JPS6155411B2 - - Google Patents
Info
- Publication number
- JPS6155411B2 JPS6155411B2 JP55014547A JP1454780A JPS6155411B2 JP S6155411 B2 JPS6155411 B2 JP S6155411B2 JP 55014547 A JP55014547 A JP 55014547A JP 1454780 A JP1454780 A JP 1454780A JP S6155411 B2 JPS6155411 B2 JP S6155411B2
- Authority
- JP
- Japan
- Prior art keywords
- filter
- activated carbon
- nonwoven fabric
- air
- alkali
- 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
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A50/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
- Y02A50/20—Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
Landscapes
- Treating Waste Gases (AREA)
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
- Catalysts (AREA)
Description
【発明の詳細な説明】
本発明は、空気中に存在する臭い、二酸化窒素
(NO2)、一酸化炭素(CO)等を水蒸気存在下の
室温で除去するフイルターに関するもので、過
面積が広く、用途に応じて各除去剤の構成を任意
に選べしかも除去剤の交換が容易で、かつ圧力損
失が低い特徴を有する有害ガス除去フイルターを
提供するものである。Detailed Description of the Invention The present invention relates to a filter that removes odors, nitrogen dioxide (NO 2 ), carbon monoxide (CO), etc. present in the air at room temperature in the presence of water vapor. The present invention provides a harmful gas removal filter that allows the configuration of each removal agent to be selected arbitrarily depending on the application, allows easy replacement of the removal agent, and has low pressure loss.
NO2やCOは、自動車のエンジン、石油ストー
ブなどの家庭用暖房器具より発生するので、高速
道路の料金徴収所、地下駐車場、換気設備の不十
分な自動車用トンネル、交通量の多い都心部など
で働いたり、居住したり、通過したりする人々
は、気分が悪くなつたり頭痛を訴えたりすること
があつた。一方、石油ストーブを長時間燃焼させ
た場合、室内の換気が不十分であると、室内の
COやNO2の濃度が高くなつて最終的に中毒症状
を起すことがあつた。このようにNO2,COは人
体に対して有害であり、またNO2は鼻、目などの
粘膜質に刺激を与え最終的には吸器系に疾患を及
ぼす惧れがあつた。さらにCOも視覚、精神機能
に障害を与え、最終的には脈はく後退、けいれん
をともなう失神に至る惧れがあつた。そのため室
内に存在するNO2やCOの除去が強く望まれてお
り、また、臭いも不快な気持にさせるのでそれの
除去が望まれていた。 NO 2 and CO are emitted by car engines, kerosene heaters, and other household heaters, so they can be used at expressway toll collection stations, underground parking lots, car tunnels with inadequate ventilation, and urban centers with heavy traffic. People working, living in, or passing through the area sometimes felt sick and complained of headaches. On the other hand, if a kerosene stove is burnt for a long time and there is insufficient ventilation indoors,
The concentration of CO and NO 2 increased, eventually causing poisoning symptoms. As described above, NO 2 and CO are harmful to the human body, and NO 2 irritates the mucous membranes of the nose, eyes, etc., and may eventually cause diseases in the respiratory system. Furthermore, CO also impaired vision and mental function, and there was a risk that it would eventually lead to pulse failure and syncope accompanied by convulsions. For this reason, there is a strong desire to remove NO 2 and CO that exist indoors, and the smell also makes people feel uncomfortable, so it has been desired to remove it.
空気中に存在するNO2を除去するものとして
は、従来活性炭があつたが、この活性炭は、NO2
を吸着するので除去容量が小さくすぐに寿命に達
し、高温でNO2をNOに還元し、操作条件により
吸着したNO2が脱着する欠点があつた。従来用い
られていたアルカリと粉末活性炭とセメント剤の
混練成型物は、組成のアルカリがNO2と反応して
塩を作る乾式吸収剤であるので除去容量が大き
く、活性炭の10倍の寿命があり、NOへの還元、
NO2の脱着もないものであつた。 Activated carbon has traditionally been used to remove NO 2 present in the air, but this activated carbon
The removal capacity is small and the product reaches the end of its service life quickly, and NO 2 is reduced to NO at high temperatures, and the adsorbed NO 2 can be desorbed depending on the operating conditions. The conventionally used mixture of alkali, powdered activated carbon, and cement agent is a dry absorbent in which the alkali in the composition reacts with NO 2 to form salt, so it has a large removal capacity and has a lifespan 10 times longer than that of activated carbon. , reduction to NO,
No. 2 was not attached or detached.
さらにCOをCO2に酸化する触媒として、ホプ
カライト触媒、貴金属触媒があるが、ホプカライ
ト触媒はMnO260%,CuO40%の混合物、または
MnO250%,CuO30%,CoO15%,Ag2O5%の混
合物であり、常温でも活性を発揮するが水蒸気の
存在で活性が低下する欠点があつた。貴金属触媒
はアルミナや活性炭の担体に白金やパラジウムな
どの貴金属を担持させたものであるが、比較的高
温(80℃以上)で活性を発揮し、アルカリと粉末
活性炭とセメント材の混練成型物に白金、ルテニ
ウム、ロジウムの群より選んだ1種以上とパラジ
ウムを同時に、もしくはパラジウム単独を担持さ
せた触媒は水蒸気存在下で室温でもCOを酸化す
るものであつた。 Furthermore, there are hopcalite catalysts and noble metal catalysts as catalysts for oxidizing CO to CO 2. Hopcalite catalysts are mixtures of 60% MnO 2 and 40% CuO, or
It is a mixture of 50% MnO 2 , 30% CuO, 15% CoO, and 5% Ag 2 O, and although it exhibits activity even at room temperature, it has the disadvantage that its activity decreases in the presence of water vapor. Noble metal catalysts are made by supporting precious metals such as platinum or palladium on alumina or activated carbon carriers, and they exhibit their activity at relatively high temperatures (over 80°C), making them suitable for mixing and molding of alkali, powdered activated carbon, and cement materials. Catalysts on which one or more selected from the group of platinum, ruthenium, and rhodium and palladium were simultaneously supported, or on which palladium alone was supported, oxidized CO even at room temperature in the presence of water vapor.
よつて水蒸気存在下の室温でNO2を除去するも
のとしては、アルカリと粉末活性炭とセメントの
混練成型物、COをCO2に酸化するものとして
は、アルカリと粉末活性炭とセメント材の混練成
型物に白金、ルテニウム、ロジウムの群より選ん
だ1種以上とパラジウムを同時に、もしくはパラ
ジウム単独を担持させた触媒がそれぞれ最適であ
り、これらの混練成型物、触媒は空調用フイルタ
ーとして適用でき、また、脱臭用としては活性炭
が用いられる。 Therefore, for removing NO 2 at room temperature in the presence of water vapor, there is a kneaded molded product of alkali, powdered activated carbon, and cement, and for oxidizing CO to CO 2 , a kneaded molded product of alkali, powdered activated carbon, and cement material is used. A catalyst in which one or more selected from the group of platinum, ruthenium, and rhodium and palladium are supported at the same time or palladium alone is optimal, and these kneaded and molded products and catalysts can be used as air conditioning filters, and Activated carbon is used for deodorization.
空調用フイルターとしては圧力損失が低く、有
害ガス除去率が高いものが望まれ、圧力損失はフ
イルターの厚み(層高)、フイルター層を通過す
る空気流速の2乗に比例して増加する。除去率は
厚みが厚いほど、空気流速が遅いほど高くなる。
そこでフイルター過面積をできるだけ大きくし
て、通過する空気流速を遅くなすことにより、圧
力損失を低めて除去率を高める工夫がなされ、ハ
ニカム型構造や材をジグザグにする構造はその
一例である。しかし、ハニカム型は製造が難しく
割れなどの不良を生じやすかつたので、製造ノウ
ハウの確立が容易でなく、また製造設備も大規模
で高価で容易に製造できない難点があつた。材
をジグザグにする構造の場合は、10〜30メツシユ
程度のペレツト品をポリプロピレン繊維の間には
さみこむ不織布タイプであるので、不織布をジグ
ザグに折り曲げるだけでよいのであるが、ジグザ
グ状の不織布をフイルターとして固定する方法に
難点があり、過面積をさほど大きくできない欠
点があつた。 A filter for air conditioning is desired to have a low pressure loss and a high harmful gas removal rate, and the pressure loss increases in proportion to the thickness (layer height) of the filter and the square of the air flow rate passing through the filter layer. The removal rate increases as the thickness increases and the air flow rate decreases.
Therefore, efforts have been made to reduce the pressure loss and increase the removal rate by increasing the filter area as much as possible and slowing the air flow rate through it. Examples of this are honeycomb structures and structures in which the material is zigzag. However, the honeycomb type was difficult to manufacture and was prone to defects such as cracks, so it was difficult to establish manufacturing know-how, and the manufacturing equipment was large and expensive, making it difficult to manufacture. In the case of a structure in which the material is zigzag, it is a non-woven fabric type in which about 10 to 30 mesh pellets are sandwiched between polypropylene fibers, so it is only necessary to fold the non-woven fabric in a zigzag pattern, but it is also possible to use a zigzag-shaped non-woven fabric as a filter. There was a problem with the fixing method, and the disadvantage was that the oversurface area could not be made very large.
また性格の異なる有害ガス除去剤を2種類以上
同時に用いる場合、従来は各除去剤のみを充填し
たフイルターを重ねて用いていたので、フイルタ
ー全体として圧力損失が高くなる問題があつた。
また同一フイルターに性格の異なる有害ガス除去
剤を混合させて充填する方法も保守点検の面より
好ましくなかつた。 Furthermore, when using two or more types of harmful gas removers with different characteristics at the same time, conventionally, filters filled with only each remover were stacked one on top of the other, resulting in a problem of high pressure loss for the filter as a whole.
Furthermore, the method of filling the same filter with a mixture of harmful gas removing agents having different properties is also undesirable from the viewpoint of maintenance and inspection.
本発明は、過面積が広く、用途に応じて各除
剤の構成が任意であり、除去剤の交換が容易でか
つ低圧力損失であるフイルターを提供するもので
あり、空気中に存在する臭い、NO2,COを水蒸
気存在下の室温で除去する除去剤を充填し、その
充填物を着脱自在な構成となしているものであ
る。 The present invention provides a filter that has a large overarea, allows the configuration of each remover to be arbitrarily selected depending on the application, allows easy replacement of the remover, and has low pressure loss. , NO 2 , and CO at room temperature in the presence of water vapor, and the filling is detachable.
以下本発明の一実施例について活性炭、CO酸
化触媒、NO2除去剤を個々に2枚の繊維の間にに
はさみ込んだ不織布タイプに構成した有害ガス除
去フイルターの場合を詳述する。第1図は不織布
の外観図、第2図は断面図を示し、1は活性炭、
アルカリと粉末活性炭とセメント材の混練成型物
(NO2除去剤)、およびアルカリと粉末活性炭とセ
メント材の混練成型物に白金・ルテニウム、ロジ
ウムの群より選んだ1種類以上とパラジウムを同
時に、もしくはパラジウム単独を担持させた触媒
(CO酸化触媒)からなるガス除去剤、2はポリプ
ロピレンなどの高分子繊維、3は不織布で、この
不織布3は高分子繊維2の間に、活性炭、NO2除
去剤、CO酸化触媒の充填物をそれぞれ単独で独
立にはさみ込んだものである。不織布3はニード
ルパンチを用いた製法、熱融着を用いた製法等で
製作される。 Hereinafter, one embodiment of the present invention will be described in detail about a harmful gas removal filter constructed of a nonwoven fabric type in which activated carbon, a CO oxidation catalyst, and an NO 2 removal agent are individually sandwiched between two fibers. Fig. 1 shows an external view of the nonwoven fabric, Fig. 2 shows a cross-sectional view, and 1 shows activated carbon;
A kneaded molded product of alkali, powdered activated carbon, and cement material (NO 2 removal agent), and a kneaded molded product of alkali, powdered activated carbon, and cement material are mixed with one or more selected from the group of platinum, ruthenium, and rhodium and palladium at the same time, or A gas removing agent consisting of a catalyst (CO oxidation catalyst) supporting only palladium, 2 is a polymeric fiber such as polypropylene, 3 is a nonwoven fabric, and this nonwoven fabric 3 has activated carbon and an NO 2 removing agent between the polymeric fibers 2. , a CO oxidation catalyst filler is sandwiched between each independently. The nonwoven fabric 3 is manufactured by a manufacturing method using needle punching, a manufacturing method using heat fusion, or the like.
第3図は過層の構成を示し、第3図は第1図
の平板状不織布3を丸めて円柱状の不織布3′に
成型したもの、第4図に示す金属もしくはプラス
チツクス製の骨子4の周囲に不織布3′を取付け
過層としている。なお5は遮閉板、6は突起で
ある。不織布3′が強度的に強く、指などで容易
に押し潰れる心配がない場合は骨子4は不用であ
り、不織布3′の底面部の片方のみを金属もしく
はプラスチツクス面で覆つてもよい。骨子4は円
柱状の構造とし、その周囲に不織布3′を取付け
た際に周囲より空気のもれがない寸法とする。ま
た、底面部の片面は空気の出入りが自由に出来る
様に開放とし、他面は空気の出入りが出来ない様
に遮閉板5を置く。側面部は不織布を固定すると
ともに、空気の出入りが自由に出来ず、不織布を
固定した際に指などで容易に押し潰れない形状と
し、不織布3′と骨子4とは熱融着等で固定され
ている。過層の形状であるが、円柱状だけでな
く、三角柱、四角柱、六角柱、多角柱、円錐、三
角錐、多角錐などの形状も可能である。 FIG. 3 shows the structure of an overlayer, in which the flat nonwoven fabric 3 shown in FIG. A nonwoven fabric 3' is attached around the periphery to form an overlayer. Note that 5 is a shielding plate and 6 is a protrusion. If the nonwoven fabric 3' is strong and will not be easily crushed by fingers, the skeleton 4 is unnecessary, and only one side of the bottom surface of the nonwoven fabric 3' may be covered with a metal or plastic surface. The skeleton 4 has a cylindrical structure and has dimensions that prevent air from leaking from the surrounding area when the nonwoven fabric 3' is attached around it. Further, one side of the bottom part is open so that air can freely enter and exit, and a shielding plate 5 is placed on the other side so that air cannot enter and exit. The side part fixes the nonwoven fabric, has a shape that does not allow air to freely enter and exit, and does not easily crush the nonwoven fabric with fingers, etc. when the nonwoven fabric is fixed, and the nonwoven fabric 3' and the skeleton 4 are fixed by heat fusion or the like. ing. The shape of the overlayer is not limited to a cylindrical shape, but also triangular prisms, quadrangular prisms, hexagonal prisms, polygonal prisms, cones, triangular pyramids, polygonal pyramids, and other shapes.
第5図は過層における空気の流れを示すもの
で、8は開放部、9は側面部を示し、空気は開放
部8より導入され、側面部9より排出され、ま
た、その逆の流れも可能である。 Figure 5 shows the flow of air in the superlayer, where 8 is an open part and 9 is a side part. Air is introduced from the open part 8 and exhausted from the side part 9, and vice versa. It is possible.
第6図は有ガス除去フイルターにおける空気の
流れを示すもので、10は過層、11は固定板
を示し、過層10は固定板11に複数枚着脱自
在な構成で固定されて有害ガス除去フイルターを
形成する。空気は固定板11の前面より導入さ
れ、開放部8を通つて過層10の側面より排出
され、また、その逆の流れも可能である。過層
10は第4図の突起6により固定板11に着脱自
在な構成で固定される。固定板11には開放部8
が正確にはいる大きさの穴が過層10の数だけ
あいている。 Figure 6 shows the air flow in the gas removal filter, where 10 is an overlayer, 11 is a fixed plate, and the overlayer 10 is detachably fixed to the fixed plate 11 to remove harmful gases. Form a filter. Air is introduced from the front surface of the fixed plate 11 and exhausted from the side surface of the overlayer 10 through the opening 8, and vice versa. The overlayer 10 is removably fixed to the fixing plate 11 by the projections 6 shown in FIG. The fixed plate 11 has an open part 8
There are exactly the same number of holes as there are 10 in the superlayer.
第7図は有害ガス除去フイルターにおける活性
炭、NO2除去剤、CO酸化触媒の配置の一例を示
すもので、12は活性炭、13はNO2除去剤、1
4はCO酸化触媒で、活性炭12、NO2除去剤1
3、CO酸化触媒14からなる過層は固定板1
1に任意に配置されており、使用環境雰囲気およ
び用途により最適な構成で配置される。 Figure 7 shows an example of the arrangement of activated carbon, NO 2 removal agent, and CO oxidation catalyst in a harmful gas removal filter, where 12 is activated carbon, 13 is NO 2 removal agent, and 1
4 is CO oxidation catalyst, activated carbon 12, NO 2 removal agent 1
3. The superlayer consisting of CO oxidation catalyst 14 is fixed plate 1
1, and are arranged in an optimal configuration depending on the usage environment and application.
アルカリと粉末活性炭とセメント材の混練成型
物は常温でNO2を除去し、その製法は、アルカリ
として炭酸カリウム(K2CO3)、水酸化カルシウ
ム〔Ca(OH)2〕、セメント材として焼石膏
(CaSO4・1/2H2O)を選び、炭酸カリウム/水酸
化カルシウム/焼石膏/粉末活性炭=30/30/
20/20(wt%)の組成にカルボキシメチルセル
ロースナトリウム1.0wt%と水を添加して混練成
型したものを乾燥して10〜20メツシユに分級し
た。この混練成型物の空間速度とNO2除去率の関
係は第8図に示す通りで、NO2が混練成型物を通
過して除去される理由は、混練成型物の組成であ
るアルカリとNO2が反応して塩を作り、NO2を吸
収することによる。 The molded mixture of alkali, powdered activated carbon, and cement material removes NO 2 at room temperature, and its manufacturing method uses potassium carbonate (K 2 CO 3 ) as the alkali, calcium hydroxide [Ca(OH) 2 ] as the cement material, and sintering as the cement material. Select gypsum (CaSO 4 1/2H 2 O) and add potassium carbonate/calcium hydroxide/calcined gypsum/powdered activated carbon = 30/30/
A 20/20 (wt%) composition was mixed with 1.0 wt% sodium carboxymethylcellulose and water, dried, and classified into 10 to 20 meshes. The relationship between the space velocity and the NO 2 removal rate of this kneaded molded product is as shown in Figure 8, and the reason why NO 2 is removed through the kneaded molded product is because of the alkali and NO 2 in the composition of the kneaded molded product. by reacting to form salts and absorbing NO 2 .
2NO2+K2CO3→KNO2+KNO3+CO2
4NO2+2Ca(OH)2→
Ca(NO2)2+Ca(NO3)2+2H2O
なお条件はNO21.0ppm、温度30℃、相対湿度
55%とした。 2NO 2 +K 2 CO 3 →KNO 2 +KNO 3 +CO 2 4NO 2 +2Ca(OH) 2 → Ca(NO 2 ) 2 +Ca(NO 3 ) 2 +2H 2 O Conditions are NO 2 1.0ppm, temperature 30℃, relative humidity
It was set at 55%.
またアルカリとセメント剤と粉末活性炭の混練
成型物に白金・ルテニウム・ロジウムの群より選
んだ1種以上とパラジウムを同時に、もしくはパ
ラジウム単独で担持させた触媒は常温加湿下でも
COをCO2に酸化し、その製法はカルカリとして
炭酸カリウム、セメント剤としてアルミナセメン
トを選び、炭酸カリウム/アルミナセメント/粉
末活性炭=10/60/30(wt%)の組成にカルボ
キシメチルセルロースナトリウム0.5wt%と水を
添加して混練成型したものを乾燥して10〜20メツ
シユに分級した。上記混練成型物に貴金属として
白金・パラジウムが各0.3wt%同時担持される様
に手順の最適化を計つた後、水素化ホウ素ナトリ
ウムで還元したのち充分に水洗し約100℃で乾燥
して触媒となした。触媒の温度とCO転換率の関
係は第9図に示し、触媒はCOを酸化してCO2に
転換させるものである。 In addition, catalysts in which one or more selected from the group of platinum, ruthenium, and rhodium and palladium are simultaneously supported on a kneaded molded product of alkali, cement agent, and powdered activated carbon, or palladium alone can be used even under normal temperature and humid conditions.
CO is oxidized to CO 2 , and the manufacturing method is to select potassium carbonate as the alkali and alumina cement as the cement agent, and add 0.5wt of sodium carboxymethyl cellulose to the composition of potassium carbonate/alumina cement/powdered activated carbon = 10/60/30 (wt%). % and water were added, kneaded and molded, dried and classified into 10 to 20 meshes. After optimizing the procedure so that 0.3wt% each of platinum and palladium as precious metals were simultaneously supported on the above kneaded and molded product, the mixture was reduced with sodium borohydride, thoroughly washed with water, dried at approximately 100°C, and then catalyzed. He said. The relationship between catalyst temperature and CO conversion rate is shown in Figure 9. The catalyst oxidizes CO and converts it into CO 2 .
2CO+O2→2CO2
なお条件はCO100ppm、SV24000/時、絶対湿
度0.0145Kg/Kg乾空気となした。 2CO+O 2 →2CO 2The conditions were CO100ppm, SV24000/hour, and absolute humidity 0.0145Kg/Kg dry air.
効果の判定として、フイルターを試作して送風
機の空気流れ部に設置し、室内濃度減衰を測定し
た。フイルターは活性炭、NO2除去剤、CO酸化
触媒を個々にポリプロピレンの繊維の間に充填し
た不織布で構成し、充填密度はポリプロピレン単
位面積(cm2)あたり0.04gの充填物が充填される
様にしたものである。この不織布を第5図に示す
様に円柱状に加工成型してフイルターを試作し
た。フイルターの開放部の内径は15mm、側面部の
高さ方向の長さは30mmとなし、このフイルターを
第6図に示す様に固定板(40cm×40cm)に固定し
て最終フイルターとなした。有害ガス除去フイル
ターは活性炭フイルター30%、NO2除去剤フイル
ター30%、CO酸化触媒フイルター40%となる様
に個々のフイルターを均一分散させた。 To evaluate the effectiveness, we made a prototype filter, installed it in the airflow section of a blower, and measured the indoor concentration attenuation. The filter is composed of a nonwoven fabric in which activated carbon, NO 2 removing agent, and CO oxidation catalyst are individually filled between polypropylene fibers, and the packing density is set to 0.04 g per unit area (cm 2 ) of polypropylene. This is what I did. This nonwoven fabric was processed and molded into a cylindrical shape as shown in FIG. 5 to fabricate a filter. The inner diameter of the open part of the filter was 15 mm, and the length of the side part in the height direction was 30 mm. This filter was fixed to a fixed plate (40 cm x 40 cm) as shown in Figure 6 to form the final filter. The harmful gas removal filters were made by uniformly dispersing individual filters such that the activated carbon filter was 30%, the NO 2 removal agent filter was 30%, and the CO oxidation catalyst filter was 40%.
有害ガス除去フイルターを送風能力4.0Nm3/
分の送風能力をもつ市販の空気清浄機に設置し、
この空気清浄機を換気回数0.5回/時の6畳の部
屋(内容積30m3)で運転して室内のNO2,COの
濃度減衰を連続測定した。測定はNO2は化学発光
式の低濃度用NOx分析計、COは非分散形赤外線
方式の低濃度用CO分析計を用いておこなつた。
室内の温度は25℃、相対湿度は62%であり、室内
にあらかじめNO2とCOを市販の標準ガスボンベ
を用いて送入し、室内のNO2濃度が1.00ppm、
CO濃度が20ppmに同時になる様にガス量を調整
した。室内の濃度が同時にNO21.00ppm、
CO20ppmとなるとガスの送入を中止して空気清
浄機を運転した。室内の濃度分布は標準ガスボン
ベより送入したNO2,COを送風機を用いて拡散
しているので均一である。室内の濃度を測定する
場所は部屋の中央部であり、人が立つた場合に口
もとにあたる場所となし、空気清浄機は壁側の中
央部に設置した。第10図にはNO2の濃度減衰
を、第11図にはCOの濃度減衰を示し、NO2除
去剤・CO酸化触媒の効果がわかる。なお曲線A
は本実施例におけるフイルターを有する場合、B
は積層タイプフイルターを有する場合、Cはフイ
ルターを有さない場合である。 Blow capacity of harmful gas removal filter: 4.0Nm 3 /
Installed in a commercially available air purifier that has the air blowing capacity of
This air purifier was operated in a 6-tatami room (internal volume: 30 m 3 ) with a ventilation frequency of 0.5 times/hour, and the concentration decay of NO 2 and CO in the room was continuously measured. Measurements were made using a chemiluminescent low-concentration NO x analyzer for NO 2 and a non-dispersive infrared low-concentration CO analyzer for CO.
The indoor temperature was 25°C and the relative humidity was 62%. NO 2 and CO were injected into the room in advance using a commercially available standard gas cylinder, and the NO 2 concentration in the room was 1.00 ppm.
The gas amount was adjusted so that the CO concentration was 20 ppm at the same time. The indoor concentration is NO 2 1.00ppm at the same time,
When CO reached 20 ppm, gas supply was stopped and the air purifier was operated. The concentration distribution in the room is uniform because NO 2 and CO are introduced from standard gas cylinders and diffused using a blower. The indoor concentration was measured in the center of the room, which would be near the mouth of a person when standing, and the air purifier was installed in the center of the wall. Fig. 10 shows the NO 2 concentration decay, and Fig. 11 shows the CO concentration decay, which shows the effect of the NO 2 remover and CO oxidation catalyst. Note that curve A
has the filter in this example, B
C has a multilayer filter, and C has no filter.
最終フイルターの圧力損失を第12図に示す通
りであつた。NO2除去剤を充填した不織布、CO
酸化触媒を充填した不織布を空気の流れ方向に重
ねて用いた場合の効果は第10〜12図に示す通
りで、このフイルターの構成は、NO2除去剤、
CO酸化触媒を0.04g/cm2の充填密度でポリプロピ
レン繊維の間に個々に充填した不織布を重ねて用
い、空気の流れに対して垂直に設置したものでこ
こでは積層タイプとしている。 The pressure loss of the final filter was as shown in FIG. Non-woven fabric filled with NO2 remover, CO
The effect of using nonwoven fabrics filled with oxidation catalysts stacked in the direction of air flow is as shown in Figures 10 to 12. The structure of this filter is as follows:
A stacked nonwoven fabric in which a CO oxidation catalyst is individually packed between polypropylene fibers at a packing density of 0.04 g/cm 2 is used, and is installed perpendicular to the air flow, and here it is a laminated type.
本発明は以上のように臭い、二酸化窒素、一酸
化炭素の除去が容易で、また、他の除去剤を取り
外すことなく各々の除去剤を交替でき、さらに、
不織布の表面積を容易に大きくできるため、通過
するガスの流速を大きく低下させない等のすぐれ
た効果を奏するフイルタを提供する工業的価値の
大なるものである。 As described above, the present invention makes it easy to remove odors, nitrogen dioxide, and carbon monoxide, and each remover can be replaced without removing other removers, and further,
Since the surface area of the nonwoven fabric can be easily increased, it is of great industrial value to provide a filter that exhibits excellent effects such as not significantly reducing the flow rate of gas passing through it.
第1図は不織布の外観図、第2図は同断面図、
第3図は過層の構成図、第4図は骨子の斜視
図、第5図は過層の完成図、第6図は有害ガス
除去フイルターの完成図、第7図は有害ガス除去
剤の配置図、第8図はNO2除去剤のSV特性図、
第9図はCO酸化触媒の温度特性図、第10図は
NO2濃度減衰図、第11図はCO濃度減衰図、第
12図は圧力損失特性図である。
Figure 1 is an external view of the nonwoven fabric, Figure 2 is a cross-sectional view of the same,
Figure 3 is a configuration diagram of the overlayer, Figure 4 is a perspective view of the skeleton, Figure 5 is a completed diagram of the overlayer, Figure 6 is a completed view of the harmful gas removal filter, and Figure 7 is a diagram of the harmful gas removal agent. Layout diagram, Figure 8 is the SV characteristic diagram of the NO 2 remover,
Figure 9 is a temperature characteristic diagram of the CO oxidation catalyst, and Figure 10 is
FIG. 11 is a NO 2 concentration decay diagram, FIG. 11 is a CO concentration decay diagram, and FIG. 12 is a pressure loss characteristic diagram.
Claims (1)
除去剤等を各々不織布に充填し、この一種以上の
不織布を過層に設けた固定板の孔に各々着脱自
在に取り付けてなる有害ガス除去フイルター。1. A harmful gas removal filter in which activated carbon, a nitrogen dioxide removing agent, a carbon monoxide removing agent, etc. are each filled in a nonwoven fabric, and these nonwoven fabrics are each removably attached to holes in a fixing plate provided in an overlayer. .
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP1454780A JPS56111025A (en) | 1980-02-07 | 1980-02-07 | Harmful gas removing filter |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP1454780A JPS56111025A (en) | 1980-02-07 | 1980-02-07 | Harmful gas removing filter |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS56111025A JPS56111025A (en) | 1981-09-02 |
| JPS6155411B2 true JPS6155411B2 (en) | 1986-11-27 |
Family
ID=11864171
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP1454780A Granted JPS56111025A (en) | 1980-02-07 | 1980-02-07 | Harmful gas removing filter |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS56111025A (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US5451558A (en) * | 1994-02-04 | 1995-09-19 | Goal Line Environmental Technologies | Process for the reaction and absorption of gaseous air pollutants, apparatus therefor and method of making the same |
| JP2003088759A (en) * | 2001-09-18 | 2003-03-25 | Mitsubishi Paper Mills Ltd | Low temperature oxidation catalyst filter |
Family Cites Families (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS6025177B2 (en) * | 1977-04-20 | 1985-06-17 | 松下電器産業株式会社 | gas purification equipment |
-
1980
- 1980-02-07 JP JP1454780A patent/JPS56111025A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS56111025A (en) | 1981-09-02 |
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