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JPS6322185B2 - - Google Patents
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JPS6322185B2 - - Google Patents

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Publication number
JPS6322185B2
JPS6322185B2 JP59188776A JP18877684A JPS6322185B2 JP S6322185 B2 JPS6322185 B2 JP S6322185B2 JP 59188776 A JP59188776 A JP 59188776A JP 18877684 A JP18877684 A JP 18877684A JP S6322185 B2 JPS6322185 B2 JP S6322185B2
Authority
JP
Japan
Prior art keywords
carrier
catalyst
oxide
activated carbon
metal oxide
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
JP59188776A
Other languages
Japanese (ja)
Other versions
JPS6168135A (en
Inventor
Kenichiro Sugimori
Masaru Yamamoto
Ikuo Horii
Hajime Matsushita
Shigeo Ishiguro
Hiroshi Ichise
Shigenobu Mizusaki
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
Original Assignee
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 Japan Tobacco Inc filed Critical Japan Tobacco Inc
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)

Description

【発明の詳細な説明】[Detailed description of the invention]

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。 (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
つ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り至らしめる。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。 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。 (従来の技術) 従来、かかる観点からたばこ主流煙中のCO濃
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。 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。 1 COの生成の少ない原料を選択して使用する
方法。 2 フイルター部分に開孔を設け、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つ
て低減する方法。 3 酸化触媒や酸化剤あるいは吸着剤をフイルタ
ー部分又はシガレツトホルダー等に充填あるい
は保持してCOを酸化又は捕促して低減する方
法。 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。 しかし、3の方法について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在存する
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。 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
るホプカリツ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(Brit.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
つた。 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、いわゆるワツカー(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(レドツクス)系内に有効に取り込
み、気相中の酸素によつてCOを酸化するという
機構が提案されている(ジヤーナル・エア・ポリ
ユーシヨン・コントロール・アソシエーシヨン
(J.Air Pollution Control Assoc.)28、253
(1978))。 このワツカー型触媒は、基本的には基質に対す
る活性化合物としてPdX2又はM2PdX2(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、それに対するレドツクス対として
CuX2(Xはハロゲン原子)が用いられる。 一般に金属酸化を用いた低温での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低減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。 このようなワツカー型触媒をCOの低減用に使
用した発明には、COによつ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54−110400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
られるワツカー型触媒は、溶液としての均一系、
あるいはアルミナ、シリカ、アルミノケイ酸塩、
モレキユラーシーブ、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。 しかし、かかる従来の発明によるワツカー型触
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γ−アルミナを用い
た場合にはCOの酸化活性が高く、たばこのフイ
ルター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
ばこ香喫味へ及ぼす悪影響は認められなかつたも
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。 〔発明が解決しようとする問題点〕 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CO
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。 CO除去剤を実際にたばこ、主としてシガレツ
トに適用するに際しては、CO除去剤を構成する
CO酸化触媒を担体に保持させてシガレツトのフ
イ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ツ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
詳細に研究を行なつた結果、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つた。 〔問題点を解決するための手段〕 すなわち、本発明のたばこ煙中の一酸化炭素除
去剤は、パラジウム塩と銅塩とを担体上に担持さ
せた触媒であつて、該担体として金属酸化物と活
性炭との混合組成物を用いたことを特徴とするも
のである。 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500〜1300
m2/gを有するものであることが望ましい。 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(Al2O3)、シリカ(SiO2)、五酸化隣(P2O5
及び遷移金属酸化物または複合酸化物からなる群
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
(Al2O3・2SiO2・2H2O)、石綿(MgO・SiO2)、
ゼピオライト(Mg8H2(Si4O113・3H2O)、ゼオ
ライト(Na2Al2Si3O10・xH2O)、ケイソウ土
(SiO2を主成分とし、組成中にAl2O3、Fe2O3
MgO、CaOを含む。)などの使用が好ましい。 又、遷移金属酸化物としては、例えば、酸化銅
(CuO)、酸化ジルコニウム(ZrO2)、酸化チタン
(TiO2)、酸化ニツケル(NiO)、酸化コバルト
(C0O)等を好適に使用することができる。 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
末と金属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ゲル、アル
ミナゾル、水ガラスなどで練り固め、20〜60メツ
シユ程度の粒状に成型、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。 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。 次に、本発明に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〜
0.2m mol/gの範囲が良く、又、銅塩について
は0.1〜2.0m 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。 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
び銅塩を溶解し、この全量を担体の細孔内に吸収
させる、いわゆるポアフイリング法や、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。 以上のようにして調製された本発明のCO除去
剤はたばこのフイルター部分あるいはシガレツト
ホルダー等に充填して使用に供する。 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CO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。 (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。 調製例 1 200メツシユ以下の粒度に粉砕したヤシガラ炭
10g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35ml
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メツシ
ユの粒度に揃え、担体Aを得た。 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15g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35ml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。次いで放冷した後粉砕し、20〜60
メツシユに粒度を揃え、担体Bを得た。 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10g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30ml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。 調整例 4 200メツ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35mlを加え、充
分混練した後、150℃で乾燥した。次いで粉砕し、
20〜60メツシユに粒度を揃え、担体Dを得た。 調製例 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30mlを加えて充分混練した後、
120℃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つた。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。 調製例 6 200メツ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)5gおよび酸化ニツケル(NiO)5gを乾式
にて充分混合した後、濃度30重量%のシリカゾル
30ml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時間熱処理を行なつた
後、粉砕して20〜60メツシユの粒度に揃え、担体
Fを得た。 (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/濃度の塩化パラジウム
水溶液2m、1モル/濃度の塩化第二銅水溶
液1mおよび1モル/濃度の硝酸銅水溶液1m
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40℃で乾固し、本発明の担体担
持触媒A′,B′,C′,D′およびE′得た。担体Fに
ついては、担体3gに対して銅塩として1モル/
の塩化第二銅と硫酸銅の水溶液をそれぞれ
1.5m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。 (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200mgを、製
品シガレツト(商品名ハイライト)のフイルター
部分に充填した。このシガレツトを自動喫煙装置
に接続し、標準喫煙条件(35m吸引/1パフ、
2秒/1パフ)で6パフ吸煙させ、得られた主流
煙ガス中のCO濃度を非分散型赤外分光光度計
(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イ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つた。
The present invention relates to a remover that selectively removes carbon monoxide from tobacco smoke generated during smoking without adversely affecting the aroma and taste of tobacco. (Industrial application field) Carbon monoxide (hereinafter also simply referred to as CO), which is generally generated by incomplete combustion of carbon or carbon-containing compounds.
Because it binds tightly to hemoglobin in the blood and significantly inhibits the blood's role in oxygen absorption and transport, it can cause acute poisoning symptoms such as headaches and dizziness, and in severe cases can even lead to death. Also, CO
It is said that long-term exposure to these substances can cause chronic heart disease. This CO is contained in a few percent of the so-called mainstream smoke that smokers directly inhale when they smoke cigarettes, and although it is significantly diluted by the air that is simultaneously inhaled before reaching the human lungs. It is believed that this contributes to the chronic increase in the concentration of CO-bound hemoglobin in the blood of smokers, and there is a desire to reduce CO from tobacco smoke. (Prior Art) From this point of view, many attempts have been made to reduce the CO concentration in mainstream cigarette smoke.
Many proposals have been made in patent specifications and the like. These proposals can be broadly classified as follows. 1. A method of selecting and using raw materials that generate less CO. 2. A method of suppressing the generation of CO by creating holes in the filter part or using high porosity wrapping paper, or reducing the generated CO by diffusion from the wrapping paper. 3. A method of reducing CO by oxidizing or capturing it by filling or holding an oxidation catalyst, oxidizing agent, or adsorbent in a filter part or cigarette holder, etc. Among methods 1 to 3 above, methods 1 and 2 have been extensively studied to date, and some of them have been commercialized. However, the current situation is that no definitively effective method has yet been found for method 3. The reasons for this include the extremely short contact time between tobacco smoke and the oxidation catalyst and other fillers, the presence of inhibiting components such as moisture and tar in the surrounding environment, and 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. Examples of substances that have been proposed for the purpose of reducing CO in tobacco smoke by method 3 above include the so-called hopcalite-based composite oxide catalyst (Japanese Patent Laid-Open No. 1983-1972), 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 (Brit.pat. No. 1315374)
However, all of them are significantly deactivated by moisture, and follow-up tests show almost no removal effect. or,
There are also many disclosures regarding precious metal supported catalysts (Japanese Patent Application Laid-Open No. 1983-1999)
-73344, 53-149192, 55-137039)
However, as a result of further testing, it became clear that sufficient effectiveness could not be expected in removing CO from smoke. However, on the other hand, the so-called Wacker type catalyst, which was developed for the purpose of synthesizing acetaldehyde using ethylene as a raw material and using oxygen in the gas phase, has high activity against CO oxidation. ,
A mechanism has been proposed in which water is effectively introduced into the redox system and CO is oxidized by oxygen in the gas phase (J.Air Pollution Control Association). Assoc.) 28, 253
(1978)). This Watzker type catalyst basically uses PdX 2 or M 2 PdX 2 (X is a halogen atom, M is a group Ia metal in the periodic table) as an active compound for the substrate, and also as a redox pair for the substrate.
CuX 2 (X is a halogen atom) is used. The presence of moisture, which is generally considered undesirable in low-temperature CO oxidation using metal oxidation, works effectively in this type of catalyst;
It can be said to be an ideal catalyst when used under humid conditions such as CO reduction. Inventions using such Watzker-type catalysts for CO reduction include the addition of copper salts other than copper halides (mainly copper nitrate) to promote reoxidation of palladium salts reduced by CO. A method of increasing activity by adding three components (Japanese Patent Application Laid-open No. 50-33990), an example of adding tin ions, etc. to promote reoxidation (Japanese Patent Application Laid-open No. 110400/1983), 1
There is an example (Japanese Unexamined Patent Publication No. 55-97252) in which a copper salt of 20% is coexisting. The Watzker type catalyst seen in these inventions related to CO oxidation is a homogeneous system as a solution,
Or alumina, silica, aluminosilicate,
It is used as a heterogeneous catalyst supported on various carriers such as molecular sieves and activated carbon. However, when a catalyst in which the Watzker type catalyst according to the conventional invention is supported on the above-mentioned carrier, which is known as a catalyst carrier, is used for the purpose of reducing CO in mainstream cigarette smoke, the effect is not necessarily sufficient. On the other hand, when γ-alumina is used as a carrier, the oxidation activity of CO is high, and the reduction rate of CO in tobacco smoke when filled in the filter part of the cigarette is also extremely high, but it does not significantly reduce the aroma and taste of tobacco smoke. It has the disadvantage of lowering This is considered to be due to the physical and chemical properties of the γ-alumina surface. Furthermore, when activated carbon alone is used as a carrier, although no adverse effect on tobacco flavor was observed, there is a drawback that a sufficient CO reduction effect cannot be obtained. [Problems to be solved by the invention] The present invention has been made in view of the above-mentioned problems of conventional catalysts for reducing CO2.
The purpose of the present invention is to provide a CO removal agent that has a high reduction effect and does not adversely affect the aroma and taste of tobacco smoke. When actually applying a CO remover to cigarettes, mainly cigarettes, the CO remover is
It is necessary to hold the CO oxidation catalyst on a carrier and fill it in the filter or holder of a cigarette. Therefore, the present inventors investigated in detail the relationship between the type of carrier on which the catalyst should be supported, the oxidation activity of CO, and the effect on the aroma and taste of tobacco smoke regarding the Watzker type catalyst consisting of a combination of palladium salt and copper salt. As a result of research, it was discovered that when a mixed composition of metal oxide and activated carbon is used as a carrier, a highly active CO removal catalyst can be obtained that does not adversely affect the aroma and taste, leading to the present invention. Ivy. [Means for Solving the Problems] That is, the agent for removing carbon monoxide from tobacco smoke of the present invention is a catalyst in which a palladium salt and a copper salt are supported on a carrier, and the carrier is a metal oxide. and activated carbon. 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. In addition, the specific surface area of these activated carbons is approximately 500 to 1300 according to the BET measurement method.
m 2 /g. Next, metal oxides that are mixed with activated carbon include magnesium oxide (MgO), aluminum oxide (Al 2 O 3 ), silica (SiO 2 ), and pentoxide (P 2 O 5 ).
and transition metal oxides or composite oxides, or silicate minerals containing one or more of magnesium or aluminum in the composition, such as kaolinite (Al 2 O 3・2SiO 2・2H 2 O), asbestos (MgO・SiO 2 ),
Zepiolite (Mg 8 H 2 (Si 4 O 11 ) 3・3H 2 O), zeolite (Na 2 Al 2 Si 3 O 10・xH 2 O), diatomaceous earth (mainly composed of SiO 2 , with Al 2 in the composition) O3 , Fe2O3 ,
Contains MgO and CaO. ) etc. are preferably used. Further, as the transition metal oxide, for example, copper oxide (CuO), zirconium oxide (ZrO 2 ), titanium oxide (TiO 2 ), nickel oxide (NiO), cobalt oxide (C 0 O), etc. are preferably used. be able to. Next, any known method may be used to solidify the activated carbon and the metal oxide to form a carrier. For example, the activated carbon powder and the metal oxide powder may be mixed in an aqueous solution of a water-soluble polymer such as polyvinyl alcohol, silica gel, alumina sol, water glass, etc. Knead and harden, form into granules of about 20 to 60 mesh, and pre-dry to about 100 mesh.
A method such as heat treatment at a temperature of .degree. C. or higher may be employed. 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. Next, in the present invention, the supported amount of the catalyst component contained in the CO removing agent is 0.01 to 0.01 for palladium salt.
A good range is 0.2 m mol/g, and for copper salts, 0.1 to 2.0 m mol/g, preferably 0.4 to 1.0 m
The range of mol/g is good. Furthermore, as types of palladium salts and copper salts, chlorides, nitrates, sulfates, etc. can be used. As a method for supporting the above metal salt catalyst on a mixed composition carrier of metal oxide and activated carbon, the pore volume of the carrier is measured in advance by the BET method, etc., and palladium is added to a volume of water approximately equal to that volume. The so-called pore-filling method involves dissolving the salt and copper salt and absorbing the entire amount into the pores of the carrier, or by immersing the carrier in a mixed aqueous solution of palladium salt and copper salt.
A method such as the so-called impregnation method, in which the solution is concentrated using a rotary evaporator or the like and salts are precipitated onto the carrier, can be applied, but the latter impregnation method is more convenient and It is excellent because there is no need to set any particular restrictions on the concentration. The CO remover of the present invention prepared as described above is used by filling it into a cigarette filter or a cigarette holder. The present invention will be explained in more detail with reference to Examples below. Using the CO remover of the present invention not only makes it possible to significantly reduce CO in tobacco smoke, but also improves the aroma and taste of tobacco smoke. has no negative effect,
In fact, it was found to have excellent effects such as reducing the irritation caused by smoke. (Example) (1) Preparation of carriers First, six types of catalyst carriers A according to the present invention made of a mixed composition of metal oxide and activated carbon were prepared by the following method.
~F was prepared. Preparation example 1 Coconut husk charcoal crushed to a particle size of 200 mesh or less
After thoroughly mixing 10g and 10g of diatomaceous earth powder with a dry mixer, 35ml of silica sol with a concentration of 30% by weight is obtained.
was added. After thoroughly kneading this mixture, 120
It was dried and solidified at ℃. Next, the carrier A was obtained by pulverizing the particles to a particle size of 20 to 60 meshes. Preparation Example 2 15 g of coal-based activated carbon pulverized to a particle size of 200 mesh or less and 5 g of silica-alumina powder were thoroughly mixed in a dry mixer, and then 35 ml of silica sol having a concentration of 20% by weight was added and further thoroughly kneaded. This kneaded material
After drying at 120°C, the temperature was raised to 300°C and heat treated for an additional 2 hours. Next, let it cool and crush it to 20 to 60
The particle size was made uniform in the mesh to obtain carrier B. Preparation Example 3 After thoroughly mixing 10 g of coal-based activated carbon pulverized to a particle size of 200 mesh or less and 10 g of cupric oxide (CuO), 30 ml of silica sol having a concentration of 30% by weight was added and further thoroughly kneaded. This kneaded material was dried at 120°C, then ground, and the particle size was adjusted to 20 to 60 mesh.
I got it. Adjustment example 4 Coconut husk charcoal crushed to a particle size of 200 mesh or less
Magnesium pyrophosphate (2MgO・P 2 O 5 ) in 10g
10 g of powder and 35 ml of No. 3 sodium silicate were added, thoroughly kneaded, and then dried at 150°C. Then crush it,
The particle size was adjusted to 20 to 60 mesh to obtain carrier D. Preparation example 5 Coal charcoal crushed to a particle size of 200 mesh or less
After adding 30ml of silica sol with a concentration of 30% by weight to 10g and 10g of kaolinite powder and thoroughly kneading,
Dry at 120°C. Then, heat treatment was further performed at 800° C. for 2 hours in a nitrogen stream. After cooling, crush it for 20 minutes.
A carrier E was obtained by adjusting the particle size to ~60 mesh. Preparation example 6 Coal charcoal crushed to a particle size of 200 mesh or less
After thoroughly mixing 10 g of zirconium oxide (ZrO 2 ), 5 g of zirconium oxide (ZrO 2 ) prepared to the same particle size, and 5 g of nickel oxide (NiO) in a dry method, a silica sol with a concentration of 30% by weight was prepared.
30 ml was added, thoroughly kneaded, and dried at 120°C. Next, this was further heat-treated at 300° C. for 2 hours, and then pulverized to a particle size of 20 to 60 mesh to obtain carrier F. (2) Preparation of carrier-supported catalyst For each 3 g of the above-mentioned supports A to E prepared by the method in (1), 2 m of a 0.1 mol/concentration palladium chloride aqueous solution, 1 m of a 1 mol/concentration cupric chloride aqueous solution, and 1 m of 1 mol/concentration copper nitrate aqueous solution
A mixed aqueous solution consisting of the following was added to impregnate the carrier with the catalyst component consisting of the palladium salt and the copper salt. Each was dried at 40°C to obtain carrier-supported catalysts A', B', C', D' and E' of the present invention. Regarding carrier F, 1 mol/copper salt per 3 g of carrier
aqueous solutions of cupric chloride and copper sulfate, respectively.
Catalyst F' was obtained in the same manner as in the case of supports A to E except that 1.5 m was used. (3) Test for removing CO from tobacco smoke 200 mg each of the carrier-supported catalysts of the present invention obtained in (2) were filled into the filter portion of a product cigarette (trade name Highlight). Connect this cigarette to an automatic smoking device and set it under standard smoking conditions (35m suction/1 puff,
Six puffs were inhaled at a rate of 2 seconds/1 puff), and the CO concentration in the resulting mainstream smoke gas was measured using a non-dispersive infrared spectrophotometer (ND-IR). Furthermore, using γ-alumina and coconut shell charcoal as carriers, A to E
In the same way as in the case of the carrier, the CO concentration was measured in the same way using the catalyst supporting the catalyst components as a comparison sample, and
The CO concentration was similarly measured using a filter filled with the same amount of coconut husk charcoal as a control. From the above measured values, the CO removal rate relative to the control was calculated and the results were as shown in Table 1.

【表】 なお、CO除去率は次式を用いて算出した。 CO除去率(%) =(1−試料のCO濃度/対照のCO濃度)×100 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イルターは、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
有するものであつた。 (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
味評価を行なつた結果を第2表に示した。
[Table] The CO removal rate was calculated using the following formula. CO removal rate (%) = (1 - CO concentration of sample / CO concentration of control) x 100 As is clear from the results in Table 1, the filter filled with the carrier-supported catalyst of the present invention has only coconut husk charcoal as a carrier. The catalyst showed a CO removal rate 2 to 2.7 times higher than that of the γ-alumina support. (4) Flavor and taste test for tobacco smoke Samples obtained in the same manner as in (3) were evaluated by 10 trained specialized sensory panel members, and the results are shown in Table 2. .

【表】【table】

【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
炭フイルターと差がなく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。 (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。
[Table] As seen in the evaluation in Table 2, the carrier-supported catalyst of the present invention has almost no negative effect on the flavor of tobacco smoke, and all the panelists agreed that the catalyst had almost no negative effect on the aroma and flavor of tobacco smoke, and all the panelists agreed that there was no difference in flavor and aroma from the control product, the coconut husk charcoal filter. It was rated as excellent. On the other hand, it has been found that the γ-alumina carrier catalyst has a significant negative effect on the aroma and taste of cigarettes. (Effects of the invention) As described above in detail including the examples,
A mixed composition of metal oxide and activated carbon is used as a carrier,
The CO removal catalyst of the present invention, which is made by supporting a mixture of palladium salt and copper salt, can significantly reduce CO in smoke without reducing the aroma and taste of tobacco smoke.

Claims (1)

【特許請求の範囲】 1 パラジウム塩と銅塩とを担体上に担持させた
触媒であつて、該担体として金属酸化物と活性炭
との混合組成物を用いたことを特徴とする、たば
こ煙中の一酸化炭素除去剤。 2 金属酸化物が、マグネシウム、アルミニウ
ム、ケイ素、リンおよび遷移金属元素からなる群
より選ばれた1種以上の金属を含む酸化物または
複合酸化物である、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 金属酸化物が、マグネシウムまたはアルミニ
ウムの少なくともいづれか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。
[Claims] 1. A catalyst in which a palladium salt and a copper salt are supported on a carrier, characterized in that a mixed composition of a metal oxide and activated carbon is used as the carrier. Carbon monoxide remover. 2. The cigarette according to claim 1, wherein the metal oxide is an oxide or composite oxide containing one or more metals selected from the group consisting of magnesium, aluminum, silicon, phosphorus, and transition metal elements. Carbon monoxide remover in smoke. 3. The carbon monoxide remover in tobacco smoke according to claim 1, wherein the metal oxide is a silicate mineral containing at least either magnesium or aluminum.
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 JPS6168135A (en) 1986-04-08
JPS6322185B2 true 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)

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* Cited by examiner, † Cited by third party
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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
CA2455412C (en) * 2001-08-02 2008-01-29 Japan Tobacco Inc. Cigarette 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
CN104905408B (en) * 2014-07-16 2019-02-12 青岛海大生物集团有限公司 A kind of marine organisms cigarette filters the preparation method of malicious material

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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

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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
CN104307472A (en) * 2014-10-17 2015-01-28 甘成模 Modified molecular sieve used in cigarette filter tip, and preparation method of modified molecular sieve used in cigarette filter tip
CN104307472B (en) * 2014-10-17 2016-05-11 甘成模 A kind of for cigarette filter modified molecular screen and preparation method

Also Published As

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