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JP2009028593A - Refreshing method of exhaust gas cleaning catalyst - Google Patents

Refreshing method of exhaust gas cleaning catalyst Download PDF

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JP2009028593A
JP2009028593A JP2007193038A JP2007193038A JP2009028593A JP 2009028593 A JP2009028593 A JP 2009028593A JP 2007193038 A JP2007193038 A JP 2007193038A JP 2007193038 A JP2007193038 A JP 2007193038A JP 2009028593 A JP2009028593 A JP 2009028593A
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catalyst
exhaust gas
temperature
oxygen
composite oxide
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Seiji Miyoshi
誠治 三好
Hideji Iwakuni
秀治 岩国
Hirosuke Sumita
弘祐 住田
Akihide Takami
明秀 高見
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Mazda Motor Corp
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Abstract

<P>PROBLEM TO BE SOLVED: To regenerate exhaust gas cleaning catalyst deteriorated by being exposed to high temperature exhaust gas. <P>SOLUTION: Oxygen-lack exhaust gas is passed through the catalyst 3 containing a CeZr-based composite oxide formed by carrying the catalyst metal for more than a predetermined time, in the case that the catalyst 3 is determined and the determined result is obtained when high temperature oxygen-surplus exhaust gas flows in for more than a predetermined time. <P>COPYRIGHT: (C)2009,JPO&INPIT

Description

本発明は、排気ガス浄化用触媒のリフレッシュ方法に関する。     The present invention relates to a method for refreshing an exhaust gas purifying catalyst.

エンジンから排出される排気ガスの浄化には、触媒金属としてのPt、Pd、Rh等が活性アルミナ、Ce含有酸素吸蔵材等のサポート材に担持されてなる触媒が使用されることが多い。例えば、Pt担持酸素吸蔵材、Rh担持酸素吸蔵材、Pd担持アルミナ等のように、無機酸化物粒子の表面に触媒金属が分散担持されている触媒である。     For purification of exhaust gas discharged from the engine, a catalyst is often used in which Pt, Pd, Rh, etc. as catalyst metals are supported on a support material such as activated alumina or a Ce-containing oxygen storage material. For example, a catalyst in which a catalytic metal is dispersedly supported on the surface of inorganic oxide particles, such as a Pt-supported oxygen storage material, an Rh-supported oxygen storage material, and a Pd-supported alumina.

アルミナは、耐熱性が高く且つ比表面積が大きいので、触媒金属の高分散担持に適したサポート材である。一方、酸素吸蔵材は、排気ガスが酸素過剰状態にあるときに排気ガス中の酸素を吸蔵し、排気ガスが酸素不足状態になると、吸蔵していた酸素を放出する性質を有する。従って、酸素吸蔵材は、排気ガスの酸素濃度変動を吸収することに役立ち、また、その放出酸素は触媒金属による排気ガスの浄化を促進する。     Alumina has a high heat resistance and a large specific surface area, and is therefore a support material suitable for highly dispersed support of catalyst metal. On the other hand, the oxygen storage material has a property of storing oxygen in the exhaust gas when the exhaust gas is in an oxygen excess state and releasing the stored oxygen when the exhaust gas is in an oxygen deficient state. Therefore, the oxygen storage material is useful for absorbing fluctuations in the oxygen concentration of the exhaust gas, and the released oxygen promotes purification of the exhaust gas by the catalytic metal.

このような酸素吸蔵材としては、Ce酸化物の他、CeとZrとの複合酸化物、Ceと他の希土類元素との複合酸化物が知られている。例えば、特許文献1には、平均粒径10nm未満の一次粒子が凝集して形成された中空状のCeZr複合酸化物に触媒金属を担持してなる触媒が記載されている。しかし、そのような触媒であっても、高温の排気ガスに晒されると、触媒活性が低下する。     As such oxygen storage materials, Ce and Zr composite oxides, and Ce and other rare earth composite oxides are known in addition to Ce oxides. For example, Patent Document 1 describes a catalyst in which a catalytic metal is supported on a hollow CeZr composite oxide formed by agglomerating primary particles having an average particle size of less than 10 nm. However, even if such a catalyst is exposed to high-temperature exhaust gas, the catalytic activity decreases.

これに対して、特許文献2には、例えばCeZrY複合酸化物やZrLa複合酸化物にPtを担持させてなる触媒に対して、酸素を含む酸化雰囲気中にて加熱する酸化処理、及び還元処理を施すことにより、該触媒をリフレッシュするという方法が開示されている。すなわち、粒成長したPtが、上記酸化処理により酸化物となって、CeZrY複合酸化物等の担体上で拡がって分散し、この分散したPt酸化物が、その後の還元処理によって、微細なPt金属粒子となり、触媒活性が復活する、というものである。また、その触媒のリフレッシュは、触媒を搭載した自動車の運転時間や走行距離に応じて定期的に行なう、或いは触媒の下流にNOxセンサやCOセンサを設けて触媒性能を検出し、その値が基準値を超えた時に行なう、というものである。
特開2007−136419号公報 特開2007−29768号公報
On the other hand, Patent Document 2 discloses, for example, an oxidation treatment and a reduction treatment in which a catalyst formed by supporting Pt on a CeZrY composite oxide or a ZrLa composite oxide is heated in an oxidizing atmosphere containing oxygen. A method of refreshing the catalyst by applying is disclosed. That is, the grain-grown Pt becomes an oxide by the above oxidation treatment, spreads and disperses on a support such as a CeZrY composite oxide, and the dispersed Pt oxide is converted into fine Pt metal by a subsequent reduction treatment. It becomes particles and the catalytic activity is restored. The catalyst is refreshed periodically according to the driving time and mileage of the vehicle equipped with the catalyst, or a NOx sensor or CO sensor is provided downstream of the catalyst to detect the catalyst performance, and the value is the reference. This is done when the value is exceeded.
JP 2007-136419 A JP 2007-29768 A

しかし、上記特許文献2に記載のリフレッシュ方法の場合、劣化した触媒に酸化処理を行ない、続いてその触媒に還元処理を施す必要があり、触媒のリフレッシュ処理が煩雑であって手間がかかる。     However, in the refresh method described in Patent Document 2, it is necessary to subject the deteriorated catalyst to an oxidation treatment and subsequently to a reduction treatment on the catalyst, and the catalyst refresh treatment is complicated and troublesome.

そこで、本発明は、劣化した触媒を簡単にリフレッシュできるようにすることを課題とする。     Therefore, an object of the present invention is to make it possible to easily refresh a deteriorated catalyst.

本発明者は、かかる課題に対して、触媒に所定の負荷がかかったときに触媒が劣化したと判定するようにすれば、簡単なリフレッシュ処理で触媒を再生させることができることを見出し、本発明を完成させた。     The present inventor has found that the catalyst can be regenerated by a simple refresh process if it is determined that the catalyst has deteriorated when a predetermined load is applied to the catalyst. Was completed.

本発明は、エンジンの排気ガス通路に配設された排気ガス浄化用触媒のリフレッシュ方法であって、
上記触媒は、触媒金属を担持してなるCeZr系複合酸化物を含有しており、
温度が所定値Tt以上であり且つ酸素過剰の排気ガス(ガス中の還元成分を完全燃焼するのに必要な化学量論比を超える濃度の酸素を含む排気ガス)が上記触媒に流入している時間が所定時間Tm0以上になったときに、上記触媒の排気ガス浄化機能が劣化したと判定し、
上記触媒の劣化を判定したときは、酸素不足の排気ガス(ガス中の還元成分を完全燃焼するのに必要な化学量論比よりも少ない濃度の酸素を含む排気ガス)を上記触媒に所定時間Tm1以上流入させることにより、上記触媒の排気ガス浄化機能を回復させることを特徴とする。
The present invention is a method for refreshing an exhaust gas purifying catalyst disposed in an exhaust gas passage of an engine,
The catalyst contains a CeZr-based composite oxide that supports a catalytic metal,
Exhaust gas having a temperature equal to or higher than the predetermined value Tt and containing excess oxygen (exhaust gas containing oxygen at a concentration exceeding the stoichiometric ratio necessary for complete combustion of the reducing components in the gas) flows into the catalyst. When the time exceeds the predetermined time Tm0, it is determined that the exhaust gas purification function of the catalyst has deteriorated,
When the deterioration of the catalyst is determined, oxygen-deficient exhaust gas (exhaust gas containing oxygen at a concentration lower than the stoichiometric ratio necessary for complete combustion of the reducing components in the gas) is supplied to the catalyst for a predetermined time. The exhaust gas purifying function of the catalyst is recovered by allowing the catalyst to flow in at least Tm1.

すなわち、単に自動車の運転時間や走行距離が所定値を超えたことを検出し、或いはNOxセンサ等によって触媒性能の低下を検出しても、そのときの触媒の劣化状態は必ずしも同じではない。触媒がストイキ雰囲気の高温排気ガスに長時間晒されたのか、或いは酸化性雰囲気の高温排気ガスに長時間晒されたのかなど、触媒が晒された排気ガスの状態によって触媒の劣化状態は異なる。そのため、かかる運転時間等や触媒性能低下の検出を契機とする場合、触媒を確実に再生させることが難しくなる。     That is, simply detecting that the driving time or mileage of a vehicle exceeds a predetermined value, or detecting a decrease in catalyst performance by a NOx sensor or the like, does not necessarily mean that the catalyst is deteriorated at that time. Whether the catalyst has been exposed to high-temperature exhaust gas in a stoichiometric atmosphere for a long time or whether it has been exposed to high-temperature exhaust gas in an oxidizing atmosphere for a long time, the deterioration state of the catalyst differs depending on the state of the exhaust gas to which the catalyst has been exposed. For this reason, it is difficult to reliably regenerate the catalyst when triggered by such an operation time or a decrease in catalyst performance.

これに対して、本発明では、触媒金属を担持してなるCeZr系複合酸化物を含有する触媒を対象とし、且つ所定値Ttよりも高温の酸素過剰排気ガスがその触媒に所定時間Tm0以上流入したときに、当該触媒が劣化したと判定するから、酸化処理を事前に施すことなく、還元処理のみによって、すなわち、酸素不足の排気ガスを上記触媒に所定時間Tm1以上流入させることによって、当該触媒の排気ガス浄化機能を回復させることできる。     On the other hand, in the present invention, a catalyst containing a CeZr-based composite oxide supporting a catalytic metal is used, and oxygen-exhaust exhaust gas having a temperature higher than a predetermined value Tt flows into the catalyst for a predetermined time Tm0 or more. Therefore, it is determined that the catalyst has deteriorated. Therefore, without performing oxidation treatment in advance, only the reduction treatment is performed, that is, the oxygen-deficient exhaust gas is allowed to flow into the catalyst for a predetermined time Tm1 or more. The exhaust gas purification function can be recovered.

上記触媒の劣化を判定したときは、上記触媒に流入する排気ガス温度を上記所定値Ttよりも低い所定範囲に低下させることが好ましい。これにより、触媒金属粒子の粒成長を抑制することができる。     When it is determined that the catalyst has deteriorated, it is preferable that the temperature of the exhaust gas flowing into the catalyst is lowered to a predetermined range lower than the predetermined value Tt. Thereby, the grain growth of catalyst metal particles can be suppressed.

上記CeZr系複合酸化物が噴霧熱分解法により製造されたものであれば、高温の排気ガスに晒されても、その一次粒子径は小さく(中空状微粒子にした場合、15nm以下)、すなわち、その比表面積や細孔容積が比較的大きく、該複合酸化物に担持されている触媒金属の強度の凝集は生じ難い。従って、この場合の触媒の劣化は主として触媒金属の酸化によると考えられる。よって、かかる噴霧熱分解法によるCeZr系複合酸化物を採用した触媒の場合、その再生にあたっては、従来のような触媒金属を分散させるための酸化処理は特に必要ではなく、上述の還元処理によって触媒金属の酸化状態を変化させることにより、その排気ガス浄化機能を回復させることができる。     If the CeZr-based composite oxide is produced by spray pyrolysis, the primary particle size is small even when exposed to high-temperature exhaust gas (15 nm or less in the case of hollow fine particles). Its specific surface area and pore volume are relatively large, and the agglomeration of the strength of the catalytic metal supported on the composite oxide hardly occurs. Therefore, it is considered that the deterioration of the catalyst in this case is mainly due to the oxidation of the catalyst metal. Therefore, in the case of the catalyst employing the CeZr-based composite oxide by the spray pyrolysis method, in the regeneration, the conventional oxidation treatment for dispersing the catalyst metal is not necessary. The exhaust gas purification function can be recovered by changing the oxidation state of the metal.

本発明によれば、触媒金属を担持してなるCeZr系複合酸化物を含有する触媒を対象とし、且つ所定値Ttよりも高温の酸素過剰排気ガスがその触媒に所定時間Tm0以上流入したときに、当該触媒が劣化したと判定し、その判定が得られたときに、酸素不足排気ガスを上記触媒に所定時間Tm1以上流入させるようにしたから、事前に酸化処理を施すことなく、当該触媒の排気ガス浄化機能を回復させることできる。     According to the present invention, when a catalyst containing a CeZr-based composite oxide carrying a catalytic metal is targeted, and oxygen-exhaust exhaust gas having a temperature higher than a predetermined value Tt flows into the catalyst for a predetermined time Tm0 or more. Since it is determined that the catalyst has deteriorated and the determination is obtained, the oxygen-deficient exhaust gas is allowed to flow into the catalyst for a predetermined time Tm1 or more. The exhaust gas purification function can be restored.

また、触媒が劣化したと判定したとき、該触媒に流入する排気ガス温度を低下させるようにすれば、触媒金属粒子の粒成長を避けることができる。     Further, if it is determined that the catalyst has deteriorated, the temperature of the exhaust gas flowing into the catalyst is lowered, so that the growth of catalyst metal particles can be avoided.

また、噴霧熱分解法によるCeZr系複合酸化物を採用した触媒の場合、上記処理によってその排気ガス浄化機能が回復し易くなる。     Further, in the case of a catalyst that employs a CeZr-based composite oxide by spray pyrolysis, the exhaust gas purification function can be easily recovered by the above treatment.

以下、本発明の実施形態を図面に基づいて説明する。尚、以下の好ましい実施形態の説明は、本質的に例示に過ぎず、本発明、その適用物或いはその用途を制限することを意図するものではない。     Hereinafter, embodiments of the present invention will be described with reference to the drawings. It should be noted that the following description of the preferred embodiment is merely illustrative in nature, and is not intended to limit the present invention, its application, or its use.

<触媒リフレッシュ方法の概要>
図1は本発明に係る触媒リフレッシュ方法を実行するためのエンジンの排気ガス浄化装置の構成を示す。同図において、1はエンジン、2はその排気ガス通路であり、該排気ガス通路2に、触媒金属を担持してなるCeZr系複合酸化物を含有する排気ガス浄化用触媒3が設けられている。触媒3よりも上流側の排気ガス通路2には、触媒3に流入する排気ガスの温度を検出する温度検出手段4と、その排気ガスの酸素濃度(A/F)を検出する上流側酸素濃度検出手段5とが設けられている。触媒3よりも下流側の排気ガス通路2には、触媒3を通過した排気ガスの酸素濃度を検出する下流側酸素濃度検出手段6が設けられている。
<Overview of catalyst refresh method>
FIG. 1 shows the configuration of an exhaust gas purifying apparatus for an engine for executing the catalyst refreshing method according to the present invention. In the figure, reference numeral 1 denotes an engine, and 2 denotes an exhaust gas passage thereof. The exhaust gas passage 2 is provided with an exhaust gas purification catalyst 3 containing a CeZr-based composite oxide carrying a catalytic metal. . In the exhaust gas passage 2 upstream of the catalyst 3, temperature detecting means 4 for detecting the temperature of the exhaust gas flowing into the catalyst 3 and upstream oxygen concentration for detecting the oxygen concentration (A / F) of the exhaust gas. Detection means 5 is provided. In the exhaust gas passage 2 downstream of the catalyst 3, downstream oxygen concentration detection means 6 for detecting the oxygen concentration of the exhaust gas that has passed through the catalyst 3 is provided.

上記温度検出手段4及び酸素濃度検出手段5,6の検出信号はマイクロコンピュータを利用したエンジン制御手段7に与えられる。すなわち、制御手段7は、触媒3に流入する排気ガスの温度、酸素濃度及び触媒3への流入時間に基いて、触媒3が劣化しているか否かの判定を行ない、その劣化を判定したときは、エンジン制御により、触媒に流入する排気ガスの酸素濃度を変化させて触媒3の再生を図る。     Detection signals from the temperature detection means 4 and the oxygen concentration detection means 5 and 6 are given to an engine control means 7 using a microcomputer. That is, the control means 7 determines whether or not the catalyst 3 has deteriorated based on the temperature of the exhaust gas flowing into the catalyst 3, the oxygen concentration, and the inflow time to the catalyst 3. The engine 3 controls the regeneration of the catalyst 3 by changing the oxygen concentration of the exhaust gas flowing into the catalyst.

この場合、温度が所定値Tt以上であり且つ酸素過剰状態である排気ガスが触媒3に流入している時間が、所定時間Tm0以上になったときに、触媒3の排気ガス浄化機能が劣化したと判定し、酸素不足状態である排気ガスを触媒3に所定時間Tm1以上流入させることにより、また、必要に応じて、排気ガス温度を上記所定値Ttよりも低い所定範囲に低下させることにより、該触媒3の排気ガス浄化機能を回復させる。     In this case, the exhaust gas purification function of the catalyst 3 deteriorated when the time during which the exhaust gas whose temperature is equal to or higher than the predetermined value Tt and oxygen is excessive flows into the catalyst 3 becomes equal to or longer than the predetermined time Tm0. The exhaust gas in an oxygen-deficient state is allowed to flow into the catalyst 3 for a predetermined time Tm1 or more, and if necessary, the exhaust gas temperature is lowered to a predetermined range lower than the predetermined value Tt, The exhaust gas purification function of the catalyst 3 is restored.

<触媒リフレッシュのための好ましいエンジン制御>
図2は触媒3の劣化判定及び再生のためのエンジン制御フローを示す。スタート後、温度検出手段4及び酸素濃度検出手段5の検出値を読込み、ステップS1において触媒3に流入する排気ガス温度Tsが所定温度Tt以上か否かを判定する。排気ガス温度Tsが所定値Tt以上であるときはステップS2に進み、触媒3に流入する排気ガスのA/Fが所定値以上にリーン(酸素過剰の排気ガス)か否かを判定する。A/Fリーンが判定されたときはステップS3に進み、Ts≧Tt且つA/Fリーンの排気ガスが触媒3に流入した時間をタイマーでカウントし、その時間の現時点までの積算値TMが所定値Tm0を超えたか否かを判定する。これは触媒3が劣化しているか否かの判定である。
<Preferable engine control for catalyst refresh>
FIG. 2 shows an engine control flow for determining deterioration and regeneration of the catalyst 3. After the start, the detection values of the temperature detection means 4 and the oxygen concentration detection means 5 are read, and it is determined in step S1 whether or not the exhaust gas temperature Ts flowing into the catalyst 3 is equal to or higher than a predetermined temperature Tt. When the exhaust gas temperature Ts is equal to or higher than the predetermined value Tt, the routine proceeds to step S2, and it is determined whether or not the A / F of the exhaust gas flowing into the catalyst 3 is lean (oxygen excess exhaust gas) above the predetermined value. When A / F lean is determined, the process proceeds to step S3, the time when Ts ≧ Tt and the exhaust gas of A / F lean flows into the catalyst 3 is counted by a timer, and the integrated value TM up to the present time of that time is predetermined. It is determined whether or not the value Tm0 has been exceeded. This is a determination as to whether or not the catalyst 3 has deteriorated.

上記積算値TM>Tm0により触媒3の劣化を判定したときはステップS4に進み、排気ガスのA/Fを所定のリッチ状態(酸素不足の排気ガス)にするとともに、必要に応じて排気ガス温度Tsを低下させる。これは、触媒3の再生処理(還元処理)である。続くステップ5でタイマーをスタートさせ、再生処理時間TNが所定値Tm1を超えたか、つまり、再生処理が終了したか否かを判定し、該再生処理が終了するまで、A/Fリッチ化及び排気ガス温度の低下による再生処理を継続する。     When the deterioration of the catalyst 3 is determined based on the integrated value TM> Tm0, the process proceeds to step S4 to set the exhaust gas A / F to a predetermined rich state (exhaust gas lacking oxygen), and if necessary, the exhaust gas temperature. Reduce Ts. This is a regeneration process (reduction process) of the catalyst 3. In the next step 5, the timer is started to determine whether or not the regeneration processing time TN has exceeded the predetermined value Tm1, that is, whether or not the regeneration process has been completed, and A / F enrichment and exhaust are performed until the regeneration process is completed. Continue regeneration by reducing gas temperature.

上記劣化判定のための排気ガス温度Tsの所定値Ttとしては650℃程度が好ましい。このような高温の排気ガスが触媒3に流入する状態が続くと、触媒3が比較的短い時間で劣化するからである。この場合、上記積算値TMの所定値Tm0は例えば5秒に設定すればよい。但し、触媒3の劣化には温度と時間が関係し、650℃よりも低い温度(例えば500℃程度)の排気ガスであっても、触媒3に流入する時間が長くなると、触媒3の劣化を招く。従って、排気ガス温度Tsの所定値Ttを低く設定するときは、それに応じて上記積算値TMの所定値Tm0を長くすればよい。     The predetermined value Tt of the exhaust gas temperature Ts for determining the deterioration is preferably about 650 ° C. This is because if such a high-temperature exhaust gas continues to flow into the catalyst 3, the catalyst 3 deteriorates in a relatively short time. In this case, the predetermined value Tm0 of the integrated value TM may be set to 5 seconds, for example. However, the deterioration of the catalyst 3 is related to temperature and time. Even if the exhaust gas has a temperature lower than 650 ° C. (for example, about 500 ° C.), if the time for flowing into the catalyst 3 becomes long, the deterioration of the catalyst 3 is reduced. Invite. Therefore, when the predetermined value Tt of the exhaust gas temperature Ts is set low, the predetermined value Tm0 of the integrated value TM may be lengthened accordingly.

上記劣化判定のための排気ガスのA/F値は例えば17とすることが好ましい。このようなA/Fリーンの排気ガスが触媒3に流入する状態が続くと、触媒3が比較的短い時間で劣化するからである。但し、このA/Fに関しても、そのリーン度合いが低い(例えばA/F=16或いはA/F=15.5)場合でも、そのような排気ガスが触媒3に流入する時間が長くなったり、或いは排気ガス温度Tsが高いケースでは、触媒3の劣化を招く。従って、A/Fリーン度合いを低く設定するときは、それに応じて排気ガス温度Tsの所定値Ttを高めに設定し、或いは積算値TMの所定値Tm0を長くすればよい。     The A / F value of the exhaust gas for determining the deterioration is preferably set to 17, for example. This is because if the state where such exhaust gas of A / F lean flows into the catalyst 3 continues, the catalyst 3 deteriorates in a relatively short time. However, even with respect to this A / F, even when the lean degree is low (for example, A / F = 16 or A / F = 15.5), the time during which such exhaust gas flows into the catalyst 3 becomes long, Alternatively, in the case where the exhaust gas temperature Ts is high, the catalyst 3 is deteriorated. Therefore, when the A / F lean degree is set low, the predetermined value Tt of the exhaust gas temperature Ts may be set higher or the predetermined value Tm0 of the integrated value TM may be increased accordingly.

上記触媒の再生処理条件に関し、上記A/Fは13.6以上14.6以下することが好ましい。A/F≧13.6とするのは、エンジン燃費の悪化或いはエンジンの異常燃焼を避けるためであり、A/F≦14.6とするのは排気ガスを還元性雰囲気にして触媒3の再生を図るためである。より好ましいのはA/Fを14.3以上14.6以下することである。再生処理時間TNの所定値Tm1は例えば1秒以上600秒以下とすればよい。短時間では触媒3の再生が難しくなり、長時間では燃費の悪化を招く。好ましいのは、所定値Tm1を2秒以上30秒以下とすことである。     Regarding the regeneration treatment conditions for the catalyst, the A / F is preferably 13.6 or more and 14.6 or less. A / F ≧ 13.6 is for avoiding deterioration of engine fuel consumption or abnormal combustion of the engine, and A / F ≦ 14.6 is for regeneration of the catalyst 3 by making the exhaust gas a reducing atmosphere. It is for aiming at. More preferably, A / F is 14.3 or more and 14.6 or less. The predetermined value Tm1 of the reproduction processing time TN may be, for example, 1 second or more and 600 seconds or less. The regeneration of the catalyst 3 becomes difficult in a short time, and the fuel consumption is deteriorated in a long time. It is preferable that the predetermined value Tm1 is 2 seconds or more and 30 seconds or less.

上記再生処理における排気ガス温度Tsの低下は必須ではなく、劣化判定における排気ガス温度Tsの所定値Ttを高めに設定したときに、排気ガス温度Tsを低下させて触媒金属の粒成長を防止する。例えば、劣化判定における排気ガス温度Tsの所定値Ttを650℃以上に設定するときは、当該再生処理時の排気ガス温度Tsを450℃以上650℃未満になるように低下させればよい。好ましいのは、排気ガス温度Tsを500℃以上600℃以下、さらには530℃以上580℃以下にすることである。以上から明らかなように、劣化判定における排気ガス温度Tsの所定値Ttを600℃以下の低めに設定するときは、再生処理にあたっての排気ガス温度Tsの低下は必ずしも要しない。     The reduction of the exhaust gas temperature Ts in the regeneration process is not essential, and when the predetermined value Tt of the exhaust gas temperature Ts in the deterioration determination is set higher, the exhaust gas temperature Ts is lowered to prevent catalyst metal grain growth. . For example, when the predetermined value Tt of the exhaust gas temperature Ts in the deterioration determination is set to 650 ° C. or higher, the exhaust gas temperature Ts during the regeneration process may be lowered to 450 ° C. or higher and lower than 650 ° C. It is preferable to set the exhaust gas temperature Ts to 500 ° C. or more and 600 ° C. or less, and further 530 ° C. or more and 580 ° C. or less. As is clear from the above, when the predetermined value Tt of the exhaust gas temperature Ts in the deterioration determination is set to a low value of 600 ° C. or less, the exhaust gas temperature Ts is not necessarily lowered during the regeneration process.

上記再生処理にあたっては、燃料の吸気行程噴射(主噴射)後の膨張行程又は排気行程において少量の燃料をエンジンに供給する後噴射を実行することにより、或いは上記主噴射量を増量することにより、排気ガスのA/Fをリッチにすることができる。また、そのような燃料噴射制御により、エンジンの混合気のA/Fをオーバリッチ(理論空燃比よりもリッチ)にすると、燃料の潜熱により排気ガス温度の低下が図れる。上記後噴射と共に、排気ガスのA/Fが理論空燃比よりもリーンにならない程度に二次エアを供給することにより、排気ガス温度Tsを低下させるようにしてもよい。     In the regeneration process, by performing post-injection in which a small amount of fuel is supplied to the engine in the expansion stroke or exhaust stroke after fuel intake stroke injection (main injection), or by increasing the main injection amount, The A / F of the exhaust gas can be made rich. Further, if the A / F of the air-fuel mixture of the engine is overrich (richer than the theoretical air-fuel ratio) by such fuel injection control, the exhaust gas temperature can be lowered due to the latent heat of the fuel. The exhaust gas temperature Ts may be lowered by supplying the secondary air to such an extent that the exhaust gas A / F does not become leaner than the stoichiometric air-fuel ratio together with the post-injection.

<排気ガス浄化用触媒3の具体例>
排気ガス浄化用触媒3として、Pt/中空微細粒子、Pt/微細粒子及びPt/通常粒子を準備した。これらはいずれも、CeZr系複合酸化物粒子としての、Ce0.19Zr0.81(CeO:ZrO=25:75(質量比))に触媒金属としてPtを1質量%担持させたものであるが、各々の複合酸化物粒子の調製法が互いに異なる。以下、調製法を説明する。
<Specific Example of Exhaust Gas Purification Catalyst 3>
As the exhaust gas purification catalyst 3, Pt / hollow fine particles, Pt / fine particles, and Pt / normal particles were prepared. In any of these, Ce 0.19 Zr 0.81 O 2 (CeO 2 : ZrO 2 = 25: 75 (mass ratio)) as CeZr-based composite oxide particles was supported by 1 mass% of Pt as a catalyst metal. However, the preparation method of each composite oxide particle is different from each other. Hereinafter, the preparation method will be described.

−調製法−
Pt/中空微細粒子は、上記複合酸化物粒子の調製に噴霧熱分解法を採用して、これを中空状微細粒子とした。すなわち、オキシ硝酸ジルコニウム、硝酸セリウム及び硫酸マグネシウムの各所定量を水に溶解させてなる原料溶液を、空気をキャリアガスとして噴霧することにより、液滴化させて加熱炉に供給した。加熱炉の炉室温度は800℃以上1000℃以下とした。加熱炉を出た粒子をバグフィルターによって捕集し、これを水洗後、乾燥させて、当該CeZr複合酸化物の中空微細粒子を得た。
-Preparation method-
For the Pt / hollow fine particles, a spray pyrolysis method was adopted for the preparation of the composite oxide particles, and these were made into hollow fine particles. That is, a raw material solution prepared by dissolving predetermined amounts of zirconium oxynitrate, cerium nitrate and magnesium sulfate in water was sprayed as air as a carrier gas to form droplets and supplied to the heating furnace. The furnace chamber temperature of the heating furnace was set to 800 ° C. or higher and 1000 ° C. or lower. Particles exiting the heating furnace were collected by a bag filter, washed with water and dried to obtain hollow fine particles of the CeZr composite oxide.

上記中空微細粒子にPt溶液を含浸させ、200℃の温度に2時間保持する乾燥処理、及び600℃の温度に2時間保持する焼成処理(大気雰囲気)を行なうことにより、当該触媒(Pt/中空微細粒子)を得た。     The hollow fine particles are impregnated with a Pt solution, dried at a temperature of 200 ° C. for 2 hours, and subjected to a firing treatment (atmosphere) at a temperature of 600 ° C. for 2 hours, whereby the catalyst (Pt / hollow) Fine particles) were obtained.

なお、上記硫酸マグネシウムは、当該複合酸化物粒子を中空構造にするために上記原料溶液に添加したものであり、得られた中空微細粒子には残存していない。     In addition, the said magnesium sulfate is added to the said raw material solution in order to make the said composite oxide particle into a hollow structure, and does not remain | survive in the obtained hollow fine particle.

Pt/微細粒子は、上記CeZr複合酸化物粒子の調製に同じく噴霧熱分解法を採用したが、上記原料溶液には硫酸マグネシウムを添加しないようにして、上記複合酸化物粒子を中実微細粒子とした。その他は上記Pt/中空微細粒子と同じ方法によって当該触媒(Pt/微細粒子)を得た。     For the Pt / fine particles, the spray pyrolysis method was similarly used for the preparation of the CeZr composite oxide particles, but the composite oxide particles were made solid solid particles without adding magnesium sulfate to the raw material solution. did. Other than that, the catalyst (Pt / fine particles) was obtained in the same manner as the Pt / hollow fine particles.

Pt/通常粒子は、上記複合酸化物粒子の調製に共沈法を採用した。すなわち、オキシ硝酸ジルコニウムと硝酸セリウムを混合し、水を加えて室温で約1時間攪拌した。次に、この硝酸塩混合溶液とアンモニア水とを室温〜80℃で混合して中和処理を行ない、白濁した溶液を一昼夜放置し、生成したケーキを遠心分離器にかけ、十分に水洗した。この水洗したケーキを約150℃の温度で乾燥させた後、400℃の温度に5時間保持するという条件で焼成した後、粉砕して、当該CeZr複合酸化物の中実粒子を得た。そうして、その他は上記Pt/中空微細粒子と同じ方法によって当該触媒(Pt/通常粒子)を得た。     For Pt / normal particles, a coprecipitation method was used for preparing the composite oxide particles. That is, zirconium oxynitrate and cerium nitrate were mixed, water was added, and the mixture was stirred at room temperature for about 1 hour. Next, this nitrate mixed solution and aqueous ammonia were mixed at room temperature to 80 ° C. for neutralization, and the cloudy solution was allowed to stand for a whole day and night. The cake washed with water was dried at a temperature of about 150 ° C. and then fired under the condition that it was held at a temperature of 400 ° C. for 5 hours, and then pulverized to obtain solid particles of the CeZr composite oxide. Thus, the catalyst (Pt / normal particles) was obtained by the same method as the above Pt / hollow fine particles.

−触媒の一次粒子径−
上記3種類の触媒について、大気雰囲気で800℃の温度に24時間保持する熱処理(酸化)を施した後、TEM(透過型電子顕微鏡)写真を撮影した。図3はPt/中空微細粒子のTEM写真、図4はPt/微細粒子のTEM写真、図5はPt/通常粒子のTEM写真である。TEM観察の結果、各々の平均一次粒子径は、噴霧熱分解法を採用したPt/中空微細粒子が10nm以上15nm以下の範囲にあり、Pt/微細粒子が10nm以上20nm以下の範囲にあり、共沈法を採用したPt/通常粒子が15nm以上30nm以下の範囲にあった。因みに、初期品(上記熱処理前)の平均一次粒子径は、TEM観察によれば、Pt/中空微細粒子及びPt/微細粒子はいずれも5nm以上10nm以下の範囲にあり、Pt/通常粒子が10nm以上20nm以下の範囲にあった。
-Primary particle size of catalyst-
The above three kinds of catalysts were subjected to heat treatment (oxidation) held at a temperature of 800 ° C. for 24 hours in an air atmosphere, and then a TEM (transmission electron microscope) photograph was taken. 3 is a TEM photograph of Pt / hollow fine particles, FIG. 4 is a TEM photograph of Pt / fine particles, and FIG. 5 is a TEM photograph of Pt / normal particles. As a result of TEM observation, the average primary particle diameter of each of the Pt / hollow fine particles adopting the spray pyrolysis method is in the range of 10 nm to 15 nm, and the Pt / fine particles is in the range of 10 nm to 20 nm. Pt / normal particles adopting the precipitation method were in the range of 15 nm to 30 nm. Incidentally, the average primary particle size of the initial product (before the above heat treatment) is, according to TEM observation, that both Pt / hollow fine particles and Pt / fine particles are in the range of 5 nm to 10 nm, and Pt / normal particles are 10 nm. It was in the range of 20 nm or less.

すなわち、CeZr系複合酸化物を噴霧熱分解法で調製した触媒は、高温の排気ガスに晒されても、その一次粒子径は、CeZr系複合酸化物を共沈法で調製した触媒よりも小さく、20nm又は15nmよりも大きくなることが少ないことがわかる。     That is, even when a catalyst prepared by spray pyrolysis of CeZr-based composite oxide is exposed to high-temperature exhaust gas, its primary particle size is smaller than that of a catalyst prepared by co-precipitation of CeZr-based composite oxide. It can be seen that it is less likely to be larger than 20 nm or 15 nm.

−触媒の比表面積−
上記3種類の触媒各々の上記初期品及び上記熱処理(酸化)品でのBET比表面積を測定した。結果を図6に示す。初期品の比表面積は上記3種類の触媒間で大差はないが、熱処理(酸化)品では、噴霧熱分解法を採用したPt/中空微細粒子が最も大きく60m/g程度、Pt/微細粒子が次に大きく50m/g程度、共沈法を採用したPt/通常粒子は小さく20m/g弱となった。同図の「熱処理(酸化)品」の方に付記した%数値は、熱処理による比表面積の低下率である。比表面積の低下率は、Pt/中空微細粒子→Pt/微細粒子→Pt/通常粒子の順で大きくなっている。
-Specific surface area of the catalyst-
The BET specific surface area of each of the three types of catalysts in the initial product and the heat-treated (oxidized) product was measured. The results are shown in FIG. The specific surface area of the initial product is not significantly different among the above three types of catalysts, but in the heat-treated (oxidized) product, Pt / hollow fine particles employing the spray pyrolysis method are the largest, about 60 m 2 / g, Pt / fine particles However, Pt / ordinary particles employing the coprecipitation method were as small as about 50 m 2 / g, and were slightly smaller than 20 m 2 / g. The% value added to the “heat treated (oxidized) product” in the figure is the rate of decrease of the specific surface area due to the heat treatment. The reduction rate of the specific surface area increases in the order of Pt / hollow fine particles → Pt / fine particles → Pt / normal particles.

すなわち、CeZr系複合酸化物を噴霧熱分解法で調製した触媒は、高温の排気ガスに晒されたときの比表面積の低下率が小さく、40m/g以上又は50m/g以上の比表面積を有し、耐熱性が高いことがわかる。この点は上記一次粒子径が小さいことと符合している。 That is, the catalyst prepared by spray pyrolysis of CeZr-based composite oxide has a small decrease in specific surface area when exposed to high-temperature exhaust gas, and has a specific surface area of 40 m 2 / g or more or 50 m 2 / g or more. It can be seen that the heat resistance is high. This point coincides with the small primary particle size.

−触媒の細孔特性−
上記3種類の触媒各々の上記熱処理(酸化)品での細孔分布を島津製作所社製の細孔分布測定装置を用いて調べた。結果を図7に示す。共沈法を採用したPt/通常粒子では、細孔径50nm付近にシャープなピークを有する細孔分布であるが、噴霧熱分解法を採用したPt/微細粒子では、細孔径30nm付近を中心とする幅広な細孔分布になり、Pt/中空微細粒子ではさらに幅広な細孔分布になっている。各触媒の細孔分布から求めた細孔容積量は、表1に示すとおり、Pt/中空微細粒子→Pt/微細粒子→Pt/通常粒子の順で小さくなっており、CeZr系複合酸化物を噴霧熱分解法で調製した触媒では、高温の排気ガスに晒された後でも、0.3cm/g以上の細孔容積が確保され、耐熱性が高いことがわかる。この点は、上記一次粒子径が小さいこと、並びに比表面積の低下率が小さいことと符号している。なお、図7の縦軸はlog微分細孔容積を表しており、表1の細孔容積は積算細孔容積で表している。
-Pore characteristics of catalyst-
The pore distribution in the heat-treated (oxidized) product of each of the three types of catalysts was examined using a pore distribution measuring device manufactured by Shimadzu Corporation. The results are shown in FIG. In Pt / normal particles adopting the coprecipitation method, the pore distribution has a sharp peak in the vicinity of the pore diameter of 50 nm, but in Pt / fine particles adopting the spray pyrolysis method, the pore diameter is around 30 nm. The pore distribution is wide, and the Pt / hollow fine particles have a wider pore distribution. As shown in Table 1, the pore volume obtained from the pore distribution of each catalyst decreases in the order of Pt / hollow fine particles → Pt / fine particles → Pt / normal particles. It can be seen that the catalyst prepared by the spray pyrolysis method has a high heat resistance because a pore volume of 0.3 cm 3 / g or more is secured even after being exposed to high-temperature exhaust gas. This point signifies that the primary particle size is small and that the reduction rate of the specific surface area is small. In addition, the vertical axis | shaft of FIG. 7 represents the log differential pore volume, and the pore volume of Table 1 is represented by the integrated pore volume.

以上の一次粒子径、比表面積及び細孔容積の測定結果から、噴霧熱分解法を採用したPt/中空微細粒子及びPt/微細粒子は、耐熱性が高く、高温の排気ガスに晒されても、Ptの強度の凝集は生じないことがわかる。     From the above measurement results of the primary particle diameter, specific surface area and pore volume, Pt / hollow fine particles and Pt / fine particles adopting the spray pyrolysis method have high heat resistance and can be exposed to high-temperature exhaust gas. It can be seen that there is no aggregation of Pt strength.

<触媒リフレッシュの効果>
−触媒の再生処理による排気ガス浄化性能の変化−
上記3種類の触媒各々の上記熱処理(酸化)品、並びに該熱処理後に再生処理(還元)を行なった再生処理品について、COの浄化に関するライトオフ性能を調べた。この場合、上記熱処理(酸化)の大気雰囲気は酸素過剰の排気ガスに相当し、触媒は当該熱処理により劣化したとみることができる。上記再生処理は、上記熱処理(酸化)品を温度600℃の2.2%COガス(残;He)雰囲気に10分間保持する、というものである。このCOガス雰囲気は酸素不足の排気ガスに相当する。
<Effect of catalyst refresh>
-Changes in exhaust gas purification performance due to catalyst regeneration-
The light-off performance related to the purification of CO was examined for the heat treatment (oxidation) product of each of the three types of catalysts and the regeneration treatment product subjected to regeneration treatment (reduction) after the heat treatment. In this case, the atmosphere of the heat treatment (oxidation) corresponds to an exhaust gas containing excess oxygen, and it can be considered that the catalyst has deteriorated due to the heat treatment. The regeneration treatment is to hold the heat treatment (oxidation) product in a 2.2% CO gas (residue; He) atmosphere at a temperature of 600 ° C. for 10 minutes. This CO gas atmosphere corresponds to an oxygen-deficient exhaust gas.

ライトオフ性能の測定にあたっては、各触媒0.05gに、CO濃度1%、O濃度0.5%(残;He)の模擬排気ガスを96000h−1の空間速度で供給しながら、20℃/分の速度で模擬排気ガス温度を高めていった。そして、CO浄化率が50%に到達する温度(ライトオフ温度)を求めた。結果を図8に示す。 In the measurement of the light-off performance, a simulated exhaust gas having a CO concentration of 1% and an O 2 concentration of 0.5% (remaining: He) was supplied to 0.05 g of each catalyst at a space velocity of 96000 h −1 while maintaining 20 ° C. The simulated exhaust gas temperature was increased at a rate of / min. The temperature at which the CO purification rate reaches 50% (light-off temperature) was determined. The results are shown in FIG.

上記3種類の触媒のいずれも、CO浄化率50%到達温度は再生処理によって低下している。すなわち、排気ガス浄化機能が回復している。特に、CeZr複酸化物の調製に噴霧熱分解法を採用したPt/中空微細粒子及びPt/微細粒子では、当該到達温度が100℃前後も低下している。     In any of the above three types of catalysts, the temperature at which the CO purification rate reaches 50% is lowered by the regeneration treatment. That is, the exhaust gas purification function is restored. In particular, in the case of Pt / hollow fine particles and Pt / fine particles that employ the spray pyrolysis method for the preparation of CeZr double oxide, the ultimate temperature is reduced to around 100 ° C.

−触媒のPt電子状態の変化−
上記3種類の触媒各々の上記熱処理(酸化)品、並びに該熱処理後に上記再生処理を行なった再生処理品について、XPS(X線光電子分光)分析により、Ptの3d吸収のピークを測定した。
-Changes in the Pt electronic state of the catalyst-
The peak of 3d absorption of Pt was measured by XPS (X-ray photoelectron spectroscopy) analysis of the heat-treated (oxidized) product of each of the three types of catalysts and the regenerated product obtained by performing the regeneration treatment after the heat treatment.

熱処理(酸化)品の結果を図9に示し、再生処理品の結果を図10に示す。上記3種類の触媒のいずれも、上記再生処理により、Ptの酸化状態が熱処理(酸化)品に比べて還元側に変化していることがわかる。このPtの酸化状態の変化が当該触媒の排気ガス浄化機能の回復に結びついていると考えられる。     FIG. 9 shows the result of the heat-treated (oxidized) product, and FIG. 10 shows the result of the regenerated product. It can be seen that in any of the three types of catalysts, the oxidation state of Pt is changed to the reduction side as compared with the heat-treated (oxidized) product by the regeneration treatment. It is considered that this change in the oxidation state of Pt leads to the recovery of the exhaust gas purification function of the catalyst.

−触媒の酸素放出特性の変化−
上記3種類の触媒各々の上記熱処理(酸化)品、並びに該熱処理後に上記再生処理を行なった再生処理品について、酸素放出特性(CO−TPR)を調べた。すなわち、各触媒0.05gに、OとHeとの混合ガス(O;20%)を供給しながら、昇温させて600℃に10分間保持した後、室温まで冷却する前処理(酸素吸蔵処理)を行なった。しかる後、2.2%COガス(残;He)を供給しながら、20K/分の速度で昇温してゆき、各温度におけるCO量を計測した。そのCO量は触媒から放出された酸素量に対応する。
-Changes in catalyst oxygen release characteristics-
The oxygen release characteristics (CO-TPR) of the heat-treated (oxidized) product of each of the three types of catalysts and the regenerated product subjected to the regeneration treatment after the heat treatment were examined. That is, while supplying a mixed gas of O 2 and He (O 2 ; 20%) to 0.05 g of each catalyst, the temperature was raised and held at 600 ° C. for 10 minutes, and then cooled to room temperature (oxygen) Occlusion treatment). Thereafter, while supplying 2.2% CO gas (residue; He), the temperature was increased at a rate of 20 K / min, and the amount of CO 2 at each temperature was measured. The amount of CO 2 corresponds to the amount of oxygen released from the catalyst.

熱処理(酸化)品の結果を図11に示し、再生処理品の結果を図12に示す。熱処理(酸化)品の場合、酸素放出開始温度は、Pt/通常粒子では420K付近であるが、Pt/中空微細粒子及びPt/微細粒子では340Kないし350Kと低い。そうして、上記3種類の触媒のいずれも、上記再生処理により、上記熱処理(酸化)品に比べて、より低温側で酸素が放出されるように、酸素放出特性が変化している。特にPt/中空微細粒子は、その傾向が強く、420K〜560K(150℃〜290℃)において酸素放出量が多くなっている。このような低温側での酸素放出量の増大が当該触媒の排気ガス浄化機能の回復に結びついていると考えられる。     FIG. 11 shows the result of the heat-treated (oxidized) product, and FIG. 12 shows the result of the regenerated product. In the case of the heat-treated (oxidized) product, the oxygen release start temperature is around 420 K for Pt / normal particles, but is as low as 340 K to 350 K for Pt / hollow fine particles and Pt / fine particles. As a result, the oxygen release characteristics of all of the three types of catalysts are changed so that oxygen is released at a lower temperature by the regeneration process than the heat-treated (oxidized) product. In particular, Pt / hollow fine particles have a strong tendency, and the amount of released oxygen increases at 420K to 560K (150 ° C to 290 ° C). Such an increase in the amount of released oxygen on the low temperature side is considered to lead to the recovery of the exhaust gas purification function of the catalyst.

本発明に係るエンジンの排気ガス浄化装置の構成図である。It is a block diagram of the exhaust-gas purification apparatus of the engine which concerns on this invention. 本発明に係る触媒の劣化判定及び再生のためのエンジン制御のフロー図である。It is a flowchart of engine control for catalyst deterioration determination and regeneration according to the present invention. Pt/中空微細粒子触媒のTEM写真である。It is a TEM photograph of Pt / hollow fine particle catalyst. Pt/微細粒子触媒のTEM写真図である。It is a TEM photograph figure of Pt / fine particle catalyst. Pt/通常粒子触媒のTEM写真図である。It is a TEM photograph figure of Pt / normal particle catalyst. 3種類の触媒の初期品及び熱処理品のBET比表面積を示すグラフ図である。It is a graph which shows the BET specific surface area of the initial goods and heat-treated goods of three types of catalysts. 3種類の触媒の熱処理品の細孔分布を示すグラフ図である。It is a graph which shows the pore distribution of the heat processing goods of three types of catalysts. 3種類の触媒の再生処理前後のCO浄化率50%到達温度を示すグラフ図である。It is a graph which shows the CO purification rate 50% attainment temperature before and behind the regeneration process of three types of catalysts. 3種類の触媒の熱処理品のXPS分析によるPt電子状態を示すグラフ図である。It is a graph which shows the Pt electronic state by the XPS analysis of the heat processing goods of three types of catalysts. 3種類の触媒の再生処理品のXPS分析によるPt電子状態を示すグラフ図である。It is a graph which shows the Pt electronic state by the XPS analysis of the regeneration process goods of three types of catalysts. 3種類の触媒の熱処理品の酸素放出特性を示すグラフ図である。It is a graph which shows the oxygen release characteristic of the heat processing goods of three types of catalysts. 3種類の触媒の再生処理品の酸素放出特性を示すグラフ図である。It is a graph which shows the oxygen release characteristic of the reproduction | regeneration processing goods of three types of catalysts.

符号の説明Explanation of symbols

1 エンジン
2 排気ガス通路
3 排気ガス浄化用触媒
4 温度検出手段
5,6 酸素濃度検出手段
7 制御手段
DESCRIPTION OF SYMBOLS 1 Engine 2 Exhaust gas passage 3 Exhaust gas purification catalyst 4 Temperature detection means 5, 6 Oxygen concentration detection means 7 Control means

Claims (3)

エンジンの排気ガス通路に配設された排気ガス浄化用触媒のリフレッシュ方法であって、
上記触媒は、触媒金属を担持してなるCeZr系複合酸化物を含有しており、
温度が所定値Tt以上であり且つ酸素過剰の排気ガスが上記触媒に流入している時間が所定時間Tm0以上になったときに、上記触媒の排気ガス浄化機能が劣化したと判定し、
上記触媒の劣化を判定したときは、酸素不足の排気ガスを上記触媒に所定時間Tm1以上流入させることにより、上記触媒の排気ガス浄化機能を回復させることを特徴とする排気ガス浄化用触媒のリフレッシュ方法。
A method for refreshing an exhaust gas purifying catalyst disposed in an exhaust gas passage of an engine,
The catalyst contains a CeZr-based composite oxide that supports a catalytic metal,
It is determined that the exhaust gas purification function of the catalyst has deteriorated when the temperature is equal to or higher than a predetermined value Tt and the time during which oxygen-exhaust exhaust gas flows into the catalyst reaches a predetermined time Tm0;
When the deterioration of the catalyst is judged, the exhaust gas purifying catalyst is refreshed by allowing the exhaust gas having an oxygen shortage to flow into the catalyst for a predetermined time Tm1 or more to restore the exhaust gas purifying function of the catalyst. Method.
請求項1において、
上記触媒の劣化を判定したときは、上記触媒に流入する排気ガス温度を上記所定値Ttよりも低い所定範囲に低下させることを特徴とする排気ガス浄化用触媒のリフレッシュ方法。
In claim 1,
A method for refreshing an exhaust gas purifying catalyst, wherein when the deterioration of the catalyst is determined, the temperature of the exhaust gas flowing into the catalyst is lowered to a predetermined range lower than the predetermined value Tt.
請求項1又は請求項2において、
上記CeZr系複合酸化物は噴霧熱分解法により製造されたものであることを特徴とする排気ガス浄化用触媒のリフレッシュ方法。
In claim 1 or claim 2,
A method for refreshing an exhaust gas purifying catalyst, characterized in that the CeZr-based composite oxide is produced by spray pyrolysis.
JP2007193038A 2007-07-25 2007-07-25 Refreshing method of exhaust gas cleaning catalyst Pending JP2009028593A (en)

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Cited By (4)

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Publication number Priority date Publication date Assignee Title
JP2013525255A (en) * 2010-05-06 2013-06-20 ロデイア・オペラシヨン Compositions comprising zirconium, cerium and at least one other rare earth oxide and having a specific porosity, a process for preparing them, and their use in catalysis
JP2015529536A (en) * 2012-04-05 2015-10-08 ユミコア アクチェンゲゼルシャフト ウント コンパニー コマンディートゲゼルシャフト Method for removing carbon monoxide and hydrocarbons from exhaust gas of a lean burn internal combustion engine
JP2018105292A (en) * 2016-12-28 2018-07-05 トヨタ自動車株式会社 Exhaust emission control system of internal combustion engine and use method of exhaust emission purification catalyst
CN118681334A (en) * 2024-08-26 2024-09-24 中建材玻璃新材料研究院集团有限公司 A process for treating waste gas from sintering of glass-ceramics

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2013525255A (en) * 2010-05-06 2013-06-20 ロデイア・オペラシヨン Compositions comprising zirconium, cerium and at least one other rare earth oxide and having a specific porosity, a process for preparing them, and their use in catalysis
JP2015529536A (en) * 2012-04-05 2015-10-08 ユミコア アクチェンゲゼルシャフト ウント コンパニー コマンディートゲゼルシャフト Method for removing carbon monoxide and hydrocarbons from exhaust gas of a lean burn internal combustion engine
JP2018105292A (en) * 2016-12-28 2018-07-05 トヨタ自動車株式会社 Exhaust emission control system of internal combustion engine and use method of exhaust emission purification catalyst
CN108252814A (en) * 2016-12-28 2018-07-06 丰田自动车株式会社 The control method of the emission control system of internal combustion engine, the application method of exhaust gas purification catalyst and air-fuel ratio
US10537852B2 (en) 2016-12-28 2020-01-21 Toyota Jidosha Kabushiki Kaisha Exhaust-gas-purifying system of internal combustion engine, method of using exhaust-gas-purifying catalyst and method of controlling air-fuel ratio
CN108252814B (en) * 2016-12-28 2021-05-07 丰田自动车株式会社 Exhaust gas purification system for internal combustion engine, method for using exhaust gas purification catalyst, and method for controlling air-fuel ratio
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