性成分は、水や
アルカリ塩類などが潮解した液との接触角が大きく、撥
水性の機能を有し、従って、触媒表面に付着したアルカ
リ塩類が潮解して液状となっても、これらの液を触媒表
面上で球状化させて弾くことができ、潮解性成分の表面
張力による触媒内部への進入を防止することができる。
その結果、触媒細孔の閉塞や活性点の変質による触媒活
性の低下が防止される。一方、有機多孔性の皮膜は、液
体を接触角による撥水性の機能で弾くが、反応ガスや蒸
気などの気体は通すため、ハロゲン含有有機化合物の触
媒による分解反応を妨げることはない。従って、本発明
の触媒を用いることにより、排ガス中に潮解性成分が含
まれる場合でも、装置の起動停止時における触媒層を高
温に維持しなくても、長期間にわたり触媒活性を高く維
持することができる。
A film containing an organic porous component is formed on the surface of the catalyst according to the present invention. The organic porous component has a large contact angle with a liquid deliquescent of water or alkali salts and has a high water repellency. It has a function, so even if the alkali salts attached to the catalyst surface deliquesce and become liquid, these liquids can be spheroidized and repelled on the catalyst surface, and the inside of the catalyst due to the surface tension of the deliquescent component Can be prevented.
As a result, a decrease in catalytic activity due to blockage of the catalyst pores and deterioration of the active site is prevented. On the other hand, an organic porous film repels a liquid by a function of water repellency by a contact angle, but does not hinder a decomposition reaction of a halogen-containing organic compound by a catalyst because a gas such as a reaction gas or a vapor passes therethrough. Therefore, by using the catalyst of the present invention, even when the deliquescent component is contained in the exhaust gas, the catalyst activity can be maintained at a high level for a long period of time without maintaining the catalyst layer at a high temperature when the apparatus is stopped. Can be.

【0010】[0010]

【発明の実施の形態】本発明に用いられるハロゲン含有
有機化合物を酸化分解する機能を有する成分としては、
ダイオキシン類等のハロゲン含有有機化合物を酸化浄化
できる成分であれば特に制限なく、例えば、Ti、Z
r、SiおよびAlの少なくとも一種の金属酸化物に、
V、MoおよびWの少なくとも一種の金属酸化物を添加
した触媒組成物を用いることができる。このような触媒
組成物を用いることにより、ハロゲン含有有機化合物の
みならず、同時に窒素酸化物も高効率で除去することが
できる。
DESCRIPTION OF THE PREFERRED EMBODIMENTS Components having a function of oxidatively decomposing a halogen-containing organic compound used in the present invention include:
There is no particular limitation on components capable of oxidizing and purifying halogen-containing organic compounds such as dioxins.
r, at least one metal oxide of Si and Al,
A catalyst composition to which at least one metal oxide of V, Mo and W is added can be used. By using such a catalyst composition, not only halogen-containing organic compounds but also nitrogen oxides can be removed with high efficiency.

【0011】また、NOx、SOxなどの存在下でもハ
ロゲン含有有機化合物の分解性能に優れるPt、Pd、
Ru、RhおよびIrの少なくとも一種を含む貴金属系
触媒組成物や、ハロゲン含有有機化合物の酸化分解に優
れるCr、Mn、Fe、Co、NiおよびCuの少なく
とも一種を含む遷移金属系触媒組成物を用いることもで
きる。上記した触媒組成物は、該触媒組成物の表面に、
後述する有機多孔性成分の皮膜を容易に形成できるよう
に、通常、板状、ハニカム状、粒状などに成型した成型
体として用いられる。例えば、板状成形体は、網状無機
繊維基材の間およびその網目間に触媒組成物を埋めこむ
ことにより得られる。
Further, Pt, Pd, and Pt which are excellent in decomposing performance of a halogen-containing organic compound even in the presence of NOx, SOx, etc.
Use a noble metal based catalyst composition containing at least one of Ru, Rh and Ir, and a transition metal based catalyst composition containing at least one of Cr, Mn, Fe, Co, Ni and Cu which is excellent in oxidative decomposition of halogen-containing organic compounds. You can also. The catalyst composition described above, on the surface of the catalyst composition,
In order to easily form a film of an organic porous component described later, it is usually used as a molded product formed into a plate, a honeycomb, a granule, or the like. For example, the plate-like molded body is obtained by embedding the catalyst composition between the mesh-like inorganic fiber base materials and between the meshes.

【0012】本発明において、有機多孔性成分として
は、フッ素樹脂、アクリル樹脂、ポリアミド樹脂、シリ
コン樹脂などの有機撥水性樹脂が用いられ、これらは単
独でまたは2種以上組み合わせて使用してもよい。有機
多孔性成分の皮膜は、例えば、上記した有機撥水性樹脂
の微粒子を水に分散させてスラリーまたはエマルジョン
とし、これを前記触媒組成物の成型体に刷毛、ローラ、
スプレーにより塗布し、または成型体に含浸させ、その
後、乾燥して水分を蒸発させることにより形成すること
ができる。また有機撥水性樹脂の微粒子を単独で分散さ
せたスラリーの代わりに、シリカなどの無機酸化物微粒
子と共分散させたスラリーや、触媒成分粒子と共分散さ
せたスラリーを用いることもできる。また成分中に有機
バインダなどを多く含んでいるものは、皮膜形成後、焼
成して除去してもよい。
In the present invention, as the organic porous component, an organic water-repellent resin such as a fluororesin, an acrylic resin, a polyamide resin and a silicone resin is used, and these may be used alone or in combination of two or more. . The film of the organic porous component, for example, by dispersing the fine particles of the organic water-repellent resin in water to form a slurry or an emulsion, and brushing the molded product of the catalyst composition with a brush, a roller,
It can be formed by applying by spraying or impregnating a molded body, and then drying and evaporating water. Instead of a slurry in which organic water-repellent resin particles are dispersed alone, a slurry in which inorganic oxide particles such as silica are co-dispersed or a slurry in which catalyst component particles are co-dispersed can also be used. Those containing a large amount of an organic binder or the like in the components may be removed by firing after forming the film.

【0013】上記有機撥水性樹脂の微粒子は、球状の微
粒子であっても、またはフィブリルのような微細な繊維
状物であってもよい。該微粒子のサイズは、触媒の細孔
に入り込んで閉塞しないように、一般には500Å以上
とするのが好ましい。また有機多孔性成分の皮膜は、皮
膜の厚さが厚くなると、撥水効果は向上するが、触媒内
への排ガスの拡散が阻害され、触媒の活性が低下し易く
なり、またコスト高を招き、一方、皮膜の厚さが薄くな
ると、皮膜が形成されない箇所が生じやすくなり、そこ
から潮解したアルカリ液が進入し、触媒の劣化が生じや
すくなるため、薄くてかつ緻密な皮膜を形成するのが好
ましい。このためには、触媒表面に、あらかじめ低濃度
の有機撥水性樹脂を含む分散液を塗布して乾燥した後、
上記濃度より高濃度の有機撥水性樹脂を含む分散液をさ
らに塗布して乾燥するのが好ましい。
The fine particles of the organic water-repellent resin may be spherical fine particles or fine fibrous materials such as fibrils. In general, the size of the fine particles is preferably 500 ° or more so as not to enter the pores of the catalyst and block. In addition, when the thickness of the organic porous component coating is increased, the water repellent effect is improved, but the diffusion of exhaust gas into the catalyst is hindered, the activity of the catalyst is easily reduced, and the cost is increased. On the other hand, when the thickness of the film is reduced, a portion where the film is not formed is apt to be formed, and the deliquescent alkali solution enters from there, and the catalyst is easily deteriorated, so that a thin and dense film is formed. Is preferred. To this end, a dispersion containing a low-concentration organic water-repellent resin is applied to the catalyst surface in advance and dried,
It is preferable that a dispersion containing an organic water-repellent resin having a concentration higher than the above concentration is further applied and dried.

【0014】本発明における触媒を用いて潮解成分を含
む排ガス中のハロゲン含有有機化合物を分解させるに
は、触媒の活性、分解効率、ランニングコストまたは耐
久性等の点から、該触媒と排ガスを120〜350℃の
温度で接触させるのが好ましく、より好ましくは200
〜250℃の温度である。
In order to decompose the halogen-containing organic compound in the exhaust gas containing the deliquescent component using the catalyst of the present invention, the catalyst and the exhaust gas must be decomposed in view of the activity, decomposition efficiency, running cost or durability of the catalyst. The contact is preferably carried out at a temperature of ~ 350 ° C, more preferably 200 ° C.
温度 250 ° C.

【0015】[0015]

【実施例】以下、本発明を実施例によりさらに詳細に説
明するが、本発明はこれらに限定されるものではない。 実施例1 酸化チタン粉末およびメタバナジン酸アンモニウムに、
蓚酸および水を加え、ニーダで混練して原子比(V/T
i)が10/90である触媒ペーストを調製した。一
方、繊維径9μmのEガラス繊維1400本の捻糸を1
0本/インチで平織りにした網状物に、チタニア、シリ
カゾルおよびポリビニルアルコールのスラリーを含浸し
て乾燥し、剛性のある触媒基材を作製した。
EXAMPLES Hereinafter, the present invention will be described in more detail with reference to Examples, but the present invention is not limited thereto. Example 1 Titanium oxide powder and ammonium metavanadate
Add oxalic acid and water, knead with a kneader, and adjust the atomic ratio (V / T
A catalyst paste having i) of 10/90 was prepared. On the other hand, 1400 twisted yarns of E glass fiber having a fiber diameter of 9 μm
A mesh of titania, silica sol and polyvinyl alcohol was impregnated and dried in a net-like material plain woven at 0 pieces / inch to produce a rigid catalyst substrate.

【0016】触媒ペーストを二枚の触媒基材の間に挟
み、圧延ローラを通して厚さ1.0mmの板状成型体を成
型し、さらに該成型体を12時間大気中で風乾後、50
0℃で2時間焼成して板状触媒とした。この板状触媒を
活性測定用の寸法20×100mmに切断し、フッ素樹脂
懸濁液(三井・デュポンフロロケミカル社製、MDFデ
ィスパージョン、30−J)のフッ素樹脂濃度を36重
量%に希釈した溶液に含浸し、液切りして大気中で乾燥
し、この工程を2回繰り返して触媒表面に有機多孔性の
皮膜を形成した。このときの皮膜の厚さは約0.05mm
であった。
The catalyst paste is sandwiched between two catalyst base materials, a 1.0 mm-thick plate-like molded product is molded through a rolling roller, and the molded product is air-dried in the air for 12 hours.
It was calcined at 0 ° C. for 2 hours to obtain a plate catalyst. This plate-like catalyst was cut into a size of 20 × 100 mm for activity measurement, and the fluororesin concentration of a fluororesin suspension (MDF dispersion, 30-J, manufactured by DuPont Fluorochemicals, Mitsui) was reduced to 36% by weight. The solution was impregnated, drained, and dried in the air. This process was repeated twice to form an organic porous film on the catalyst surface. The thickness of the film at this time is about 0.05mm
Met.

【0017】実施例2 酸化チタン粉末、モリブデン酸アンモニウムおよびメタ
バナジン酸アンモニウムに、蓚酸、強度を持たせるため
の無機繊維(商品名カオウール)および水を加え、ニー
ダで混練し、原子比(V/Ti/Mo)が7/88/5
である触媒ペーストを得た。得られた触媒ペーストを、
実施例1と同様にして触媒基材二枚の間に挟み、圧延ロ
ーラを通して厚さ1.0mmの板状成型体を成型し、さら
に12時間大気中で風乾後、500℃で2時間焼成して
板状触媒とした。該板状触媒を20×100mmに切断
後、実施例1に示すフッ素樹脂懸濁液の希釈溶液に10
重量%の触媒粉末を加えた溶液を用いて実施例1と同様
にして触媒表面に有機多孔性の皮膜を形成した。このと
きの皮膜の厚さは約0.05mmであった。
EXAMPLE 2 To titanium oxide powder, ammonium molybdate and ammonium metavanadate, oxalic acid, inorganic fiber (trade name: kao wool) for imparting strength and water were added, and the mixture was kneaded with a kneader to obtain an atomic ratio (V / Ti). / Mo) is 7/88/5
Was obtained. The obtained catalyst paste is
In the same manner as in Example 1, sandwiched between two catalyst substrates, a 1.0 mm-thick plate-like molded product was molded through a rolling roller, further air-dried in the air for 12 hours, and then fired at 500 ° C. for 2 hours. To obtain a plate-like catalyst. After cutting the plate-like catalyst into 20 × 100 mm, 10 μl was added to the diluted solution of the fluororesin suspension shown in Example 1.
An organic porous film was formed on the surface of the catalyst in the same manner as in Example 1 using a solution to which the catalyst powder was added by weight%. At this time, the thickness of the film was about 0.05 mm.

【0018】実施例3 実施例2において、モリブデン酸アンモニウムのかわり
にメタタングステン酸アンモニウムを用いて調整した原
子比(V/Ti/W)が7/88/5である触媒ペース
トを用いた以外は実施例2と同様の方法で板状触媒を作
製し、さらにこの触媒表面に有機多孔性の皮膜を形成し
た。
Example 3 In Example 2, a catalyst paste having an atomic ratio (V / Ti / W) of 7/88/5 adjusted by using ammonium metatungstate instead of ammonium molybdate was used. A plate-like catalyst was prepared in the same manner as in Example 2, and an organic porous film was formed on the surface of the catalyst.

【0019】実施例4 酸化チタンのペーストを実施例1に示した触媒基材に圧
延して板状成型体を得た。この成型体に、Ptの担持量
が触媒重量に対して0.5重量%となるようジニトロジ
アンミン白金酸水溶液を吸いきり含浸させ、次いで50
0℃で2時間焼成して板状触媒を得た。この触媒表面に
実施例1と同様の操作により有機多孔性の皮膜を形成し
た。
Example 4 A paste of titanium oxide was rolled on the catalyst substrate shown in Example 1 to obtain a plate-like molded body. The molded body was sucked and impregnated with an aqueous solution of dinitrodiammineplatinic acid so that the supported amount of Pt was 0.5% by weight based on the weight of the catalyst.
It was calcined at 0 ° C. for 2 hours to obtain a plate-like catalyst. An organic porous film was formed on the surface of the catalyst by the same operation as in Example 1.

【0020】実施例5 酸化アルミニウムのペーストを実施例1に示した触媒基
材に圧延して板状成型体を得た。この成型体にPdの担
持量が触媒重量に対して1重量%となるよう硝酸パラジ
ウム水溶液を吸いきり含浸させ、500℃で2時間焼成
して板状触媒を得た。この触媒表面に、アクリル樹脂エ
マルジョン(カンペ、水性アクリルペイント)を用いて
実施例1と同様の操作により有機多孔性の皮膜を形成し
た。このときの皮膜の厚さは約0.05mmであった。
Example 5 An aluminum oxide paste was rolled on the catalyst substrate shown in Example 1 to obtain a plate-like molded body. An aqueous solution of palladium nitrate was sucked and impregnated into the molded body so that the amount of Pd to be supported was 1% by weight based on the weight of the catalyst, and calcined at 500 ° C. for 2 hours to obtain a plate-like catalyst. An organic porous film was formed on the surface of the catalyst by the same operation as in Example 1 using an acrylic resin emulsion (Campe, water-based acrylic paint). At this time, the thickness of the film was about 0.05 mm.

【0021】実施例6 実施例4において、ジニトロジアンミン白金酸水溶液の
変わりに、Cuが触媒重量に対して5重量%となるよう
硝酸銅水溶液を吸いきり含浸させた以外は、実施例4と
は同様の操作を行って板状触媒に有機多孔性の皮膜を形
成した。
Example 6 Example 4 differs from Example 4 in that, instead of the dinitrodiammineplatinic acid aqueous solution, a copper nitrate aqueous solution was sucked and impregnated so that Cu was 5% by weight with respect to the catalyst weight. The same operation was performed to form an organic porous film on the plate catalyst.

【0022】実施例7 実施例1で得られた板状成型体に、Mnが触媒重量の5
重量%となるよう硝酸マンガン水溶液を吸いきり含浸
し、500℃で2時間焼成して板状触媒とした後、この
触媒表面に実施例1と同様の操作により有機多孔性の皮
膜を形成した。
Example 7 Mn was added to the plate-like molded product obtained in Example 1 in an amount of 5% by weight of the catalyst.
An aqueous solution of manganese nitrate was sucked and impregnated so as to have a weight percentage, and calcined at 500 ° C. for 2 hours to obtain a plate-shaped catalyst. Then, an organic porous film was formed on the surface of the catalyst by the same operation as in Example 1.

【0023】比較例1 実施例1において、板状触媒の表面に有機多孔性の皮膜
を形成する操作を行わなかった。 比較例2 実施例4において、板状触媒の表面に有機多孔性の皮膜
を形成する操作を行わなかった。
Comparative Example 1 In Example 1, the operation of forming an organic porous film on the surface of the plate catalyst was not performed. Comparative Example 2 In Example 4, the operation of forming an organic porous film on the surface of the plate catalyst was not performed.

【0024】<劣化試験I>実施例1〜7および比較例
1、2で得られた板状触媒を用いて表1に示す条件にて
クロロベンゼンの分解率を測定した。さらに、触媒表面
に触媒重量の約20重量%の塩化カルシウムを分散し、
飽和水蒸気条件の室温で24時間放置する模擬劣化試験
を実施した。試験後、表面に付着している塩化カルシウ
ムを水洗した触媒を用いて、クロロベンゼンの分解率お
よび触媒中のカルシウム含有量を測定し、その結果を表
2に示した。
<Deterioration Test I> Using the plate catalysts obtained in Examples 1 to 7 and Comparative Examples 1 and 2, the decomposition rate of chlorobenzene was measured under the conditions shown in Table 1. Further, about 20% by weight of the catalyst weight of calcium chloride is dispersed on the catalyst surface,
A simulated deterioration test was performed in which the sample was left at room temperature under saturated steam conditions for 24 hours. After the test, the decomposition rate of chlorobenzene and the calcium content in the catalyst were measured using a catalyst in which calcium chloride adhering to the surface was washed with water. The results are shown in Table 2.

【0025】<劣化試験II>上記劣化試験において、実
施例1および比較例1で得られた板状触媒を用い、かつ
塩化カルシウムの代わりに硫酸ナトリウムを用いた以外
は上記と同様の方法で模擬劣化試験を行い、試験後のク
ロロベンゼンの分解率および触媒中のナトリウム含有量
を測定し、その結果を表2に示した。
<Deterioration Test II> In the above degradation test, a simulation was performed in the same manner as described above, except that the plate catalysts obtained in Example 1 and Comparative Example 1 were used, and sodium sulfate was used instead of calcium chloride. A deterioration test was performed, and the decomposition rate of chlorobenzene and the sodium content in the catalyst after the test were measured. The results are shown in Table 2.

【0026】[0026]

【表1】 [Table 1]

【0027】[0027]

【表2】 [Table 2]

【0028】表2から明らかなように、本発明における
表面に有機多孔性の皮膜を形成し、撥水性を持たせた触
媒(実施例1〜7)のクロロベンゼンの分解率は、初期
の活性は有機多孔性の皮膜を形成しない比較例1〜2ひ
比べに若干劣るものの、加速劣化試験後も高い活性が維
持される。これに対し、比較例1〜2における従来の触
媒は、初期の活性こそ本発明より若干優れてはいるが、
加速劣化試験後ではほとんど活性がなくなるまで活性低
下する。
As is clear from Table 2, the decomposition rate of chlorobenzene of the catalyst (Examples 1 to 7) of the present invention in which an organic porous film was formed on the surface to impart water repellency was determined. Although slightly inferior to Comparative Examples 1 and 2 in which an organic porous film is not formed, high activity is maintained even after the accelerated deterioration test. On the other hand, the conventional catalysts of Comparative Examples 1 and 2 are slightly better in initial activity than the present invention,
After the accelerated deterioration test, the activity decreases until almost no activity occurs.

【0029】上記結果は、加速劣化試験後の触媒中に含
まれるアルカリ濃度の測定結果から容易に推察できる。
すなわち、従来の触媒からは多量のカルシウムまたはナ
トリウムが検出されたのに対し、本発明による触媒から
はほとんど検出されなかった。このことから、本発明に
おける触媒は、表面に形成した有機多孔性の皮膜により
撥水性の機能を有し、潮解性の塩化カルシウムや硫酸ナ
トリウムの触媒中への進入が阻害され、活性の低下が防
止されていることが分かる。
The above result can be easily inferred from the measurement result of the alkali concentration contained in the catalyst after the accelerated deterioration test.
That is, while a large amount of calcium or sodium was detected from the conventional catalyst, it was hardly detected from the catalyst according to the present invention. From this, the catalyst of the present invention has a water-repellent function due to the organic porous film formed on the surface, inhibits the entry of deliquescent calcium chloride and sodium sulfate into the catalyst, and reduces the activity. It can be seen that it is prevented.

【0030】[0030]

【発明の効果】本発明のハロゲン含有有機化合物分解触
媒によれば、アルカリ金属、アルカリ土類金属などを含
む排ガスのハロゲン含有有機化合物の浄化においても、
アルカリ塩類の潮解による触媒の活性低下を防止するこ
とが可能となり、装置の起動停止時において触媒層を高
温に維持することなく長期にわたり高活性を維持するこ
とが可能となる。また本発明のハロゲン含有有機化合物
分解触媒を用いることにより、ゴミ焼却設備などから排
出される有害物質であるダイオキシン類を長期間高い分
解率で浄化することが可能となる。
According to the catalyst for decomposing a halogen-containing organic compound of the present invention, the purification of a halogen-containing organic compound in an exhaust gas containing an alkali metal, an alkaline earth metal or the like can be performed.
It is possible to prevent a decrease in the activity of the catalyst due to the deliquescence of the alkali salts, and it is possible to maintain a high activity for a long time without maintaining the catalyst layer at a high temperature when the apparatus is stopped. Further, by using the halogen-containing organic compound decomposition catalyst of the present invention, it is possible to purify dioxins, which are harmful substances discharged from refuse incineration facilities, at a high decomposition rate for a long period of time.

フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) B01J 23/30 B01J 23/34 A 23/34 23/40 A 23/40 23/70 A 23/648 B01D 53/36 ZABG 23/70 B01J 23/64 102A 23/847 23/84 301A Fターム(参考) 4D048 AA11 AB03 BA03Y BA06X BA06Y BA07X BA07Y BA08Y BA23X BA23Y BA25Y BA26X BA26Y BA27X BA28X BA28Y BA30X BA35X BA35Y BA36Y BA38Y BA41X BB01 BB03 BB08 BB11 BC07 4G069 AA01 AA08 AA11 BA01A BA02A BA04A BA05A BA22A BA22B BB04A BC31A BC54A BC58A BC59A BC60A BC62A BC66A BC67A BC68A BC70A BC71A BC72A BC74A BC75A CA02 CA10 CA19 EA08 EB10 ED01 EE01 EE02 Continued on the front page (51) Int.Cl. 7 Identification symbol FI Theme coat II (Reference) B01J 23/30 B01J 23/34 A 23/34 23/40 A 23/40 23/70 A 23/648 B01D 53/36 ZABG 23/70 B01J 23/64 102A 23/847 23/84 301A F term (reference) 4D048 AA11 AB03 BA03Y BA06X BA06Y BA07X BA07Y BA08Y BA23X BA23Y BA25Y BA26X BA26Y BA27X BA28X BA28Y BA30X BA35X BA35Y BA36B BB38 BC01 AA01 AA08 AA11 BA01A BA02A BA04A BA05A BA22A BA22B BB04A BC31A BC54A BC58A BC59A BC60A BC62A BC66A BC67A BC68A BC70A BC71A BC72A BC74A BC75A CA02 CA10 CA19 EA08 EB10 ED01 EE01 EE02

Claims (7)

【特許請求の範囲】[Claims] 【請求項1】 ハロゲン含有有機化合物を酸化分解する
機能を有する成分の表面に、有機多孔性成分皮膜、有機
多孔性成分と無機酸化物粒子の混合皮膜または有機多孔
性成分と触媒成分粒子の混合皮膜を形成したことを特徴
とするハロゲン含有有機化合物分解触媒。
An organic porous component film, a mixed film of an organic porous component and inorganic oxide particles, or a mixture of an organic porous component and a catalyst component particle on a surface of a component having a function of oxidizing and decomposing a halogen-containing organic compound. A catalyst for decomposing a halogen-containing organic compound, which has a film formed thereon.
【請求項2】 前記触媒が、Ti、Zr、SiおよびA
lの少なくとも一種の金属酸化物と、V、MoおよびW
の少なくとも一種の金属酸化物とを含有することを特徴
とする請求項1記載のハロゲン含有有機化合物分解触
媒。
2. The catalyst according to claim 1, wherein the catalyst comprises Ti, Zr, Si and A.
l, at least one metal oxide, V, Mo and W
The halogen-containing organic compound decomposition catalyst according to claim 1, comprising at least one metal oxide of the following.
【請求項3】 前記触媒が、活性成分としてPt、P
d、Ru、RhおよびIrの少なくとも一種の貴金属系
成分を含有することを特徴とする請求項1記載のハロゲ
ン含有有機化合物分解触媒。
3. The catalyst according to claim 1, wherein Pt, P
The halogen-containing organic compound decomposition catalyst according to claim 1, further comprising at least one noble metal component of d, Ru, Rh, and Ir.
【請求項4】 前記触媒が、活性成分としてCr、M
n、Fe、Co、NiおよびCuの少なくとも一種の遷
移金属系成分を含有することを特徴とする請求項1記載
のハロゲン含有有機化合物分解触媒。
4. The catalyst according to claim 1, wherein the active component is Cr or M.
The halogen-containing organic compound decomposition catalyst according to claim 1, further comprising at least one transition metal component of n, Fe, Co, Ni, and Cu.
【請求項5】 前記有機多孔性成分が、フッ素樹脂、ア
クリル樹脂、ポリアミド樹脂およびシリコン樹脂の少な
くとも一種を含むことを特徴とする請求項1〜4のいず
れかに記載のハロゲン含有有機化合物分解触媒。
5. The halogen-containing organic compound decomposition catalyst according to claim 1, wherein the organic porous component contains at least one of a fluororesin, an acrylic resin, a polyamide resin, and a silicone resin. .
【請求項6】 有機多孔性成分、有機多孔性成分と無機
酸化物粒子の混合物および有機多孔性成分と触媒成分粒
子の混合物からなる群から選ばれた少なくとも一種のス
ラリーまたはエマルジョンを、ハロゲン含有有機化合物
分解触媒の表面に塗布した後、乾燥させて多孔性皮膜を
形成することを特徴とするハロゲン含有有機化合物分解
触媒の製法。
6. A halogen-containing organic compound comprising at least one slurry or emulsion selected from the group consisting of an organic porous component, a mixture of an organic porous component and inorganic oxide particles, and a mixture of an organic porous component and a catalyst component particles. A method for producing a halogen-containing organic compound decomposition catalyst, which is applied to the surface of a compound decomposition catalyst and then dried to form a porous film.
【請求項7】 潮解成分を含む排ガスを請求項1〜5の
いずれかに記載の触媒と120〜350℃の温度で接触
させてハロゲン含有有機化合物を分解することを特徴と
する排ガス処理方法。
7. An exhaust gas treatment method, comprising contacting an exhaust gas containing a deliquescent component with the catalyst according to claim 1 at a temperature of 120 to 350 ° C. to decompose the halogen-containing organic compound.
JP33776798A 1998-11-27 1998-11-27 Exhaust gas treatment method Expired - Fee Related JP3762121B2 (en)

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Application Number Priority Date Filing Date Title
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JP3762121B2 JP3762121B2 (en) 2006-04-05

Family

ID=18311779

Family Applications (1)

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Country Status (1)

Country Link
JP (1) JP3762121B2 (en)

Also Published As

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