JPS6333419B2 - - Google Patents
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- Publication number
- JPS6333419B2 JPS6333419B2 JP57136819A JP13681982A JPS6333419B2 JP S6333419 B2 JPS6333419 B2 JP S6333419B2 JP 57136819 A JP57136819 A JP 57136819A JP 13681982 A JP13681982 A JP 13681982A JP S6333419 B2 JPS6333419 B2 JP S6333419B2
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- Prior art keywords
- palladium
- catalyst
- pulse
- present
- oxidation
- Prior art date
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- Catalysts (AREA)
- Cigarettes, Filters, And Manufacturing Of Filters (AREA)
Description
【発明の詳細な説明】
この発明は、パラジウムあるいはパラジウム化
合物と、活性二酸化マンガンとの混合物よりなる
一酸化炭素酸化触媒の製造法の改良に関する。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to an improved method for producing a carbon monoxide oxidation catalyst comprising a mixture of palladium or a palladium compound and activated manganese dioxide.
従来、人間の健康管理の観点から、暖房器具の
排ガスや、喫煙に伴なつて発生する一酸化炭素
(以下COと略記する)を除去もしくは低減する目
的で種々のCO酸化触媒が提案されているが、ガ
ス中に共存する微量の水分によつて失活し易い、
高温域でしか活性を示さない、COの酸化活性が
十分でない、酸化活性の持続性に乏しい、あるい
は高価であるなどの欠点を持つものが多く、実用
上満足すべきCO酸化触媒は得難い現状である。 Conventionally, from the perspective of human health management, various CO oxidation catalysts have been proposed for the purpose of removing or reducing carbon monoxide (hereinafter abbreviated as CO) generated from heating equipment exhaust gas and smoking. However, it is easily deactivated by trace amounts of moisture coexisting in the gas.
Currently, it is difficult to obtain a CO oxidation catalyst that is satisfactory for practical use, as many of them have drawbacks such as being active only at high temperatures, insufficient CO oxidation activity, poor sustainability of oxidation activity, or being expensive. be.
本発明者等は、上記のような欠点の少ないCO
酸化触媒を提供すべく、鋭意研究を重ねた結果、
パラジウムあるいはパラジウム化合物と活性二酸
化マンガンとの混合物が、上述の欠点が少なく十
分満足すべきCO酸化触媒であることを見出し、
特開昭57−65331号明細書にその内容を開示した
ところである。 The present inventors have proposed a CO
As a result of intensive research to provide an oxidation catalyst,
We have discovered that palladium or a mixture of palladium compounds and activated manganese dioxide is a fully satisfactory CO oxidation catalyst with few of the above-mentioned drawbacks,
The content thereof was disclosed in Japanese Patent Application Laid-Open No. 57-65331.
しかして、上記明細書に開示したCO酸化触媒
の製造法は、あらかじめ製造した活性二酸化マン
ガン粉末をパラジウムあるいはパラジウム化合物
粉末と単に混合するか、活性二酸化マンガンをパ
ラジウム塩類水溶液に浸漬した後、溶媒を留去
し、活性二酸化マンガン表面にパラジウム塩類を
担持させるなどの方法がとられていたが、本発明
者等は、パラジウムと活性二酸化マンガンとより
なるCO酸化触媒の製造法について更に研究を進
めた結果、貴金属であるパラジウム含量を大巾に
減少させるとともに、CO酸化活性において、上
記の製造法で得られるCO酸化触媒に比し、飛躍
的にすぐれた製造法を見出し、本発明をなすに至
つた。 Therefore, the method for producing the CO oxidation catalyst disclosed in the above specification involves simply mixing pre-produced active manganese dioxide powder with palladium or palladium compound powder, or immersing active manganese dioxide in an aqueous palladium salt solution and then removing the solvent. Methods such as distilling off the CO and supporting palladium salts on the surface of active manganese dioxide have been used, but the present inventors further researched a method for producing a CO oxidation catalyst made of palladium and active manganese dioxide. As a result, we have found a production method that significantly reduces the content of palladium, which is a precious metal, and has significantly superior CO oxidation activity compared to the CO oxidation catalyst obtained by the above production method, leading to the present invention. Ivy.
すなわち本発明は、パラジウムあるいはパラジ
ウム化合物と活性二酸化マンガンとの混合物より
なるCO酸化触媒の製造法において、活性二酸化
マンガンをパラジウムあるいはパラジウム化合物
の存在下でマンガン塩より生成させることを要旨
とする。 That is, the gist of the present invention is to produce active manganese dioxide from a manganese salt in the presence of palladium or a palladium compound in a method for producing a CO oxidation catalyst consisting of a mixture of palladium or a palladium compound and active manganese dioxide.
マンガン塩からの活性二酸化マンガン(以下
MnOxと略記する)の調製法としては、二価のマ
ンガン塩と過マンガン酸カリウム(以下KMnO4
と略記する)とからアルカリ性下で調製する方法
(J.アツテンブロウら、J.Chem.Soc.、1094
(1952))、硝酸酸性下で調製する方法(T.トルマ
ン、英国特許第1315374号)および中性溶液から
調製する方法(S.ボール、Biochem.J、42 516
(1948))などが知られているが、本発明において
使用するMnOxの調製法としては、上記のアルカ
リ性、酸性、中性下いずれの方法を用いてもよ
い。 Active manganese dioxide from manganese salts (hereinafter
As for the preparation method of divalent manganese salt and potassium permanganate (hereinafter abbreviated as KMnOx) ,
abbreviated as) under alkaline conditions (J. Atztenbrough et al., J.Chem.Soc., 1094
(1952)), the method prepared under nitric acid (T. Tolman, British Patent No. 1315374) and the method prepared from neutral solutions (S. Ball, Biochem.J, 42 516
(1948)), but any of the above-mentioned alkaline, acidic, and neutral methods may be used to prepare MnOx used in the present invention.
本発明の一酸化炭素除去触媒の製造法において
用いるパラジウムとしては水溶性のパラジウム塩
が望ましいが、不溶性のパラジウム化合物、もし
くはパラジウムブラツク等を用いることもでき
る。 The palladium used in the method for producing the carbon monoxide removal catalyst of the present invention is preferably a water-soluble palladium salt, but insoluble palladium compounds, palladium black, etc. can also be used.
パラジウムないしパラジウム化合物は、あらか
じめ二価のマンガン塩水溶液に加えておいてもよ
いし、KMnO4あるいはKMnO4水溶液と二価の
マンガン塩水溶液とを混合する際に同時に加えて
もよい。 Palladium or a palladium compound may be added to the divalent manganese salt aqueous solution in advance, or may be added at the same time when mixing KMnO 4 or the KMnO 4 aqueous solution and the divalent manganese salt aqueous solution.
KMnO4あるいはKMnO4水溶液を加えること
により生じた沈殿を十分水洗した後、ろ過、乾燥
を経て使用する。このような本発明の方法により
得られた触媒中には、添加したパラジウムが完全
に残存している。 The precipitate generated by adding KMnO 4 or KMnO 4 aqueous solution is thoroughly washed with water, filtered and dried before use. In the catalyst obtained by the method of the present invention, the added palladium completely remains.
原料として用いた二価のマンガン塩とKMnO4
の量比により、生成触媒の色調や物性に変化が認
められるが触媒活性に大きな差はない。 Divalent manganese salt and KMnO 4 used as raw materials
Although there are changes in the color tone and physical properties of the produced catalyst depending on the amount ratio, there is no major difference in catalytic activity.
得られた粉末状の触媒は、そのまま用いてもよ
いし、圧縮成型や、CMC等のバインダーを用い
た公知の成型法によりペレツト状や粒状にして用
いてもよい。 The obtained powdered catalyst may be used as it is, or may be made into pellets or granules by compression molding or a known molding method using a binder such as CMC.
本発明の方法によつて得られる触媒の特性は、
本発明者等が先に開示した特開昭57−65331号明
細書記載のパラジウム/MnOx系触媒と比較し
て、パラジウム含量が1/10以下、すなわち0.5%
以下で、室温でのCO酸化活性や耐水性において
顕著な効果を有している点にある。 The properties of the catalyst obtained by the method of the present invention are as follows:
Compared to the palladium/MnOx catalyst described in JP-A-57-65331 previously disclosed by the present inventors, the palladium content is 1/10 or less, that is, 0.5%.
The following points show that it has remarkable effects on CO oxidation activity and water resistance at room temperature.
本発明によるCO酸化触媒の用途としては、防
毒マスク用のCO除去剤、車内や室内など閉鎖空
間におけるエアークリーナー用空気清浄剤、フイ
ルターやシガレツトホルダーに充填使用するたば
こ煙中COの低減剤など巾広い。 The CO oxidation catalyst of the present invention can be used as a CO remover for gas masks, as an air purifier for air cleaners in closed spaces such as inside cars or indoors, and as a reducer for CO in cigarette smoke used to fill filters and cigarette holders. Wide.
以下に実施例を用いて本発明の詳細を説明す
る。なおCO酸化活性の検定はパルス法により行
つた。すなわち一定量の乾燥触媒を内径6mmのガ
ラス管に充填した後、毎分60mlの流速でヘリウム
をキヤリヤーガスとして用い乍らCO含有ガスの
パルスを室温で通過させ、パルス中のガスの組成
変化をガスクロマトグラフイーで定量した。パル
ス容量は各10ml、パルス中のガス組成はCO5%、
O25%、残余分ヘリウムである。本明細書におい
てガス組成を表わす%は標準状態における容量%
を、その他の%は重量での割合を示す。 The details of the present invention will be explained below using Examples. The CO oxidation activity was assayed by the pulse method. Specifically, after filling a glass tube with an inner diameter of 6 mm with a certain amount of dry catalyst, a pulse of CO-containing gas is passed through it at room temperature using helium as a carrier gas at a flow rate of 60 ml per minute, and changes in the composition of the gas during the pulse are measured using a gas chromameter. It was quantified by tography. Pulse volume is 10ml each, gas composition during pulse is CO5%,
O 2 5%, remainder helium. In this specification, % representing gas composition is volume % under standard conditions.
, and other percentages are by weight.
実施例 1
10gの硝酸マンガン(Mn(NO3)2・6H2O)を
100mlの水に溶解し、これに40mgの塩化パラジウ
ムを溶解した2mlの水を加えた。さらに5mlの濃
硝酸を加えた後、溶液をよく撹拌しながら、5%
KMnO4水溶液100mlをゆつくり滴下した。滴下
終了後30分間撹拌を続け、次いで生じた沈殿を蒸
留水で十分洗浄し、過マンガン酸イオンの桃色が
ほとんど認められなくなつたら、これを減圧ろ過
した。得られた固形物を風乾し、さらに100℃で
24時間乾燥し、5.6gの本発明法による黒褐色粉
末触媒を得た。Example 1 10g of manganese nitrate (Mn(NO 3 ) 2.6H 2 O)
It was dissolved in 100 ml of water, and to this was added 2 ml of water in which 40 mg of palladium chloride was dissolved. After adding another 5 ml of concentrated nitric acid, while stirring the solution well,
100 ml of KMnO 4 aqueous solution was slowly added dropwise. Stirring was continued for 30 minutes after the dropwise addition was completed, and the resulting precipitate was thoroughly washed with distilled water, and when the pink color of permanganate ions was almost no longer observed, it was filtered under reduced pressure. The obtained solid was air-dried and further heated at 100℃.
After drying for 24 hours, 5.6 g of a blackish brown powder catalyst according to the present invention was obtained.
このものの原子吸光法による分析では加えたパ
ラジウム元素が完全に残存しており、その含有率
は得られた触媒中0.43%であつた。 Analysis of this material by atomic absorption spectroscopy showed that the added palladium element remained completely, and its content was 0.43% in the obtained catalyst.
この触媒100mgを用い、パルス法でCO酸化活性
を調べた。このパルス試験の結果、10パルス以上
にわたりパルス中のCOは完全に消失し、COと等
モルのCO2の生成が認められた。 Using 100 mg of this catalyst, the CO oxidation activity was examined using the pulse method. As a result of this pulse test, the CO in the pulse completely disappeared over 10 pulses or more, and it was observed that CO 2 with an equimolar amount of CO was produced.
一方対照として、5gのMnOxを5%硝酸パラ
ジウム水溶液10mlに浸漬した後、減圧下で乾燥し
9.1%の硝酸パラジウムを含有するMnOx触媒を
調製した。このものを100mgはかりとり、同様に
パルス試験に供したところ、第1パルス中のCO
低減率は86%であり、パルス回数とともに徐々に
活性は低下、第5パルスにおけるCO低減率は76
%であつた。 On the other hand, as a control, 5 g of MnOx was immersed in 10 ml of 5% palladium nitrate aqueous solution and then dried under reduced pressure.
A MnOx catalyst containing 9.1% palladium nitrate was prepared. When 100 mg of this material was weighed and subjected to the same pulse test, the CO during the first pulse was
The reduction rate was 86%, and the activity gradually decreased with the number of pulses, and the CO reduction rate at the 5th pulse was 76%.
It was %.
実施例 2
10gの硫酸マンガン(MnSO4・4〜5H2O)を
100mlの水に溶解し、これに40%水酸化ナトリウ
ム水溶液10mlと50mgの硝酸パラジウムを加えた。
この溶液をよく撹拌しつつ5%KMnO4水溶液
200mlをゆつくり滴下した。以下実施例1で述べ
たと同様の処理を行ない、本発明による黒褐色の
乾燥粉末触媒6.0gを得た。この触媒中のパラジ
ウム含量は0.37%であつた。Example 2 10g of manganese sulfate ( MnSO4.4 ~ 5H2O )
It was dissolved in 100 ml of water, and 10 ml of 40% aqueous sodium hydroxide solution and 50 mg of palladium nitrate were added thereto.
While stirring this solution well, add 5% KMnO 4 aqueous solution.
200ml was slowly dripped. Thereafter, the same treatment as described in Example 1 was carried out to obtain 6.0 g of a blackish brown dry powder catalyst according to the present invention. The palladium content in this catalyst was 0.37%.
この触媒100mgをはかりとり、パルス法でCO酸
化活性を調べたところ、10パルス以上にわたり、
パルス中のCOを完全にCO2に変換した。 When 100 mg of this catalyst was weighed and the CO oxidation activity was examined using the pulse method, it was found that over 10 pulses,
The CO in the pulse was completely converted to CO2 .
実施例 3
実施例1で得た本発明法による乾燥触媒を22℃
で相対湿度60%の室内に一週間放置したところ、
14%の重量増加が認められた。このうちから100
mgをはかりとり、パルス法でCO酸化活性を測定
したところ、第1パルスではCOの37%がCO2に
変換された。引き続いて第2パルスを通過させた
ところ、58%のCOがCO2に変換された。パルス
回数の増加とともにCO酸化活性が高まり、5パ
ルス目で完全にCOのピークが消失した。Example 3 The dried catalyst obtained by the method of the present invention obtained in Example 1 was heated at 22°C.
When I left it in a room with relative humidity of 60% for a week,
A 14% weight increase was observed. 100 out of these
When mg was weighed and the CO oxidation activity was measured using the pulse method, 37% of the CO was converted to CO 2 in the first pulse. A second pulse was subsequently passed and 58% of the CO was converted to CO2 . CO oxidation activity increased as the number of pulses increased, and the CO peak completely disappeared at the fifth pulse.
一方、実施例1で用いたと同様の対照品を一週
間相対湿度60%の室内に放置した後、そのうちか
ら100mgをはかりとりパルス試験を行つた。その
結果第1パルス中のCOのCO2への変換率は22%
であり、第10パルスでのCO変換率80%がほとん
ど定常的活性であつた。 On the other hand, a control product similar to that used in Example 1 was left in a room with a relative humidity of 60% for one week, and then 100 mg was weighed out and a pulse test was conducted. As a result, the conversion rate of CO to CO 2 during the first pulse was 22%.
The CO conversion rate at the 10th pulse was 80%, indicating almost steady activity.
実施例 4
10gの酢酸マンガン(Mn(CH3COO)2・
4H2O)に、50mgの塩化パラジウムを溶解した10
mlの0.1N塩酸と水150mlを加えた。混合液を撹拌
しながら5gのKMnO4粉末をゆつくりと加え
た。30分間撹拌を続けた後、生じた沈殿を蒸留水
で傾斜法を用いて洗浄し、次いでろ過した。得ら
れた沈澱物を風乾し、さらに110℃で24時間乾燥
し、本発明法による黒褐色粉末触媒5.8gを得た。
触媒中のパラジウム含量は0.50%であつた。この
触媒100mgをはかりとり、パルス法でCO酸化活性
を調べたところ、10パルス以上にわたり、COを
完全にCO2に変換した。Example 4 10g of manganese acetate (Mn(CH 3 COO) 2 .
4H 2 O) with 50 mg of palladium chloride dissolved in 10
ml of 0.1N hydrochloric acid and 150 ml of water were added. While stirring the mixture, 5 g of KMnO 4 powder was slowly added. After continued stirring for 30 minutes, the resulting precipitate was washed with distilled water using a decanting method and then filtered. The obtained precipitate was air-dried and further dried at 110° C. for 24 hours to obtain 5.8 g of a blackish brown powder catalyst according to the method of the present invention.
The palladium content in the catalyst was 0.50%. When 100 mg of this catalyst was weighed and the CO oxidation activity was examined using the pulse method, CO was completely converted to CO 2 over 10 pulses or more.
実施例 5
実施例2と同様にして製造した黒褐色粉末触媒
3gに、2%CMC水溶液2mlを加えてよく練り、
16メツシユのふるいを用いてふるい目から押し出
し、直径約1mmの顆粒状に成型した。これを110
℃で16時間乾燥した後、そのうちから300mgをは
かりとり内径6mmのガラス管に充填した。このガ
ラス管の一端に日本専売公社製紙巻たばこ、商品
名「マイルドセブン」をセロハンテープで取りつ
けた。ガラス管の他端を自動喫煙装置に挿入し、
標準喫煙条件(1パフ/分、2秒/パフ、35ml/
パフ、すい殻長30mm)で触媒層を通過して得られ
た煙のうち、ガス相を非分散型赤外分光光度計
(富士電機計装KK製)で分析した。Example 5 2 ml of a 2% CMC aqueous solution was added to 3 g of a dark brown powder catalyst produced in the same manner as in Example 2, and the mixture was thoroughly kneaded.
The mixture was extruded through a 16-mesh sieve and formed into granules with a diameter of about 1 mm. This is 110
After drying at ℃ for 16 hours, 300 mg of the mixture was weighed and filled into a glass tube with an inner diameter of 6 mm. To one end of this glass tube, a cigarette manufactured by Japan Monopoly Corporation (trade name: Mild Seven) was attached with cellophane tape. Insert the other end of the glass tube into the automatic smoking device,
Standard smoking conditions (1 puff/min, 2 seconds/puff, 35ml/
The gas phase of the smoke obtained by passing through the catalyst layer using a puff (shell length: 30 mm) was analyzed using a non-dispersive infrared spectrophotometer (manufactured by Fuji Electric Keiso KK).
本発明による触媒のかわりに、実施例1で対照
試料として用いた触媒300mgを充填したガラス管
に「マイルドセブン」を取り付けたものをコント
ロール1、また100mgの活性炭のみを充填したガ
ラス管に「マイルドセブン」を取り付けたものを
コントロール2として同様にガス相を分析した。 Instead of the catalyst according to the present invention, "Mild Seven" was attached to a glass tube filled with 300 mg of the catalyst used as a control sample in Example 1 as Control 1, and "Mild Seven" was attached to a glass tube filled only with 100 mg of activated carbon. The gas phase was analyzed in the same manner using the control 2 as control 2.
この結果、コントロール1の煙中COはコント
ロール2に比べて32%減少していたが、本発明に
よる触媒を取り付けたシガレツト煙中のCO濃度
はコントロール2に比べて53%減少していた。 As a result, the CO in the smoke of Control 1 was reduced by 32% compared to Control 2, but the CO concentration in the smoke of cigarettes equipped with the catalyst of the present invention was reduced by 53% compared to Control 2.
実施例 6
10gの硝酸マンガンに50mgのパラジウムブラツ
クを加え、よく撹拌しつつ、これに5%KMnO4
水溶液100mlを約10分間で滴下した。滴下終了後
30分間撹拌を続けた後、生成した沈殿を蒸留水で
十分洗浄し、次いでろ過した。次いで100℃で24
時間乾燥して本発明法による黒色の粉末触媒6.0
gを得た。この触媒中には0.81%のパラジウムが
含有されていた。この触媒100mgをはかりとりパ
ルス試験を行つた。Example 6 Add 50 mg of palladium black to 10 g of manganese nitrate, and add 5% KMnO 4 to this while stirring well.
100 ml of the aqueous solution was added dropwise over about 10 minutes. After dripping
After continued stirring for 30 minutes, the generated precipitate was thoroughly washed with distilled water and then filtered. Then 24 at 100℃
Black powder catalyst according to the invention method after drying for 6.0 hours
I got g. This catalyst contained 0.81% palladium. 100 mg of this catalyst was weighed and a pulse test was conducted.
一方、特開昭57−56331号の実施例1と同様の
方法、すなわち30gの硫酸マンガン(MnSO4・
4H2O)を溶かした350mlの水に、35mlの濃硝酸
を加え、次いで21gの粉末状KMnO4を加えて調
製したMnOx粉末5gに50mgのパラジウムブラツ
クをよく混合し、110℃で24時間乾燥したものを
対照として100mgはかりとりパルス試験を行つた。 On the other hand, 30 g of manganese sulfate ( MnSO4 .
4H2O ) was dissolved in 350ml of water, 35ml of concentrated nitric acid was added, and then 21g of powdered KMnO4 was added. 50mg of palladium black was mixed well with 5g of MnOx powder, and the mixture was dried at 110℃ for 24 hours. As a control, we weighed 100 mg and conducted a pulse test.
この結果、対照の第1パルス中COの低減率は
32%であつたのに対し、本発明法により製造した
触媒は、第1パルス中のCOを100%CO2に変換し
た。 As a result, the reduction rate of CO during the first pulse of the control was
The catalyst produced by the method of the present invention converted 100% of the CO in the first pulse to CO2 , compared to 32%.
以上の実施例から明らかなように、本発明の方
法によつて製造されたCO酸化触媒は、特開昭57
−56331号により製造した触媒に比べて、低いパ
ラジウム含有率でしかも常温でガス中のCOを効
率よく酸化する能力を持つとともに、保存時の雰
囲気中の水分に対しても高い抵抗性を示すなど顕
著な効果を有することが実証された。 As is clear from the above examples, the CO oxidation catalyst produced by the method of the present invention is
-Compared to the catalyst manufactured by No. 56331, it has a lower palladium content, has the ability to efficiently oxidize CO in gas at room temperature, and exhibits high resistance to moisture in the atmosphere during storage. It has been demonstrated that it has a significant effect.
Claims (1)
二酸化マンガンからなる一酸化炭素の酸化触媒の
製造方法において、活性二酸化マンガンを、パラ
ジウムあるいはパラジウム化合物の存在する溶液
中で、二価のマンガン塩と過マンガン酸カリウム
を反応させて生成せしめることを特徴とする一酸
化炭素の酸化触媒の製造法。1. In a method for producing a carbon monoxide oxidation catalyst consisting of palladium or a palladium compound and active manganese dioxide, active manganese dioxide is reacted with a divalent manganese salt and potassium permanganate in a solution containing palladium or a palladium compound. 1. A method for producing a carbon monoxide oxidation catalyst, the method comprising: producing a carbon monoxide oxidation catalyst;
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP57136819A JPS5929036A (en) | 1982-08-07 | 1982-08-07 | Preparation of catalyst for removing carbon monooxide |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP57136819A JPS5929036A (en) | 1982-08-07 | 1982-08-07 | Preparation of catalyst for removing carbon monooxide |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5929036A JPS5929036A (en) | 1984-02-16 |
| JPS6333419B2 true JPS6333419B2 (en) | 1988-07-05 |
Family
ID=15184243
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP57136819A Granted JPS5929036A (en) | 1982-08-07 | 1982-08-07 | Preparation of catalyst for removing carbon monooxide |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS5929036A (en) |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| FR2841438A1 (en) * | 2002-06-26 | 2004-01-02 | Rhodia Elect & Catalysis | CIGARETTE COMPRISING A CATALYST FOR THE TREATMENT OF SMOKE |
-
1982
- 1982-08-07 JP JP57136819A patent/JPS5929036A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS5929036A (en) | 1984-02-16 |
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