JPH0555186B2 - - Google Patents
Info
- Publication number
- JPH0555186B2 JPH0555186B2 JP63151104A JP15110488A JPH0555186B2 JP H0555186 B2 JPH0555186 B2 JP H0555186B2 JP 63151104 A JP63151104 A JP 63151104A JP 15110488 A JP15110488 A JP 15110488A JP H0555186 B2 JPH0555186 B2 JP H0555186B2
- Authority
- JP
- Japan
- Prior art keywords
- catalyst
- ozone
- present
- manganese
- air
- 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.)
- Expired - Lifetime
Links
Landscapes
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
- Catalysts (AREA)
Description
【発明の詳細な説明】
<産業上の利用分野>
本発明は、悪臭ガスをオゾンを用いて触媒の存
在下に脱臭する処理に使用された使用済触媒を再
生する方法に関する。DETAILED DESCRIPTION OF THE INVENTION <Industrial Application Field> The present invention relates to a method for regenerating a used catalyst used in the treatment of deodorizing malodorous gas using ozone in the presence of a catalyst.
<従来技術とその問題点>
オゾンを用いる脱臭方法はオゾンが有する強力
な酸化能力によるものであることは知られてい
る。この脱臭方法は触媒を使用して接触的に行な
うことにより、その効果が飛躍的に大きくなる。
触媒の活性物質としてマンガン、鉄、コバルト、
ニツケル、亜鉛、銀、白金、パラジウムおよびロ
ジウム等が挙げられるが、性能および耐久性の面
でマンガンがもつとも良好である。<Prior art and its problems> It is known that the deodorizing method using ozone is based on the strong oxidizing ability of ozone. When this deodorizing method is carried out catalytically using a catalyst, its effectiveness is dramatically increased.
Manganese, iron, cobalt,
Examples include nickel, zinc, silver, platinum, palladium, and rhodium, but manganese is better in terms of performance and durability.
しかし、マンガン触媒においても、長期間の使
用により、触媒活性が低下してくる。従つて、触
媒活性が劣化した触媒を再生する方法が必要とな
つてくる。かかる再生方法として、アンモニア水
溶液で洗浄後、水洗、乾燥し、次いで200〜300℃
の不活性ガス雰囲気中で焼成する方法が知られて
いる(特開昭58−219942号公報)。しかし、この
方法は臭気の強いアンモニアにより作業環境が汚
染されたり工程も多くて決して簡便な方法とはい
えない。 However, even with manganese catalysts, the catalytic activity decreases after long-term use. Therefore, there is a need for a method for regenerating a catalyst whose catalytic activity has deteriorated. Such a regeneration method involves washing with an ammonia aqueous solution, washing with water, drying, and then heating at 200 to 300°C.
A method of firing in an inert gas atmosphere is known (JP-A-58-219942). However, this method contaminates the working environment with ammonia, which has a strong odor, and requires many steps, so it cannot be called an easy method.
<発明が解決しようとしている問題点>
本発明の目的は、オゾンを用いる触媒脱臭法で
使用された、マンガンを主活性成分とする使用済
触媒を簡便かつ十分に再生する方法を提供するこ
とにある。<Problems to be Solved by the Invention> An object of the present invention is to provide a simple and sufficient method for regenerating a spent catalyst containing manganese as the main active ingredient, which was used in a catalytic deodorization method using ozone. be.
<問題点を解決するための手段>
本発明者等は、上記目的に沿つて鋭意研究した
結果、マンガンを主活性成分とする触媒を用いる
場合にはアンモニア水などで洗浄しなくとも単に
空気中もしくは酸素中で焼成するだけで十分触媒
活性が回復することを見いだし、更に検討した結
果本発明を完成したものである。即ち本発明は、
オゾンを用いる触媒脱臭法で使用された、マンガ
ンを主活性成分とする使用済触媒を、空気中もし
くは酸素中で100〜500℃で焼成する触媒再生方法
である。<Means for solving the problem> As a result of intensive research in line with the above objectives, the present inventors have found that when using a catalyst containing manganese as the main active ingredient, it can be easily removed from the air without washing with aqueous ammonia or the like. Alternatively, the inventors discovered that catalytic activity could be sufficiently recovered by simply calcining in oxygen, and as a result of further studies, the present invention was completed. That is, the present invention
This is a catalyst regeneration method in which a spent catalyst containing manganese as the main active ingredient, which was used in a catalytic deodorization method using ozone, is calcined at 100 to 500°C in air or oxygen.
本発明において、触媒の再成は空気中もしくは
酸素中で100〜500℃、好ましくは200〜450℃で焼
成して行なう。オゾンを用いる脱臭方法における
触媒活性の低下原因として、触媒上に反応生成物
が付着して被毒物質になること、オゾンにより触
媒表面が酸化されマンガン過酸化物が生成し蓄積
することなどが考えられる。また処理ガス中に含
まれるダストや水分、ミストの触媒表面への付着
も原因の一つと考えられる。単純な水分吸着など
触媒の活性劣化度合が小さい場合には100〜150℃
程度での乾燥でも十分であるが、通常の場合は
200〜500℃で焼成するのがよい。500℃を越える
温度で焼成しても触媒再生効果は増加せず、装置
が大がかりになつたりエネルギーが余計に必要に
なつたりして不利である。通常、焼成時間1〜5
時間程度で焼成炉を用いて行なう。 In the present invention, the catalyst is regenerated by firing in air or oxygen at 100 to 500°C, preferably 200 to 450°C. Possible causes of decreased catalyst activity in deodorizing methods using ozone include reaction products adhering to the catalyst and becoming poisonous substances, and ozone oxidizing the catalyst surface and producing manganese peroxide, which accumulates. It will be done. It is also thought that one of the causes is the adhesion of dust, moisture, and mist contained in the processing gas to the catalyst surface. 100 to 150℃ when the degree of catalyst activity deterioration is small, such as due to simple moisture adsorption.
It is sufficient to dry it to a certain degree, but in normal cases
It is best to bake at 200-500℃. Calcining at a temperature exceeding 500°C does not increase the catalyst regeneration effect and is disadvantageous in that the equipment becomes bulky and additional energy is required. Usually baking time 1-5
This is done using a firing furnace in about an hour.
本発明の方法に従つて再生することにより、薬
液による処理が不要で、工程および装置が簡略化
でき、再生処理が簡便に行なえる。 By regenerating according to the method of the present invention, treatment with a chemical solution is not required, the process and equipment can be simplified, and the regeneration process can be performed easily.
以下、実施例により本発明をさらに詳細に説明
するが、本発明の実施例のみに限定されるもので
はない。 Hereinafter, the present invention will be explained in more detail with reference to Examples, but the present invention is not limited only to the Examples.
<実施例>
オゾン分解用触媒として、チタン−珪素からな
る複合酸化物と二酸化マンガンからなり、組成が
各々の重量比で85:15である触媒を用いた。該触
媒に硫化メチル10ppmおよびオゾンを20ppm含有
する空気を室温下、空間速度50000hr-1にて通じ、
空気の脱臭処理を行なつた。処理を開始してから
4000時間後硫化メチル除去率およびオゾン分解効
率を測定したところ、それぞれ63%、71%であつ
た。触媒を取り出し、電気加熱式焼成炉に入れて
加熱、400℃、3時間焼成し、触媒の再生を行な
つた。<Example> As an ozone decomposition catalyst, a catalyst consisting of a composite oxide of titanium-silicon and manganese dioxide and having a composition of 85:15 in weight ratio of each was used. Air containing 10 ppm of methyl sulfide and 20 ppm of ozone was passed through the catalyst at a space velocity of 50,000 hr -1 at room temperature,
The air was deodorized. After starting the process
When the methyl sulfide removal rate and ozone decomposition efficiency were measured after 4000 hours, they were 63% and 71%, respectively. The catalyst was taken out, placed in an electrically heated calcining furnace, heated, and calcined at 400°C for 3 hours to regenerate the catalyst.
再生後の触媒を前回と同じ条件下でオゾン分解
処理に用いた。処理開始直後の硫化メチル除去率
およびオゾン分解効率はそれぞれ96%、99%であ
り、触媒活性が十分に回復していた。 The regenerated catalyst was used for ozone decomposition treatment under the same conditions as before. Immediately after the start of treatment, the methyl sulfide removal rate and ozone decomposition efficiency were 96% and 99%, respectively, indicating that the catalyst activity had been sufficiently recovered.
Claims (1)
ンガンを主活性成分とする使用済触媒を、空気中
もしくは酸素中で100〜500℃で焼成することを特
徴とする触媒再生方法。1. A catalyst regeneration method characterized by calcining a spent catalyst containing manganese as a main active ingredient, which was used in a catalytic deodorization method using ozone, at 100 to 500°C in air or oxygen.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP63151104A JPH024450A (en) | 1988-06-21 | 1988-06-21 | Catalyst regeneration process |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP63151104A JPH024450A (en) | 1988-06-21 | 1988-06-21 | Catalyst regeneration process |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH024450A JPH024450A (en) | 1990-01-09 |
| JPH0555186B2 true JPH0555186B2 (en) | 1993-08-16 |
Family
ID=15511434
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP63151104A Granted JPH024450A (en) | 1988-06-21 | 1988-06-21 | Catalyst regeneration process |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH024450A (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP4318054B2 (en) | 2007-01-11 | 2009-08-19 | 株式会社デンソー | Automotive local cooling system |
| CN114453031B (en) * | 2022-02-17 | 2023-04-25 | 中国环境科学研究院 | A kind of catalyst regeneration method and application |
Family Cites Families (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5314688A (en) * | 1976-07-28 | 1978-02-09 | Toshiba Corp | Production of ozone decomposition catalyst |
| JPS542992A (en) * | 1977-06-09 | 1979-01-10 | Kobe Steel Ltd | Catalyst regenerating method by heating |
| JPS5330978A (en) * | 1976-09-03 | 1978-03-23 | Toshiba Corp | Deodorizing apparatus |
| JPS5581730A (en) * | 1978-12-15 | 1980-06-20 | Toshiba Corp | Continuous deodorizing method |
| JPS58219942A (en) * | 1982-06-14 | 1983-12-21 | Mitsubishi Heavy Ind Ltd | Regeneration of catalyst |
| JPS6120334A (en) * | 1984-07-09 | 1986-01-29 | Oki Electric Ind Co Ltd | Manufacture of semiconductor device |
| JPS6279848A (en) * | 1985-10-01 | 1987-04-13 | Osaka Sekiyu Kagaku Kk | Method for reactivation of oxide catalyst for removing arsenic in hydrocarbon |
| JPS6297643A (en) * | 1985-10-25 | 1987-05-07 | Nippon Shokubai Kagaku Kogyo Co Ltd | Ozone decomposing catalyst |
| JPS63126525A (en) * | 1986-11-18 | 1988-05-30 | Nippon Shokubai Kagaku Kogyo Co Ltd | Deodorizing device |
-
1988
- 1988-06-21 JP JP63151104A patent/JPH024450A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPH024450A (en) | 1990-01-09 |
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