JP3460290B2 - Honeycomb deodorizer - Google Patents
Honeycomb deodorizerInfo
- Publication number
- JP3460290B2 JP3460290B2 JP00682794A JP682794A JP3460290B2 JP 3460290 B2 JP3460290 B2 JP 3460290B2 JP 00682794 A JP00682794 A JP 00682794A JP 682794 A JP682794 A JP 682794A JP 3460290 B2 JP3460290 B2 JP 3460290B2
- Authority
- JP
- Japan
- Prior art keywords
- deodorizing
- honeycomb
- base material
- activated carbon
- ozone
- 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
Links
Landscapes
- Catalysts (AREA)
- Disinfection, Sterilisation Or Deodorisation Of Air (AREA)
- Treating Waste Gases (AREA)
- Separation Of Gases By Adsorption (AREA)
- Filtering Of Dispersed Particles In Gases (AREA)
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
Description
【0001】[0001]
【産業上の利用分野】本発明は、空気の浄化、特に家庭
内、車内での悪臭を除去するために用いられるハニカム
脱臭材に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a honeycomb deodorizing material used for purifying air, particularly for removing a bad odor at home or in a vehicle.
【0002】[0002]
【従来の技術】従来より、固体材料による空気の浄化、
悪臭の除去方法として、物理的脱臭……無機系脱臭材
(ゼオライト、シリカ、アルミナ)或いは活性炭等、多
孔性材料の微細構造に悪臭分子が可逆的に物理吸着する
方法、化学的脱臭……固体表面に悪臭分子との酸−塩
基反応、付加反応、重合反応、イオン結合等の化学反応
を起こさせる官能基を導入することで、空気中の悪臭分
子と不可逆に反応させて除去する方法、オゾン脱臭触
媒……触媒表面上の活性点に悪臭分子を吸着させた後、
オゾンを表面上に通過させ、活性点でオゾンを分解さ
せ、オゾンの酸化性を利用して悪臭分子を酸化分解させ
る方法、燃焼酸化触媒……悪臭分子を触媒表面に吸着
させると同時に、触媒を200℃〜400℃に加熱し、
空気中の酸素を利用して酸化分解を伴った触媒反応を起
こさせる方法、などの各種方法が提案されている。これ
ら固体材料の形状としては、従来は粉体、粒状の脱臭材
を移動床、固定床の形態で使用されている。また近年で
は脱臭材をハニカム状に成形したものを使用して空気の
圧力損失を低減させる工夫がなされている。このハニカ
ム状成形体は、従来の粉体、粒状の脱臭材を移動床、固
定床の形態で使用する場合と比較して圧力損失が少な
く、しかも組立て、取り替え時のハンドリングに優れて
いるという利点がある(例えば特開平2−126856
号公報参照)。2. Description of the Related Art Conventionally, purification of air by solid materials,
As a method for removing malodor, physical deodorization: a method of reversibly physically adsorbing malodorous molecules to the fine structure of a porous material such as an inorganic deodorant (zeolite, silica, alumina) or activated carbon, chemical deodorization: solid Acid-base reaction with malodorous molecule, addition reaction, polymerization reaction, by introducing a functional group that causes a chemical reaction such as ionic bond on the surface, a method of irreversibly reacting with malodorous molecule in the air to remove it, ozone Deodorizing catalyst ... After adsorbing malodorous molecules on the active sites on the catalyst surface,
A method of passing ozone over the surface, decomposing ozone at active points, and oxidatively decomposing malodorous molecules by utilizing the oxidizing property of ozone, combustion oxidation catalyst .... Heat to 200-400 ° C,
Various methods such as a method of utilizing oxygen in the air to cause a catalytic reaction accompanied by oxidative decomposition have been proposed. As the shape of these solid materials, powder and granular deodorizing materials have been conventionally used in the form of moving beds and fixed beds. Further, in recent years, a device for reducing the pressure loss of air has been devised by using a deodorizing material formed in a honeycomb shape. This honeycomb-shaped compact has less pressure loss than the conventional powder or granular deodorant material used in the form of moving bed or fixed bed, and is excellent in handling during assembly and replacement. (For example, Japanese Patent Laid-Open No. 2-126856)
(See Japanese Patent Publication).
【0003】[0003]
【発明が解決しようとする課題】ところが、従来のハニ
カム状成形体は、圧力損失が少なく、ハンドリングに優
れているという利点はあるが、その反面、空気とハニカ
ム状成形体表面との接触効率は従来の粉体、粒状の脱臭
材の場合と比べて低く、悪臭の除去効率が低下するとい
う問題がある。しかも通常のハニカム状成形体の処理能
力はある空間速度SV[=処理風量(L/hr)/ハニ
カム容量(L)]を越えると、極端に低下するため、悪
臭の発生する局所空間の脱臭にも不都合な点があった。
そのうえ、従来のハニカム状成形体は、組成面での制約
から脱臭範囲が狭く、例えばアルカリ性の悪臭には脱臭
効果があっても、酸性の悪臭には脱臭効果が発現しない
という問題もあった。However, the conventional honeycomb molded body has the advantages of low pressure loss and excellent handling, but on the other hand, the contact efficiency between air and the surface of the honeycomb molded body is low. It is lower than conventional powder and granular deodorizing materials, and there is a problem that the efficiency of removing malodor decreases. Moreover, the processing capacity of the ordinary honeycomb-shaped molded body is extremely reduced when it exceeds a certain space velocity SV [= processing air volume (L / hr) / honeycomb capacity (L)], so that deodorization of a local space where a bad odor occurs But there was a disadvantage.
In addition, the conventional honeycomb-shaped molded body has a narrow deodorizing range due to restrictions in terms of composition. For example, even if the alkaline malodor has a deodorizing effect, the acidic malodor does not exhibit the deodorizing effect.
【0004】本発明は、上記従来の課題に鑑みてなされ
たもので、その目的とするところは、空気との接触効率
が良く、しかも各種の悪臭に対して広く脱臭範囲をカバ
ーして脱臭性能をより向上させることができ、複合臭気
に対する性能向上と悪臭の再放出防止を図ることがで
き、さらに悪臭の発生する局所空間の脱臭にも最適に使
用できる高性能なハニカム脱臭材を提供するにある。The present invention has been made in view of the above-mentioned conventional problems, and its object is to achieve good deodorizing performance by providing good contact efficiency with air and covering a wide deodorizing range against various malodors. In order to provide a high-performance honeycomb deodorizing material, which can further improve the performance, improve the performance against complex odors and prevent re-emission of malodors, and can also be optimally used for deodorizing local spaces where malodors occur. is there.
【0005】[0005]
【課題を解決するための手段】上記従来の課題を解決す
るために、本発明は、セル空間2aを有するハニカム脱
臭基材2と、ハニカム脱臭基材2のセル空間2a内に充
填されてハニカム脱臭基材2とは異なる材質から成る脱
臭材3とを備え、ハニカム脱臭基材2の構成材料が無機
系脱臭材からなり、脱臭材3の構成材料が、有機系脱臭
材、活性炭材料、オゾン脱臭触媒、燃焼酸化触媒から選
ばれた一種或いは二種以上の組み合わせから成ることを
特徴とする。In order to solve the above conventional problems, the present invention provides a honeycomb deodorizing base material 2 having a cell space 2a and a honeycomb deodorizing base material 2 which is filled in the cell space 2a. A deodorizing material 3 made of a material different from the deodorizing base material 2 is provided, and the constituent material of the honeycomb deodorizing base material 2 is inorganic.
Made from the system deodorizer, configuration material of the deodorizing material 3, organic-based deodorizer, characterized activated carbon material, an ozone deodorizing catalyst, in that it consists of one or two or more kinds selected from burning oxidation catalyst.
【0006】[0006]
【0007】上記脱臭材3の形状は、粉体、粒状、繊維
状の各形状から選ばれた一種或いは二種以上の組み合わ
せから成るものが好ましい。The deodorizing material 3 preferably has a shape of one kind or a combination of two or more kinds selected from powdery, granular and fibrous shapes.
【0008】[0008]
【作用】本発明によれば、ハニカム脱臭材1は、ハニカ
ム脱臭基材2のセル空間2a内に、ハニカム脱臭基材2
の材質と異なる材質の脱臭材3を充填して構成されると
共に、ハニカム脱臭基材2の構成材料が無機系脱臭材か
らなり、脱臭材3の構成材料が、有機系脱臭材、活性炭
材料、オゾン脱臭触媒、燃焼酸化触媒から選ばれた一種
或いは二種以上の組み合わせより成る。According to the present invention, the honeycomb deodorizing material 1 is placed in the cell space 2a of the honeycomb deodorizing base material 2 in the honeycomb deodorizing base material 2.
The deodorizing material 3 is made of a material different from the above material, and whether the constituent material of the honeycomb deodorizing base material 2 is an inorganic deodorizing material.
Rannahli, configuration material of the deodorizing material 3, organic-based deodorizer, activated carbon materials, the ozone deodorizing catalyst, consisting of one or a combination of two or more selected from burning oxidation catalyst.
【0009】ここで、無機系脱臭材としては、コーディ
ェライト組成に酸化亜鉛を混入して燃焼した後に塩化亜
鉛を添着した素材や、アルミナ−シリカをベースにした
素材、ゼオライト等の多孔性の無機系の脱臭材が挙げら
れる。また有機系脱臭材としては、各種植物抽出物並び
に消臭に有効な有機化合物等を固体物質に含浸添着した
有機系の脱臭材が挙げられる。さらに活性炭材料として
は、繊維状活性炭を含む活性炭が挙げられる。Here, as the inorganic deodorant, a material in which zinc oxide is mixed in cordierite composition and burned and then zinc chloride is added, a material based on alumina-silica, or a porous inorganic material such as zeolite is used. Examples include deodorant materials of the system. Examples of the organic deodorant include various plant extracts and organic deodorants obtained by impregnating and adhering a solid substance with an organic compound effective for deodorization. Further, examples of the activated carbon material include activated carbon including fibrous activated carbon.
【0010】このように、低圧損型のハニカム脱臭基材
2のセル空間2a内にハニカム脱臭基材2とは異なる材
質から成る脱臭材3を充填することにより、空気とハニ
カム脱臭基材2、脱臭材3との接触効率が夫々良くな
り、脱臭性能を向上させることができる。しかも、空間
速度が一定値を越えた場合であっても接触効率が極端に
低下しなくなり、悪臭の発生する局所空間の脱臭にも好
都合に使用できるようになる。さらに、ハニカム脱臭基
材2と脱臭材3とは異なる材質から構成されるので、各
種の悪臭に対して広く脱臭範囲をカバーでき、脱臭性能
をより向上させることができる結果、複合臭気に対する
性能向上と悪臭の再放出防止を図ることができる。In this way, by filling the cell space 2a of the low pressure loss type honeycomb deodorizing base material 2 with the deodorizing material 3 made of a material different from that of the honeycomb deodorizing base material 2, air and the honeycomb deodorizing base material 2, The contact efficiency with the deodorizing material 3 is improved, and the deodorizing performance can be improved. Moreover, even if the space velocity exceeds a certain value, the contact efficiency does not extremely decrease, and it can be conveniently used for deodorizing the local space where a bad odor is generated. Furthermore, since the honeycomb deodorizing base material 2 and the deodorizing material 3 are made of different materials, a wide deodorizing range can be covered against various kinds of bad odors, and the deodorizing performance can be further improved. It is possible to prevent the re-emission of a bad smell.
【0011】また、オゾン脱臭触媒としては、MnO2
、TiO2 の他に、Ag,Au,Pt,Pd,C等の
酸化金属類、貴金属類、炭素等挙げられ、触媒活性を有
するオゾン脱臭触媒であればどれでもよい。また燃焼酸
化触媒は、Pt,Pd,Ag,Au等の貴金属類が挙げ
られ、触媒活性を有する燃焼酸化触媒であればよく、特
に酸化活性温度が低温であるのが望ましい。なお、無機
系脱臭材、有機系脱臭材、活性炭材料は前述したものと
同じである。このようにオゾン脱臭触媒との組み合わ
せ、或いは燃焼酸化触媒との組み合わせによれば、より
高性能なハニカム脱臭材を提供できるようになる。[0011] In addition, as the ozone deodorizing catalyst, MnO2
, TiO2, metal oxides such as Ag, Au, Pt, Pd, and C, noble metals, carbon, and the like, and any ozone deodorizing catalyst having catalytic activity may be used. Examples of the combustion oxidation catalyst include noble metals such as Pt, Pd, Ag, Au and the like, and any combustion oxidation catalyst having catalytic activity may be used, and it is particularly desirable that the oxidation activation temperature is low. The inorganic deodorant, the organic deodorant, and the activated carbon material are the same as those described above. As described above, by combining with the ozone deodorizing catalyst or with the combustion oxidizing catalyst, it becomes possible to provide a honeycomb deodorizing material with higher performance.
【0012】以下、ハニカム脱臭基材2と脱臭材3の各
構成材料の組み合わせ例を表1に示す。
(以下余
白)Table 1 shows examples of combinations of the constituent materials of the honeycomb deodorizing base material 2 and the deodorizing material 3.
(Below margin)
【0013】[0013]
【表1】 [Table 1]
【0014】上記表1中、ハニカム脱臭基材2と脱臭材
3とは異質の材質から構成されるものであり、例えばハ
ニカム脱臭基材2が無機系脱臭材の場合は、脱臭材は無
機系脱臭材以外の他の材質(例えば有機系脱臭材、活性
炭材料、オゾン脱臭触媒、燃焼酸化触媒)が選ばれる。
このように異種の材料の組み合わせにより、各種悪臭に
対して広い脱臭範囲をカバーでき、各悪臭に対する脱臭
効果が向上する。In Table 1, the honeycomb deodorizing base material 2 and the deodorizing material 3 are made of different materials. For example, when the honeycomb deodorizing base material 2 is an inorganic deodorizing material, the deodorizing material is an inorganic deodorizing material. Materials other than the deodorizing material (for example, organic deodorizing material, activated carbon material, ozone deodorizing catalyst, combustion oxidation catalyst) are selected.
In this way, by combining different kinds of materials, a wide deodorizing range can be covered for various malodors, and the deodorizing effect for each malodor is improved.
【0015】また、上記脱臭材3の形状としては、粉
体、粒状、繊維状の各形状から選ばれた一種或いは二種
以上の組み合わせが好ましい。この粉体、粒状、繊維状
の各形状は表面積が大きく、これら形状の脱臭材3を低
圧損型のハニカム脱臭基材2のセル空間2a内に充填す
ることにより、空気との接触効率をより向上させること
ができる。The shape of the deodorizing material 3 is preferably one or a combination of two or more selected from powdery, granular and fibrous shapes. Each of the powder, granular, and fibrous shapes has a large surface area, and by filling the cell space 2a of the low-pressure loss type honeycomb deodorizing base material 2 with the deodorizing material 3 having these shapes, the contact efficiency with air can be further improved. Can be improved.
【0016】[0016]
【実施例】以下、本発明を実施例により詳細に説明す
る。上記ハニカム脱臭基材2と脱臭材3から成るハニカ
ム脱臭材1の構造を図1に示す。同図において、ハニカ
ム脱臭基材2の多数のセル空間2a内にハニカム脱臭材
1と異種の脱臭材3が充填されている。このとき、脱臭
材3の流出防止のために、セル空間2aの出入口に不織
布4のような流出防止用の濾過材が設けられているのが
望ましい。さらに脱臭性能をより向上させるためには図
2に示すように、1つのハニカム脱臭基材2に対して複
数種の脱臭材3A,3B,3C,3Dを充填するように
してもよく、この場合、より広い範囲で脱臭性能を発現
させることができる。
(実施例1,2)コーディェライト組成の無機材料にZ
nOを20%含有した基材を60セル/inch2 に押
出し成形し、750℃で焼成し、90mm×90mm×
30mmのハニカム状成形体を得た。さらにこのハニカ
ム状成形体を25%塩化亜鉛水溶液に含浸後、70℃で
2時間乾燥し、無機系のハニカム脱臭基材を作製した。
次いで、この無機系のハニカム脱臭基材のセル出口側の
端面に流出防止用の濾過材として不織布を張り付け、そ
の後、反対方向のセル入口から粒状活性炭20g(平均
粒径0.5mm、比表面積1000m2 /g)を各セル
空間内に均一に充填し、その後、セル出口に不織布を張
り付けたものを実施例1とした。EXAMPLES The present invention will be described in detail below with reference to examples. FIG. 1 shows the structure of the honeycomb deodorizing material 1 including the honeycomb deodorizing base material 2 and the deodorizing material 3. In the figure, a large number of cell spaces 2a of the honeycomb deodorizing base material 2 are filled with the deodorizing material 3 different from the honeycomb deodorizing material 1. At this time, in order to prevent the deodorizing material 3 from flowing out, it is desirable that a filtering material such as a non-woven fabric 4 is provided at the entrance and exit of the cell space 2a. In order to further improve the deodorizing performance, as shown in FIG. 2, one honeycomb deodorizing base material 2 may be filled with a plurality of types of deodorizing materials 3A, 3B, 3C, 3D. The deodorizing performance can be expressed in a wider range. (Examples 1 and 2) Z was added to an inorganic material having a cordierite composition.
A base material containing 20% of nO was extruded into 60 cells / inch 2 and fired at 750 ° C., 90 mm × 90 mm ×
A 30 mm honeycomb molded body was obtained. Further, this honeycomb-shaped molded body was impregnated with a 25% zinc chloride aqueous solution and then dried at 70 ° C. for 2 hours to prepare an inorganic honeycomb deodorizing base material.
Next, a non-woven fabric is attached to the end face of the inorganic honeycomb deodorizing base material on the cell outlet side as a filter material for preventing outflow, and thereafter, 20 g of granular activated carbon (average particle size 0.5 mm, specific surface area 1000 m) from the cell inlet in the opposite direction. 2 / g) was uniformly filled in each cell space, and then a non-woven fabric was attached to the cell outlet to form Example 1.
【0017】一方、実施例1で作製されたハニカム脱臭
基材のセル入口から繊維状活性炭10g(ピッチ径15
mm長、比表面積1500m2 /g)を各セル空間内に
均一に充填したものを実施例2とした。実施例1、実施
例2で得られたハニカム脱臭材の脱臭率の測定を図3に
示す脱臭率測定装置4を用いて行なった。悪臭発生源5
にタバコ(マイルドセブン)の副流煙を発生させ、サン
プル収納カラム6に実施例1、実施例2のサンプル7を
設置し、エアポンプ8で吸引してフロー流路系を構成す
る。このサンプル7の前後では、臭いセンサを用いて悪
臭分析in、悪臭分析outでサンプル7の脱臭率を測
定した。尚、脱臭率は次式で求めた。On the other hand, 10 g of fibrous activated carbon (pitch diameter: 15) was introduced from the cell inlet of the honeycomb deodorizing base material prepared in Example 1.
Example 2 was one in which each cell space was uniformly filled with a length of mm and a specific surface area of 1500 m 2 / g. The deodorizing rate of the honeycomb deodorizing materials obtained in Examples 1 and 2 was measured using a deodorizing rate measuring device 4 shown in FIG. Offensive odor source 5
A sidestream smoke of cigarette (mild seven) is generated in the sample, the sample 7 of each of the first and second examples is installed in the sample storage column 6, and suction is performed by the air pump 8 to form a flow channel system. Before and after the sample 7, the odor sensor was used to measure the deodorization rate of the sample 7 by the malodor analysis in and the malodor analysis out. The deodorization rate was calculated by the following formula.
【0018】脱臭率=[(悪臭分析in値−悪臭分析out
値)×100 /悪臭分析in値]
さらに脱臭性能の比較として、ハニカム脱臭基材と粒状
活性炭、繊維状活性炭との直列での組み合わせを比較例
1,2とした。以下、実施例1,2、比較例1,2の測
定結果を表2に示す。尚、測定条件はSV=5000
0、常温下とした。Deodorization rate = [(Odor analysis in value-Odor analysis out
(Value) × 100 / insoluble odor analysis in value] Further, as a comparison of deodorizing performance, Comparative Examples 1 and 2 are combinations of a honeycomb deodorizing base material, granular activated carbon and fibrous activated carbon in series. Table 2 below shows the measurement results of Examples 1 and 2 and Comparative Examples 1 and 2. The measurement condition is SV = 5000
0, at room temperature.
【0019】[0019]
【表2】 [Table 2]
【0020】(実施例3,4)粉末活性炭を原料にフェ
ノール樹脂、粘土等を加え、60セル/inch2 に押
出し成形し、その後、850℃で水蒸気賦活し、950
m2 /gの活性炭ハニカムを調整した(90mm×90
mm×25mm)。活性炭ハニカムの端面に不織布を張
り付けた後、アンモニア脱臭用の粒状活性炭10g(平
均粒径0.3mm)と、アセトアルデヒド脱臭用の粒状
活性炭10g(平均粒径0.3mm)とを混合したもの
を各セル空間内に均一に充填したものを実施例3とし
た。(Examples 3 and 4) Powdered activated carbon was used as a raw material, to which phenol resin, clay and the like were added, and extrusion molding was performed at 60 cells / inch 2 , and then steam activation at 850 ° C. was performed to obtain 950.
An activated carbon honeycomb of m 2 / g was prepared (90 mm × 90
mm × 25 mm). A non-woven fabric was attached to the end face of the activated carbon honeycomb, and 10 g of granular activated carbon for deodorizing ammonia (average particle size 0.3 mm) and 10 g of granular activated carbon for deodorizing acetaldehyde (average particle size 0.3 mm) were mixed together. Example 3 was one in which the cell space was uniformly filled.
【0021】一方、実施例3で作製された活性炭ハニカ
ムに繊維状活性炭5gを均一に充填した後、フローライ
ト(0.5mm径)に松の熱水抽出物、クエン酸、グリ
セリン等を水溶液で含浸後、風乾させた脱臭材10gを
各セル空間内に均一に充填したものを実施例4とした。
実施例3、実施例4で得られたハニカム脱臭材の脱臭率
の測定を図3に示す脱臭率測定装置を用いて行なった。
悪臭発生源5に大便のヘッドスペースガスとタバコ(マ
イルドセブン)の副流煙を混合したものを使用した。ま
た評価としては図3の悪臭分析outの部分でテドラー
パックに採取し、パネラー10名による六段階臭気強度
表示法による判定を行なった。このときの比較として
は、各実施例3,4の材料を直列に並べた形で評価し
た。以下、実施例3,4、比較例3,4の測定結果を表
3に示す。On the other hand, the activated carbon honeycomb prepared in Example 3 was uniformly filled with 5 g of fibrous activated carbon, and then hot light extract of pine, citric acid, glycerin, etc. was added to the fluorite (0.5 mm diameter) as an aqueous solution. After impregnation, 10 g of the air-dried deodorizing material was uniformly filled in each cell space, which was set as Example 4.
The deodorizing rates of the honeycomb deodorizing materials obtained in Examples 3 and 4 were measured using the deodorizing rate measuring device shown in FIG.
A mixture of stool headspace gas and sidestream smoke of cigarettes (mild seven) was used as the malodor source 5. As the evaluation, the odor analysis out portion in FIG. 3 was sampled in a Tedlar pack, and judged by a six-stage odor intensity display method by 10 panelists. For comparison at this time, the materials of Examples 3 and 4 were evaluated in the form of being arranged in series. The measurement results of Examples 3 and 4 and Comparative Examples 3 and 4 are shown in Table 3 below.
【0022】[0022]
【表3】 [Table 3]
【0023】(実施例5)MnO2 を触媒活性とするオ
ゾン脱臭触媒ハニカム(200セル/inch2、50
mm×48mm×48mm)の各セル空間に繊維状活性
炭12gを充填したものを実施例5とした。このとき、
悪臭発生源5としては、通常の家庭から排出される生ゴ
ミを35℃、70%RHで3日間放置したヘッドスペー
スガスを用いた。このときの原臭の臭気強度は六段階臭
気強度表示法で5(パネラー10名の平均値)であっ
た。尚、測定実験は、図3に示す脱臭率測定装置のサン
プル7上流に沿面放電を用いたオゾン発生器13からオ
ゾンを発生させた。(Example 5) Ozone deodorizing catalyst honeycomb (200 cells / inch 2 , 50) having MnO 2 as catalytic activity
(mm × 48 mm × 48 mm) filled with 12 g of fibrous activated carbon in each cell space was set as Example 5. At this time,
As the malodor generating source 5, headspace gas was used in which raw garbage discharged from an ordinary household was left at 35 ° C. and 70% RH for 3 days. The odor intensity of the original odor at this time was 5 (average value of 10 panelists) by the 6-step odor intensity display method. In the measurement experiment, ozone was generated from the ozone generator 13 using creeping discharge upstream of the sample 7 of the deodorizing rate measuring device shown in FIG.
【0024】また、サンプルのSV=28000時で1
ppmのオゾンが発生するように調整した。この条件で
SV=125000時での悪臭分析outにおける臭い
袋への臭気採取による臭気強度評価をパネラー10名で
行なったところ、以下の表4に示す測定結果が得られ
た。また臭気採取はオゾン分解処理後、オゾン発生を停
止した状態でサンプリングし、比較例5として実施例5
の材料を直列に並べた形で行なった。
(実施例6,7)実施例3で用いた活性炭ハニカム60
セル/inch2 の各セル空間に、Ptを触媒活性成分
とする粒状の酸化触媒10g(0.7mm粒径)を均一
に充填したものを実施例6とした。そして、評価の際に
は、図3の脱臭率測定装置のサンプル7の部分をヒータ
11によって約120℃になるように加熱した。Further, the sample SV = 28,000 hours is 1
It was adjusted to generate ppm ozone. Under this condition, the odor intensity was evaluated by collecting the odor in the odor bag in the odor analysis out at SV = 125,000 hours by 10 panelists, and the measurement results shown in Table 4 below were obtained. In addition, for the odor collection, after the ozone decomposition treatment, sampling was performed in a state where ozone generation was stopped, and Example 5 was used as Comparative Example 5.
The above materials were arranged in series. (Examples 6 and 7) Activated carbon honeycomb 60 used in Example 3
Example 6 was a case where 10 g (0.7 mm particle size) of a granular oxidation catalyst containing Pt as a catalytically active component was uniformly filled in each cell space of the cell / inch 2 . Then, at the time of evaluation, the portion of the sample 7 of the deodorization rate measuring device of FIG. 3 was heated by the heater 11 to about 120 ° C.
【0025】さらに、130セル/inch2 のPt,
Auを触媒活性成分とするハニカム状の酸化触媒(90
mm×90mm×25mm)に繊維状活性炭9gを各セ
ル空間内に充填したものを実施例7とした。評価の際に
は図3の脱臭率測定装置のサンプルの部分をヒータ11
によって約120℃になるように加熱した。実施例6,
7では、空間速度SV=18000で評価した。尚、測
定は実施例5と同様の悪臭源を流入させ、加熱・冷却
後、再度新鮮な無臭空気をサンプル内に導入し、実施例
5と同様な測定を行なった。また、比較として、実施例
6,7での材料を直列に並べて評価した。以下、表4に
実施例5,6,7と比較例5,6,7の測定結果を示
す。 (以下余白)Further, Pt of 130 cells / inch 2 ,
A honeycomb-shaped oxidation catalyst (90 containing Au as a catalytically active component)
(mm × 90 mm × 25 mm) with 9 g of fibrous activated carbon filled in each cell space was set as Example 7. At the time of evaluation, the portion of the sample of the deodorizing rate measuring device of FIG.
To about 120 ° C. Example 6,
7, the space velocity SV was evaluated as 18,000. In addition, the same odor source as in Example 5 was introduced, and after heating and cooling, fresh odorless air was again introduced into the sample, and the same measurement as in Example 5 was performed. Further, for comparison, the materials of Examples 6 and 7 were arranged in series and evaluated. Table 4 below shows the measurement results of Examples 5, 6 and 7 and Comparative Examples 5, 6 and 7. (Below margin)
【0026】[0026]
【表4】 [Table 4]
【0027】[0027]
【発明の効果】上述のように請求項1記載の発明は、ハ
ニカム脱臭基材のセル空間内に、ハニカム脱臭基材とは
異なる材質から成る脱臭材を充填してハニカム脱臭材を
構成し、ハニカム脱臭基材の構成材料が無機系脱臭材か
らなり、脱臭材の構成材料が、有機系脱臭材、活性炭材
料、オゾン脱臭触媒、燃焼酸化触媒から選ばれた一種或
いは二種以上の組み合わせとしたから、空気とハニカム
脱臭基材、脱臭材との接触効率が良くなり、脱臭性能が
向上すると共に悪臭の発生する局所空間の脱臭にも最適
に使用できる。しかも各種の悪臭に対して広く脱臭範囲
をカバーして脱臭性能をより向上させることができるの
で、複合臭気に対する性能向上と悪臭の再放出防止を図
ることができる結果、高性能なハニカム脱臭材が得られ
る。As described above, according to the first aspect of the invention, the honeycomb deodorizing material is formed by filling the cell space of the honeycomb deodorizing base material with a deodorizing material made of a material different from that of the honeycomb deodorizing base material, Whether the constituent material of the honeycomb deodorizing base material is an inorganic deodorizing material
Rannahli, configuration material of the deodorizing material, organic-based deodorizer, activated carbon materials, the ozone deodorizing catalyst, because the a kind or in a combination of two or more selected from burning oxidation catalyst, air and honeycomb deodorizing substrate, deodorizing The contact efficiency with the material is improved, the deodorizing performance is improved, and it can be optimally used for deodorizing the local space where a bad odor is generated. Moreover, since it is possible to cover a wide range of deodorization with respect to various bad odors and further improve the deodorizing performance, it is possible to improve the performance against complex odors and prevent re-emission of bad odors. can get.
【0028】[0028]
【0029】請求項2記載の発明は、脱臭材の形状とし
ては、粉体、粒状、繊維状の各形状から選ばれた一種或
いは二種以上の組み合わせとしたから、脱臭材の表面積
が大きくなり、空気との接触効率をより向上させて脱臭
性能を一層向上させることができる。According to the second aspect of the present invention, the shape of the deodorizing material is one or a combination of two or more selected from powdery, granular and fibrous shapes. Therefore, the surface area of the deodorizing material becomes large. The contact efficiency with air can be further improved, and the deodorizing performance can be further improved.
【図1】(a)は本発明の一実施例のハニカム脱臭材を
正面から見た模式図、(b)はハニカム脱臭材の一部を
斜めから見た模式図である。FIG. 1 (a) is a schematic view of a honeycomb deodorizing material according to an embodiment of the present invention as seen from the front, and FIG. 1 (b) is a schematic view of a portion of the honeycomb deodorizing material as seen obliquely.
【図2】(a)は本発明の他の実施例のハニカム脱臭材
を正面から見た模式図、(b)はハニカム脱臭材の一部
を斜めから見た模式図である。FIG. 2A is a schematic view of a honeycomb deodorizing material according to another embodiment of the present invention as seen from the front, and FIG. 2B is a schematic view of a portion of the honeycomb deodorizing material as seen obliquely.
【図3】同上の脱臭率測定装置の概略図である。FIG. 3 is a schematic view of the above deodorizing rate measuring device.
1 ハニカム脱臭材 2 ハニカム脱臭基材 2a セル空間 3 脱臭材 1 Honeycomb deodorant 2 Honeycomb deodorant base material 2a cell space 3 deodorant
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI B01D 53/81 B01J 23/34 A 53/86 ZAB 23/42 A B01J 20/28 B01D 53/34 116J 23/34 53/36 ZABF 23/42 ZABH (56)参考文献 特開 昭59−142843(JP,A) 特開 昭63−319022(JP,A) 特開 平2−126856(JP,A) 実開 昭57−39627(JP,U) 実開 平4−923(JP,U) (58)調査した分野(Int.Cl.7,DB名) A61L 9/00 B01D 53/02 B01D 53/34 ─────────────────────────────────────────────────── ─── Continued Front Page (51) Int.Cl. 7 Identification Code FI B01D 53/81 B01J 23/34 A 53/86 ZAB 23/42 A B01J 20/28 B01D 53/34 116J 23/34 53/36 ZABF 23/42 ZABH (56) Reference JP-A-59-142843 (JP, A) JP-A-63-319022 (JP, A) JP-A-2-126856 (JP, A) Practical application Sho-57-39627 ( JP, U) Actual Kaihei 4-923 (JP, U) (58) Fields investigated (Int.Cl. 7 , DB name) A61L 9/00 B01D 53/02 B01D 53/34
Claims (2)
カム脱臭基材とは異なる材質から成る脱臭材が充填さ
れ、ハニカム脱臭基材の構成材料が無機系脱臭材からな
り、脱臭材の構成材料が、有機系脱臭材、活性炭材料、
オゾン脱臭触媒、燃焼酸化触媒から選ばれた一種或いは
二種以上の組み合わせから成ることを特徴とするハニカ
ム脱臭材。1. A deodorizing material made of a material different from that of the honeycomb deodorizing base material is filled in the cell space of the honeycomb deodorizing base material, and the constituent material of the honeycomb deodorizing base material is made of an inorganic deodorizing material.
Ri, configuration material of deodorizing material, organic-based deodorizing material, activated carbon material,
A honeycomb deodorizing material comprising one or a combination of two or more selected from an ozone deodorizing catalyst and a combustion oxidation catalyst .
各形状から選ばれた一種或いは二種以上の組み合わせか
ら成ることを特徴とする請求項1記載のハニカム脱臭
材。 2. The shape of the deodorizing material is powder, granular or fibrous.
Is it one kind or a combination of two or more kinds selected from each shape?
Honeycomb deodorization according to claim 1, characterized by comprising al
Material.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP00682794A JP3460290B2 (en) | 1994-01-26 | 1994-01-26 | Honeycomb deodorizer |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP00682794A JP3460290B2 (en) | 1994-01-26 | 1994-01-26 | Honeycomb deodorizer |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH07204442A JPH07204442A (en) | 1995-08-08 |
JP3460290B2 true JP3460290B2 (en) | 2003-10-27 |
Family
ID=11649060
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP00682794A Expired - Fee Related JP3460290B2 (en) | 1994-01-26 | 1994-01-26 | Honeycomb deodorizer |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP3460290B2 (en) |
Families Citing this family (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP4833521B2 (en) * | 2004-04-20 | 2011-12-07 | 富士工業株式会社 | Range hood fan deodorizing material and range hood fan comprising the deodorizing material |
JP4856514B2 (en) * | 2006-10-20 | 2012-01-18 | 株式会社日立製作所 | Exhalation component collector, exhalation component collection device, exhalation component collector manufacturing method, exhalation component analysis device, and exhalation component analysis method |
JP5404730B2 (en) * | 2011-10-05 | 2014-02-05 | シャープ株式会社 | Filter and air purifier |
KR101894477B1 (en) * | 2017-05-30 | 2018-09-04 | (주)한독크린텍 | Deodorization Filter of Air Cleaner to Seletive Change of Filter |
WO2024135747A1 (en) * | 2022-12-20 | 2024-06-27 | 日本碍子株式会社 | Reactor, gas recovery device, and gas recovery system |
WO2024135745A1 (en) * | 2022-12-20 | 2024-06-27 | 日本碍子株式会社 | Reactor and method for manufacturing same, gas recovery device, and gas recovery system |
-
1994
- 1994-01-26 JP JP00682794A patent/JP3460290B2/en not_active Expired - Fee Related
Also Published As
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JPH07204442A (en) | 1995-08-08 |
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