JP3106567B2 - Exhaust gas purification device - Google Patents

Exhaust gas purification device

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Publication number
JP3106567B2
JP3106567B2 JP03188324A JP18832491A JP3106567B2 JP 3106567 B2 JP3106567 B2 JP 3106567B2 JP 03188324 A JP03188324 A JP 03188324A JP 18832491 A JP18832491 A JP 18832491A JP 3106567 B2 JP3106567 B2 JP 3106567B2
Authority
JP
Japan
Prior art keywords
catalyst
exhaust gas
nox
zro
alumina
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
Application number
JP03188324A
Other languages
Japanese (ja)
Other versions
JPH057777A (en
Inventor
秀昭 村木
健治 加藤
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.)
Toyota Motor Corp
Original Assignee
Toyota Motor Corp
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Filing date
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Priority to JP03188324A priority Critical patent/JP3106567B2/en
Publication of JPH057777A publication Critical patent/JPH057777A/en
Application granted granted Critical
Publication of JP3106567B2 publication Critical patent/JP3106567B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【産業上の利用分野】本発明は、排気ガス中の窒素酸化
物(以下、NOx ともいう)を、酸素過剰雰囲気中で還
元することのできる排気ガス浄化用触媒を備えた排気浄
化装置に関し、自動車用内燃機関の排気ガス中のNOx
の還元等に用いられる。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an exhaust gas purifying system provided with an exhaust gas purifying catalyst capable of reducing nitrogen oxides (hereinafter also referred to as NOx) in exhaust gas in an oxygen-excess atmosphere.
Relates apparatus, NOx in the exhaust gas of an automotive internal combustion engine
It is used for reduction and the like.

【0002】[0002]

【従来の技術】自動車用内燃機関は、性能上低燃費であ
ることが要求される他、近年、地球温暖化防止等の観点
からCO2 の排出を少なくすることが望まれている。こ
れらの要求を一挙に満足する解決策として、ストイキ
(理論空燃比)より空燃比リーン側で燃焼させるリーン
バーンエンジンが開発され、一部実用化されている。
2. Description of the Related Art Internal combustion engines for automobiles are required to have low fuel consumption in terms of performance, and in recent years, it has been desired to reduce CO 2 emissions from the viewpoint of preventing global warming. As a solution that satisfies these requirements at once, a lean burn engine that burns on the air-fuel ratio lean side from stoichiometric air (stoichiometric air-fuel ratio) has been developed and partially put into practical use.

【0003】しかし、リーンバーンエンジンでは、排気
が酸素過剰雰囲気のため、三元触媒(ストイキにおける
燃焼の排気ガスに対してはNOx 、CO、HCの浄化に
効果をもつ)によって、排気ガス中のNOx を還元する
ことができない。
However, in a lean-burn engine, since the exhaust gas is in an oxygen-excess atmosphere, a three-way catalyst (which has an effect of purifying NOx, CO, and HC with respect to exhaust gas generated by stoichiometric combustion) is used. NOx cannot be reduced.

【0004】これを解決するために、特開平1−139
145号公報は、CuまたはCoをイオン交換してゼオ
ライトに担持せしめた触媒を内燃機関の排気系の上流部
に設け、排気系の下流部に貴金属系触媒を設置した排気
浄化装置を提案している。
In order to solve this problem, Japanese Patent Laid-Open Publication No.
No. 145 proposes an exhaust purification device in which a catalyst in which Cu or Co is ion-exchanged and supported on zeolite is provided in an upstream portion of an exhaust system of an internal combustion engine, and a noble metal catalyst is provided in a downstream portion of the exhaust system. I have.

【0005】[0005]

【発明が解決しようとする課題】しかし、Coをアルミ
ナ、ゼオライト等に担持して構成した触媒は、高温時
(約600°C以上)にCoAl2 4 を生成し、触媒
の劣化を引き起こす。また、CuやNiであってもAl
と反応し、触媒劣化が生じる。
However, a catalyst formed by supporting Co on alumina, zeolite or the like generates CoAl 2 O 4 at a high temperature (about 600 ° C. or higher), causing deterioration of the catalyst. Further, even if Cu or Ni is used,
And catalyst deterioration occurs.

【0006】本発明の目的は、酸素過剰雰囲気でNOx
を還元する触媒であって、耐高温劣化性をもつ排気ガス
浄化用触媒を備えた排気浄化装置を提供することにあ
る。
SUMMARY OF THE INVENTION It is an object of the present invention to provide a NOx
It is an object of the present invention to provide an exhaust gas purifying apparatus provided with a catalyst for purifying exhaust gas, which has a resistance to high-temperature deterioration, which is a catalyst for reducing methane.

【0007】[0007]

【課題を解決するための手段】上記目的を達成する本発
明はつぎの通りである。 内燃機関の排気系に、排気ガス
中の窒素酸化物を、酸素過剰雰囲気中で、炭化水素の存
在下で還元するための、ZrO 2 に遷移金属をイオン交
換して担持させた触媒を設け、該触媒より下流側にアル
ミナにPtを担持させたPt/アルミナ触媒を設けたこ
とを特徴とする排気ガス浄化装置。
In order to achieve the object of the present onset to achieve the above purpose
The light is as follows. Exhaust gas in the exhaust system of the internal combustion engine
Nitrogen oxides in an oxygen-excess atmosphere in the presence of hydrocarbons.
Ion exchange of transition metal with ZrO 2 for reduction in presence
In this case, a supported catalyst is provided.
Pt / alumina catalyst with Pt supported on Mina
An exhaust gas purification device characterized by the following.

【0008】[0008]

【作用】上記本発明の排気ガス浄化装置では、Co、C
u等の遷移金属は、高温になってもZrO2 と反応しな
い。また、ZrO2 の耐熱温度は非常に高く、900°
Cでも耐える。これらの結果、遷移金属をZrO2 に担
持した触媒は、ゼオライトやアルミナに担持させたもの
に比べて、耐高温劣化が改善される。また、Coは高温
において優れたNOx 浄化活性を示す。したがって、C
o等をZrO2 に担持した触媒を、高温部である内燃機
関の排気系上流部に設けることによって、内燃機関から
の排気ガス中のNOx を高いNOx 浄化率で還元でき、
しかも耐久性に優れた排気浄化装置が得られる。また、
Co等をZrO 2 に担持した触媒を設け、その下流にP
t/アルミナ触媒を設けたので、広い温度範囲において
高いNOx 浄化率が得られる。
In the exhaust gas purifying apparatus of the present invention, Co, C
Transition metals such as u do not react with ZrO 2 even at high temperatures. Also, the heat resistance temperature of ZrO 2 is very high, 900 °
C can withstand. As a result, the catalyst in which the transition metal is supported on ZrO 2 has improved resistance to high-temperature deterioration as compared with the catalyst in which the transition metal is supported on zeolite or alumina. Also, Co exhibits excellent NOx purification activity at high temperatures. Therefore, C
By providing a catalyst carrying o and the like on ZrO 2 in the exhaust system upstream of the internal combustion engine, which is a high temperature portion, NOx in exhaust gas from the internal combustion engine can be reduced at a high NOx purification rate,
In addition, an exhaust purification device having excellent durability can be obtained. Also,
A catalyst supporting Co or the like on ZrO 2 is provided, and P
t / Alumina catalyst provided, so over a wide temperature range
A high NOx purification rate is obtained.

【0009】[0009]

【実施例】図1は、本発明の一実施例の排気浄化装置に
用いられる排気ガス浄化用触媒2を示している。図1に
示す如く、触媒2は、多数の独立流路をもつコーディエ
ライトの一体性(モノリス)担体4と、前記独立流路表
面にコーティングされたジルコニア(ZrO2 )層6
と、該ジルコニア層6にイオン交換して担持された遷移
金属8から成る。遷移金属8としては、コバルト(C
o)、銅(Cu)、ニッケル(Ni)が、高温でのNO
x 浄化特性が優れているので、使用に適する。
FIG. 1 shows an exhaust gas purifying apparatus according to an embodiment of the present invention.
1 shows an exhaust gas purification catalyst 2 to be used . As shown in FIG. 1, a catalyst 2 comprises a cordierite monolith carrier 4 having a large number of independent flow paths, and a zirconia (ZrO 2 ) layer 6 coated on the surface of the independent flow paths.
And a transition metal 8 carried on the zirconia layer 6 by ion exchange. As the transition metal 8, cobalt (C
o), copper (Cu), nickel (Ni)
x Suitable for use because of its excellent purification properties.

【0010】触媒2がCo/ZrO2 触媒である場合の
実施例について説明する。ジルコニア粉末100部と市
販の硝酸アルミニウム水溶液14部とを水および硝酸と
共にボールミリングすることによりウオッシュコートス
ラリーを生成させた。そして断面積1in2 当たり約4
00の流路を含む0.65リッターのコーディエライト
の一体性担体をウオッシュコートスラリー中に浸漬し
た。続いて圧縮空気で一体性担体のセル内の過剰液を吹
き去り、この一体性担体を乾燥し、700°Cで一時間
焼成し、一体性担体上に約50ミクロンのジルコニアを
コートした。次に該一体性担体を0.23mol/lの
濃度の硝酸コバルト水溶液に浸漬し、乾燥後、600°
Cで1時間焼成して33g/lの酸化コバルトを担持し
た。かくして触媒2を作製した。
An embodiment in which the catalyst 2 is a Co / ZrO 2 catalyst will be described. Wash coat slurry was produced by ball milling 100 parts of zirconia powder and 14 parts of a commercially available aqueous solution of aluminum nitrate together with water and nitric acid. The cross-sectional area 1in 2 per about 4
A 0.65 liter cordierite integral carrier containing 00 channels was immersed in the washcoat slurry. Subsequently, the excess liquid in the cells of the integral carrier was blown off with compressed air, and the integral carrier was dried and baked at 700 ° C. for 1 hour to coat about 50 μm of zirconia on the integral carrier. Next, the integrated carrier was immersed in a 0.23 mol / l aqueous solution of cobalt nitrate, dried,
C. for 1 hour to carry 33 g / l of cobalt oxide. Thus, catalyst 2 was prepared.

【0011】上記のCo/ZrO2 触媒とは別に、貴金
属系リーンNOx 触媒として、Ptをアルミナに担持し
た触媒10を、次のようにして作製した。1.3リッタ
ーのコーディエライトの一体性担体を用いて上記と同様
にして一体性担体上にアルミナをコートした。次に硝酸
セリウム2.5mol/lの水溶液に上記のアルミナを
コートした一体性担体を浸漬し、乾燥後600°Cで3
時間、空気中で焼成し、該担体上に酸化セリウム0.1
5mol/lを担持した。次に0.005mol/lの
濃度のジニトロジアンミン白金の硝酸酸性水溶液に浸漬
し、乾燥後、200°Cで1時間焼成して1.5g/l
の白金を担持した。かくしてPt/アルミナ触媒10を
作製した。
Apart from the above-mentioned Co / ZrO 2 catalyst, a catalyst 10 carrying Pt on alumina was prepared as a noble metal-based lean NOx catalyst as follows. Alumina was coated on the integral carrier in the same manner as described above using 1.3 liter of the cordierite integral carrier. Next, the above-mentioned integral carrier coated with alumina was immersed in an aqueous solution of cerium nitrate 2.5 mol / l, dried, and dried at 600 ° C. for 3 hours.
Calcium for 0.1 hour on the support
5 mol / l was loaded. Next, it is immersed in a 0.005 mol / l dinitrodiammineplatinum aqueous solution of nitric acid, dried and calcined at 200 ° C. for 1 hour to give 1.5 g / l.
Of platinum was supported. Thus, a Pt / alumina catalyst 10 was produced.

【0012】図2は、Co/ZrO2 触媒2およびPt
/アルミナ触媒10のNOx 浄化作用のメカニズムを示
す。排気ガス中に含まれる炭化水素(HC)は、触媒部
で一部が部分酸化されて活性種を生じ、残りは完全酸化
されてCO2 とH2 Oになる。活性種の一部は触媒2、
10の助けを借りてNOx と反応してNOx を還元し、
2 、CO2 、H2 Oにして浄化する。また、活性種の
残りは酸化されて最終的にCO2 になる。上記のメカニ
ズムから明らかなように、NOx の浄化にはHCが必要
である。
FIG. 2 shows Co / ZrO 2 catalyst 2 and Pt
2 shows the mechanism of the NOx purification action of the alumina catalyst 10. Part of hydrocarbons (HC) contained in the exhaust gas is partially oxidized in the catalyst part to generate active species, and the remaining parts are completely oxidized to CO 2 and H 2 O. Some of the active species are catalyst 2,
React with NOx with the help of 10 to reduce NOx,
Purify with N 2 , CO 2 , H 2 O. In addition, the remaining active species are oxidized to finally become CO 2 . As is clear from the above mechanism, HC is required for NOx purification.

【0013】図3は、Co/ZrO2 触媒2とPt/ア
ルミナ触媒10がどの温度領域で高いNOx 浄化率を示
すかの概略を示している。Coは高温域で良好なNOx
浄化率を示すので、Co/ZrO2 触媒2のNOx 浄化
率の山は曲線Aに示すように高温側にあらわれる。これ
に対し、Pt系リーンNOx 触媒10のNOx 浄化率の
山は曲線Bに示すように比較的低温側にあらわれる。
FIG. 3 schematically shows in which temperature range the Co / ZrO 2 catalyst 2 and the Pt / alumina catalyst 10 exhibit a high NOx purification rate. Co is good NOx in high temperature range
Since the purification rate is shown, the peak of the NOx purification rate of the Co / ZrO 2 catalyst 2 appears on the high temperature side as shown by the curve A. On the other hand, the peak of the NOx purification rate of the Pt-based lean NOx catalyst 10 appears on the relatively low temperature side as shown by the curve B.

【0014】図4は希薄燃焼可能な内燃機関12の排気
系14に、遷移金属たとえばCoをイオン交換してZr
2 に担持させた触媒2とPt系リーンNOx 触媒10
を配設した排気浄化システムを示している。Co/Zr
2 触媒2は高温部、すなわち排気系14の上流部に配
置され、Pt系リーンNOx 触媒10は排気系14の下
流部に配置されている。
FIG. 4 shows that the exhaust system 14 of the internal combustion engine 12 capable of lean combustion is ion-exchanged with a transition metal,
Catalyst 2 supported on O 2 and Pt-based lean NOx catalyst 10
1 shows an exhaust gas purification system provided with. Co / Zr
The O 2 catalyst 2 is disposed at a high temperature portion, that is, upstream of the exhaust system 14, and the Pt-based lean NOx catalyst 10 is disposed downstream of the exhaust system 14.

【0015】なお、運転条件を検出するための各種のセ
ンサが設けられており、スロットル開度センサ16、吸
気圧力センサ18、燃焼圧センサ20が含まれる。セン
サ出力は電子制御装置(ECU)22に送られる。ま
た、ECU22の出力信号によりEGR弁24が制御さ
れるようになっている。EGR(排気再循環)量が大に
なると燃焼が若干犠牲にされて未燃炭化水素が増え、触
媒2、10へのHC供給量が増加する。
Various sensors for detecting operating conditions are provided, and include a throttle opening sensor 16, an intake pressure sensor 18, and a combustion pressure sensor 20. The sensor output is sent to an electronic control unit (ECU) 22. Further, the EGR valve 24 is controlled by an output signal of the ECU 22. When the EGR (exhaust gas recirculation) amount increases, combustion is slightly sacrificed, unburned hydrocarbons increase, and the amount of HC supplied to the catalysts 2, 10 increases.

【0016】図4の排気浄化システムの作用を図5およ
び図3の曲線Cに示す。ただし、図5にはPt/アルミ
ナ触媒のみを設置してCo/ZrO2 触媒を設けない場
合を比較例として示してある。図3の曲線Cからわかる
ように、排気高温となる運転領域ではCo/ZrO2
媒2が効果的に働いてNOx を浄化し、排気低温となる
運転領域ではPt/アルミナ触媒10が効果的に働いて
NOx を浄化する。したがって、高いNOx 浄化域を示
せる温度域が、曲線A、Bに比べて拡がっている。
The operation of the exhaust gas purification system shown in FIG. 4 is shown by a curve C in FIGS. 5 and 3. However, FIG. 5 shows a case where only the Pt / alumina catalyst is provided and the Co / ZrO 2 catalyst is not provided as a comparative example. As can be seen from the curve C in FIG. 3, the Co / ZrO 2 catalyst 2 effectively works to purify NOx in the operating region where the exhaust gas temperature is high, and the Pt / alumina catalyst 10 is effective in the operating region where the exhaust gas temperature is low. Working to purify NOx. Therefore, the temperature range in which a high NOx purification range can be shown is wider than curves A and B.

【0017】図5は図4のシステムにおける車速とNO
x 浄化率との関係を示している。車速が高速の時は排気
温が高くなるが、Co/ZrO2 触媒2が効果的に働い
てNOx を浄化するので、高いNOx 浄化率を示してい
る。また、低速域では排気温も低くなるが、Pt/アル
ミナ触媒10が効果的に働いてNOx を浄化するので、
高いNOx 浄化率を示す。したがって、低速だろうが高
速だろうが高いNOx浄化率を示すことができる。これ
に対し、比較例では高速では高温となってPt系リーン
NOx 触媒10のNOx 浄化率が落ちるのでシステムと
してのNOx 浄化率も低下している。
FIG. 5 shows vehicle speed and NO in the system of FIG.
x Shows relationship with purification rate. When the vehicle speed is high, the exhaust gas temperature becomes high, but the Co / ZrO 2 catalyst 2 works effectively to purify NOx, so that a high NOx purification rate is shown. Further, although the exhaust gas temperature becomes low in the low speed range, the Pt / alumina catalyst 10 works effectively to purify NOx, so that
It shows a high NOx purification rate. Therefore, a high NOx purification rate can be exhibited regardless of whether the speed is low or high. On the other hand, in the comparative example, the temperature becomes high at a high speed, and the NOx purification rate of the Pt-based lean NOx catalyst 10 decreases, so that the NOx purification rate of the system also decreases.

【0018】また、CoはZrO2 に担持されているの
で、Coがアルミナやゼオライトに担持されるような場
合に高温域で生じるCoAl2 4 が生成されず、Co
/ZrO2 触媒2は従来の触媒の高温劣化の問題も解決
している。
Further, since Co is supported on ZrO 2 , when Co is supported on alumina or zeolite, CoAl 2 O 4 generated in a high temperature range is not generated, and Co is not generated.
The / ZrO 2 catalyst 2 also solves the problem of high temperature degradation of conventional catalysts.

【0019】また、高温域では、排気ガス中のHCの触
媒での完全酸化が促進され活性種の生成量が減少してN
Ox 浄化率の低下が生じるおそれがあるので、それを防
止するために、各種運転センサから信号をECU22に
入力し、ECU22にて排気高温となる運転領域か否か
を判定し、排気高温となる運転領域となる場合はEGR
弁24の開度を大にしてEGR量を増やし、未燃燃料か
ら生成されたHCをCo/ZrO2 触媒2に供給するよ
うにする。上記実施例では、触媒2の遷移金属としてC
oを例にとったが、Cu、Ni等であってもよい。
In a high temperature range, the complete oxidation of HC in the exhaust gas by the catalyst is promoted, and the amount of active species generated decreases, and
Since there is a possibility that the Ox purification rate may decrease, in order to prevent this, signals from various operation sensors are input to the ECU 22, and the ECU 22 determines whether or not the operating region is at a high exhaust gas temperature, and the high exhaust gas temperature is reached. EGR when operating
The EGR amount is increased by increasing the opening of the valve 24 so that HC generated from the unburned fuel is supplied to the Co / ZrO 2 catalyst 2. In the above embodiment, the transition metal of the catalyst 2 is C
Although o is taken as an example, Cu, Ni or the like may be used.

【0020】[0020]

【発明の効果】本発明によれば、内燃機関の排気系に、
排気ガス中の窒素酸化物を、酸素過剰雰囲気中で、炭化
水素の存在下で還元するための、ZrO 2 に遷移金属を
イオン 交換して担持させた触媒を設け、該触媒より下流
側にアルミナにPtを担持させたPt/アルミナ触媒を
設けたので、遷移金属としてたとえばCoを例にとると
(CuやNiでも同様)、 (イ) Coは高温にあって優れたNOx 浄化性能を示
すことにより高温において良好なNOx 浄化率が得ら
れ、 (ロ) 担体にZrO2 を使用したために担体にアルミ
ナやゼオライトを使用した場合のようなCoAl2 4
が生成されないことにより触媒の高温劣化が防止され (ハ) ZrO2 が優れた耐熱性をもつことにより優れ
た高温耐久性が得られ、 (ニ) 高いNOx浄化率が得られる温度範囲が広が
る。
According to the present invention, the exhaust system of an internal combustion engine
Nitrogen oxides in exhaust gas are carbonized in an oxygen-rich atmosphere.
Transition metal to ZrO 2 for reduction in the presence of hydrogen
Provide a catalyst supported by ion exchange, and
Pt / alumina catalyst with Pt supported on alumina on the side
Since there is provided, taking as an example such as Co as the transition metal (as also Cu or Ni), (b) Co is good NOx purification rate is obtained at a high temperature by showing excellent NOx purification performance In the high-temperature (B) CoAl 2 O 4 as in the case where alumina or zeolite is used for the carrier because ZrO 2 is used for the carrier.
There is prevented the high temperature deterioration of the catalyst by not generated, the (c) excellent high-temperature durability by having the ZrO 2 excellent heat resistance resulting et al is, (d) a higher temperature range the NOx purification rate is obtained Hiroga
You.

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

【図1】本発明の一実施例に係る排気ガス浄化用触媒一
部を断面にして示した側面図である。
FIG. 1 is a side view showing a cross section of a part of an exhaust gas purifying catalyst according to an embodiment of the present invention.

【図2】図1の触媒のNOx 浄化メカニズムを示すブロ
ック図である。
FIG. 2 is a block diagram showing a NOx purification mechanism of the catalyst of FIG.

【図3】種々の触媒または触媒の組合せのNOx 浄化率
と温度との関係図である。
FIG. 3 is a graph showing the relationship between the NOx purification rate and temperature of various catalysts or combinations of catalysts.

【図4】図1の触媒を装着した内燃機関の排気浄化装置
の系統図である。
FIG. 4 is a system diagram of an exhaust gas purification device for an internal combustion engine equipped with the catalyst of FIG. 1;

【図5】図4の系統および比較例の系統のNOx 浄化率
と車速との関係図である。
FIG. 5 is a relationship diagram between the NOx purification rate and the vehicle speed of the system of FIG. 4 and the system of the comparative example.

【符号の説明】[Explanation of symbols]

2 触媒(Co/ZrO2 触媒) 4 コーディエライトモノリス担体 6 ジルコニア(ZrO2 )層 8 遷移金属(たとえばCo)10 Pt/アルミナ触媒 2 Catalyst (Co / ZrO 2 catalyst) 4 Cordierite monolith support 6 Zirconia (ZrO 2 ) layer 8 Transition metal (for example, Co) 10 Pt / alumina catalyst

フロントページの続き (58)調査した分野(Int.Cl.7,DB名) B01J 21/00 - 37/36 B01D 53/86 - 53/96 CA(STN)Continuation of the front page (58) Field surveyed (Int. Cl. 7 , DB name) B01J 21/00-37/36 B01D 53/86-53/96 CA (STN)

Claims (1)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 内燃機関の排気系に、排気ガス中の窒素
酸化物を、酸素過剰雰囲気中で、炭化水素の存在下で還
元するための、ZrO2 に遷移金属をイオン交換して担
持させた触媒を設け、該触媒より下流側にアルミナにP
tを担持させたPt/アルミナ触媒を設けたことを特徴
とする排気ガス浄化装置
To 1. A exhaust system of an internal combustion engine, the nitrogen oxides in the exhaust gas, in an oxygen-rich atmosphere, the order to reduced in the presence of hydrocarbons, a transition metal is ion-exchanged to the ZrO 2 carrier And a catalyst is provided on the downstream side of the catalyst.
An exhaust gas purification device comprising a Pt / alumina catalyst supporting t .
JP03188324A 1991-07-03 1991-07-03 Exhaust gas purification device Expired - Fee Related JP3106567B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP03188324A JP3106567B2 (en) 1991-07-03 1991-07-03 Exhaust gas purification device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP03188324A JP3106567B2 (en) 1991-07-03 1991-07-03 Exhaust gas purification device

Publications (2)

Publication Number Publication Date
JPH057777A JPH057777A (en) 1993-01-19
JP3106567B2 true JP3106567B2 (en) 2000-11-06

Family

ID=16221614

Family Applications (1)

Application Number Title Priority Date Filing Date
JP03188324A Expired - Fee Related JP3106567B2 (en) 1991-07-03 1991-07-03 Exhaust gas purification device

Country Status (1)

Country Link
JP (1) JP3106567B2 (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6600135B2 (en) 2000-09-12 2003-07-29 Daihen Corporation Method and apparatus for controlling AC pulse arc welding and welding power source apparatus

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2609974B2 (en) * 1992-06-24 1997-05-14 工業技術院長 Catalyst for catalytic reduction of nitrogen oxides
JPH11244663A (en) * 1998-03-04 1999-09-14 Toyota Central Res & Dev Lab Inc Exhaust gas cleaning device

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6600135B2 (en) 2000-09-12 2003-07-29 Daihen Corporation Method and apparatus for controlling AC pulse arc welding and welding power source apparatus

Also Published As

Publication number Publication date
JPH057777A (en) 1993-01-19

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