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JPH0312934B2 - - Google Patents
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JPH0312934B2 - - Google Patents

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Publication number
JPH0312934B2
JPH0312934B2 JP59095185A JP9518584A JPH0312934B2 JP H0312934 B2 JPH0312934 B2 JP H0312934B2 JP 59095185 A JP59095185 A JP 59095185A JP 9518584 A JP9518584 A JP 9518584A JP H0312934 B2 JPH0312934 B2 JP H0312934B2
Authority
JP
Japan
Prior art keywords
gold
catalyst
oxide
combustion
hydrogen
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
JP59095185A
Other languages
Japanese (ja)
Other versions
JPS60238148A (en
Inventor
Masaki Haruta
Hiroshi Sano
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.)
National Institute of Advanced Industrial Science and Technology AIST
Original Assignee
Agency of Industrial Science and Technology
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 Agency of Industrial Science and Technology filed Critical Agency of Industrial Science and Technology
Priority to JP59095185A priority Critical patent/JPS60238148A/en
Publication of JPS60238148A publication Critical patent/JPS60238148A/en
Publication of JPH0312934B2 publication Critical patent/JPH0312934B2/ja
Granted legal-status Critical Current

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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

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  • Catalysts (AREA)
  • Respiratory Apparatuses And Protective Means (AREA)
  • Gas Burners (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)

Description

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

本発明は、水素、一酸化炭素および炭化水素な
どの可燃性ガスの接触燃焼用触媒に関し、より詳
細にはこれらの可燃性ガスを比較的低温で容易に
無炎完全燃焼させうる金系酸化物触媒に関する。 従来、一酸化炭素やメタン、プロパン等の炭化
水素を触媒上で酸化し熱に変える接触燃焼法は、
自動車排ガスをはじめとする各種の排ガス中の有
害成分の除去や、空気中の可燃性ガスの検知など
の分野で応用されているが、近年になつて窒素酸
化物(NOx)を発生しない安全でクリーンな燃
焼方式として各種の暖房、厨房および加熱用機器
への応用が関心を集めている。 そして、かかる接触燃焼を安全に、かつ効率良
く行うためには高活性で耐久性のある酸化触媒が
要求され、通常では白金系金属触媒、あるいは遷
移金属酸化物触媒ば使用されている。 しかし、白金系金属触媒は一酸化炭素の接触燃
焼に対する活性が低く、一方遷移金属酸化物触媒
は水素や炭化水素に対する活性が低いので、一酸
化炭素に対しても水素や炭化水素系燃料に対して
も高い活性を持つ触媒の開発が望まれていた。 本発明はかかる従来の要望に答えてなされたも
のであり、特に、微量でも中毒症状を引き起こす
一酸化炭素を低温で接触燃焼できる触媒を提供せ
んとするものである。 本発明はかかる目的達成のためになされたもの
であり、マンガン、鉄、コバルト、ニツケル、及
び銅からなる群から選ばれた少なくとも一種の金
属の酸化物と金とからなる金系酸化物複合触媒で
ある。 ここで、マンガン、鉄、コバルト、ニツケル及
び銅の酸化物は化学的にはMnO2、Fe2O3
Co3O4、NiOおよびCuOで表され、塩化金酸
(HAuCl4)水溶液とマンガン()、鉄()、
コバルト()、ニツケル()、および銅()
の塩化物、硫酸塩、または硝酸塩などの水溶液製
塩水溶液との混合液に炭酸アルカリ、水酸化アル
カリ、アンモニアなどの中和剤の水溶液を反応さ
せた中和塩類を共沈させ、次いで焼成することに
より得られる。マンガン−金系酸化物の場合は、
マンガン()の前記水溶性塩と塩化金酸の混合
水溶液と前記中和剤と過マンガン酸カリウム、次
亜塩素酸ナトリウム、臭素酸ナトリウムなどの酸
化剤との混合水溶液を反応させて共沈させること
もできる。 あるいは、金と前記金属の水酸化物を別々に沈
殿させ、しかる後に両沈殿物を混練しても良い。 次いで、得られた沈殿物を水洗、乾燥後、空気
の存在下、通常300〜700℃で焼成して触媒を調製
する。 得られた触媒中の金の含有量は通常1〜50原子
%であり、好ましくは2〜20原子%、最も好まし
くは2〜10原子%である。 ここで原子%とは触媒中の特定金属の原子数
の、触媒を構成する全金属の原子数に対する百分
率であり、たとえばAuの原子%は(Au原子数/
全金属の原子数)×100で表される。 かかる本発明の触媒は、触媒単独で使用の目的
に応じた粒体、成形体として使用しても良いし、
あるいは、アルミナ、シリカ等の無機耐熱性物質
に担持して使用することもできる。 更に本発明の触媒は水素、一酸化炭素、および
炭化水素系可燃性ガスの無炎完全燃焼用触媒とし
て使用されるものである。 ここで炭化水素系可燃性ガスとは、メタン、エ
タン、プロパン、ブタン等の低級脂肪族炭化水素
であるばかりでなく、ベンゼン、トルエン、キシ
レン等の低級芳香族炭化水素、シクロヘキセン、
シクロヘキサン等の低級脂環族炭化水素およびメ
タノール、アルコール等の含酸系有機化合物を含
むものである。 本発明の触媒は、それを構成する金あるいは金
酸化物やマンガン、コバルトなどの遷移金属酸化
物を単独で使用した触媒に比べ、高い触媒活性を
有している。 例えば、後述するように酸化金(Au2O3)、酸
化コバルト(Co3O4)、酸化マンガン(MnO2
等、各々単独では、第1図の曲線〜に示すよ
うに80℃以上の温度が水素の接触燃焼の開始に必
要であるが、これらを複合化することにより20℃
で燃焼が開始できる。また、本発明の金系酸化物
触媒は一酸化炭素の接触燃焼に対して極めて高い
活性を示し、特にFe−Au系酸化物は第3図の右
端の曲線に示すように−30℃以下でも一酸化炭素
を完全に燃焼できる。 以上のように本発明の触媒は、低い温度で水
素、一酸化炭素などの可燃性ガスを接触燃焼でき
るので、大気汚染や火災危険性のない燃焼器とし
て各種暖房用、厨房用に、また食品工業や医薬品
工業における乾燥、加熱プロセスなどに利用が期
待され、実用的利点は極めて大きい。さらに、室
温以下でも使用できるので、空気中の一酸化炭素
除去用フイルターや防毒マスクにも利用が可能で
ある。 以下に本発明の実施例を述べる。 実施例 1 硝酸マンガン6水塩77.5gと塩化金酸4水塩
20.6gの混合水溶液1500mlを過マンガン酸カリウ
ム28.4gと炭酸ナトリウム43.9g混合水溶液1000
mlに撹拌しながら約10分間で添加し、添加終了後
も約2時間撹拌を続けた。 このようにして得られた沈殿物を数回傾瀉法を
繰り返して十分に水洗し、濾過した。これを120
℃で12時間乾燥した後粉砕し、空気流通下400℃
で5時間焼成して、Mn−Au系酸化物触媒(原子
%90:10)を得た。これをふるい分けして触媒と
して用いた。 実施例 2 硝酸第二鉄9水塩109gと塩化金酸4水塩12.4
gの混合水溶液1500mlを炭酸ナトリウム57.2gの
水溶液1000mlに撹拌しながら約10分間で添加し、
添加終了後も約2時間撹拌を続けた。 このようにして得られた沈殿物を数回傾瀉法を
繰り返して十分に水洗し、濾過した。これを120
℃で12時間乾燥した後粉砕し、空気流通下400℃
で5時間焼成して、Fe−Au系酸化物触媒(原子
%90:10)を得た。これをふるい分けして触媒と
して用いた。 実施例 3 実施例1あるいは2と同様な方法で得られた金
およびマンガン、鉄、コバルト、ニツケル、銅の
少なくとも一種以上を含む酸化物触媒を用いて、
水素に対する接触燃焼活性を調べた。なお、触媒
はそれぞれ400℃で5時間焼成し、42−70メツシ
ユに粉砕したものを0.30g用い、水素1容積%の
空気混合ガスを100ml/分で流通させた。結果を
第1図および第1表に示す。
The present invention is a gold oxide that can easily burn these combustion gas at a relatively low temperature at relatively low temperature, regarding the combustion catalyst for combustion gas such as hydrogen, carbon monoxide, and hydrogen carbon. Regarding catalysts. Conventionally, the catalytic combustion method converts hydrocarbons such as carbon monoxide, methane, and propane into heat by oxidizing them on a catalyst.
It is used in fields such as the removal of harmful components from various types of exhaust gas, including automobile exhaust gas, and the detection of flammable gases in the air, but in recent years, there has been an increase in the number of safe methods that do not emit nitrogen oxides (NOx). As a clean combustion method, its application to various heating, kitchen, and heating equipment is attracting attention. In order to carry out such catalytic combustion safely and efficiently, a highly active and durable oxidation catalyst is required, and platinum-based metal catalysts or transition metal oxide catalysts are usually used. However, platinum-based metal catalysts have low activity against catalytic combustion of carbon monoxide, while transition metal oxide catalysts have low activity against hydrogen and hydrocarbons. There was a desire to develop a catalyst with high activity. The present invention has been made in response to such conventional needs, and in particular, it is an object of the present invention to provide a catalyst that can catalytically burn carbon monoxide, which causes poisoning symptoms even in minute amounts, at low temperatures. The present invention has been made to achieve such an object, and provides a gold-based oxide composite catalyst comprising gold and an oxide of at least one metal selected from the group consisting of manganese, iron, cobalt, nickel, and copper. It is. Here, oxides of manganese, iron, cobalt, nickel and copper are chemically known as MnO 2 , Fe 2 O 3 ,
Represented by Co 3 O 4 , NiO and CuO, an aqueous solution of chloroauric acid (HAuCl 4 ) and manganese (), iron (),
Cobalt (), Nickel (), and Copper ()
Co-precipitating neutralized salts by reacting an aqueous solution of a neutralizing agent such as an alkali carbonate, an alkali hydroxide, or ammonia with a mixed solution of an aqueous salt solution such as a chloride, sulfate, or nitrate, and then firing. It is obtained by In the case of manganese-gold oxides,
A mixed aqueous solution of the water-soluble salt of manganese () and chloroauric acid is reacted with a mixed aqueous solution of the neutralizing agent and an oxidizing agent such as potassium permanganate, sodium hypochlorite, and sodium bromate to cause coprecipitation. You can also do that. Alternatively, gold and the hydroxide of the metal may be precipitated separately, and then both precipitates may be kneaded. Next, the obtained precipitate is washed with water, dried, and then calcined in the presence of air, usually at 300 to 700°C, to prepare a catalyst. The content of gold in the resulting catalyst is usually 1 to 50 atomic %, preferably 2 to 20 atomic %, most preferably 2 to 10 atomic %. Here, atomic % is the percentage of the number of atoms of a specific metal in the catalyst to the number of atoms of all metals constituting the catalyst. For example, atomic % of Au is (number of Au atoms /
It is expressed as (number of atoms of all metals) x 100. The catalyst of the present invention may be used alone in the form of granules or molded bodies depending on the purpose of use, or
Alternatively, it may be supported on an inorganic heat-resistant substance such as alumina or silica. Furthermore, the catalyst of the present invention is used as a catalyst for complete flameless combustion of hydrogen, carbon monoxide, and hydrocarbon-based combustible gases. Here, the hydrocarbon-based combustible gases include not only lower aliphatic hydrocarbons such as methane, ethane, propane, and butane, but also lower aromatic hydrocarbons such as benzene, toluene, and xylene, cyclohexene,
It contains lower alicyclic hydrocarbons such as cyclohexane and acid-containing organic compounds such as methanol and alcohol. The catalyst of the present invention has higher catalytic activity than a catalyst using only gold, a gold oxide, or a transition metal oxide such as manganese or cobalt. For example, as described below, gold oxide (Au 2 O 3 ), cobalt oxide (Co 3 O 4 ), manganese oxide (MnO 2 )
Each of these alone requires a temperature of 80°C or higher to initiate catalytic combustion of hydrogen, as shown in the curves in Figure 1, but by combining these, temperatures of 20°C or higher are required.
Combustion can be started. In addition, the gold-based oxide catalyst of the present invention exhibits extremely high activity for catalytic combustion of carbon monoxide, and in particular, the Fe-Au-based oxide catalyst exhibits extremely high activity even below -30°C, as shown in the rightmost curve in Figure 3. Carbon monoxide can be completely combusted. As described above, the catalyst of the present invention can catalytically burn combustible gases such as hydrogen and carbon monoxide at low temperatures, so it can be used as a combustor that does not cause air pollution or fire hazards, and can be used for various types of heating, kitchens, and food. It is expected to be used in drying and heating processes in industry and the pharmaceutical industry, and its practical advantages are extremely large. Furthermore, since it can be used even below room temperature, it can also be used in filters for removing carbon monoxide from the air and gas masks. Examples of the present invention will be described below. Example 1 77.5g of manganese nitrate hexahydrate and chloroauric acid tetrahydrate
Add 1500ml of a mixed aqueous solution of 20.6g to 1000ml of a mixed aqueous solution of 28.4g of potassium permanganate and 43.9g of sodium carbonate.
ml over about 10 minutes with stirring, and stirring was continued for about 2 hours after the addition was completed. The thus obtained precipitate was thoroughly washed with water by repeating the decanting process several times, and then filtered. This is 120
After drying for 12 hours at °C, crush and store at 400 °C under air circulation.
The mixture was calcined for 5 hours to obtain a Mn-Au based oxide catalyst (atomic % 90:10). This was sieved and used as a catalyst. Example 2 109 g of ferric nitrate nonahydrate and 12.4 g of chloroauric acid tetrahydrate
1500 ml of a mixed aqueous solution of 57.2 g of sodium carbonate was added over about 10 minutes with stirring,
Stirring was continued for about 2 hours after the addition was completed. The thus obtained precipitate was thoroughly washed with water by repeating the decanting process several times, and then filtered. This is 120
After drying for 12 hours at °C, crush and store at 400 °C under air circulation.
The mixture was fired for 5 hours to obtain an Fe-Au based oxide catalyst (atomic % 90:10). This was sieved and used as a catalyst. Example 3 Using an oxide catalyst containing gold and at least one of manganese, iron, cobalt, nickel, and copper obtained in the same manner as in Example 1 or 2,
The catalytic combustion activity towards hydrogen was investigated. Each catalyst was calcined at 400 DEG C. for 5 hours and pulverized into 42-70 mesh, 0.30 g of which was used, and an air mixed gas containing 1% by volume of hydrogen was passed through at 100 ml/min. The results are shown in FIG. 1 and Table 1.

【表】 第1表から明らかなように、金との複合化によ
り、酸化物の触媒活性は大巾に向上する。このこ
とは金を全く含まない比較例、例えばMnO2
独、Fe2O3単独の場合のT1/2(水素の50%が燃
焼消失する温度)との比較が示すように、金の添
加によるT1/2の著しい低下から明らかである。 実施例 4 実施例2と同様な方法で得られたFe−Au系、
Co−Au系およびNi−Au系複合酸化物触媒を用
いた場合の、水素の50%燃焼率温度(T1/2)と
金の含有率との関係について検討した。結果を第
2図に示す。第2図から明らかなように、金を1
原子%添加するだけでT1/2は急激に低下し、著
しい活性の向上が見られる。更に金の添加量が増
加すると、T1/2は一層低下し、Fe−Au系およ
びCo−Au系の場合は5原子%で、Ni−Au系の
場合は10原子%の所でT1/2が最低となり、それ
以上の金含有率ではT1/2が逆に高くなる。した
がつて、これらの金系複合酸化物では活性の極大
が得られる最適金含有率が存在し、金5〜10原子
%含むことが最も望ましい。特にFe−Au系では
金5原子%の所でT1/2が39℃となり、最も活性
の高い触媒が得られた。 実施例 5 実施例4で得られたFe−Au(原子%95:5)
酸化物、Co−Au(原子%91:10)酸化物、およ
びNi−Au(原子%90:10)酸化物について、一
酸化炭素に対する接触燃焼活性を調べた。結果を
第3図に示す。測定の条件は実施例4において水
素を一酸化炭素に代えただけで、他は全く同一で
ある。上記3種の複合酸化物触媒では、一酸化炭
素の酸化は0℃以下で容易に進行し、極めて高い
触媒活性を有していることが明らかである。従来
から一酸化炭素の酸化触媒として市販されている
ホプカライト触媒では、本発明による触媒と同じ
活性を得るには約70℃高い温度が必要である。ま
た、アルミナやシリカに担持したパラジウム触媒
は、一般的に酸化触媒として最も優れたものであ
るが、本発明の触媒と比較すると極め活性が低い
ことがわかつた。さらに、金をアルミナに担持し
た触媒では、300℃以上にならないと触媒活性が
現われず、金を鉄、コバルト、ニツケルの酸化物
と組み合わせることにより、活性が非常に顕著に
向上することが明らかである。水素の燃焼の場合
(実施例3)と同様に、一酸化炭素の燃焼におい
ても、コバルトや鉄の酸化物だけでは高い温度を
必要とし、このことからも金とこれらの酸化物と
の複合化による活性向上の効果が明らかである。 実施例 6 実施例4で得られた金を5原子%含むFe−Au
系、Co−Au系、Ni−Au系酸化物のX線回析を
測定したところ、第4図および第5図の結果を得
た。このX線回析パターンより金は金属の状態で
存在していることがわかつた。従つて、金と鉄、
コバルト等の遷移金属酸化物との複合効果は新し
い複合酸化物相が形成されるために出現するもの
でなく、これら遷移金属酸化物中に分散した微粒
子状金の作用であると考えられるので、微粒子金
を蒸着法で添加するか、予め作成した金コロイド
微粒子と上記遷移金属酸化物とを混練することに
より同様の効果が期待される。そこで、上述の2
通りの方法でFe2O3−Au系複合物を調製して触
媒活性を測定したところ、実施例4で得られた触
媒とほぼ同様の活性が得られた。 実施例 7 硝酸コバルト6水塩29g、硝酸マンガン6水塩
3.5g、塩化金属4水塩2gの混合水溶液1000ml
を、過マンガン酸カリウム1.3gと炭酸ナトリウ
ム15.2gの混合水溶液500mlに撹拌しながら約20
分間で添加し、添加終了後も約2時間撹拌を続け
た。 このようにして得られた沈殿物を数回傾瀉法を
繰り返して十分に水洗し濾過した。これを120℃
で一昼夜乾燥後粉砕し、空気流通下400℃で10時
間焼成してCo−Mn−Au系酸化物触媒(原子%
80:16:4)を得た。これをふるい分けして触媒
として用いた。実施例3と同様な条件で水素燃焼
に対する活性を調べたところ、図1の曲線に示
すように低い温度で高い燃焼率を得た。水素の50
%燃焼率温度が69℃であり、この3元系複合酸化
物を構成するCo3O4、MnO2、Au2O3またはAuを
単独で使用した場合より50℃以上低い温度とな
り、本発明の効果は3元系複合酸化物にも出現す
ることが明らかとなつた。 実施例 8 実施例7と同様な方法で各種のCo−Mn−Au
系複合酸化物を調製し、マンガンに対するコバル
トの原子比Co/Mn=20/4にして、コバルト20
原子に対する金の原子数Xを種々変化させた。こ
うして得られたCo−Mn−Au(原子比20:4:
X)複合酸化物の水素燃焼に対する触媒活性を測
定した結果、水素が50%燃焼するのに要する温度
(T1/2、℃)とXとの関係は第6図のようであつ
た。図から明らかなように、金を含まないCo−
Mn(原子比20:4)複合酸化物だけではT1/2が
130℃と高いのに対し、X=1以上の金を含むも
のではT1/2が約70℃となり、金を添加すること
により触媒活性が顕著に向上した。
[Table] As is clear from Table 1, the catalytic activity of the oxide is greatly improved by complexing it with gold. This is shown by the comparison with T1/2 (temperature at which 50% of hydrogen is burned out) of comparative examples that do not contain any gold, such as MnO 2 alone or Fe 2 O 3 alone, as shown by the addition of gold. This is evident from the significant decrease in T1/2. Example 4 Fe-Au system obtained by the same method as Example 2,
The relationship between the 50% combustion rate temperature (T1/2) of hydrogen and the gold content when using Co-Au-based and Ni-Au-based composite oxide catalysts was investigated. The results are shown in Figure 2. As is clear from Figure 2, gold is
Just by adding atomic percent, T1/2 decreases rapidly, and a remarkable improvement in activity is observed. Further, as the amount of gold added increases, T1/2 decreases further, and T1/2 decreases at 5 atom% for Fe-Au and Co-Au systems, and at 10 atom% for Ni-Au systems. is the lowest, and if the gold content is higher than that, T1/2 becomes higher. Therefore, in these gold-based composite oxides, there is an optimum gold content at which the maximum activity is obtained, and it is most desirable that the gold content be 5 to 10 atomic percent. In particular, in the Fe-Au system, T1/2 was 39°C at 5 atomic % gold, and the most active catalyst was obtained. Example 5 Fe-Au obtained in Example 4 (atomic % 95:5)
The catalytic combustion activity against carbon monoxide was investigated for Co-Au (atomic % 91:10) oxide and Ni-Au (atomic % 90:10) oxide. The results are shown in Figure 3. The measurement conditions were exactly the same as in Example 4 except that hydrogen was replaced with carbon monoxide. It is clear that the above three types of composite oxide catalysts easily oxidize carbon monoxide at temperatures below 0°C and have extremely high catalytic activity. Hopcalite catalysts, conventionally commercially available as carbon monoxide oxidation catalysts, require temperatures approximately 70° C. higher to achieve the same activity as the catalysts of the present invention. Furthermore, palladium catalysts supported on alumina or silica are generally the best oxidation catalysts, but it was found that their activity was extremely low compared to the catalyst of the present invention. Furthermore, catalysts with gold supported on alumina do not exhibit catalytic activity until the temperature exceeds 300°C, and it is clear that combining gold with oxides of iron, cobalt, and nickel significantly increases the activity. be. As in the case of hydrogen combustion (Example 3), the combustion of carbon monoxide requires high temperatures when using only cobalt or iron oxides, and for this reason, it is necessary to combine gold and these oxides. The effect of improving activity is clear. Example 6 Fe-Au containing 5 at% of gold obtained in Example 4
When X-ray diffraction was measured for the oxides of Co-Au, Co-Au, and Ni-Au, the results shown in Figures 4 and 5 were obtained. This X-ray diffraction pattern revealed that gold existed in a metallic state. Therefore, gold and iron,
The composite effect with transition metal oxides such as cobalt does not appear due to the formation of a new composite oxide phase, but is thought to be due to the effect of fine particulate gold dispersed in these transition metal oxides. A similar effect can be expected by adding fine gold particles by vapor deposition or by kneading previously prepared gold colloid fine particles and the transition metal oxide. Therefore, the above 2
When a Fe 2 O 3 -Au-based composite was prepared in the same manner and the catalytic activity was measured, almost the same activity as the catalyst obtained in Example 4 was obtained. Example 7 Cobalt nitrate hexahydrate 29g, manganese nitrate hexahydrate
1000ml mixed aqueous solution of 3.5g and 2g of metal chloride tetrahydrate
was added to 500 ml of a mixed aqueous solution of 1.3 g of potassium permanganate and 15.2 g of sodium carbonate while stirring.
The mixture was added within a few minutes, and stirring was continued for about 2 hours after the addition was completed. The thus obtained precipitate was thoroughly washed with water by repeating the decanting process several times, and then filtered. This at 120℃
The Co-Mn-Au based oxide catalyst (atomic%
80:16:4). This was sieved and used as a catalyst. When the activity against hydrogen combustion was investigated under the same conditions as in Example 3, a high combustion rate was obtained at low temperatures as shown in the curve of FIG. hydrogen 50
The % combustion rate temperature is 69°C, which is 50°C or more lower than when Co 3 O 4 , MnO 2 , Au 2 O 3 or Au that constitute this ternary composite oxide is used alone, and the present invention It has become clear that this effect also appears in ternary composite oxides. Example 8 Various types of Co-Mn-Au were prepared in the same manner as in Example 7.
A system composite oxide is prepared, the atomic ratio of cobalt to manganese is Co/Mn=20/4, and cobalt 20
The number of gold atoms (X) relative to atoms was varied. Co-Mn-Au (atomic ratio 20:4:
X) As a result of measuring the catalytic activity of the composite oxide for hydrogen combustion, the relationship between X and the temperature required for 50% hydrogen combustion (T1/2, °C) was as shown in Figure 6. As is clear from the figure, Co− does not contain gold.
Mn (atomic ratio 20:4) composite oxide alone has T1/2.
In contrast, T1/2 was as high as 130°C, whereas in those containing gold with X=1 or more, T1/2 was about 70°C, and the catalyst activity was significantly improved by adding gold.

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

第1図は、希薄水素/空気混合気の触媒燃焼。
使用した触媒は、:Fe/Au=19/1、:
Co/Mn/Au=20/4/1、:Au、:
Au2O3、:Co3O4、:NiO、:MnO2
:Fe2O3、第2図は、水素の触媒燃焼立上り温
度(T1/2)の金含有量依存性。第3図は、一酸
化炭素の触媒燃焼速度の温度依存性。第4図は、
ニツケル−金系、コバルト−金系触媒のX線回析
パターン、Ni−Au系:Ni/Au=19/1、表面
積54m2/g、Co−Au系:Co/Au=19/1、表
面積79m2/g、第5図は、鉄−金系触媒のX線回
析パターン。第6図は、Co−Mn−Au系複合酸
化物触媒の触媒燃焼立上り温度の金含有依存性。
Figure 1 shows catalytic combustion of a dilute hydrogen/air mixture.
The catalyst used was: Fe/Au=19/1:
Co/Mn/Au=20/4/1, :Au, :
Au2O3 , : Co3O4 , :NiO, : MnO2 ,
:Fe 2 O 3 , Figure 2 shows the dependence of hydrogen catalytic combustion start-up temperature (T1/2) on gold content. Figure 3 shows the temperature dependence of the catalytic combustion rate of carbon monoxide. Figure 4 shows
X-ray diffraction patterns of nickel-gold and cobalt-gold catalysts, Ni-Au system: Ni/Au = 19/1, surface area 54 m 2 /g, Co-Au system: Co/Au = 19/1, surface area 79m 2 /g, Figure 5 is the X-ray diffraction pattern of the iron-gold catalyst. Figure 6 shows the gold content dependence of the catalytic combustion start-up temperature of a Co-Mn-Au composite oxide catalyst.

Claims (1)

【特許請求の範囲】[Claims] 1 マンガン、鉄、コバルト、ニツケル、及び銅
からなる群から選ばれた少なくとも一種の金属酸
化物と金とからなる可燃性ガスの接触燃焼用触
媒。
1. A catalyst for catalytic combustion of combustible gas, comprising gold and at least one metal oxide selected from the group consisting of manganese, iron, cobalt, nickel, and copper.
JP59095185A 1984-05-11 1984-05-11 Auriferous oxide catalyst for catalytic combustion of combustible gas Granted JPS60238148A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP59095185A JPS60238148A (en) 1984-05-11 1984-05-11 Auriferous oxide catalyst for catalytic combustion of combustible gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP59095185A JPS60238148A (en) 1984-05-11 1984-05-11 Auriferous oxide catalyst for catalytic combustion of combustible gas

Publications (2)

Publication Number Publication Date
JPS60238148A JPS60238148A (en) 1985-11-27
JPH0312934B2 true JPH0312934B2 (en) 1991-02-21

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ID=14130689

Family Applications (1)

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Country Status (1)

Country Link
JP (1) JPS60238148A (en)

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JPS6483513A (en) * 1987-09-24 1989-03-29 Agency Ind Science Techn Ultrafine gold particle immobilized alkaline earth metallic compound, production thereof, oxidation catalyst, reduction catalyst and combustible gas sensor element
JPH0235915A (en) * 1988-07-26 1990-02-06 Nippon Sanso Kk Removing process and carbon monoxide
JPH02252610A (en) * 1989-03-24 1990-10-11 Agency Of Ind Science & Technol Production of gold ultrafine granule-fixed oxide
US5425632A (en) * 1990-11-26 1995-06-20 Catalytica, Inc. Process for burning combustible mixtures
US5281128A (en) * 1990-11-26 1994-01-25 Catalytica, Inc. Multistage process for combusting fuel mixtures
US5326253A (en) * 1990-11-26 1994-07-05 Catalytica, Inc. Partial combustion process and a catalyst structure for use in the process
US5259754A (en) * 1990-11-26 1993-11-09 Catalytica, Inc. Partial combustion catalyst of palladium on a zirconia support and a process for using it
US5250489A (en) * 1990-11-26 1993-10-05 Catalytica, Inc. Catalyst structure having integral heat exchange
US5248251A (en) * 1990-11-26 1993-09-28 Catalytica, Inc. Graded palladium-containing partial combustion catalyst and a process for using it
US5258349A (en) * 1990-11-26 1993-11-02 Catalytica, Inc. Graded palladium-containing partial combustion catalyst
US5258340A (en) * 1991-02-15 1993-11-02 Philip Morris Incorporated Mixed transition metal oxide catalysts for conversion of carbon monoxide and method for producing the catalysts
US5266543A (en) * 1991-07-31 1993-11-30 Matsushita Electric Industrial Co., Ltd. Catalytic composite for deodorizing odorous gases and a method for preparing the same
JP2832336B2 (en) * 1995-11-07 1998-12-09 工業技術院長 Gold ultrafine particle-immobilized substance and method for producing the same
JP3758411B2 (en) 1999-04-08 2006-03-22 トヨタ自動車株式会社 Exhaust gas purification catalyst
AU2003211726A1 (en) * 2002-05-01 2003-12-12 National Institute Of Advanced Industrial Science And Technology Catalyst for water gas shift reaction
CA2575482C (en) * 2004-06-08 2011-01-18 National Institute Of Advanced Industrial Science And Technology Catalyst for carbon monoxide removal and method of removing carbon monoxide with the catalyst
JP5010547B2 (en) * 2008-07-10 2012-08-29 公立大学法人首都大学東京 Highly active catalyst and method for producing the same
GB201119171D0 (en) 2011-11-07 2011-12-21 Johnson Matthey Plc Gas treatment
CN104128199B (en) * 2014-07-08 2016-06-08 东南大学 A kind of nano catalyst and its preparation method

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