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JPH0375202B2 - - Google Patents
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JPH0375202B2 - - Google Patents

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Publication number
JPH0375202B2
JPH0375202B2 JP57199220A JP19922082A JPH0375202B2 JP H0375202 B2 JPH0375202 B2 JP H0375202B2 JP 57199220 A JP57199220 A JP 57199220A JP 19922082 A JP19922082 A JP 19922082A JP H0375202 B2 JPH0375202 B2 JP H0375202B2
Authority
JP
Japan
Prior art keywords
catalyst
exhaust gas
enamel
supported
purification device
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
JP57199220A
Other languages
Japanese (ja)
Other versions
JPS5990620A (en
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 filed Critical
Priority to JP57199220A priority Critical patent/JPS5990620A/en
Publication of JPS5990620A publication Critical patent/JPS5990620A/en
Publication of JPH0375202B2 publication Critical patent/JPH0375202B2/ja
Granted 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】[Detailed description of the invention]

産業上の利用分野 本発明は、排ガス中の有害ガス成分を浄化処理
する装置に関する。 従来例の構成とその問題点 家庭用の各種燃焼機器から排出される排気ガス
の浄化処理が強く求められているが、従来よりこ
れに対処するために、耐熱耐食性金網を触媒とし
て使用する方法、あるいは有機系結着剤を溶解さ
せた液に触媒粉末を分散させた溶液を前述の金網
に付着させて焼成担持したものを使用する方法等
が比較的安価で構成が容易な手段として用いられ
る例がある。しかし、金網自身が徐々に酸化変質
して初期の浄化能が低下したり、あるいは担持し
た触媒が金網との熱膨張の違いで脱落したりする
など、信頼性に乏しいという欠点をもつている。
また前者においては、排ガス中の窒素酸化物
(NOx)などの酸化性ガスと一酸化炭素(CO)、
炭化水素(HC)などの還元性ガスを同時に処理
することが困難であるという問題ももつている。 発明の目的 本発明は、前記問題点に鑑み、排ガス中の酸化
性ガス成分と還元性ガス成分を同時に効率よく処
理できる触媒を用い、信頼性が高くしかも容易に
実施できる排ガス浄化装置を提供しようとするも
のである。 発明の構成 本発明は、一般式La1-X/2Sr1+X/2Co1-xMexO3
(MeはFe、Mn、Cr、V、Tiから選ぶ一種の元
素、O<X<1)で表され、酸化性ガスの還元と
還元性ガスの酸化を同時に行なう能力をもつペロ
ブスカイト型複合酸化物を触媒として使用し、こ
れをほうろうによつて金属網などの耐熱性金属多
孔体に担持した排ガス浄化装置である。 本発明で用いる触媒は、組成を前記式のように
定めることによつて触媒活性が最も高く、かつ特
耐安定性に優れたものとすることができ、さらに
これをほうろうで金属多孔体に担持し、触媒動作
時におけるほうろうの緩衝作用を利用することに
よつて触媒の脱落を防止し、かつ金属多孔体の酸
化変質も防止できるために信頼性を高めることが
できる。 実施例の説明 第1図は組成がLa1-xSrxCo1-yFeyO3である酸
化物触媒の活性例を示す。触媒として所定の組成
になるように各成分元素の酸化物もしくは炭酸塩
を混合し、焼成して得た複合酸化物を1g/個の
ペレツトに成型して焼結したものを用いた。ペレ
ツト4個を一定容積の反応容器に入れ、大気圧に
調整したCO100ppm、O25%、残部N2の均一混合
ガスを流入させ、触媒に接触して1分後の反応容
器内のガス圧を測定し、その変化率をもつて触媒
活性とした。温度は300℃とした。 図からy=0でx=0.5、y=0.3でx=0.65、
y=0.6でx=0.8、y=1.0でx=1.0の各元素比
になる場合にそれぞれ活性が最大になることがわ
かる。 第2図は同じ触媒についてのNO2分解活性の
例を示す。前記と同様にして作製したペレツト45
個を内径20mmの石英管に充填し、電気炉に固定し
て温度を300℃に保つた。そしてNO240ppm、残
部N2の均一混合ガスをSV=10000h-1で触媒層に
流入し、定常状態に達したときの出口側NO2
度を測定して流入ガス濃度に対する減少率を求め
たものである。この場合もCO酸化の場合と同様
にy=Oでx=0.5、y=0.3でx=0.65、y=0.6
でx=0.8、y=1.0でx=1.0の各元素比になる場
合にNO2減少率がそれぞれ最大になる結果を得
た。 以上において活性のピークを示す酸化物組成は
La0.5Sr0.5CoO3、La0.35Sr0.65Co0.7Fe0.3O3、La0.2
Sr0.8Co0.4Fe0.6O3、SrFeO3となつた。ところで
LaCoO3においてはCoは+3価であるが、Aサイ
トのLaをSr2+で置換するとCo4+が生じる。さら
にBサイトのCoを置換するFeが+4価で入ると
すると、前記4つの酸化物では電気的中性条件か
らCo3+とCo4+が等量存在することになる。つま
りCo3+とCo4+が等量存在するようにAサイトと
Bサイトの置換量を決定することで高活性を付与
できると考えられる。即ちBサイト置換元素Me
の量をxとすると、高活性触媒組成をLa1-X/2
Sr1+X/2Co1-xMexO3と表すことができる。 次に浄化装置の実施例を説明する。 実施例としてx=0.3とした場合、即ちLa0.35
Sr0.65Co0.7Me0.3O3(Me=Fe、Mn、Cr、V、Ti)
と表せる酸化物触媒をステンレス鋼SUH21のエ
キスパンドメタル製金網に高融点ほうろうで担持
したものをとりあげる。直径120mmのステンレス
鋼SUH21の金網に融点約900℃の高融点ほうろう
をスプレーによつて塗布し、さらにこの上に、前
述と同様にして合成した複合酸化物を約300メツ
シユの大きさの粉末にしたものをスプレーで均一
に付着させた。これを所定温度で熱処理して触媒
粉末が均一に強固に担持された網を得た。 第3図は触媒を担持した金属網の要部の断面を
示す。触媒粒子1はほうろう2によつて完全にお
おわれることなく、図のように表面が露出するよ
うに金網3に担持され、触媒としての機能を発揮
する。 第4図はこの網4を市販のポータブル・ガスス
トーブの燃焼筒の上部に取り付けたところを示す
概略断面図である。燃焼部5で発生した排ガスは
流路6を通つて排ガス浄化装置4に達し、浄化さ
れて排出される。 このガスストーブを燃焼させたときの、浄化装
置通過後の排ガス中のCOおよびNO2濃度の変化
を以下の表に示す。なお浄化装置通過前のCO濃
度は37ppm、NO2濃度は6ppmである。データは
1回目の燃焼時の濃度と30分燃焼、30分消火のサ
イクルを5000回くりかえした後の濃度とをあわせ
て記してある。燃焼時の浄化装置上流側の排ガス
温度は約700℃である。比較例としてステンレス
鋼SUH21の金属網そのものと、メチルセルロー
スの10重量%水溶液に同様の触媒粉末を均一に分
散させ、これをステンレス鋼SUH21の金属網に
均一に塗布し、焼成して担持させたものを反応に
供した。触媒担持量は実施例、比較例共に約1g
であつた。また表の触媒組成は、La0.35Sr0.65
Co0.7Me0.3O3におけるMeで示している。
INDUSTRIAL APPLICATION FIELD The present invention relates to an apparatus for purifying harmful gas components in exhaust gas. Conventional configurations and their problems There is a strong demand for purification treatment of exhaust gas emitted from various household combustion appliances, and in order to deal with this, conventional methods have been developed that use heat-resistant and corrosion-resistant wire mesh as a catalyst. Alternatively, a method of using a solution in which catalyst powder is dispersed in a solution of an organic binder and depositing it on the wire mesh described above and firing it is an example of a relatively inexpensive and easy-to-configure method. There is. However, it has the disadvantage of poor reliability, such as the wire mesh itself gradually oxidizing and deteriorating, reducing its initial purification ability, or the supported catalyst falling off due to differences in thermal expansion with the wire mesh.
In the former case, oxidizing gases such as nitrogen oxides ( NOx ) and carbon monoxide (CO) in exhaust gas,
Another problem is that it is difficult to simultaneously process reducing gases such as hydrocarbons (HC). Purpose of the Invention In view of the above-mentioned problems, the present invention provides an exhaust gas purification device that is highly reliable and easy to implement, using a catalyst that can efficiently treat oxidizing gas components and reducing gas components in exhaust gas at the same time. That is. Structure of the Invention The present invention is based on the general formula La 1-X/2 Sr 1+X/2 Co 1-x M x O 3
(Me is an element selected from Fe, Mn, Cr, V, and Ti, O<X<1), and is a perovskite-type composite oxide that has the ability to simultaneously reduce oxidizing gases and oxidize reducing gases. This is an exhaust gas purification device that uses as a catalyst and supports this on a heat-resistant metal porous body such as a metal net with enamel. By determining the composition as shown in the above formula, the catalyst used in the present invention can have the highest catalytic activity and excellent stability. However, by utilizing the buffering effect of enamel during catalyst operation, it is possible to prevent the catalyst from falling off and also to prevent oxidative deterioration of the metal porous body, thereby increasing reliability. Description of Examples FIG. 1 shows an example of the activity of an oxide catalyst having the composition La 1-x Sr x Co 1-y Fe y O 3 . As a catalyst, a composite oxide obtained by mixing oxides or carbonates of each component element so as to have a predetermined composition and firing the mixture was molded into 1 g/pellet and sintered. Four pellets were placed in a reaction vessel with a fixed volume, and a homogeneous mixed gas of 100 ppm CO, 5% O 2 , and the balance N 2 adjusted to atmospheric pressure was introduced, and the gas pressure inside the reaction vessel was measured 1 minute after contact with the catalyst. was measured, and the rate of change was taken as the catalytic activity. The temperature was 300°C. From the figure, when y=0, x=0.5, when y=0.3, x=0.65,
It can be seen that the activity is maximized when each element ratio is x=0.8 at y=0.6 and x=1.0 at y=1.0. Figure 2 shows an example of NO2 decomposition activity for the same catalyst. Pellet 45 produced in the same manner as above
The samples were filled into a quartz tube with an inner diameter of 20 mm, and the tube was fixed in an electric furnace to maintain the temperature at 300°C. Then, a homogeneous mixed gas of 40 ppm NO 2 and the balance N 2 was flowed into the catalyst layer at SV = 10000 h -1 , and when a steady state was reached, the NO 2 concentration on the outlet side was measured and the rate of decrease with respect to the inflow gas concentration was determined. It is something. In this case, as in the case of CO oxidation, y=O and x=0.5, y=0.3 and x=0.65, y=0.6
We obtained the results that the NO 2 reduction rate is maximum when each element ratio is x = 0.8, y = 1.0, and x = 1.0. The oxide composition showing the activity peak in the above is
La 0.5 Sr 0.5 CoO 3 , La 0.35 Sr 0.65 Co 0.7 Fe 0.3 O 3 , La 0.2
Sr 0.8 Co 0.4 Fe 0.6 O 3 and SrFeO 3 were formed. by the way
In LaCoO 3 , Co has a valence of +3, but when La at the A site is replaced with Sr 2+ , Co 4+ is generated. Furthermore, assuming that Fe substituting Co at the B site enters with a valence of +4, Co 3+ and Co 4+ will exist in equal amounts in the four oxides due to the electrically neutral condition. In other words, it is thought that high activity can be imparted by determining the amount of substitution at the A site and B site so that Co 3+ and Co 4+ are present in equal amounts. That is, the B site substitution element Me
If the amount of is x, then the highly active catalyst composition is La 1-X/2
It can be expressed as Sr 1+X/2 Co 1-x Me x O 3 . Next, an example of the purification device will be described. As an example, when x=0.3, that is, La 0.35
Sr 0.65 Co 0.7 Me 0.3 O 3 (Me=Fe, Mn, Cr, V, Ti)
An oxide catalyst expressed as follows is supported on an expanded metal mesh made of stainless steel SUH21 with high melting point enamel. High-melting point enamel with a melting point of approximately 900°C was applied to a stainless steel SUH21 wire mesh with a diameter of 120 mm by spraying, and on top of this, the composite oxide synthesized in the same manner as described above was powdered into a powder approximately 300 mesh in size. Spray it on the surface evenly. This was heat-treated at a predetermined temperature to obtain a net in which the catalyst powder was evenly and firmly supported. FIG. 3 shows a cross section of the main part of the metal mesh supporting the catalyst. The catalyst particles 1 are not completely covered with the enamel 2, but are supported on the wire mesh 3 so that the surface is exposed as shown in the figure, and exhibits the function as a catalyst. FIG. 4 is a schematic sectional view showing the net 4 attached to the upper part of the combustion tube of a commercially available portable gas stove. The exhaust gas generated in the combustion section 5 passes through the flow path 6 and reaches the exhaust gas purification device 4, where it is purified and discharged. The table below shows the changes in the CO and NO 2 concentrations in the exhaust gas after passing through the purifier when this gas stove is burned. Note that the CO concentration before passing through the purification device is 37 ppm, and the NO 2 concentration is 6 ppm. The data includes the concentration during the first combustion and the concentration after repeating the cycle of 30 minutes of combustion and 30 minutes of extinguishing 5000 times. The exhaust gas temperature on the upstream side of the purification device during combustion is approximately 700°C. As a comparative example, a metal mesh made of stainless steel SUH21 itself and a similar catalyst powder uniformly dispersed in a 10% by weight aqueous solution of methyl cellulose were uniformly applied to the metal mesh made of stainless steel SUH21 and baked to support it. was subjected to the reaction. The amount of catalyst supported was approximately 1 g in both the examples and comparative examples.
It was hot. The catalyst composition in the table is La 0.35 Sr 0.65
Shown as Me in Co 0.7 Me 0.3 O 3 .

【表】 5000サイクルの燃焼試験後の触媒担持量は、従
来の担持法によるものが約0.4〜0.6gであるのに
比べ、本発明によるものは初期担持量に対する変
化が殆んど認められなかつた。触媒酸化物と金属
網の熱膨張にわずかながら差が存在し、直接担持
すると徐々に触媒の脱落が生じるのに対し、ほう
ろうで担持したものは触媒動作時にはほうろうが
わずかに軟化し、緩衝作用を生じて触媒粒子の脱
落を防止する効果が表れるものと考えられる。さ
らに、燃焼サイクル試験後の担持状態をみても、
触媒粒子の表面がほうろうでおおわれることもな
く初期の状態を保つており、特性の維持安定化に
大きく寄与していることがわかる。使用する金属
網はステンレス鋼SUH21以外の耐熱耐食鋼でも
よく、ほうろうも低融点のものを使用するなど、
使用条件により適宜選択して構成することができ
る。 発明の効果 以上のように本発明の排ガス浄化装置は、酸化
性ガスと還元性ガスを同時に効率よく処理でき、
しかも特性安定性に優れ信頼性の高いものであ
る。さらに比較的安価で構成も容易であるなどの
特徴をもつている。
[Table] The amount of catalyst supported after 5000 cycles of combustion test was approximately 0.4 to 0.6 g using the conventional method, whereas the amount of catalyst supported using the present invention showed almost no change from the initial amount supported. Ta. There is a slight difference in thermal expansion between the catalyst oxide and the metal mesh, and when supported directly, the catalyst gradually falls off, whereas when supported with enamel, the enamel softens slightly during catalytic operation, resulting in a buffering effect. This is thought to be effective in preventing catalyst particles from falling off. Furthermore, looking at the loading state after the combustion cycle test,
It can be seen that the surface of the catalyst particles is not covered with enamel and maintains its initial state, which greatly contributes to maintaining and stabilizing the characteristics. The metal mesh used may be made of heat-resistant and corrosion-resistant steel other than stainless steel SUH21, and the enamel used must be of low melting point.
It can be appropriately selected and configured depending on the conditions of use. Effects of the Invention As described above, the exhaust gas purification device of the present invention can efficiently process oxidizing gas and reducing gas at the same time.
Moreover, it has excellent characteristic stability and high reliability. Furthermore, it has features such as being relatively inexpensive and easy to configure.

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

第1図はLa1-xSrxCo1-yFeyO3のCO酸化活性を
示す図、第2図は同じくNO2分解活性を示す図、
第3図は触媒担持金属網の要部断面図、第4図は
触媒浄化装置付きガスストーブの燃焼部の概略断
面図である。 1……触媒粒子、2……ほうろう層、3……金
属部分。
Figure 1 shows the CO oxidation activity of La 1-x Sr x Co 1-y Fe y O 3 , Figure 2 also shows the NO 2 decomposition activity,
FIG. 3 is a sectional view of a main part of the catalyst-supporting metal mesh, and FIG. 4 is a schematic sectional view of the combustion section of a gas stove with a catalyst purification device. 1...Catalyst particles, 2...Enamel layer, 3...Metal part.

Claims (1)

【特許請求の範囲】[Claims] 1 一般式La1-X/2Sr1+X/2Co1-xMexO3(MeはFe、
Mn、Cr、V、Tiから選ぶ一種の元素、O<X<
1)で表されるペロブスカイト型複合酸化物触媒
をほうろうによつて金属多孔体に担持させた排ガ
ス浄化装置。
1 General formula La 1-X/2 Sr 1+X/2 Co 1-x Me x O 3 (Me is Fe,
A type of element selected from Mn, Cr, V, Ti, O<X<
An exhaust gas purification device in which a perovskite-type composite oxide catalyst represented by 1) is supported on a metal porous body using enamel.
JP57199220A 1982-11-12 1982-11-12 Cleaning-up device for waste gas Granted JPS5990620A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP57199220A JPS5990620A (en) 1982-11-12 1982-11-12 Cleaning-up device for waste gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP57199220A JPS5990620A (en) 1982-11-12 1982-11-12 Cleaning-up device for waste gas

Publications (2)

Publication Number Publication Date
JPS5990620A JPS5990620A (en) 1984-05-25
JPH0375202B2 true JPH0375202B2 (en) 1991-11-29

Family

ID=16404133

Family Applications (1)

Application Number Title Priority Date Filing Date
JP57199220A Granted JPS5990620A (en) 1982-11-12 1982-11-12 Cleaning-up device for waste gas

Country Status (1)

Country Link
JP (1) JPS5990620A (en)

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS57159528A (en) * 1981-03-27 1982-10-01 Matsushita Electric Ind Co Ltd Combustion apparatus

Also Published As

Publication number Publication date
JPS5990620A (en) 1984-05-25

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