JPS60202735A - Adsorbent of aldehydes in gaseous phase - Google Patents

Adsorbent of aldehydes in gaseous phase

Info

Publication number
JPS60202735A
JPS60202735A JP59056516A JP5651684A JPS60202735A JP S60202735 A JPS60202735 A JP S60202735A JP 59056516 A JP59056516 A JP 59056516A JP 5651684 A JP5651684 A JP 5651684A JP S60202735 A JPS60202735 A JP S60202735A
Authority
JP
Japan
Prior art keywords
activated carbon
amine
adsorbent
carbon material
pore diameter
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.)
Granted
Application number
JP59056516A
Other languages
Japanese (ja)
Other versions
JPS6324414B2 (en
Inventor
Nobuo Ishizaki
石崎 信男
Hiroshi Shimizu
博 清水
Seiji Watanuki
政治 渡抜
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.)
Toyobo Co Ltd
Original Assignee
Toyobo 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 Toyobo Co Ltd filed Critical Toyobo Co Ltd
Priority to JP59056516A priority Critical patent/JPS60202735A/en
Publication of JPS60202735A publication Critical patent/JPS60202735A/en
Publication of JPS6324414B2 publication Critical patent/JPS6324414B2/ja
Granted legal-status Critical Current

Links

Abstract

PURPOSE:To obtain an adsorbent capable of removing aldehydes in a gaseous phase for a long period by depositing an aliphatic primary amine or a secondary amine on an activated carbon material having specified pore volume. CONSTITUTION:An aliphatic primary amine or a secondary amine having <=10mm.Hg vapor pressure at 20 deg.C is deposited on an activated carbon material having <=3.00Angstrom pore diameter and >=0.4cc/g pore volume wherein the volume occupied by the pores having <=30Angstrom pore diameter is regulated to >=80%. The adsorptive performance is further improved by depositing said amine buffered with a weak acid (e.g., acetic acid) having 3.5-5.5pKa. The obtained adsorbent shows an excellent adsorptive performance to poisonous and highly irritant gaseous aldehyde, and the rescattering of the deposited chemicals is eliminated, and the deterioration due to the adsorption of other organic gases is reduced. The ventilation resistance is low when used in an automobile or in a living room, and the air conditioning effect is not decreased significantly.

Description

【発明の詳細な説明】 本発明は気相中のアルデヒド類に対して優れた吸着性能
を発揮する・活性炭素吸着剤に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to an activated carbon adsorbent that exhibits excellent adsorption performance for aldehydes in the gas phase.

閉された小空間でのタバコの煙中の刺激性成分(例えば
アセトアルデヒド、ホルムアルデヒド)を効率よく除失
するフィルターの要望は増大しつつある。
There is an increasing demand for a filter that efficiently removes irritating components (eg, acetaldehyde, formaldehyde) from cigarette smoke in a small, closed space.

通常の粒状活性炭吸着剤は、空気中の有害物質(例えば
ベンゼン、クロロホルム等)を低濃度でも比較的高い平
衡吸着量で吸着するため現在広く利用されている。しか
しながら、これらの吸着剤はホルムアルデヒド、アセト
アルデヒド、アクロレインの如き低濃度で刺激性の強い
アルデヒド類ガス成分に対しては平衡吸着量が低く、か
つ吸着されたガスが濃縮されて脱着するという欠点を有
していた。
Conventional granular activated carbon adsorbents are currently widely used because they adsorb harmful substances in the air (eg, benzene, chloroform, etc.) with a relatively high equilibrium adsorption amount even at low concentrations. However, these adsorbents have the disadvantage that the equilibrium adsorption amount is low for highly irritating aldehyde gas components such as formaldehyde, acetaldehyde, and acrolein, and that the adsorbed gas is concentrated and desorbed. Was.

上記欠点を解消すべく、例えば特開昭56−53744
号公報に記載の如く活性炭にアニリンを添着させた吸着
剤を用いて気相中のアルデヒド類を除失する方法が試み
られている。しかしながらこの方法とても満足な結果を
与えるものでない。というのは使用する活性炭は通常の
ヤシガラ活性炭! 2 1− bayya−sxr、a
a、+4−1+−1+ −P A1. 7+11?+ 
y−m −−9以下の細孔容積量が小さいため添着剤(
アニリン)の添着効果が小さいという欠点を内在させる
ものであったし、添着剤(アニリン)自身アルデヒド類
の吸着に対して経時的に不安定なデメリットを有し、又
発ガン性があるとされているものなので実用化には問題
があった。
In order to eliminate the above drawbacks, for example, Japanese Patent Application Laid-Open No. 56-53744
As described in the above publication, a method has been attempted in which aldehydes in the gas phase are removed using an adsorbent in which activated carbon is impregnated with aniline. However, this method does not give very satisfactory results. The activated carbon used is regular coconut shell activated carbon! 2 1- bayya-sxr,a
a, +4-1+-1+ -P A1. 7+11? +
Since the pore volume of ym−9 or less is small, the adhesive (
However, the impregnant (aniline) itself has the disadvantage of being unstable over time when adsorbing aldehydes, and is said to be carcinogenic. However, there were problems in putting it into practical use.

本発明者等は、かかる在来技術を改良すべく検討した結
果、特異な細孔構造を有する活性炭素材に特定のアミン
化合物を添着させて作製した吸着剤が人体に何等悪影響
を及ぼすことなく気相中のアルデヒド類を効率よく長期
間に亘り除去することを見い出して本発明に到達した。
As a result of studies aimed at improving this conventional technology, the present inventors have discovered that an adsorbent made by impregnating a specific amine compound with an activated carbon material having a unique pore structure has no adverse effect on the human body and has no adverse effect on the human body. The present invention was achieved by discovering that aldehydes in the phase can be efficiently removed over a long period of time.

尚、活性炭素の細孔直径および細孔容積は、常圧下の液
体窒素の沸点(−195,8℃)における吸着側の窒素
ガス吸着等混線を用いてクランストン−インクレー(C
ranston −Inkley )の計算法によりめ
た。なお、多分子吸着層と相対圧との関係は t(X)=3.54(5/1n(PS/P))’fなる
修正フレンケルーハルシ−(Frenkel−Halg
ey)の式(慶伊富長「吸着」共立出版)より計算した
The pore diameter and pore volume of activated carbon are determined by Cranston-Inkley (C
Ranston-Inkley) calculation method. The relationship between the multimolecular adsorption layer and the relative pressure is expressed by the modified Frenkel-Halsey (t(X) = 3.54(5/1n(PS/P))'f).
ey) (Keii Tominaga "Adsorption" Kyoritsu Shuppan).

但し、細孔直径300Xに相当する相対圧での窒素ガス
吸着量に標準状態における気体窒素の密度の比(1,5
84X10−3)を乗じた値を細孔直径3ooX以下の
全細孔容積とみなした。
However, the ratio (1,5
The value multiplied by 84×10−3) was regarded as the total pore volume with a pore diameter of 3ooX or less.

まず本発明において使用する活性炭素材について説明す
る。本発明に用いる活性炭素材は細孔直径300X以下
の細孔の容積が0.4cc/f以上、且つ細孔直径ao
X以下の細孔容積の細孔直径300X以下の細孔容積に
対して占める比率(以下αと略称)が80%以上の活性
炭素材であることが必須である。
First, the activated carbon material used in the present invention will be explained. The activated carbon material used in the present invention has a pore volume of 0.4 cc/f or more with a pore diameter of 300X or less, and a pore diameter of ao
It is essential that the activated carbon material has a ratio of pore volume of X or less to pore volume of pore diameter of 300X or less (hereinafter abbreviated as α) of 80% or more.

即ち、細孔直径300X以下の細孔容積Vlが0.4e
c/を未満であったり、細孔直径aoX以下の比率αが
80%未満の活性炭素材の使用では、いくら本発明のア
ミン化合物を添着したとしてもその添着効果および寿命
が充分でなく好ましい結果を与えない。
That is, the pore volume Vl with a pore diameter of 300X or less is 0.4e.
If an activated carbon material is used in which the ratio α of the pore diameter aoX or less is less than 80%, no matter how much the amine compound of the present invention is impregnated, the impregnation effect and lifespan will be insufficient, resulting in unfavorable results. I won't give it.

上記、特定細孔構造を有する活性炭素材は、例えば次の
ような方法で製造される。即ち、(1)再生セルロース
繊維、ノボラック型フェノール樹脂繊維を炭化後、水蒸
気で高温活性化処理を施す方法(2)市販粒状ヤシガラ
活性炭を高温下、水蒸気で再活性化処理を施す方法等を
挙げることができる。
The above activated carbon material having a specific pore structure is manufactured, for example, by the following method. Namely, (1) a method in which regenerated cellulose fibers or novolac type phenolic resin fibers are carbonized and then subjected to high temperature activation treatment with steam; (2) a method in which commercially available granular coconut shell activated carbon is subjected to reactivation treatment with steam at high temperature, etc. be able to.

もちろん、細孔直径300X以下の細孔容積が0.4c
c/ f’以上で、且つ、細孔直径aoX以下の細孔容
積の占める比率が80%以上の活性炭素を与える方法で
あれば、上記方法に限定されるものではない。
Of course, the pore volume of pore diameters of 300X or less is 0.4c.
The method is not limited to the above method as long as it provides activated carbon with a ratio of 80% or more of the pore volume having a diameter of c/f' or more and a pore diameter of aoX or less.

活性炭素材の形状は上記の如く粉末状、粒状、繊維状い
ずれでもよいが吸着性、添着処理の容易さの点より微粒
状、粉末状、特に粒径が30μ以下の微粉末状が好適で
ある。
The activated carbon material may be in the form of powder, granules, or fibers as described above, but from the viewpoint of adsorption and ease of impregnation, fine particles or powder, particularly fine powder with a particle size of 30 μm or less, are preferable. .

本発明は前述した様な活性炭素材を用いることにより添
着層の吸着面積を物理的に増加させて気相中のアルデヒ
ド類を効率よく除去するものであるが、他方用いる添着
剤自身、公知のものに比してアルデヒド類を経時依存が
なくよく化学的に吸着するものであってこれらの物理的
、化学的作用が相乗的に働いて顕著なアルデヒド吸着、
除去がはじめてなされたものである。
The present invention uses the above-mentioned activated carbon material to physically increase the adsorption area of the impregnating layer and efficiently remove aldehydes in the gas phase.On the other hand, the impregnant itself used is a known one. In contrast, it chemically adsorbs aldehydes without any time dependence, and these physical and chemical effects work synergistically to achieve remarkable aldehyde adsorption.
This is the first time it has been removed.

次に本発明に用いるアミン化合物について説明する。本
発明に用いるアミン化合物は20℃での蒸気圧がl O
+trmHt以下の脂肪族系第1級アミンもしくは第2
級アミンのものであることが必須である。第1級アミン
/第2級アミンの中でも蒸気圧が10 rmnHfを超
えるものは添着後飛散するとか、臭気が立つ等問題が多
い。本発明に用いる脂肪族第1級アミンあるいは第2級
アミンとしてモノエタノールアミン、N−アミノエチル
エタノールアミン、N−メチルエタノールアミン、エチ
ルモノエタノールアミン、ジメチルエタノールアミン、
ジエチルエタノールアミン等のエタノール系アミン;モ
ノイソプロパツールアミン:トリエチレンテトラミン、
テトラエチレンペンタミン、ヘキサメチレンジアミン、
ベンジルアミン、キシリレンジアミン等が挙げられるが
、好適には上記のエタノール系アミンが挙げられる(な
お、本発明の脂肪族系アミンとは芳香環にN原子が直接
結合しないアミン化合物であり、ベンジルアミン、キシ
リレンジアミンの様な芳香環とN原子との間にCH2基
が介在しているものも含む)。なお、脂肪族系第3級ア
ミンはアルデヒドと反応性が低いので本発明では採用し
ない。また芳香族アミン(アニリン、フェニレンジアミ
ン、ナフチルアミン等)は前述した様に人体への有害性
、また保存中(このものを添着して作製したフィルター
を保存中)の分解が惹起し、吸着性能が経時的に減少す
るので本発明では採用しない。
Next, the amine compound used in the present invention will be explained. The amine compound used in the present invention has a vapor pressure of 1 O at 20°C.
+trmHt or less aliphatic primary amine or secondary
It is essential that it be a class amine. Among primary amines/secondary amines, those having a vapor pressure exceeding 10 rmnHf have many problems such as scattering after impregnation or emitting odor. As the aliphatic primary amine or secondary amine used in the present invention, monoethanolamine, N-aminoethylethanolamine, N-methylethanolamine, ethylmonoethanolamine, dimethylethanolamine,
Ethanol-based amines such as diethylethanolamine; monoisopropanolamine: triethylenetetramine;
Tetraethylenepentamine, hexamethylenediamine,
Examples include benzylamine, xylylene diamine, etc., and preferably the above-mentioned ethanol amines (in addition, the aliphatic amine of the present invention is an amine compound in which the N atom is not directly bonded to the aromatic ring; (Includes those in which a CH2 group is interposed between the aromatic ring and the N atom, such as amines and xylylene diamines). Note that aliphatic tertiary amines are not used in the present invention because they have low reactivity with aldehydes. In addition, aromatic amines (aniline, phenylenediamine, naphthylamine, etc.) are harmful to the human body, as mentioned above, and decompose during storage (filters made with these amines are stored), resulting in poor adsorption performance. Since it decreases over time, it is not adopted in the present invention.

また本発明の吸着剤は活性炭素材に上記アミン化合物を
添着して作製されるが、アミン化合物の活性炭素材への
添着量は0.1〜50重量%、好ましくは1〜30重泄
%である。添着は、20℃での蒸気圧10 mm)II
F以下の脂肪族系第1級アミン又は第2級アミンの溶液
を活性炭素材にスプレー塗布後、乾燥する方法あるいは
所定濃度の該アミン化合物溶液に、所定量の活性炭素材
を浸漬、濾過すること等により達成できる。
Further, the adsorbent of the present invention is produced by impregnating the above amine compound onto an activated carbon material, and the amount of the amine compound impregnated onto the activated carbon material is 0.1 to 50% by weight, preferably 1 to 30% by weight. . Impregnation is carried out at a vapor pressure of 10 mm at 20°C) II
A method of spraying a solution of aliphatic primary amine or secondary amine of F or less on an activated carbon material and then drying it, or immersing a predetermined amount of the activated carbon material in a solution of the amine compound with a predetermined concentration and filtering it. This can be achieved by

さらに、該アミンとして下記のようなpKaが3.5〜
5.5の弱酸で緩衝したものを添着すると、さらにアル
デヒドガスへの除去効果が向上する。即ち、酢酸、プロ
ピオン酸、酪酸、れ1草酸、カプリン酸、エナント酸(
CH3(CH2)5 C0OH) 、ペラルゴン酸(C
H3−(CH2)7−Coon)、のような飽和モノカ
ルボン酸、乳酸、琥珀酸、安息香酸、グルタミン酸、カ
ルボキシメチルセルロース(CMC)、アルギン酸、ポ
リメタリック酸等がある。緩衝の方法としては、アミン
水溶液に弱酸あるいは弱酸の塩を添加する方法あるいは
、アミンを吸着させた活性炭スラリーに弱酸あるいは弱
酸の塩を添加する方法がある。
Furthermore, the amine has a pKa of 3.5 to 3.5 as shown below.
When a weak acid buffered with 5.5 is impregnated, the removal effect on aldehyde gas is further improved. Namely, acetic acid, propionic acid, butyric acid, phenolic acid, capric acid, enanthic acid (
CH3(CH2)5C0OH), pelargonic acid (C
Examples include saturated monocarboxylic acids such as H3-(CH2)7-Coon), lactic acid, succinic acid, benzoic acid, glutamic acid, carboxymethylcellulose (CMC), alginic acid, polymetallic acid, and the like. Buffering methods include a method of adding a weak acid or a salt of a weak acid to an aqueous amine solution, or a method of adding a weak acid or a salt of a weak acid to an activated carbon slurry on which an amine has been adsorbed.

本発明に係る吸着剤は例えばフィルター用途に適用され
る。本発明の吸着剤を適用するフィルターは、(1)本
発明に係る微粉末状の活性炭素材に本発明のアミンを添
着後、アルギン酸ソーダ、カルボキシメチルセルロース
、水ガラス、シリカゾル、ポリスチレン溶液等の溶液に
分散し、紙、不織布、フオーム材、ハニカム状フィルタ
ー、多孔性の粒状物等に塗布、乾燥してつくる方法、あ
るいは(6)該活性炭素材を通気性のあるシート状ある
いはシート化、段加工後、ハニカム状に成形し、この後
アミン添着処理を施す方法あるいは(ト)微粒状の活性
炭素材に本発明のアミンを添着後、不織布、トウ、織物
等に接着剤とともにまぶす方法等がある。
The adsorbent according to the present invention is applied, for example, to filter applications. A filter to which the adsorbent of the present invention is applied is produced by (1) impregnating the amine of the present invention on the finely powdered activated carbon material of the present invention, and then impregnating it with a solution such as sodium alginate, carboxymethyl cellulose, water glass, silica sol, or polystyrene solution. A method in which the activated carbon material is dispersed, applied to paper, nonwoven fabric, foam material, honeycomb filter, porous granular material, etc., and dried; (g) A method in which the amine of the present invention is impregnated with a finely divided activated carbon material and then sprinkled on a nonwoven fabric, tow, textile, etc. with an adhesive.

特に、吸着剤のアルデヒド類ガスへの接触効率と通気性
のバランスが良好なハニカム状フィルターあるいは多孔
性ウレタン・フオーム(商品名:エバー・ライト・スコ
ツト;プリジストンタイヤKK)へのコーティング・フ
ィルターの使用が好ましい。
In particular, coating filters with honeycomb-like filters or porous urethane foam (product name: Ever Light Scotto; Prigiston Tire KK) have a good balance between adsorbent contact efficiency with aldehyde gases and air permeability. Use is preferred.

本発明の吸着剤は、特定の分子構造を有するアミンが特
定の細孔分布をもつ活性炭床に添着されているため、有
害かつ高刺激性のアルデヒドガスに対し優れた吸着性能
を示すこと、添着薬品の再飛散が無いこと、又、アルデ
ヒド・ガスのみに選択的に化学吸着するため、他の有機
性ガスの吸着による劣化が小さいという特徴を有する。
The adsorbent of the present invention has an amine with a specific molecular structure impregnated on an activated carbon bed with a specific pore distribution, so it exhibits excellent adsorption performance for harmful and highly irritating aldehyde gas. It has the characteristics that there is no re-scattering of chemicals, and because it chemically adsorbs selectively only to aldehyde gas, there is little deterioration due to adsorption of other organic gases.

従って、ホルムアルデヒド、アセトアルデヒド等が充満
しやすい自動車内、電車車輌内、喫茶店、鋏画館、遊ぎ
場あるいは、家庭の居間に本発明に係る吸着剤を使用し
たフィルターを設置すると効率よく上記有害ガスを除去
し、通気抵抗も低く、室内の暖冷房効果を低下させるこ
とが少ないというメリットを有する。又、シガレット・
フィルター用吸着剤として使用すると、タバコ煙の刺激
成分を効率よく除去するため喫味の改良効果が計れると
いう特徴も有する。
Therefore, if a filter using the adsorbent of the present invention is installed in the interior of a car, train car, coffee shop, scissor art gallery, playground, or living room where formaldehyde, acetaldehyde, etc. are likely to be filled, the above harmful gases can be efficiently removed. It has the advantage of eliminating airflow, low ventilation resistance, and less deterioration of indoor heating and cooling effects. Also, cigarettes
When used as an adsorbent for filters, it efficiently removes the irritating components of tobacco smoke, thereby improving smoking taste.

以下本発明の実施例を記載するが、本発明はこれら実施
例に何ら限定されるものではない。
Examples of the present invention will be described below, but the present invention is not limited to these Examples in any way.

実施例1 1.5dの再生セルレース繊維に、リン酸アンモニウム
を10重量%含浸、乾燥後、不活性ガス中で室温から6
0℃/hの昇温速度で300Cまで熱処理を施し耐炎性
繊維を得た。次いで、この耐炎性繊維を水蒸気含有不活
性ガス中で400℃/hrの昇温速度で900℃まで昇
温し、lhrその温度で保持し、活性化処理を施した。
Example 1 A 1.5 d recycled cellulose fiber was impregnated with 10% by weight of ammonium phosphate, dried, and heated from room temperature to 6 % by weight in an inert gas.
Heat treatment was performed to 300C at a heating rate of 0C/h to obtain flame-resistant fibers. Next, this flame-resistant fiber was heated to 900° C. at a heating rate of 400° C./hr in an inert gas containing water vapor, maintained at that temperature for 1 hr, and subjected to an activation treatment.

vlが0.78 cc / ?、α−92%の繊維状活
性炭が得られた。上記活性炭素材60部、沖水度が5R
30°に叩解されたNBKPパルプ(針葉樹プリーチン
ダクラフトパルブ)40部及びポリビニルアルコール繊
維7部の組成で、ヤンキー型湿式抄紙機で活性炭素ペー
パーを452/靜の目付で抄造した。ペーパー厚◆0.
20+as+の活性倹素紙を得た。次いで該炭素紙をコ
ルゲート加工機でピッチ巾3.1mm、ピッチ高2.1
胴の片面段ポール・シートに形成した。
vl is 0.78 cc/? , α-92% fibrous activated carbon was obtained. 60 parts of the above activated carbon material, offshore water temperature is 5R
Activated carbon paper was made with a Yankee type wet paper machine to a weight of 452/m2 using a composition of 40 parts of NBKP pulp (softwood Pulichinda kraft pulp) beaten to 30° and 7 parts of polyvinyl alcohol fiber. Paper thickness ◆0.
A 20+as+ activated alumina paper was obtained. Next, the carbon paper was processed using a corrugating machine to a pitch width of 3.1 mm and a pitch height of 2.1 mm.
The body was formed into a corrugated pole sheet on one side.

該片面段ボール・シートを、層長2.Ocmにスリット
後、直径15crnの円板状に巻き上げ、ノ・ニカム状
フィルターを得た。
The single-sided corrugated sheet was coated with a layer length of 2. After slitting it into 0 cm, it was rolled up into a disk shape with a diameter of 15 crn to obtain a nicum-shaped filter.

該ハニカム・フィルターを、琥珀酸でPH7kmM整し
たアミノエチル・エタノールアミン(20℃での蒸気圧
0.01+llInHf以下)の20重値%の水溶液に
30分間浸漬後、風乾し、アミノエチル・エタノールア
ミンが20重値%添着されたフィルターを得た。得られ
たフィルターについて下記の方法に基づいてアルデヒド
ガス吸着性を評価した。
The honeycomb filter was immersed for 30 minutes in a 20% by weight aqueous solution of aminoethyl ethanolamine (vapour pressure at 20°C of 0.01+llInHf or less) whose pH was adjusted to 7kmM with succinic acid, and then air-dried. A filter was obtained in which 20% by weight of impregnated with. The aldehyde gas adsorption properties of the obtained filters were evaluated based on the following method.

即ち、該フィルタ〒を市販の小型室内空気清浄器(松下
電工製 エアーリフレ)に装填した。
That is, the filter was loaded into a commercially available small indoor air purifier (Air Refle, manufactured by Matsushita Electric Works).

該空気清浄器を2.7−のアセトアルデヒドガスを約3
 ppmで満たされたプラスチック製ボックスの中央に
設置し、風輩0.53rr?/jthで運転した。アセ
トアルデヒドガスの減衰曲線を30分にわたりFrD法
式ガスクロマトグラフで測定した。該減衰曲線を1次反
応式と仮定して、その反応速度定数を計算し、これをフ
ィルターのアセトアルデヒドガスへの吸収能のメジャー
とした。上記の評価によるフィルターのアセトアルデヒ
ド吸着性能を表1に示す。なお、第1表中温着後3 h
rs、1 weekとあるのはフィルター作製後3時間
、1週間放置した後のフィルター性能である。なお、フ
ィルターを放置した場所は映画館とした。
The air purifier contains about 2.7-m of acetaldehyde gas.
Installed in the center of a plastic box filled with ppm, the wind was 0.53rr? I drove at /jth. The decay curve of acetaldehyde gas was measured over 30 minutes using an FrD gas chromatograph. Assuming that the attenuation curve is a first-order reaction equation, the reaction rate constant was calculated and used as a measure of the filter's ability to absorb acetaldehyde gas. Table 1 shows the acetaldehyde adsorption performance of the filter based on the above evaluation. In addition, in Table 1, 3 hours after warming
rs, 1 week indicates the filter performance after being left for 3 hours after filter production and for 1 week. The location where the filter was left was a movie theater.

比較例1 実施例1の活性化条件を850℃、0.5hrで変更し
、 V1= 0.35 cc / fα= 97 % の繊維状活性炭を得た。
Comparative Example 1 The activation conditions of Example 1 were changed to 850° C. for 0.5 hr, and fibrous activated carbon with V1 = 0.35 cc/fα = 97% was obtained.

該活性炭を用い実施例1と同じように抄紙、段ホール、
ハニカム・フィルターをつくす、琥珀酸中和アミノエチ
ルエタノールアミンを20重量%添着処理して実施例1
と同じ方法でアセトアルデヒドの性能評価を試みた。第
1表に結果を示す。
Using the activated carbon, paper making, corrugated holes,
Example 1 by impregnating 20% by weight of succinic acid neutralized aminoethylethanolamine to form a honeycomb filter
We attempted to evaluate the performance of acetaldehyde using the same method. Table 1 shows the results.

比較例2 実施例1で得た再生セルロース系活性炭素繊維に酢酸マ
グネジウッドを含浸・添着後900℃の水蒸気含有燃焼
ガス雰囲気で再活性化処理を施し、Vlが0.90 c
c / t αが55% の繊維状活性炭を得た。これを用いて、実施例1と同じ
ように抄紙、段ボール、ハニカム・フィルターをつくり
、琥珀酸中和アミノエチルエタノールアミンを20重値
%添着処理して実施例1と同じ方法でアセトアルデヒド
の性能評価を試みた。
Comparative Example 2 The regenerated cellulose-based activated carbon fiber obtained in Example 1 was impregnated and impregnated with acetic acid magnezwood and then subjected to reactivation treatment in a steam-containing combustion gas atmosphere at 900°C, resulting in a Vl of 0.90 c.
Fibrous activated carbon with c/t α of 55% was obtained. Using this, paper, cardboard, and honeycomb filters were made in the same manner as in Example 1, impregnated with 20% by weight of succinic acid neutralized aminoethylethanolamine, and the performance of acetaldehyde was evaluated in the same manner as in Example 1. I tried.

第1表に結果を示す。Table 1 shows the results.

実施例2 2dの7ボラツク型フエノール樹脂繊維を、水蒸気含有
不活性ガス中で400℃/hの昇温速度で900℃まで
2h、そ、の温度で保持し、活性化処理を施した。
Example 2 A 7-borac type phenolic resin fiber of 2d was activated by holding it at a temperature of 900° C. for 2 hours at a heating rate of 400° C./h in an inert gas containing water vapor.

Vlが0.80 cc / f αが95% の繊維状活性炭が得られた。これを用いて、実施例1と
同じように抄紙、段ボール、ハニカム・フィルターをつ
くり、プロピオン酸中和アミノエチルエタノールアミン
を20重値%添着処理して実施例1と同じ方法でアセト
アルデヒドの性能評価を試みた。第1表に結果を示す。
Fibrous activated carbon with a Vl of 0.80 cc/f α of 95% was obtained. Using this, paper, cardboard, and honeycomb filters were made in the same manner as in Example 1, impregnated with 20% by weight of propionic acid neutralized aminoethylethanolamine, and the performance of acetaldehyde was evaluated in the same manner as in Example 1. I tried. Table 1 shows the results.

比較例3 市販ヤシガラ活性炭 Vl = 0.30 cc / ? α=97% を粗粉砕後、ボール・ミルで平均粒径20μmに微゛粉
陸した。該活性炭素を用いて実施例1と同様に抄紙、段
ボール化後、バニカム・フィルターをつくり、プロピオ
ン酸中和アミノエチルエタノールアミンを20重値%添
着処理した後、実施例1と同様な方法でアセトアルデヒ
ドの吸収速度を測定した。結果を第1表に示す。
Comparative Example 3 Commercially available coconut shell activated carbon Vl = 0.30 cc/? After coarsely pulverizing α=97%, it was pulverized to a fine powder with an average particle size of 20 μm using a ball mill. After making paper and corrugating the activated carbon in the same manner as in Example 1, a vanicum filter was made, and after being impregnated with 20% by weight of propionic acid neutralized aminoethylethanolamine, it was processed in the same manner as in Example 1. The absorption rate of acetaldehyde was measured. The results are shown in Table 1.

比較例4 市販石炭系活性炭 V1= 0.50 cc / f α = 60 % をポール・ミルで、平均粒径20μmに微粉砕後、実施
例1と同じく、抄紙、段ボール、ハニカム・フィルター
をつくり、アミンエチル・エタノールアミンを20重1
%添着処理して、アセトアルデヒドの吸収速度を測定し
た。結果を第1表に示す0比較例5 実施例2のハニカム・フィルターに、プロピオン酸中和
トリブチルアミンを20重量%添着処理してアセトアル
デヒドの吸収速度を測定した。
Comparative Example 4 After pulverizing commercially available coal-based activated carbon V1 = 0.50 cc / f α = 60% to an average particle size of 20 μm using a pole mill, paper, cardboard, and honeycomb filters were made in the same manner as in Example 1. 20 parts of amine ethyl ethanolamine
% impregnation treatment and the absorption rate of acetaldehyde was measured. The results are shown in Table 1.0 Comparative Example 5 The honeycomb filter of Example 2 was impregnated with 20% by weight of propionic acid-neutralized tributylamine, and the absorption rate of acetaldehyde was measured.

比較例6 実施例2のハニカム・フィルターにプロピオン酸中和ト
リエタノールアミンを20重量%添着処理して、アセト
アルデヒドの吸収速度を測定した。
Comparative Example 6 The honeycomb filter of Example 2 was impregnated with 20% by weight of propionic acid-neutralized triethanolamine, and the absorption rate of acetaldehyde was measured.

実施例3 比較例3で用いた8〜14メツシユのヤシガラ活性炭を
50〜1oo5ツシユに粗粉砕し、ロータリーキルン炉
で、900℃の燃焼ガス雰囲気下5時間再賦活処理を施
し、 Vl = 0.59 cc / ? α =85 % の活性炭素を得た。
Example 3 The coconut shell activated carbon of 8 to 14 meshes used in Comparative Example 3 was coarsely ground into 50 to 105 meshes, and subjected to reactivation treatment in a rotary kiln furnace for 5 hours in a combustion gas atmosphere at 900°C, resulting in Vl = 0.59. cc/? Activated carbon with α=85% was obtained.

該活性炭をボール・ミルで平均粒径20μmに微粉砕し
た。該活性炭素を用いて、実施例1と同様にペーパー化
、段成型、ハニカム フィルター化後、酢酸でPH7に
調整したNメチルエタノールアミン水溶液に含浸、乾燥
することにより、該アミンを20重1%添着後、実施例
1と同様な方法でアセトアルデヒドの吸収速度を測定し
た。結果を第1表に示す。
The activated carbon was pulverized in a ball mill to an average particle size of 20 μm. Using the activated carbon, the activated carbon was made into paper, stage molded, and honeycomb filtered in the same manner as in Example 1, and then impregnated with an aqueous solution of N-methylethanolamine adjusted to pH 7 with acetic acid and dried to obtain 20% by weight of the amine. After impregnation, the absorption rate of acetaldehyde was measured in the same manner as in Example 1. The results are shown in Table 1.

比較例7 実1m 例、3のハニカム・フィルターにアニリンを2
0重量%添着処理して実施例1と同様にアセトアルデヒ
ドの吸収速度を測定した。結果を第1表に示す。アニリ
ンを使用する場合吸着性が経時的に著しく減少すること
がわかる。
Comparative Example 7 Actual 1 m Example, 2 aniline was applied to the honeycomb filter of 3.
The absorption rate of acetaldehyde was measured in the same manner as in Example 1 after 0% by weight impregnation treatment. The results are shown in Table 1. It can be seen that when using aniline, the adsorption properties decrease significantly over time.

比較例8 実7f[3のハニカム・フィルターにトリエチレンジア
ミン(1,4ジアザビシクロ〔2,2,2〕オクタン)
を20重1%添着処理して実施例1と同様な方法でアセ
トアルデヒドの吸収速度を測定した。
Comparative Example 8 Triethylenediamine (1,4 diazabicyclo[2,2,2]octane) in the honeycomb filter of 7F[3]
The absorption rate of acetaldehyde was measured in the same manner as in Example 1.

結果を第1表に示す。The results are shown in Table 1.

比較例9 実施例3のハニカム・フィルターにn−プロピルアミン
(20℃の蒸気圧250 +++mHf )を20重量
%添着処理して、アセトアルデヒドの吸収速度を測定し
た。結果を第1表に示す。
Comparative Example 9 The honeycomb filter of Example 3 was impregnated with 20% by weight of n-propylamine (vapor pressure 250 +++ mHf at 20°C), and the absorption rate of acetaldehyde was measured. The results are shown in Table 1.

Claims (3)

【特許請求の範囲】[Claims] (1)細孔直径a、ooX以下の細孔容積が0.4 c
c71以上で、且つ細孔直径aoX以下の細孔容積の占
める比率が80%以上の活性炭素材に20℃での蒸気圧
が10mHf以下の脂肪族系第1級アミンもしくは第2
級アミンを添着させたことを特徴とする気相中のアルデ
ヒド類の吸着剤。
(1) Pore diameter a, pore volume below ooX is 0.4 c
C71 or more, and the ratio of the pore volume of the pores having a pore diameter of aoX or less is 80% or more, and an aliphatic primary amine or a secondary
An adsorbent for aldehydes in a gas phase, characterized by impregnating a class amine.
(2) 脂肪族系アミンがエタノール系アミンである特
許請求の範囲第(1)項記載の吸着剤。
(2) The adsorbent according to claim (1), wherein the aliphatic amine is an ethanol amine.
(3)該アミンが、pKa 3.5〜5.5の弱酸で緩
衝されたものである特許請求の範囲第(1)項記載の吸
着剤。
(3) The adsorbent according to claim (1), wherein the amine is buffered with a weak acid having a pKa of 3.5 to 5.5.
JP59056516A 1984-03-23 1984-03-23 Adsorbent of aldehydes in gaseous phase Granted JPS60202735A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP59056516A JPS60202735A (en) 1984-03-23 1984-03-23 Adsorbent of aldehydes in gaseous phase

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP59056516A JPS60202735A (en) 1984-03-23 1984-03-23 Adsorbent of aldehydes in gaseous phase

Publications (2)

Publication Number Publication Date
JPS60202735A true JPS60202735A (en) 1985-10-14
JPS6324414B2 JPS6324414B2 (en) 1988-05-20

Family

ID=13029283

Family Applications (1)

Application Number Title Priority Date Filing Date
JP59056516A Granted JPS60202735A (en) 1984-03-23 1984-03-23 Adsorbent of aldehydes in gaseous phase

Country Status (1)

Country Link
JP (1) JPS60202735A (en)

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006275487A (en) * 2005-03-30 2006-10-12 Shimizu Corp Carbon dioxide removing air conditioning system
JP2008080328A (en) * 2006-08-31 2008-04-10 Toray Ind Inc Adsorbent, filtering media, and air filter
CN101890263A (en) * 2010-06-17 2010-11-24 佛山市顺德区阿波罗环保器材有限公司 Filter material for removing aldehydes
JP2012020229A (en) * 2010-07-14 2012-02-02 Kao Corp Method for manufacturing activated carbon particle
JP2014171970A (en) * 2013-03-08 2014-09-22 Japan Enviro Chemicals Ltd Adsorbent
WO2015046417A1 (en) 2013-09-27 2015-04-02 東洋紡株式会社 Aldehyde removal material
JP6471256B1 (en) * 2018-05-18 2019-02-13 ユニチカ株式会社 Deodorizing material and deodorizing sheet
JP2019198619A (en) * 2018-11-22 2019-11-21 ユニチカ株式会社 Deodorant and deodorizing sheet

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5080969A (en) * 1973-11-21 1975-07-01
JPS56113342A (en) * 1980-02-13 1981-09-07 Nippon Kasei Kk Adsorbent for lower level aldehyde

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5080969A (en) * 1973-11-21 1975-07-01
JPS56113342A (en) * 1980-02-13 1981-09-07 Nippon Kasei Kk Adsorbent for lower level aldehyde

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006275487A (en) * 2005-03-30 2006-10-12 Shimizu Corp Carbon dioxide removing air conditioning system
JP2008080328A (en) * 2006-08-31 2008-04-10 Toray Ind Inc Adsorbent, filtering media, and air filter
CN101890263A (en) * 2010-06-17 2010-11-24 佛山市顺德区阿波罗环保器材有限公司 Filter material for removing aldehydes
JP2012020229A (en) * 2010-07-14 2012-02-02 Kao Corp Method for manufacturing activated carbon particle
JP2014171970A (en) * 2013-03-08 2014-09-22 Japan Enviro Chemicals Ltd Adsorbent
WO2015046417A1 (en) 2013-09-27 2015-04-02 東洋紡株式会社 Aldehyde removal material
JP6471256B1 (en) * 2018-05-18 2019-02-13 ユニチカ株式会社 Deodorizing material and deodorizing sheet
JP2019198542A (en) * 2018-05-18 2019-11-21 ユニチカ株式会社 Deodorant and deodorizing sheet
JP2019198619A (en) * 2018-11-22 2019-11-21 ユニチカ株式会社 Deodorant and deodorizing sheet

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