JPH0580258B2 - - Google Patents
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- Publication number
- JPH0580258B2 JPH0580258B2 JP62141695A JP14169587A JPH0580258B2 JP H0580258 B2 JPH0580258 B2 JP H0580258B2 JP 62141695 A JP62141695 A JP 62141695A JP 14169587 A JP14169587 A JP 14169587A JP H0580258 B2 JPH0580258 B2 JP H0580258B2
- Authority
- JP
- Japan
- Prior art keywords
- catalyst
- mgo
- oxide
- exhaust gas
- element selected
- 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 - Fee Related
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- 239000003054 catalyst Substances 0.000 claims description 45
- 239000007789 gas Substances 0.000 claims description 15
- 230000003647 oxidation Effects 0.000 claims description 11
- 238000007254 oxidation reaction Methods 0.000 claims description 11
- 229910052742 iron Inorganic materials 0.000 claims description 6
- 229910052751 metal Inorganic materials 0.000 claims description 5
- 239000002184 metal Substances 0.000 claims description 5
- 229910052684 Cerium Inorganic materials 0.000 claims description 4
- 229910052779 Neodymium Inorganic materials 0.000 claims description 4
- 229910052777 Praseodymium Inorganic materials 0.000 claims description 4
- 229910052746 lanthanum Inorganic materials 0.000 claims description 4
- 229910052759 nickel Inorganic materials 0.000 claims description 4
- 238000000746 purification Methods 0.000 claims description 4
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 3
- 229910052748 manganese Inorganic materials 0.000 claims description 3
- 229910052760 oxygen Inorganic materials 0.000 claims description 3
- 239000001301 oxygen Substances 0.000 claims description 3
- 229910052720 vanadium Inorganic materials 0.000 claims description 3
- 239000000919 ceramic Substances 0.000 claims description 2
- 229910052804 chromium Inorganic materials 0.000 claims description 2
- 229910052719 titanium Inorganic materials 0.000 claims description 2
- 239000000956 alloy Substances 0.000 claims 1
- 229910045601 alloy Inorganic materials 0.000 claims 1
- 230000003197 catalytic effect Effects 0.000 description 12
- 238000002485 combustion reaction Methods 0.000 description 7
- 230000007423 decrease Effects 0.000 description 6
- 239000000203 mixture Substances 0.000 description 5
- 229910000510 noble metal Inorganic materials 0.000 description 5
- 238000002156 mixing Methods 0.000 description 4
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 4
- 229910018072 Al 2 O 3 Inorganic materials 0.000 description 3
- MUBZPKHOEPUJKR-UHFFFAOYSA-N Oxalic acid Chemical compound OC(=O)C(O)=O MUBZPKHOEPUJKR-UHFFFAOYSA-N 0.000 description 3
- 230000003247 decreasing effect Effects 0.000 description 3
- 230000000694 effects Effects 0.000 description 3
- 239000006260 foam Substances 0.000 description 3
- 229910004298 SiO 2 Inorganic materials 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 238000010304 firing Methods 0.000 description 2
- 239000003350 kerosene Substances 0.000 description 2
- 238000005259 measurement Methods 0.000 description 2
- 229910052763 palladium Inorganic materials 0.000 description 2
- 229910052697 platinum Inorganic materials 0.000 description 2
- 229910020599 Co 3 O 4 Inorganic materials 0.000 description 1
- 230000010718 Oxidation Activity Effects 0.000 description 1
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 150000001413 amino acids Chemical class 0.000 description 1
- 238000001354 calcination Methods 0.000 description 1
- 239000003518 caustics Substances 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 229910052878 cordierite Inorganic materials 0.000 description 1
- JSKIRARMQDRGJZ-UHFFFAOYSA-N dimagnesium dioxido-bis[(1-oxido-3-oxo-2,4,6,8,9-pentaoxa-1,3-disila-5,7-dialuminabicyclo[3.3.1]nonan-7-yl)oxy]silane Chemical compound [Mg++].[Mg++].[O-][Si]([O-])(O[Al]1O[Al]2O[Si](=O)O[Si]([O-])(O1)O2)O[Al]1O[Al]2O[Si](=O)O[Si]([O-])(O1)O2 JSKIRARMQDRGJZ-UHFFFAOYSA-N 0.000 description 1
- KZHJGOXRZJKJNY-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Si]=O.O=[Al]O[Al]=O.O=[Al]O[Al]=O.O=[Al]O[Al]=O KZHJGOXRZJKJNY-UHFFFAOYSA-N 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 229910000000 metal hydroxide Inorganic materials 0.000 description 1
- 150000004692 metal hydroxides Chemical class 0.000 description 1
- 238000000034 method Methods 0.000 description 1
- 229910052863 mullite Inorganic materials 0.000 description 1
- 150000002823 nitrates Chemical class 0.000 description 1
- 150000003891 oxalate salts Chemical class 0.000 description 1
- 235000006408 oxalic acid Nutrition 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
Landscapes
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
- Catalysts (AREA)
Description
【発明の詳細な説明】
産業上の利用分野
本発明は、各種燃焼機器や内燃機関の燃焼排ガ
ス中に含まれるCO、HC等の有害ガスを無害な
CO2、H2Oに変化させるとともに、還元雰囲気下
ではNOxも浄化することのできる触媒体に関す
るものである。[Detailed Description of the Invention] Industrial Application Field The present invention is a method for removing harmful gases such as CO and HC contained in the combustion exhaust gas of various combustion equipment and internal combustion engines.
This invention relates to a catalyst that can convert CO 2 and H 2 O and also purify NO x in a reducing atmosphere.
従来の技術
従来、この種の触媒としてはPt、Pd等の貴金
属触媒やCuO、MnO2、Co3O4等の酸化物触媒が
用いられている。前者は、三元触媒として自動車
排気ガス浄化触媒に用いられておりCO、HC等の
酸化、また還元雰囲気下では、NOx浄化を行う
ことができるが高価である。後者は、高温・還元
雰囲気下では容易に還元されて触媒活性が低下す
るので主として酸素存在下でCO、HC等の酸化触
媒として用いられている。これに対して、Ln1-x
AxCo1-yMyO3-〓系酸化物触媒は、CO、HC等の
酸化活性が高く、高温・還元雰囲気下でも還元さ
れにくく、かつ、還元雰囲気下においてNOxの
浄化を行うことができ、しかも、Pt、Pd等の貴
金属に比べて安価な酸化物触媒である。Conventional Technology Conventionally, noble metal catalysts such as Pt and Pd, and oxide catalysts such as CuO, MnO 2 and Co 3 O 4 have been used as this type of catalyst. The former is used as a three-way catalyst in automobile exhaust gas purification catalysts, and can oxidize CO, HC, etc., and purify NO x in a reducing atmosphere, but is expensive. The latter is used as an oxidation catalyst for CO, HC, etc. mainly in the presence of oxygen because it is easily reduced and its catalytic activity decreases at high temperatures and in a reducing atmosphere. In contrast, Ln 1-x
A x Co 1-y M y O 3- 〓-based oxide catalyst has high oxidation activity for CO, HC, etc., is difficult to reduce even at high temperatures and in a reducing atmosphere, and purifies NO x in a reducing atmosphere. Moreover, it is an oxide catalyst that is cheaper than noble metals such as Pt and Pd.
発明が解決しようとする問題点
一般式Ln1-xAxCo1-yMyO3-〓で表わされる酸化
物触媒は、水蒸気とNOxを多量に含む排気ガス
雰囲気中においてAのアルカリ土類元素が容易に
硝酸塩化し、触媒能が低下する。Problems to be Solved by the Invention The oxide catalyst represented by the general formula Ln 1-x A x Co 1-y M y O 3- Earth elements easily turn into nitrates, reducing catalytic ability.
問題点を解決するための手段
本発明は、前記の問題点を解決するため、一般
式Ln1-xAxCo1-yMyO3-〓(LnはLa、Ce、Pr、Nd
から選ぶ少なくとも一種の元素、AはCa、Sr、
Baから選ぶ少なくとも一種の元素、MはCr、
Mn、Fe、Ni、Vから選ぶ少なくとも一種の元
素、0<x<1、0<y<1、δは常温大気圧時
における酸化物の酸素欠損数であり、0<δ<
0.5)で表わされる酸化物触媒にMgOあるいは
MgOを主成分とする酸化物を混合、もしくは焼
成したものである。Means for Solving the Problems The present invention solves the above problems by using the general formula Ln 1-x A x Co 1-y M y O 3- (Ln is La, Ce, Pr, Nd
At least one element selected from A is Ca, Sr,
At least one element selected from Ba, M is Cr,
At least one element selected from Mn, Fe, Ni, and V, 0<x<1, 0<y<1, δ is the number of oxygen vacancies in the oxide at room temperature and atmospheric pressure, 0<δ<
MgO or
It is a mixture or fired product of oxide whose main component is MgO.
作 用
本発明になる触媒体では、MgOは塩基点とし
て働き400℃近くの温度まで雰囲気中のNOxを吸
収して、また、400℃以上では分解して元に戻る。
このためMgOあるいはMgOを主成分とする酸化
物と混合、もしくは焼成することにより酸化物触
媒のNOxによる触媒活性の低下がなくなる。Function In the catalyst body of the present invention, MgO acts as a basic site and absorbs NO x in the atmosphere up to a temperature of nearly 400°C, and decomposes and returns to its original state at temperatures above 400°C.
Therefore, by mixing with MgO or an oxide containing MgO as a main component or firing it, the catalytic activity of the oxide catalyst is prevented from decreasing due to NO x .
実施例
本実施例ではLa0.5Sr0.5CoO3-〓、S=0.05から
なる酸化物を用いた場合について述べる。La0.5
Sr0.5CoO3-〓は、各成分の金属塩を含む溶液とし
ゆう酸、アミン酸あるいは苛性アルカリの混合液
を用いて金属しゆう酸塩と金属水酸化物の混合体
として沈殿させ、ろ過、洗浄、乾燥後、空気中
800℃で10時間焼成して作成した。Example In this example, a case will be described in which an oxide consisting of La 0.5 Sr 0.5 CoO 3- 〓, S=0.05 is used. La 0.5
Sr 0.5 CoO 3- 〓 is precipitated as a mixture of metal oxalates and metal hydroxides using a solution containing the metal salts of each component and a mixture of oxalic acid, amino acid or caustic alkali, filtered, After cleaning and drying, in the air
It was created by firing at 800℃ for 10 hours.
上記酸化物触媒にMgOを重量比7:3の割合
で混合し、金属Ni発泡体からなる担体に担持し
測定試料とした。 MgO was mixed with the above oxide catalyst at a weight ratio of 7:3, and the mixture was supported on a carrier made of metallic Ni foam to prepare a measurement sample.
触媒体の特性評価として、触媒体を管状電気炉
に通した石英ガラス管内に設置し、温度を300℃
に設定してCO20ppm、NOx50ppm、H2O7%含む
石油ストーブ燃焼排気ガスを送り、COの酸化率
を測定した。また、サイクル寿命試験として、上
記と同成分の石油ストーブ排ガスを送りながら、
触媒体の温度を、300℃で3時間、600℃で1時間
交互に保持し、これを1サイクルとして500回行
い、各サイクルごとの300℃におけるCO酸化率を
測定した。 To evaluate the characteristics of the catalyst, the catalyst was placed inside a quartz glass tube passed through a tubular electric furnace, and the temperature was raised to 300°C.
The oxidation rate of CO was measured by setting 20ppm of CO, 50ppm of NOx , and 7% H 2 O to send oil stove combustion exhaust gas. In addition, as a cycle life test, while sending kerosene stove exhaust gas with the same composition as above,
The temperature of the catalyst body was alternately maintained at 300° C. for 3 hours and at 600° C. for 1 hour, and this was repeated 500 times as one cycle, and the CO oxidation rate at 300° C. was measured for each cycle.
比較のために同様の方法で作成したLa0.5Sr0.5
CoO3-〓を同重量金属Ni発泡体に担持した触媒体
についても同様の試験を行つた。 La 0.5 Sr 0.5 made in a similar way for comparison
Similar tests were conducted on a catalyst body in which CoO 3- 〓 was supported on a metal Ni foam of the same weight.
第1図にCO20ppm、NOx50ppm、H2O7%含ん
だ石油ストーブ燃焼排気ガスを300℃に設定した
触媒体に連続して送つた時のCO酸化率の測定結
果を示した。この結果よりMgOを混合すること
で水蒸気とNOxを含む排気ガス雰囲気下に長時
間おいても触媒能が低下しないことが認められ
た。また、触媒能が低下したMgOを混合した触
媒体を室温で一日放置し、300℃のCO酸化率を測
定した結果、触媒能の回復が認められた。これは
MgOの塩基性によつて、NOxによつてダメージ
を受けた部分からNO2 -、NO3 -が引き抜かれた
ためである。 Figure 1 shows the measurement results of the CO oxidation rate when kerosene stove combustion exhaust gas containing 20 ppm of CO, 50 ppm of NO x , and 7% of H 2 O was continuously sent to a catalyst body set at 300°C. From this result, it was confirmed that by mixing MgO, the catalytic performance did not decrease even if the catalyst was left in an exhaust gas atmosphere containing water vapor and NO x for a long time. In addition, the catalyst body mixed with MgO, whose catalytic ability had decreased, was left at room temperature for one day and the CO oxidation rate at 300°C was measured, and as a result, recovery of the catalytic ability was observed. this is
This is because NO 2 - and NO 3 - were extracted from the part damaged by NO x due to the basicity of MgO.
第2図にCO20ppm、NOx50ppm、H2O7%含ん
だ石油ストーブ燃焼排気ガスを送り、触媒体を
300℃で3時間、600℃で1時間交互に保持する
500回のサイクル寿命試験の300℃におけるCO酸
化率の変化を示した。この結果より、MgOを混
合することにより、NOxを吸収したMgOが600℃
で完全に元のMgOに戻るために酸化物触媒の
NOxによる触媒能の低下が非常に少ないことが
認められた。 Oil stove combustion exhaust gas containing 20ppm of CO, 50ppm of NO
Hold alternately at 300℃ for 3 hours and at 600℃ for 1 hour.
The changes in CO oxidation rate at 300℃ during 500 cycle life tests are shown. From this result, by mixing MgO, MgO that has absorbed NO x can be heated to 600°C.
of the oxide catalyst to completely return to the original MgO.
It was observed that the decrease in catalytic performance due to NO x was extremely small.
さらに還元雰囲気下におけるNOx還元試験で
は、MgOを混合した触媒体についてもLa0.5Sr0.5
CoO3-〓だけの触媒体と同様にNOxを還元するこ
とが認められた。 Furthermore, in a NO x reduction test under a reducing atmosphere, the catalyst body containing MgO also showed La 0.5 Sr 0.5
It was confirmed that the catalyst reduced NO x in the same way as the catalyst containing only CoO 3- 〓.
MgOと混合した触媒をコージエライト、ムラ
イト等のセラミツク担体に担持した触媒体を空気
中600℃で100時間加熱処理し、300℃でのCO酸化
率の測定を行つたが、触媒能の低下はほとんどな
かつた。これは、La0.5Sr0.5CoO3-〓だけの触媒で
はCoがSiO2やAl2O3と反応して触媒能が低下して
いたが、MgOを混合した触媒では、MgOが触媒
とSiO2やAl2O3との反応を防止するためである。 A catalyst body in which a catalyst mixed with MgO was supported on a ceramic support such as cordierite or mullite was heat treated in air at 600℃ for 100 hours, and the CO oxidation rate was measured at 300℃, but there was almost no decrease in catalytic performance. Nakatsuta. This is because in the case of a catalyst containing only La 0.5 Sr 0.5 CoO 3- 〓, Co reacted with SiO 2 and Al 2 O 3 and the catalytic performance decreased, but in a catalyst containing MgO, MgO interacted with the catalyst and SiO 2 This is to prevent reactions with Al 2 O 3 and Al 2 O 3 .
以上のように本発明になる排ガス浄化用触媒体
は、水蒸気とNOxを多量に含む排ガス雰囲気に
おいても触媒能の低下がほとんどなく、また、
600℃という、一般の燃焼機器でも容易に得るこ
とのできる温度で再生可能な触媒体である。 As described above, the catalyst body for exhaust gas purification according to the present invention shows almost no decrease in catalytic performance even in an exhaust gas atmosphere containing a large amount of water vapor and NOx , and
It is a catalyst that can be regenerated at a temperature of 600°C, which can be easily obtained using general combustion equipment.
さらに、実施例ではLnがLa、AがSr、の場合
についてのみ述べたが、LaがCe、Pr、Ndまたは
La、Ce、Pr、Ndを二種以上含む場合、AがCa、
BaまたはSr、Ca、Baを二種以上含む場合、Mが
Cr、Mn、Fe、Ni、Vまたは、それらを二種以
上含む場合の酸化触媒体についても同様の効果が
得られた。また、担体として金属Ni発泡体を用
いた場合のみを述べたがFe、TiまたはNi、Fe、
Tiを主成分とする金属担体を用いた場合でも同
様の効果が得られた。 Furthermore, in the embodiment, only the case where Ln is La and A is Sr, but La is Ce, Pr, Nd or
When containing two or more types of La, Ce, Pr, and Nd, A is Ca,
When containing Ba or two or more types of Sr, Ca, and Ba, M
Similar effects were obtained with oxidation catalysts containing Cr, Mn, Fe, Ni, V, or two or more thereof. In addition, although only the case where metallic Ni foam was used as the carrier was described, Fe, Ti or Ni, Fe,
A similar effect was obtained even when a metal support containing Ti as a main component was used.
このような酸化物触媒にPt族貴金属触媒を添
加すると従来のPt族貴金属触媒を用いた触媒体
に比べて、極めて少量のPt族貴金属触媒の添加
で同程度の触媒能を得ることができた。 When a Pt group noble metal catalyst is added to such an oxide catalyst, it was possible to obtain the same level of catalytic activity with the addition of an extremely small amount of the Pt group noble metal catalyst compared to a catalyst body using a conventional Pt group noble metal catalyst. .
発明の効果
本発明によりLn1-xAxCo1-yMyO3-〓で表わされ
る酸化物触媒にMgOあるいは、MgOを主成分と
する酸化物を混合、もしくは焼成することによ
り、水蒸気とNOxを多量に含む排気ガス雰囲気
においても触媒能がほとんど低下せず、安価な触
媒体を得ることができる。Effects of the Invention According to the present invention, by mixing or calcining MgO or an oxide mainly composed of MgO with an oxide catalyst represented by Ln 1-x A x Co 1-y M y O 3- Even in an exhaust gas atmosphere containing a large amount of NO x , the catalytic performance hardly decreases, and an inexpensive catalyst body can be obtained.
第1図は本発明の一実施例の触媒体の300℃に
おける水蒸気とNOxを含んだ排気ガスに対する
CO酸化率の安定性を示す特性図、第2図は同触
媒体の水蒸気とNOxを含んだ排気ガスを連続し
て送り、触媒体温度を300℃3時間、600℃1時間
で交互に保持したサイクル寿命試験を行つた時の
300℃におけるCO酸化率の安定性を示す特性図で
ある。
Figure 1 shows how the catalyst of one embodiment of the present invention reacts to exhaust gas containing water vapor and NO x at 300°C.
Figure 2 is a characteristic diagram showing the stability of the CO oxidation rate. Exhaust gas containing water vapor and NO When carrying out a cycle life test
FIG. 2 is a characteristic diagram showing the stability of CO oxidation rate at 300°C.
Claims (1)
Pr、Ndから選ぶ少なくとも一種の元素、Aは
Ca、Sr、Baから選ぶ少なくとも一種の元素、M
はFe、Mn、Cr、Vから選ぶ少なくとも一種の元
素、0<x<1、0<y<1、δは常温大気圧時
における酸化物の酸素欠損数であり、0<δ<
0.5)で表される酸化触媒とMgOあるいはMgOを
主成分とする酸化物と混合もしくは、焼成したこ
とを特徴とする排ガス浄化用触媒体。 2 Ni、Fe、Tiから選ぶ少なくとも一種の元素
からなる金属、もしくは、それらを主成分とする
合金からなる担体に酸化物触媒を担持したことを
特徴とする特許請求の範囲第1項記載の排ガス浄
化用触媒体。 3 セラミツク担体に酸化物触媒を担持したこと
を特徴とする特許請求の範囲第1項記載の排ガス
浄化触媒体。[Claims] 1 General formula Ln 1-x A x Co 1-y M y O 3- (Ln is La, Ce,
At least one element selected from Pr and Nd, A is
At least one element selected from Ca, Sr, and Ba, M
is at least one element selected from Fe, Mn, Cr, and V, 0<x<1, 0<y<1, δ is the number of oxygen vacancies in the oxide at room temperature and atmospheric pressure, and 0<δ<
0.5) and an oxidation catalyst represented by MgO or an oxide whose main component is MgO. 2. The exhaust gas according to claim 1, characterized in that the oxide catalyst is supported on a carrier made of a metal made of at least one element selected from Ni, Fe, and Ti, or an alloy made of these as main components. Catalyst for purification. 3. The exhaust gas purification catalyst body according to claim 1, characterized in that an oxide catalyst is supported on a ceramic carrier.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP62141695A JPS63305940A (en) | 1987-06-05 | 1987-06-05 | Catalytic body for purifying exhaust gas |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP62141695A JPS63305940A (en) | 1987-06-05 | 1987-06-05 | Catalytic body for purifying exhaust gas |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS63305940A JPS63305940A (en) | 1988-12-13 |
| JPH0580258B2 true JPH0580258B2 (en) | 1993-11-08 |
Family
ID=15298060
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP62141695A Granted JPS63305940A (en) | 1987-06-05 | 1987-06-05 | Catalytic body for purifying exhaust gas |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS63305940A (en) |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN109487299B (en) * | 2018-12-03 | 2020-12-25 | 山西大学 | High-temperature electrolysis of CO2Cathode material of electrolytic cell and preparation method thereof |
-
1987
- 1987-06-05 JP JP62141695A patent/JPS63305940A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS63305940A (en) | 1988-12-13 |
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