JP3126012B2 - How to Prevent Odor Generation from Ozone Filter - Google Patents

How to Prevent Odor Generation from Ozone Filter

Info

Publication number
JP3126012B2
JP3126012B2 JP06229060A JP22906094A JP3126012B2 JP 3126012 B2 JP3126012 B2 JP 3126012B2 JP 06229060 A JP06229060 A JP 06229060A JP 22906094 A JP22906094 A JP 22906094A JP 3126012 B2 JP3126012 B2 JP 3126012B2
Authority
JP
Japan
Prior art keywords
ozone
manganese dioxide
ozone filter
catalyst
carrier
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 - Fee Related
Application number
JP06229060A
Other languages
Japanese (ja)
Other versions
JPH0871369A (en
Inventor
功 寺田
慎一郎 荒井
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.)
Nichias Corp
Original Assignee
Nichias Corp
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 Nichias Corp filed Critical Nichias Corp
Priority to JP06229060A priority Critical patent/JP3126012B2/en
Priority to GB9516983A priority patent/GB2292698B/en
Priority to US08/519,097 priority patent/US5698165A/en
Priority to DE19531179A priority patent/DE19531179B4/en
Publication of JPH0871369A publication Critical patent/JPH0871369A/en
Application granted granted Critical
Publication of JP3126012B2 publication Critical patent/JP3126012B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related 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

Description

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

【0001】[0001]

【産業上の利用分野】本発明は、活性二酸化マンガン触
媒を用いたオゾンフィルターからの悪臭発生を防止する
方法に関するものである。なお、この明細書では、静電
式複写機、レーザプリンタ等の事務用機器から発生した
オゾンを低濃度で含有するが格別悪臭を感じさせるわけ
ではない室内空気を処理してオゾンを分解するためのフ
ィルターに限定された意味で「オゾンフィルター」とい
う。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for preventing an odor from being generated from an ozone filter using an active manganese dioxide catalyst. Note that, in this specification,
Generated from office equipment such as portable copiers and laser printers
Although it contains ozone at a low concentration, it makes you feel a particularly bad smell
For decomposing ozone by treating indoor air that is not
"Ozone filter" in a sense limited to filters
U.

【0002】[0002]

【従来の技術】オゾンは人類にとって善悪2面の作用を
示す。すなわち、オゾンはその強力な酸化能に基づく殺
菌作用を医療、食品などの分野で広く利用されている
が、一方では、オゾン自身の毒性に基づき、空気中の濃
度が0.1ppmを超えると呼吸器系に刺激を感じさせ、5
0ppm以上では生命に危険を及ぼす。したがって、近
年、静電式複写機、レーザプリンタなどオゾンを発生す
る事務用機器が普及してオゾン発生原因が増加するに伴
い、空気中のオゾンの簡単な分解法の開発が望まれるに
至った。
2. Description of the Related Art Ozone has two effects on humankind. In other words, ozone is widely used in the fields of medicine, food, etc. for its bactericidal action based on its strong oxidizing ability. On the other hand, based on the toxicity of ozone itself, when the concentration in air exceeds 0.1 ppm, respiration occurs. Make the system feel stimulus 5
Above 0 ppm it is dangerous to life. Accordingly, in recent years, with the spread of office equipment that generates ozone, such as electrostatic copying machines and laser printers, and the causes of ozone generation have increased, it has been desired to develop a simple method for decomposing ozone in air. .

【0003】従来、空気中の低濃度オゾンを無害化する
技術としては、活性炭吸着法、加熱分解法、湿式法、お
よび接触分解法などがあるが、接触分解は安全性が高
く、常温で実施可能であり、小規模実施も容易であるな
ど、多くの点で有利である。オゾンの接触分解を小規模
で簡単に実施することを可能にしたオゾンフィルターの
一例は特開平5−23591号公報に記載されており、
そこでは、活性二酸化マンガン触媒を高空隙率の紙から
なるハニカム構造の担体に担持させたオゾンフィルター
が提案されている。
Conventionally, techniques for detoxifying low-concentration ozone in the air include an activated carbon adsorption method, a thermal decomposition method, a wet method, and a catalytic cracking method. However, catalytic cracking is highly safe and is carried out at room temperature. It is advantageous in many respects, such as being possible and easy to implement on a small scale. An example of an ozone filter which enables simple and small-scale catalytic decomposition of ozone is described in JP-A-5-23591.
Here, an ozone filter in which an active manganese dioxide catalyst is supported on a carrier having a honeycomb structure made of high porosity paper has been proposed.

【0004】活性二酸化マンガン触媒を用いたオゾンフ
ィルターは、長期にわたって優れたオゾン分解能を示す
特長がある。しかしながら、まれにではあるが、長期間
使用すると、オゾン分解能には異常がなくても悪臭を発
するようになる場合があり、問題点として指摘されてい
る。
[0004] An ozone filter using an active manganese dioxide catalyst has the feature of exhibiting excellent ozone resolution over a long period of time. However, in rare cases, when used for a long period of time, an odor may be generated even if there is no abnormality in the ozone resolution, and this is pointed out as a problem.

【0005】[0005]

【発明が解決しようとする課題】本発明者らは、長期間
使用した結果悪臭を発するに至った上記オゾンフィルタ
ーを調べた結果、フィルターには多数の有機化合物が吸
着されていることを確認した。確認された有機化合物の
主なものは、アセトン、2-プロパノール、tert-ブタノ
ール、メチルエチルケトン、低級脂肪酸類、クロロホル
ム、トルエン、酢酸ブチル、エチルベンゼン、キシレ
ン、ブチルエチルケトン、スチレン、α-メチルスチレ
ン、o-キシレン、アセトフェノン、tert-ブチルフェニ
ルエーテル、ジメチルビフェニル等である。使用開始前
のオゾンフィルターにはこれらの化合物は吸着されてい
ないか、吸着されていてもごく僅かであるから、これら
の化合物はフィルターの使用開始後に、吸着能力もある
二酸化マンガンによって吸着されたものと推定される。
DISCLOSURE OF THE INVENTION The present inventors have examined the above-mentioned ozone filter which emits a bad smell as a result of long-term use, and as a result, have confirmed that a large number of organic compounds are adsorbed on the filter. . The main organic compounds identified are acetone, 2-propanol, tert-butanol, methyl ethyl ketone, lower fatty acids, chloroform, toluene, butyl acetate, ethyl benzene, xylene, butyl ethyl ketone, styrene, α-methyl styrene, o -Xylene, acetophenone, tert-butylphenyl ether, dimethylbiphenyl and the like. These compounds are not adsorbed on the ozone filter before use, or they are adsorbed to a very small extent. It is estimated to be.

【0006】通常の環境の大気中にほとんど存在しない
これらの化合物がフィルターに吸着されていた理由は、
次のように考えられる。空気中には人間や動植物が放出
した微量の有機成分、たとえば汗、煙草のけむり、香料
等に由来する有機物が含まれていて、これらがオゾンフ
ィルターを通過する。また、オゾンフィルターが装着さ
れている機器が作動中に放出する有機物たとえばトナー
や機械油等に由来する微量の有機物も、オゾンフィルタ
ーを通過する。オゾンフィルターに接触した有機物の一
部は、そのまま、または二酸化マンガンとオゾンの作用
によって酸化・分解されたのち、二酸化マンガンに吸着
されてフィルター上に蓄積する。
[0006] The reason that these compounds, which are hardly present in the atmosphere of the normal environment, were adsorbed on the filter, was as follows.
It is considered as follows. The air contains a trace amount of organic components emitted by humans and animals and plants, for example, organic substances derived from sweat, cigarettes, perfumes, etc., which pass through the ozone filter. Further, a small amount of organic substances, such as organic substances originating from toner, machine oil, etc., released during operation of the device equipped with the ozone filter also passes through the ozone filter. Some of the organic substances that have come into contact with the ozone filter are oxidized and decomposed as they are or by the action of manganese dioxide and ozone, and then adsorbed by manganese dioxide and accumulate on the filter.

【0007】これらの有機物は、悪臭の強い物質であっ
ても二酸化マンガンに吸着されてしまえば何の問題もな
いが、フィルターの使用期間が長くなり二酸化マンガン
の吸着能力が飽和した後は処理済み空気に混じって大気
中に放出されるから、それらの幾つかの臭いが複合して
不快臭を感じさせることになるものと思われる。そこで
本発明の目的は、オゾン分解能に優れた活性二酸化マン
ガン触媒を用いたオゾンフィルターを、長期間使用した
後も悪臭を感じさせることのないように改良する方法
提供することにある。
[0007] These organic substances have no problem if they are adsorbed by manganese dioxide, even if they are substances with strong odor. It is believed that some of these odors combine to give an unpleasant odor because they are released into the atmosphere in the air. Accordingly, an object of the present invention is to provide a method for improving an ozone filter using an active manganese dioxide catalyst having excellent ozone decomposability so that it does not give off a bad smell even after long-term use.

【0008】[0008]

【課題を解決するための手段】上記目的は、微粉末状活
性二酸化マンガン触媒と共にSiO/Al
(モル比)が15以上のゼオライト粉末を高空隙率の無
機繊維製紙からなる担体に担持させることにより達成さ
れた。
SUMMARY OF THE INVENTION The object of the present invention is to provide a fine powdered active manganese dioxide catalyst and a zeolite powder having a SiO 2 / Al 2 O 3 ratio (molar ratio) of 15 or more together with a high porosity inorganic fiber paper carrier. was achieved by Rukoto is supported on.

【0009】ここで用いるSiO2/Al23比が15以
上のゼオライトは、SiO2/Al23比が2〜15程度
の通常のゼオライトが強い親水性を示し乾燥剤に使われ
たりするのとは対照的に、水蒸気よりも炭化水素系化合
物をよく吸着する能力があることで知られている(以
下、この疎水性の強いゼオライトを疎水性ゼオライトと
いう)。その代表的な例の組成は、HAlSi3572、H
AlSi2552である(特表昭60−501495号公
報,特開平1−31457号公報参照)。入手容易な市
販品としては、SiO2/Al23比50〜500程度の
ものがある。
[0009] SiO 2 / Al 2 O 3 ratio of 15 or more zeolites used here, or SiO 2 / Al 2 O 3 ratio is used in desiccant showed a strong hydrophilicity is normal zeolite of about 2-15 On the contrary, it is known that it has an ability to adsorb hydrocarbon compounds better than water vapor (hereinafter, this zeolite having strong hydrophobicity is referred to as hydrophobic zeolite). The composition of a representative example is HAlSi 35 O 72 , H
AlSi 25 O 52 (see Japanese Patent Application Laid-Open No. 60-501495 and JP-A-1-31457). Commercially available products that are easily available include those having a SiO 2 / Al 2 O 3 ratio of about 50 to 500.

【0010】疎水性ゼオライトの粉末を二酸化マンガン
触媒と共に担体に担持させて得られるオゾンフィルター
は、長期間使用しても悪臭を感じさせることがない。そ
の理由はまだ解明されていないが、疎水性ゼオライトが
前述のオゾンによる酸化後の、もしくは酸化前の、大気
中有機物のいずれかを二酸化マンガン触媒の近傍におい
て吸着することが、悪臭原因物質の放出阻止に役立って
いるものと推察される。
[0010] Manganese dioxide is used as the powder of the hydrophobic zeolite.
An ozone filter obtained by being supported on a carrier together with a catalyst does not give off a bad smell even when used for a long time. Although the reason has not yet been elucidated, the fact that the hydrophobic zeolite adsorbs any of the organic substances in the atmosphere after or before oxidation with ozone in the vicinity of the manganese dioxide catalyst releases odor-causing substances. It is presumed to have helped to prevent it.

【0011】[0011]

【0012】以下、本発明による悪臭発生防止方法につ
いて詳述する。オゾン分解触媒として用いる二酸化マン
ガンは特に限定されるものではなく、市販品のほか任意
の製造法によるものを用いることができるが、特に好ま
しいのは、粒径が0.3〜50μmで比表面積が150
/g以上の微粉末状活性二酸化マンガンである。こ
の微粉末状活性二酸化マンガンは、無機繊維製紙からな
る担体に多量に、且つ担体芯部まで均一に担持させるこ
とができる。このような微粉末状かつ比表面積の大きい
二酸化マンガン触媒は、たとえば炭酸マンガンの水中懸
濁物に次亜塩素酸塩、過マンガン酸塩等の酸化剤の水溶
液を作用させ、生じた二酸化マンガンの沈殿を酸処理
し、さらにアルカリで中和する方法(特公昭55−84
56号)等により、容易に製造することができる。
Hereinafter, a method for preventing the generation of offensive odors according to the present invention will be described.
It will be described in detail . The manganese dioxide used as the ozonolysis catalyst is not particularly limited, and may be a commercially available product or any product produced by an arbitrary production method. Particularly preferred is a particle size of 0.3 to 50 μm and a specific surface area of 0.3 to 50 μm. 150
It is a fine powdered active manganese dioxide of m 2 / g or more. This fine powdered active manganese dioxide can be uniformly supported on a carrier made of inorganic fiber paper in a large amount and even to the carrier core. Such a finely powdered manganese dioxide catalyst having a large specific surface area is prepared by, for example, allowing an aqueous solution of an oxidizing agent such as hypochlorite or permanganate to act on a suspension of manganese carbonate in water to produce a manganese dioxide. A method in which the precipitate is treated with an acid and neutralized with an alkali (Japanese Patent Publication No. 55-84).
No. 56) and the like.

【0013】疎水性ゼオライトとしては、望ましくは粒
径が1〜10μm程度の、前述の組成のものを用いる。
As the hydrophobic zeolite, those having the above-mentioned composition having a particle size of about 1 to 10 μm are preferably used.

【0014】二酸化マンガン触媒と疎水性ゼオライトを
担持させる高空隙率の無機繊維製紙からなる担体は、た
とえば特開昭59−10345号公報に記載されてい
る。すなわち、アルミナ繊維、シリカアルミナ繊維、ガ
ラス繊維、ロックウール等の無機繊維からなり且つ70
〜95%という高い空隙率を有する紙、およびこの紙を
加工して得られたハニカム構造体である。使用可能な市
販品としては、“ハニクル”(ニチアス株式会社製品)
がある。なお、空隙率とは下記の式から求められる値で
ある。 空隙率(%)=(1−見かけの密度/真の密度)×100
[0014] A carrier comprising a high porosity inorganic fiber paper supporting a manganese dioxide catalyst and a hydrophobic zeolite is described, for example, in JP-A-59-10345. That is, it is made of inorganic fiber such as alumina fiber, silica-alumina fiber, glass fiber, rock wool and the like.
A paper having a high porosity of about 95% and a honeycomb structure obtained by processing the paper. "Hanicle" (a product of Nichias Co., Ltd.)
There is. The porosity is a value obtained from the following equation. Porosity (%) = (1−apparent density / true density) × 100

【0015】紙の厚さは特に限定されるものではない
が、最も適当なのは約0.1〜0.4mmである。
The thickness of the paper is not particularly limited, but is most preferably about 0.1 to 0.4 mm.

【0016】無機繊維製紙からなるハニカム構造の担体
は、大風量の被処理空気を低い圧力損失で効率よく処理
するのに最適のものであり、低濃度オゾン含有空気を処
理する二酸化マンガン触媒の担体として優れている。ま
た、切断加工が可能であるから任意の形状と寸法のもの
を容易に製造することができ、落としても割れないとい
う特長がある。好ましいハニカム構造体は、有効表面積
8〜40cm2/cm3(特に好ましくは20〜40cm2/c
m3)、開口率50〜90%(特に好ましくは50〜70
%)のものである。
The honeycomb-structured carrier made of inorganic fiber paper is most suitable for efficiently treating a large air volume of air to be treated with low pressure loss, and is a carrier of a manganese dioxide catalyst for treating low-concentration ozone-containing air. As excellent. In addition, since it can be cut, any shape and size can be easily manufactured, and there is a feature that it does not crack even if dropped. Preferred honeycomb structures have an effective surface area of 8 to 40 cm 2 / cm 3 (particularly preferably 20 to 40 cm 2 / c
m 3 ), an aperture ratio of 50 to 90% (particularly preferably 50 to 70%)
%)belongs to.

【0017】上述の担体に微粉末状活性二酸化マンガン
と疎水性ゼオライトを担持させるには、活性二酸化マン
ガンと疎水性ゼオライトの懸濁液に無機質結合剤たとえ
ばシリカゾル、アルミナゾル、チタニアゾル、またはこ
れらの混合物等を加えたものを浸漬または塗工により担
体に含浸し、乾燥すればよい。このとき、結合剤の使用
量は必要最小限度に制限することが望ましく、過剰に使
用すると二酸化マンガンの表面を覆って触媒活性の低下
を招く。一度に必要量の触媒を固定することが困難な場
合は、適量の触媒が固定されるまで、触媒含浸処理と乾
燥を反復する。疎水性ゼオライトの好適担持量は、二酸
化マンガン触媒100重量部当たり約15〜40重量部
である。疎水性ゼオライトの量が十分でないと悪臭発生
を完全に阻止することができない。一方、必要以上に担
持させると、二酸化マンガン触媒の担持量を制限するば
かりか、触媒のオゾン分解活性を阻害する傾向がある。
In order to support finely powdered active manganese dioxide and hydrophobic zeolite on the above-mentioned carrier, an inorganic binder such as silica sol, alumina sol, titania sol, or a mixture thereof is added to a suspension of active manganese dioxide and hydrophobic zeolite. What is necessary is just to impregnate the carrier by immersion or coating with the addition, and to dry it. At this time, the amount of the binder used is desirably limited to a necessary minimum. If the binder is used in excess, the surface of the manganese dioxide is covered and the catalytic activity is reduced. If it is difficult to fix the required amount of catalyst at one time, the catalyst impregnation and drying are repeated until an appropriate amount of catalyst is fixed. The preferred supported amount of hydrophobic zeolite is diacid
About 15-40 parts by weight per 100 parts by weight of manganese oxide catalyst
It is. Insufficient amount of hydrophobic zeolite produces odor
Cannot be completely prevented. On the other hand,
Limit the amount of supported manganese dioxide catalyst.
It tends to inhibit the ozonolysis activity of the catalyst.

【0018】活性二酸化マンガンと疎水性ゼオライト
は、結合剤を添加した懸濁液を別々に調製しておき、一
方の含浸・固定処理を終わった後で他方を担持させても
よい。
The active manganese dioxide and the hydrophobic zeolite may be prepared by separately preparing a suspension to which a binder has been added, and carrying one of the suspensions after the impregnation / fixing treatment.

【0019】担体に二酸化マンガン触媒と疎水性ゼオラ
イトを担持させるにあたり、紙の繊維間空隙の一部は空
隙のまま残るようにして、残存空隙率、すなわち触媒と
ゼオライトを担持させた後に上記空隙率算出式に従って
計算される空隙率を50〜85%程度にすると、担体を
構成する紙の芯部に固定された触媒の表面まで被処理空
気が拡散し易く、二酸化マンガン触媒の利用率がよくな
る。
When the manganese dioxide catalyst and the hydrophobic zeolite are supported on the carrier, a part of the interfiber space of the paper is left as a void, so that the remaining porosity, that is, the porosity after the catalyst and the zeolite are supported. When the porosity calculated according to the calculation formula is about 50 to 85%, the air to be treated easily diffuses to the surface of the catalyst fixed to the core of the paper constituting the carrier, and the utilization rate of the manganese dioxide catalyst is improved.

【0020】[0020]

【実施例】【Example】

実施例1 繊維径が2〜3μmのシリカアルミナ繊維と少量の有機
質結合剤よりなる厚さ0.1mm、空隙率90%の紙をコ
ルゲート紙に加工し、未加工の平らなものとコルゲート
加工したものとを交互に重ね合わせ、接点をシリカ系接
着剤で接着することにより、セル数560/in2のハニ
カム構造担体を得た。
Example 1 A paper having a thickness of 0.1 mm and a porosity of 90% made of silica-alumina fiber having a fiber diameter of 2 to 3 μm and a small amount of an organic binder was processed into corrugated paper and corrugated with an unprocessed flat paper. The honeycomb structure carrier having 560 / in 2 cells was obtained by alternately stacking the contacts and bonding the contacts with a silica-based adhesive.

【0021】一方、硫酸マンガン水溶液と炭酸ソーダ水
溶液とを反応させて生じた沈殿を水洗、乾燥することに
より得られた炭酸マンガン1kgを水2000mlに懸濁さ
せ、60℃に加温して撹拌しながら少しずつ次亜塩素酸
ソーダ水溶液を加えた。これにより、炭酸マンガンは炭
酸ガスを発生しながら反応して黒色の二酸化マンガンに
変化した。反応完了後、生成した二酸化マンガンの沈殿
を濾過し、水洗して乾燥した。得られた二酸化マンガン
粉末は、比表面積が220m2/g、平均粒径が5μmであ
った。
On the other hand, a precipitate formed by reacting an aqueous solution of manganese sulfate and an aqueous solution of sodium carbonate is washed with water and dried, and 1 kg of manganese carbonate obtained is suspended in 2000 ml of water, heated to 60 ° C. and stirred. The sodium hypochlorite aqueous solution was added little by little while adding. As a result, manganese carbonate reacted while generating carbon dioxide gas and changed to black manganese dioxide. After the completion of the reaction, the formed precipitate of manganese dioxide was filtered, washed with water and dried. The obtained manganese dioxide powder had a specific surface area of 220 m 2 / g and an average particle size of 5 μm.

【0022】上記二酸化マンガン粉末100重量部、疎
水性ゼオライト(SiO2/Al23=150)30重量
部、およびシリカゾル(固形分30重量%)100重量
部を水200重量部と混合し、得られたスラリーに上記
ハニカム構造担体(寸法:セル開口面100mm×100
mm,通気方向長さ15mm)を浸漬し、乾燥した。その
後、上記浸漬、乾燥をさらに1回繰り返すことにより、
二酸化マンガン担持量が46g/m2、疎水性ゼオライト担
持量が14g/m2、残存空隙率が70%のオゾンフィルタ
ーを得た。
100 parts by weight of the above manganese dioxide powder, 30 parts by weight of a hydrophobic zeolite (SiO 2 / Al 2 O 3 = 150), and 100 parts by weight of silica sol (solid content: 30% by weight) were mixed with 200 parts by weight of water. The resulting slurry was added to the above honeycomb structured carrier (dimensions: cell opening surface 100 mm × 100).
mm, 15 mm in the ventilation direction) and dried. Then, by repeating the above immersion and drying once more,
An ozone filter having a manganese dioxide loading of 46 g / m 2 , a hydrophobic zeolite loading of 14 g / m 2 , and a residual porosity of 70% was obtained.

【0023】比較例1 疎水性ゼオライトを添加しないほかは実施例1と同様に
して調製した触媒スラリーで実施例1と同様の担持処理
を行い、二酸化マンガン担持量が46g/m2のオゾンフィ
ルターを製造した。
COMPARATIVE EXAMPLE 1 A catalyst slurry prepared in the same manner as in Example 1 except that hydrophobic zeolite was not added was subjected to the same loading treatment as in Example 1 to obtain an ozone filter having a manganese dioxide loading of 46 g / m 2. Manufactured.

【0024】次に、上記各例のオゾンフィルターについ
て、下記の方法でオゾン分解能を調べた。 試験法:無声放電型オゾン発生機で除湿空気を処理して
得られたオゾン含有空気を清浄な空気で希釈して、オゾ
ン濃度0.5ppm、温度27℃、相対湿度80%の被処理
ガスを調製する。この被処理ガスを空間速度28万/H
rで、ハニカム構造担体のセル開口面が通気方向に対し
て直角になるように配置した上記オゾンフィルターに流
し続ける。所定時間経過後に、出口側空気を採取してオ
ゾン分解率(次式による)を測定する。 オゾン分解率(%)=(入口オゾン濃度−出口オゾン濃
度)×100/入口オゾン濃度
Next, the ozone resolution of the ozone filters of the above examples was examined by the following method. Test method: Ozone-containing air obtained by treating dehumidified air with a silent discharge type ozone generator was diluted with clean air to obtain a gas to be treated having an ozone concentration of 0.5 ppm, a temperature of 27 ° C. and a relative humidity of 80%. Prepare. The gas to be treated is converted to a space velocity of 280,000 / H
In r, the cell is kept flowing through the ozone filter arranged so that the cell opening surface of the honeycomb structure carrier is perpendicular to the ventilation direction. After a lapse of a predetermined time, the outlet side air is sampled and the ozone decomposition rate (by the following formula) is measured. Ozone decomposition rate (%) = (inlet ozone concentration−outlet ozone concentration) × 100 / inlet ozone concentration

【0025】測定結果は次のとおりで、疎水性ゼオライ
トを混合担持させた実施例製品はオゾン分解能が若干低
下したが、実用上は十分な分解能のものと認められた。
The measurement results are as follows. The ozone decomposing ability of the product of the embodiment in which the hydrophobic zeolite was mixed and supported was slightly lowered, but it was confirmed that the ozone resolving power was sufficient for practical use.

【0026】次に、各例オゾンフィルターを静電記録式
複写機に装着して連続使用し、悪臭を発生するに至る複
写枚数を比較する試験を行なったところ、比較例製品装
着機は10万枚複写した時点で悪臭を感じたが、実施例
製品装着機は18万枚複写後も悪臭を感じさせなかっ
た。
Next, a test was carried out to compare the number of copies leading to the generation of offensive odors by attaching the ozone filter to the electrostatic recording type copier and continuously using the same. At the time of copying the sheets, an odor was felt, but the machine equipped with the product of the example did not feel the odor even after copying 180,000 sheets.

【0027】[0027]

【発明の効果】上述のように、本発明によれば二酸化マ
ンガン触媒を用いたオゾンフィルターを長期間使用して
も悪臭が発生しないようにすることができ、オゾンを発
生する機器周辺の作業環境を良好に保つことができる。
As described above , according to the present invention , the amount of
Long-term use of ozone filters using gun catalysts
Also, it is possible to prevent the generation of a bad odor, and it is possible to maintain a favorable working environment around the equipment that generates ozone.

───────────────────────────────────────────────────── フロントページの続き (56)参考文献 特開 平4−7038(JP,A) 特開 平4−313320(JP,A) 特開 平3−42016(JP,A) 特開 昭59−10345(JP,A) 特開 平5−23591(JP,A) 特開 昭63−7844(JP,A) 特開 平5−261294(JP,A) 特開 平3−8447(JP,A) (58)調査した分野(Int.Cl.7,DB名) B01D 53/86 B01J 21/00 - 38/74 B01D 39/00 - 39/20 ──────────────────────────────────────────────────続 き Continuation of the front page (56) References JP-A-4-7038 (JP, A) JP-A-4-313320 (JP, A) JP-A-3-42016 (JP, A) 10345 (JP, A) JP-A-5-23591 (JP, A) JP-A-63-7844 (JP, A) JP-A-5-261294 (JP, A) JP-A-3-8447 (JP, A) (58) Field surveyed (Int.Cl. 7 , DB name) B01D 53/86 B01J 21/00-38/74 B01D 39/00-39/20

Claims (1)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 オゾン分解能を有する微粉末状活性二酸
化マンガンを高空隙率の無機繊維製紙からなる担体に担
持させてオゾンフィルターを製造するに当たり、上記微
粉末状活性二酸化マンガンと共にSiO/Al
比が15以上のゼオライト粉末を担体に担持させること
を特徴とするオゾンフィルターからの悪臭発生を防止す
る方法。
A fine powdered active diacid having ozone decomposability
Manganese oxide supported on a carrier made of inorganic fiber paper with high porosity
When manufacturing an ozone filter with
SiO 2 / Al 2 O 3 with powdered active manganese dioxide
Supporting a zeolite powder having a ratio of 15 or more on a carrier
Prevents offensive odor from the ozone filter
Way.
JP06229060A 1994-08-31 1994-08-31 How to Prevent Odor Generation from Ozone Filter Expired - Fee Related JP3126012B2 (en)

Priority Applications (4)

Application Number Priority Date Filing Date Title
JP06229060A JP3126012B2 (en) 1994-08-31 1994-08-31 How to Prevent Odor Generation from Ozone Filter
GB9516983A GB2292698B (en) 1994-08-31 1995-08-18 Ozone filter and process for producing the same
US08/519,097 US5698165A (en) 1994-08-31 1995-08-24 Ozone filter and process for producing the same
DE19531179A DE19531179B4 (en) 1994-08-31 1995-08-24 Ozone filter and process for its preparation

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP06229060A JP3126012B2 (en) 1994-08-31 1994-08-31 How to Prevent Odor Generation from Ozone Filter

Publications (2)

Publication Number Publication Date
JPH0871369A JPH0871369A (en) 1996-03-19
JP3126012B2 true JP3126012B2 (en) 2001-01-22

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ID=16886115

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Country Link
JP (1) JP3126012B2 (en)

Family Cites Families (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5910345A (en) * 1983-06-06 1984-01-19 Nichias Corp Carrier of catalyst
JPS637844A (en) * 1986-06-30 1988-01-13 Kubota Ltd Filter material for decomposing ozone
JPH038447A (en) * 1989-03-07 1991-01-16 Sakai Chem Ind Co Ltd Catalyst for decomposition of ozone
JPH0738937B2 (en) * 1989-07-06 1995-05-01 株式会社日本触媒 Deodorization method
JP3072521B2 (en) * 1990-04-24 2000-07-31 株式会社キャタラー Method for producing ozone decomposition catalyst
JP2699666B2 (en) * 1991-01-31 1998-01-19 ダイキン工業株式会社 Deodorizing device
JPH0691957B2 (en) * 1991-07-19 1994-11-16 ニチアス株式会社 Ozone filter and its manufacturing method
JPH05261294A (en) * 1992-03-23 1993-10-12 Cataler Kogyo Kk Catalyst for decomposing ozone and its production

Also Published As

Publication number Publication date
JPH0871369A (en) 1996-03-19

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