JPS5949050B2 - How to remove ozone - Google Patents

How to remove ozone

Info

Publication number
JPS5949050B2
JPS5949050B2 JP51089853A JP8985376A JPS5949050B2 JP S5949050 B2 JPS5949050 B2 JP S5949050B2 JP 51089853 A JP51089853 A JP 51089853A JP 8985376 A JP8985376 A JP 8985376A JP S5949050 B2 JPS5949050 B2 JP S5949050B2
Authority
JP
Japan
Prior art keywords
ozone
activated carbon
catalyst
palladium
removal rate
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
Application number
JP51089853A
Other languages
Japanese (ja)
Other versions
JPS5314665A (en
Inventor
信男 石崎
洋一 鈴木
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.)
Toyobo Co Ltd
Original Assignee
Toyobo Co 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 Toyobo Co Ltd filed Critical Toyobo Co Ltd
Priority to JP51089853A priority Critical patent/JPS5949050B2/en
Publication of JPS5314665A publication Critical patent/JPS5314665A/en
Publication of JPS5949050B2 publication Critical patent/JPS5949050B2/en
Expired legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A50/00TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/20Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters

Landscapes

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

Description

【発明の詳細な説明】 本発明は、空気中に含まれる人体に有害なオゾンを除去
する方法に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for removing ozone contained in the air that is harmful to the human body.

オゾンは強力な酸化作用を有する為、空気中の浮遊菌の
殺菌、空気の脱臭など空気の浄化剤として種々の用途が
提案されているが、オゾンは非常に臭気の強い気体であ
り、したがって空気中に0.1p1mの濃度で存在する
だけで、息切れ、めまい、頭痛、吐き気などの生理作用
が生じることがあり人体に対して無害であるとはいえな
い。
Because ozone has a strong oxidizing effect, various uses have been proposed as an air purifying agent, such as sterilizing airborne bacteria and deodorizing the air.However, ozone is a gas with a very strong odor, so it Even if it is present at a concentration of 0.1 pm, it can cause physiological effects such as shortness of breath, dizziness, headache, and nausea, so it cannot be said that it is harmless to the human body.

従来オゾンを除去する方法として活性炭、二酸化マンガ
ン等の物質にオゾンを通す方法が公知であるが除去率、
寿命、圧損等の点で不満足であつた。
Conventional methods for removing ozone include passing ozone through substances such as activated carbon and manganese dioxide, but the removal rate and
It was unsatisfactory in terms of life, pressure loss, etc.

従来、粒状活性炭にパラジウムを担持させたものが提案
されているが、触媒の効率が低く、除去率を高めようと
すると層厚を数センチメートル以上を採る必要があり、
圧損の上昇が避けることができなかった。
Conventionally, palladium supported on granular activated carbon has been proposed, but the efficiency of the catalyst is low, and in order to increase the removal rate, the layer thickness must be several centimeters or more.
An increase in pressure drop could not be avoided.

本発明はかかる欠点を改善すべく見出されたものである
The present invention was discovered to improve these drawbacks.

皿ち、全細孔容積が0.3cc/g以上で、半径100
Å以下の細孔が容積比率の全細孔の70%以上である活
性炭素繊維に、白金または/およびパラジウムを金属単
体として担持したオゾン分解触媒を提供するものである
Plate, total pore volume is 0.3cc/g or more, radius 100
The present invention provides an ozone decomposition catalyst in which platinum or/and palladium is supported as an elemental metal on activated carbon fibers in which pores of Å or smaller account for 70% or more of the total pores by volume.

セルロース繊維、アクリロニトリル繊維、フェノール柑
脂繊維、レジナス・ピッチ繊維等の前駆体繊維を適当な
方法、耐炎化処理後、焼成賦活することによって得られ
る活性炭素繊維が本発明に用いられる。
Activated carbon fibers obtained by flame-proofing precursor fibers such as cellulose fibers, acrylonitrile fibers, phenolic citrus fibers, and resinous pitch fibers by an appropriate method and then firing and activating the fibers are used in the present invention.

活性炭素繊維含有集合体はペーパー状、不織布状、シー
ト状、魂状等種々の形態をとることが出来る。
The activated carbon fiber-containing aggregate can take various forms such as paper, non-woven fabric, sheet, and fiber.

この活性炭素繊維集合体に白金又は/及びパラジウムを
金属単体として担持させて触媒とする。
This activated carbon fiber aggregate supports platinum and/or palladium as a single metal to form a catalyst.

この白金又は/及びパラジウム単体の担持量は、金属換
算にして活性炭素繊維重量に対して0.5〜10重量%
の範囲であればよいが1〜5重量%がとくに好ましい。
The supported amount of platinum or/and palladium alone is 0.5 to 10% by weight based on the weight of activated carbon fiber in terms of metal.
The content may be within the range of 1 to 5% by weight, particularly preferably 1 to 5% by weight.

白金又は/及びパラジウム単体の担持は白金又は/及び
パラジウムの塩類を活性炭素繊維に含浸後、環元、熱分
解等通常の方法で行なうことが出来る。
Supporting of platinum or/and palladium alone can be carried out by impregnating activated carbon fibers with salts of platinum or/and palladium, and then using a conventional method such as ring removal or thermal decomposition.

本発明の方法によると高比表面積で均一なミクロ・ポア
ー分布を有する活性炭素繊維上に金属触媒が担持されて
いる為、通常の活性炭に触媒を担持したものより、活性
、寿命が非常に長いという特徴を有する。
According to the method of the present invention, the metal catalyst is supported on activated carbon fibers that have a high specific surface area and a uniform micro-pore distribution, so the activity and life are much longer than those in which the catalyst is supported on ordinary activated carbon. It has the following characteristics.

本発明の触媒は金属触媒の分散度が良好であり、これが
触媒作用の向上に寄与しているものと推測される。
The catalyst of the present invention has a good degree of dispersion of the metal catalyst, and it is presumed that this contributes to the improvement of the catalytic action.

さらに繊維状である為、酸化速度が大きく、圧力損失が
低いという利点も有する。
Furthermore, since it is fibrous, it has the advantage of high oxidation rate and low pressure loss.

本触媒に遭電すると容易にフィルタ一部分が均一に高温
に加熱され、除去性能が一層向上するという利点も有す
る。
Another advantage is that when the catalyst encounters electricity, a portion of the filter is easily heated to a high temperature uniformly, further improving the removal performance.

実施例 1 パラジウムを5重量%担持した細孔容積0.5cc/g
、半径100Å以下の細孔容積比率96%の活性炭素繊
維(厚33mm)のフェルト2枚を(目付200g/m
つを、下図のようなアルミ枠の両面にSvS金鋼をはっ
たユニットに充填し、0.2ppmオゾンを含有する排
ガスを1.5m・/minの風量で流したところ、初期
のオゾン除去率は98%であり、90%の除去率を約1
000時間保持した。
Example 1 Pore volume 0.5 cc/g with 5% by weight of palladium supported
, two sheets of activated carbon fiber felt (thickness 33 mm) with a pore volume ratio of 96% with a radius of 100 Å or less (fabric weight 200 g/m
When the unit was filled with SvS gold steel on both sides of an aluminum frame as shown in the figure below, and exhaust gas containing 0.2 ppm ozone was flowed at a flow rate of 1.5 m/min, initial ozone removal was achieved. The removal rate is 98%, and the removal rate of 90% is approximately 1
It was held for 000 hours.

圧損は、2mmH2Oであった。The pressure drop was 2 mmH2O.

比較例 1 パラジウムを0.5%担持した6−10メツシユのヤシ
ガラ活性炭を、実施例と同じユニットに充填し、0.2
f)[のオゾンを含有するガスを流したところ初期の
除去率は50%であり、オゾン臭が強く感ぜられた。
Comparative Example 1 6-10 mesh coconut shell activated carbon carrying 0.5% palladium was filled into the same unit as in the example, and 0.2% palladium was loaded.
f) When a gas containing ozone was flowed, the initial removal rate was 50%, and a strong ozone odor was felt.

次にユニットの厚さを50mmにして上記の活性炭触媒
を充填し同様にオゾン処理を行なった。
Next, the unit was made to have a thickness of 50 mm, filled with the above activated carbon catalyst, and ozone treated in the same manner.

初期の除去率は91%であったが、150時間経過時の
除去率は87%に低下していた。
The initial removal rate was 91%, but the removal rate after 150 hours had decreased to 87%.

圧力損失は6mmH2Oであった。The pressure drop was 6 mmH2O.

実施例 2 細孔容積0.45cm/g半径100Å以下の細孔の容
積比率が90%の活性炭素繊維フェルト (厚さ4mm
)に白金触媒を5重量%担持させた。
Example 2 Activated carbon fiber felt with a pore volume of 0.45 cm/g and a volume ratio of pores with a radius of 100 Å or less of 90% (thickness: 4 mm)
) was loaded with 5% by weight of platinum catalyst.

このフェルトを実施例1と同じユニットに入れて0.0
5pIrnのオゾン含有排ガスを1.5m37m1nの
風量で流して処理した。
Put this felt into the same unit as in Example 1 and get 0.0
The treatment was carried out by flowing ozone-containing exhaust gas of 5 pIrn at an air volume of 1.5 m37 m1n.

オゾンの初期除去率は93%であり、90%の除去率は
916時間保持した。
The initial ozone removal rate was 93%, and the 90% removal rate was maintained for 916 hours.

なお圧損は2.6mmH2Oであった。Note that the pressure loss was 2.6 mmH2O.

比較例 2 実施例2に記載した活性炭素繊維フェルトを25枚重ね
合せて実施列1と同様なアルミ枠に入れて0.2pIr
nオゾン含有ガスを1.5 m37m1nの風量で処理
したところ初期のオゾン除去率は90%であったが、5
0時間後のオゾン除去率は28%であった。
Comparative Example 2 25 sheets of activated carbon fiber felt described in Example 2 were stacked together, placed in an aluminum frame similar to Example 1, and heated to 0.2 pIr.
When the ozone-containing gas was treated with an air volume of 1.5 m37 m1n, the initial ozone removal rate was 90%, but the
The ozone removal rate after 0 hours was 28%.

又圧損は10mmHgであった。Moreover, the pressure loss was 10 mmHg.

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

図面は本発明方法の実施に使用した吸着ユニットの例で
ある。
The drawing shows an example of an adsorption unit used to carry out the method of the present invention.

Claims (1)

【特許請求の範囲】[Claims] 1 全細孔の容積が0.3cc/g以上であり、半径1
00Å以下の細孔が容積比率で全細孔の70%以上であ
る活性炭素繊維に、白金または/およびパラジウムを金
属単体として担持した触媒にオゾンを接触せしめること
を特徴とするオゾンの除去方法。
1 The volume of all pores is 0.3 cc/g or more, and the radius is 1
A method for removing ozone, which comprises bringing ozone into contact with a catalyst in which platinum or/and palladium is supported as an elemental metal on activated carbon fibers in which pores of 00 Å or less account for 70% or more of the total pores in terms of volume ratio.
JP51089853A 1976-07-27 1976-07-27 How to remove ozone Expired JPS5949050B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP51089853A JPS5949050B2 (en) 1976-07-27 1976-07-27 How to remove ozone

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP51089853A JPS5949050B2 (en) 1976-07-27 1976-07-27 How to remove ozone

Publications (2)

Publication Number Publication Date
JPS5314665A JPS5314665A (en) 1978-02-09
JPS5949050B2 true JPS5949050B2 (en) 1984-11-30

Family

ID=13982329

Family Applications (1)

Application Number Title Priority Date Filing Date
JP51089853A Expired JPS5949050B2 (en) 1976-07-27 1976-07-27 How to remove ozone

Country Status (1)

Country Link
JP (1) JPS5949050B2 (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH02307511A (en) * 1989-05-19 1990-12-20 Sakai Chem Ind Co Ltd Ozone decomposer
JPH02307509A (en) * 1989-05-19 1990-12-20 Sakai Chem Ind Co Ltd Ozone decomposer
JPH02307510A (en) * 1989-05-19 1990-12-20 Sakai Chem Ind Co Ltd Ozone decomposer

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS4982593A (en) * 1972-12-15 1974-08-08

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS4982593A (en) * 1972-12-15 1974-08-08

Also Published As

Publication number Publication date
JPS5314665A (en) 1978-02-09

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