JPH02284648A - Activated catalyst for deodorizing ozone - Google Patents

Activated catalyst for deodorizing ozone

Info

Publication number
JPH02284648A
JPH02284648A JP1105774A JP10577489A JPH02284648A JP H02284648 A JPH02284648 A JP H02284648A JP 1105774 A JP1105774 A JP 1105774A JP 10577489 A JP10577489 A JP 10577489A JP H02284648 A JPH02284648 A JP H02284648A
Authority
JP
Japan
Prior art keywords
catalyst
ozone
reducing agent
reducing
soln
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
JP1105774A
Other languages
Japanese (ja)
Other versions
JP2615196B2 (en
Inventor
Kazuo Sakanaya
和夫 魚屋
Katsuo Seki
勝男 関
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 Heavy Industries Ltd
Original Assignee
Mitsubishi Heavy Industries Ltd
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 Mitsubishi Heavy Industries Ltd filed Critical Mitsubishi Heavy Industries Ltd
Priority to JP1105774A priority Critical patent/JP2615196B2/en
Publication of JPH02284648A publication Critical patent/JPH02284648A/en
Application granted granted Critical
Publication of JP2615196B2 publication Critical patent/JP2615196B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

Links

Landscapes

  • Treating Waste Gases (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)
  • Catalysts (AREA)

Abstract

PURPOSE:To obtain the catalyst which has high performance and also continuously stabilized performance by carrying one or more kinds of metallic oxides on the carbonaceous material and treating the obtained ozone deodorizing catalyst by a reductive soln. and thereafter drying it. CONSTITUTION:In a catalyst producing stage 1, both the starting raw material M1 of a catalytic activator made of one or more kinds of oxides of metals such as vanadium, chromium and manganese and a catalytic carrier M2 such as activated carbon and graphite are molded by an impregnating method and a kneading method. Thereafter the molded body is dried and calcined. Then in a reducing stage 2, the molded body is immersed in a reducing agent soln. M3 such as a formaldehyde aq. soln. and reducing treatment operation is performed while sufficiently agitating the same. Furthermore in a drying stage 3, the vacuum drying operation is performed to separate the reducing agent M3 remaining in the pores of the catalyst and a product M4 is obtained. Therein the ozone decomposing effect is enhanced with increase in the reducing agent concn. Thereby high activation of the catalyst is enabled.

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明は活性化されたオゾン脱臭触媒に関し、特に下水
、し尿、ごみ焼却施設から発生する臭気をオゾン脱臭す
るに際して使用するに適した活性化オゾン脱臭触媒に関
する。
[Detailed Description of the Invention] [Industrial Application Field] The present invention relates to an activated ozone deodorizing catalyst, particularly an activated ozone deodorizing catalyst suitable for use in ozone deodorizing of odors generated from sewage, human waste, and garbage incineration facilities. Regarding ozone deodorizing catalyst.

〔従来の技術〕[Conventional technology]

悪臭成分を気相中でオゾンによシ酸化分解するオゾン脱
臭(悪臭の除去)方法が既に提供されているが、(特公
昭63−39283号公報)この提案方法では、炭素質
材料からなる担体上に金属酸化物を担持させた触媒層を
複数居直列に配設し、かつ、該各層の前部にそれぞれオ
ゾン注入手段を設けることが特徴の1つになっている。
An ozone deodorization (offensive odor removal) method has already been proposed in which odor components are oxidized and decomposed by ozone in the gas phase. One of the features is that a plurality of catalyst layers each carrying a metal oxide are arranged in series, and an ozone injection means is provided in front of each layer.

この提案方法でいう触媒とは、例えば粒状、破砕状また
は粉末状活性炭、グツファイト、炭素繊維などからなる
触媒担体上に、バナジウム、クロム、マンガン、鉄、コ
バルト、ニッケル、銅、銀、亜鉛などの金属酸化物の1
種以上を担持させたもので、必要に応じて白金、バヲジ
ウム、ロジウム、ルテニウムなどを助触媒としてこの金
属酸化物と共に担持させているものである。
The catalyst used in this proposed method is, for example, a catalyst carrier made of granular, crushed or powdered activated carbon, gutphite, carbon fiber, etc. metal oxide 1
If necessary, platinum, barodium, rhodium, ruthenium, etc. are supported together with the metal oxide as a co-catalyst.

この提案方法では触れていないが、上記触媒を製造する
ためには、触媒活性金属酸化物と担体とを成形、乾燥後
、還元雰囲気条件下での焼成が必要にかり、高活性な触
媒を連続して安定製造するのは容易でない面があった。
Although not mentioned in this proposed method, in order to produce the above catalyst, it is necessary to mold the catalytically active metal oxide and the carrier, dry it, and then sinter it under reducing atmosphere conditions, which allows continuous production of the highly active catalyst. However, it was not easy to produce it stably.

〔発明が解決しようとする課題〕[Problem to be solved by the invention]

本発明は、上記技術水準に鑑み、従来のオゾン脱臭触媒
よυ高活性で、かつ、連続して安定した性能をもつオゾ
ン脱臭触媒を提供1〜ようとするものである。
In view of the above-mentioned state of the art, the present invention aims to provide an ozone deodorizing catalyst which is more active than conventional ozone deodorizing catalysts and has continuously stable performance.

〔課題を解決するための手段〕[Means to solve the problem]

本発明は1種以上の金属酸化物を炭素質材料に担持して
なるオゾン脱臭触媒を、還元溶液で処理したのち乾燥し
てなることを特徴とする活性化オゾン脱臭触媒である。
The present invention is an activated ozone deodorizing catalyst, which is obtained by treating an ozone deodorizing catalyst in which one or more metal oxides are supported on a carbonaceous material with a reducing solution and then drying the catalyst.

本発明でいう1種以上の金属酸化物を炭素質材料に担持
したオゾン脱臭触媒とは、粒状、破砕状または粉末状活
性炭、グクファイト、炭素繊維などからなる担体上に、
活性成分としてバナジウム、クロム、マンガン、鉄、コ
バ/I/l、ニッケル、銅、銀、亜鉛などの金属酸化物
の1種以上を担持させたもの、及び必要に応じて白金、
バッジラム、ロジウム、ルテニウムfr、トを助触媒と
して前記金属酸化物と共に担持させたものを成形、乾燥
、焼成してなるものをいう。
The ozone deodorizing catalyst in which one or more metal oxides are supported on a carbonaceous material as used in the present invention refers to an ozone deodorizing catalyst in which one or more metal oxides are supported on a carbonaceous material, and an ozone deodorizing catalyst in which one or more metal oxides are supported on a carbonaceous material is a
One or more metal oxides such as vanadium, chromium, manganese, iron, Koba/I/L, nickel, copper, silver, and zinc are supported as active ingredients, and if necessary, platinum,
It refers to a product obtained by molding, drying, and calcining a product in which badge rhum, rhodium, ruthenium fr, and to are supported together with the metal oxides mentioned above as cocatalysts.

本発明触媒は上記公知のオゾン脱臭触媒を還元溶液で処
理した後、乾燥したものであるが、還元溶液とはホルム
ア/l/ダヒド水溶液、アセトアルデヒドなどの低沸点
アルデヒド水溶液、ヒドロキシルアミン、アスコロビン
酸などの水溶性還元剤が用いられる。還元溶液処理後の
乾燥は酸化を防ぐため、−殻内に100〜180 ’C
The catalyst of the present invention is obtained by treating the above-mentioned known ozone deodorizing catalyst with a reducing solution and then drying it. The reducing solution is a formala/l/dahyde aqueous solution, a low boiling point aldehyde aqueous solution such as acetaldehyde, hydroxylamine, ascobic acid, etc. A water-soluble reducing agent is used. Drying after the reducing solution treatment is carried out at -100-180'C inside the shell to prevent oxidation.
.

好ましくは105=150°Cで行うのが好−!、I−
く、触媒細孔内に残留する還元溶液を除去するためにも
減圧下で行うのが好ましい。
Preferably it is carried out at 105=150°C! ,I-
In addition, it is preferable to carry out the reaction under reduced pressure in order to remove the reducing solution remaining in the catalyst pores.

〔作用〕[Effect]

前記した1種以上の金属酸化物を炭素質材料に担持した
触媒を還元溶液で処理することによって、前記触媒担体
に担持した金属酸化物は部分還元され、このような状態
になった触媒は悪臭成分を酸化分解するオゾン脱臭法に
おける有効な触媒として作用する。
By treating the catalyst in which one or more of the metal oxides described above supported on a carbonaceous material with a reducing solution, the metal oxide supported on the catalyst carrier is partially reduced, and the catalyst in such a state has a bad odor. Acts as an effective catalyst in ozone deodorization methods that oxidize and decompose components.

以下、本発明の活性化オゾン脱臭触媒の製造例の概要を
第1図によって説明する。第1図において、M、は触媒
活性体となる金属酸化物の出発原料、M、は触媒担体、
M、は還元剤溶液、鳩は製品、1は従来触媒製造工程、
2は還元処理工程、3は乾燥工程を示す。
Hereinafter, an outline of a manufacturing example of the activated ozone deodorizing catalyst of the present invention will be explained with reference to FIG. In FIG. 1, M is a starting material for a metal oxide that becomes a catalyst active body, M is a catalyst carrier,
M is the reducing agent solution, pigeon is the product, 1 is the conventional catalyst manufacturing process,
2 indicates a reduction treatment step, and 3 indicates a drying step.

触媒活性体出発原料M、と触媒担体M、を含浸法又は混
練法によって成形後(成形はベレット状、ハニカム状、
繊維布状いづれでもよい)、乾燥・焼成する従来触媒製
造工程1を経たのち、還元工程2において還元処理する
。ここでは、還元剤を含む溶液中に上記触媒製造工程1
を径由した触媒を浸漬、十分にかきまぜI7て還元処理
操作を行なうととKある。還元剤としては、例えばホμ
ムアμ/デヒド水溶液、アセトアルデヒドの低沸点ア/
l/デヒド類、ヒドロキシアミン、アスコロビン酸など
、とくに水溶性還元剤が好ましい、、また、還元剤の濃
度は(11〜10wt%、好ましくは0.5〜5 wt
%がよく、触媒重量に列して1〜5倍(N量)、好まし
くは1〜3倍がよい。溶液温度は室温でよいが、効果を
高めるため、50〜40°Cに上げること本できる。た
だし、その場合は還元剤の蒸発が起ることもあるので注
意を要す。浸漬時間は適宜、金属酸化物の還元処理状態
に合せて調整することになるが、概ね1〜10時間であ
る。
After molding the catalyst active starting material M and the catalyst carrier M by an impregnation method or a kneading method (the molding is performed in a pellet shape, a honeycomb shape,
After passing through the conventional catalyst production step 1 of drying and firing (either in the form of fiber cloth), it is subjected to reduction treatment in the reduction step 2. Here, the above catalyst manufacturing step 1 is added to a solution containing a reducing agent.
The catalyst is immersed and thoroughly stirred to carry out the reduction treatment. As the reducing agent, for example,
Mua μ / Dehyde aqueous solution, low boiling point a of acetaldehyde /
Water-soluble reducing agents such as l/dehydes, hydroxyamines, ascobic acid, etc. are particularly preferable, and the concentration of the reducing agent is (11 to 10 wt%, preferably 0.5 to 5 wt%).
%, preferably 1 to 5 times (N amount), preferably 1 to 3 times the weight of the catalyst. The solution temperature may be at room temperature, but it can be raised to 50 to 40°C to enhance the effect. However, care must be taken in this case as evaporation of the reducing agent may occur. The immersion time will be adjusted as appropriate depending on the state of the reduction treatment of the metal oxide, but is approximately 1 to 10 hours.

つぎに、還元処理した触媒は100−180’C%好ま
しくは105〜150°Cの雰囲気下で乾燥する。乾燥
の促進、及び触媒細孔内に残留する還元剤を迅速に1離
脱するためにも減圧乾燥操作が好ましい。
Next, the reduced catalyst is dried in an atmosphere of 100-180'C%, preferably 105-150C. Drying under reduced pressure is also preferred in order to accelerate drying and quickly remove the reducing agent remaining in the catalyst pores.

第2図に、ホルマリン水溶液を還元剤と1〜だときの効
果の一例を示す。触媒は粒状ヤシガラ活性炭を担体とし
、コバ/1/)酸化物を担持1.たものである。還元剤
濃度の増加に伴いオゾン分解効果(脱臭効果と比例する
)が増大する。1〔実施例〕 ヤシガフ活性炭(4〜6鴎φX4〜10鱈I])を担体
として、酸化コバルトを4wt%担持した触媒を、2 
wt%ホルマリン水溶液に約2時間浸漬したのち取出し
て、水切りし、130°Cで水分およびホルマリン臭が
なくなる壕で減圧乾燥した。
FIG. 2 shows an example of the effect when an aqueous formalin solution is mixed with a reducing agent. The catalyst uses granular coconut shell activated carbon as a carrier, and supports 1. It is something that As the reducing agent concentration increases, the ozone decomposition effect (proportional to the deodorizing effect) increases. 1 [Example] A catalyst in which 4 wt % of cobalt oxide was supported on coconut activated carbon (4 to 6 φX 4 to 10 cod I) was
After being immersed in a wt% formalin aqueous solution for about 2 hours, it was taken out, drained, and dried under reduced pressure at 130°C in a trench to eliminate moisture and formalin odor.

その後、オゾン濃度10 ppmを含む空気を、上記触
[38si!充てんした反応管に、S■=I(−1 toooo   の条件下で通して出口オゾン濃度を測
定し、オゾン分解率を求めた。
Thereafter, air containing an ozone concentration of 10 ppm was introduced into the air [38si! The ozone concentration at the outlet was measured by passing the mixture through the filled reaction tube under the condition of S■=I(-1 toooo), and the ozone decomposition rate was determined.

その結果、オゾン分解率は9995%であった。これに
対し、還元処理をしない触媒のオゾン分解率は99.8
5%であり、両者に差が認められた。
As a result, the ozone decomposition rate was 9995%. In contrast, the ozone decomposition rate of the catalyst without reduction treatment was 99.8.
5%, and a difference was observed between the two.

上記実施例は活性成分として酸化ゴバルトを使用したも
のであるが、その他前記活性触媒成分としてあげた金属
酸化物も該実施例とはソ同様な結果が得られた。
Although the above example used gobalt oxide as the active component, similar results were obtained with other metal oxides listed as the active catalyst component.

〔発明の効果〕〔Effect of the invention〕

戻素質材料触謀担体に金属酸化物を担持した触媒を、還
元溶液にて処理することによって、触媒の高活性化を図
ることができ、恕臭成分を酸化分解するオゾン脱臭法に
おける有効な触媒とすることができた。
By treating a catalyst in which a metal oxide is supported on a catalyst carrier with a reducing solution, the catalyst can be highly activated, making it an effective catalyst in the ozone deodorization method that oxidizes and decomposes odor components. I was able to do this.

【図面の簡単な説明】[Brief explanation of drawings]

第1図は本発明の活性化オゾン脱臭触媒の製造例の工程
図、第2図は本発明触媒の還元溶液処理の効果を示す図
表である。
FIG. 1 is a process diagram of an example of manufacturing the activated ozone deodorizing catalyst of the present invention, and FIG. 2 is a chart showing the effect of treating the catalyst of the present invention with a reducing solution.

Claims (1)

【特許請求の範囲】[Claims] 1種以上の金属酸化物を炭素質材料に担持してなるオゾ
ン脱臭触媒を、還元溶液で処理したのち乾燥してなるこ
とを特徴とする活性化オゾン脱臭触媒。
An activated ozone deodorizing catalyst characterized in that it is obtained by treating an ozone deodorizing catalyst comprising one or more metal oxides supported on a carbonaceous material with a reducing solution and then drying the catalyst.
JP1105774A 1989-04-27 1989-04-27 Method for producing activated ozone deodorizing catalyst Expired - Lifetime JP2615196B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP1105774A JP2615196B2 (en) 1989-04-27 1989-04-27 Method for producing activated ozone deodorizing catalyst

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP1105774A JP2615196B2 (en) 1989-04-27 1989-04-27 Method for producing activated ozone deodorizing catalyst

Publications (2)

Publication Number Publication Date
JPH02284648A true JPH02284648A (en) 1990-11-22
JP2615196B2 JP2615196B2 (en) 1997-05-28

Family

ID=14416508

Family Applications (1)

Application Number Title Priority Date Filing Date
JP1105774A Expired - Lifetime JP2615196B2 (en) 1989-04-27 1989-04-27 Method for producing activated ozone deodorizing catalyst

Country Status (1)

Country Link
JP (1) JP2615196B2 (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0643014A1 (en) * 1993-09-14 1995-03-15 Kuraray Chemical Co., Ltd. Deodorant comprising metal oxide-carrying activated carbon
CN111617767A (en) * 2020-06-03 2020-09-04 南京神克隆水务有限公司 Ozone oxidation catalyst for wastewater treatment and preparation method thereof
CN112264010A (en) * 2020-10-26 2021-01-26 珠海格力电器股份有限公司 Catalyst for normal-temperature decomposition of formaldehyde and preparation method thereof
CN116371419A (en) * 2023-04-21 2023-07-04 中南大学 Microbial carbon-supported manganese-cobalt catalyst and preparation method and application thereof

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5216875A (en) * 1975-07-30 1977-02-08 Hitachi Ltd Splash prevnter for rotational dryer

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5216875A (en) * 1975-07-30 1977-02-08 Hitachi Ltd Splash prevnter for rotational dryer

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0643014A1 (en) * 1993-09-14 1995-03-15 Kuraray Chemical Co., Ltd. Deodorant comprising metal oxide-carrying activated carbon
CN111617767A (en) * 2020-06-03 2020-09-04 南京神克隆水务有限公司 Ozone oxidation catalyst for wastewater treatment and preparation method thereof
CN111617767B (en) * 2020-06-03 2023-08-29 南京神克隆科技有限公司 Ozone oxidation catalyst for wastewater treatment and preparation method thereof
CN112264010A (en) * 2020-10-26 2021-01-26 珠海格力电器股份有限公司 Catalyst for normal-temperature decomposition of formaldehyde and preparation method thereof
CN116371419A (en) * 2023-04-21 2023-07-04 中南大学 Microbial carbon-supported manganese-cobalt catalyst and preparation method and application thereof

Also Published As

Publication number Publication date
JP2615196B2 (en) 1997-05-28

Similar Documents

Publication Publication Date Title
EP0643014B1 (en) Deodorant comprising metal oxide-carrying activated carbon
US5296435A (en) Catalyst and a method of prepare the catalyst
DE2422988A1 (en) PROCESS FOR THE DECOMPOSITION OF HYDROCARBONS
CN106669668B (en) A kind of catalyst and its preparation method and application for amine odor purification
CN108380182A (en) Phenolic resin-based activated carbon and its preparation method and application
JPH02284648A (en) Activated catalyst for deodorizing ozone
KR100506813B1 (en) Mn oxide catalyst for decomposing ozone and the method therefor
JP4201910B2 (en) Titanium oxide composite biomass carbide, method for producing the same, and method for decomposing chemical substances thereby
JPH0780299A (en) Metal oxide added activated carbon catalyst
JPH0210696B2 (en)
JPH0290923A (en) Deodorizing method
JPH07313867A (en) Deodorant composition
JP3135790B2 (en) Deodorant with air cleaning power
JPH082411B2 (en) Deodorization method
JPH0692614A (en) Ozone decomposer and its production
JP2002306581A (en) Deodorant and method of preparation for the same
JP2934978B2 (en) Sepiolite porous body, method for producing the same, and adsorption decomposition catalyst using the same
JP2982661B2 (en) Deodorizing and sterilizing components
JP2663230B2 (en) Air-purified product and method for producing the same
JPH0780056A (en) Deodorizing method
JPH02307511A (en) Ozone decomposer
JPH0647274A (en) Air cleaning material and its production
JPH02253848A (en) Catalyst for decomposition of ozone
JP4639276B2 (en) Deodorant, method for producing the same, and deodorizer
JPH07204442A (en) Honeycomb deodorizing material