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JPS6027375A - Tobacco filter - Google Patents

Tobacco filter

Info

Publication number
JPS6027375A
JPS6027375A JP58133505A JP13350583A JPS6027375A JP S6027375 A JPS6027375 A JP S6027375A JP 58133505 A JP58133505 A JP 58133505A JP 13350583 A JP13350583 A JP 13350583A JP S6027375 A JPS6027375 A JP S6027375A
Authority
JP
Japan
Prior art keywords
activated carbon
particle size
filter
acetaldehyde
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.)
Granted
Application number
JP58133505A
Other languages
Japanese (ja)
Other versions
JPS6045918B2 (en
Inventor
玉置 昭道
伸一郎 田中
和生 前田
石崎 信男
博 清水
木戸 満州男
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.)
Japan Tobacco Inc
Toyobo Co Ltd
Original Assignee
Toyobo Co Ltd
Japan Tobacco and Salt Public Corp
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, Japan Tobacco and Salt Public Corp 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)

Abstract

(57)【要約】本公報は電子出願前の出願データであるた
め要約のデータは記録されません。
(57) [Summary] This bulletin contains application data before electronic filing, so abstract data is not recorded.

Description

【発明の詳細な説明】 本発明は改善されたたば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 filter for tobacco smoke, and more particularly to a filter for tobacco smoke that has improved flavor and flavor and contains strongly basic finely powdered activated carbon made from vegetable raw materials. It's about filters.

一般にたばこの喫煙に伴なって発生する煙りは、粒子相
成分と蒸気相成分とに大別される。粒子相成分はタール
(テルペン類、フェノール類なとの化学成分を含む)、
アルカロイドにコニンなど)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。
Generally, the smoke generated by smoking cigarettes is roughly divided into particle phase components and vapor phase components. The particle phase components are tar (including chemical components such as terpenes and phenols),
The vapor phase components include carbon monoxide, methane, acetaldehyde, isoprene, acetone, toluene, etc., and these components contain components that are undesirable in terms of smoking hygiene. .

たばこ煙用フィルターは、これらの成分を症過あるいは
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mraや不織布などのフィルター喧材により
癌過され、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、キャビンのフィ
ルターがこれに該当し、所謂チャコールフィルター付き
たばこと称される。
Cigarette smoke filters remove these components by absorption or adsorption.The above particle-phase components are mainly filtered through filter materials such as acetate MRA and nonwoven fabric, while vapor-phase components are mainly filtered through the filter. It is adsorbed and removed by activated carbon attached or filled inside. for example,
Of the tobacco products currently available on the market from Japan Monopoly Corporation,
Filters under the product names Seven Star, Mild Seven, and Cabin fall under this category, and are called cigarettes with charcoal filters.

しかLながら、このようなチャコールフィルター付きた
ばこは、チャコールティストと称する独特の好ましくな
い喫味を有しており、これがチャコールフィルターの大
きな欠点とされいる。
However, such charcoal-filtered cigarettes have a unique unpleasant smoking taste called charcoal taste, which is considered to be a major drawback of charcoal filters.

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哲を改善する目的で種
々の試みがなされており、例えば、活性炭に酪性基を宥
する多孔性合成吸着剤を含有させる手段(特開昭53−
107489号公報)、該活性炭にタンニン酎金属キレ
ート化合物を含有させる手段(特開昭53−99399
9号公報)、含窒素活性化i5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。
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 for causing
No. 107489), a means for incorporating a tannin and metal chelate compound into the activated carbon (Japanese Unexamined Patent Publication No. 53-99399)
9), means using nitrogen-containing activated i5 fibers (
Japanese Unexamined Patent Publication No. 53-88400) and the like have been proposed.

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。
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.

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、耐酸、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っていたところ、前述のチ
ャコールティ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、塩基仕
度からなる要因を適宜に選択することにより、チャコー
ルティストを抑制し、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、本発明をなすに至った。
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, acid resistance, and hydrogen cyanide. Tist is closely related to the abundance ratio of irritating substances in smoke, and surprisingly, by appropriately selecting factors such as raw materials, pore size, particle size, and base preparation of activated carbon to be included in cigarette filters, We have succeeded in obtaining a filter for tobacco smoke that suppresses charcoal tint and has improved aroma and taste, leading to the present invention.

即ち、本発明は、植物性原料からなり、塩基仕度がPH
9以上で、細孔直径が20人以下の細孔容積が0 、1
0cc/g以上、且つ30μm以卜゛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。
That is, the present invention is made of vegetable raw materials and has a base condition of PH.
9 or more, pore diameter is 20 or less, pore volume is 0, 1
The aroma and taste of the smoker is improved by containing ultrafine powder activated carbon of 0 cc/g or more and 30 μm or more. Regarding tobacco smoke filters.

従来の活性炭は、比較的大きい表面活性を有するものが
あるものの塩基仕度が小さく、アセトアルデヒド等の刺
激性7A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っていなかった。本発明によれば、
たばこ煙雨フィルター中に、植物性原料からなり、塩基
仕度がpH9以上で、細孔直径20Å以下の細孔容積が
0. l0cc/g以上、且つ平均粒径が301Lm以
下の超微粉末活性炭を含有させることによって、香喫味
の改善が達成できる。以下、本発明の詳細な説明する。
Although some conventional activated carbons have relatively high surface activity, they have a low basicity and have a low adsorption capacity for irritating 7A gas phase components such as acetaldehyde, and have not been able to improve the problems of conventional filters. According to the invention,
The tobacco smoke rain filter is made of vegetable raw materials, has a base condition of pH 9 or higher, has a pore diameter of 20 Å or less, and has a pore volume of 0. By incorporating ultrafine activated carbon powder with an average particle diameter of 10 cc/g or more and 301 Lm or less, the aroma and taste can be improved. The present invention will be explained in detail below.

まず、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。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、パームカラ、コイヤダ
ストの如き南洋植物;イビール、タカクチイーの如き豆
科植物;木材パルプ、木綿、リンターパルプ等が用いら
れる。他のピンチ、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
うな合成系の原本1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、植物性原本゛]を用いて
平均粒径30Bm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?人がある。
First, it is essential that the activated carbon according to the present invention be produced from vegetable raw materials. As such vegetable raw materials, wood (preferably coniferous); South Sea plants such as coconut husk, palm cara, and coir dust; leguminous plants such as Ibir and Takakuchii; wood pulp, cotton, linter pulp, etc. are used. Activated carbon is also produced from other materials such as mineral materials such as coal, petroleum sludge, or synthetic materials such as polyacrylonitrile fibers and phenolic resins.
In order to make ultrafine powdered activated carbon with an average particle size of 30 Bm or less using plant-derived original material, which has a much inferior taste when filtered and is undesirable than the above-mentioned plant materials, the following method is used. ? There are people.

針葉樹系の木材を粉砕機により200〜2000 pm
の粒度になるように粉砕する。その後平炉で20〜50
時間かけて室温より500°C迄シ1温して炭化処理を
行ない粒径lOO〜1000gm、炭素含有率70%の
炭化物を得る。該炭化物を空気移送型の旋動賦活炉によ
り1200〜1300°Cで数秒間賦活処理を施す。
Coniferous wood is crushed to 200-2000 pm using a crusher.
Grind to a particle size of After that, 20-50 in open hearth
Carbonization treatment is carried out by heating from room temperature to 500° C. over a period of time to obtain a carbide having a particle size of 100 to 1000 gm and a carbon content of 70%. The carbide is activated at 1200 to 1300° C. for several seconds in an air-transfer type rotary activation furnace.

かかる賦活処理は通常の活性炭の賦活処理では占え及ば
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ン古処
理するため、多数にtl基性フ、(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OH基、キノン2(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っても得られ
る。再賦活雰囲気としては、水蒸気の他に濃度の高いW
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(以下中に″粒径″と記したものは平均粒径を意味す
る)が30gmを超えるといくら塩基性庶が高くても吸
着成分間のバランスに起因するチャコールティストの除
去、抑制を行うことは難かしい。微粉砕化処理は、50
〜lOOμm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20Å以下で細孔の6枯(以下ミクロボア
細孔容積と略称する)はO,l0cc/g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0.10
cc/g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、フィリップス法に準する
方法、つまりpH7に調製した0、1 NKCI水溶液
100+al中に活性L’O,1gを投入し、24時時
間上うした後pHメーターで液のpHを測定することに
よりめる(例えば工業化学雑誌87.2019(198
4))。上記方法でめられる塩基性度は、水溶液中のC
I−イオンによってイオン交換されたOH−イオンの六
を評価しているものと推察される。また、平均粒径は計
数原理による粒度測定法の一つであるコールタ−カウン
ター法(例えば粉体光学研究合繊「粉体粒度測定法」)
により測定したものである。
This activation treatment involves high temperatures that cannot be reached by ordinary activated carbon activation treatment, and as will be described later, highly reactive wood-based raw materials are treated in active gases such as carbon dioxide and steam, so many It is thought that tl-based F, () is generated on the activated carbon surface. Although the mechanism of formation is not clear, it is assumed that OH group, Quinone 2 (2) is generated by activation of carbon dioxide gas. 900
It can also be obtained by reactivation for a long time at high temperatures above ℃. In addition to water vapor, the reactivation atmosphere includes a high concentration of W.
Acid gas is preferred. 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 referred to as "particle size" means average particle size) exceeds 30 gm, it must be Even if the properties are high, it is difficult to remove or suppress charcoal dust due to the imbalance between adsorbed components. The pulverization process is 50
It is made by pulverizing activated carbon coarsely pulverized to ~100 μm using a ball mill or the like for a long time. It is essential that the activated carbon has a pore diameter of 20 Å or less and a pore volume (hereinafter abbreviated as micropore pore volume) of 0.10 cc/g or more. That is, the microbore pore volume is 0.10
If it is less than cc/g, vapor phase components such as isoprene, acetone, and acetaldehyde will not be effectively adsorbed, which is undesirable in terms of smoking hygiene and flavor. The basicity of the activated carbon thus obtained was determined by a method similar to the Phillips method, in which 1 g of activated L'O was added to 100+ al of a 0.1 NKCI aqueous solution adjusted to pH 7, and left to stand for 24 hours. Determine by measuring the pH of the liquid with a pH meter (for example, Industrial Chemistry Magazine 87.2019 (198
4)). The basicity determined by the above method is C in an aqueous solution.
It is presumed that six OH- ions ion-exchanged by I- ions are being evaluated. In addition, the average particle size can be measured using the Coulter Counter method, which is one of the particle size measurement methods based on the counting principle (e.g., powder optics research synthetic fibers ``Powder Particle Size Measurement Method'').
It was measured by.

さらに活性炭の細孔直径及び細孔容積は、常圧ドの液体
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 −1nkley)の計算法(例えば慶
伊富長「吸着」共立出版)によりめた。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瓜の比(1,584X 10
−3 )を乗じたイ+fjを全細孔容積とみなし、また
、細孔直径300人から20人までの累積細孔容積から
差し引いた伯を細孔直径容積とした。
Furthermore, the pore diameter and pore volume of activated carbon can be calculated using the Cranston-Inklay (C
ranston -1nkley) (for example, Kei Tominaga, "Adsorption", Kyoritsu Shuppan). However, the ratio of gaseous nitrogen to the amount of nitrogen gas adsorbed at a relative pressure corresponding to a pore diameter of 300 A under standard conditions (1,584 x 10
-3) multiplied by i+fj was regarded as the total pore volume, and the value subtracted from the cumulative pore volume from 300 to 20 pore diameters was defined as the pore diameter volume.

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、木材パルプ繊維、アセテ
ート繊維等と混合し不織布状に成形する方法、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。この際活性炭の使用Rはフィルター1
本当り15〜100mgが好適である。
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 acetate fiber portion, or by mixing it with wood pulp fibers, acetate fibers, etc. and forming it into a non-woven fabric. Methods include spraying and adhering to non-woven fabrics or tows together with adhesives, methods of dispersing in a dispersion medium containing an adhesive polymer that provides a highly viscous solution such as sodium alginate to create a paste-like impregnating solution, and roller printing, etc. Examples include a method of printing on a nonwoven fabric using a printing method used in printing, dyeing, etc., and a method of making fine particles using a binder such as carboxymethyl cellulose or polyvinyl alcohol and interposing them between acetate fiber tows. At this time, activated carbon is used for filter 1.
A weight of 15 to 100 mg is suitable.

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場の増加
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41L潤される。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
の除去ないしは抑制に加えて、植物性原料を出発原料に
選択している点も寄学するところ大である。
The reason why the activated carbon of the present invention specifically adsorbs and removes acetaldehyde, formaldehyde, cyanide gas, etc. is not clear, but the active carbon increases the active surface area due to the small particle size and the base area with high basicity. The increase in 41L is due to a synergistic effect on the reaction with acetaldehyde, etc. In terms of improving the aroma and flavor, in addition to the high basicity and the removal or suppression of irritating vapor phase components through the selection of ultra-fine powders, the selection of plant-based raw materials as starting materials is also a major plus. .

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)になどの合成原料からの活性炭もたばこ焼用フィル
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。
Activated carbon made from synthetic raw materials such as acrylonitrile-based activated carbon fibers and phenolic resin-based activated carbon fibers has been considered as a cigarette burning filter, but it has the disadvantage of not having a good aroma and taste, so it has not been put to practical use as a cigarette filter. Not done.

このように本発明に係わる活性炭は、インプレン、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に多液の吸着性を有するもの
であるため、従来のチャコールフィルターの欠点を改良
することができる。
As described above, the activated carbon according to the present invention has adsorption properties of imprene and acetone that are on the same level as conventional activated carbon, and has specific multi-liquid adsorption properties for irritating vapor phase components such as acetaldehyde, formaldehyde, and cyanide gas. Since it has the properties of charcoal filters, it is possible to improve the drawbacks of conventional charcoal filters.

次に実験例を挙げて本発明の特徴を明確にする。Next, experimental examples will be given to clarify the characteristics of the present invention.

実験例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200〜2000用m針葉樹系木材屑。(1) Wood raw materials Coniferous wood waste with a particle size of 200 to 2000 m.

(2)炭化処理 該木材屑を、平炉で一昼夜200から5000CにA温
、加熱することにより、収−1130%で炭素含有70
%の、粒径が1100−1000JLの炭化物を得た。
(2) Carbonization treatment By heating the wood chips in an open hearth at temperature A from 200 to 5000C for a day and night, the wood chips are heated to a temperature of A, with a yield of -1130% and a carbon content of 70%.
% of carbide with a particle size of 1100-1000 JL was obtained.

(3)賦活処理 イ)該炭化物を流動賦活炉で滞留時間10秒、温度12
00〜1300℃、水/に気10%含有雰囲気で処理し
、粒径30〜200gmの活性炭を得た。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1粒径15
終m、ミクロポア細孔容積Q、38cc/H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50JLm、塩基仕度pH9,7、ミクロポア細
孔容積Q、38cc/Hの活性炭を得た。(サンプル名
:1−b)口)滞留時間5秒、温度1200〜1300
°C1水八気10%含有雰囲気で処理し、粒径30〜3
00gmの活性炭を得た。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18JLm、塩基仕
度pH9,7、ミクロポア細孔容積0.32cc/gの
活性炭を得た。(サンプル名:1−c) ハ)滞留時間20秒、温度1000℃、水蒸気10%含
有雰囲気で処理し、粒径30〜200gmの活性炭を得
た。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15#Lm、塩基性度p’H8,7、ミクロポア
細孔容積Q、34cc/gの活性炭を了りだ。
(3) Activation treatment a) The carbide is placed in a fluidized activation furnace for a residence time of 10 seconds and a temperature of 12
Activated carbon having a particle size of 30 to 200 gm was obtained by treatment at 00 to 1300° C. in an atmosphere containing 10% water/nitrogen. By pulverizing the activated carbon in a ball mill for 24 hours, a particle size of 15
Activated carbon with a final micropore volume Q of 38 cc/H was obtained. (Sample name = 1-a) Furthermore, activated carbon having a particle size of 50 JLm, a basic pH of 9.7, and a micropore pore volume Q of 38 cc/H was obtained by sieving the activated carbon before pulverization. (Sample name: 1-b) Residence time 5 seconds, temperature 1200-1300
Treated in an atmosphere containing 10% water and air at °C1, particle size 30-3
00 gm of activated carbon was obtained. The activated carbon was milled in a ball mill for 24 hours.
By time-pulverizing treatment, activated carbon having a particle size of 18 JLm, a basic pH of 9.7, and a micropore volume of 0.32 cc/g was obtained. (Sample name: 1-c) c) Activated carbon having a particle size of 30 to 200 gm was obtained by processing in an atmosphere containing 10% water vapor at a residence time of 20 seconds and a temperature of 1000°C. By pulverizing the activated carbon with a ball mill, activated carbon with a particle size of 15 #Lm, basicity p'H of 8.7, and micropore volume Q of 34 cc/g was obtained.

(サンプル名:1−d) 実験例2 市販の8〜14メツシユのヤシカラ活性炭(塩)^仕度
PH7、比表面積600m/g)を150〜3’OOJ
Lmに粉砕し、ロータリー・キルン炉により、900°
Cで燃焼ガス雰囲気下5詩間再賦活処理を施した。該活
性炭をボールミルで100時間粉砕処理を施すことによ
り、粒径15舊m、塩基性度PH9,5、ミクロポア細
孔容積0.4 cc/g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45 g m 、 塩基仕度p
H9,3,ミクロポア細孔容積0.39cc/g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
5ルm、塩基性度pH7、ミクロポア細孔容積0.35
cc/gの活性炭を得た。(サンプル名:2−c) 実験例3 粒瓜200〜2000 gmの針葉樹系木材屑を、50
屯星%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っ
て、塩基仕度pH5,3、ミクロポア細孔容積Q、15
cc/g、粒径15pmの活性tgを得た。(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℃で処理することにより、粒径1
5μm、塩基性度pH9,5,ミクロボア細孔容1□−
0,08cc/gの活性炭を得た。(サンプル名:3−
b) 実験例4 市販ポリアクリロニトリル繊維を300°Cの空気中耐
炎化処理を施した後、850℃の水蒸気含<1雰囲気下
で賦活処理を行ない、繊維状活性炭を得た後、ボールミ
ル粉砕処理を施し、粒径15pm、塩基仕度pH9,3
、ミクロポア細孔容積0.25ccノgの活性炭を得た
。(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維状活性炭を
得た後、ボールミル粉砕処理を施し、粒径15JLm、
t!基性度pH9,2、ミクロポア細孔容積0.45c
c/gの活性炭を得た。(サンプル名:5) 以上の実験例で得た活性炭を用いて以−ヒの如き手段で
たばこ焼用フィルターを作製した。即ち、゛活性炭15
部をアルギン酸ソーダー水溶液10部に散布し、均一な
ペーストを作った後、木材、<ルプからなる乾式不織布
(目付40 g/rn2、厚み2.2 ffim)にロ
ーラー捺染機で、プリント処理を施し、活性炭を30 
tng/rr+2添着したシートをイ°Iた。
(Sample name: 1-d) Experimental example 2 Commercially available coconut activated carbon (salt) of 8 to 14 mesh (preparation pH 7, specific surface area 600 m/g) was mixed with 150 to 3'OOJ
Pulverized to Lm and heated at 900° in a rotary kiln.
At C, reactivation treatment was performed for 5 cycles under a combustion gas atmosphere. The activated carbon was pulverized in a ball mill for 100 hours to obtain activated carbon having a particle size of 15 mm, a basicity of PH 9.5, and a micropore volume of 0.4 cc/g. (Sample name: 2-a) In addition, the activated carbon after 5 hours of ball mill pulverization was sieved to have a particle size of 45 g m and a base grade of p.
Activated carbon with H9,3 and micropore volume of 0.39 cc/g 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.
5 lm, basicity pH 7, micropore pore volume 0.35
cc/g of activated carbon was obtained. (Sample name: 2-c) Experimental example 3 200 to 2000 gm of coniferous wood chips were mixed with 50
Mix with aqueous solution of zinc chloride (Tunxing%) and heat at 700℃ in a multi-stage bed furnace.
After performing carbonization and activation treatment by heating at an elevated temperature to
An active tg of cc/g and particle size of 15 pm was obtained. (Sample name: 3-a) In addition, by further treating the activated carbon at 700°C in an air stream containing ammonia gas, the particle size
5μm, basicity pH 9.5, micropore pore volume 1□-
0.08 cc/g of activated carbon was obtained. (Sample name: 3-
b) Experimental Example 4 After subjecting commercially available polyacrylonitrile fibers to flame-retardant treatment in the air at 300°C, activation treatment was performed in an atmosphere containing <1 steam at 850°C to obtain fibrous activated carbon, which was then pulverized in a ball mill. Particle size: 15 pm, base preparation pH: 9.3
, activated carbon with a micropore volume of 0.25 cc was obtained. (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 fibrous activated carbon, and then pulverized in a ball mill to obtain particles with a particle size of 15 JLm,
T! Basicity pH 9.2, micropore pore volume 0.45c
c/g of activated carbon was obtained. (Sample name: 5) Using the activated carbon obtained in the above experimental example, a cigarette burning filter was produced by the following method. That is, "activated carbon 15
After making a uniform paste by spraying 10 parts of aqueous solution of sodium alginate, a printing process was applied to a dry non-woven fabric made of wood (fabric weight 40 g/rn2, thickness 2.2 ffim) using a roller printing machine. , activated carbon 30
The sheet attached with tng/rr+2 was added.

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7字型に折り曲げ
た後、回転する内径先細になったローターにより、より
合せ、さらに絞ることとによって円筒状に巻き上げ直径
8mmの円筒をつくった。この円筒の外側に薄い紙を巻
きつけた後、長さloa+mの活性炭添着フィルターを
得た。該フィルターを長さ7mm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。
Four of these sheets are used and fed side by side so that the striped patterns of the four sheets match, and after being folded into an S-shape or a 7-shape, they are twisted by a rotating rotor with a tapered inner diameter, and then By squeezing and rolling it up into a cylindrical shape, a cylinder with a diameter of 8 mm was made. After wrapping a thin paper around the outside of this cylinder, an activated carbon-impregnated filter having a length loa+m was obtained. This filter was joined to an acetate fiber filter having a length of 7 mm, and a cigarette smoke filter having a length of 17 mm was manufactured.

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
、ノ入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All+
定した結果を第1表に示す。なお吸着率は次のようにし
てめた。
For the various cigarette smoke filters trial-manufactured as described above, the adsorption rates of cyanide gas, acetaldehyde, isoprene, and acetone as components of the incoming gas phase were determined to be All +
The determined results are shown in Table 1. The adsorption rate was determined as follows.

即ち、−1−配力法により試製したフィルターを日本専
売公社製品「ハイライト」からフィルタ一部分を取除い
た部分に接合したものを供試たばことし、同じ「ハイラ
イト」をコントロールとして、定fQ早型自動喫煙器を
用い、次の条件で吸煙させた。
In other words, a test cigarette was prepared by attaching a filter manufactured by the -1-force distribution method to a part of the Japan Monopoly Public Corporation product "Highlight" with a portion of the filter removed, and the same "Highlight" was used as a control to obtain a constant fQ. Using an early type automatic smoker, the subjects smoked under the following conditions.

7Xl: liX: 17.5ml/see吸煙l′I
ν間: 2sec/回 吸煙頻度: 1回/ll11n 燃焼長: 50mm 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1ンの吸着率は、極細ガラ
ス繊維フィルターを通過した8バフ分の煙のうち1.9
5m1をガスクロマトゲフィーに導入し、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)をめ
た。
7Xl: liX: 17.5ml/see smoking l'I
ν interval: 2 sec/times Smoke frequency: 1 time/ll11n Combustion length: 50 mm Number of smokes: 4 pieces/extra-fine glass fiber filter 1.9 out of smoke
5 ml was introduced into a gas chromatography system, the peak height of the control was set as Hs, and the adsorption rate (F) was calculated using the following formula.

F(%) −(H−Hs) /HX I OO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のNaOH?a液に吸収され
たガス吸収液を蒸留後、比色法によりCN−6をめた。
F(%) -(H-Hs) /HX I OO Also, the cyanide gas adsorption rate is based on the tar and 0.5N NaOH collected on the ultra-fine glass fiber filter. After distilling the gas absorption liquid absorbed in liquid a, CN-6 was obtained by a colorimetric method.

(例えば、日本公衆衛生学会誌28,100 (198
1))第1表の結果より次の様に考察することができる
(For example, Journal of the Japanese Society of Public Health 28,100 (198
1)) From the results in Table 1, the following can be considered.

(+)サンプル名(1−b)及び(2−b)は何れも植
物原料からなるもので、塩基仕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。
(+) Sample names (1-b) and (2-b) are both made of plant materials, and have appropriate base preparation and micropore pore volume, but because the particle size is too large, they contain acetaldehyde and cyanide gas. adsorption rate is low.

(2)サンプル名(1−d)、(2−c)及び(3−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、塩基仕度が低すぎる為、(1−d
)及び(2−c)は全体的に吸HXf=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 sizes and micropore pore volumes, but the base preparation is too low, so (1-d
) and (2-c) have low overall HXf= absorption, and (3
In -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
及び塩基仕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。
(3) Sample name (3-b) is made of plant material and has appropriate particle size and base preparation, but the adsorption rate of acetaldehyde and cyanide gas is extremely low because the micropore pore volume is too small.

(4)これらに対しサンプル名(1−a)、(1−c)
及び(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で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17)ずれも著しく優れており、且つ各吸着成
分がノくランスよく除去されている為、チャコールティ
ストの発現もなかった。特に煙りの刺激に関与するシア
ン系ガス、アセトアルデヒドの吸着能が一段と向−tz
している為、たばこの香喫味の改善に大きく寄グするこ
とがわかった。
(4) Sample names (1-a) and (1-c) for these
and (2-b) satisfy all the specified requirements of the present invention, and the adsorption rate of acetaldehyde, isoprene, acetone, and cyanide gases, which are the main components in tobacco smoke, is significantly different from that of conventional products17). It was excellent, and since each adsorbed component was removed well, there was no appearance of charcoal tint. In particular, the adsorption ability of cyanide gas and acetaldehyde, which are involved in smoke irritation, has further improved.
It was found that this greatly contributed to improving the aroma and taste of cigarettes.

出願人 11本専売公社Applicant: 11 Monopoly Public Corporation

Claims (1)

【特許請求の範囲】[Claims] 植物性原料からなり、塩基性度がPH9以上で、細孔直
径20A以下の細孔容積が0.10cc/g以−し、且
つ平均粒径が30pLm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〇
It is made of vegetable raw materials, and contains ultrafine powder activated carbon with a basicity of PH9 or higher, a pore diameter of 20A or less, a pore volume of 0.10cc/g or less, and an average particle size of 30pLm or less. Cigarette smoke filter with improved flavor
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 true JPS6027375A (en) 1985-02-12
JPS6045918B2 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)

Cited By (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
GB2395650A (en) * 2002-11-27 2004-06-02 Filtrona Int Ltd Activated carbon cigarette filter
US7842736B2 (en) 2000-08-09 2010-11-30 British American Tobacco (Investments) Limited Porous carbons
US8591855B2 (en) 2000-08-09 2013-11-26 British American Tobacco (Investments) Limited Porous carbons
US9907336B2 (en) 2005-03-29 2018-03-06 British American Tobacco (Investments) Limited Porous carbon materials and smoking articles and smoke filters therefor incorporating such materials

Cited By (13)

* 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
JPH044244B2 (en) * 1985-03-29 1992-01-27
US8227518B2 (en) 2000-08-09 2012-07-24 British American Tobacco (Investments) Ltd. Porous carbons
US7842736B2 (en) 2000-08-09 2010-11-30 British American Tobacco (Investments) Limited Porous carbons
US7850942B2 (en) 2000-08-09 2010-12-14 British American Tobacco (Investments) Ltd. Porous carbons
US8591855B2 (en) 2000-08-09 2013-11-26 British American Tobacco (Investments) Limited Porous carbons
WO2004047571A3 (en) * 2002-11-27 2004-09-16 Filtrona Int Ltd Tobacco smoke filter
GB2395650B (en) * 2002-11-27 2005-09-07 Filtrona Int Ltd Tobacco smoke filter
JP2006507824A (en) * 2002-11-27 2006-03-09 フィルトロナ インターナショナル リミティド Cigarette smoke filter
JP4808969B2 (en) * 2002-11-27 2011-11-02 フィルトロナ インターナショナル リミティド Cigarette smoke filter
GB2395650A (en) * 2002-11-27 2004-06-02 Filtrona Int Ltd Activated carbon cigarette filter
US8402977B2 (en) 2002-11-27 2013-03-26 Filtrona International Limited Tobacco smoke filter
US9907336B2 (en) 2005-03-29 2018-03-06 British American Tobacco (Investments) Limited Porous carbon materials and smoking articles and smoke filters therefor incorporating such materials

Also Published As

Publication number Publication date
JPS6045918B2 (en) 1985-10-12

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