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JPH0615035B2 - Air purifier - Google Patents
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JPH0615035B2 - Air purifier - Google Patents

Air purifier

Info

Publication number
JPH0615035B2
JPH0615035B2 JP63314474A JP31447488A JPH0615035B2 JP H0615035 B2 JPH0615035 B2 JP H0615035B2 JP 63314474 A JP63314474 A JP 63314474A JP 31447488 A JP31447488 A JP 31447488A JP H0615035 B2 JPH0615035 B2 JP H0615035B2
Authority
JP
Japan
Prior art keywords
activated carbon
aniline
air purifying
impregnated
adsorption
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
JP63314474A
Other languages
Japanese (ja)
Other versions
JPH02160041A (en
Inventor
修三 徳満
昇 成尾
泰 鷹野
輝弘 岡田
浩史 内田
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 JP63314474A priority Critical patent/JPH0615035B2/en
Publication of JPH02160041A publication Critical patent/JPH02160041A/en
Publication of JPH0615035B2 publication Critical patent/JPH0615035B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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  • Disinfection, Sterilisation Or Deodorisation Of Air (AREA)
  • Treating Waste Gases (AREA)
  • Separation Of Gases By Adsorption (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Description

【発明の詳細な説明】 産業上の利用分野 本発明はオフィス、家庭等の室内空気の臭気除去に有効
な空気浄化剤に関するものである。
TECHNICAL FIELD The present invention relates to an air purifying agent effective for removing odors from indoor air in offices, homes and the like.

従来の技術 オフィス、家庭等の生活空間で発生する悪臭には、組成
的にはアセトアルデヒドなどの低級脂肪族アルデヒド、
アンモニア、低級アミン、炭化水素、硫化水素、メチル
メルカプタン等が含まれている。その代表的なものとし
て、たばこを喫煙したときに発生する臭気がある。
Conventional technology The composition of the bad odors generated in living spaces such as offices and homes is lower aliphatic aldehydes such as acetaldehyde,
It contains ammonia, lower amines, hydrocarbons, hydrogen sulfide, methyl mercaptan, etc. A typical example is the odor generated when smoking a cigarette.

一方、一般的に空気浄化剤としては、活性炭が良く使用
される。活性炭は無極性吸着剤として極めて優れた吸着
性を有する特異な材質で、ほとんどすべてのガス状物質
に対して高い吸着性を示す。しかし、通常の活性炭では
上記悪臭のなかで低級脂肪族アルデヒドやアンモニア、
低級アミンを除去することが困難である。
On the other hand, generally, activated carbon is often used as an air purifying agent. Activated carbon is a peculiar material that has extremely excellent adsorptivity as a non-polar adsorbent, and exhibits high adsorptivity for almost all gaseous substances. However, with ordinary activated carbon, lower aliphatic aldehyde and ammonia,
It is difficult to remove lower amines.

上記活性炭の欠点を解決する方法として、活性炭にアニ
リンを添着した吸着剤は特公昭60−54095号公報
に開示され、活性炭100部にアニリン1〜30部を添
着したものは気相中のアセトアルデヒドなどの低級脂肪
族アルデヒドの吸着に有効であると記載されている。
As a method for solving the above-mentioned drawbacks of activated carbon, an adsorbent in which activated carbon is impregnated with aniline is disclosed in Japanese Examined Patent Publication No. 54095/1985, and 100 parts of activated carbon impregnated with 1 to 30 parts of aniline is acetaldehyde in a gas phase. Is described as being effective in adsorbing lower aliphatic aldehydes.

さらに、活性炭等の多孔性物質に硫酸やリン酸などの無
機酸を添着させて脱臭剤に使用するものは既に公知の技
術であり、アンモニア及び低級アミンの優れた吸着剤と
して実用化されている。
Furthermore, a technique of impregnating a porous substance such as activated carbon with an inorganic acid such as sulfuric acid or phosphoric acid to be used as a deodorant is a known technique, and has been put into practical use as an excellent adsorbent for ammonia and lower amines. .

また、先に本発明者等は上記無機酸を添着した活性炭に
さらにアニリンを添着することによって、アンモニア及
び低級アミンの吸着性能に優れると共に、低級脂肪族ア
ルデヒドの再放出が防げることを見出だし実用化した。
In addition, the present inventors previously found that by adsorbing aniline to the activated carbon impregnated with the above-mentioned inorganic acid, the adsorption performance of ammonia and lower amines is excellent, and the re-release of lower aliphatic aldehydes can be prevented. Turned into

発明が解決しようとする課題 しかして、上記種々の活性炭を混合することによって、
生活空間の悪臭はおおよそ除去できる。しかし、上記従
来の活性炭のなかで、アニリンを添着した活性炭は耐久
性において課題があった。それは、アニリンの活性炭へ
の吸着保持力が弱いため、多量に添着しても熱などが加
わることによって脱離し、低級脂肪族アルデヒドの吸着
力が弱くなるという課題があった。
DISCLOSURE OF THE INVENTION Problems to be Solved by the Invention Therefore, by mixing the above various activated carbons,
The stench in the living space can be removed. However, among the above-mentioned conventional activated carbons, activated carbon impregnated with aniline has a problem in durability. Since the aniline has a weak adsorptivity to activated carbon, it has a problem that even if a large amount of aniline is impregnated, the aniline is desorbed by the addition of heat or the like, and the adsorptivity of the lower aliphatic aldehyde becomes weak.

本発明の目的は、臭気に含まれるあらゆる成分の吸着能
力にすぐれ、また吸着能力の持続性においてバランスの
とれた性能の空気浄化剤を得ることにある。
An object of the present invention is to obtain an air purifier having excellent adsorption ability for all components contained in odor and having balanced performance in the persistence of adsorption ability.

課題を解決するための手段 これらの目的を達成するために本発明は、第1の手段と
してリン酸アニリン塩とアニリンの双方を添着した活性
炭、アニリンとリン酸の双方を添着した活性炭および/
あるいはアニリンを添着した活性炭を混合せしめたもの
を空気浄化剤としたものである。
Means for Solving the Problems In order to achieve these objects, the present invention provides, as a first means, activated carbon in which both an aniline phosphate salt and aniline are impregnated, activated carbon in which both aniline and phosphoric acid are impregnated, and / or
Alternatively, a mixture of activated carbon impregnated with aniline is used as an air purifying agent.

また第2の手段として、リン酸アニリン塩とアニリンの
双方を添着した活性炭20重量%〜80重量%、アニリ
ンとリン酸の双方を添着した活性炭15重量%〜60重
量%およびアニリンを添着した活性炭0重量%〜35重
量%を混合せしめたものを空気浄化剤としたものであ
る。第3,4の手段として、上記2つの空気浄化剤を使
って空気浄化フィルタ並びに空気清浄装置としたもので
ある。
As the second means, 20% to 80% by weight of activated carbon impregnated with both aniline phosphate and aniline, 15% to 60% by weight of activated carbon impregnated with both aniline and phosphoric acid, and activated carbon impregnated with aniline. A mixture of 0% by weight to 35% by weight was used as an air purifying agent. As the third and fourth means, an air purifying filter and an air purifying device using the above two air purifying agents are provided.

作 用 リン酸アニリン塩とアニリンの双方を添着した活性炭に
おいては、アニリンとアルデヒドの付加反応により低級
脂肪族アルデヒドの吸着性にすぐれ、またアニリンガス
の脱離が無いため、その耐久性においてもすぐれてい
る。さらにリン酸アニリン塩は活性炭のマクロポア、割
れ目あるいは表面部分に添着されるので、ミクロポアの
活性の低下が少なく、炭化水素の吸着性にもすぐれてい
る。またリン酸アニリン塩、アニリンの添着量をコント
ロールすることによって、硫化水素、メチルメルカプタ
ンの吸着性あるいは触媒分解性も良好なものとなる。ア
ニリンとリン酸の双方を添着した活性炭は、リン酸との
中和反応によりアンモニアや低級アミンの吸着性にすぐ
れ、また低級脂肪族アルデヒドの再放出がない。アニリ
ンを添着した活性炭は、その添着量をコントロールする
ことによって、炭化水素、硫化水素、メチルメルカプタ
ンの吸着性あるいは触媒分解性にすぐれ、低級脂肪族ア
ルデヒドの再放出がないものとなる。したがって、これ
らの3種類の活性炭を混合することによって、あらゆる
臭気を除去でき、優れた高い性能を長く持続できるもの
である。
Activated carbon impregnated with both aniline phosphate and aniline for use has excellent adsorptivity for lower aliphatic aldehydes due to the addition reaction of aniline and aldehyde, and also has excellent durability because it does not desorb aniline gas. ing. Furthermore, since the aniline phosphate is attached to the macropores, cracks or surface portions of the activated carbon, the activity of the micropores is less reduced and the adsorption of hydrocarbons is excellent. Further, by controlling the amount of aniline phosphate and aniline impregnated, the adsorbability of hydrogen sulfide and methyl mercaptan or the catalytic decomposability becomes good. Activated carbon impregnated with both aniline and phosphoric acid has excellent adsorptivity for ammonia and lower amines due to the neutralization reaction with phosphoric acid, and does not re-release lower aliphatic aldehydes. By controlling the amount of impregnated aniline, activated carbon is excellent in the adsorptivity or catalytic decomposition of hydrocarbons, hydrogen sulfide, and methyl mercaptan and does not cause re-emission of lower aliphatic aldehyde. Therefore, by mixing these three types of activated carbon, all odors can be removed, and excellent high performance can be maintained for a long time.

また、空気浄化剤の混合割合をリン酸アニリン塩とアニ
リンの双方を添着した活性炭20重量%〜80重量%、
アニリンとリン酸の双方を添着した活性炭15重量%〜
60重量%およびアニリンを添着した活性炭0重量%〜
35重量%とすることにより、臭気成分であるアセトア
ルデヒドなどの低級脂肪族アルデヒド、アンモニア、低
級アミン、炭化水素、硫化水素、メチルメルカプタン等
のあらゆる成分の吸着能力にすぐれ、その吸着能力の持
続性においてもバランスのとれたものにできるものであ
る。
Further, the mixing ratio of the air purifying agent is 20 wt% to 80 wt% of activated carbon impregnated with both aniline phosphate and aniline,
15% by weight of activated carbon impregnated with both aniline and phosphoric acid
60% by weight and 0% by weight of activated carbon impregnated with aniline
By adjusting the amount to 35% by weight, the odorous components such as acetaldehyde and other lower aliphatic aldehydes, ammonia, lower amines, hydrocarbons, hydrogen sulfide, methyl mercaptan and the like have excellent adsorption ability, and the adsorption ability is maintained. Can be well-balanced.

実施例 以下実施例を挙げて具体的に本発明を説明するが、これ
らの実施例は本発明を何等限定するものではない。
EXAMPLES The present invention will be specifically described below with reference to examples, but these examples do not limit the present invention in any way.

実施例1 ここで使用する活性炭は、通常1gあたり数百m2あるい
はそれ以上の大きな表面積を有し、高い吸着性を示す炭
素材料であれば広範囲に使用できる。活性炭の原料は通
常椰子殻又は木材等の炭化物あるいは石炭が使用される
がいずれでも良い。又賦活法も水蒸気あるいは二酸化炭
素により高温で又は塩化亜鉛,リン酸,濃硫酸処理等い
づれの方法により得られたものでもよいが、ここでは水
蒸気賦活法が望ましい。また形状は破砕炭、造粒炭ある
いは顆粒炭のいづれでも効果は認められるが、圧損失及
び入替え等取り扱い上、造粒炭または活性炭を添着した
シート状吸着層が便利である。
Example 1 The activated carbon used here generally has a large surface area of several hundred m 2 per 1 g or more, and can be used in a wide range as long as it is a carbon material showing high adsorptivity. As a raw material for the activated carbon, a charcoal such as a palm shell or wood is usually used, or coal is used. The activation method may be obtained by steam or carbon dioxide at a high temperature or by any method such as treatment with zinc chloride, phosphoric acid or concentrated sulfuric acid, but the steam activation method is preferred here. In addition, although the shape is effective with any of crushed coal, granulated coal or granulated coal, a sheet-shaped adsorption layer impregnated with granulated coal or activated carbon is convenient in terms of handling such as pressure loss and replacement.

次にここで使用する第1表に示した活性炭の調整方法に
ついて説明する。A1の活性炭は、通常の吸着能力を持
つ6〜12メッシュの破砕状椰子殻活性炭100部に対
しリン酸アニリン塩結晶を100メッシュ以下に粉砕し
た微粉末6部を水20部に懸濁させた液を作り、活性炭
を良くかき交ぜながらリン酸アニリン塩の懸濁液を少量
づつ良くかき交ぜながらふりかけた。その後添着した活
性炭を、温度120℃の乾燥機中で3時間乾燥したもの
を密閉した容器に取り、アニリンを4部ふりかけ、密閉
状態で温度40℃の恒温槽に40時間放置し、アニリン
を活性炭全体に平均的に添着させた。A2の活性炭は、
A1で使った物と同じ椰子殻活性炭100部を密閉した
容器に取り、アニリンを4部ふりかけ、密閉状態で温度
40℃の恒温槽に40時間放置し、アニリンを活性炭全
体に平均的に添着させた。B2の活性炭は、A2と同じ
方法でアニリン8部を添着した。A3の活性炭は、A1
で使った物と同じ椰子殻活性炭100部にA2と同じ方
法でアニリン4部を添着する。そして次に、リン酸を添
着するには、リン酸35部の溶液中に浸漬して、活性炭
の細孔中に十分吸着せしめた後、ろ別乾燥するかあるい
は溶液をふりかけて十分に含浸させたものを乾燥しても
よい。
Next, a method for adjusting the activated carbon shown in Table 1 used here will be described. As for the activated carbon of A1, 6 parts of fine powder obtained by crushing aniline phosphate crystals to 100 mesh or less was suspended in 20 parts of water with respect to 100 parts of 6-12 mesh crushed palm shell activated carbon having normal adsorption ability. A liquid was prepared, and the suspension of aniline phosphate was sprinkled with good stirring while stirring well with activated carbon. After that, the activated carbon impregnated was dried in a dryer at a temperature of 120 ° C. for 3 hours, placed in a sealed container, sprinkled with 4 parts of aniline, and left in a thermostatic bath at a temperature of 40 ° C. for 40 hours in a sealed state to activate the activated carbon. It was attached to the whole on average. A2 activated carbon is
100 parts of the same coconut shell activated carbon as used in A1 is placed in a sealed container, 4 parts of aniline is sprinkled, and the mixture is left in a closed oven at a temperature of 40 ° C. for 40 hours in a sealed state so that aniline is evenly attached to the entire activated carbon. It was The activated carbon of B2 was impregnated with 8 parts of aniline in the same manner as A2. A3 activated carbon is A1
4 parts of aniline are impregnated on 100 parts of the same coconut shell activated carbon as used in the same way as in A2. Then, in order to impregnate phosphoric acid, it is dipped in a solution of 35 parts of phosphoric acid to be sufficiently adsorbed in the pores of activated carbon, and then filtered and dried or sprinkled with the solution to sufficiently impregnate it. It may be dried.

次にこのようにして作った活性炭を第1表の様に配合
し、これを2g取って容量3.97のガラス瓶に入れ
た後、所定量のアセトアルデヒド容液を注入し、気化さ
せる。次に25℃相対湿度60%の恒温恒湿槽中に放置
し、アセトアルデヒド濃度をガス検知器で測定した。平
衡に達した場合のアセトアルデヒド吸着量とガス濃度の
関係を調べ等温吸着線を測定した。さらに、活性炭の耐
熱性を調べるため、活性炭を乾燥機で150℃×20分
処理し、室温まで冷却したものの中から2g抜き取っ
て、上記した方法でアセトアルデヒド吸着量とガス濃度
の関係を調べ等温吸着線を測定した。
Next, the activated carbon thus prepared is blended as shown in Table 1, 2 g of this is put into a glass bottle having a volume of 3.97, and a predetermined amount of acetaldehyde solution is injected and vaporized. Next, it was left in a thermo-hygrostat at 25 ° C and a relative humidity of 60%, and the acetaldehyde concentration was measured by a gas detector. When the equilibrium was reached, the relationship between the adsorbed amount of acetaldehyde and the gas concentration was investigated, and the isotherm adsorption line was measured. Furthermore, in order to investigate the heat resistance of activated carbon, 2 g of activated carbon was treated with a dryer at 150 ° C for 20 minutes and cooled to room temperature, and the relationship between the adsorbed amount of acetaldehyde and the gas concentration was investigated by the above-mentioned method. The line was measured.

これらの等温吸着線の測定結果を、第1図に示す。a1
は配合Aの常態時の等温吸着線、b1は配合Bの常態時
の等温吸着線、a2は配合Aの加熱後の等温吸着線、b
2は配合Bの加熱後の等温吸着線である。この結果から
明らかなように、常態時においても配合Aの実施例のほ
うが、アセトアルデヒドの吸着量は大きいが、150℃
で加熱するとその差はさらにひらき、実施例の配合Aの
ほうが耐熱性においても優れている。
The measurement results of these isothermal adsorption lines are shown in FIG. a1
Is the isotherm adsorption curve of formulation A under normal conditions, b1 is the isotherm adsorption curve of formulation B under normal conditions, a2 is the isotherm adsorption line of compound A after heating, b
2 is the isotherm adsorption line of compound B after heating. As is clear from these results, the adsorbed amount of acetaldehyde was larger in the Example of Formulation A even in the normal state, but at 150 ° C.
When heated at 1, the difference becomes even more pronounced, and the compounding A of the example is superior in heat resistance.

実施例2 実施例1と同じ活性炭A1,A2,A3の配合を第2表
に示す割合で変えて、代表的な悪臭成分であるアセトア
ルデヒド、アンモニア、硫化水素ベンゼンの等温吸着線
を実施例1と同じ方法で測定した。その結果を第2図〜
第5図に示す。3種類の活性炭の望ましい混合比率は、
第2図〜第5図に示したような結果に基づくものであ
り、アルデヒド類の多いたばこ臭等に対してはA1を多
く、アミン類、アンモニアの多い魚臭、ペット臭等に対
してはA3を多く、含硫黄化合物、炭化水素の多い野菜
などの生ごみ臭、トイレ臭、皮革臭等に対してはA2を
多く配合すれば良い。
Example 2 By changing the composition of the same activated carbons A1, A2 and A3 as in Example 1 in the proportions shown in Table 2, the isothermal adsorption lines of typical malodorous components such as acetaldehyde, ammonia and hydrogen sulfide benzene were obtained by the same method as in Example 1. It was measured. The result is shown in FIG.
It is shown in FIG. The desirable mixing ratio of the three types of activated carbon is
Based on the results shown in FIGS. 2 to 5, A1 is large for tobacco odor with a lot of aldehydes, and fish odor with a lot of amines and ammonia, pet odor, etc. It is sufficient to add a large amount of A3 and a large amount of A2 for the smell of food waste such as vegetables containing a large amount of sulfur-containing compounds and hydrocarbons, toilet odor, and leather odor.

実施例3 次に本発明の空気浄化剤を使った空気浄化フィルター及
び空気清浄装置について実施例を挙げて説明する。ここ
で用いる空気浄化剤の活性炭、及びその配合を第3表に
示す。なおX1〜3,Y1の調整方法は実施例1と同じ
ように行った。第6図は本発明の空気浄化フィルタの全
体図であり、第7図はその一部拡大図である。1はクラ
フト紙等で出来たハニカム状基材である。ここではセル
寸法12mm、厚み7mmの物を用いた。2は配合X、ある
いは配合Yの空気浄化剤でハニカム状基剤の中に、各々
300g均一に充填する。空気浄化剤2の粒子は、6〜
12メッシュの破砕状のものを使用した。又3は不織布
であり、ポリエステル,アクリル,PP,PE等の熱可
塑性樹脂からなる繊維状不織布で、綿のように弾性を幾
分残しているもので、目付重量10〜50g/m2、風速
1m/secの時の圧損1mmAq以下のものを使用する。
ハニカム状基材1と不織布3を接合するための接着シー
ト4として、無溶剤型で熱融着型樹脂(ナイロン系,ア
クリル系など)を繊維状にし、かつ開口率の高い不織布
すなわちくもの巣状接着シートを用いる。
Example 3 Next, an air purifying filter and an air purifying device using the air purifying agent of the present invention will be described with reference to examples. Table 3 shows the activated carbon used as the air purifying agent and its composition. The method of adjusting X1 to 3 and Y1 was the same as in Example 1. FIG. 6 is an overall view of the air purification filter of the present invention, and FIG. 7 is a partially enlarged view thereof. Reference numeral 1 is a honeycomb substrate made of kraft paper or the like. Here, a cell having a cell size of 12 mm and a thickness of 7 mm was used. No. 2 is an air purifying agent of the composition X or the composition Y, and 300 g of each is uniformly filled in the honeycomb base material. Particles of the air purifying agent 2 are 6 to
A 12 mesh crushed product was used. Reference numeral 3 is a non-woven fabric, which is a fibrous non-woven fabric made of a thermoplastic resin such as polyester, acrylic, PP, PE, etc., which retains some elasticity like cotton, and has a basis weight of 10 to 50 g / m 2 and a wind speed. Use a pressure loss of 1 mmAq or less at 1 m / sec.
As an adhesive sheet 4 for joining the honeycomb-shaped base material 1 and the non-woven fabric 3, a solvent-free, heat-fusion-type resin (nylon-based, acrylic-based, etc.) is made into a fibrous form and has a high aperture ratio Adhesive sheet is used.

加工の手順としては、まずハニカム状基材1と不織布3
をくもの巣状接着シート4でホットプレス等により片面
のみを接合し、ついで、空気浄化剤2を均一にその上か
ら散布する。ついでその上からくもの巣状接着シート4
を置き、ホットプレス等で加熱することでフィルタSが
完成する。
As the processing procedure, first, the honeycomb-shaped substrate 1 and the non-woven fabric 3
Only one side is joined by a hot press or the like with the web-like adhesive sheet 4, and then the air purifying agent 2 is evenly sprayed from above. Then spider web adhesive sheet 4
Is placed and heated by a hot press or the like to complete the filter S.

このようにして得られた空気浄化フィルタSは第8図に
示すように実際の空気清浄装置に使用される。5は空気
吸い込み口、6は空気吹き出し口、7はコントロール
部、8はフィルタをセットする治具である。この空気清
浄装置の上から見た内部構造を第9図に示す。空気浄化
フィルタSは治具8により第9図のようにセットされ
る。9は空気中の大きい粉塵を除去するプレフィルタ、
10は静電集塵用フィルタ、11はモータ、12はファ
ン部、13は空気の流路を示す。14は電気集塵のため
の高電圧発生用の陽極の放電極、15は対極としての金
属板、16は静電集塵フィルタ10を分極させるために
静電集塵フィルタ10の後にセットしたラス金網等の導
電体の接地極である。
The air purifying filter S thus obtained is used in an actual air purifying device as shown in FIG. Reference numeral 5 is an air inlet, 6 is an air outlet, 7 is a controller, and 8 is a jig for setting a filter. FIG. 9 shows the internal structure of the air purifying apparatus when viewed from above. The air purification filter S is set by the jig 8 as shown in FIG. 9 is a pre-filter for removing large dust in the air,
10 is a filter for electrostatic dust collection, 11 is a motor, 12 is a fan part, and 13 is a flow path of air. 14 is an anode discharge electrode for generating a high voltage for electrostatic dust collection, 15 is a metal plate as a counter electrode, 16 is a lath set after the electrostatic dust collection filter 10 to polarize the electrostatic dust collection filter 10. It is a ground electrode for conductors such as wire mesh.

このようにして得られた空気清浄装置を、ガラス製の1
m3ボックスに入れ、同時に火をつけたたばこ(セブンス
ター)10本を入れて自然燃焼させながら、空気清浄装
置を運転して煙及び臭いを吸着させた。煙及び臭いの濃
度がほぼ一定になったところでさらにたばこ10本を入
れて燃焼させた。この様にして1日に30本のたばこを
吸着させ、約20時間経過後さらに30本吸着させる。
これを繰り返して合計120本のたばこを吸着させた。
この空気浄化フィルタSをポリエチレンの袋に入れて約
20時間放置した後、空気清浄装置にセットしてたばこ
の臭い及び硫化水素の吸着減衰曲線を測定した。その測
定方法は、空気清浄装置を中に置いたガラス製の1m3
ックスに火をつけたたばこ(セブンスター)1本を入
れ、ボックス内をファンで撹拌してたばこを燃焼させる
と共に、中の煙及び臭いを均一に分散させる。たばこが
全部燃焼したところで初期値を測定し、その後空気清浄
装置を運転して、運転時間と残存臭気量の関係を調べ吸
着減衰曲線を測定した。硫化水素の場合は、上記のたば
この代わりに約1%の硫化水素の標準ガスを入れ、初期
濃度を約20ppmに調整して行った。ガス濃度の分析
は、たばこ臭の中の沸点−70℃以上の脂肪族炭化水
素、芳香族炭化水素、ケトン類、アルデヒド類、カルボ
ン酸、ニコチンやピリジンの窒素化合物等のトータル
(ほとんど無臭の成分も含む。これをFIDトータルと呼
ぶ。)、およびアセトアルデヒドをFID(flameionizatio
n detector)付き高感度ガスクロマトグラフで、またた
ばこ臭中のアンモニアの濃度はガス検知管で、さらに硫
化水素はFPD(flamephotometric detector)付き高感度ガ
スクロマトグラフで行った。空気清浄装置の風量は2.
8m2/minで運転した。この結果を第10図〜第13図
に示す。これらから明らかなように、本発明の実施例の
配合Xにおいては、他の臭気成分の吸着能力をほぼ維持
しながら、アセトアルデヒドの吸着能力の耐久寿命が優
れたものとなっている。
The air purifying device thus obtained is made of glass 1
The air purifying device was operated to adsorb smoke and odor while putting 10 cigarettes (Seven Stars) that were ignited at the same time in a m 3 box and allowing them to spontaneously burn. When the smoke and odor concentrations became almost constant, 10 more cigarettes were added and burned. In this way, 30 cigarettes are adsorbed per day, and another 30 cigarettes are adsorbed after a lapse of about 20 hours.
By repeating this, a total of 120 cigarettes were adsorbed.
The air purifying filter S was put in a polyethylene bag and left for about 20 hours, and then set in an air purifying apparatus to measure the odor of cigarette and the adsorption decay curve of hydrogen sulfide. The measuring method is as follows: Put one lit cigarette (Seven Star) in a glass 1 m 3 box with an air purifier inside, stir the inside of the box with a fan to burn the cigarette, and Disperse smoke and odor evenly. The initial value was measured when all the tobacco had burned, and then the air purifier was operated to examine the relationship between the operating time and the amount of residual odor, and the adsorption decay curve was measured. In the case of hydrogen sulfide, a standard gas of about 1% hydrogen sulfide was added instead of the above-mentioned cigarette, and the initial concentration was adjusted to about 20 ppm. Analysis of gas concentration is carried out by analyzing the total (almost odorless components) such as aliphatic hydrocarbons, aromatic hydrocarbons, ketones, aldehydes, carboxylic acids, nitrogen compounds of nicotine and pyridine having a boiling point of -70 ° C or higher in tobacco odor. Including FID (flameionizatio) and acetaldehyde.
n detector) with a high sensitivity gas chromatograph, the concentration of ammonia in cigarette odor was detected with a gas detector tube, and hydrogen sulfide was measured with a high sensitivity gas chromatograph with an FPD (flame photometric detector). The air volume of the air purifier is 2.
It was operated at 8 m 2 / min. The results are shown in FIGS. 10 to 13. As is clear from these, in the formulation X of the example of the present invention, the durability of the acetaldehyde adsorbing ability is excellent while the adsorbing ability of other odorous components is almost maintained.

発明の効果 上記した各実施例から明らかなように、本発明の空気浄
化剤及び空気浄化フィルタ並びに空気清浄装置は、いか
なる臭気も除去でき、かつ耐久性に優れたものである。
また、臭気に含まれるあらゆる成分の吸着能力に優れ、
さらに吸着能力の持続性においてバランスのとれた性能
を得ることができる。
EFFECTS OF THE INVENTION As is clear from the above-mentioned embodiments, the air purifying agent, the air purifying filter, and the air purifying apparatus of the present invention can remove any odor and have excellent durability.
Also, it excels in the ability to adsorb all components contained in odor,
Further, it is possible to obtain a balanced performance in the persistence of the adsorption capacity.

【図面の簡単な説明】[Brief description of drawings]

第1図は本発明の空気浄化剤の実施例と従来例の常態時
と加熱後のアセトアルデヒドの等温吸着線、第2図は各
種空気浄化剤の配合比を変えたときのアセトアルデヒド
の等温吸着線、第3図は各種空気浄化剤の配合比を変え
たときのアンモニアの等温吸着線、第4図は各種空気浄
化剤の配合比を変えたときの硫化水素の等温吸着線、第
5図は各種空気浄化剤の配合比を変えたときのベンゼン
の等温吸着線、第6図は本発明の空気浄化フィルタの一
実施例の断面図、第7図は第6図の一部分の拡大断面
図、第8図、第9図は本発明の空気浄化フィルタの使用
される空気清浄装置の斜視図及び断面図、第10図〜第
13図は本発明の空気清浄装置において、たばこ120本
の負荷をかけた後のFIDトータル、アセトアルデヒド、
アンモニア、硫化水素の吸着減衰曲線である。 2……空気浄化剤、S……空気浄化フィルタ
FIG. 1 is an isotherm adsorption line of acetaldehyde of the air purifying agent of the present invention and a conventional example, and FIG. 2 is an isotherm adsorption line of acetaldehyde when the mixing ratio of various air purifying agents is changed. Fig. 3 is an isotherm adsorption line of ammonia when the mixing ratio of various air purifying agents is changed, Fig. 4 is an isotherm adsorption line of hydrogen sulfide when the mixing ratio of various air purifying agents is changed, and Fig. 5 is Isothermal adsorption lines of benzene when the blending ratio of various air purifying agents is changed, Fig. 6 is a sectional view of an embodiment of the air purifying filter of the present invention, Fig. 7 is an enlarged sectional view of a part of Fig. 6, 8 and 9 are perspective views and cross-sectional views of an air purifying device in which the air purifying filter of the present invention is used, and FIGS. 10 to 13 show the load of 120 cigarettes in the air purifying device of the present invention. FID total after application, acetaldehyde,
It is an adsorption decay curve of ammonia and hydrogen sulfide. 2 ... Air purification agent, S ... Air purification filter

───────────────────────────────────────────────────── フロントページの続き (72)発明者 鷹野 泰 大阪府門真市大字門真1006 松下電器産業 株式会社内 (72)発明者 岡田 輝弘 岡山県備前市鶴海3111 (72)発明者 内田 浩史 岡山県備前市鶴海4125 ─────────────────────────────────────────────────── ─── Continuation of the front page (72) Inventor Yasushi Takano 1006 Kadoma, Kadoma City, Osaka Prefecture Matsushita Electric Industrial Co., Ltd. 4125 Tsurumi, Ichi

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】リン酸アニリン塩とアニリンの双方を添着
した活性炭、アニリンとリン酸の双方を添着した活性炭
および/あるいはアニリンを添着した活性炭を混合せし
めてなる空気浄化剤。
1. An air purifying agent obtained by mixing activated carbon containing both aniline phosphate and aniline, activated carbon containing both aniline and phosphoric acid, and / or activated carbon containing aniline.
【請求項2】リン酸アニリン塩とアニリンの双方を添着
した活性炭20重量%〜80重量%、アニリンとリン酸
の双方を添着した活性炭15重量%〜60重量%および
アニリンを添着した活性炭0重量%〜35重量%を混合
せしめてなる空気浄化剤。
2. 20% to 80% by weight of activated carbon impregnated with both aniline phosphate and aniline, 15% to 60% by weight of activated carbon impregnated with both aniline and phosphoric acid, and 0% of activated carbon impregnated with aniline. % To 35% by weight of an air purifying agent.
JP63314474A 1988-12-12 1988-12-12 Air purifier Expired - Lifetime JPH0615035B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP63314474A JPH0615035B2 (en) 1988-12-12 1988-12-12 Air purifier

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP63314474A JPH0615035B2 (en) 1988-12-12 1988-12-12 Air purifier

Publications (2)

Publication Number Publication Date
JPH02160041A JPH02160041A (en) 1990-06-20
JPH0615035B2 true JPH0615035B2 (en) 1994-03-02

Family

ID=18053764

Family Applications (1)

Application Number Title Priority Date Filing Date
JP63314474A Expired - Lifetime JPH0615035B2 (en) 1988-12-12 1988-12-12 Air purifier

Country Status (1)

Country Link
JP (1) JPH0615035B2 (en)

Also Published As

Publication number Publication date
JPH02160041A (en) 1990-06-20

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