JPS6168135A - Agent for removing carbon monoxide in tobacco smoke - Google Patents

Agent for removing carbon monoxide in tobacco smoke

Info

Publication number
JPS6168135A
JPS6168135A JP59188776A JP18877684A JPS6168135A JP S6168135 A JPS6168135 A JP S6168135A JP 59188776 A JP59188776 A JP 59188776A JP 18877684 A JP18877684 A JP 18877684A JP S6168135 A JPS6168135 A JP S6168135A
Authority
JP
Japan
Prior art keywords
carrier
tobacco smoke
smoke
activated carbon
catalyst
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
JP59188776A
Other languages
Japanese (ja)
Other versions
JPS6322185B2 (en
Inventor
Kenichiro Sugimori
健一郎 杉森
Masaru Yamamoto
勝 山本
Ikuo Horii
堀井 郁男
Hajime Matsushita
松下 肇
Shigeo Ishiguro
石黒 繁夫
Hiroshi Ichise
市瀬 宏
Shigenobu Mizusaki
水崎 茂暢
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.)
Topy Industries Ltd
Japan Tobacco Inc
Original Assignee
Topy Industries Ltd
Japan Tobacco Inc
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 Topy Industries Ltd, Japan Tobacco Inc filed Critical Topy Industries Ltd
Priority to JP59188776A priority Critical patent/JPS6168135A/en
Publication of JPS6168135A publication Critical patent/JPS6168135A/en
Publication of JPS6322185B2 publication Critical patent/JPS6322185B2/ja
Granted legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A50/00TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/20Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters

Landscapes

  • Catalysts (AREA)
  • Cigarettes, Filters, And Manufacturing Of Filters (AREA)
  • Treating Waste Gases (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

PURPOSE:To obtain a CO-removing agent capable of reducing remarkably CO in smoke without deteriorating the flavor of tobacco smoke by using a mixed composition of metallic oxides and activated carbon as a carrier, and depositing a Pd salt and a copper salt on the carrier. CONSTITUTION:A mixture of a Pd salt and a copper salt is deposited on a carrier consisting of a mixed composition of metallic oxides and activated carbon. A material contg. >=1 kind selected from a group consisting of MgO, Al2O3, SiO2, P2O5, or transition metal oxides (e.g., CuO) is used as said metallic oxides. Besides, said metallic oxide is a silicate ore contg. >=1 kind between MgO or Al2O3 in the composition, and kaolinite and zeolite can be exemplified. In this case, the amt. of the metallic oxide to be contained in the mixed composition of activated carbon and metallic oxides is preferably regulated to 10-90wt%. By this CO-removing agent thus obtained, CO in smoke can be remarkably reduced without deteriorating the flavor of the tobacco smoke.

Description

【発明の詳細な説明】 本発明は、たばこの香喫味に悪影響を及ぼすことなく、
喫煙時に発生するたばこ煙から一酸化炭素を選択的に除
去する除去剤に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention provides the following advantages:
This invention relates to a remover that selectively removes carbon monoxide from tobacco smoke generated during smoking.

(産業上の利用分野) 一般に、炭素や含炭素化合物の不完全燃焼によって発生
する一酸化炭素(以下単にCOともいう)は、血液中の
ヘモグロビンと強固に結合し、血液の酸素吸収及び運搬
の役割を著しく阻害するため、頭痛、めまいなどの急性
中毒症状をひき起し、甚だしい場合には死に至らしめる
。又、COに長期的に曝露された場合には慢性心臓疾患
を惹起するといわれている。
(Industrial Application Field) In general, carbon monoxide (hereinafter simply referred to as CO), which is generated by incomplete combustion of carbon and carbon-containing compounds, binds tightly to hemoglobin in the blood and inhibits oxygen absorption and transport in the blood. Because it significantly impedes the function of the drug, it can cause acute poisoning symptoms such as headache and dizziness, and in extreme cases, it can lead to death. Furthermore, long-term exposure to CO is said to cause chronic heart disease.

このCOは喫煙者がたばこを喫煙した際に直接吸入する
煙いわゆる主流煙中にも数パーセント含有されており、
これは人体の肺に達するまでに同時に吸入される空気に
より大幅に稀釈されるものの、喫煙者の血中CO結合ヘ
モグロビンの慢性的な濃度上昇に寄与しているとされ、
たばこ煙中からのCOの低減が望まれている。
This CO is also contained in several percent of the smoke that smokers directly inhale when they smoke cigarettes, so-called mainstream smoke.
Although this is greatly diluted by the air that is simultaneously inhaled before reaching the lungs of the human body, it is thought to contribute to the chronic concentration of CO-bound hemoglobin in the blood of smokers.
It is desired to reduce CO from tobacco smoke.

(従来の技術) 従来、かかる観点からたばこ主流煙中のCO’b’lJ
度を低減させようとする試みが盛んに行なわれ、特許明
細書等において多くの提案がなされている。
(Prior Art) Conventionally, from this point of view, CO'b'lJ in mainstream cigarette smoke has been
Many attempts have been made to reduce the degree of damage, and many proposals have been made in patent specifications and the like.

これらの提案は大別すると以下のように分類することが
できる。
These proposals can be broadly classified as follows.

1)Coの生成の少ない原料を選択して使用する方法。1) A method of selecting and using raw materials that generate less Co.

2)フィルタ一部分に開孔を設け、あるいは巻紙に高気
孔度のものを使用してCOの生成を抑制したり、生成し
たCOを巻紙からの拡散によって低減する方法。
2) A method of suppressing the production of CO by providing holes in a portion of the filter or using a wrapping paper with high porosity, or reducing the generated CO by diffusion from the wrapping paper.

3)酸化触媒や酸化剤あるいは吸着剤をフィルタ一部分
又はシガレットホルダー等に充填あるいは保持してCO
を酸化又は捕捉して低減する方法。
3) Fill or hold an oxidation catalyst, oxidizer, or adsorbent in a part of the filter or cigarette holder, etc. to reduce CO
A method of reducing it by oxidizing or capturing it.

上記1)〜3)の方法の中、1)、2)の方法について
は現在までに広範な検討がなされており、その一部につ
いては製品化もなされている。
Among the methods 1) to 3) above, methods 1) and 2) have been extensively studied to date, and some of them have been commercialized.

しかし、3)の方法については未だ決定的に有効なもの
が見出されていないのが現状である。その理由としては
、たばこ煙と上記酸化触媒その他の充填剤との接触時間
が極めて短時間であること、周囲環境に水分やタールな
どの阻害成分が共存すること、充填剤自体の毒性を配慮
する必要があることのほかにたばこの香喫味が損なわれ
ることなど多くの問題点が存することが挙げられる。
However, as for method 3), no definitively effective method has yet been found. The reasons for this are that the contact time between tobacco smoke and the oxidation catalyst and other fillers is extremely short, that inhibiting components such as moisture and tar coexist in the surrounding environment, and that consideration must be given to the toxicity of the fillers themselves. In addition to the necessity, there are many other problems, such as the fact that the aroma and taste of cigarettes is impaired.

上記3)の方法によりたばこ煙中のCOを低減する目的
で提案された物質としては、例えば、酸化銅と酸化マン
ガンの複合物を主体とした、いわゆるホプカリフト系複
合酸化物触媒(特開昭51−72988号、特開昭53
−96399号)や、酸化マンガンなどの金属酸化物触
媒(Br1t、 Pat。
Examples of substances that have been proposed for the purpose of reducing CO in tobacco smoke by method 3) include the so-called hopkalift-based composite oxide catalyst (Japanese Unexamined Patent Application Publication No. 51/1982), which is mainly composed of a composite of copper oxide and manganese oxide. -72988, JP-A-53
-96399) and metal oxide catalysts such as manganese oxide (Br1t, Pat.

第1315374号)があるが、いずれも水分による失
活が著しく、追試の結果では殆ど除去効果が認められな
い。又、貴金属担持触媒についても多くの開示(特開昭
55−73344号、同53−149192号、同55
−137039号)があるが、追試した結果、煙中CO
の除去に関しては充分な効果を期待し得ないことが明ら
かとなった。
No. 1315374), but all of them suffer from significant deactivation due to moisture, and follow-up tests show almost no removal effect. In addition, there are many disclosures regarding precious metal supported catalysts (JP-A-55-73344, JP-A-53-149192, JP-A-55).
-137039), but as a result of additional tests, CO in smoke
It has become clear that no sufficient effect can be expected in the removal of .

しかし、一方、エチレンを原料とし、気相中の酸素を利
用してアセトアルデヒドを合成する目的で開発された、
いわゆるワソカー(Wacker)型の触媒は、COの
酸化に対して高活性であり、又、水を酸化還元(レドッ
クス)系内に有効に取り込み、気相中の酸素によってC
Oを酸化するという機構が提案されている(ジャーナル
・エア・ポリューション・コントロール・アソシエーシ
ョン(J、 Air Po1lution Contr
ol As5oc、) 2 B、253(1978))
However, on the other hand, it was developed for the purpose of synthesizing acetaldehyde using ethylene as a raw material and using oxygen in the gas phase.
The so-called Wacker type catalyst is highly active for CO oxidation, and also effectively incorporates water into the redox system and oxidizes CO using oxygen in the gas phase.
A mechanism has been proposed to oxidize O (Journal Air Pollution Control Association).
ol As5oc, ) 2 B, 253 (1978))
.

このワフカー型触媒は、基本的には基質に対する活性化
合物としてPdX2又はM2 PdX2 (Xはハロゲ
ン原子、Mは周期律表におけるIa族金属)を使用し、
又、それに対するレドックス対としてCuX2 (Xは
ハロゲン原子)が用いられる。
This Wachker type catalyst basically uses PdX2 or M2 PdX2 (X is a halogen atom, M is a group Ia metal in the periodic table) as an active compound for the substrate,
Moreover, CuX2 (X is a halogen atom) is used as a redox pair for this.

一般に金属酸化物を用いた低温でのCOの酸化において
望ましくないとされる水分の存在が、この系の触媒では
逆に有効に働くため、たばこ煙中のCO低域のように多
湿な条件下での使用に際して格好の触媒ということがで
きる。
The presence of moisture, which is generally considered undesirable in low-temperature CO oxidation using metal oxides, works effectively in this type of catalyst, so under humid conditions such as the low range of CO in cigarette smoke. It can be said to be an excellent catalyst for use in

このようなワソカー型触媒をcoの低減用に使用した発
明には、COによって還元されたパラジウム塩の再酸化
を促進するために、ハロゲン化銅以外の銅塩(主として
硝酸銅)を第3成分として添加して活性を高める方法(
特開昭50−33990号公報)や、同様に再酸化促進
のためにスズイオン等を添加する例(特開昭54−11
0400号公報)、1価の銅塩を共存させた例(特開昭
55−97252号公報)がある。これらのcO酸化に
関する発明にみられるワラカー型触媒は、溶液としての
均−系、あるいはアルミナ、シリカ、アルミノケイ酸塩
、モレキュラーシーブ、活性炭などの各種担体に担持さ
せた不均一系触媒として用いられている。
In the invention using such a Wasoker-type catalyst for reducing CO, copper salts other than copper halides (mainly copper nitrate) are added as a third component in order to promote reoxidation of palladium salts reduced by CO. How to increase activity by adding as
(Japanese Unexamined Patent Publication No. 50-33990) and an example in which tin ions are added to promote reoxidation (Japanese Unexamined Patent Publication No. 54-11).
No. 0400), and an example in which a monovalent copper salt was coexisting (Japanese Patent Application Laid-Open No. 55-97252). The Varaker-type catalysts seen in these inventions related to cO oxidation can be used as homogeneous catalysts in the form of solutions or as heterogeneous catalysts supported on various carriers such as alumina, silica, aluminosilicate, molecular sieves, and activated carbon. There is.

しかし、かかる従来の発明によるワラカー型触媒を触媒
担体として公知である上述の担体に担持させた触媒を、
たばこ主流煙中のCOを低減する目的で使用した場合に
は、その効果は必ずしも充分でなく、一方、担体として
T−アルミナを用いた場合にはcoの酸化活性が高く、
たばこのフィルタ一部分に充填した場合のたばこ煙中の
co低減率も極めて高いが、たばこ煙の香喫味を著しく
低下させるという欠点がある。これは、γ−アルミナ表
面の物理、化学的性質によるものと考えられる。又、活
性炭のみを担体とした場合には、たぼこ香喫味へ及ぼす
悪影響は認められなかったものの、充分なCOの低減効
果が得られないという欠点がある。
However, the catalyst in which the Waraker-type catalyst according to the conventional invention is supported on the above-mentioned carrier, which is known as a catalyst carrier,
When used for the purpose of reducing CO in mainstream tobacco smoke, the effect is not necessarily sufficient; on the other hand, when T-alumina is used as a carrier, the oxidation activity of co is high;
Although the reduction rate of CO in tobacco smoke is extremely high when it is partially filled in a cigarette filter, it has the disadvantage that it significantly reduces the aroma and taste of tobacco smoke. This is considered to be due to the physical and chemical properties of the γ-alumina surface. In addition, when activated carbon alone is used as a carrier, although no adverse effect on the taste of Taboko was observed, there is a drawback that a sufficient CO reduction effect cannot be obtained.

〔発明が解決しようとする問題点〕[Problem that the invention seeks to solve]

本発明は従来のCO低減用触媒の上述した問題点に鑑が
みてなされたもので、たばこ煙中のC○低減効果が高く
、かつ、たばこ煙の香喫味に悪影響を及ぼさないCO除
去剤を提供することを目的とする。
The present invention was made in view of the above-mentioned problems of conventional CO reduction catalysts, and provides a CO removal agent that is highly effective in reducing C○ in tobacco smoke and does not adversely affect the aroma and taste of tobacco smoke. The purpose is to provide.

C○除去剤を実際にたばこ、主としてシガレットに適用
するに際しては、CO除去剤を構成するC○酸化触媒を
担体に保持させてシガレットのフィルターやホルダー内
に充填して使用する必要がある。そこで、本発明者らは
パラジウム塩と銅塩の組合せからなるワラカー型触媒に
ついて、これを担持すべき担体の種類とCOの酸化活性
との関係及びたばこ煙の香喫味に及ぼす影響等について
詳細に研究を行なった結果、金属酸化物と活性炭との混
合組成物を担体とした場合に、高活性でしかも香喫味に
悪影響を及ぼさないCO除去触媒が得られることを見出
し本発明をなすに至った。
When actually applying a CO remover to tobacco, mainly cigarettes, it is necessary to hold the CO oxidation catalyst constituting the CO remover on a carrier and fill it into a cigarette filter or holder. Therefore, the present inventors investigated in detail the relationship between the type of carrier on which the catalyst should be supported and the oxidation activity of CO, and the effect on the aroma and taste of tobacco smoke regarding the Varaka type catalyst consisting of a combination of palladium salt and copper salt. As a result of research, the inventors discovered that a highly active CO removal catalyst that does not adversely affect the aroma and flavor can be obtained when a mixed composition of metal oxides and activated carbon is used as a carrier, leading to the present invention. .

〔問題点を解決するための手段〕[Means for solving problems]

すなわち、本発明は、金属酸化物と活性炭との混合組成
物から成る担体に、パラジウム塩と銅塩との混合物を担
持させたことを特徴とするたばこ煙中の一酸化炭素除去
剤である。
That is, the present invention is a carbon monoxide remover in tobacco smoke, characterized in that a mixture of a palladium salt and a copper salt is supported on a carrier made of a mixed composition of a metal oxide and activated carbon.

本発明において、担体の一組成物として使用される活性
炭は特に制限はなく、ヤシガラ炭、パーム炭、針葉樹炭
等の植物系活性炭もしくは石炭系活性炭が好適に使用さ
れる。又、これらの活性炭の比表面積はB、E、T、測
定法による約500〜1300m/gを有するものであ
ることが望ましい。
In the present invention, the activated carbon used as a carrier composition is not particularly limited, and vegetable activated carbon or coal-based activated carbon such as coconut shell charcoal, palm charcoal, and softwood charcoal is preferably used. Further, it is desirable that these activated carbons have a specific surface area of about 500 to 1300 m/g as determined by B, E, and T measurement methods.

次に活性炭と混合使用される金属酸化物としては、酸化
マグネシウム(MgO)、酸化アルミニウム(A12o
3)、シリカ(Si02)、五酸化燐(P2O3)及び
遷移金属酸化物からなる群より選ばれる1種以上を含む
金属酸化物、もしくは組成中にマグネシウム又はアルミ
ニウムの1種以上を含むケイ酸塩鉱物、例えばカオリナ
イト(A1203 ・2SiO□ ・2H20)、石綿
(Mgo−3io2)、セピオライト (Mgg H2
(Si4011)3 ・3H20)、ゼオライト(Na
2 A12S 1301o−XH20) 、ケイソウ±
(Si02を主成分とし、組成中にA 1203 、F
e2O3、MgO,CaOを含む。)などの使用が好ま
しい。
Next, as metal oxides mixed with activated carbon, magnesium oxide (MgO), aluminum oxide (A12O
3) A metal oxide containing one or more selected from the group consisting of silica (Si02), phosphorus pentoxide (P2O3), and transition metal oxides, or a silicate containing one or more of magnesium or aluminum in its composition. Minerals such as kaolinite (A1203 ・2SiO□ ・2H20), asbestos (Mgo-3io2), sepiolite (Mgg H2
(Si4011)3 ・3H20), zeolite (Na
2 A12S 1301o-XH20), diatomaceous ±
(Si02 is the main component, A 1203 , F
Contains e2O3, MgO, and CaO. ) etc. are preferred.

又、遷移金属酸化物としては、例えば、酸化銅(Cub
)、酸化ジルコニウム(ZrO2)、酸化チタン(T 
i O□)、酸化ニッケル(Nip)、酸化コバル) 
(Co O)等を好適に使用することができる。
Further, as the transition metal oxide, for example, copper oxide (Cub
), zirconium oxide (ZrO2), titanium oxide (T
i O□), nickel oxide (Nip), cobal oxide)
(Co 2 O) etc. can be suitably used.

次に活性炭と金属酸化物とを固めて担体とする方法とし
ては公知の方法でよく、例えば活性炭粉末と全屈酸化物
粉末とをポリビニルアルコール等の水溶性高分子水溶液
もしくはシリカゾル、アルミナゾル、水ガラスなどで練
り固め、20〜60メツシュ程度の粒状に成型、予備乾
燥したのち約100℃以上の温度で加熱処理する等の方
法が採用され得る。
Next, any known method may be used to solidify the activated carbon and the metal oxide to form a carrier. For example, activated carbon powder and total oxide powder may be mixed in an aqueous solution of a water-soluble polymer such as polyvinyl alcohol, silica sol, alumina sol, or water glass. Methods such as kneading and hardening the mixture, forming it into particles of about 20 to 60 meshes, pre-drying, and then heat-treating at a temperature of about 100° C. or higher may be employed.

この場合、活性炭と金属酸化物の混合組成物中に含有さ
れる金属酸化物の配合量は、10〜90重量%が好まし
く、更に好ましくは30〜70重量%が良い。
In this case, the amount of metal oxide contained in the mixed composition of activated carbon and metal oxide is preferably 10 to 90% by weight, more preferably 30 to 70% by weight.

次に、本発明のCO除去剤中に含有される触媒成分の担
持量は、パラジウム塩については0.01〜0.2  
m mol/ gの範囲が良く、又、銅塩については0
.1〜2.0 m mol/ g、好ましくは0.4〜
1゜0m mol/ gの範囲が良い。更にパラジウム
塩および銅塩の種類としては、塩化物、硝酸塩、硫酸塩
等が使用できる。
Next, the supported amount of the catalyst component contained in the CO removing agent of the present invention is 0.01 to 0.2 for palladium salts.
The range of m mol/g is good, and 0 for copper salts.
.. 1-2.0 mmol/g, preferably 0.4-2.0 mmol/g
A range of 1°0 mmol/g is preferable. Furthermore, as types of palladium salts and copper salts, chlorides, nitrates, sulfates, etc. can be used.

上記の金属塩触媒を金属酸化物と活性炭との混合組成物
担体へ担持させる方法としては、予め担体の細孔容積を
B、E、T、法等で測定しておき、その容積にほぼ等し
い体積の水にパラジウム塩および銅塩を熔解し、この全
量を担体の細孔内に吸収させる、いわゆるボアフィリン
グ法や、パラジウム塩と銅塩の混合水溶液中に担体を浸
漬した後、ロータリーエバポレータ等を用いて溶液を濃
縮し担体上に塩類を析出させる、いわゆる含浸法などの
方法を適用することができるが、後者の含浸法の方が簡
便さの点、および活性成分の溶液の濃度に特に制限を設
ける必要がないことなどから優れている。
As a method for supporting the above-mentioned metal salt catalyst on a mixed composition carrier of metal oxide and activated carbon, the pore volume of the carrier is measured in advance using the B, E, T method, etc., and the volume is approximately equal to that of the carrier. The so-called bore filling method involves dissolving a palladium salt and a copper salt in a volume of water and absorbing the entire amount into the pores of the carrier, or by immersing the carrier in a mixed aqueous solution of a palladium salt and a copper salt, and then using a rotary evaporator, etc. It is possible to apply a method such as the so-called impregnation method, in which the solution is concentrated and the salts are precipitated onto the carrier using It is excellent because it does not require any restrictions.

以上のようにして調製された本発明のCO除去剤はたば
このフィルタ一部分あるいはシガレットホルダー等に充
填して使用に供する。
The CO remover of the present invention prepared as described above is used by filling a portion of a cigarette filter or a cigarette holder.

以下実施例を掲げて本発明を更に詳しく説明するが、本
発明のCO除去剤を使用すればたばこ煙中のC○を顕著
に低減することが可能となるのみならず、たばこ煙の香
喫味にも悪影響を与えず、むしろ煙の刺激を軽減するな
ど優れた効果を有することが判明した。
The present invention will be explained in more detail with reference to Examples below. By using the CO remover of the present invention, it is possible not only to significantly reduce C○ in tobacco smoke, but also to improve the aroma and flavor of tobacco smoke. It has been found that it does not have any negative effects on smoke, but rather has excellent effects such as reducing the irritation caused by smoke.

(実施例) (1)担体の調製 先ず以下の方法で金属酸化物と活性炭との混合組成物か
らなる6種類の本発明に係る触媒担体A−Fを調製した
(Example) (1) Preparation of carrier First, six types of catalyst carriers A to F according to the present invention made of a mixed composition of metal oxide and activated carbon were prepared by the following method.

調製例1 200メソシユ以下の粒度に粉砕したヤシガラ炭Log
およびケイソウ土粉末10gを乾式混合機で充分に混合
した後、濃度30重量%のシリカゾル35m/を添加し
た。この混合物を充分混練した後、120℃で乾燥固化
した。次いで粉砕して20〜60メソシユの粒度に揃え
、担体(A)を得た。
Preparation Example 1 Coconut husk charcoal pulverized to a particle size of 200 mesosius or less
After sufficiently mixing 10 g of diatomaceous earth powder with a dry mixer, 35 m/m of silica sol having a concentration of 30% by weight was added. After thoroughly kneading this mixture, it was dried and solidified at 120°C. The particles were then pulverized to a particle size of 20 to 60 mesoyu to obtain a carrier (A).

調製例2 200メツシユ以下の粒度に粉砕した石炭系活性炭15
gおよびシリカアルミナ粉末5gとを乾式混合機で充分
に混合した後、濃度20重量%のシリカゾル35mAを
加えて更に充分混練した。この混練物を120℃で乾燥
した後、300℃に上昇して更に2時間加熱処理した。
Preparation Example 2 Coal-based activated carbon 15 crushed to a particle size of 200 mesh or less
g and 5 g of silica alumina powder were thoroughly mixed using a dry mixer, and then 35 mA of silica sol having a concentration of 20% by weight was added and further thoroughly kneaded. After drying this kneaded product at 120°C, the temperature was raised to 300°C and heat-treated for further 2 hours.

次いで放冷した後粉砕し、20〜60メソシユに粒度を
揃え、担体(B)を得た。
Next, the mixture was allowed to cool and then ground to obtain a carrier (B) with a uniform particle size of 20 to 60 granules.

調製例3 200メツシユ以下の粒度に粉砕した石炭系活性炭Lo
gと酸化第二銅(CuO)10gを充分混合した後、濃
度30重量%のシリカゾル3 Q m 7!を加えて更
に充分混練した。この混練物を120℃で乾燥した後粉
砕し、20〜60メツシユに粒度を揃え、担体(C)を
得た。
Preparation Example 3 Coal-based activated carbon Lo crushed to a particle size of 200 mesh or less
After thoroughly mixing 10 g of cupric oxide (CuO) with 10 g of cupric oxide (CuO), a silica sol 3 Q m 7! was added and thoroughly kneaded. This kneaded product was dried at 120° C. and then pulverized to have a uniform particle size of 20 to 60 mesh to obtain a carrier (C).

8周部例 4 200メソシユ以下の粒度に粉砕したヤシガラ炭10g
にピロリン酸マグネシウム(2Mgo・P2O5)粉末
10gおよび3号ケイ酸ソーダ35mj2を加え、充分
混練した後、150°Cで乾燥した。次いで粉砕し、2
0〜60メツシユに粒度を揃え、担体(D)を得た。
Example 4: 10 g of coconut husk charcoal crushed to a particle size of 200 mesosius or less
10 g of magnesium pyrophosphate (2Mgo.P2O5) powder and 35 mj2 of No. 3 sodium silicate were added to the mixture, thoroughly kneaded, and then dried at 150°C. Then crush, 2
The particle size was adjusted to 0 to 60 mesh to obtain a carrier (D).

S周部例5 200メツシユ以下の粒度に粉砕したコール炭10gお
よびカオリナイト粉末10gに、濃度30重量%のシリ
カゾル30m2を加えて充分混練した後、120°Cで
乾燥した。次いで更に800℃で2時間、窒素気流中で
熱処理を行なった。放冷後粉砕して20〜60メツシユ
の粒度に揃え、担体(E)を得た。
S Peripheral Example 5 30 m2 of silica sol having a concentration of 30% by weight was added to 10 g of coal charcoal and 10 g of kaolinite powder crushed to a particle size of 200 mesh or less, thoroughly kneaded, and then dried at 120°C. Then, heat treatment was further performed at 800° C. for 2 hours in a nitrogen stream. After being left to cool, it was pulverized to a particle size of 20 to 60 mesh to obtain a carrier (E).

II製例6 200メソシユ以下の粒度に粉砕したコール炭10g、
同様の粒度に調製した酸化ジルコニウム(ZrO2)5
gおよび酸化ニッケル(Ni0)5gを乾式にて充分混
合した後、濃度30重量%のシリカゾル3Qm6を加え
て充分混練し、120℃で乾燥した。次いでこれを更に
300℃で2時間熱処理を行なった後、粉砕して20〜
60メツシユの粒度に揃え、担体(F)を得た。
II Preparation Example 6 10 g of coal charcoal crushed to a particle size of 200 mesosius or less,
Zirconium oxide (ZrO2) prepared to similar particle size5
After dry mixing 5 g of nickel oxide (Ni0) and 5 g of nickel oxide (Ni0), silica sol 3Qm6 with a concentration of 30% by weight was added, thoroughly kneaded, and dried at 120°C. Next, this was further heat-treated at 300°C for 2 hours, and then crushed to give a
The particle size was adjusted to 60 mesh to obtain a carrier (F).

(2)担体担持触媒の調製 (1)の方法でそれぞれ調製した上記担体(A)〜(E
)の各3gに対し、0.1モル/β濃度の塩化パラジウ
ム水溶液2mで、1モル/β濃度の塩化第二銅水溶液1
mj!および1モル/β濃度の硝酸銅水溶液1mlから
なる混合水溶液をそれぞれ添加し、パラジウム塩および
銅塩からなる触媒成分を担体に含浸した。それぞれを4
0°Cで乾固し、本発明の担体担持触媒(A)′(B)
’  、(C)’  、(D)’および(E)′得た。
(2) Preparation of carrier-supported catalyst The above-mentioned carriers (A) to (E) each prepared by the method (1)
), 2 m of palladium chloride aqueous solution with 0.1 mol/β concentration, 1 ml of cupric chloride aqueous solution with 1 mol/β concentration
mj! A mixed aqueous solution consisting of 1 ml of a copper nitrate aqueous solution having a concentration of 1 mol/β was added to the carrier to impregnate the catalyst component consisting of a palladium salt and a copper salt. 4 each
The carrier-supported catalyst (A)′(B) of the present invention was dried at 0°C.
', (C)', (D)' and (E)' were obtained.

担体(F)については、担体3gに対して銅塩として1
モル/7!の塩化第二銅と硫酸銅の水溶液をそれぞれ1
.5 m lを用いた以外は担体(A)〜(E)の場合
と同様に操作し、触媒(F)′を得た。
Regarding carrier (F), 1 as copper salt per 3 g of carrier.
Mol/7! 1 each of aqueous solutions of cupric chloride and copper sulfate
.. Catalyst (F)' was obtained in the same manner as in the case of supports (A) to (E) except that 5 ml was used.

(3)たばこ煙中のCO除去試験 (2)で得た本発明の担体担持触媒各20 Qmgを、
製品シガレット(商品名ハイライト)のフィルタ一部分
に充填した。このシガレットを自動喫煙装置に接続し、
標準喫煙条件(35m7!吸引/1パフ、2秒/1パフ
)で6パブ吸煙させ、得られた主流煙ガス中のC○濃度
を非分散型赤外分光光度針(ND−IR)を用いて測定
した。又、γ−アルミナおよびヤシガラ炭をそれぞれ担
体とし、A−Eの担体の場合と同様に触媒成分を担持さ
せた触媒を対比試料として同様にCO濃度を測定し、又
、ヤシガラ炭のみを同量フィルターに充填したものを対
照として同様にCO濃度を測定した。以上の測定値から
、対照に対するCO除去率を算出した結果は第1表に示
すとおりであった。
(3) 20 Qmg of each of the carrier-supported catalysts of the present invention obtained in the test for removing CO in tobacco smoke (2),
A portion of the filter of a product cigarette (product name highlight) was filled with it. Connect this cigarette to an automatic smoking device,
Smoking was performed for 6 puffs under standard smoking conditions (35m7! inhalation/1 puff, 2 seconds/1 puff), and the C○ concentration in the obtained mainstream smoke gas was measured using a non-dispersive infrared spectrophotometer needle (ND-IR). It was measured using In addition, using γ-alumina and coconut husk charcoal as carriers, the CO concentration was measured in the same way as a comparison sample with a catalyst on which catalyst components were supported in the same way as in the case of the carriers A-E, and the same amount of only coconut husk charcoal was used as a comparison sample. The CO concentration was similarly measured using the filter filled as a control. From the above measured values, the CO removal rate relative to the control was calculated and the results are shown in Table 1.

第  1  表 なお、CO除去率は次式を用いて算出した。Table 1 Note that the CO removal rate was calculated using the following formula.

第1表の結果から明らかなように、本発明の担体担持触
媒を充填したフィルターは、ヤシガラ炭単独を担体とし
た触媒に比べ、2〜2.7倍のCO除去率を示し、γ−
アルミナ担体に匹敵する性能を有するものであった。
As is clear from the results in Table 1, the filter filled with the carrier-supported catalyst of the present invention exhibited a CO removal rate 2 to 2.7 times higher than that of the catalyst using coconut husk charcoal alone as a carrier, and the γ-
It had performance comparable to that of an alumina carrier.

(4)たばこ煙に対する香喫味試験 (3)と同様にして得た試料について、訓練された専門
官能検査パネル10名により、たばこ煙の香喫味評価を
行なった結果を第2表に示した。
(4) Cigarette Smoke Flavor and Flavor Test Samples obtained in the same manner as in (3) were evaluated by a trained professional sensory panel of 10 people, and the results are shown in Table 2.

第2表 第2表の評価にみられるように、本発明の担体担持触媒
はたばこ煙の香喫味に与える悪影響はほとんどなく、パ
ネル全員が対照品であるヤシガラ炭フィルターと差がな
(香喫味が優れていると評価した。一方、γ−アルミナ
担体触媒は、たばこの香喫味に著しく負の影響を与える
ことが判明した。
Table 2 As seen in the evaluations in Table 2, the carrier-supported catalyst of the present invention has almost no adverse effect on the aroma and flavor of tobacco smoke, and all panelists agreed that there was no difference between the control product and the coconut husk charcoal filter. On the other hand, the γ-alumina carrier catalyst was found to have a significant negative impact on the aroma and taste of tobacco.

(発明の効果) 以上、実施例を含めて詳細に説明したように、金属酸化
物と活性炭との混合組成物を担体とし、これにパラジウ
ム塩と銅塩との混合物を担持させて成る本発明のCO除
去触媒は、たばこ煙の香喫味を低下させることなく、煙
中のCOを顕著に低減させることができる。
(Effects of the Invention) As described in detail above, including the Examples, the present invention comprises a mixed composition of a metal oxide and activated carbon as a carrier, and a mixture of a palladium salt and a copper salt supported on the carrier. This CO removal catalyst can significantly reduce CO in smoke without reducing the aroma and taste of tobacco smoke.

特許出願人     ト ビ −エ業株式会社同   
日本専売公社
Patent applicant: TOBIA GYO Co., Ltd.
Japan Monopoly Corporation

Claims (3)

【特許請求の範囲】[Claims] (1)金属酸化物と活性炭との混合組成物から成る担体
にパラジウム塩と銅塩との混合物を担持させたことを特
徴とするたばこ煙中の一酸化炭素除去剤。
(1) An agent for removing carbon monoxide from tobacco smoke, characterized in that a mixture of a palladium salt and a copper salt is supported on a carrier made of a mixed composition of a metal oxide and activated carbon.
(2)金属酸化物がMgO、Al_2O_3、SiO_
2、P_2O_5もしくは遷移金属酸化物からなる群よ
り選ばれる1種以上を含むことを特徴とする特許請求の
範囲第1項記載のたばこ煙中の一酸化炭素除去剤。
(2) Metal oxides are MgO, Al_2O_3, SiO_
2. The carbon monoxide remover in tobacco smoke according to claim 1, which contains one or more selected from the group consisting of P_2O_5 and transition metal oxides.
(3)金属酸化物が、その組成中にMgO、又はAl_
2O_3の1種以上を含むケイ酸塩鉱物である特許請求
の範囲第1項記載のたばこ煙中の一酸化炭素除去剤。
(3) The metal oxide contains MgO or Al_
The carbon monoxide remover in tobacco smoke according to claim 1, which is a silicate mineral containing one or more of 2O_3.
JP59188776A 1984-09-11 1984-09-11 Agent for removing carbon monoxide in tobacco smoke Granted JPS6168135A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP59188776A JPS6168135A (en) 1984-09-11 1984-09-11 Agent for removing carbon monoxide in tobacco smoke

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP59188776A JPS6168135A (en) 1984-09-11 1984-09-11 Agent for removing carbon monoxide in tobacco smoke

Publications (2)

Publication Number Publication Date
JPS6168135A true JPS6168135A (en) 1986-04-08
JPS6322185B2 JPS6322185B2 (en) 1988-05-11

Family

ID=16229584

Family Applications (1)

Application Number Title Priority Date Filing Date
JP59188776A Granted JPS6168135A (en) 1984-09-11 1984-09-11 Agent for removing carbon monoxide in tobacco smoke

Country Status (1)

Country Link
JP (1) JPS6168135A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2003013287A1 (en) * 2001-08-02 2003-02-20 Japan Tobacco Inc. Filter for cigarette
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
CN104905408A (en) * 2014-07-16 2015-09-16 青岛海大生物集团有限公司 Preparation method of marine organism cigarette toxin filter-out material
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

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2009123023A1 (en) * 2008-04-01 2009-10-08 日本たばこ産業株式会社 Cigarette filters
CN104307472B (en) * 2014-10-17 2016-05-11 甘成模 A kind of for cigarette filter modified molecular screen and preparation method

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS58119338A (en) * 1982-01-08 1983-07-15 Kogyo Kaihatsu Kenkyusho Co-absorbent for gas mask
JPS59136134A (en) * 1983-01-27 1984-08-04 Hidefumi Hirai Manufacture of carbon monoxide adsorbent

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS58119338A (en) * 1982-01-08 1983-07-15 Kogyo Kaihatsu Kenkyusho Co-absorbent for gas mask
JPS59136134A (en) * 1983-01-27 1984-08-04 Hidefumi Hirai Manufacture of carbon monoxide adsorbent

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
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
US8227518B2 (en) 2000-08-09 2012-07-24 British American Tobacco (Investments) Ltd. Porous carbons
US8591855B2 (en) 2000-08-09 2013-11-26 British American Tobacco (Investments) Limited Porous carbons
WO2003013287A1 (en) * 2001-08-02 2003-02-20 Japan Tobacco Inc. Filter for cigarette
CN100367886C (en) * 2001-08-02 2008-02-13 日本烟草产业株式会社 Filter for cigarette
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
CN104905408A (en) * 2014-07-16 2015-09-16 青岛海大生物集团有限公司 Preparation method of marine organism cigarette toxin filter-out material

Also Published As

Publication number Publication date
JPS6322185B2 (en) 1988-05-11

Similar Documents

Publication Publication Date Title
US8104484B2 (en) Smoking articles and smoking materials
RU2277364C2 (en) Cigarette with reduced release of side-stream smoke, having burning paper
ES2372702T3 (en) CIGARETTE COMPONENTS WITH ENCAPSULATED CATALYZER PARTICLES AND METHODS FOR MANUFACTURING AND USE.
EP0000625B1 (en) Tobacco smoke filter element with alkali ferrate supported on granular material
US20060225753A1 (en) Tobacco smoke filter and tobacco blend for altering mainstream smoke
CN101611927B (en) Catalyst capable of reducing carbon monoxide content in cigarette smoke, preparation method and application of same
JPS6168135A (en) Agent for removing carbon monoxide in tobacco smoke
HU192213B (en) Method for producing smoke filter neutralizing the materials injurious the health being in tobacco smoke particularly aldehydes
US20050121045A1 (en) Treatment of mainstream smoke constituents by use of oxygen storage and donor metal oxide oxidation catalyst
US3338246A (en) Smoking tobacco preparation
US3875949A (en) Tobacco smoke filter
JP4166365B2 (en) Cigarettes and cigarettes
KR100694546B1 (en) Method for preparing tobacco filter composition for reducing tar and nicotine
JPH09140370A (en) Tobacco element and its production
WO1998055211A1 (en) A compound for removing harmful components from cigarette smoking and a method for preparing the compound
JPS61227842A (en) Removing agent for carbon monoxide
CN101999756A (en) Absorbent for reducing hydrocyanic acid content of main stream smoke of cigarettes and use thereof
JPS5926337B2 (en) carbon monoxide remover
KR101505112B1 (en) Filtering media for smoking, cigarette filter and cigarette paper using the same
JPS5988078A (en) Tobacco filter
JPS60224483A (en) Agent for removing carbon monooxide in tobacco smoke
JPS63169980A (en) Additive containing filter for tobacco
JPS601874B2 (en) tobacco filter
KR870000839B1 (en) Manufacturing method of manufactured catalyst adding tobacco
US3842070A (en) Filtering material