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JPH0373336B2 - - Google Patents
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JPH0373336B2 - - Google Patents

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Publication number
JPH0373336B2
JPH0373336B2 JP58180607A JP18060783A JPH0373336B2 JP H0373336 B2 JPH0373336 B2 JP H0373336B2 JP 58180607 A JP58180607 A JP 58180607A JP 18060783 A JP18060783 A JP 18060783A JP H0373336 B2 JPH0373336 B2 JP H0373336B2
Authority
JP
Japan
Prior art keywords
catalyst
manganese dioxide
cobalt
ruthenium
nickel
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 - Lifetime
Application number
JP58180607A
Other languages
Japanese (ja)
Other versions
JPS6072977A (en
Inventor
Hajime Matsushita
Shigeo Ishiguro
Ayumi Iwashita
Yasuhei Nitori
Hiroshi Ichise
Akira Izumi
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 JP58180607A priority Critical patent/JPS6072977A/en
Publication of JPS6072977A publication Critical patent/JPS6072977A/en
Publication of JPH0373336B2 publication Critical patent/JPH0373336B2/ja
Granted legal-status Critical Current

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  • Carbon And Carbon Compounds (AREA)
  • Catalysts (AREA)

Description

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

[産業上の利用分野] 本発明は、ガス中の一酸化炭素(以下CO)を
選択的に酸化し、無毒の二酸化炭素(以下CO2
に変換させる酸化触媒の製造方法に関する。 [従来の技術] 炭素や炭化水素といつた炭素化合物の不完全燃
焼によつて生ずるCOは、大気汚染ガスのうちで
も最も有毒なものの1つである。COは酸素(以
下O2)吸収・運搬の役目をする血液中ヘモグロ
ビンとの結合力が強く(O2の結合力の200〜300
倍)、このため、人体が高濃度のCOにさらされる
と、中枢組織の酸素欠乏による急性中毒を引き起
こし、さらには死に至るのである。また、低濃度
COの長期的な暴露によつては心臓疾患を引き起
こすといわれている。このため、自動車排気ガス
等による大気汚染、暖房器具の排ガスや喫煙によ
る室内汚染を防止する方法や、また、鉱山での爆
発事故や火災の際の保安のための環境ガス中CO
濃度を低減させる方法の確立が強く望まれてい
る。 これまでに提案されているCO除去方法は、(1)
吸着剤に吸着させる、(2)吸収液に吸収させる、(3)
酸化剤あるいは酸化触媒を用いて無毒なCO2に変
換する、の3方法に大別できる。 (1)の方法として、ポルフイリン金属錯体を吸着
剤として用いる方法(特公昭54−22951号公報)
や活性炭とモレキユラーシーブを組み合わせて用
いる方法(米国特許第3658069号明細書)などが
あるが、前者はCOの吸着速度が比較的遅い欠点
があり、また後者は吸着と同時に脱着が速やかに
起こり十分な除去ができないという欠点がある。 (2)の方法の例としては、塩化第一銅と塩化アル
ミニウム錯体のトルエン溶液にCOを吸収させる
コソーブ法(西ドイツ特許第1944405号明細書、
同第2414801号明細書)や銅アンミン錯イオン溶
液を用いた銅液洗浄法などが公知であるが、前者
は微量の水分によつてCO吸収活性を失うこと、
後者は銅()イオンが容易に酸化されることに
よつてCOの吸収活性を失うという欠点があり、
このため両者とも装置が大がかりになるため使用
上の制約が多い。 (3)の例としては、古くから二酸化マンガンと酸
化第二銅を主体とした酸化触媒ホブカライトが知
られており、この触媒は常温またはそれ以下の温
度域でも高いCOの酸化活性を有するが、微量の
水分によつて容易に活性を失うため密封して保存
し、さらに使用に際しては処理すべきガスをあら
かじめ完全に乾燥しておかなければならないとい
う不便がある。 一方COをCO2に酸化させる触媒として、金属
単体あるいは金属化合物が多数知られているが、
それらのほとんどは活性を失う温度領域が常温よ
りかなり高温であり、かつガス中の水分によつて
簡単に失活する。 わずかに白金・パラジウム等の貴金属の一部が
常温でCOの酸化活性を有し、水分に対しても比
較的安定な活性を持続するが、活性自体は極めて
低い。 [発明が解決しようとする課題] 上記事情に鑑み、本発明の課題は、CO酸化活
性を常温でも有効に発揮し、また、白金・パラジ
ウム等に比較して安価で製造容易な新しい高活性
のCO酸化触媒の製造方法を提供することである。 [課題を解決するための手段] 本発明者は上記の課題を解決すべく鋭意研究を
行つた結果、二酸化マンガン粉末をコバルト、ル
テニウム、またはニツケルの無機酸または有機酸
塩水溶液に含浸させ、二酸化マンガンの表面に該
金属塩を吸着させ、乾燥後、さらに過マンガン酸
カリウム(以下KMnO4)水溶液で処理すること
により製造される触媒がよく目的に適合すること
を見いだし本発明を完成するに至つた。 以下、本発明の一酸化炭素酸化触媒の製造方法
を詳細に説明する。 本発明で用いることのできる二酸化マンガン
は、二価のマンガン塩の電解酸化法、二価のマン
ガン塩とKMnO4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(J.トルマ
ン 英国特許第1315374号)及び中性溶液から調
製する方法(S.ボール Biochem.J.42、516
(1948))などのいずれの方法によつても調製する
ことができる。 また、調製した二酸化マンガンは、破砕、分級
し、20〜60メツシユの粒径のものを用いるのが好
ましい。この粉末二酸化マンガンを、コバルト、
ルテニウムまたはニツケルの無機酸または有機酸
塩水溶液、好ましくは、塩酸塩、硝酸塩、硫酸
塩、酢酸塩水溶液に含浸させる。これらの金属塩
は、単独水溶液で用いても、二種類以上の混合溶
液として用いても良い。 この二酸化マンガン含浸溶液を減圧下水を留去
し、二酸化マンガンの表面に金属塩を吸着させ、
110℃で一晩乾燥させる。 この金属塩の吸着量は金属に換算して0.1〜20
%の範囲が好適であり、予めこの量に相当する金
属塩を前記水溶液に溶解しておく。 こうして得られた金属塩担持二酸化マンガン
を、KMnO4水溶液、好ましくは飽和KMnO4
含浸させ、5〜30分間、好ましくは10分間酸化処
理を行い、濾別後、蒸留水で過マンガン酸イオン
の桃色が認められなくなるまで洗浄する。その
後、110℃で一晩乾燥することにより、本発明の
一酸化炭素酸化触媒を得ることができる。 この酸化触媒は、さらにCMC等の適当なバイ
ンダーを加えたり、圧縮成形するなどして適当な
形状として用いることができる。 [実施例] 以下、実施例に基づいて本発明を更に詳細に説
明する。しかし、これら実施例の記載は本発明の
範囲を限定するものではない。 実施例 1 50gの硝酸マンガン6水塩を300mlの蒸留水に
溶解し、これに50gの濃硝酸を加えた。別に50g
のKMnO4を21の蒸留水に溶解し、この溶液を撹
はんしながら先に調製した硝酸酸性硝酸マンガン
水溶液を除々に加えた。撹はんしながら10分間放
置し、生じた二酸化マンガンを傾斜法によつて洗
浄し、さらに吸引濾過しながら濾液の色がほとん
ど無色になるまで蒸留水で洗浄した。次いで110
℃で一晩乾燥し、得られた25gの塊状の二酸化マ
ンガンを破砕し、20〜60メツシユのものを分別し
た。この二酸化マンガンを5mg塩化コバルト6水
塩/mlの水溶液8mlに浸し、減圧下で水を留去し
た後110℃で一晩乾燥した。こうして得られ塩化
コバルト担持二酸化マンガンを、さらに飽和
KMnO4水溶液10mlに浸し、10分間放置後、濾別
し、過マンガン酸イオンの桃色が認められなくな
るまで蒸留水で洗浄した。次いで110℃で一晩乾
燥し、金属に換算して1.0wt%のコバルトを担持
した触媒を得た。これと同様の手順で金属コバル
トとして、0.02、0.2、2.0、4.0、6.0、8.0、10.0、
12.0、14.0、wt%のコバルトを担持した触媒を調
製した。これらの触媒を各200mg使用し、下記手
順でCO除去率を測定した。触媒をガラス管に
充填し、ガラスウールで充填物の両端を押さえ
る。このガラス管にキヤリヤガスとしてヘリウ
ムを流しながら反応ガス(CO5%、O24%、
CH44%、He87%)のパルスを常温(22℃)で10
ml与える。ガラス管を通過したガスを直接ガス
クロマトグラフに導き、ガス成分を分析する。結
果を第1図に、また各触媒の平均CO減少率を第
2図に示した。コバルト添加量2.0〜8.0wt%の範
囲の酸化剤がCO高活性であり、それらは平均90
%のCOを除去した。 実施例 2 電解酸化法によつて製造された市販の二酸化マ
ンガン4gを100mgの塩化コバルト6水塩を溶解
した25mlの水溶液に浸し、減圧下で水を留去し
た。以下実施例1と同様な手順により、KMnO4
処理、洗浄、乾燥を行い、得られた触媒を200mg
をパルス試験に供した。表−1に認められるよう
に、得られた触媒は高いCO酸化活性を示した。
[Industrial Application Field] The present invention selectively oxidizes carbon monoxide (hereinafter referred to as CO) in gas and converts it into non-toxic carbon dioxide (hereinafter referred to as CO 2 ).
The present invention relates to a method for producing an oxidation catalyst for converting into. [Prior Art] CO, which is produced by the incomplete combustion of carbon compounds such as carbon and hydrocarbons, is one of the most toxic air polluting gases. CO has a strong binding force with hemoglobin in the blood, which plays a role in absorbing and transporting oxygen (hereinafter referred to as O 2 ) (200-300% of the binding force of O 2 ).
For this reason, when the human body is exposed to high concentrations of CO, it causes acute poisoning due to lack of oxygen in the central tissues, and even death. Also, low concentration
Long-term exposure to CO is said to cause heart disease. For this reason, we are developing methods to prevent air pollution from automobile exhaust gas, indoor pollution from heating equipment exhaust gas and smoking, and CO2 contained in environmental gases for safety in the event of explosions or fires at mines.
There is a strong desire to establish a method to reduce the concentration. The CO removal methods proposed so far are (1)
Adsorb to adsorbent, (2) Absorb to absorbent, (3)
It can be roughly divided into three methods: converting it into non-toxic CO 2 using an oxidizing agent or an oxidizing catalyst. As method (1), a method using a porphyrin metal complex as an adsorbent (Japanese Patent Publication No. 54-22951)
There are methods that use a combination of activated carbon and molecular sieves (U.S. Pat. No. 3,658,069), but the former has the disadvantage that the CO adsorption rate is relatively slow, and the latter has the disadvantage that CO adsorption and desorption occur quickly at the same time. The disadvantage is that it cannot be removed sufficiently. An example of method (2) is the Kosorb method (West German Patent No. 1944405), in which CO is absorbed into a toluene solution of cuprous chloride and aluminum chloride complex;
No. 2414801) and a copper solution cleaning method using a copper ammine complex ion solution are known, but the former loses CO absorption activity due to trace amounts of water.
The latter has the disadvantage that the copper() ions are easily oxidized and lose CO absorption activity.
For this reason, both require large-scale devices and are subject to many restrictions in use. As an example of (3), the oxidation catalyst hobcalite, which mainly consists of manganese dioxide and cupric oxide, has been known for a long time, and this catalyst has high CO oxidation activity even at room temperature or lower. Since it easily loses its activity due to trace amounts of moisture, it is inconvenient that it must be stored in a sealed container and that the gas to be treated must be completely dried before use. On the other hand, many metals or metal compounds are known as catalysts for oxidizing CO to CO 2 .
Most of them lose their activity in a temperature range considerably higher than room temperature, and are easily deactivated by moisture in the gas. Although a small portion of precious metals such as platinum and palladium have CO oxidation activity at room temperature and remain relatively stable in the presence of moisture, the activity itself is extremely low. [Problems to be Solved by the Invention] In view of the above circumstances, an object of the present invention is to develop a new highly active material that effectively exhibits CO oxidation activity even at room temperature, and which is cheaper and easier to manufacture than platinum, palladium, etc. An object of the present invention is to provide a method for producing a CO oxidation catalyst. [Means for Solving the Problems] As a result of intensive research to solve the above problems, the present inventor impregnated manganese dioxide powder with an aqueous solution of an inorganic acid or an organic acid salt of cobalt, ruthenium, or nickel, and obtained carbon dioxide. They discovered that a catalyst produced by adsorbing the metal salt on the surface of manganese, drying it, and then treating it with an aqueous solution of potassium permanganate (hereinafter referred to as KMnO 4 ) was well suited for the purpose, and led to the completion of the present invention. Ivy. Hereinafter, the method for producing the carbon monoxide oxidation catalyst of the present invention will be explained in detail. Manganese dioxide that can be used in the present invention can be prepared by the electrolytic oxidation method of divalent manganese salt, or by the method of preparing it from divalent manganese salt and KMnO 4 under alkaline conditions (J. Atztenbrough et al. J. Chem. Soc. 1094).
(1952)), the method prepared under nitric acid acidity (J. Tolman British Patent No. 1315374) and the method prepared from a neutral solution (S. Ball Biochem. J.42, 516).
(1948)). Moreover, it is preferable to crush and classify the prepared manganese dioxide and use one having a particle size of 20 to 60 mesh. This powdered manganese dioxide, cobalt,
It is impregnated with an aqueous solution of an inorganic or organic acid salt of ruthenium or nickel, preferably an aqueous solution of hydrochloride, nitrate, sulfate, or acetate. These metal salts may be used as a single aqueous solution or as a mixed solution of two or more types. The water from this manganese dioxide impregnated solution is distilled off under reduced pressure, and the metal salt is adsorbed onto the surface of the manganese dioxide.
Dry at 110°C overnight. The adsorption amount of this metal salt is 0.1 to 20 in terms of metal.
% range, and a metal salt corresponding to this amount is dissolved in advance in the aqueous solution. The metal salt-supported manganese dioxide obtained in this way is impregnated with an aqueous KMnO 4 solution, preferably saturated KMnO 4 , and oxidized for 5 to 30 minutes, preferably 10 minutes. After filtering, permanganate ions are removed with distilled water. Wash until pink color is no longer recognized. Thereafter, the carbon monoxide oxidation catalyst of the present invention can be obtained by drying at 110° C. overnight. This oxidation catalyst can be used in a suitable shape by further adding a suitable binder such as CMC or compression molding. [Examples] Hereinafter, the present invention will be explained in more detail based on Examples. However, the description of these examples is not intended to limit the scope of the invention. Example 1 50 g of manganese nitrate hexahydrate was dissolved in 300 ml of distilled water, and 50 g of concentrated nitric acid was added thereto. 50g separately
of KMnO 4 was dissolved in 21 parts of distilled water, and while stirring this solution, the previously prepared aqueous solution of nitric acid and manganese nitrate was gradually added. The mixture was left to stand for 10 minutes with stirring, and the produced manganese dioxide was washed by a decanting method, and further washed with distilled water while filtering with suction until the filtrate became almost colorless. then 110
After drying at ℃ overnight, 25 g of the obtained lump-like manganese dioxide was crushed, and 20 to 60 pieces were separated. This manganese dioxide was immersed in 8 ml of an aqueous solution containing 5 mg of cobalt chloride hexahydrate/ml, water was distilled off under reduced pressure, and the mixture was dried at 110° C. overnight. The thus obtained cobalt chloride-supported manganese dioxide is further saturated.
It was immersed in 10 ml of KMnO 4 aqueous solution, left for 10 minutes, filtered, and washed with distilled water until the pink color of permanganate ions was no longer observed. Next, it was dried at 110° C. overnight to obtain a catalyst supporting 1.0 wt % of cobalt in terms of metal. Using the same procedure as this, as metal cobalt, 0.02, 0.2, 2.0, 4.0, 6.0, 8.0, 10.0,
Catalysts supporting 12.0, 14.0, and 14.0 wt% of cobalt were prepared. Using 200 mg of each of these catalysts, the CO removal rate was measured according to the following procedure. Fill a glass tube with the catalyst and press both ends of the packing with glass wool. While flowing helium as a carrier gas through this glass tube, reactant gases (CO5%, O 2 4%,
CH4 4 %, He87%) pulses for 10 minutes at room temperature (22°C)
Give ml. The gas that has passed through the glass tube is led directly to a gas chromatograph to analyze the gas components. The results are shown in Figure 1, and the average CO reduction rate of each catalyst is shown in Figure 2. Oxidizers with cobalt additions ranging from 2.0 to 8.0 wt% are CO highly active, and they have an average of 90
% CO removed. Example 2 4 g of commercially available manganese dioxide produced by electrolytic oxidation method was immersed in 25 ml of an aqueous solution containing 100 mg of cobalt chloride hexahydrate, and water was distilled off under reduced pressure. Following the same procedure as in Example 1, KMnO 4
After treatment, washing and drying, 200 mg of the obtained catalyst
was subjected to a pulse test. As seen in Table 1, the obtained catalyst showed high CO oxidation activity.

【表】 実施例 3 実施例1で得た二酸化マンガンを5mg塩化ルテ
ニウム/mlの水溶液45.5mlに含浸させ、減圧下で
水を留去した。次いで実施例1と同様の手順で触
媒調製を行い、1.0wt%のルテニウムを担持した
触媒を得た。また、同様にして0.02〜25.0wt%の
範囲のルテニウムを担持した数種の触媒を調製し
た。得られた触媒各200mgにつてパルス試験を行
つたところ、第3図、第4図のような結果となつ
た。CO酸化に最適なルテニウム添加率は12.0〜
14.0wt%であり、そのCO除去率は約40%であつ
た。 実施例 4 実施例1の塩化コバルト6水塩の代わりに塩化
ニツケルを用いる以外は、同様の方法により、
0.02〜14.0wt%の範囲のニツケルを担持した10種
類の触媒を調製した。この触媒各200mgをパルス
試験に供し、第5図、第6図に示す結果を得た。
CO酸化に適したニツケル添加率は4.0〜8.0wt%
であり、6.0wt%の触媒のCO除去率は35%であつ
た。 実施例 5 20gの無水硫酸マンガンを100mlの水に溶解し
撹はんしながらこれに10gのKMnO4と5gの水
酸化ナトリウムを溶解した300mlの蒸留水を除々
に加えた。生じた黒褐色の沈澱を吸引濾過によつ
て濾過し、さらに蒸留水で濾液がほとんど無色と
なるまで洗浄した。次ぎにこれを110℃で一夜乾
燥し、二酸化マンガンの粉末を得た。このうちか
ら1gをとり、5mg塩化コバルト6水塩/mlの水
溶液16mlに含浸し、以下実施例と同様な方法で
KMnO4処理、洗浄、乾燥を行い、2.0wt%のコバ
ルトを含有する触媒を得た。この触媒200mgにつ
いてパルス試験を行つた結果を表−2に示した。
[Table] Example 3 The manganese dioxide obtained in Example 1 was impregnated with 45.5 ml of an aqueous solution containing 5 mg ruthenium chloride/ml, and water was distilled off under reduced pressure. Next, a catalyst was prepared in the same manner as in Example 1 to obtain a catalyst supporting 1.0 wt% of ruthenium. In addition, several types of catalysts supporting ruthenium in a range of 0.02 to 25.0 wt% were prepared in the same manner. A pulse test was conducted on 200 mg of each of the catalysts obtained, and the results were as shown in FIGS. 3 and 4. The optimal ruthenium addition rate for CO oxidation is 12.0~
The CO removal rate was 14.0wt%, and the CO removal rate was about 40%. Example 4 By the same method except that nickel chloride was used instead of cobalt chloride hexahydrate in Example 1,
Ten types of catalysts with nickel supported ranging from 0.02 to 14.0 wt% were prepared. 200 mg of each of these catalysts was subjected to a pulse test, and the results shown in FIGS. 5 and 6 were obtained.
Nickel addition rate suitable for CO oxidation is 4.0 to 8.0wt%
The CO removal rate of the 6.0wt% catalyst was 35%. Example 5 20 g of anhydrous manganese sulfate was dissolved in 100 ml of water, and while stirring, 300 ml of distilled water in which 10 g of KMnO 4 and 5 g of sodium hydroxide had been dissolved was gradually added. The resulting blackish brown precipitate was filtered by suction filtration, and further washed with distilled water until the filtrate became almost colorless. Next, this was dried at 110°C overnight to obtain manganese dioxide powder. Take 1 g of this, impregnate it with 16 ml of an aqueous solution containing 5 mg cobalt chloride hexahydrate/ml, and proceed in the same manner as in the example.
After KMnO 4 treatment, washing, and drying, a catalyst containing 2.0 wt% cobalt was obtained. Table 2 shows the results of a pulse test performed on 200 mg of this catalyst.

【表】 実施例 6 実施例1で用いた塩化コバルト6水塩の代わり
に、硝酸コバルト6水塩、硫酸ルテニウム、酢酸
ニツケル4水塩をそれぞれ用いる以外は同様な方
法で、各種の触媒を製造した。各々の触媒200mg
をパルス試験に供し、表−3に示す結果を得た。
塩酸塩以外の無機酸塩または有機酸塩でも同様の
高いCO酸化活性を有することがわかる。
[Table] Example 6 Various catalysts were produced in the same manner except that cobalt nitrate hexahydrate, ruthenium sulfate, and nickel acetate tetrahydrate were used in place of the cobalt chloride hexahydrate used in Example 1. did. 200mg of each catalyst
was subjected to a pulse test, and the results shown in Table 3 were obtained.
It can be seen that inorganic or organic acid salts other than hydrochloride have similar high CO oxidation activity.

【表】 [発明の効果] 本発明の製造方法による一酸化炭素酸化触媒に
よれば、常温でも高い触媒活性を有しており、か
つ水分の存在による失活が極めて少なく、安定な
触媒活性を維持するので、従来の触媒に比べて効
果的に一酸化炭素を無害な二酸化炭素に酸化でき
る。
[Table] [Effects of the Invention] The carbon monoxide oxidation catalyst produced by the production method of the present invention has high catalytic activity even at room temperature, has very little deactivation due to the presence of moisture, and has stable catalytic activity. This makes it possible to oxidize carbon monoxide to harmless carbon dioxide more effectively than conventional catalysts.

【図面の簡単な説明】[Brief explanation of drawings]

第1図はコバルト−二酸化マンガン系触媒のパ
ルス試験結果のグラフであり、第2図はコバルト
−二酸化マンガン系触媒の平均CO減少率のグラ
フであり、第3図はルテニウム−二酸化マンガン
系触媒のパルス試験結果のグラフであり、第4図
はルテニウム−二酸化マンガン系触媒の平均CO
減少率のグラフであり、第5図はニツケル−二酸
化マンガン系触媒のパルス試験結果であり、第6
図はニツケル−二酸化マンガンの平均CO減少率
のグラフである。
Figure 1 is a graph of pulse test results for a cobalt-manganese dioxide catalyst, Figure 2 is a graph of the average CO reduction rate for a cobalt-manganese dioxide catalyst, and Figure 3 is a graph of the average CO reduction rate for a ruthenium-manganese dioxide catalyst. This is a graph of the pulse test results, and Figure 4 shows the average CO of the ruthenium-manganese dioxide catalyst.
Figure 5 is a graph of the reduction rate; Figure 5 is the pulse test result of the nickel-manganese dioxide catalyst; Figure 6 is the graph of the reduction rate;
The figure is a graph of the average CO reduction rate of nickel-manganese dioxide.

Claims (1)

【特許請求の範囲】 1 二酸化マンガンをコバルト、ルテニウム、ニ
ツケルなる群から選ばれる金属の無機酸塩または
有機酸塩の水溶液で含浸し、ついで過マンガン酸
カリウムで酸化処理することを特徴とする一酸化
炭素酸化触媒の製造方法。 2 コバルト、ルテニウム、ニツケルなる群から
選ばれる金属の無機酸塩または有機酸塩が、塩
酸、硝酸、硫酸、酢酸なる群から選ばれる酸の塩
であることを特徴とする特許請求項1記載の一酸
化炭素酸化触媒の製造方法。
[Claims] 1. A method characterized in that manganese dioxide is impregnated with an aqueous solution of an inorganic or organic acid salt of a metal selected from the group consisting of cobalt, ruthenium, and nickel, and then oxidized with potassium permanganate. A method for producing a carbon oxide oxidation catalyst. 2. The inorganic or organic acid salt of a metal selected from the group consisting of cobalt, ruthenium, and nickel is a salt of an acid selected from the group consisting of hydrochloric acid, nitric acid, sulfuric acid, and acetic acid. A method for producing a carbon monoxide oxidation catalyst.
JP58180607A 1983-09-30 1983-09-30 Oxidizing agent for carbon monoxide Granted JPS6072977A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP58180607A JPS6072977A (en) 1983-09-30 1983-09-30 Oxidizing agent for carbon monoxide

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP58180607A JPS6072977A (en) 1983-09-30 1983-09-30 Oxidizing agent for carbon monoxide

Publications (2)

Publication Number Publication Date
JPS6072977A JPS6072977A (en) 1985-04-25
JPH0373336B2 true JPH0373336B2 (en) 1991-11-21

Family

ID=16086202

Family Applications (1)

Application Number Title Priority Date Filing Date
JP58180607A Granted JPS6072977A (en) 1983-09-30 1983-09-30 Oxidizing agent for carbon monoxide

Country Status (1)

Country Link
JP (1) JPS6072977A (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2004058633A2 (en) * 2002-12-20 2004-07-15 Honda Giken Kogyo Kabushiki Kaisha Platinum-free ruthenium-cobalt catalyst formulations for hydrogen generation
WO2010090193A1 (en) * 2009-02-04 2010-08-12 リケンテクノス株式会社 Film capable of oxidizing carbon monoxide and use thereof

Family Cites Families (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS4910190A (en) * 1972-04-12 1974-01-29
JPS5036387A (en) * 1973-08-02 1975-04-05
JPS50139087A (en) * 1974-04-26 1975-11-06
JPS525434A (en) * 1975-07-01 1977-01-17 Hitachi Ltd Oxygen electrode for fuel cell
JPS526277A (en) * 1975-07-02 1977-01-18 Shii Esu Shii Kk Packing bag for charging powder* coffee grain* etc*
JPS53142393A (en) * 1977-05-17 1978-12-12 Matsushita Electric Ind Co Ltd Production of gas purification catalyst

Also Published As

Publication number Publication date
JPS6072977A (en) 1985-04-25

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