Catalyst for purifying exhaust gas and manufacturing method thereof

Abstract: Catalyst manufactured by loading first noble metal on a support and loading second noble metal on a second support, preparing a coating containing both components on a carrier and impregnating the catalyst layer with a NOx adsorbing material such as alkaline (earth) metal or rare earth metal compounds. Preferably Pt on alumina/ceria and Rh on an oxide of Mn, Co, Ti or Fe are used. The NOx absorbing material is preferably Ba. Optionally the catalyst contains a second layer of Pt, Rh/zeolite after which both layers are impregnated with the NOx adsorbing compound.

Description: The present invention relates to a catalyst for purifying exhaust gas and manufacturing method thereof. Conventional three-way catalysts are not always sufficient to lower a level of NOx in the exhaust and thereby to purify the exhaust gas because of high oxygen concentration of the exhaust gas while an engine operates at lean-bum conditions. Japanese Unexamined Patent Publication No. 9 - 38493 discloses a catalyst effective to purify NOx in a high oxygen concentration exhaust gas which comprises a catalytic noble metal and a NOx absorbent carried in order on a support material of a composite oxide made of alumina combined with lanthanum (La) and/or cobalt (Co). It is said in the publication that while, at high temperatures, alumina reacts with the NOx absorbent to cause a reduction in its own specific surface area and clogging of its pores, and further to cause sintering of the catalytic noble metal, the composite oxide is prevented from thermal deterioration. In a manufacturing method of the catalyst, after forming a layer of cobalt alumina complex oxide by impregnating cobalt (Co) into an alumina layer carried on a support and then drying and calcining it, the cobalt-alumina complex oxide layer is impregnated with platinum (Pt) and dried, and is subsequently impregnated with rhodium (Rh), then dried and calcined. Finally, the catalyst is completed by impregnating barium (Ba) into the cobalt-alumina composite oxide layer then drying and calcining it. In the catalyst made by the above method, platinum (Pt) and rhodium (Rh) carried on a single particle of cobalt-alumina composite oxide stay close to or overlap each other. The catalyst in which two different kinds of noble metal particles are carried on a single particle of support material tends to make an alloy thereof when it is exposed to a high temperature gas, which leads to aggravation of catalytic performance. The US-A-4 727 052 teaches a method of making a catalyst composition comprising an activated alumina coating stabilized against thermal degradation includes applying a coating of alumina having one or more platinum group metal catalytic components dispersed thereon onto a carrier substrate and calcining the coating. A slurry of a mixture of Rh carrying alumina and Pt carrying ceria is prepared and coated on a substrate, and the slurry is adjusted so as to have a Rh content made less than a Pt content. In the EP-A-0 507 590, an exhaust gas purifying catalyst is disclosed for simultaneous removal of carbon monoxide, hydrocarbons and nitrogen oxides from an exhaust gas from an internal-combustion engine. The catalyst carries, on a monolithic carrier, a mixture comprising a catalytically active component comprising palladium, an alkaine earth metal oxide cerium oxide, zirconium oxide and an activated alumina. As seen from example 7, there is a slurry of a mixture of a powder of CeOi-ZrOi, titanium oxide, alumina, silica, paradium and barium. The US-A-5 490 977 discloses a catalyst composition suitable for three-way conversion of internal combustion engine, e.g. automobile gasoline engine, exhaust gases which includes a catalytic material disposed in on a carrier. The catalytic material contains a co-formed (e. g.., co-precipitated) rare earth oxide-zirconia support on which a first rhodium catalytic component is dispersed, and an alumina support having a platinum catalytic component dispersed thereon. In this catalyst, rear earth metals carry a noble metal. The EP-A-0 822 005 discloses a catalyst purifying exhaust gases, which comprises (a) iridium, (b) at least one element selected from the group consisting of alkali metals and alkaline earth metals, and (c) at least one element selected from the group consisting of elements of the Group IIIB in the Periodic Table, elements of the Group IVA in the Periodic Table (except carbon element), and iron family elements, as carried by an oxide of at least one element selected from titanium family elements. Example 1 of this reference teaches to impregnate a powder of titanium oxide with a mixture of a solution containing of Ir, K or Ba, and Nd. The DE 197 42 705 A discloses a catalyst comprising a base catalyst layer comprising Pt and B carried by AlO2 and an upper catalyst layer containing Pt and Rh carried by Zeolith. The Pt and the Rh in the upper catalyst layer activate NOx and HC, and the Ba in the base catalyst layer disperse the Pt. The catalyst comprises an inner layer having Pt and Ba carried on alumina and ceria and an outer layer having Pt and Rh earned on zeolite. The EP-A-0 485 180 discloses a catalyst composition for purification of exhaust gas, comprises (a) high-silica zeolite having a Si/Al ratio of 40 or more which has been subjected to ion exchange with at least one metal selected from Pt, Pd, Rh, Ir and Ru, and (b) a heat-resistant oxide containing at least one metal selected from Pt, Pd, Rh, Ir and Ru. The catalyst composition is supported on a monolith carrier as a single layer or with the two components (a) and (b) as separate layers. The catalyst comprises a mixture of noble metal carrying zeolite with alumina that carries Pt and Rh and contains an alkali earth metal, and TiOa, ZrOa, or a composite oxide of them. The US-A-5 677 258 discloses an exhaust gas emission control catalyst which includes an under catalyst layer containing at least one of barium and lanthanum and an over catalyst layer containing an agent for absorbing water in a gas, at least one of the under catalyst layer and over catalyst layer containing catalytic metal. The catalyst comprises an inner layer of alumina carrying Ba and Pt and an outer layer of zeolite (crystal metal silicate). It is an object of the invention to provide an improved catalyst having a NOx absorbent capable of absorbing NOx in an exhaust gas while the exhaust gas has high oxygen concentration and desorbing NOx into an exhaust gas while the exhaust gas has low oxygen concentration. Another object of the invention is to provide an improved catalyst containing different kinds of catalytic noble metals for catalyzing reduction of NOx which provides an increased thermal stability of each catalytic noble metal to keep the capability of catalyzing reduction of NOx. Another object of the invention is to provide a manufacturing method of the improved catalyst. The foregoing objects of the invention is accomplished by a method of manufacturing an exhaust gas purifying catalyst and an exhaust gas catalyst for purifying an exhaust gas according to the independant method and apparatus claims. Advantageous embodiments of the invention are defined in the sub-claims. Specifically, the catalyst manufacturing method comprising the steps of forming a powdered first catalyst having the first noble metal carried on a support material but not containing the second noble metal, forming a powdered second catalyst having the second noble metal carried on a support material but not containing the first noble metal, mixing the powdered first catalyst with the powdered second catalyst to produce a mixture, and impregnating a solution of NOx absorbent into the mixture to carry the NOx absorbent on the support materials. The catalyst manufactured by the above method has the first noble metal and the second noble metal on separate support materials, either same or different kinds, which prevents the two noble metals from forming an alloy when the catalyst is exposed to high temperatures. Thus each noble metal cooperates with the NOx absorbent to catalyze reduction of NOx, thereby purifying the exhaust gas. Furthermore, even when these noble metals cooperate with each other to function as a catalyst, they exhibit sufficiently their own functions. Furthermore, it is a matter of importance of the method in which NOx absorbent is not separately supported by the catalytic materials but impregnated in the mixture that the NOx adsorbent is partly supported by the support materials such that a particle of the NOx absorbent is jointly supported by both of a particle of the support material bearing the first noble metal and a particle of the support material bearing the second noble metal, and by both first and second noble metal particles as well. Accordingly, each of the first and second noble metals on a same NOx absorbent particle cooperates with the NOx absorbent particle to help the catalyst to lower the level of NOx in the exhaust gas with an effect of causing the catalyst to easily increase its NOx purification efficiency. In particular, in the case where the first and second noble metals play different NOx purifying actions, both first and second noble metal particles achieve their roles on a same NOx absorbent particle, which is advantageous to NOx purification through the mediation of NOx absorbent. Further, the second noble metal makes up a reduction in NOx purification efficiency due to sintering of the first noble metal. An exhaust gas purifying catalyst is obtained by coating the catalyst on a substrate to form a catalyst layer there on. The catalyst layer has a mixture of the support material bearing the first noble metal and the NOx absorbent but not containing the second noble metal and the support material bearing the second noble metal and the NOx absorbent but not containing the first noble metal. In the mixture, a part of the NOx absorbent is jointly supported by both support materials bearing the first and second noble metals, respectively. As the support material for the first noble metal and/or the second noble metal, aluminum oxide (Al 2 O 3 ), ceria (CeO 2 ) or at least one of oxides of manganese (Mn), cobalt (Co), titanium (Ti) and iron (Fe) may be used. The first and second noble metals are carried separately on support materials which may be either of the same kind or of different kinds. The exhaust gas purifying catalyst keeps high NOx purification efficiency even after it has been exposed to a high temperature exhaust gas. Carrying the first and second noble metals on different kinds of support materials separately provides improved catalytic performance. Generally, it can be said that the thermal resistance of a catalyst depends on the thermal stability of support material of the catalyst and that the support material having high thermal stability usually has small specific surface area. It also can be said that, in the case of using two different kinds of noble metals, the amount of one noble metal can often be smaller than that of the other. In this case, a reduction in catalytic performance of the catalyst due to thermal deterioration is prevented by bearing the first noble metal on the first support material with a greater specific surface area whose first noble metal content per unit mass of the support material may be high and bearing the second noble metal on the second support material with a smaller specific surface but with a high thermal stability whose noble metal content may be low. This is because the required amount of the second noble metal is kept even if the first noble metal on the first support material is partly lost or buried in the first support material due to sintering of the first support material. Bearing the second noble metal which may be small in amount on a support material having a large specific area but a low thermal resistance together with the first noble metal prevents significant aggravation of catalytic performance due to a reduction in the amount of the second noble metal caused through sintering of the support material. It was found by the inventor of this invention, for example, that Pt had high NOx purification efficiency at high oxygen concentration of the exhaust gas and showed a tendency to lower its Nox purification efficiency at low oxygen concentration of the exhaust gas and that using a small amount of Rh together with Pt was effective on restraining lowering the NOx purification efficiency. From the fact, it was concluded that an improved catalyst could be obtained by bearing Pt as the first noble metal on the first support material having a large specific surface area and Rh as the second noble metal which may be small in amount on the second support material with a small specific surface area but with high thermal stability. In the catalyst, when the oxygen concentration of the exhaust gas is high, which indicates that the fuel mixture is lean, NO in the exhaust gas is oxidized to NO 2 by means of Pt to become easily adsorbed to the NOx adsorbent. When the oxygen concentration of the exhaust gas is lowered or, in other words, when a stoichiometric air-to-fuel ratio or an air-fuel ratio smaller than the stoichiometric air-to-fuel ratio is provided, Pt and Rh catalyzes reduction of NOx desorbed from the NOx absorbent. In this catalyzing mechanism, it is considered that Pt has NOx purification efficiency for low oxygen concentration of the exhaust gas higher than Rh. Accordingly, in the catalyst which contains a NOx absorbent particle jointly supported by both Pr bearing support material particle and Rh bearing support material particle, when the NOx oxidized by Pt and adsorbed by the NOx adsorbent while the oxygen concentration of the exhaust gas is high is desorbed, the NOx is reduced and purified mainly by Rh with high efficiency. Either Al 2 O 3 or CeO 2 , alone or in combination, may be used for the first support material. On the other hand, at least one kind of metal oxide selected from the group including oxides of Mn, Co, Ti and Fe is suitably used as the second support material. Mn and Co among them have higher performance for NOx purification than the remaining ones. As for Al 2 O 3 , γ-alumina is recommended. CeO 2 capable of absorbing oxygen (O 2 storage effect) is helpful to make the catalyst function as a three-way catalyst so as to purify hydrocarbons (HC) and carbon monoxide (CO) as well as NOx while the engine is operated with around a stoichiometric air-to-fuel ratio (λ =1). Oxides of a metal such as Mn is helpful not only to prevent the first support material from sintering by means of its high thermal stability but also to increase the NOx absorption capability of NOx absorbent by means of its function of converting NO in the exhaust gas into NO 2 . In the step of impregnating the mixture with a solution of NOx absorbent, it is preferred to impregnate the mixture with a solution of the first noble metal as well to bear the first noble metal additionally on the support material. That is, the first noble metal is partly supported through impregnation on the support material with the remaining part of the first noble metal pre-supported thereon. This provides an increase in thermal resistance of the catalyst and improves its NOx purification efficiency while the catalyst is still fresh or when the air-to-fuel ratio is stoichiometric. The increase in thermal resistance is provided by improved dispersion of the first noble metal partly pre-supported by the support material with an effect of preventing sintering of the first noble metal itself and sintering between the first and second noble metals while the catalyst is exposed to a high temperature exhaust gas. The improvement of NOx purification efficiency is provided by significantly enhanced cooperation the NOx absorbent with the first and second noble metals due to close disposition of the remaining part of the first noble metal as well as the NOx absorbent to the second noble metal. At least one of metals selected from the group including alkaline metals such as sodium (Na), alkali earth metals such as barium (Ba) and strontium ( Sr ) and rare earth metals such as lanthanum (La) is suitably used as the NOx absorbent. Especially Ba has an excellent capability of NOx absorption. It was also found by the inventor of this application that a double layered catalyst comprising an inner catalyst layer formed on a substrate which contained a NOx absorbent and a catalytic noble metal for catalyzing reduction of NOx and an outer catalyst layer formed over the inner zeolite layer with a noble metal borne thereon provided improved the performance of NOx purification of the catalyst. A manufacturing method of the double layered catalyst includes the steps of preparing a powdered first catalyst having Pt carried on a mixture of Al 2 O 3 and CeO 2 , preparing a powdered second catalyst having Rh carried on a metal oxide of at least one kind of metal selected from the group including Mn, Co, Ti and Fe, preparing a powdered third catalyst having Pt and Rh carried on zeolite, forming an inner layer of a mixture of the powdered first and second catalysts on a substrate, forming an outer layer of the powdered third catalyst over the inner layer; and then impregnating a solution of NOx absorbent, which comprises at least one kind of metal selected from the group consisting of alkaline metals , alkali earth metals and rare earth metals, into the inner and outer layers to have the NOx absorbent carried on the inner and outer layers. Impregnating a mixture of a NOx absorbent solution and a noble metal solution into the inner and outer layers may be made for improved dispersion of the NOx absorbent and the noble metal. The exhaust gas purifying catalyst made by the above method has double layers including the inner and outer catalyst layers formed on a substrate. The inner catalyst layer comprises a mixture of a catalytic component containing Pt and NOx absorbent carried on a mixture of Al 2 O 3 and CeO 2 , but not containing Rh and a catalytic component containing Rh and NOx absorbent carried on a metal oxide of at least one kind of metal selected from the group including Mn, Co, Ti and Fe but not containing Pt. The outer catalyst layer comprises a catalytic component containing PT, Rh and NOx absorbent carried on zeolite. In the double layered catalyst, on top of the effect as set forth that the catalyst containing Pt and Rh separately supported by Al 2 O 3 and a metal oxide such as Mn in the inner catalyst layer cause the catalyst to work with high NOx purification efficiency even after exposure to high temperature exhaaust gases, the noble metal carried on zeolite in the outer catalyst layer activates NOx and HC in the exhaust gas and in consequence improves the NOx purifying efficiency. Specifically, NO in the exhaust gas is converted to NO 2 to become easier to be absorbed by the NOx absorbent and HC becomes energetically reactive due to partial oxidization and cracking. The activated HC promotes reducing reaction of NOx. As apparent from the above explanation, since the effectiveness of using a metal oxide such as Mn as the support material for the second noble metal is considered to come from converting NO in the exhaust gas to NO 2 , it is understood that the exhaust gas purifying catalyst having a catalytic layer formed on a substrate which comprises a mixture of the powdered catalyst containing the first noble metal bome by the support material such as Al 2 O 3 but not containing the second noble metal and the powdered catalyst containing the second noble metal and NOx absorbent borne by a metal oxide as a support material capable of oxidizing NO to NO 2 but not containing the first noble metal is effective to catalyze reduction of NOx in the high oxygen concentration exhaust gas with high efficiency even after exposed to high temperatures. As described above, the catalyst according to the invention prevents the noble metals from forming an alloy due to exposure to high temperatures and causes the noble metals to catalyze reduction of NOx through cooperation with the NOx adsorbent. Because the NOx adsorbent is partly supported by the support materials such that the NOx adsorbent particle is jointly supported by both of a particle of the support material bearing the first noble metal and a particle of the support material bearing the second noble metal, and by both first and second noble metal particles as well, the first and second noble metals respectively cooperate with the NOx absorbent on each NOx adsorbent particle, so as to contribute to purification of NOx in the exhaust gas with an effect of causing the catalyst to easily increase its NOx purification efficiency. When using different kinds of support materials for the first and second noble metals, it is easy to make the best use of advantages of the respective support materials for improving the thermal resistance and an increase in NOx purification efficiency of the catalyst by bearing noble metals suitable for the support materials, respectively, on the respective support materials. For example, by bearing Pt which is required to be relatively large in amount on Al 2 O 3 and bearing Rh which may be relatively small in amount on a metal oxide such as Mn, the performance of the NOx adsorbent is improved by the metal oxide with keeping improved dispersion of Pt and Rh. Furthermore, since the metal oxide such as Mn does not bear on sintering, the thermal stability of Rh borne by the metal oxide is improved, so as to contribute to purification of NOx in the exhaust gas with an effect of causing the catalyst to easily increase its NOx purification efficiency. BRIEF DESCRIPTION OF THE DRAWINGS The above and other objects and features of the invention will be apparent from the following description of embodiments thereof when considering in conjunction with the accompanying drawings, in which: Figure 1 is a fragmentary sectional view of a catalyst in accordance with an embodiment of the invention; Figure 2 is a graph of NOx purification efficiency of sample catalysts EX-I-EX-IV of the invention and a comparative catalyst CX-I; and Figure 3 is a graph of NOx purification efficiency of sample catalysts EX-IX-EX-X of the invention and comparative catalysts CX-II - CX-IV. DETAILED DESCRIPTION OF THE EMBODIMENTS OF THE INVENTION Figure 1 shows an exhaust gas purifying catalyst C in accordance with an embodiment of the invention. The catalyst C is placed in an exhaust line (not shown) connected to a lean-bum engine for an automobile to lower emission levels of HC, CO and NOx in the exhaust gas from the engine while operating with a stoichiometric air-to-fuel ratio and further to effectively lower an emission level of NOx in the exhaust gas from the engine while operating under lean bum conditions. That is, the catalyst C has a lean NOx purification effect. Under the lean-bum condition, the oxygen concentration of an exhaust gas is about 4 or 5 to 20 % and the air-to-fuel ratio is 18 or higher. The catalyst C comprises a catalyst inner layer 2 formed on a honeycomb support 1 made of cordierite and a catalyst outer layer 3 formed over the catalyst inner layer 2. The catalyst inner layer 2 comprises a mixture of a catalytic component containing a first noble metal such as Pt and NOx adsorbent bome by a first support material, e.g. a mixture of Al 2 O 3 and CeO 2 and a catalytic component containing a second noble metal such as Rh and NOx adsorbent borne by a second support material, e.g. at least one kind of metal oxide selected from the group including Mn, Co, Ti and Fe. The first support material does not bear any second noble metal, and the second support material does not bear any first noble metal. The NOx adsorbent is partly supported by the support materials such that a particle of the NOx absorbent is jointly supported by both of a particle of the first support material and a particle of the second support material, and by both first and second noble metal particles as well. The catalyst outer layer 3 comprises a catalytic component containing noble metals such as Pt and Rh and NOx adsorbent borne by a third support material, e.g. zeolite. A noble metal such as iridium (Ir) and palladium (Pd) may also be bome together with the previously mentioned noble metals by each support material. Although Ba is uisually used as the NOx absorbent, any one of, or any combination of two of, alkali earth metals, alkaline metals and rare earth metals may be used in place of Ba. As the cerium component, ceria is used as CeO 2 and a composite oxide of cerium and zirconium may be used to have high thermal resistance. Each of the catalyst inner layer 2 and the catalyst outer layer 3 contains impurities less than 1 %. The exhaust gas purifying catalyst C is manufactured by the following processes. A powdered first catalyst is formed by bearing the first noble metal on the first support material through, for example, a drying-solidifying process. A powdered second catalyst is formed by bearing the second noble metal on the second support material through a drying-solidifying process. A powdered third catalyst is formed by bearing the third noble metal on the third support material. The powdered first and second catalysts and binder are mixed with water all together to form a slurry. The mixture slurry is wash-coated on the honeycomb member 1 and dried and calcined to form an inner coating layer. The powdered third catalyst and binder are mixed with water all together to form a slurry. The mixture slurry is wash-coated over the inner coating layer on the honeycomb member 1 to form an outer coating layer and then dried and calcined. Subsequently, the inner and outer coating layers are impregnated with a solution of NOx absorbent to bear the NOx absorbent thereon and then dried and calcined. In order to evaluate the performance of the catalysts in accordance with various examples of the invention, exemplified sample catalysts (EX) of the invention and a comparative catalyst (CX) were prepared for evaluation. Example I A Pt-contained powdered catalyst (a powdered first catalyst) was prepared by the following process. A mixture of γ-alumina and a CeO 2 - ZrO 2 composite oxide at a weight ratio of 1 : 1 was prepared and was further mixed with a Pt-dinitro-diamine solution to provide a slurry. The mixture slurry was comprised of the mixture and Pt with a weight ratio of 150 : 1. The Pt-contained powdered catalyst was prepared by spraying and drying the mixture slurry and then further drying and calcining it. In this instance, the Pt-contained powdered catalyst was dried for one hour at 100 to 200 C and calcined for two hours at 500 to 600°C. These drying and calcining conditions were also applied to other powdered catalysts of the catalyst EX-I and powdered catalysts of EX-II through EX-IIV and the comparative catalyst CX which will be described later. A Rh-contained powdered catalyst (a powdered second catalyst) was prepared by the following process. A mixture of MnO 2 and a rhodium nitrate solution was prepared as a slurry containing MnO 2 and Rh at a weight ratio of 120 : 1. A Rh-contained powdered catalyst was prepared by spraying and drying the mixture slurry and then further drying and calcining it. A Pt and Rh-contained/MFI powdered catalyst (a powdered third catalyst) was prepared by the following process. A Pt-dinitro-diamine solution and a rhodium nitrate solution were mixed to prepare a mixed solution containing Pt and Rh at a weight ratio of 75 : 1. MFI type zeolite (SiO 2 /Al 2 O 3 = 80) was added to the mixed solution to provide a mixture slurry. A Pt - Rh contained/MFI powdered catalyst was prepared by spraying and drying the mixture slurry and then further drying and calcining it. The Pt-contained powdered catalyst, the Rh-contained powdered catalyst and alumina binder were mixed all together at a weight ratio of 50 : 2 : 5 to provide a catalyst mixture. Ion-exchanged water was added to the catalyst mixture to provide a catalyst mixture slurry. A honeycomb substrate 1, which had a weight of 420 gram per liter (g/L), was dipped in the catalyst mixture slurry, and then withdrawn and dried after blowing off an excess of the catalyst mixture slurry and further calcined to form an inner coating layer as an catalyst inner layer 2 on the honeycomb substrate 1. In this instance, the wash-coating was controlled such that the coated and dried catalyst mixture was 342 gram per liter of the honeycomb substrate 1 (342 g/L). Thereafter, the Pt and Rh-contained/MFI powdered catalyst and alumina binder were mixed together at a weight ratio of 5 : 1 to provide a catalyst mixture. Ion-exchanged water was added to the catalyst mixture to provide a catalyst mixture slurry. The catalyst mixture slurry was wash-coated over the inner coating layer on the honeycomb substrate 1, and then dried and calcined to form an outer coating layer as a catalyst outer layer 3. The wash-coating was controlled such that the coated and dried catalyst mixture was 24 g/L. Finally, the catalyst inner and outer layers were impregnated with a barium acetate solution such that they contained 30 g/L Ba, and then dried and cacined to complete a sample catalyst EX-I. As summarized in Table I, the sample catalyst EX-I is featured by that Pt and Rh were separately carried on different support materials in the catalyst inner layer and a manganese oxide was used as the support material for Rh. The catalyst inner layer comprises 150 g/L γ-alumina, 150 g/L CeO 2 -ZrO 2 composite oxide and 12 g/L MnO 2 L as support materials, 30 g/L binder, and 2 g/L Pt and 0.1 g/L Rh as noble metals. The catalyst outer layer comprises 20 g/L MFI as a support material, 4 g/L binder, and 0.5 g/L Pt and 0.006 g/L Rh as noble metals. A total amount of 30 g/L Ba was carried as a NOx absorbent on both catalyst inner and outer layers. Example II A sample catalyst EX-II was similar to the sample catalyst EX-I excepting that MnO 2 was replaced with Co 2 O 3 for bearing Rh as summarized in Table I. Example III A sample catalyst EX-III was prepared by the following process. A mixture of γ-alumina, CeO 2 -ZrO 2 composite oxide and MnO 2 at a weight ratio of 25 : 25 : 2 was prepared. The mixture was further mixed with a Pt-dinitro-diamine solution to prepare a catalyst mixture slurry such that the catalyst mixture was comprised of the mixture and Pt with a weight ratio of 75 : 1 and was finished to provide a Pt-contained powdered catalyst as a powered first catalyst through the same process as that of the sample catalyst EX-I. Separately, a mixture of γ-alumina, CeO 2 -ZrO 2 composite oxide and MnO 2 at a weight ratio of 25 : 25 : 2 was prepared. The mixture was further mixed with a rhodium nitrate solution to provide a mixture slurry such that the mixture slurry was comprised of the mixture and Rh with a weight ratio of 1500 : 1 and finished to provide a Rh-contained powdered catalyst as a powdered second catalyst through the same process as that of the sample catalyst EX-I. A Pt and Rh-contained/MFI powdered catalyst was provided as a powdered third catalyst through the same process as that of the sample catalyst EX-I. The Pt-contained powdered catalyst, the Rh-contained powdered catalyst and alumina binder were mixed all together at a weight ratio of 5 : 5 : 1 to provide a catalyst mixture. Ion-exchanged water was added to the catalyst mixture to prepare s catalyst mixture a slurry. Through the wash-coating applied to the sample catalyst EX-I, an inner coating layer was formed as a catalyst inner layer 2 on a honeycomb substrate 1. The wash-coating was controlled such that the coated and dried catalyst mixture was 330 g/L. The same coating layer as those of the previous sample catalysts EX-I and EXII was formed as a catalyst outer layer 3 over the catalyst inner layer 2 such that coated and dried catalyst mixture was 24 g/L. Thereafter, the catalyst inner and outer layers 2 and 3 were impregnated with Ba such that they contained 30 g/L Ba to complete a sample catalyst EX-lll. As summarized in Table I, the sample catalyst EX-III differs from sample catalyst EX-I in that the support material bearing Rh in the catalyst inner layer 2 was not manganese oxide but included the same ones as used for bearing Pt and both support materials for Rh and Pt were made of a mixture of γ-alumina , CeO 2 -ZrO 2 composite oxide and MnO 2 . All other conditions were the same as for sample catalyst EX-I. Example IV A mixture γ -alumina and CeO 2 -ZrO 2 composite oxide at a weight ratio of 1 : 1 was prepared. The mixture was further mixed with a Pt-dinitro-diamine solution to provide a mixture slurry such that the mixture slurry contained the mixture and Pt with a weight ratio of 75 : 1. A Pt-contained powdered catalyst was prepared as a powdered first catalyst by drying and calcining the mixture slurry through the same process as that of sample catalyst EX-I. Separately, a mixture of γ-alumina and CeO 2 -ZrO 2 composite oxide at a weight ratio of 1 : 1 was prepared. The mixture was further mixed with a rhodium nitrate solution to provide a mixture slurry such that the mixture slurry contained the mixture and Rh metal with a weight ratio of 1500 : 1. A Rh-contained powdered catalyst was prepared as a powdered second catalyst by drying and calcining the mixture slurry through the same process as that of sample catalyst EX-I. A Pt and Rh-contained/MFI powdered catalyst was prepared as a powdered third catalyst in exactly the same process as that of sample catalyst EX-I. A mixture of the Pt-contained powdered catalyst, the Rh-contained powdered catalyst and alumina binder at a weight ratio of 5 : 5 : 1 was prepared. Ion-exchanged water was added to the mixture to provide a catalyst mixture slurry. The catalyst mixture slurry was wash-coated as a catalyst inner layer 2 on a honeycomb substrate 1 through the same process as that of sample catalyst EX-I such that the coated and dried catalyst mixture was 330 g/L. A catalyst outer layer 3 was formed through the same process as that of sample catalyst EX-I such that the coated and dried catalyst mixture was 24 g/L. The catalyst inner and outer layers 2 and 3 was subsequently impregnated with Ba to complete a sample catalyst EX-IV through the same process as sample catalyst EX-I. As summarized in Table I, the sample catalyst EX-IV differs from sample catalyst EX-I in that the support materials for Rh in the catalyst inner layer 2 did not include manganese oxide but was comprised of the same materials as used for Pt. All other conditions were the same as the sample catalyst EX-I. Comparative Catalyst CX A mixture of γ-alumina, a CeO 2 -ZrO 2 composite oxide and alumina binder at a weight ratio of 5 : 5 : 1 was prepared and added by Ion-exchanged water to provide a catalyst mixture slurry. The mixture slurry was wash-coated on a honeycomb substrate 1 and subsequently dried and calcined to form a catalyst mixture coating layer. The wash coating was controlled such that the dried catalyst mixture was 330 g/L. The catalyst mixture coating layer was further impregnated with a mixture of a Pt-dinitro-diamine solution and a rhodium nitrate solution. The catalyst mixture was prepared to contain Pt and Rh at a weight ratio of 20 : 1. The catalyst mixture coating layer which was adjusted to contain Pt and Rh 2.1 g/L in total amount was dried and calcined to from a catalyst inner layer 2. A catalyst outer layer 3 was formed over the catalyst inner layer 2 through the same process as that of each sample catalyst. The catalyst outer layer 3 was 24 g/L. The catalyst inner and outer layers 2 and 3 was impregnated with a barium acetate solution such that they bear 30 g/L Ba and then dried and cacined to complete a comparative catalyst CX. As summarized in Table I, the comparative catalyst CX differs from the sample catalysts EX-I through EX-IV according to the embodiments of the invention only in that Pt and Rh in the inner layer were not separately carried on different support materials but both Pt and Rh were carried together on the support materials which did not include manganese oxide nor cobalt oxide. Carried Amount EX-I EX-II EX-III EX-IV CX Inner Layer Catalyst MnO 2 12 g/L Used None used none None Co 2 O 3 12 g/L None Used none none None Support Materials for Pt and Rh Pt/Al 2 O 3 +CeO 2 Pt/Al 2 O 3 +CeO 2 Pt/Al 2 O 3 +CeO 2 +MnO 2 Pt/Al 2 O 3 +CeO 2 Pt, Rh/Al 2 O 3 +CeO 2 Rh/MnO 2 Rh/Co 2 O 3 Rh/Al 2 O 3 +CeO 2 +MnO 2 Rh/Al 2 O 3 +CeO 2 Evaluation tests were made by measuring NOx purification efficiency of the sample catalysts EX-I through EX-IV and comparative catalyst CX. In the evaluation test, each catalyst after heat-aging treatment in the atmosphere for 24 hours at 900 °C was mounted to a fixed-bed-flow type reactor. The catalyst was exposed to a gas simulated as an exhaust gas from the engine operating with a lean air-fuel mixture was flown through the fixed-bed-flow type reactor until showing stable NOx purification efficiency, and subsequently to a gas simulated as an exhaust gas from the engine operating with an enriched air-fuel mixture, which was different in composition from the previously applied simulated gas. At a point of time 130 second after switching again back to the simulated gas having composition corresponding to the lean charge combustion, measurement of NOx purification efficiency was made to determine the lean burn NOx purification performance of the catalyst. The temperature of the catalyst under test and the simulated gas was 350°C and the simulated gas had composition summarized in TABLE II. The space velocity of simulated gas stream was 25,000 h -1 . lean-burn condition fuel-rich condition HC (C 3 H 6 ) 4000 ppmC ← NO 250 ppm ← CO 0.15 % ← CO 2 10% ← H 2 650 ppm ← O 2 7% 0.5 % H 2 O 10% ← N 2 Balance ← The result of the evaluation tests is shown in Figure 2. The NOx purification efficiency is considered to depend upon whether Pt and Rh are separately carried on different support materials, respectively, in the catalyst inner layer or not, and the difference in NOx purification efficiency of sample catalyst EX-IV from comparative catalyst CX is considered to occur due to carrying Pt and Rh in the catalyst inner layer on different support materials. Because, in sample catalyst EX-IV, Pt and Rh are separately carried on their own suppor materials respectively unlike comparative catalyst CX, it is considered that Pt and Rh are prevented from forming an alloy during heat-aging treatment and consequently contribute to NOx purification of the catalyst after heat-aging. Sample catalysts EX-III and IV are different in whether each of the support materials for Pt and Rh in the catalyst inner layer contains a manganese oxide or not. Therefore, the difference in NOx purification efficiency between sample catalysts EX-III and EX-IV is considered to occur according to whether there is a manganese oxide in their support materials. In sample catalyst EX-III, it is considered that a manganese oxide restrains sintering of alumina while oxidizes NO to NO 2 which becomes easier to be adsorbed in NOx absorbent Ba, and consequently NOx purification efficiency of the sample catalyst EX-III after heat-aging remains kept higher than that of sample catalyst EX-IV. Sample catalysts EX-I and EX-III are different in whether Pt and Rh are carried by the same type of support materials, and in particular in whether Rh is carried by a manganese oxide as a support material. The difference in NOx purification efficiency of sample catalyst EX-I from the sample catalyst EX-III is considered to carry Rh on a manganese oxide. Since a manganese oxide is hard to be sintered, it is considered that Rh carried on the manganese oxide of sample catalyst EX-I is not buried in manganese oxide particles but remains held on the surfaces of the manganese oxide particles even after heat-aging treatment, which is always desirable for the catalyst to be effective in purifying NOx. While sample catalyst EX-II is different from sample catalyst EX-I in that it uses a cobalt oxide as a support material for Rh in place of a manganese oxide in sample catalyst EX-I, it has a NOx purification efficiency as high as sample catalyst EX-I. As a result, the cobalt oxide is considered to do almost the same work as the manganese oxide. One of cobalt compounds such as Co 3 O 4 may be used as the cobalt oxide with the same effect of sample catalyst II. In order to evaluate the catalyst of the invention with regard to stoichiometric NOx purification efficiency after heat aging treatment as well as lean NOx purification efficiency, sample catalysts EX-V and EX-IV were prepared. Sample catalyst EX-V was prepared by the same process as the sample catalyst EX-I excepting carrying a half of 2 g/L Pt on a support material of the powdered first catalyst and the remaining of Pt was inpregnated together with Ba in support materials of the first and second catalysts. Specifically, the catalyst inner and outer layers were impregnated with a mixture of a barium acetate solution and a Pt-dinitro-diamine solution and dried and calcined. Sample catalyst EX-VI was prepared by the same process as the sample catalyst EX-IV excepting carrying a half of 2 g/L Pt on a support material of the powdered first catalyst and the remaining of Pt was inpregnated together with Ba in support materials of the first and second catalysts. Specifically, the catalyst inner and outer layers were impregnated with a mixture of a barium acetate solution and a Pt-dinitro-diamine solution and dried and calcined. The same evaluation tests were made by measuring lean NOx purification efficiency as well as stoichiometric NOx purification efficiency after heat aging treatment of the sample catalysts EX-V and EX-VI together with EX-I, EX-II and comparative catalyst CX. The result is summarized in Table III. NOx Purification efficiency Lean Stoichiometric EX-I 77.5 % 70.1 % EX-II 79.8 % 70.9 % EX-V 73.1 % 75.8 % EX-VI 45 % 72.8 % CX 25.6 % 81.7 % Sample catalyst EX-V is different from Sample catalyst I in that a half amount of Pt is impregnated together with Ba. As apparent from Table III, sample catalyst EX-V shows lean NOx purification efficiency lower than sample catalysts EX-I and EX-II, it shows stoichiometric NOx purification efficiency greater the sample catalysts EX-I and EX-II. This is considered that Pt is impregnated with high dispersion in sample catalyst EX-V sufficiently to restrain sintering during heat aging and Pr and Ba particles are dispersed closely to Ba particles to cause enhanced cooperation between Pt, Rh and Ba particles. Sample catalyst EX-VI is different from sample catalyst EX-IV in that a half amount of Pt is impregnated together with Ba. Sample catalyst EX-VI shows both lean NOx purification efficiency and stoichiometric NOx purification efficiency greater the sample catalysts EX-IV. In order to evaluate the catalyst of the invention with regard to the difference of NOx purification efficiency before and after heat aging treatment, sample catalysts EX-VII and EX-VIII were prepared. Sample catalyst EX-VII was prepared by the same process as sample catalyst EX-I excepting that manganese oxide was replaced by titanium oxide (TiO 2 ). Sample catalyst EX-VIII was prepared by the same process as sample catalyst EX-I excepting that manganese oxide was replaced by iron oxide (Fe 2 O 3 ). The amount of TiO 2 or Fe 2 O 3 was the same as manganese oxide of sample oxide EX-I. The same evaluation tests were made by measuring lean NOx purification efficiency under the same conditions. As the result of the tests, sample catalyst EX-VII showed a lean NOx purification efficiency of 65.5 %, and sample catalyst EX-VIII showed a lean NOx purification efficiency of 58,8 %, which revealed that TiO 2 and Fe 2 O 3 are effective though inferior to manganese oxide and cobalt oxide. In order to evaluate the usefulness of manganese oxide and cobalt oxide as a support material, a powdered catalyst with Rh carried by Al 2 O 3 , a powdered catalyst with Rh carried by MnO 2 , and a powdered catalyst with Rh carried by Co 3 O 4 were prepared. Measurements were made to determine particle sizes of Rh before and after heat aging. The result is summarized in Table IV. comparative catalyst CX-I. The result is summarized in Table IV. Rh particle size Fresh After heat aging Rh/Al 2 O 3 Smaller than o.o5 nm 2.0 - 3.0 nm Rh/MnO 2 0.13 - 0.32 nm 0.12 - 0.18 nm Rh/Co 3 O 4 0.09 - 0.64 nm% 0.26 - 1.05 nm As apparent from Table IV, while Rh carried by Al 2 O 3 has a small particle size, it is sintered due to heat aging to increas its particle size. As compared with this, Rh carried by MnO 2 or Co 3 O 4 is almost free from sintering. Accordingly, it is understood the utilization of MnO 2 or Co 3 O 4 as a support material is accompanied by an advantage of NOx purification. Sample Catalyst EX-IX A mixture of γ-alumina, CeO 2 -ZrO 2 composite oxide, MnO 2 and aluminum binder with a weight ratio of 25 : 25 : 2 : 5 was mixed was ion exchanged water to provide a catalyst mixture slurry. The catalyst mixture slurry was wash coated as an inner layer 2 on a honeycomb substrate 1 having a weight 420 g/L. The wash coating was controlled such that the coated and dried catalyst layer had a weight of 342 g/L. The catalyst layer was dried at a temperature between 100 and 200°C for one hour and calcined at 500 and 600°C for two hours. Separately, a mixture of a Pt-dinitro-diamine solution and rhodium nitrate adjusted to contain Pt and Rh with a weight ratio of 75 : 1 was prepared. The mixture was spray dried together with MFI type zeolite (SiO 2 /Al 2 O) to provide catalyst powder which bome Pt and Rh on the zeeolitr and was adjusted to have a Pt and Rh content of 2.3 weight %. The catalyst powder and aluminum binder were mixed with a weight ratio of 5 : 1 and further mixed with ion exchanged water to provide a catalyst mixture slurry. This catalyst mixture slurry was wash coated as an outer catalyst layer 3 over the inner catalyst layer 2 and dried. The coated and dried catalyst layer was adjusted to be 24 g/L. The outer catalyst layer 3 was dried at a temperature between 100 and 200°C for one hour and calcined at 500 and 600°C for two hours. The inner and outer catalyst layers 2 and 3 was impregnated with a mixture of a Pt-dinitro-diamine solution, a rhodium nitrate solution and a barium acetate solution adjusted to contain Pt, Rh and Ba with a weight ratio of 20 : 1 : 300. The impregnated amount in weight was 32.1 g/L. The inner and outer catalyst layers 2 and 3 were further dried and calcined to provide a sample catalyst EX.IIIV. The inner catalyst layer 2 contained 150 g/L γ-alumina, 150 g/L CeO 2 -ZrO 2 composite oxide and 12 g/L MnO 2 as a support material, 30 g/L binder, and 2 g/L Pt and 0.1 g/L Rh as noble metals. The outer catalyst layer 3 contained 20 g/L MFI type zeolite as a support material, 4 g/L binder, and 0.5 g/L Pt and 0.006 g/L Rh as noble materials. The sample catalyst EX-IX contained 30 g/L Ba in total as a NOx adsorbent. Sample Catalyst EX-X A sample catalyst EX-X was prepared, which was similar to the sample catalyst IIIV excepting that MnO 2 was replaced with Co 2 O 3 . Comparative Catalyst CX-II A mixture of γ-alumina, CeO 2 -ZrO 2 composite oxide and aluminum binder with a weight ratio of 5 : 5 : 1 was prepared. The mixture was further mixed with ion exchanged water to prepare a catalyst mixture slurry. This catalyst mixture slurry was wash coated as an inner layer 2 on a honeycomb substrate 1 having a weight of 420 g/L and dried. The coated and dried inner catalyst layer 2 was adjusted to be 330 g/L. Finally, the inner catalyst layer 2 was dried at a temperature between 100 and 200°C for one hour and calcined at 500 and 600°C for two hours. The inner catalyst layer 2 was impregnated with a mixture of a Pt-dinitro-diamine solution and rhodium nitrate solution adjusted to have the Pt and Rh weight ratio of 20 : 1. The impregnated amount of the mixture was 2.1 g/L. The inner catalyst layer was further dried at a temperature between 100 and 200°C for one hour and calcined at 500 and 600°C for two hours. An outer inner layer 3 just the same as that of the sample catalyst EX.IX was formed over the inner catalyst layer 2 in the same process. The inner and outer catalyst layers 2 and 3 were impregnated with barium acetate solution. The impregnation was controlled such that the outer and inner catalyst layers 2 and 3 contained 30 g/L Ba. Comparative Catalyst CX-III An inner catalyst layer just the same as that of the comparative catalyst CX-II was formed on a honeycomb substrate 1. The coated and dried catalyst layer was adjusted to have a weight of 30 g/L. An outer catalyst layer 3 just the same as that of the sample catalyst EX-IX was formed over the inner catalyst layer 2. The coated and dried catalyst layer was adjusted to have a weight of 24 g/L. The inner and outer catalyst layers 2 and 3 were impregnated with Pt, Rh and Ba of 32.1 g/L in total weigh in the same process for the sample catalyst EX-IX. Comparative Catalyst CX-IV An inner catalyst layer 2 was formed on a honeycomb substrate 1 in the same process for the sample catalyst EX-IIIV. The coated and dried catalyst layer was adjusted to be 342 g/L. The inner catalyst layer 2 was impregnated with a mixture of a Pt-dinitro-diamine solution and rhodium nitrate solution adjusted to have the Pt and Rh weight ratio of 20 : 1 in the same process as that for the comparative catalyst CX-II. The impregnated amount of Pt and Rh was 2.1 g/L. An outer catalyst layer 3 just the same as that of the sample catalyst EX-IX was formed over the inner catalyst layer 2 in the same process for the sample catalyst XE-IX. The coated and dried catalyst layer was adjusted to be 24 g/L. The inner and outer catalyst layers 2 and 3 were impregnated with a barium acetate solution. The impregnation was controlled such that the inner and outer catalyst layers 2 and 3 contained 30 g/L Ba. The sample catalysts EX-IX and X and the comparative catalysts CX-II- CX-IV are summarized in Table V. Comparative Catalyst Sample Catalyst CX-II CX-III CX-IV EX-IX EX-X Amount of MnO 2 -- -- 12 g/L 12 g/L -- Amount of Co 2 O 3 -- -- -- -- 12 g/L Ba Impregnation After Pt, Rh With Pt, Rh After Pt, Rh With Pt, Rh With Pt, Rh Evaluation tests were made by measuring NOx purification efficiency in the same manner as described previously and the simulated gas as used in these tests had composition summarized in Table II. The result of the evaluation tests is shown in Figure 3. The difference between comparative catalysts CX-II and CX-III is only whether Ba is impregnated after Pt and Rh or together with PT and RH. The NOx purification efficiency difference (15.5 %) between the two is considered to result from impregnation of Ba together with PT and Rh. The difference between comparative catalysts CX-II and CX-IV is only whether a manganese oxide is contained or not. The NOx purification efficiency difference between the two is considered to be an effect of a manganese oxide additive. The sample catalyst EX-IX that contains a manganese oxide and is impregnated with Ba together with Pt and Rh shows an NOx purification efficiency greater than the comparative catalysts CX-III and CX-IV and, in particular, significantly greater than comparative catalyst CX-II by 33.9 %. An increase in NOx purification efficiency is 15.5 % resulting from the addition of a manganese oxide (comparative catalyst CX-III) and an increase in NOx purification efficiency resulting from the impregnation of Ba together with Pt and Rh is 18,9 %. Accordingly, a total increase in NOx purification efficiency of 34. 4 % is expected for a catalyst that contains a manganese oxide and impregnated with Ba together with Pt and Rh. The sample catalyst EX-IX shows a NOx purification efficiency which is comparable with the total increase due to a manganese oxide additive and simultaneous impregnation of Ba, Pt and Rh. Generally, a catalyst shows saturation of an increase in NOx purification efficiency as the noble metal content of the catalyst increases and becomes hard to provide an increase in NOx purification efficiency as its NOx purification efficiency becomes higher. In light of the fact, as was described above, it can be said that the combination of a manganese oxide additive and Ba impregnation together with Pt and Rh provides the mutual potentiating effect of them. Sample catalyst EX-X shows a NOx purification efficiency as high as the sample catalyst EX-IV. This indicates that a cobalt oxide additive in combination of Ba impregnation together with Pt and Rh is effective to provide an increase in NOx purification efficiency as large as a manganese oxide additive in combination with Ba impregnation together with Pt and Rh. Table VI shows the effect of metal oxide additives to NOx purification efficiency. The catalysts have the same composition excepting the kind of metal oxide. As apparent in Table VI, TiO 2 is effective to improve NOx purification efficiency. Even Fe 2 O 3 is more effective to improve NOx purification efficiency as compared with comparative catalyst CX-III. Catalyst Metal Oxide NOx Purification Efficiency (%) Catalyst - 1 MnO 2 58.5 % Catalyst- 2 Co 2 O 3 56.9 % Catalyst - 3 TiO 2 49.0 % Catalyst- 4 Fe 2 O 3 41.9 % Comparative NiO 38.0 % In light of the above evaluation, a combination of bearing NOx adsorbent suchas Ba on a support material by impregnating it together catalytic noble metals and containing a specific metal oxide as a catalytic component is advantageous to improvement of NOx purification efficiency of the catalyst after exposure to high temperature exhaust gases,. It is easily understood that the invention is useful and not limited to the double layered catalyst exemplified above but can be applied to other types of catalyst such as single layered catalysts with the same effect.

Claims: A method of manufacturing an exhaust gas purifying catalyst which contains NOx adsorbent consisting of at least one of metals selected from the group of alkaline metals, alkali earth metals and rare earth metals and operative to adsorb NOx in an exhaust gas from an engine, and further contains Pt and Rh operative to catalyze reduction of the NOx, comprising the steps of: preparing a powdered first catalyst carrying Pt on a first support material which is at least one of alumina and CeO 2 preparing a powdered second catalyst carrying Rh on a second support material which is at least one kind of metal oxide selected from the group of oxides of Mn, Co, Ti and Fe; providing a mixture of said powdered first catalyst and said powdered second catalyst; and impregnating said mixture with a solution of NOx adsorbent to carry said NOx adsorbent on said powdered first catalyst and said powdered second catalyst. The method of manufacturing an exhaust gas purifying catalyst as defined in claim 1, characterized in that said mixture is impregnated with said solution of NOx adsorbent together with a solution of Pt to carry NOx adsorbent and Pt on said first and second support materials. The method of claim 1 comprising the steps of: preparing a powdered first catalyst carrying Pt on a mixture of alumina and CeO 2 but not containing Rh; preparing a powdered second catalyst carrying Rh on at least one kind of metal oxide selected from the group including oxides of Mn, Co, Ti and Fe but not containing Pt; preparing a powdered third catalyst carrying Pt and Rh on zeolite; coating a mixture of said powdered first catalyst an said powdered second catalyst as a catalyst inner layer on said substrate, coating said powdered third catalyst over said inner layer as a catalyst outer layer on a substrate, and impregnating said catalyst inner and outer layers with a solution of NOx adsorbent to carry said NOx adsorbent in said catalyst inner and outer layers to manufacture an exhaust gas purifying double layered catalyst. An exhaust gas purifying catalyst having a catalyst layer on a substrate which contains NOx adsorbent consisting of at least one of metals selected from the group of alkaline metals, alkali earth metals and rare earth metals and operative to absorb NOx in an exhaust gas from an engine, and further contains Pt and Rh operative to catalyze reduction of the NOx, comprising a mixture of a first support material carrying Pt and said NOx adsorbent but not containing Rh; and a second support material carrying Rh and said NOx adsorbent but not containing Pt; wherein said first support material is at least on of alumina and CeO 2 and said second support material is at least one of the metal oxide selected from the group of oxides of Mn, Co, Ti and Fe. The exhaust gas purifying catalyst as defined in claim 4, characterized in that said second support material has a specific surface area greater than said first support material and a Rh content per unit mass of said second support material less than a Pt content of said first support material per unit mass of said first support material. The exhaust gas purifying catalyst of claim 4 comprising: a catalyst inner layer coated on said substrate, said catalyst inner layer comprising a mixture of said first support material carrying Pt and said NOx adsorbent but not containing Rh, and said second support material carrying Rh and said NOx adsorbent but not containing Pt; and a catalyst outer layer comprising a powdered third support material containing Pt and Rh on zeolite, coated over said inner layer as a catalyst outer layer on said substrate; wherein said first support material is a mixture of alumina and CeO 2 and said second support material is at least one kind of metal oxide selected from the group of oxides of Mn, Co, Ti and Fe, and said catalyst inner and outer layers carry said NOx adsorbent on said support materials. The exhaust gas purifying catalyst as defined in claim 6, characterized in that said second support material has a surface area greater than said first support material and a Rh content per unit mass of said second support material less than the Pt content of said first support material per unit mass of said first support material.

Inventors: IWAKUNI HIDEHARU, KYOGOKU MAKOTO, OKAMOTO KENJI, TAKAMI AKIHIDE, YAMADA HIROSHI, IWAKUNI, HIDEHARU, KYOGOKU, MAKOTO, OKAMOTO, KENJI, TAKAMI, AKIHIDE, YAMADA, HIROSHI
Applicants: MAZDA MOTOR, MAZDA MOTOR CORPORATION
Application year: 1999
Main classification: B01J37
IPC codes: B01D53, B01J23, B01J37