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JPS589690B2 - Treatment method for exhaust gas containing carbon monoxide - Google Patents
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JPS589690B2 - Treatment method for exhaust gas containing carbon monoxide - Google Patents

Treatment method for exhaust gas containing carbon monoxide

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Publication number
JPS589690B2
JPS589690B2 JP53042490A JP4249078A JPS589690B2 JP S589690 B2 JPS589690 B2 JP S589690B2 JP 53042490 A JP53042490 A JP 53042490A JP 4249078 A JP4249078 A JP 4249078A JP S589690 B2 JPS589690 B2 JP S589690B2
Authority
JP
Japan
Prior art keywords
catalyst
exhaust gas
steel material
carbon monoxide
aqueous solution
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
JP53042490A
Other languages
Japanese (ja)
Other versions
JPS54134072A (en
Inventor
稲葉栄也
鬼塚重則
紙野康美
木原繁雄
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.)
Kanadevia Corp
Original Assignee
Hitachi Shipbuilding and Engineering Co Ltd
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 Hitachi Shipbuilding and Engineering Co Ltd filed Critical Hitachi Shipbuilding and Engineering Co Ltd
Priority to JP53042490A priority Critical patent/JPS589690B2/en
Publication of JPS54134072A publication Critical patent/JPS54134072A/en
Publication of JPS589690B2 publication Critical patent/JPS589690B2/en
Expired legal-status Critical Current

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  • Exhaust Gas Treatment By Means Of Catalyst (AREA)
  • Catalysts (AREA)

Description

【発明の詳細な説明】 この発明は、各種排ガスに含まれる一酸化炭素(CO)
を酸化して無害な炭酸ガス(CO2)になす排ガスの処
理方法に関する。
[Detailed Description of the Invention] This invention deals with carbon monoxide (CO) contained in various exhaust gases.
The present invention relates to a method for treating exhaust gas by oxidizing CO2 to harmless carbon dioxide (CO2).

触媒反応において、常に問題となるのは触媒の活性およ
び寿命であるが、さらに触媒の形状に起因する圧損失も
大きな問題の一つである。
In catalytic reactions, the activity and life of the catalyst are always a problem, but pressure loss due to the shape of the catalyst is also a major problem.

特に排ガス処理の場合のように、大量のガスを常圧で処
理する場合には、圧損失が大きくなる可能性が高く、ブ
ロア等の消費電力の増大を招き稼動コストが高くなる問
題がある。
In particular, when a large amount of gas is treated at normal pressure, as in the case of exhaust gas treatment, there is a high possibility that the pressure loss will be large, leading to an increase in the power consumption of the blower and the like, resulting in an increase in operating costs.

この圧損失の問題を解決するため、従来の粒状担体に代
って、セラミック製のハニカム状担体が開発され実際に
使用されつつある。
In order to solve this problem of pressure loss, ceramic honeycomb carriers have been developed and are now being used in place of conventional granular carriers.

しかし、この担体は破損しやすいという強度上の欠点が
あり、排ガス処理のような大量の処理には適していない
However, this carrier has a strength disadvantage in that it is easily damaged, and is not suitable for large-scale treatment such as exhaust gas treatment.

本発明者らは上記の点に鑑み、圧損失の問題を生じるこ
となく、シかも強度的にも優れたCO酸化用触媒を開発
し、この発明を完成するに至った。
In view of the above points, the present inventors have developed a CO oxidation catalyst that does not cause the problem of pressure loss and has excellent strength and strength, and has completed the present invention.

すなわち、本発明は、排ガス中の一酸化炭素を接触的に
無害化する排ガスの処理方法において、リング状、ハニ
カム状、プレート状などの所定形状を有する鋼材をAl
メッキ処理し、表面がメッキされた鋼材を熱処理して鋼
材中にAlを拡散せしめ、AI拡散表層を有する鋼材を
AI可溶性溶液でAI溶出処理して、表層を多孔質化し
、この鋼材を酸化処理し、こうして得られた触媒基材を
、Ba(OH)2で弱アルカリ性に調整されたH2Pt
Cl6水溶液に浸漬して触媒基材にPtを含有せしめ、
pt含有触媒基材を乾燥してCO酸化触媒を製造し、こ
の触媒を使用して排ガスの接触反応を行うことを特徴と
するCO含有排ガスの処理方法である。
That is, the present invention provides an exhaust gas treatment method for catalytically detoxifying carbon monoxide in the exhaust gas, in which a steel material having a predetermined shape such as a ring shape, a honeycomb shape, or a plate shape is treated with aluminum.
The steel material with the plated surface is heat treated to diffuse Al into the steel material, the steel material having an AI diffusion surface layer is subjected to AI elution treatment with an AI soluble solution to make the surface layer porous, and this steel material is oxidized. Then, the catalyst base material obtained in this way was heated with H2Pt which had been adjusted to be slightly alkaline with Ba(OH)2.
The catalyst base material is made to contain Pt by immersion in a Cl6 aqueous solution,
This is a method for treating CO-containing exhaust gas, which is characterized by drying a PT-containing catalyst base material to produce a CO oxidation catalyst, and using this catalyst to carry out a catalytic reaction of exhaust gas.

上記において、リング状、ハニカム状、プレート状など
の所定形状を有する鋼材を用いる理由は、該鋼材が大き
な強度を有し、大量の排ガス処理に際しても圧損失の生
じる恐れが小さいためである。
In the above, the reason why a steel material having a predetermined shape such as a ring shape, a honeycomb shape, or a plate shape is used is that the steel material has high strength and there is little risk of pressure loss occurring even when processing a large amount of exhaust gas.

また、鋼材としては、ステンレス鋼、炭素鋼、純鉄など
が用いられるが、これらに限定されない。
Further, as the steel material, stainless steel, carbon steel, pure iron, etc. are used, but the material is not limited to these.

鋼材のMメツキ処理は、溶融メッキ法、拡散浸透メッキ
法、真空蒸着メッキ法、溶射法などの方法によって行わ
れる。
M-plating treatment of steel materials is performed by a method such as a hot-dip plating method, a diffusion-penetration plating method, a vacuum evaporation plating method, a thermal spraying method, or the like.

特に溶融メッキ法は、操作上最も簡単で経済的であるた
め好んで用いられる。
In particular, the hot-dip plating method is preferred because it is the simplest and most economical in terms of operation.

表面がAIメッキされた鋼材の熱処理は、AIの融点(
660℃)以上の温度好ましくは約800℃で、数分間
〜数時間好ましくは約1時間行なわれる。
Heat treatment of steel materials whose surfaces are plated with AI is done at the melting point of AI (
660°C or higher, preferably about 800°C, for several minutes to several hours, preferably about 1 hour.

Alの溶出処理は、AI可溶性溶液に浸漬するか、また
は該鋼材の合金層にAl可溶性溶液をスプレーすること
によって行われる。
The Al elution treatment is performed by immersing the steel in an AI-soluble solution or by spraying the Al-soluble solution onto the alloy layer of the steel material.

AI可溶性溶液としては、可性ンーダのようなアルカリ
金属水酸化物、アルカリ金属炭酸塩、アルカリ土類金属
水酸化物、鉱酸などの水溶液が用いられる。
As the AI-soluble solution, an aqueous solution of an alkali metal hydroxide, an alkali metal carbonate, an alkaline earth metal hydroxide, a mineral acid, etc., is used.

このAI溶出によって鋼材表層は多孔質化される。This AI elution makes the surface layer of the steel material porous.

表層が多孔質化された鋼材の酸化処理は、緩和な条件下
で行われるのが好ましい。
The oxidation treatment of the steel material whose surface layer has been made porous is preferably carried out under mild conditions.

処理温度、処理時間、酸素濃度に特に限定はされないが
、通常は、常温〜400℃において、酸素を0.1〜2
1容量%含む雰囲気中で、0.1〜2時間処理を行う。
There are no particular limitations on the treatment temperature, treatment time, or oxygen concentration, but usually the oxygen concentration is 0.1 to 2 at room temperature to 400°C.
The treatment is carried out for 0.1 to 2 hours in an atmosphere containing 1% by volume.

こうして、この発明における触媒の基材が形成される。In this way, the base material of the catalyst in this invention is formed.

触媒基材のH2PtCl6水溶液への浸漬処理は、Ba
(OH)2水溶液で弱アルカリ性に調整されかつPtO
.01〜1.0重量%を含むH2ptCl6水溶液を用
いて行うのが好ましい。
The immersion treatment of the catalyst base material in the H2PtCl6 aqueous solution
Adjusted to weak alkalinity with (OH)2 aqueous solution and PtO
.. It is preferable to use an aqueous H2ptCl6 solution containing 01 to 1.0% by weight.

弱アルカリ性として好ましい山値は8〜10である。The preferred peak value for weak alkalinity is 8-10.

浸漬時間は10分間〜1時間が好ましい。The immersion time is preferably 10 minutes to 1 hour.

この浸漬処理によって触媒基材にPtが含有される。This dipping treatment causes the catalyst base material to contain Pt.

浸漬後、pi含有触媒基材を溶液から増り出し、約10
0℃またはこれより若干高温で乾燥する。
After soaking, the pi-containing catalyst substrate was extracted from the solution and
Dry at 0°C or slightly higher temperature.

こうして得られた触媒はPtO.0 0 01〜1.0
重量%を含む。
The catalyst thus obtained was PtO. 0 0 01~1.0
Including weight %.

なおBa(OH)2は比較的水に溶けにくい物質である
ため、通常は健和水溶液として用いられる。
Since Ba(OH)2 is a substance that is relatively insoluble in water, it is usually used as a healthy aqueous solution.

たとえば、H2PtCl6水溶液の弱アルカリ性への調
整は、最終的に調製されるべきH2PiCl6水溶液の
10〜15倍の濃度のH2PtCl6水溶液を用意し、
これにBa(OH)2の飽和水溶液を添加して該水溶液
を弱アルカリ性となし、さらに水を所定量加えることに
よってなされる。
For example, to adjust the H2PtCl6 aqueous solution to weak alkalinity, prepare an H2PtCl6 aqueous solution with a concentration 10 to 15 times that of the H2PiCl6 aqueous solution to be finally prepared.
This is done by adding a saturated aqueous solution of Ba(OH)2 to make the aqueous solution weakly alkaline, and then adding a predetermined amount of water.

ここで、仮にBa(OH)2で弱アルカリ化していない
H2Ptel6水溶液を用いた場合には、該水溶液は強
酸性(pFI直1〜2)術ため、触媒基材の腐食を生じ
適当でない。
Here, if an aqueous H2Ptel6 solution that has not been weakly alkalized with Ba(OH)2 is used, the aqueous solution is strongly acidic (pFI direct 1 to 2), which would lead to corrosion of the catalyst base material, which would not be appropriate.

またpH調整剤としてBa(OH)2の代りにアンモニ
ア水を用いる場合には、pH=3〜4においてすでに懸
濁物が生じ、黄色沈澱が生成する。
Furthermore, when aqueous ammonia is used instead of Ba(OH)2 as a pH adjuster, a suspension is already formed at pH=3 to 4, and a yellow precipitate is formed.

そのためアンモニア水は使用できない。Therefore, ammonia water cannot be used.

また苛性カリを用いた場合には、沈澱は生じないが、完
成触媒のCO酸化活性がほとんどみられない。
Furthermore, when caustic potash is used, no precipitation occurs, but almost no CO oxidation activity is observed in the finished catalyst.

そのため苛性カリも好ましくない。Therefore, caustic potash is also not preferred.

こうして得られた触媒に、CO含有排ガスを接触通過さ
せる。
A CO-containing exhaust gas is passed through the catalyst thus obtained.

その結果、圧損失を少なくして、低温領域においてCo
の完全酸化を達成することができる。
As a result, pressure loss is reduced and Co
Complete oxidation of can be achieved.

また、排ガス中に二酸化イオウ(S02)が共存する場
合においても、触媒はこれによって被毒されずに安定し
た活性を示し、しかもSO2の無水硫酸(SO3)への
酸化に対しては小さな活性しか示さない。
Furthermore, even when sulfur dioxide (S02) coexists in the exhaust gas, the catalyst is not poisoned by it and exhibits stable activity, and has only a small activity against the oxidation of SO2 to sulfuric anhydride (SO3). Not shown.

そして、H2PtCl6水溶液に添加されたBa (O
H)2は、CO酸化触媒の活性に何ら悪影響を与えるこ
となく、得られた触媒は依然として高い活性を有する。
Then, Ba (O
H)2 does not have any negative effect on the activity of the CO oxidation catalyst, and the resulting catalyst still has high activity.

しかも触媒基材は鋼材でできているので、従来のセラミ
クス系の触媒に比較して、その熱伝導性が著しく高い。
Moreover, since the catalyst base material is made of steel, its thermal conductivity is significantly higher than that of conventional ceramic catalysts.

したがってこの触媒を用いると、COの酸化反応のよう
な著しい発熱反応においても、発生した反応熱を容易に
除去することができる。
Therefore, when this catalyst is used, the generated reaction heat can be easily removed even in a significantly exothermic reaction such as the oxidation reaction of CO.

実施例 1 触媒の製造 50X25X2頷のステンレス鋼SUS 304(J
IS)製プレートを、700℃の溶融アルミニウム浴に
5分間浸漬し、ついで浴から増り出したプレートを電気
炉内において800℃で加熱処理した。
Example 1 Manufacture of catalyst Stainless steel SUS 304 (J
A plate made by IS) was immersed in a molten aluminum bath at 700°C for 5 minutes, and then the plate that came out of the bath was heat-treated at 800°C in an electric furnace.

冷却後、80℃の1 0 %NaOH水溶液にプレート
を3時間浸漬し、これを液から取り出した後水洗した。
After cooling, the plate was immersed in a 10% NaOH aqueous solution at 80° C. for 3 hours, taken out from the solution, and washed with water.

さらに、酸素2容量%と残部窒素とからなる気流中に1
00℃にて1時間放置し、次いで酸素10容量%と残部
窒素とからなる気流中に200℃にて1時間放置して、
最後に空気中に300℃にて1時間放置して、プレート
の酸化処理を行い触媒基材を形成した。
Furthermore, in an air stream consisting of 2% by volume oxygen and the balance nitrogen, 1%
It was left at 00°C for 1 hour, and then left at 200°C for 1 hour in an air stream consisting of 10% by volume of oxygen and the balance nitrogen.
Finally, the plate was left to stand in air at 300° C. for 1 hour to oxidize the plate to form a catalyst base material.

他方、Ptl重量%を含むH2PtC7I6水溶液を1
0d用意し、これにBa(OH)2の飽和水溶液を滴下
して世を8〜9に調整した。
On the other hand, 1% of H2PtC7I6 aqueous solution containing Ptl by weight was added.
0d was prepared, and a saturated aqueous solution of Ba(OH)2 was added dropwise thereto to adjust the temperature to 8-9.

そして、全体が1001dになるように水を添加して浸
漬処理液を調整した。
Then, water was added to adjust the immersion treatment liquid so that the total amount was 1001 d.

この溶液は1昼夜放置しても全く沈澱を生じなかった。This solution did not form any precipitate even if it was left for one day and night.

そこでこの溶液に先に形成した触媒基材を室温にて1時
間浸漬し、処理品を溶液から増り出した後110℃で1
時間乾燥して、触媒を得た。
Therefore, the previously formed catalyst base material was immersed in this solution for 1 hour at room temperature, and after the treated product was taken out of the solution, it was heated to 110°C for 1 hour.
After drying for several hours, a catalyst was obtained.

活性試験 こうして得られた触媒について、CO酸化率およびSO
J化率を測定した。
Activity test For the catalyst thus obtained, CO oxidation rate and SO
The J conversion rate was measured.

始めに、この試験で用いる石英製流通型反応装置につい
て説明しておく。
First, the quartz flow-through reactor used in this test will be explained.

第1図において、1は内径30+mの石英製反応管で、
環状電気炉内にセットされている。
In Fig. 1, 1 is a quartz reaction tube with an inner diameter of 30+ m;
It is set inside a circular electric furnace.

2は多数の通気孔3を有する石英製下部水平板、4は石
英製上部水平板、5は上下1対の水平板2,4にわたっ
て設けられた左右1対の石英製垂直板で、これには板状
触媒を支持する多数の突起6が設けられている。
2 is a lower horizontal plate made of quartz having a large number of ventilation holes 3; 4 is an upper horizontal plate made of quartz; 5 is a pair of left and right vertical plates made of quartz provided over the pair of upper and lower horizontal plates 2 and 4; A large number of protrusions 6 are provided to support the plate-shaped catalyst.

そして1対の垂直石英板5の間の空隙7は上方に開口し
ていて、ここから板状触媒が充填されるようになされて
いる。
The gap 7 between the pair of vertical quartz plates 5 is open upward, and the plate-shaped catalyst is filled from there.

8は温度計保護管である。まず、上記反応装置の空隙7
に触媒Aを充填し、ついで環状電気炉によって反応温度
を250℃から450℃に変化させて、表1に示される
組成割合の試験用調製排ガスを、乾燥状態を基準にして
1.2l/分(S.T.P.)の流量で反応管に流した
,CO酸化率およびSO2酸化率は、次式により求めた
8 is a thermometer protection tube. First, the cavity 7 of the reactor
was charged with catalyst A, and then the reaction temperature was changed from 250°C to 450°C using a circular electric furnace, and the prepared exhaust gas for testing having the composition ratio shown in Table 1 was heated at 1.2 l/min based on the dry state. The CO oxidation rate and SO2 oxidation rate were determined by the following equations when flowing into the reaction tube at a flow rate of (S.T.P.).

試験結果を第2図に示す。The test results are shown in Figure 2.

実施例 2 実施例1の操作に続いて、450℃にて2時間通ガスを
行い、その後再び実施例1と同様の条件で操作を行って
、CO酸化率およびS02酸化率を測定した。
Example 2 Following the operation in Example 1, gas was passed at 450° C. for 2 hours, and then the operation was performed again under the same conditions as in Example 1 to measure the CO oxidation rate and the S02 oxidation rate.

結果を第2図に示す。実施例 3 実施例2の操作に続いて、さらに450℃にて2時間通
ガスを行い、ついど実施例1と同様の操作でCO酸化率
を測定した。
The results are shown in Figure 2. Example 3 Following the operation in Example 2, gas was further passed at 450° C. for 2 hours, and the CO oxidation rate was measured in the same manner as in Example 1.

結果を同じく第2図に示す。The results are also shown in FIG.

実施例 4 Pi 3重量%を含むH2PtCd6水溶液10dを用
意し、これにBa(OH)2の飽和水溶液を滴下して、
川を8〜9に調整した。
Example 4 10 d of H2PtCd6 aqueous solution containing 3% by weight of Pi was prepared, and a saturated aqueous solution of Ba(OH)2 was added dropwise thereto.
I adjusted the river to 8-9.

そして、全体が100rrLlになるように水を添加し
て浸漬処理液を調製した。
Then, water was added so that the total amount was 100 rrLl to prepare an immersion treatment liquid.

この溶液に実施例1で形成した触媒基材を1時間浸漬し
、処理品を溶液から増り出しだ後110℃で1時間乾燥
して、触媒を得た。
The catalyst base material formed in Example 1 was immersed in this solution for 1 hour, and after the treated product was taken out of the solution, it was dried at 110° C. for 1 hour to obtain a catalyst.

この触媒について実施例1と同様の操作によりCO酸化
率およびS02酸化率を測定した。
Regarding this catalyst, the CO oxidation rate and the S02 oxidation rate were measured in the same manner as in Example 1.

結果を第3図に示す。The results are shown in Figure 3.

実施例 5 実施例の操作に続いて、450℃にて2時間通ガスを行
い、ついで実施例1と同様の操作CO酸化率およびS0
2酸化率を測定した。
Example 5 The procedure of the example was followed by gassing at 450° C. for 2 hours, followed by the same operation as in Example 1 with CO oxidation rate and SO
The oxidation rate was measured.

結果を第3図に示す。The results are shown in Figure 3.

実施例 6 実施例5の操作に続いて、さらに450℃にて2時間通
ガスを行い、ついで実施例1と同様の操作でCO酸化率
およびSQ,酸化率を測定した。
Example 6 Following the operation in Example 5, gas was further passed at 450° C. for 2 hours, and then the CO oxidation rate, SQ, and oxidation rate were measured in the same manner as in Example 1.

結果を同じく第3図に示す。The results are also shown in FIG.

比較例 1 pti含有浸漬処理液としてPt1重量%を含むH2P
tCl6水溶液を、pH調整しないでそのまま用い、他
の操作を実施例1と同様に行って触媒を得、ついでこの
触媒について実施例1と同様の操作でCO酸化率および
SQ,酸化率を測定した。
Comparative Example 1 H2P containing 1% by weight of Pt as pti-containing immersion treatment liquid
Using the tCl6 aqueous solution as it was without adjusting the pH, other operations were performed in the same manner as in Example 1 to obtain a catalyst, and then the CO oxidation rate, SQ, and oxidation rate of this catalyst were measured in the same manner as in Example 1. .

結果を第4図に示す。The results are shown in Figure 4.

比較例 2 比較例1の操作に続いて、450℃にて2時間通ガスを
行い、ついで実施例1と同様の操作でCO酸化率および
So2酸化率を測定した。
Comparative Example 2 Following the operation in Comparative Example 1, gas was passed at 450° C. for 2 hours, and then the CO oxidation rate and the So2 oxidation rate were measured in the same manner as in Example 1.

結果を同じく第4図に示す。The results are also shown in FIG.

比較例 3 PH調整剤としてBa(OH)2水溶液の代わりにKO
H水溶液を用い、他の操作を実施例1と同様に行って触
媒を得、ついでこの触媒について実施例1と同様の操作
でCO酸化率およびS02酸化率を測定した。
Comparative Example 3 KO was used instead of Ba(OH)2 aqueous solution as a pH adjuster.
Using an H aqueous solution, other operations were performed in the same manner as in Example 1 to obtain a catalyst, and then the CO oxidation rate and S02 oxidation rate of this catalyst were measured in the same manner as in Example 1.

結果を第5図に示す。比較例 4 実施例3の操作に続いて、450℃にて2時間通ガスを
行い、ついで実施例1と同様の操作でCO酸化率および
S02酸化率を測定した。
The results are shown in Figure 5. Comparative Example 4 Following the operation in Example 3, gas was passed at 450° C. for 2 hours, and then the CO oxidation rate and the S02 oxidation rate were measured in the same manner as in Example 1.

結果を同じく第5図に示す。The results are also shown in FIG.

比較例 5 PH調整剤としてB a (OH )2水溶液の代わり
にNaOH水溶液を用い、他の操作を実施例1と同様に
行って触媒を得、ついでこの触媒について実施例1と同
様の操作でCO酸化率およびSo2酸化率を測定した。
Comparative Example 5 Using NaOH aqueous solution instead of B a (OH ) 2 aqueous solution as a PH adjuster, other operations were performed in the same manner as in Example 1 to obtain a catalyst, and then this catalyst was subjected to the same operations as in Example 1. The CO oxidation rate and the So2 oxidation rate were measured.

結果を第6図に示す。第2図および第3図と第4図、第
5図および第6図との比較からわかるように、この発明
の方法によれば、排ガス中のCoの酸化を効率よくなし
得、また排ガス中にSO2が共存していても、SO2の
酸化を極力抑制することができる。
The results are shown in Figure 6. As can be seen from a comparison between FIGS. 2 and 3 and FIGS. 4, 5, and 6, according to the method of the present invention, Co in the exhaust gas can be efficiently oxidized. Even if SO2 coexists, oxidation of SO2 can be suppressed as much as possible.

しかも触媒は耐SO2性に優れているので、これを長期
にわたって安定持続的に使用することができる。
Moreover, since the catalyst has excellent SO2 resistance, it can be used stably and continuously for a long period of time.

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

第1図は活性試験用反応装置を示す切欠き斜視図、第2
図から第6図1では各触媒についての反応温度と酸化率
の関係を示すグラフで、第2図は実施例1,2および3
の触媒、第3図は実施例4,5および6の触媒、第4図
は比較例1および2の触媒、第5図は比較例3および4
の触媒、第6図は比較例5の触媒にそれぞれ関するもの
である。
Figure 1 is a cutaway perspective view showing the reaction device for activity testing;
From Figure 6 Figure 1 is a graph showing the relationship between reaction temperature and oxidation rate for each catalyst, and Figure 2 is a graph showing the relationship between the reaction temperature and oxidation rate for each catalyst.
Figure 3 shows the catalysts of Examples 4, 5 and 6, Figure 4 shows the catalysts of Comparative Examples 1 and 2, and Figure 5 shows the catalysts of Comparative Examples 3 and 4.
and FIG. 6 relates to the catalyst of Comparative Example 5, respectively.

Claims (1)

【特許請求の範囲】[Claims] 1 排ガス中の一酸化炭素を接触的に酸化無害化する排
ガスの処理方法において、リング状 ハニカム状、プレ
ート状などの所定形状を有する鋼材をアルミニウムメッ
キ処理し、表面がメッキされた鋼材を熱処理して鋼材中
にアルミニウムを拡散せしめ、アルミニウム拡散表層を
有する鋼材をアルミニウム可溶性溶液でアルミニウム溶
出処理して表層を多孔質化し、この鋼材を酸化処理し、
こうして得られた触媒基材を、水酸化バリウムで弱アル
カリ性に調整された塩化白金酸水溶液に浸漬して触媒基
材に白金を含有せしめ、白金含有触媒基材を乾燥して一
酸化炭素酸化触媒を製造し、この触媒を使用して排ガス
の接触反応を行うことを特徴とする一酸化炭素含有排ガ
スの処理方法。
1. In an exhaust gas treatment method that oxidizes and detoxifies carbon monoxide in exhaust gas, a steel material having a predetermined shape such as a ring shape, a honeycomb shape, or a plate shape is aluminum-plated, and the steel material with the plated surface is heat-treated. diffuse aluminum into the steel material, treat the steel material with an aluminum diffused surface layer with an aluminum soluble solution to make the surface layer porous, and oxidize the steel material,
The catalyst base thus obtained is immersed in a chloroplatinic acid aqueous solution adjusted to be weakly alkaline with barium hydroxide to make the catalyst base contain platinum, and the platinum-containing catalyst base is dried to become a carbon monoxide oxidation catalyst. A method for treating exhaust gas containing carbon monoxide, which comprises producing a catalyst and carrying out a catalytic reaction of exhaust gas using this catalyst.
JP53042490A 1978-04-11 1978-04-11 Treatment method for exhaust gas containing carbon monoxide Expired JPS589690B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP53042490A JPS589690B2 (en) 1978-04-11 1978-04-11 Treatment method for exhaust gas containing carbon monoxide

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP53042490A JPS589690B2 (en) 1978-04-11 1978-04-11 Treatment method for exhaust gas containing carbon monoxide

Publications (2)

Publication Number Publication Date
JPS54134072A JPS54134072A (en) 1979-10-18
JPS589690B2 true JPS589690B2 (en) 1983-02-22

Family

ID=12637496

Family Applications (1)

Application Number Title Priority Date Filing Date
JP53042490A Expired JPS589690B2 (en) 1978-04-11 1978-04-11 Treatment method for exhaust gas containing carbon monoxide

Country Status (1)

Country Link
JP (1) JPS589690B2 (en)

Also Published As

Publication number Publication date
JPS54134072A (en) 1979-10-18

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