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JPS6045918B2 - Tobacco smoke filter - Google Patents
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JPS6045918B2 - Tobacco smoke filter - Google Patents

Tobacco smoke filter

Info

Publication number
JPS6045918B2
JPS6045918B2 JP58133505A JP13350583A JPS6045918B2 JP S6045918 B2 JPS6045918 B2 JP S6045918B2 JP 58133505 A JP58133505 A JP 58133505A JP 13350583 A JP13350583 A JP 13350583A JP S6045918 B2 JPS6045918 B2 JP S6045918B2
Authority
JP
Japan
Prior art keywords
activated carbon
particle size
filter
basicity
pore volume
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
Application number
JP58133505A
Other languages
Japanese (ja)
Other versions
JPS6027375A (en
Inventor
昭道 玉置
伸一郎 田中
和生 前田
信男 石崎
博 清水
満州男 木戸
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 JP58133505A priority Critical patent/JPS6045918B2/en
Publication of JPS6027375A publication Critical patent/JPS6027375A/en
Publication of JPS6045918B2 publication Critical patent/JPS6045918B2/en
Expired legal-status Critical Current

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  • Cigarettes, Filters, And Manufacturing Of Filters (AREA)
  • Carbon And Carbon Compounds (AREA)

Description

【発明の詳細な説明】 本発明は改善されたたはこ煙用フィルターに関するもの
であり、さらに詳しくは植物性原料からなる強塩基性の
微粉末状活性炭を含む香喫味の改善された、たばこ煙用
フィルターに関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to an improved tobacco smoke filter, and more particularly to a tobacco smoke filter with improved flavor and flavor that contains strongly basic finely powdered activated carbon made from vegetable raw materials. This relates to smoke filters.

一般にたはこの喫煙に伴なつて発生する煙りは、粒子相
成分と蒸気相成分とに大別される。
In general, the smoke generated during smoking is roughly divided into a particle phase component and a vapor phase component.

粒子相成分はタール(テルペン類、フェノール類などの
化学成分を含む)、アルカロイド(ニコニンなど)等か
らなり、また蒸気相成分は一酸化炭素、メタン、アセト
アルデヒド、イソプレン、アセトン、トルエン等からな
るもので、これらの成分中には喫煙衛生上望ましくない
成分の含まれている。たばこ煙用フィルターは、これら
の成分を濾過あるいは吸着除去するものであり、上記粒
子相成分は主としてアセテート繊維や不織布などのフィ
ルター濾材により濾過され、一方蒸気相成分は主に、フ
ィルター中に添着または充填した活性炭により吸着除去
される。例えば、現在市販されている日本専売公社のた
ばこ製品のうち、商品名セブンスター、マイルドセブン
、ギヤピンのフィルターがこれに該当し、所謂チヤコー
ルフイルター付きたばこと称される。しかしながら、こ
のようなチヤコールフイルター付きたばこは、チヤコー
ルテイストと称する独特の好ましくない喫味を有してお
り、これがチヤコールフイルターの大きな欠点とされい
る。
Particle phase components consist of tar (including chemical components such as terpenes and phenols), alkaloids (niconicine, etc.), and vapor phase components consist of carbon monoxide, methane, acetaldehyde, isoprene, acetone, toluene, etc. These ingredients contain ingredients that are undesirable in terms of smoking hygiene. Tobacco smoke filters filter or adsorb and remove these components, and the particulate phase components are mainly filtered through filter media such as acetate fibers and nonwoven fabrics, while the vapor phase components are mainly filtered through filter media such as acetate fibers and nonwoven fabrics. It is adsorbed and removed by packed activated carbon. For example, among the tobacco products currently on the market made by Japan Monopoly Corporation, filters with the trade names Seven Star, Mild Seven, and Gear Pin fall under this category, and are called cigarettes with a charcoal filter. However, such cigarettes with a charcoal filter have a unique unpleasant taste called charcoal taste, which is considered to be a major drawback of the charcoal filter.

これまでに、活性炭含有たばこフィルターのたばこの喫
味に及ぼす前述の好ましくない影響を改・善する目的で
種々の試みがなされており、例えは、活性炭に酸性基を
有する多孔性合成吸着剤を含有させる手段(特開昭53
−10740吟公報)、該活性炭にタンニン酸金属キレ
ート化合物を含有される手段(特開昭53−88300
吟公報)、含窒素活フ性化炭素繊維を利用する手段(特
開昭53−88400号公報)等が提案されている。し
かし、これらの技術手段では、たばこ煙中の特定の好ま
しくない成分だけを選択的に吸着除去する効果という観
点からみると充分とは言えない。即ちこれらのフィルタ
ー付きたばこは、喫煙時に好ましい香喫味成分をも除去
する欠点を有している。本発明者等は、たばこ煙中の刺
激性物質例えば、ホルムアルデヒド、アセトアルデヒド
、蟻酸、酢酸、シアン化水素等の化合物を効率よく除去
し得る活性炭フィルターの開発を目的として研究を行つ
ていたところ、前述のチヤコールテイストは刺激性物質
相互の煙中における存在比と関係が深いこと、そして意
外にも、たばこフィルターに含有させる活性炭の原材料
、細孔径、粒度、塩基性度からなる要因を適宜に選択す
ることにより、チヤコールテイストを抑制し、香喫味の
改善されたたばこ煙用フィルターを得ることに成功し、
本発明をなすに至つた。
To date, various attempts have been made to improve the aforementioned unfavorable effects of activated carbon-containing cigarette filters on the smoking taste of cigarettes. Means to cause
-10740 Gin Publication), means for containing a tannic acid metal chelate compound in the activated carbon (Japanese Patent Application Laid-open No. 53-88300)
(Japanese Unexamined Patent Application Publication No. 1988-88400) and the like have been proposed. However, these technical means cannot be said to be sufficient from the viewpoint of the effect of selectively adsorbing and removing only specific undesirable components in tobacco smoke. That is, these filter-tipped cigarettes have the disadvantage that they also remove desirable flavor components during smoking. The present inventors were conducting research with the aim of developing an activated carbon filter that can efficiently remove irritating substances in tobacco smoke, such as formaldehyde, acetaldehyde, formic acid, acetic acid, hydrogen cyanide, etc. Charcoal taste is closely related to the abundance ratio of irritating substances in smoke, and surprisingly, factors such as raw materials, pore size, particle size, and basicity of activated carbon to be included in cigarette filters are selected appropriately. As a result, we succeeded in obtaining a cigarette smoke filter that suppresses the charcoal taste and improves the aroma and taste.
The present invention has now been accomplished.

即ち、本発明は、植物性原料からなり、塩基性度がPH
9以上で、細孔直径20A以下の細孔容積が0.10c
c/ダ以上、且つ30μm以下の超微粉末活性炭を含有
してなる香喫味の改良された、たばこ煙用フィルターに
関する。従来の活性炭は、比較的大きい表面活性を有す
るものがあるものの塩基性度が小さく、アセトアルデヒ
ド等の刺激性蒸気相成分の吸着能が低く、従来フィルタ
ーの問題点を改善するに至つていなかつた。
That is, the present invention is made of vegetable raw materials and has a basicity of PH
9 or more, and the pore volume with a pore diameter of 20A or less is 0.10c
The present invention relates to a filter for tobacco smoke with improved flavor and flavor, which contains ultrafine powdered activated carbon with a particle size of c/d or more and 30 μm or less. Although some conventional activated carbons have relatively high surface activity, they have low basicity and have a low adsorption capacity for irritating vapor phase components such as acetaldehyde, so they have not been able to improve the problems of conventional filters. .

本発明によれば、たばこ煙用フィルター中に、植物性原
料からなり、塩基性度がPH9以上て、細孔直径20A
以下の細孔容積が0.10cc/q以上、且つ平均粒径
か30pm以下の超微粉末活性炭を含有させることによ
つて、香喫味の改善が達成.できる。以下、本発明を詳
細に説明する。ます、本発明に係る活性炭は植物性原料
より製造することが必須である。
According to the present invention, a tobacco smoke filter is made of vegetable raw materials, has a basicity of PH9 or more, and has a pore diameter of 20A.
By incorporating ultrafine powdered activated carbon with a pore volume of 0.10 cc/q or more and an average particle size of 30 pm or less, the aroma and taste can be improved. can. The present invention will be explained in detail below. First, it is essential that the activated carbon according to the present invention be produced from vegetable raw materials.

かかる植物性原料としては、木材(好ましくは針葉樹系
);ヤシガラ、パームガラ、コイヤダストの如き南洋植
物;イピール、タカクテイーの如き豆料植物;木材バル
ブ、木綿、リンダーパルプ等が用いられる。他のピッチ
、石炭、石油スラッジのような鉱物質系又はポリアクリ
ロニトリル繊維、フェノール樹脂のような合成系の原料
からも活性炭は製造されてい・るが、これを使用したフ
ィルターでの喫味は、上記植物原料よりはるかに劣り好
ましくない。植物性原料を用いて平均粒径30pm以下
という超微粉末状活性炭をつくるには、例えば次のよう
な方法がある。針葉樹系の木材を粉砕機により200〜
2000pmの粒度になるように粉砕する。
As such vegetable raw materials, wood (preferably coniferous); South Sea plants such as coconut husk, palm husk, and coir dust; leguminous plants such as Ipir and Takakutei; wood bulbs, cotton, and linder pulp are used. Activated carbon is also manufactured from mineral materials such as pitch, coal, petroleum sludge, or synthetic materials such as polyacrylonitrile fibers and phenolic resin, but the taste of filters using these materials is as follows. It is much inferior to plant materials and is not preferred. For example, the following method can be used to produce ultrafine activated carbon powder with an average particle size of 30 pm or less using vegetable raw materials. Coniferous wood is crushed by a crusher to 200~
Grind to a particle size of 2000pm.

その後平炉で20〜(4)時間かけて室温より500℃
迄昇温して炭化処理を行ない粒径100〜1000pm
1炭素含有率70%の炭化物を得る。該炭化物を空気移
送型の流動賦活炉により1200〜1300℃で数秒間
賦活処理を施す。かかる賦活処理は通常の活性炭の賦活
処理では考え及ばない高温であり、しかも後述する如く
反応)性の高い木質系の原料を炭酸ガス、水蒸気等の活
性ガス中で賦活処理するため、多数に塩基性基が活性炭
表面に生成するものと思われる。生成機構については明
らかではないが、炭酸ガス賦活による0H基、キノン基
の生成と推察される。また、−別法としてヤシガラ活性
炭を900℃以上の高温で長時間再賦活することによつ
ても得られる。再賦活雰囲気としては、水蒸気の他に濃
度の高い炭酸ガスが好ましい。活性炭は上述の方法で製
造されるが、たばこフィルターとして採用するためには
その平均粒径(以下単に“粒径゛と記したものは平均粒
径を意味する)が30μmを超えるといくら塩基性度が
高くても吸着成分間のバランスに起因するチヤコールテ
イストの除去、抑制を行うことは難かしい。微粉砕化処
理は、50〜100μmに粗粉砕された活性炭をボール
ミル等で長時間、粉砕処理することによりなされる。な
お、活性炭の細孔直径は20A以下で細孔の容積(以下
ミクロボア細孔容積と略称する)は0.10cc/y以
上であることが必須である。即ち、ミクロボア細孔容積
が0.10cc/qに満ない場合はイソプレン、アセト
ン、アセトアルデヒド等の蒸気相成分の吸着が有効にな
されず喫煙衛生上または、香喫味上望ましくない。この
ようにして得られた活性炭の塩基性度は、フィリップ法
に準する方法、つまりPH7に調製した0.1NKC1
水溶液100m1中に活性炭0.1yを投入し、2肴間
振とうした後PHメーターて液のPHを測定することに
より求める(例えば工業化学雑誌67、2019(19
64))。上記方法で求められる塩基性度は、水溶液中
のC1−イオンによつてイオン交換された0H−イオン
の量を評価しているものと推察される。また、平均粒径
は訂数原理による粒度測定法の一つであるコールターカ
ウンター法(例えば粉体光学研究会編1粉体粒度測定法
ョ)により測定したものである。さらに活性炭の細孔直
径及び細孔容積は、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温線を用いて
、クランストンーインクレー(CranstOn−1n
k1ey)の計算法(例えば慶伊富長7吸着ョ共立出版
)により求めた。
After that, it is heated to 500℃ from room temperature in an open hearth for 20 to (4) hours.
Carbonization treatment is carried out by raising the temperature to a temperature of 100 to 1000 pm.
A carbide with a carbon content of 70% is obtained. The carbide is subjected to activation treatment at 1200 to 1300° C. for several seconds in an air transfer type fluidized activation furnace. This activation treatment involves a high temperature that would be unimaginable for ordinary activated carbon activation treatment, and as will be described later, since the highly reactive wood-based raw material is activated in an active gas such as carbon dioxide gas or water vapor, many bases are used. It is thought that functional groups are generated on the surface of activated carbon. Although the formation mechanism is not clear, it is presumed that OH groups and quinone groups are generated by carbon dioxide activation. Alternatively, it can also be obtained by reactivating coconut shell activated carbon at a high temperature of 900° C. or higher for a long period of time. In addition to water vapor, highly concentrated carbon dioxide gas is preferable as the reactivation atmosphere. Activated carbon is produced by the method described above, but in order to be used as a cigarette filter, if its average particle size (hereinafter simply referred to as "particle size" means average particle size) exceeds 30 μm, it must be basic enough. Even if the carbon content is high, it is difficult to remove or suppress the charcoal taste caused by the balance between adsorbed components.The fine pulverization process involves pulverizing activated carbon coarsely pulverized to 50 to 100 μm in a ball mill or the like for a long time. It is essential that the activated carbon has a pore diameter of 20 A or less and a pore volume (hereinafter referred to as micropore pore volume) of 0.10 cc/y or more. If the pore volume is less than 0.10 cc/q, vapor phase components such as isoprene, acetone, acetaldehyde, etc. will not be effectively adsorbed, which is undesirable from the standpoint of smoking hygiene or flavor.The activated carbon thus obtained The basicity of
It is determined by adding 0.1 y of activated carbon into 100 ml of aqueous solution, shaking for 2 minutes, and then measuring the pH of the liquid with a PH meter (for example, Industrial Chemistry Magazine 67, 2019 (19
64)). It is presumed that the basicity determined by the above method evaluates the amount of OH- ions ion-exchanged by C1- ions in the aqueous solution. Further, the average particle size was measured by the Coulter counter method, which is one of the particle size measurement methods based on the correction principle (for example, Powder Particle Size Measurement Method, 1, edited by Powder Optics Study Group). Furthermore, the pore diameter and pore volume of activated carbon are the boiling point of liquid nitrogen under normal pressure (-195
.. Using the nitrogen gas adsorption isotherm on the adsorption side at
k1ey) calculation method (for example, Kei Tominaga 7 adsorption method Kyoritsu Shuppan).

但し、細孔直径300A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
84×10−3)を乗じた値を全細孔容積とみなし、ま
た、細孔直径300Aから20八までの累積細孔容積か
ら差し引いた値を細孔直径容積と1した。このようにし
て得た活性炭をフィルターとするには、アセテート繊維
のトウにまぶし、これと別のアセテート繊維単独部分と
を組合せる方法、木材バルブ繊維、アセテート繊維等と
混合し不織布1状に成形する方法、接着剤と共に不織布
あるいはトウに吹きつけ散布付着せしめる方法、アルギ
ン酸ソーダのような高粘性の溶液を与える接着性高分子
を含有した分散媒に分散させペースト状の添着液を作り
、ローラー捺染等印刷、染色等で用い二られる印捺法で
不織布状に印捺する方法、カルボキシメチルセルローズ
、ポリビニルアルコールのようなバインダーを用い細粒
状化して、アセテート繊維トウ間に介在させる方法など
がある。
However, the ratio (1.5
The value multiplied by 84 x 10-3) was regarded as the total pore volume, and the value subtracted from the cumulative pore volume of pore diameters from 300A to 208A was defined as the pore diameter volume. The activated carbon thus obtained can be used as a filter by sprinkling it on a tow of acetate fibers, combining it with another single piece of acetate fiber, or by mixing it with wood valve fibers, acetate fibers, etc. and forming it into a nonwoven fabric. A method of spraying and adhering it to a nonwoven fabric or tow together with an adhesive, a method of dispersing it in a dispersion medium containing an adhesive polymer such as sodium alginate that provides a highly viscous solution, and creating a paste-like impregnating liquid, and roller printing. Examples include a method of printing on a nonwoven fabric using a printing method used in printing, dyeing, etc., and a method of forming fine particles using a binder such as carboxymethyl cellulose or polyvinyl alcohol and interposing them between acetate fiber tows.

この際活性炭の使用量はフィルター1本当り15〜10
0;Mgが好適である。このように本発明の活性炭が、
アセトアルデヒド、ホルムアルデヒド、シアン系ガス等
を特異的に吸着除去する理由については明らかではない
が、粒径が小さいことによる活性表面の増大及び.塩基
性度の大きい塩基量の増加とが、アセトアルデヒド等と
の反応に相乗的に作用したためであると推測される。
At this time, the amount of activated carbon used is 15 to 10 per filter.
0; Mg is preferred. In this way, the activated carbon of the present invention
The reason why acetaldehyde, formaldehyde, cyanide gas, etc. are specifically adsorbed and removed is not clear, but the reason is that the active surface increases due to the small particle size and... It is presumed that this is because the increase in the amount of base with high basicity acted synergistically on the reaction with acetaldehyde and the like.

香喫味の改良については高い塩基性度、超微粉末の選択
による刺激性蒸気相成分の除去ないしか抑制に加えて、
植物性原料を出発原料に選択している点も寄与するとこ
ろ大である。アクリロニトリル系活性炭素繊維、フェノ
ール樹脂系活性炭などの合成原料からの活性炭もたばこ
煙用フィルターとして検討されてきてはいるが、香喫味
が良くない不都合が内在するため、たばこフィルターと
して実用化はなされていない。このように本発明に係わ
る活性炭は、イソプレン、アセトンの吸着性は従来の活
性炭と同程度である上にアセトアルデヒド、ホルムアル
デヒド、シアン系ガス等刺激性蒸気相成分に対して特異
的”こ多量の吸着性を有するものであるため、従来のチ
ヤコールフイルターの欠点を改良することができる。次
に実験例を挙げて本発明の特徴を明確にする。
In order to improve the aroma and taste, in addition to the removal or suppression of irritating vapor phase components through the selection of high basicity and ultra-fine powder,
The fact that plant-based raw materials are selected as starting materials also contributes greatly. Activated carbon made from synthetic raw materials such as acrylonitrile-based activated carbon fiber and phenolic resin-based activated carbon has been considered as a filter for cigarette smoke, but it has not been put to practical use as a cigarette filter due to the inherent disadvantage that it does not have a good aroma or taste. do not have. As described above, the activated carbon according to the present invention has adsorption properties for isoprene and acetone that are comparable to those of conventional activated carbon, and also has specific adsorption properties for irritating vapor phase components such as acetaldehyde, formaldehyde, and cyanide gas. Therefore, the drawbacks of conventional charcoal filters can be improved.Next, experimental examples will be given to clarify the characteristics of the present invention.

夷験例1 用いる活性炭は次の様に製造した。Experimental example 1 The activated carbon used was manufactured as follows.

(1)木質原料 粒度が200〜2000pm針葉樹系木材屑。(1) Wood raw materials Coniferous wood waste with a particle size of 200 to 2000 pm.

(2)炭化処理該木材屑を、平炉で一昼夜200から5
00℃に昇温、加熱することにより、収率30%で炭素
含有70%の、粒径が100〜1000μmの炭化物を
得た。
(2) Carbonization process The wood chips are heated in an open hearth for a day and a night at 200 to 50% carbonization.
By raising the temperature to 00° C. and heating, a carbide having a yield of 30%, a carbon content of 70%, and a particle size of 100 to 1000 μm was obtained.

(3)賦活処理 イ 該炭化物を流動賦活炉で滞留時間w秒、温度120
0〜1300℃、水蒸気10%含有雰囲気で処理し、粒
径30〜200pmの活性炭を得た。
(3) Activation treatment a The carbide is placed in a fluidized activation furnace for a residence time of w seconds and a temperature of 120
Activated carbon having a particle size of 30 to 200 pm was obtained by treatment at 0 to 1300°C in an atmosphere containing 10% water vapor.

該活性炭をボールミルで2楊間粉砕処理することにより
、粒径15μm1ミクロボア細孔容積0.38cc/y
の活性炭を得た。(サンプル名:1−a) また、粉砕
処理前の活性炭をふるい分けすることにより、粒径50
pm1塩基性度PH9.7、ミクロボア細孔容積0.3
6cc/yの活性炭を得た。
By pulverizing the activated carbon for 2 millimeters in a ball mill, the particle size was 15 μm and the pore volume of 1 microbore was 0.38 cc/y.
of activated carbon was obtained. (Sample name: 1-a) In addition, by sieving the activated carbon before pulverization, the particle size of 50
pm1 basicity PH9.7, micropore pore volume 0.3
6 cc/y of activated carbon was obtained.

(サンプル名:1−b)口 滞留時間5秒、温度120
0〜1300′C1水蒸気10%含有雰囲気で処理し、
粒径30〜300pmの活性炭を得た。
(Sample name: 1-b) Mouth Residence time 5 seconds, temperature 120
0~1300'C1 Treated in an atmosphere containing 10% water vapor,
Activated carbon with a particle size of 30 to 300 pm was obtained.

該活性炭をボールミルで24時間粉砕処理することによ
り、粒径18μm1塩基性度PH9.7、ミクロボア細
孔容積0.32cc/yの活性炭を得た。(サンプル名
:1−c)ハ 滞留時間2囲2、温度1000℃、水蒸
気10%含有雰囲気で処理し、粒径30〜200pmの
活性炭を得た。
The activated carbon was pulverized in a ball mill for 24 hours to obtain activated carbon having a particle size of 18 μm, a basicity of PH 9.7, and a micropore pore volume of 0.32 cc/y. (Sample name: 1-c) C. Activated carbon having a particle size of 30 to 200 pm was obtained by treatment in an atmosphere containing 10% water vapor for a residence time of 2.2 pm and a temperature of 1000°C.

該活性炭をボールミルで粉砕処理を施すことにより、粒
径15μm、塩基性度PH9.7、ミクロボア細孔容積
0.34cc/fの活性炭を得た。(サンプル名:1−
d)実験例2 市販の8〜14メッシュのヤシガラ活性炭(塩基性度P
H7、比表面積600ボ/y)を150〜300pmに
粉砕し、ロータリー・キルン炉により、900′Cて燃
焼ガス雰囲気下5時間再賦活処理を施した。
The activated carbon was pulverized with a ball mill to obtain activated carbon having a particle size of 15 μm, basicity of pH 9.7, and micropore pore volume of 0.34 cc/f. (Sample name: 1-
d) Experimental Example 2 Commercially available 8-14 mesh coconut shell activated carbon (basicity P
H7 (specific surface area: 600 bo/y) was pulverized to 150-300 pm, and reactivated in a rotary kiln at 900'C in a combustion gas atmosphere for 5 hours.

該活性炭をボールミルで10叫間粉砕処理を施すことに
より、粒径15μm、塩基性度PH9.5sミクロボア
細孔容積0.4cc/yの活性炭を得た。(サンプル名
:2−a)また、ボールミル粉砕処理5時間後の活性炭
を、ふるい分けすることにより粒径45μm1塩基性度
PH9.&ミクロボア細孔容積0.39cc/yの活性
炭を得た。(サンプル名:2−b)さらに該市販ヤシガ
ラ活性炭をボールミル粉砕処理を施すことにより粒径1
5μm1塩基性度PH7、ミクロボア細孔容積0.35
cc/9の活性炭を得た。
The activated carbon was pulverized for 10 minutes in a ball mill to obtain activated carbon having a particle size of 15 μm, a basicity of PH 9.5, and a micropore pore volume of 0.4 cc/y. (Sample name: 2-a) Furthermore, the activated carbon after 5 hours of ball mill pulverization was sieved to obtain particle size of 45 μm, basicity of PH 9. & Activated carbon with a micropore pore volume of 0.39 cc/y was obtained. (Sample name: 2-b) Furthermore, by subjecting the commercially available coconut shell activated carbon to ball mill pulverization treatment, the particle size was 1.
5μm1 basicity PH7, micropore pore volume 0.35
Activated carbon of cc/9 was obtained.

(サンプル名:2−c)実験例3 粒度200〜2000pmの針葉樹系木材屑を、50重
量%の塩化亜鉛水溶液と混合し、多段床炉で700℃ま
で昇温加熱することにより、炭化、賦活処理を施した後
、塩酸水溶液で洗浄し、ボールミル粉砕処理を行なつて
、塩基性度PH5.3、ミクロボア細孔容積0.15c
c/y、粒径15μmの活性炭を得5た。
(Sample name: 2-c) Experimental example 3 Coniferous wood chips with a particle size of 200 to 2000 pm were mixed with a 50% by weight zinc chloride aqueous solution and heated to 700°C in a multi-stage bed furnace to carbonize and activate the mixture. After the treatment, it is washed with an aqueous hydrochloric acid solution and pulverized in a ball mill to obtain a basicity of PH5.3 and a micropore pore volume of 0.15c.
Activated carbon with c/y and particle size of 15 μm was obtained.

(サンプル名:3−a)また、該活性炭をさらにアンモ
ニアガス含有空気流中で、700℃て処理することによ
り、粒径15μm1塩基性度PH9.\ ミクロボア細
孔容積0.08cc/yの活性炭を得た。
(Sample name: 3-a) Furthermore, by further treating the activated carbon in an air stream containing ammonia gas at 700°C, the particle size was 15 μm, the basicity was 9. \ Activated carbon with a micropore pore volume of 0.08 cc/y was obtained.

(サンプル名:3−b)2実験例4市販ポリアクリロニ
トリル繊維を300℃の空気中耐炎化処理を施した後、
850゜Cの水蒸気含有雰気下て賦活処理を行ない、繊
維状活性炭を得た後、ボールミル粉砕処理を施し、粒径
15μm、塩3基性度PH9.3、ミクロボア細孔容積
0.25cc/gの活性炭を得た。
(Sample name: 3-b) 2 Experimental example 4 After subjecting commercially available polyacrylonitrile fibers to flame resistance treatment in air at 300°C,
Activation treatment was performed in a steam-containing atmosphere at 850°C to obtain fibrous activated carbon, which was then subjected to ball mill pulverization treatment to obtain a product with a particle size of 15 μm, salt tribasicity PH of 9.3, and micropore pore volume of 0.25 cc/ g of activated carbon was obtained.

(サンプル名:4)実験例5 市販ノボラック型フェノール樹脂繊維を、900℃の水
蒸気含有雰囲気下で炭化処理をおこない繊3維状活性炭
を得た後、ボールミル粉砕処理を施し、粒径15μm、
塩基性度PH9.2、ミクロボア細孔容積0.45cc
/yの活性炭を得た。
(Sample name: 4) Experimental example 5 Commercially available novolak type phenolic resin fibers were carbonized in a steam-containing atmosphere at 900°C to obtain Fiber 3 fibrous activated carbon, which was then pulverized in a ball mill to obtain particles with a particle size of 15 μm and
Basicity PH9.2, Micropore pore volume 0.45cc
/y of activated carbon was obtained.

(サンプル名:5)以上の実験例で得た活性炭を用いて
以上の如き4手段でたばこ煙用フィルターを作製した。
(Sample name: 5) Using the activated carbon obtained in the above experimental example, a cigarette smoke filter was produced by the above four methods.

即ち、活性炭15部をアルギン酸ソーダー水溶液m部に
散布し、均一なペーストを作つた後、木材バルブからな
る乾式不織布(目付40y/d1厚み2.2薗)にロー
ラー捺染機で、プリント処理を施し、活性炭を30mg
/イ添着したシートを得た。該シートを4枚使用し、4
枚のしまの柄が一致するように並べて送り、これをS字
型あるいはz字型に折り曲げた後、回転する内径先細に
なつたローターにより、より合せ、さらに絞ることとに
よつて円筒状に巻き上げ直径8w0nの円筒をつくつj
た。
That is, 15 parts of activated carbon was sprinkled on m parts of an aqueous solution of sodium alginate to make a uniform paste, and then a dry non-woven fabric made of wood bulbs (fabric weight 40y/d1 thickness 2.2m) was printed using a roller printing machine. , 30mg of activated carbon
/A attached sheet was obtained. Use 4 sheets, 4
The sheets are fed side by side so that the striped patterns match, and after being bent into an S-shape or Z-shape, they are twisted by a rotating rotor with a tapered inner diameter and further squeezed into a cylindrical shape. Roll up to make a cylinder with a diameter of 8w0n.
Ta.

この円筒の外側に薄い紙を巻きつけた後、長さ1071
77!の活性炭添着フィルターを得た。該フィルターを
長さ7T!Unのアセテート繊維フィルターと接合し、
長さ17mmのたばこ煙用フィルターを試製した。以上
の様に試製した各種たばこ煙用フィルターについて、蒸
気相成分としてシアン系ガス、アセトアルデヒド、イソ
プレン及びアセトンの吸着率をそれぞれ測定した結果を
第1表に示す。
After wrapping a thin paper around the outside of this cylinder, the length is 1071
77! An activated carbon impregnated filter was obtained. The length of this filter is 7T! Combined with Un's acetate fiber filter,
A cigarette smoke filter with a length of 17 mm was manufactured as a trial product. Table 1 shows the results of measuring the adsorption rates of cyan gas, acetaldehyde, isoprene, and acetone as vapor phase components for the various cigarette smoke filters trial-produced as described above.

なお吸着率は次のようにして求めた。即ち、上記方法に
より試製したフィルターを日本専売公社製品し)イライ
トョからフィルター部分を取除いた部分に操合したもの
を供試たばことし、同じし)イライトョをコントロール
として、定流量型自動喫煙器を用い、次の条件で吸煙さ
せた。
The adsorption rate was determined as follows. That is, a filter manufactured by the above method was manufactured by Japan Monopoly Corporation, and a test cigarette was prepared by removing the filter part from Iraito. It was used and smoked under the following conditions.

流量: 17.5m1/Sec 吸煙時間:2sec/回 吸煙頻度:1回/Min 燃焼長: 50Tf$t 吸煙本数:4本/極細ガラス繊維フィルターアセトアル
デヒド、イソプレン、アセトンの吸着率は、極細ガラス
繊維フィルターを通過した8パフ分の煙のうち1.95
mtをガスクロマトグフイーに導入し、コントロールの
ピーク高さをHsとし、次式により吸着率(F)を求め
た。
Flow rate: 17.5m1/Sec Smoking time: 2sec/times Smoking frequency: 1 time/Min Combustion length: 50Tf$t Number of smokes: 4/Ultra-fine glass fiber filter The adsorption rates of acetaldehyde, isoprene, and acetone are as follows: Extra-fine glass fiber filter 1.95 out of 8 puffs of smoke passed through
mt was introduced into a gas chromatograph, the peak height of the control was set as Hs, and the adsorption rate (F) was determined using the following formula.

F(%)=(H−Hs)/H×100 また、シアン系ガス吸着率は、極細ガラス繊維フィルタ
ーに捕集されたタール及び0.5N(7)NaOH溶液
に吸収されたガス吸収液を蒸留後、比色法によりCN一
量を求めた。
F (%) = (H-Hs)/H x 100 In addition, the cyanide gas adsorption rate is based on the tar collected on the ultrafine glass fiber filter and the gas absorption liquid absorbed in the 0.5N (7) NaOH solution. After distillation, the amount of CN was determined by a colorimetric method.

(例えば、日本公衆衛生学会誌28、100(1981
)第1表の結果より次の様に考案することができる。
(For example, Journal of the Japanese Society of Public Health 28, 100 (1981
) From the results in Table 1, the following can be devised.

(1)サンプル名(1−b)及ひ(2−b)は何れも植
物原料からなるもので、塩基性度及びミクロボア細孔容
積は適正であるが、粒径が大きすぎる為アセトアルデヒ
ド及びシアン系ガスの吸着率が低い。
(1) Sample names (1-b) and (2-b) are both made from plant materials, and have appropriate basicity and micropore volume, but the particle size is too large, so acetaldehyde and cyanogen Adsorption rate of system gas is low.

(2)サンプル名(1−d)、(2−c)及び(3一a
)は何れも植物原料からなり、粒径及びミクロボア細孔
容積も適正であるが、塩基性度が低すぎる為、(1−d
)及ひ(2−c)は全体的に吸着率が低く、又(3−a
)ではアセトアルデヒド及びシアン系ガスの吸着率が極
端に低く、何れも目的を達成することができない。
(2) Sample names (1-d), (2-c) and (3-a
) are all made from plant materials and have appropriate particle size and micropore pore volume, but their basicity is too low, so (1-d
) and (2-c) have low adsorption rates overall, and (3-a)
), the adsorption rate of acetaldehyde and cyanide gas is extremely low, and neither of them can achieve the objective.

(3) サンプル名(3−b)は植物原料からなり、粒
径及び塩基性度共に適正であるが、ミクロボア細孔容積
が少なすぎる為アセトアルデヒド及びシアン系ガスの吸
着率が極端に低い。1) これらに対しサンプル名(1
−a)、(1−c)及ひ(2−b)は本発明の規定要件
をすべて満足するもので、たばこ煙中の主成分てあるア
セトアルデヒド、イソプレン、アセトン及びシアン系ガ
スの吸着率は従来品に比べていずれも著しく優れており
、且つ各吸着成分がバランスよく除去されている為、チ
ヤコールテイストの発現もなかつた。
(3) Sample name (3-b) is made of plant material and has appropriate particle size and basicity, but the adsorption rate of acetaldehyde and cyanide gas is extremely low because the micropore volume is too small. 1) Sample name (1)
-a), (1-c), and (2-b) satisfy all the specified requirements of the present invention, and the adsorption rate of acetaldehyde, isoprene, acetone, and cyanide gas, which are the main components in tobacco smoke, is All products were significantly superior to conventional products, and since each adsorbed component was removed in a well-balanced manner, no charcoal taste was observed.

Claims (1)

【特許請求の範囲】[Claims] 1 植物性原料からなり、塩基性度がpH9以上で、細
孔直径20Å以下の細孔容積が0.10cc/g以上、
且つ平均粒径が30μm以下の超微粉末活性炭を含有し
てなる香喫味の改良された、たばこ煙用フィルター。
1 Made of vegetable raw material, basicity is pH 9 or more, pore volume is 0.10 cc/g or more with a pore diameter of 20 Å or less,
A filter for tobacco smoke with improved flavor and aroma, which contains ultrafine powdered activated carbon having an average particle size of 30 μm or less.
JP58133505A 1983-07-21 1983-07-21 Tobacco smoke filter Expired JPS6045918B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP58133505A JPS6045918B2 (en) 1983-07-21 1983-07-21 Tobacco smoke filter

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP58133505A JPS6045918B2 (en) 1983-07-21 1983-07-21 Tobacco smoke filter

Publications (2)

Publication Number Publication Date
JPS6027375A JPS6027375A (en) 1985-02-12
JPS6045918B2 true JPS6045918B2 (en) 1985-10-12

Family

ID=15106335

Family Applications (1)

Application Number Title Priority Date Filing Date
JP58133505A Expired JPS6045918B2 (en) 1983-07-21 1983-07-21 Tobacco smoke filter

Country Status (1)

Country Link
JP (1) JPS6045918B2 (en)

Families Citing this family (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS61222916A (en) * 1985-03-29 1986-10-03 Kanebo Ltd Porous activated carbon
GB0019417D0 (en) 2000-08-09 2000-09-27 Mat & Separations Tech Int Ltd Mesoporous carbons
US8591855B2 (en) 2000-08-09 2013-11-26 British American Tobacco (Investments) Limited Porous carbons
GB2395650B (en) * 2002-11-27 2005-09-07 Filtrona Int Ltd Tobacco smoke filter
GB0506278D0 (en) 2005-03-29 2005-05-04 British American Tobacco Co Porous carbon materials and smoking articles and smoke filters therefor incorporating such materials

Also Published As

Publication number Publication date
JPS6027375A (en) 1985-02-12

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