JPS644786B2 - - Google Patents
Info
- Publication number
- JPS644786B2 JPS644786B2 JP60259108A JP25910885A JPS644786B2 JP S644786 B2 JPS644786 B2 JP S644786B2 JP 60259108 A JP60259108 A JP 60259108A JP 25910885 A JP25910885 A JP 25910885A JP S644786 B2 JPS644786 B2 JP S644786B2
- Authority
- JP
- Japan
- Prior art keywords
- ozone
- electric field
- deodorizer
- field device
- space
- 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
Links
- CBENFWSGALASAD-UHFFFAOYSA-N Ozone Chemical compound [O-][O+]=O CBENFWSGALASAD-UHFFFAOYSA-N 0.000 claims description 57
- 230000005684 electric field Effects 0.000 claims description 42
- 230000001877 deodorizing effect Effects 0.000 claims description 25
- 239000003054 catalyst Substances 0.000 claims description 12
- 238000000354 decomposition reaction Methods 0.000 claims description 9
- 239000011148 porous material Substances 0.000 claims description 5
- 238000001179 sorption measurement Methods 0.000 claims description 4
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 description 8
- 238000004332 deodorization Methods 0.000 description 8
- 229910000037 hydrogen sulfide Inorganic materials 0.000 description 8
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 6
- 238000009792 diffusion process Methods 0.000 description 6
- 238000000034 method Methods 0.000 description 6
- 239000001301 oxygen Substances 0.000 description 6
- 229910052760 oxygen Inorganic materials 0.000 description 6
- 239000007789 gas Substances 0.000 description 5
- 238000006243 chemical reaction Methods 0.000 description 4
- 238000002474 experimental method Methods 0.000 description 4
- 238000006864 oxidative decomposition reaction Methods 0.000 description 4
- 239000000463 material Substances 0.000 description 3
- 238000005259 measurement Methods 0.000 description 3
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 2
- 239000000919 ceramic Substances 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- BASFCYQUMIYNBI-UHFFFAOYSA-N platinum Chemical compound [Pt] BASFCYQUMIYNBI-UHFFFAOYSA-N 0.000 description 2
- QPLDLSVMHZLSFG-UHFFFAOYSA-N Copper oxide Chemical compound [Cu]=O QPLDLSVMHZLSFG-UHFFFAOYSA-N 0.000 description 1
- 239000005751 Copper oxide Substances 0.000 description 1
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 description 1
- 229920002472 Starch Polymers 0.000 description 1
- 229910021529 ammonia Inorganic materials 0.000 description 1
- 229910000431 copper oxide Inorganic materials 0.000 description 1
- 238000001514 detection method Methods 0.000 description 1
- 238000002845 discoloration Methods 0.000 description 1
- 239000006260 foam Substances 0.000 description 1
- 230000005484 gravity Effects 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 229910000480 nickel oxide Inorganic materials 0.000 description 1
- 229910000510 noble metal Inorganic materials 0.000 description 1
- 230000009965 odorless effect Effects 0.000 description 1
- GNRSAWUEBMWBQH-UHFFFAOYSA-N oxonickel Chemical compound [Ni]=O GNRSAWUEBMWBQH-UHFFFAOYSA-N 0.000 description 1
- 229910052697 platinum Inorganic materials 0.000 description 1
- 229910052700 potassium Inorganic materials 0.000 description 1
- 239000011591 potassium Substances 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 239000008107 starch Substances 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
- 229910000314 transition metal oxide Inorganic materials 0.000 description 1
- 238000009423 ventilation Methods 0.000 description 1
Landscapes
- Disinfection, Sterilisation Or Deodorisation Of Air (AREA)
Description
産業上の利用分野
この発明は、一般家庭用などの分野に適用され
るオゾンを用いた簡易脱臭器に関するものであ
る。
従来の技術
近時、オゾンによる脱臭が脚光を浴びている
が、このような脱臭装置は、オゾン発生装置、反
応室、余剰オゾンの分解設備などを必要とし装置
が大型化して設備費がかさむばかりか、高濃度の
オゾンを使用するのでオゾンの流路周辺は耐オゾ
ン性の材質にしなければならず、これらの点から
して、その利用分野は産業用に限られていた。し
かし、オゾンによる脱臭の効能は顕著なものであ
ることからして、前記以外の利用分野を開拓すべ
きであり、小型、簡易化して一般家庭などでも適
用できる脱臭器の開発が強く望まれていた。
発明が解決しようとする問題点
オゾンによる脱臭装置を小型、簡易化して一般
家庭などでも適用できるようにし、その利用分野
を拡大することにある。
問題点を解決するための手段
オゾン発生電界装置と、多孔フイルターを担体
としこれに触媒を付加処理した脱臭体または該脱
臭体及び絶縁性非通気体にて構成しかつ内部に前
記電界装置内装用の電界空間部を設けた脱臭器本
体とを具備し、前記電界装置を空間部内に配装し
たことにある。
作 用
簡易脱臭器の電界空間部内の電界装置より生成
したオゾンは、放電から得た熱・運動のエネルギ
ーによつて、脱臭体中を分解反応しながら通過し
酸素となつて外部へ拡散する。この拡散につれて
外部の悪臭性空気が脱臭体を経て空間部内にとり
込まれるが、悪臭成分はこの空間部及び脱臭体を
経て酸化分解無臭化されて外部へ拡散していく。
このように拡散ととり込みが行われることからし
て、脱臭器周辺の密封空間は時間をかけて循環し
脱臭化が進行する。
実施例
この発明の実施例を第1乃至5図により詳述す
る。第1図はこの発明簡易脱臭器の断面、斜視
図、第2図は第1図X,X線拡大断面図、第3図
は電界装置の平面図、第4図は第3図円線部分の
拡大断面図、第5図は他の実施例の断面図であ
る。
図中1はオゾン発生電界装置、2は脱臭体、3
は非通気体、4は電界空間部、5は脱臭器本体、
6は簡易脱臭器、7は耐オゾン、通気性の外被体
である。
オゾン発生電界装置1は、絶縁物層1a内に
線、または帯状電極1b,1cが平行状に埋設し
てあり、これに交流電源8からの高電圧を電線8
aを介して印加すると、該層1a表面の近傍空間
部の気体中に無声放電が発生し、その気体中の酸
素からオゾンが生成するものである。脱臭器本体
5は、三次元骨格構造により連続気孔をもたせた
吸着性の優れた多孔フイルターを担体としてお
り、これに後述するオゾン分解用の触媒を付加処
理した脱臭体2、または該脱臭体2及びセラミツ
ク板等の絶縁性非通気体3にて構成され、内部に
前記電界装置1を内装しオゾンを発生するに必要
な所要容積の電界空間部4を設けてある。即ち、
この発明の簡易脱臭器6は、前記電界装置1を空
間部4内にオゾンが発生可能にして設置したもの
である。第1、2で例示した簡易脱臭器6は、脱
臭体2及び非通気体3からなりかつ内部に電界装
置1内装用の電界空間部4を設けて脱臭器本体5
を構成し、前記非通気体3上に電界装置1をその
層1aの上面を空間部4内に露出してオゾン発生
可能に設置したものである。
第5図の簡易脱臭器6は、脱臭体2のみからな
りかつ内部に電界装置1内装用の電界空間部4を
設けて脱臭器本体5を構成し、その空間部4の中
間位置に電界装置1が配置してある。前記多孔フ
イルターには、例えば、商品名セラミツクフオー
ム((株)ブリジストン社製)、セルメツト(住友電
気工業(株)社製)があり、これらは三次元骨格構造
により連続気孔が構成されており、悪臭成分(硫
化水素、アンモニア、その他悪臭を放つ成分等々
を含む)を吸着する性質がある。また、触媒とし
ては、酸化ニツケル、銅酸化物等の遷移金属酸化
物、白金などの貴金属、もしくはこれらの混合物
が適当である。
第2図において、この発明の簡易脱臭器1は、
電界装置1の電極1b,1cに交流電源8からの
高電圧(2.1〜3.5KV)を印加すると、絶縁物層
1a表面の近傍空間部分4aの気体中に無声放電
が発生し、これによりその気体中の酸素からオゾ
ンが生成する。
O2+e-→2O
O+2O2→O3+O2
生成したオゾンO3は、放電から得た熱・運動
のエネルギーによつて、例えば、第2図のような
配置、決められた時間内においては、脱臭体2の
気孔中を後述する分解反応をしながら一点鎖線、
実線矢印の如く通過し酸素となつて外部へ拡散し
ていく。この拡散につれて、外部の悪臭性空気G
が脱臭体2の気孔中を悪臭成分の一部を吸着・濃
縮されながら二点鎖線矢印の如く通過し空間部4
内にとり込まれて、後述するように酸化分解無臭
化されて外部へ拡散していく。このように拡散と
とり込みがゆるやかに行われることからして、こ
の脱臭器6の周辺密封空間は、全体として時間を
かけて循環し脱臭化が進行する。前記オゾンの分
解反応については、次のような過程を経て脱臭体
2表面に達するまでには酸素に分解し無害とな
る。即ち、(i)空間部4内における自己分解反応
(2O3→3O2)、(ii)脱臭体2に吸着されたオゾンが
オゾン分解触媒によつて分解(O3+M→O2+O
+M、Mは触媒)する。なお、空間部4内でのオ
ゾンは、半減期が数時間乃至十数時間と比較的安
定しており、その大部分は(ii)の過程で分解する。
前記オゾンの発生量は、印加電圧、空間部の容積
などに関係し、また、オゾンの分解量は脱臭体2
の厚さ、触媒の担持量に因るので、これらを適宜
調整すればオゾンが脱臭器6外に漏れることがな
く、そして、空間部4内には高濃度のオゾン雰囲
気をつくることができる。前記悪臭成分の酸化分
解無臭化については、次のような過程によつて行
われる。即ち、(i)空間部4内におけるオゾンとの
気相酸化分解、(ii)脱臭体2に吸着されて後オゾン
または触媒により酸化分解、(iii)脱臭体に吸着され
たオゾンまたは吸着後分解したオゾンから生成す
る活性種(発生期の酸素O)による分解、がなさ
れ、主に(ii)、(iii)の過程を経て脱臭が進行する。即
ち、前記脱臭体2により一部吸着された悪臭成分
は(ii)の反応過程を経て分解する。なお、前記酸化
分解無臭化が進行し悪臭性空気G中の悪臭成分が
零に等しい状態では、電界装置1より生成するオ
ゾンは、前記オゾンの分解反応と同様の反応を繰
り返えして分解し無害となつて外部へ拡散してい
く。第6乃至8図は、この発明脱臭器6の周辺密
封空間内の空気が前述のように該脱臭器6を介し
て循環することを実験によつて実証するもので、
第9図に示す内容積15.5の密閉箱9の下壁面に
脱臭器6を設置し、側壁面の三面及び上壁面の全
面に夫々ヨウ化カリウム−でんぷん紙10を貼付
する。次いで、電界装置1に高電圧を印加してオ
ゾンを発生せしめる。紙10は、オゾンが接した
部分から変色し始めるのでオゾン発生−拡散の過
程が明確となる。この結果を第6,7,8図に示
し、電圧を印加して夫々10、30、60分後の紙10
の変色の濃さの違いをa、b、c(a<b<c)
の段階に区分した。即ち、生成したオゾンは、比
重が空気より大であるにもかかわらず第6図の左
側壁面より上昇して上壁面に当接し、そして、こ
こで向を変えて右側壁面に当接して後下壁面に下
降しており、これによりこの発明の脱臭器6は、
循環のための手段を必要とすることなく、前記の
通りの循環が繰り返えし行われる。
この発明の脱臭器1の脱臭効能を第9,10図
により説明すると、前記実験で使用した密閉箱9
中に、脱臭体2の厚さt=10mm、電界装置1と脱
臭体2との対向間隔d=5mmとする脱臭器6を設
置する。脱臭器6の電界装置1は、電線11を介
してトランス12、スライダツク13、電源14
の順に接続されている。15はパイプ、16は乾
燥器、17は送風機、18は排気孔、19は測定
孔、20は撹拌羽根である。乾燥器16により箱
9内の湿度を一定にした後、この箱9内に高濃度
の硫化水素を注射器21にて封入し、次いで、羽
根20により撹拌して内部を均一濃度(30〜
40ppm)にする。電界装置1に3.5KVの電圧を印
加すると第10図の曲線の通り、硫化水素の除
去率が時間の経過とともに大きくなる。曲線は
電界装置1に印加しない場合でその他は前記と同
じ条件であり、曲線は多孔フイルターに触媒を
付加せず、そして、電界装置1に印加しない場合
でその他は前記と同じ条件のときの結果である。
曲線については硫化水素が多孔フイルターに吸
着されること、そして、曲線は該吸着に加えて
硫化水素と触媒とが反応・分解することにより
夫々硫化水素の除去率が高まるものと考えられ
る。そこへ電界装置に印加してオゾンを発生させ
ると、前記のごとく、オゾン及び活性種による硫
化水素の分解が付加されて、曲線のように硫化
水素の除去率がより高まるのである。この発明の
脱臭器6は、該脱臭器6の外部にオゾンが全く流
出せず安全であるが、これは、以下の実験及び表
により実証できる。即ち、前記の実験で使用した
密閉箱9中に脱臭器6を設置する。この実験で
は、脱臭体2の厚さt、印加電圧KV、及び電界
装置1と脱臭体2との対向間隔dなどを変化させ
て、脱臭器6外へ流出するオゾンの濃度(ppm)
を測定した。測定に際し、オゾン用ガス検知管を
使用し測定孔19から測定した。次表はその結果
である。
INDUSTRIAL APPLICATION FIELD This invention relates to a simple deodorizer using ozone that is applied to general household use and other fields. Conventional technology Recently, deodorization using ozone has been in the spotlight, but such deodorization equipment requires an ozone generator, a reaction chamber, equipment for decomposing excess ozone, etc., which increases the size of the equipment and equipment costs. Furthermore, since highly concentrated ozone is used, the area around the ozone flow path must be made of ozone-resistant material, and from these points of view, its field of use has been limited to industrial use. However, since the effectiveness of ozone deodorization is remarkable, it is necessary to explore fields of use other than those mentioned above, and there is a strong desire to develop a deodorizer that is smaller and simpler and can be used in general households. Ta. Problems to be Solved by the Invention It is an object of the present invention to make ozone deodorizing equipment small and simple so that it can be applied in ordinary homes, and to expand its field of use. Means for Solving the Problems An ozone generating electric field device, a deodorizing body made of a porous filter as a carrier and a catalyst added thereto, or the deodorizing body and an insulating non-ventilating body, and the interior of the electric field device is and a deodorizer main body provided with an electric field space, and the electric field device is disposed within the space. Function Ozone generated by the electric field device in the electric field space of the simple deodorizer passes through the deodorizing body while decomposing and reacting due to the heat and kinetic energy obtained from the discharge, becoming oxygen and diffusing to the outside. As this diffusion occurs, external malodorous air is taken into the space through the deodorizing body, but the malodorous components are oxidized, decomposed, and deodorized through the space and the deodorizing body, and diffuse to the outside.
Given that diffusion and uptake occur in this way, the sealed space around the deodorizer takes time to circulate and deodorization progresses. Embodiment An embodiment of the present invention will be described in detail with reference to FIGS. 1 to 5. Fig. 1 is a cross-sectional and perspective view of the simple deodorizer of the present invention, Fig. 2 is an enlarged sectional view of the X and X lines in Fig. 1, Fig. 3 is a plan view of the electric field device, and Fig. 4 is the circle line in Fig. 3. FIG. 5 is an enlarged sectional view of another embodiment. In the figure, 1 is an ozone generating electric field device, 2 is a deodorizing body, and 3 is
is a non-ventilating body, 4 is an electric field space part, 5 is a deodorizer body,
6 is a simple deodorizer, and 7 is an ozone-resistant, breathable outer cover. The ozone generating electric field device 1 has wires or strip electrodes 1b and 1c buried in parallel in an insulating layer 1a, and a high voltage from an AC power source 8 is applied to the wires 8.
When it is applied through a, a silent discharge occurs in the gas in the space near the surface of the layer 1a, and ozone is generated from the oxygen in the gas. The deodorizer main body 5 has a porous filter with excellent adsorption properties that has continuous pores due to a three-dimensional skeleton structure as a carrier, and a deodorizer 2 which has been additionally treated with a catalyst for ozone decomposition, which will be described later, or the deodorizer 2. It is constructed of an insulating non-ventilated material 3 such as a ceramic plate, and is provided with an electric field space portion 4 having the required volume to house the electric field device 1 and generate ozone. That is,
A simple deodorizer 6 of the present invention has the electric field device 1 installed in the space 4 so as to be able to generate ozone. The simple deodorizer 6 exemplified in No. 1 and 2 consists of a deodorizing body 2 and a non-ventilating body 3, and an electric field space 4 for the interior of the electric field device 1 is provided inside the deodorizer main body 5.
The electric field device 1 is installed on the non-ventilated body 3 with the upper surface of the layer 1a exposed in the space 4 so that ozone can be generated. The simple deodorizer 6 shown in FIG. 5 consists of only a deodorizer 2 and has an electric field space 4 for the interior of the electric field device 1 inside to form a deodorizer main body 5, and the electric field device is located in the middle of the space 4. 1 is placed. Examples of the porous filter include the product names Ceramic Foam (manufactured by Bridgestone Corporation) and Selmet (manufactured by Sumitomo Electric Industries, Ltd.), which have continuous pores formed by a three-dimensional skeleton structure, It has the property of adsorbing malodorous components (including hydrogen sulfide, ammonia, and other malodorous components). Suitable catalysts include transition metal oxides such as nickel oxide and copper oxide, noble metals such as platinum, or mixtures thereof. In FIG. 2, the simple deodorizer 1 of the present invention is
When a high voltage (2.1 to 3.5 KV) from the AC power supply 8 is applied to the electrodes 1b and 1c of the electric field device 1, a silent discharge occurs in the gas in the space 4a near the surface of the insulating layer 1a, and this causes the gas to Ozone is produced from the oxygen inside. O 2 +e - →2O O+2O 2 →O 3 +O 2The generated ozone O 3 is generated by the thermal and kinetic energy obtained from the discharge, for example, in the arrangement shown in Figure 2, within a fixed time. , while the decomposition reaction described below takes place in the pores of the deodorizing body 2, the chain line
It passes through as shown by the solid arrow and becomes oxygen and diffuses to the outside. As this diffusion occurs, the external malodorous air G
passes through the pores of the deodorizing body 2 as shown by the two-dot chain arrow while adsorbing and concentrating a part of the malodorous components, and enters the space 4.
It is taken into the interior, oxidized, decomposed and odorless, and diffused to the outside, as will be described later. Since the diffusion and uptake are performed slowly in this way, the sealed space around the deodorizer 6 is circulated as a whole over time, and deodorization progresses. Regarding the decomposition reaction of ozone, it decomposes into oxygen and becomes harmless by the time it reaches the surface of the deodorizing body 2 through the following process. That is, (i) self-decomposition reaction (2O 3 → 3O 2 ) in the space 4, (ii) ozone adsorbed on the deodorizing body 2 is decomposed by the ozone decomposition catalyst (O 3 +M→O 2 +O
+M, M is catalyst). Note that ozone in the space 4 is relatively stable with a half-life of several hours to more than ten hours, and most of it is decomposed during the process (ii).
The amount of ozone generated is related to the applied voltage, the volume of the space, etc., and the amount of ozone decomposed depends on the deodorizing body 2.
Since this depends on the thickness of the deodorizer and the amount of catalyst supported, if these are adjusted appropriately, ozone will not leak out of the deodorizer 6, and a highly concentrated ozone atmosphere can be created in the space 4. The oxidative decomposition and deodorization of the malodorous components is carried out by the following process. That is, (i) gas-phase oxidative decomposition with ozone in the space 4, (ii) oxidative decomposition with ozone or a catalyst after being adsorbed on the deodorizing body 2, (iii) ozone adsorbed on the deodorizing body or decomposition after adsorption. The ozone is decomposed by active species (nascent oxygen O) generated from the ozone, and deodorization progresses mainly through the processes (ii) and (iii). That is, the malodorous components partially adsorbed by the deodorizing body 2 are decomposed through the reaction process (ii). Note that when the oxidative decomposition and deodorization progress and the malodorous components in the malodorous air G are equal to zero, the ozone generated by the electric field device 1 is decomposed by repeating the same reaction as the ozone decomposition reaction. It becomes harmless and spreads outside. 6 to 8 demonstrate through experiments that the air in the sealed space around the deodorizer 6 of the present invention circulates through the deodorizer 6 as described above.
A deodorizer 6 is installed on the lower wall of a sealed box 9 having an internal volume of 15.5 cm as shown in FIG. 9, and potassium iodide-starch paper 10 is pasted on three side walls and the entire top wall, respectively. Next, a high voltage is applied to the electric field device 1 to generate ozone. Since the paper 10 begins to change color from the portion where it comes into contact with ozone, the process of ozone generation and diffusion becomes clear. The results are shown in Figures 6, 7, and 8, where the paper 10, 30, and 60 minutes after applying voltage
The difference in the intensity of discoloration is a, b, c (a<b<c)
It was divided into stages. That is, the generated ozone rises from the left side wall in Fig. 6 and contacts the upper wall, even though its specific gravity is greater than that of air, and then changes direction and contacts the right wall and flows backward and downward. The deodorizer 6 of the present invention is lowered to the wall surface.
Circulation as described above is carried out repeatedly without requiring any means for circulation. The deodorizing effect of the deodorizer 1 of this invention will be explained with reference to FIGS. 9 and 10.
Inside, a deodorizer 6 is installed, in which the thickness of the deodorizer 2 is t=10 mm, and the facing distance between the electric field device 1 and the deodorizer 2 is d=5 mm. The electric field device 1 of the deodorizer 6 is connected to a transformer 12, a slider 13, and a power source 14 via an electric wire 11.
are connected in this order. 15 is a pipe, 16 is a dryer, 17 is a blower, 18 is an exhaust hole, 19 is a measurement hole, and 20 is a stirring blade. After keeping the humidity in the box 9 constant using the dryer 16, high-concentration hydrogen sulfide is sealed in the box 9 using a syringe 21, and then stirred with a blade 20 to maintain a uniform concentration (30~
40ppm). When a voltage of 3.5 KV is applied to the electric field device 1, the hydrogen sulfide removal rate increases as time passes, as shown by the curve in FIG. The curve shows the result when the electric field device 1 is not applied and the other conditions are the same as above, and the curve shows the result when no catalyst is added to the porous filter and when the electric field device 1 is not applied and the other conditions are the same as above. It is.
It is thought that the curve indicates that hydrogen sulfide is adsorbed by the porous filter, and that the removal rate of hydrogen sulfide increases due to the reaction and decomposition of hydrogen sulfide and the catalyst in addition to the adsorption. When an electric field is applied thereto to generate ozone, hydrogen sulfide is decomposed by ozone and active species as described above, and the removal rate of hydrogen sulfide further increases as shown in the curve. The deodorizer 6 of this invention is safe as no ozone leaks out of the deodorizer 6, and this can be demonstrated by the following experiment and table. That is, the deodorizer 6 is installed in the sealed box 9 used in the above experiment. In this experiment, the concentration (ppm) of ozone flowing out of the deodorizer 6 was determined by changing the thickness t of the deodorizer 2, the applied voltage KV, the facing distance d between the electric field device 1 and the deodorizer 2, etc.
was measured. The measurement was carried out through the measurement hole 19 using an ozone gas detection tube. The following table shows the results.
【表】【table】
【表】
表中の数値は、電圧印加60分後の箱9内のオゾ
ン濃度(ppm)の測定値である。即ち、オゾンの
流出を防止するためには、表中の適正値によつて
決めることができる。なお、脱臭体に代えて触媒
無処理の多孔フイルター厚さ10mmを使用し、これ
と電界装置との対向間隔を5mmにして脱臭器を構
成し、これに印加電圧2.1KVを印加したときの30
分後のオゾンの濃度は5.1ppmであつた。
発明の効果
この発明は以上のように、オゾン発生電界装置
と、多孔フイルターを担体としこれに触媒を付加
処理した脱臭体または該脱臭体及び絶縁性非通気
体にて構成しかつ内部に前記電界装置内装用の電
界空間部を設けた脱臭器本体とを具備し、前記電
界装置を空間部内にオゾン発生可能に配装したの
で、小型、簡易化が容易に行えてその利用分野が
拡大でき、一般家庭などに適用してその効果は大
きい。[Table] The values in the table are the measured values of ozone concentration (ppm) in box 9 after 60 minutes of voltage application. That is, in order to prevent the outflow of ozone, it can be determined based on the appropriate values in the table. In addition, a deodorizer was constructed by using a non-catalyst-treated porous filter with a thickness of 10 mm instead of the deodorizing body, and setting the opposing distance between this and the electric field device to 5 mm, and when an applied voltage of 2.1 KV was applied to this, the
The ozone concentration after 5 minutes was 5.1 ppm. Effects of the Invention As described above, the present invention comprises an ozone generating electric field device, a deodorizing body using a porous filter as a carrier and a catalyst added to the deodorizing body, or the deodorizing body and an insulating non-ventilating body, and the electric field inside the ozone generating electric field device. The deodorizer body is provided with an electric field space for the interior of the device, and the electric field device is installed in the space so as to be able to generate ozone, so it can be easily made smaller and simpler, and its fields of use can be expanded. The effect is great when applied to general households.
第1図はこの発明簡易脱臭器の断面斜視図、第
2図は第1図X,X線拡大断面図、第3図は電界
装置の平面図、第4図は第3図円線部分の拡大断
面図、第5図は他の実施例の断面図、第6,7,
8図は夫々オゾン発生−拡散の過程の略視的説明
図、第9図はこの発明脱臭器についての実験装
置、第10図は脱臭の効果を示すグラフである。
1……オゾン発生電界装置、2……脱臭体、3
……絶縁性非通気体、4……電界空間部、5……
脱臭器本体、6……簡易脱臭器。
Fig. 1 is a cross-sectional perspective view of the simple deodorizer of the present invention, Fig. 2 is an enlarged cross-sectional view of the An enlarged cross-sectional view, FIG. 5 is a cross-sectional view of another embodiment, Nos. 6, 7,
Fig. 8 is a schematic illustration of the process of ozone generation and diffusion, Fig. 9 is an experimental apparatus for the deodorizer of the present invention, and Fig. 10 is a graph showing the deodorizing effect. 1... Ozone generating electric field device, 2... Deodorizing body, 3
...Insulating non-ventilation material, 4...Electric field space part, 5...
Deodorizer body, 6...Simple deodorizer.
Claims (1)
り連続気孔をもたせた吸着性に優れた多孔フイル
ターを担体としこれにオゾン分解用の触媒を付加
処理した脱臭体または該脱臭体及び絶縁性非通気
体にて構成しかつ内部に前記電界装置内装用の電
界空間部を設けた脱臭器本体とを具備し、前記オ
ゾン発生電界装置を該脱臭器本体の電界空間部内
にオゾン発生可能にして設置したことを特徴とす
る簡易脱臭器。1. An ozone generating electric field device and a deodorizing body made of a porous filter with continuous pores and excellent adsorption properties as a carrier and treated with an ozone decomposition catalyst, or the deodorizing body and an insulating non-ventilating body. and a deodorizer main body having an electric field space inside for the interior of the electric field device, and the ozone generating electric field device is installed to be able to generate ozone in the electric field space of the deodorizer main body. A simple deodorizer featuring:
Priority Applications (4)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP60259108A JPS62117563A (en) | 1985-11-19 | 1985-11-19 | Simple deodorizing device |
| US06/931,392 US4842829A (en) | 1985-11-19 | 1986-11-14 | Deodorizing apparatus |
| DE19863639396 DE3639396A1 (en) | 1985-11-19 | 1986-11-18 | DEODORIZATION DEVICE |
| KR1019870000165A KR910002206B1 (en) | 1985-11-19 | 1987-01-12 | Simple deodorizing device |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP60259108A JPS62117563A (en) | 1985-11-19 | 1985-11-19 | Simple deodorizing device |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS62117563A JPS62117563A (en) | 1987-05-29 |
| JPS644786B2 true JPS644786B2 (en) | 1989-01-26 |
Family
ID=17329428
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP60259108A Granted JPS62117563A (en) | 1985-11-19 | 1985-11-19 | Simple deodorizing device |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS62117563A (en) |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2001149718A (en) * | 1999-11-24 | 2001-06-05 | Katsumi Matsumoto | Filter for air cleaner and its manufacturing method |
-
1985
- 1985-11-19 JP JP60259108A patent/JPS62117563A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS62117563A (en) | 1987-05-29 |
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