JPH0616838B2 - Air purifier - Google Patents

Air purifier

Info

Publication number
JPH0616838B2
JPH0616838B2 JP63314475A JP31447588A JPH0616838B2 JP H0616838 B2 JPH0616838 B2 JP H0616838B2 JP 63314475 A JP63314475 A JP 63314475A JP 31447588 A JP31447588 A JP 31447588A JP H0616838 B2 JPH0616838 B2 JP H0616838B2
Authority
JP
Japan
Prior art keywords
activated carbon
aniline
impregnated
air
phosphoric acid
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
JP63314475A
Other languages
Japanese (ja)
Other versions
JPH02160042A (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.)
KURARE KEMIKARU KK
Panasonic Holdings Corp
Original Assignee
KURARE KEMIKARU KK
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 KURARE KEMIKARU KK, Matsushita Electric Industrial Co Ltd filed Critical KURARE KEMIKARU KK
Priority to JP63314475A priority Critical patent/JPH0616838B2/en
Publication of JPH02160042A publication Critical patent/JPH02160042A/en
Publication of JPH0616838B2 publication Critical patent/JPH0616838B2/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、家庭等の生活空間を発生する悪臭には、組成
的にはアセトン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。
2. Description of the Related Art The malodor generated in living spaces such as offices and homes compositionally contains lower aliphatic aldehydes such as acetone aldehyde, ammonia, lower amines, hydrocarbons, hydrogen sulfide, and methyl mercaptan. 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に既に公知の技
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, it is a known technique for using a porous substance such as activated carbon or the like with an inorganic acid such as sulfuric acid or phosphoric acid to be used as a deodorant, which has been put to practical use as an excellent adsorbent for ammonia and lower amines. .

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、
生活空間の悪臭な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 bad smell of 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.

そこで、本発明はいかなる臭気も除去でき、且つ耐久性
に優れた空気浄化剤を得ること目的としている。
Then, this invention aims at obtaining the air purifying agent which can remove any odor and is excellent in durability.

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、リン酸アニリ
ン塩を添着した活性炭、リン酸を添着した活性炭を混合
せしめてなる空気浄化剤、リン酸アニリン塩を添着した
活性炭、リン酸を添着した活性炭および無添着活性炭を
混合せしめてなる空気浄化剤、リン酸アニリン塩を添着
した活性炭、リン酸を添着した活性炭およびアニリンを
添着した活性炭を混合せしめてなる空気浄化剤、リン酸
アニリン塩とアニリンの双方を添着した活性炭、リン酸
を添着した活性炭を混合せしめてなる空気浄化剤、リン
酸アニリン塩とアニリンの双方を添着した活性炭、リン
酸を添着した活性炭および無添着活性炭を混合せしめて
なる空気浄化剤、あるいはリン酸アニリン塩とアニリン
の双方を添着した活性炭、リン酸を添着した活性炭およ
びアニリンを添着した活性炭を混合せしめてなる空気浄
化剤としたものである。
Means for Solving the Problems In order to achieve these objects, the present invention is an activated carbon impregnated with an aniline phosphate, an air purifier obtained by mixing activated carbon impregnated with phosphoric acid, and an aniline phosphate is impregnated. Activated carbon, an air purifying agent obtained by mixing activated carbon impregnated with phosphoric acid and non-impregnated activated carbon, an activated air carbon impregnated with an aniline phosphate salt, an air purifying agent obtained by mixing activated carbon impregnated with phosphoric acid and activated carbon impregnated with aniline , Aniline phosphoric acid salt and aniline impregnated activated carbon, air purifier made by mixing phosphoric acid impregnated activated carbon, activated carbon impregnated both aniline phosphate salt and aniline, activated carbon impregnated with phosphoric acid An air purifier made by mixing impregnated activated carbon, activated carbon impregnated with both aniline phosphate and aniline, activated with phosphoric acid. This is an air purifier obtained by mixing activated carbon impregnated with natural carbon and aniline.

作用 リン酸アニリン塩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比較的優れている。リン酸ア
ニリン塩の添着量が多すぎて約12重量%を越えるとア
ルデヒドの吸着速度が徐々に遅くなり、また約6重量%
を越えるとPHが酸性になって硫化水素、メチルメルカ
プタンの吸着性あるいは触媒分解性が悪くなる。そこ
で、アルデヒドの吸着能力を更に良くしたい場合は、更
にアニリンを添着するか、もしくはアニリンを少量添着
した活性炭を別に混合する。一方硫化水素、メチルメル
カプタンの吸着性あるいは触媒分解性や、炭化水素の吸
着性を更に良くしたい場合は、無添着活性炭かアニリン
を少量添着した活性炭を別に混合する。リン酸を添着し
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優れている。したがって、これらの
活性炭を対象とする臭気の性質に応じて混合することに
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。またこれらは、吸着速度が早
いので空気浄化フィルタに有効であり、これを使った空
気清浄装置は優れた脱臭性能とすることができる。
Action Activated carbon impregnated with aniline phosphate has excellent adsorbability of lower aliphatic aldehydes due to the addition reaction of aniline and aldehyde, and also has excellent durability because it does not desorb aniline gas. Further, 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 relatively excellent. If the amount of aniline phosphate salt added is too much and exceeds about 12% by weight, the adsorption rate of aldehyde will gradually decrease, and about 6% by weight.
If it exceeds the range, the pH becomes acidic and the adsorptivity of hydrogen sulfide or methyl mercaptan or the catalytic decomposability deteriorates. Therefore, when it is desired to further improve the aldehyde adsorption capacity, aniline is further impregnated or activated carbon having a small amount of aniline impregnated is separately mixed. On the other hand, when it is desired to further improve the adsorptivity or catalytic decomposability of hydrogen sulfide or methyl mercaptan and the adsorptivity of hydrocarbons, non-impregnated activated carbon or activated carbon impregnated with a small amount of aniline is mixed separately. Activated carbon impregnated with phosphoric acid has excellent adsorptivity for ammonia and lower amines due to a neutralization reaction with phosphoric acid. Therefore, by mixing these activated carbons according to the properties of the target odor, all odors can be removed and excellent high performance can be maintained for a long time. Further, since these have a high adsorption speed, they are effective for an air purification filter, and an air cleaning device using this can have excellent deodorizing performance.

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。活性箪の原料は通
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 active chest, 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 and 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〜A3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、12部、15部をそれぞれ水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。A4はA1〜A3と同じ方法で
リン酸アニリン塩を添着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。次に比較試料として活性炭100部を
密閉した容器に取り、アニリンを4部、8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B1、B2と無
添着炭B3を容易した。これらの試料を用いて下記の実
験を行った。
Next, a method for adjusting the activated carbon shown in Table 1 used here will be described. Activated carbons A1 to A3 are crushed coconut shell activated carbons of 6 to 12 mesh with normal adsorption capacity 100
6 parts, 12 parts, and 15 parts of fine powder obtained by crushing aniline phosphate crystals to 100 mesh or less with 20 parts of water, respectively.
A suspension of water was prepared, and the suspension of aniline phosphate was thoroughly stirred and sprinkled on it while thoroughly stirring the activated carbon. Thereafter, the attached activated carbon was dried in a dryer at a temperature of 120 ° C. for 3 hours. A4 is the same method as A1 to A3, and the one in which aniline phosphate is impregnated is placed in a sealed container, 4 parts of aniline is sprinkled, and the aniline is left in a thermostatic chamber at a temperature of 40 ° C for 40 hours in a sealed state, and the aniline is spread over the entire activated carbon. It was attached on average. Next, as a comparative sample, 100 parts of activated carbon was placed in a closed container and sprinkled with 4 parts and 8 parts of aniline,
The mixture was allowed to stand in a thermostatic chamber at a temperature of 40 ° C. for 40 hours in a sealed state to facilitate B1 and B2 in which aniline was impregnated on the entire activated carbon and non-impregnated carbon B3. The following experiments were conducted using these samples.

容量30lのガラス瓶と内径36mmのガラス管カラムと
ダイヤフラムポンプとを連結した循環系の吸着速度測定
装置を用いた。濃度40〜70ppmのアセトアルデヒ
ドガスあるいは硫化水素ガスを前記ガラス瓶に調整し、
試料2.8gをカラムに充填する。流速45cm/sec で
ガスを循環し活性炭に吸着させる。一定時間毎にガラス
瓶内のガスをサンプリングして、アセトアルデヒドの濃
度をFID(flame ionizaton detector)付き高感度ガ
スクロマトグラフで、硫化水素はFPD(flame photom
etric detector)付き高感度ガスクロマトグラフで分析
した。7つの試料についてのアセトアルデヒドおよび硫
化水素の吸着減衰曲線を第1図、第2図に示す。アセト
アルデヒドの吸着速度はアニリン添着よりもリン酸アニ
リン塩添着のほうが早いが、リン酸アニリン塩15wt
%よりも10wt%のほうが早い。硫化水素の吸着速度
はアニリン添着よりもリン酸アニリン塩添着の方が遅
く、特に6wt%を越えると急に遅くなる。
A circulation system adsorption rate measuring device was used in which a glass bottle having a volume of 30 l, a glass tube column having an inner diameter of 36 mm, and a diaphragm pump were connected. Adjust acetaldehyde gas or hydrogen sulfide gas having a concentration of 40 to 70 ppm in the glass bottle,
The column is filled with 2.8 g of sample. A gas is circulated at a flow rate of 45 cm / sec to be adsorbed on activated carbon. The gas in the glass bottle is sampled at regular intervals, and the concentration of acetaldehyde is measured by a high-sensitivity gas chromatograph with a FID (flame ionizaton detector).
It was analyzed by a highly sensitive gas chromatograph equipped with an etric detector. Adsorption decay curves of acetaldehyde and hydrogen sulfide for seven samples are shown in FIGS. 1 and 2. The acetaldehyde adsorption rate was faster with aniline phosphate impregnation than with aniline impregnation.
10wt% is faster than 10%. The adsorption rate of hydrogen sulfide is slower in the aniline phosphate salt impregnation than in the aniline impregnation, and becomes sharply slower particularly when it exceeds 6 wt%.

実施例2 実施例1で調整したA2,A4,B2の試料を用いてア
ニリンの脱離性を調べた。温度50℃の恒温層内にセッ
トした内径50mmのガラス管カラムに試料100gを充
填し、温度50℃のフレッシュ空気を流量470ml/mi
n で通し、出口ガス中のアニリンガス濃度をFID付き
高感度ガスクロマトグラフで測定した結果を図3に示
す。アニリン8wt%添着したB2から脱離するアニリ
ン量が圧倒的に多い。
Example 2 Using the samples of A2, A4 and B2 prepared in Example 1, the aniline desorption property was examined. A glass tube column with an inner diameter of 50 mm set in a thermostatic layer at a temperature of 50 ° C. is filled with 100 g of a sample, and fresh air at a temperature of 50 ° C. is supplied at a flow rate of 470 ml / mi.
FIG. 3 shows the results obtained by measuring the aniline gas concentration in the outlet gas with a high-sensitivity gas chromatograph equipped with FID by passing n. The amount of aniline released from B2 impregnated with 8 wt% of aniline is overwhelmingly large.

実施例3 実施例1で用いた活性炭にリン酸を添着した活 性炭を加えて、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、ベンゼンの平衡吸着量を測定した。また比較例とし
て第3表に示す配合についても測定した。
Example 3 The activity obtained by impregnating the activated carbon used in Example 1 with phosphoric acid was used. Equilibrium adsorption amounts of typical malodorous components such as acetaldehyde, ammonia, hydrogen sulfide and benzene were measured by adding a charcoal and changing the proportions shown in Table 2. As a comparative example, the formulations shown in Table 3 were also measured.

リン酸を添着するには、リン酸27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
乾燥しても良い。
To impregnate phosphoric acid, dip it in a solution of 27 parts of phosphoric acid and allow it to be sufficiently adsorbed in the pores of activated carbon, then filter and dry or sprinkle the solution and dry the impregnated product. You may.

次にアセトアルデヒドの平衡吸着量の測定方法について
説明する。第2表、第3表のように配合したものをそれ
ぞれ2gとって容量3.97のガラス瓶に入れた後、
所定のアセトアルデヒド溶液を注入し気化させる。次に
25℃、RH60%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管で測定した。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。そして、ガス濃度10ppmの時
の吸着量を平衡吸着量とした。同様にしてアンモニアは
10ppm、硫化水素は1ppm、ベンゼンは5ppm
の平衡吸着量を求めた。これらの結果を第2表、第3表
に示す。比較例に比べて実施例はアセトアルデヒドに対
して優れており、全体のバランスがとれた性能となって
いる。またそれぞれの活性炭の配合を少しずつ変えるこ
とによって、アセトアルデヒド、硫化水素、ベンゼンに
対する性能を変えることができる。ここではリン酸添着
炭の量を一定にしたが、この量も増減させることによっ
て、アンモニアや他のガスに対する性能ももっと変化を
持たせることができる。
Next, a method for measuring the equilibrium adsorption amount of acetaldehyde will be described. After taking 2 g of each of the compounds shown in Tables 2 and 3 and putting them in a glass bottle having a capacity of 3.97,
A predetermined acetaldehyde solution is injected and vaporized. Next, it was left in a thermo-hygrostat at 25 ° C. and RH 60%, and the acetaldehyde concentration was measured with a gas detector tube. 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. Then, the adsorption amount when the gas concentration was 10 ppm was defined as the equilibrium adsorption amount. Similarly, ammonia is 10ppm, hydrogen sulfide is 1ppm, and benzene is 5ppm.
The equilibrium adsorption amount of was determined. The results are shown in Tables 2 and 3. The example is superior to acetaldehyde as compared with the comparative example, and the performance is well balanced as a whole. Also, the performance for acetaldehyde, hydrogen sulfide, and benzene can be changed by slightly changing the composition of each activated carbon. Here, the amount of the phosphoric acid impregnated carbon is fixed, but by increasing or decreasing this amount, the performance with respect to ammonia and other gases can be further changed.

例えばアルデヒド類の多いたばこ臭等に対してはA1や
A4を多く、アミン類、アンモニアの多い魚臭、ペット
臭等に対してはリン酸添着炭を多く、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B1やB3を多く配合すれば良い。
For example, a lot of A1 and A4 for tobacco odors containing a lot of aldehydes, a lot of phosphate-impregnated carbon for a fish odor containing a lot of amines and ammonia, and a pet odor, and vegetables containing a lot of sulfur-containing compounds and hydrocarbons. For food waste odors, toilet odors, leather odors, etc., a large amount of B1 or B3 may be added.

実施例4 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は配合X1,X4,X6および比較
例Y2である。第4図は本発明の空気浄化フィルタの全
体図であり、第5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3
00g均一に充填する。空気浄化剤2の粒子は、6〜1
2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1
m/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 4 Next, an example of an air purifying filter and an air purifying apparatus using the air purifying agent of the present invention will be described. The air purifiers used here are Formulations X1, X4, X6 and Comparative Example Y2. FIG. 4 is an overall view of the air purification filter of the present invention, and FIG. 5 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. 2 is an air purifying agent of the compound X or the compound Y, and 3 in the honeycomb base
00 g is uniformly filled. The particles of the air purifying agent 2 are 6 to 1
A crushed mesh of 2 mesh 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. 1
Use a pressure loss of 1 mmAq or less at 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6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7図に示す。空気浄化
フィルタSは治具8により第7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. 7 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
m2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60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2
0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1m2ボッ
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付き高感度
ガスクロマトグラフで行った。空気清浄装置は風量2.
8m2/min で運転した。この結果を第4表に示す。
The air purifying device thus obtained is made of glass 1
An air purifying device was operated to adsorb smoke and odor while putting 10 cigarettes (Seven Stars) that were lit at the same time in a m 2 box for spontaneous combustion. 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 60 cigarettes were adsorbed. Put this air purification filter S in a polyethylene bag for about 2
After leaving it for 0 hour, it was set in an air purifier and the odor of cigarette and the adsorption decay curve of hydrogen sulfide were measured. The measurement method is to put one cigarette (Seven Star) in a glass 1 m 2 box with an air purifier inside,
The inside of the box is agitated by a fan to burn the tobacco and to uniformly disperse the smoke and odor therein. 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. Gas concentration analysis
Aliphatic hydrocarbons, aromatic hydrocarbons, ketones, aldehydes, carboxylic acids having a boiling point of -70 ° C or higher in tobacco odor,
Nitrogen compounds such as nicotine and pyridine (including almost odorless components. This is called FID total) and acetaldehyde in a high-sensitivity gas chromatograph with FID, and the concentration of ammonia in tobacco odor are detected in a gas detector tube. Further, hydrogen sulfide was analyzed by a high-sensitivity gas chromatograph with FPD. The air purifier has an air volume of 2.
It was operated at 8 m 2 / min. The results are shown in Table 4.

これらから明らかなように、本発明の実施例の配合にお
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。
As is clear from these, in the formulation of the example of the present invention, while substantially maintaining the adsorption ability of other odorous components,
It has excellent durability life of acetaldehyde adsorption capacity.

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図は本発明に用いるリン酸アニリン塩添着炭および
リン酸アニリン塩とアニリンの双方の添着炭と従来のア
ニリン添着炭および無添着炭のアセトアルデヒドの吸着
減衰曲線、第2図は第1図と同じ活性炭についての硫化
水素の吸着減衰曲線、第3図はリン酸アニリン塩添着炭
およびリン酸アニリン塩とアニリンの双方の添着炭と従
来のアニリン添着炭に50℃の空気を流通したときに脱
離してくるアニリンの量を示すグラフ、第4図は本発明
の空気浄化フィルタの一実施例の断面図、第5図は第4
図の一部分の拡大断面図、第6図、第7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
断面図である。 2……空気浄化剤、S……空気浄化フィルタ
FIG. 1 is an adsorption decay curve of aniline phosphate-impregnated carbon used in the present invention, both aniline phosphate and aniline impregnated carbon and acetaldehyde adsorption decay curves of conventional aniline-impregnated carbon and non-impregnated carbon, and FIG. 2 is FIG. Adsorption decay curve of hydrogen sulfide for the same activated carbon as in Fig. 3, Fig. 3 shows aniline phosphate impregnated carbon, and both aniline phosphate impregnated carbon and aniline impregnated carbon and conventional aniline impregnated carbon at 50 ° C. A graph showing the amount of aniline released, FIG. 4 is a sectional view of an embodiment of the air purification filter of the present invention, and FIG.
FIG. 6 is an enlarged cross-sectional view of a part of the drawing, and FIG. 6 and FIG. 7 are a perspective view and a cross-sectional view of an air purifying device in which the air purifying filter of the present invention is used. 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 (56)参考文献 特開 昭63−283645(JP,A)Front page continued (72) Inventor Yasushi Takano 1006 Kadoma, Kadoma City, Osaka Prefecture Matsushita Electric Industrial Co., Ltd. (56) References JP-A-63-283645 (JP, A)

Claims (6)

【特許請求の範囲】[Claims] 【請求項1】リン酸アニリン塩を添着した活性炭、リン
酸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 purification agent obtained by mixing activated carbon impregnated with aniline phosphate and activated carbon impregnated with phosphoric acid.
【請求項2】リン酸アニリン塩を添着した活性炭、リン
酸を添着した活性炭および無添着活性炭を混合せしめて
なる空気浄化剤。
2. An air purifying agent obtained by mixing activated carbon impregnated with aniline phosphate, activated carbon impregnated with phosphoric acid, and activated carbon without impregnation.
【請求項3】リン酸アニリン塩を添着した活性炭、リン
酸を添着した活性炭および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。
3. An air purification agent obtained by mixing activated carbon impregnated with aniline phosphate, activated carbon impregnated with phosphoric acid and activated carbon impregnated with aniline.
【請求項4】リン酸アニリン塩とアニリンの双方を添着
した活性炭、リン酸を添着した活性炭を混合せしめてな
る空気浄化剤。
4. An air purifying agent obtained by mixing activated carbon having both aniline phosphate and aniline impregnated therein, and activated carbon having phosphoric acid impregnated therein.
【請求項5】リン酸アニリン塩とアニリンの双方を添着
した活性炭、リン酸を添着した活性炭および無添着活性
炭を混合せしめてなる空気浄化剤。
5. An air purification agent obtained by mixing activated carbon impregnated with both aniline phosphate and aniline, activated carbon impregnated with phosphoric acid and non-impregnated activated carbon.
【請求項6】リン酸アニリン塩とアニリンの双方を添着
した活性炭、リン酸を添着した活性炭およびアニリンを
添着した活性炭を混合せしめてなる空気浄化剤。
6. An air purifier obtained by mixing activated carbon having both aniline phosphate and aniline impregnated therein, activated carbon having phosphoric acid impregnated therein and activated carbon impregnated with aniline.
JP63314475A 1988-12-12 1988-12-12 Air purifier Expired - Lifetime JPH0616838B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP63314475A JPH0616838B2 (en) 1988-12-12 1988-12-12 Air purifier

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP63314475A JPH0616838B2 (en) 1988-12-12 1988-12-12 Air purifier

Publications (2)

Publication Number Publication Date
JPH02160042A JPH02160042A (en) 1990-06-20
JPH0616838B2 true JPH0616838B2 (en) 1994-03-09

Family

ID=18053774

Family Applications (1)

Application Number Title Priority Date Filing Date
JP63314475A Expired - Lifetime JPH0616838B2 (en) 1988-12-12 1988-12-12 Air purifier

Country Status (1)

Country Link
JP (1) JPH0616838B2 (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP5628747B2 (en) * 2011-06-01 2014-11-19 住江織物株式会社 Flame-retardant deodorant filter and method for producing the same

Also Published As

Publication number Publication date
JPH02160042A (en) 1990-06-20

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