Deprecated: The each() function is deprecated. This message will be suppressed on further calls in /home/zhenxiangba/zhenxiangba.com/public_html/phproxy-improved-master/index.php on line 456
JPH0478326B2 - - Google Patents
[go: Go Back, main page]

JPH0478326B2 - - Google Patents

Info

Publication number
JPH0478326B2
JPH0478326B2 JP63058733A JP5873388A JPH0478326B2 JP H0478326 B2 JPH0478326 B2 JP H0478326B2 JP 63058733 A JP63058733 A JP 63058733A JP 5873388 A JP5873388 A JP 5873388A JP H0478326 B2 JPH0478326 B2 JP H0478326B2
Authority
JP
Japan
Prior art keywords
oxide
mixed metal
iron
metal oxide
ultraviolet rays
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
Application number
JP63058733A
Other languages
Japanese (ja)
Other versions
JPH01232966A (en
Inventor
Shuzo Tokumitsu
Noboru Naruo
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.)
Panasonic Holdings Corp
Original Assignee
Matsushita Electric Industrial 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 Matsushita Electric Industrial Co Ltd filed Critical Matsushita Electric Industrial Co Ltd
Priority to JP63058733A priority Critical patent/JPH01232966A/en
Publication of JPH01232966A publication Critical patent/JPH01232966A/en
Publication of JPH0478326B2 publication Critical patent/JPH0478326B2/ja
Granted legal-status Critical Current

Links

Landscapes

  • Exhaust Gas Treatment By Means Of Catalyst (AREA)
  • Catalysts (AREA)
  • Disinfection, Sterilisation Or Deodorisation Of Air (AREA)

Description

【発明の詳細な説明】[Detailed description of the invention]

産業上の利用分野 本発明はトイレのし尿臭、ペツトの臭い、たば
この臭い、調理臭および体臭などの光触媒による
脱臭方法に関するものである。 従来の技術 家庭やオフイスで発生するタバコ臭、トイル
臭、ペツト臭、調理臭および体臭等の悪臭成分
は、アンモニア、アミン類、インドール、スカト
ールなどの窒素化合物、硫化水素、メチルメルカ
プタン、硫化メチル、二硫化メチルなどの硫黄化
合物、アルデヒド類、ケトン類、アルコール類、
脂肪酸および芳香族化合物等、低沸点から高沸点
成分まで多種多様である。 そして、従来の家庭やオフイスで使われている
脱臭方法としては、発生源に薬剤を注ぎ化学反応
させる方法、芳香俗でマスキングする方法、活性
炭やゼオライトで吸着する方法および薬剤を添着
した吸着在に悪臭を濃縮し反応させる方法があ
る。前者の2方法は局所的に消臭する方法であ
り、トイレやペツトのいるところなどに使われて
いる。一方、後者の2方法は送風機と組み合わせ
て脱臭装置として、狭い空間から広い空間まで汎
用的に使うことの出来る脱臭方法である。中でも
活性炭がもつとも有効な手段であるが、活性炭に
於いても悪臭成分のうちアンモニア、メチルアミ
ンなどの低沸点窒素化合物とホルマリン、アセト
アルデヒド、アクロレインなどの低級脂肪族アル
デヒドに対する吸着力が弱かつた。そこで薬剤を
活性炭に添着した脱臭剤が用いられている。 発明が解決しようとする課題 アンモニア、メチルアミン等の低沸点窒素化合
物は、活性炭に有機酸や無機酸を添着させた脱臭
剤で効果的に吸着でき、その吸着容量も大きいも
のである。一方ホルマリン、アセトアルデヒド、
アクロレイン等の低級脂肪族アルデヒドの吸着に
は、活性炭にアニリンを添着した脱臭剤が有効で
あるが、添着可能なアニリンの量が少ないため、
アルデヒドの吸着容量が小さく寿命が短い。最近
問題になつているたばこの臭いや、新建材・家具
から発生する臭いには、ホルマリン、アセトアル
デヒド等が多く含まれているが、有効な脱臭方法
がなかつた。 本発明は上記従来の課題を解決するものであ
り、光触媒作用による悪臭の分解を効果的に行わ
せる脱臭方法を提供することを目的とするもので
ある。 課題を解決するための手段 上記の目的を達成するために本発明の光触媒に
よる脱臭方法は、チタン酸鉄、酸化鉄、酸化ビス
マスおよび酸化モリブデンからなる群から選択さ
れた1つの酸化物と酸化チタンとの混合酸化物
と、被酸化性化合物および酸素を含む気体との共
存下で、前記混合金属酸化物に紫外線を照射する
ものである。 作 用 本発明者等は、かねてから光触媒作用によつて
悪臭を分解し無臭化することを研究してきたが、
チタン酸鉄、酸化鉄、酸化ビスマスおよび酸化モ
リブデンからなる群から選択された酸化物と酸化
チタンとの混合金属酸化物の存在下では、一般に
知られている酸化チタン単独よりも極めてアルデ
ヒド類の酸化分解能力の高いことを見出した。上
記本発明の混合金属酸化物は紫外線の照射によつ
て分解が効率良く起こるものである。 上記混合金属酸化物の作用原理については目下
詳細に研究中であるが、上記各酸化物および酸化
チタンの半導体中の価電子帯の電子が紫外線を吸
収して伝導帯に励起され、そこで生じた価電子帯
の正孔は触媒の表面にある水酸基(OH基)と反
応し、伝導帯に励起された電子は酸素(O)と反
応して、活性の高いOHラジカル、Oラジカル、
O2-が生じ、これが被酸化性化合物を酸化分解す
るものと推測される。また酸化チタンで生じた電
子および正孔と、上記各酸化物で生じた電子およ
び正孔と互いに作用しあつて相乗効果があるもの
と推測される。 さらにこの混合物金属酸化物に白金、パラジウ
ム、ロジウム、酸化ルテニウム、銀などの導電性
無機物質を担持すると、酸化分解作用は一層強力
なものとなる。中でも白金の効果は著しい。 本発明の脱臭方法はアルデヒド類の分解に優れ
るだけで無く、他の悪臭物質のアンモニア、アミ
ン類の窒素化合物、硫化水素、メルカプタン類の
硫黄化合物、ケトン類、アルコール類、脂肪酸お
よび芳香族化合物も酸化分解して無臭化出来る。 実施例 次に本発明の実施例について説明する。 本発明において使用する酸化チタンとしては、
アナターゼ型が活性が高いが、ルチル型でも良
い。また、酸化物のうちチタン酸鉄としては
FeTiO3が活性が高いが、Fe2TiO5でも良い。 導電性無機物質としては白金がもつとも効果的
であるが、パラジウム、ロジウム、銀などの貴金
属や酸化ルテニウム等でも良い。 また紫外線としては波長が400nm以下であれ
ば良く、遠紫外線でも近紫外線でも良い。これら
の紫外線は高圧水銀灯、超高圧水銀灯、低圧水銀
灯、キセノン灯等を単独で使用又は併用すること
によつて発生させうる。また脱臭方法は、特定の
反応器に被処理気体を導入してバツチ処理しても
良いし、連続処理しても良い。 本発明に用いる混合金属酸化物は、光源の表面
に塗布して使用するとか、または光源の周囲に支
持体を設けてそれに塗布または含浸して使用する
などの方法を用いる。 次に具体的な実施例について説明する。第1表
に示す重量の金属酸化物粉末をメタノールに懸濁
せしめ、この懸濁液を厚さ0.5mm*幅120mm*長さ
240mmのアルミナ−シリカ質のセラミツクペーパ
に塗布したのち乾燥し光触媒とした。また白金の
担持は、上記金属酸化物を付けたセラミツクペー
パに塩化白金酸のエタノール溶液を含浸し、熱処
理して白金微粒子として担持した。 そして、第1図のように上記構成の触媒1をス
テンレスの台2にのせて内容積36アルミ製の反
応容器3の中に、光源4から100mm離れた位置に
置いた。光源4は10ワツトの殺菌灯(紫外線出力
約1.8ワツト、主波長254nm)を用いた。この反
応容器3の中にアセトアルデヒドの飽和ガスを注
入し、フアン5で撹拌して濃度を均一にした初濃
度を測定した。そして次に殺菌灯を点灯し、アス
トアルデヒド濃度の経時変化をガスクロマトグラ
フイで調べた。その結果を混合金属酸化物触媒に
紫外線を照射しなかつた場合、触媒を使用しない
で紫外線だけ照射した場合、およびアナターゼ型
酸化チタンだけ、あるいはチタン酸鉄FeTiO3
けを上記方法でセラミツクペーパに塗布した触媒
に紫外線を照射した場合と比較して第2図に示
す。またそれぞれの条件は第1表に示す。
INDUSTRIAL APPLICATION FIELD The present invention relates to a method for deodorizing toilet odors, pet odors, cigarette odors, cooking odors, body odors, etc. using a photocatalyst. Conventional technology Bad odor components such as cigarette odor, toilet odor, pet odor, cooking odor, and body odor that occur in homes and offices are nitrogen compounds such as ammonia, amines, indole, skatole, hydrogen sulfide, methyl mercaptan, methyl sulfide, Sulfur compounds such as methyl disulfide, aldehydes, ketones, alcohols,
There are a wide variety of components, from low to high boiling points, such as fatty acids and aromatic compounds. Conventional deodorizing methods used in homes and offices include pouring chemicals into the source and causing a chemical reaction, masking with aromatic substances, adsorption with activated carbon or zeolite, and adsorption methods impregnated with chemicals. There is a way to concentrate and react with bad odors. The first two methods are local deodorization methods and are used in areas such as toilets and areas where pets are present. On the other hand, the latter two methods are deodorizing methods that can be used in combination with a blower as a deodorizing device and can be used for general purposes from narrow spaces to wide spaces. Among these, activated carbon is the most effective means, but even activated carbon has a weak adsorption power for malodorous components such as low-boiling nitrogen compounds such as ammonia and methylamine, and lower aliphatic aldehydes such as formalin, acetaldehyde, and acrolein. Therefore, deodorizers are used in which chemicals are attached to activated carbon. Problems to be Solved by the Invention Low-boiling nitrogen compounds such as ammonia and methylamine can be effectively adsorbed with a deodorizer made of activated carbon impregnated with an organic acid or an inorganic acid, and the adsorption capacity thereof is also large. On the other hand, formalin, acetaldehyde,
A deodorizer made of activated carbon impregnated with aniline is effective for adsorbing lower aliphatic aldehydes such as acrolein, but since the amount of aniline that can be impregnated is small,
The adsorption capacity for aldehydes is small and the lifespan is short. Cigarette odors and odors emitted from new construction materials and furniture, which have recently become a problem, contain many formalin, acetaldehyde, etc., but there has been no effective deodorizing method. The present invention solves the above-mentioned conventional problems, and aims to provide a deodorizing method that effectively decomposes bad odors through photocatalytic action. Means for Solving the Problems In order to achieve the above object, the photocatalytic deodorizing method of the present invention uses one oxide selected from the group consisting of iron titanate, iron oxide, bismuth oxide and molybdenum oxide and titanium oxide. The mixed metal oxide is irradiated with ultraviolet rays in the coexistence of the mixed metal oxide, an oxidizable compound, and a gas containing oxygen. Effect The present inventors have been researching the decomposition and deodorization of bad odors through photocatalytic action for some time.
In the presence of a mixed metal oxide of titanium oxide and an oxide selected from the group consisting of iron titanate, iron oxide, bismuth oxide, and molybdenum oxide, the oxidation of aldehydes is much more effective than the generally known titanium oxide alone. It was discovered that the decomposition ability was high. The mixed metal oxide of the present invention is efficiently decomposed by irradiation with ultraviolet rays. The principle of action of the mixed metal oxides mentioned above is currently being studied in detail, but electrons in the valence band of each of the above oxides and titanium oxide semiconductors absorb ultraviolet light and are excited to the conduction band, and the electrons generated there. Holes in the valence band react with hydroxyl groups (OH groups) on the surface of the catalyst, and electrons excited in the conduction band react with oxygen (O) to form highly active OH radicals, O radicals,
It is assumed that O2 - is generated and this oxidatively decomposes the oxidizable compound. Further, it is presumed that the electrons and holes generated in titanium oxide interact with the electrons and holes generated in each of the above oxides, resulting in a synergistic effect. Furthermore, when a conductive inorganic substance such as platinum, palladium, rhodium, ruthenium oxide, or silver is supported on this mixed metal oxide, the oxidative decomposition effect becomes even stronger. Among them, the effect of platinum is remarkable. The deodorizing method of the present invention is not only excellent in decomposing aldehydes, but also other malodorous substances such as ammonia, nitrogen compounds of amines, hydrogen sulfide, sulfur compounds of mercaptans, ketones, alcohols, fatty acids, and aromatic compounds. It can be decomposed by oxidation and made odorless. Examples Next, examples of the present invention will be described. The titanium oxide used in the present invention includes:
The anatase type has high activity, but the rutile type may also be used. Also, among the oxides, iron titanate
Although FeTiO 3 has high activity, Fe 2 TiO 5 may also be used. Platinum is effective as the conductive inorganic substance, but noble metals such as palladium, rhodium, and silver, ruthenium oxide, and the like may also be used. Further, the ultraviolet rays only need to have a wavelength of 400 nm or less, and may be either far ultraviolet rays or near ultraviolet rays. These ultraviolet rays can be generated by using a high-pressure mercury lamp, an ultra-high-pressure mercury lamp, a low-pressure mercury lamp, a xenon lamp, etc. alone or in combination. Further, the deodorizing method may be performed by introducing the gas to be treated into a specific reactor and performing batch treatment, or by continuous treatment. The mixed metal oxide used in the present invention is used by coating it on the surface of the light source, or by coating or impregnating a support provided around the light source. Next, specific examples will be described. Suspend the metal oxide powder of the weight shown in Table 1 in methanol, and spread this suspension to a thickness of 0.5 mm * width 120 mm * length.
It was applied to a 240 mm alumina-silica ceramic paper and dried to form a photocatalyst. Platinum was supported by impregnating a ceramic paper coated with the metal oxide with an ethanol solution of chloroplatinic acid and heat-treating the paper to support the platinum as fine particles. Then, as shown in FIG. 1, the catalyst 1 having the above structure was placed on a stainless steel stand 2 and placed in a reaction vessel 3 made of aluminum with an internal volume of 36 mm, at a distance of 100 mm from a light source 4. As light source 4, a 10 watt germicidal lamp (ultraviolet ray output approximately 1.8 watts, dominant wavelength 254 nm) was used. A saturated gas of acetaldehyde was injected into the reaction vessel 3, stirred with a fan 5 to make the concentration uniform, and the initial concentration was measured. Next, a germicidal lamp was turned on, and changes in the astaldehyde concentration over time were examined using gas chromatography. The results were shown when the mixed metal oxide catalyst was not irradiated with ultraviolet rays, when only ultraviolet rays were irradiated without using a catalyst, and when only anatase titanium oxide or only iron titanate FeTiO 3 was applied to ceramic paper using the above method. Figure 2 shows a comparison of the case where the catalyst was irradiated with ultraviolet rays. Further, the respective conditions are shown in Table 1.

【表】 第2図に示すように、酸化チタンとチタン酸鉄
の混合金属酸化物の存在下でアセトアルデヒドと
酸素を含む気体に紫外線を照射すると、アセトア
ルデヒドは極めて効果的に分解され無臭化する。
さらに白金を担持した混合金属酸化物を用いると
さらに効果的に分解が進む。また、酸化チタンと
チタン酸鉄の混合金属酸化物は酸化チタン単独よ
りも光触媒効果が大きい。このように本発明によ
れば、従来活性炭で吸着することが難しかつたア
ルデヒドを、極低濃度まで分解し無臭化すること
ができる。 またこの実施例によればアルデヒドの分解に限
らず、他の悪臭物質のアンモニア、アミン類等の
窒素化合物、硫化水素、メルカプタン類等の硫黄
化合物、ケトン類、アルコール類、脂肪酸及び芳
香族化合物も酸化して無臭化できる。更には一酸
化炭素も二酸化炭素に酸化し無害化出来る。 なお、実施例の方法に他の吸着剤や化学的方法
を組み合わせて用いることによつてすぐれた脱臭
能力を得ることができる。 次に、上記実施例におけるチタン酸鉄に代え
て、順次、酸化鉄、酸化ビスマスおよび酸化モリ
ブデンを選択して、上記実施例と同様に実験した
結果を示す。 酸化鉄の場合の条件は第2表のとおりであり、
結果を第3図に示す。酸化鉄としては活性の高い
α−Fe2O3を用いたが、γ−Fe2O3、Fe3O4
FeOを使用してもよい。
[Table] As shown in Figure 2, when a gas containing acetaldehyde and oxygen is irradiated with ultraviolet rays in the presence of a mixed metal oxide of titanium oxide and iron titanate, acetaldehyde is extremely effectively decomposed and rendered odorless.
Furthermore, if a mixed metal oxide supporting platinum is used, the decomposition proceeds even more effectively. Further, a mixed metal oxide of titanium oxide and iron titanate has a greater photocatalytic effect than titanium oxide alone. As described above, according to the present invention, aldehydes, which have conventionally been difficult to adsorb with activated carbon, can be decomposed to extremely low concentrations and rendered odorless. Furthermore, according to this embodiment, the decomposition is not limited to aldehydes, but also other malodorous substances such as ammonia, nitrogen compounds such as amines, hydrogen sulfide, sulfur compounds such as mercaptans, ketones, alcohols, fatty acids, and aromatic compounds. Can be oxidized and made odorless. Furthermore, carbon monoxide can also be oxidized to carbon dioxide and rendered harmless. In addition, excellent deodorizing ability can be obtained by using the method of the example in combination with other adsorbents or chemical methods. Next, the results of an experiment conducted in the same manner as in the above example, in which iron oxide, bismuth oxide, and molybdenum oxide were sequentially selected in place of iron titanate in the above example, will be shown. The conditions for iron oxide are as shown in Table 2.
The results are shown in Figure 3. α-Fe 2 O 3 with high activity was used as iron oxide, but γ-Fe 2 O 3 , Fe 3 O 4 ,
FeO may also be used.

【表】 酸化ビスマスの場合の上面は第3表のとおりで
あり、結果を第4図に示す。酸化ビスマスとして
は活性の高いα−Bi2O3を用いたが、β型、γ
型、δ型を使用してもよい。
[Table] The upper surface of bismuth oxide is shown in Table 3, and the results are shown in FIG. α-Bi 2 O 3 with high activity was used as bismuth oxide, but β-type and γ-type
type, δ type may also be used.

【表】【table】

【表】 酸化モリブデンの場合は第4表のとおりであ
り、結果を第5図に示す。酸化モリブデンとして
はMoO3を使用したが、MoO2か両者の中間状態
の酸化物でもよい。
[Table] Table 4 shows the results for molybdenum oxide, and the results are shown in Figure 5. Although MoO 3 was used as the molybdenum oxide, it may be MoO 2 or an oxide in an intermediate state between the two.

【表】 発明の効果 上記した各実施例からあきらかなとおり、本発
明の光触媒による脱臭方法は、活性炭で吸着が難
しかつたアルデヒドを極めて低い濃度まで分解し
無臭化することができるとともに、他の悪臭物質
のアンモニア、アミン類等の窒素化合物、硫化水
素、メルカプタン類等の硫黄化合物、ケトン類、
アルコール類、脂肪酸及び芳香族化合物も酸化し
て無臭化できる。さらに一酸化炭素も二酸化炭素
に酸化して無害化できるというすぐれた効果を有
している。
[Table] Effects of the Invention As is clear from the examples described above, the deodorizing method using a photocatalyst of the present invention can decompose aldehydes, which were difficult to adsorb with activated carbon, to an extremely low concentration and make them odorless. Malodorous substances such as ammonia, nitrogen compounds such as amines, hydrogen sulfide, sulfur compounds such as mercaptans, ketones,
Alcohols, fatty acids and aromatic compounds can also be oxidized to make them odorless. Furthermore, it has the excellent effect of oxidizing carbon monoxide to carbon dioxide and rendering it harmless.

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

第1図は本発明の光触媒による分解性能を測定
する装置の断面図、第2図〜第5図は本発明の各
実施例におけるアセトアルデヒドの分解曲線図で
ある。 1……触媒、4……光源。
FIG. 1 is a sectional view of an apparatus for measuring the decomposition performance of the photocatalyst of the present invention, and FIGS. 2 to 5 are decomposition curve diagrams of acetaldehyde in each example of the present invention. 1...Catalyst, 4...Light source.

Claims (1)

【特許請求の範囲】[Claims] 1 チタン酸鉄、酸化鉄、酸化ビスマスおよび酸
化モリブデンからなる群から選択された1つの酸
化物と酸化チタンとの混合酸化物と、被酸化性化
合物および酸素を含む気体との共存下で、前記混
合金属酸化物に紫外線を照射する光触媒による脱
臭方法。
1. In the coexistence of a mixed oxide of titanium oxide and one oxide selected from the group consisting of iron titanate, iron oxide, bismuth oxide, and molybdenum oxide, and an oxidizable compound and a gas containing oxygen, A deodorizing method using a photocatalyst that irradiates mixed metal oxides with ultraviolet light.
JP63058733A 1988-03-11 1988-03-11 Deodorizing method by photocatalyst Granted JPH01232966A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP63058733A JPH01232966A (en) 1988-03-11 1988-03-11 Deodorizing method by photocatalyst

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP63058733A JPH01232966A (en) 1988-03-11 1988-03-11 Deodorizing method by photocatalyst

Publications (2)

Publication Number Publication Date
JPH01232966A JPH01232966A (en) 1989-09-18
JPH0478326B2 true JPH0478326B2 (en) 1992-12-10

Family

ID=13092710

Family Applications (1)

Application Number Title Priority Date Filing Date
JP63058733A Granted JPH01232966A (en) 1988-03-11 1988-03-11 Deodorizing method by photocatalyst

Country Status (1)

Country Link
JP (1) JPH01232966A (en)

Families Citing this family (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
AU676299B2 (en) 1993-06-28 1997-03-06 Akira Fujishima Photocatalyst composite and process for producing the same
TW431907B (en) * 1994-02-07 2001-05-01 Ishihara Sangyo Kaisha Method of removing harmful materials
AU702827B2 (en) * 1994-02-07 1999-03-04 Ishihara Sangyo Kaisha Ltd. Titanium oxide photocatalyst and method of producing the same
TW365547B (en) * 1994-12-26 1999-08-01 Takeda Chemical Industries Ltd Catalytic compositions and a deodorizing method using the same
DE69930399T2 (en) * 1998-09-30 2006-12-07 Nippon Sheet Glass Co., Ltd. PHOTOCATORATORY ITEMS FOR PREVENTING CONSTROGENSES AND DEPOSITS, METHOD FOR PRODUCING THE ARTICLE
EP1175938A1 (en) 2000-07-29 2002-01-30 The Hydrogen Solar Production Company Limited Photocatalytic film of iron oxide, electrode with such a photocatalytic film, method of producing such films, photoelectrochemical cell with the electrode and photoelectrochemical system with the cell, for the cleavage of water into hydrogen and oxygen
UA82806C2 (en) * 2007-06-21 2008-05-12 Вадим Вадимович Милоцкий METHOD OF DISPOSAL OF MIXED ORGANIC HOUSEHOLD AND INDUSTRIAL WASTE
KR100913784B1 (en) * 2008-01-17 2009-08-26 인하대학교 산학협력단 Photocatalyst having titanium oxide-titanium iron junction structure and its manufacturing method

Also Published As

Publication number Publication date
JPH01232966A (en) 1989-09-18

Similar Documents

Publication Publication Date Title
JP5775248B2 (en) Photocatalyst material, organic matter decomposition method, interior member, air cleaning device, oxidizer manufacturing device
KR101334967B1 (en) Photocatalytic material, method of decomposing organic substance, interior member, air cleaning device, and device for producing oxidizing agent
JPH0512967B2 (en)
JPS63230171A (en) Deodorizing apparatus
JPH03106420A (en) Deodorizing method for photo-catalyst
JPH0478326B2 (en)
JP2000317269A (en) Deodorizing device
KR20150011062A (en) Deodorizing apparatus using ceramic membrane and plasma
JPH07114925B2 (en) Photocatalytic deodorization method
JPH01288322A (en) Deodorization by photocatalyst
JPH0515488B2 (en)
JP2000218161A (en) Photocatalyst
CN108240687B (en) Deodorizing method and deodorizing device
JPH067906B2 (en) Photocatalytic deodorization method
JPH02169040A (en) How to regenerate photocatalyst
CN108295640A (en) A kind of odor treatment method and equipment
JPH0229365B2 (en)
JPH0290924A (en) Deodorization method using photocatalyst
JPH02169039A (en) How to regenerate photocatalyst
Lin Applying Ag–TiO2/functional filter for abating odor exhausted from semiconductor and opti-electronic industries
JPH0442056B2 (en)
JPH0532321B2 (en)
JPH01159031A (en) Deodorizing method and device using photocatalyst
JP2000316961A (en) Deodorizing apparatus
JP2004024472A (en) Deodorizer and deodorizing method

Legal Events

Date Code Title Description
LAPS Cancellation because of no payment of annual fees