JP5086964B2 - Method for producing exhaust gas purifying catalyst - Google Patents
Method for producing exhaust gas purifying catalyst Download PDFInfo
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- JP5086964B2 JP5086964B2 JP2008262219A JP2008262219A JP5086964B2 JP 5086964 B2 JP5086964 B2 JP 5086964B2 JP 2008262219 A JP2008262219 A JP 2008262219A JP 2008262219 A JP2008262219 A JP 2008262219A JP 5086964 B2 JP5086964 B2 JP 5086964B2
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- 239000003054 catalyst Substances 0.000 title claims description 40
- 238000004519 manufacturing process Methods 0.000 title claims description 22
- 239000002245 particle Substances 0.000 claims description 25
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 claims description 18
- 239000002131 composite material Substances 0.000 claims description 16
- MCMNRKCIXSYSNV-UHFFFAOYSA-N ZrO2 Inorganic materials O=[Zr]=O MCMNRKCIXSYSNV-UHFFFAOYSA-N 0.000 claims description 15
- 239000007769 metal material Substances 0.000 claims description 14
- 238000000746 purification Methods 0.000 claims description 14
- 239000002002 slurry Substances 0.000 claims description 13
- 239000011230 binding agent Substances 0.000 claims description 12
- 239000007787 solid Substances 0.000 claims description 10
- 239000004034 viscosity adjusting agent Substances 0.000 claims description 10
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 10
- 229910000510 noble metal Inorganic materials 0.000 claims description 6
- 229910052763 palladium Inorganic materials 0.000 claims description 4
- 229910052697 platinum Inorganic materials 0.000 claims description 4
- 239000000203 mixture Substances 0.000 claims description 3
- 229910052703 rhodium Inorganic materials 0.000 claims description 3
- 239000004094 surface-active agent Substances 0.000 claims description 2
- 238000000034 method Methods 0.000 claims 1
- 239000007789 gas Substances 0.000 description 21
- 239000000243 solution Substances 0.000 description 11
- 239000010948 rhodium Substances 0.000 description 8
- 238000010438 heat treatment Methods 0.000 description 6
- 230000000052 comparative effect Effects 0.000 description 5
- 229910052751 metal Inorganic materials 0.000 description 5
- 239000002184 metal Substances 0.000 description 5
- 229910001220 stainless steel Inorganic materials 0.000 description 4
- 239000010935 stainless steel Substances 0.000 description 4
- MWUXSHHQAYIFBG-UHFFFAOYSA-N Nitric oxide Chemical compound O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 3
- 239000010410 layer Substances 0.000 description 3
- 238000001238 wet grinding Methods 0.000 description 3
- 239000004215 Carbon black (E152) Substances 0.000 description 2
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 2
- 239000012298 atmosphere Substances 0.000 description 2
- 238000007664 blowing Methods 0.000 description 2
- 229910002091 carbon monoxide Inorganic materials 0.000 description 2
- 238000002485 combustion reaction Methods 0.000 description 2
- 239000012153 distilled water Substances 0.000 description 2
- 229930195733 hydrocarbon Natural products 0.000 description 2
- 150000002430 hydrocarbons Chemical class 0.000 description 2
- 238000002156 mixing Methods 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 239000002344 surface layer Substances 0.000 description 2
- 229910018072 Al 2 O 3 Inorganic materials 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 239000007864 aqueous solution Substances 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 239000000919 ceramic Substances 0.000 description 1
- CETPSERCERDGAM-UHFFFAOYSA-N ceric oxide Chemical compound O=[Ce]=O CETPSERCERDGAM-UHFFFAOYSA-N 0.000 description 1
- 229910000422 cerium(IV) oxide Inorganic materials 0.000 description 1
- 239000000084 colloidal system Substances 0.000 description 1
- 238000001816 cooling Methods 0.000 description 1
- 238000007865 diluting Methods 0.000 description 1
- 238000004299 exfoliation Methods 0.000 description 1
- 239000010419 fine particle Substances 0.000 description 1
- 238000000227 grinding Methods 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 239000002736 nonionic surfactant Substances 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000008188 pellet Substances 0.000 description 1
- VSIIXMUUUJUKCM-UHFFFAOYSA-D pentacalcium;fluoride;triphosphate Chemical group [F-].[Ca+2].[Ca+2].[Ca+2].[Ca+2].[Ca+2].[O-]P([O-])([O-])=O.[O-]P([O-])([O-])=O.[O-]P([O-])([O-])=O VSIIXMUUUJUKCM-UHFFFAOYSA-D 0.000 description 1
- 238000011056 performance test Methods 0.000 description 1
- 239000010970 precious metal Substances 0.000 description 1
- SONJTKJMTWTJCT-UHFFFAOYSA-K rhodium(iii) chloride Chemical compound [Cl-].[Cl-].[Cl-].[Rh+3] SONJTKJMTWTJCT-UHFFFAOYSA-K 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 239000011232 storage material Substances 0.000 description 1
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A50/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
- Y02A50/20—Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
Landscapes
- Catalysts (AREA)
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
Description
本発明は排気ガス浄化用触媒の製造方法に関し、より詳しくは、金属材料からなる担体上に直接に設けられているが耐剥離性に優れていることにより過酷な熱条件下及び振動条件下でも長時間にわたって優れた浄化性能を発揮する排気ガス浄化用触媒、例えばオートバイ等の内燃機関排気ガス雰囲気で長時間にわたって優れた浄化性能を発揮する排気ガス浄化用触媒の製造方法に関する。 The present invention relates to a method for producing an exhaust gas purifying catalyst. More specifically, the present invention is provided directly on a support made of a metal material, but is excellent in exfoliation resistance. The present invention relates to a method for producing an exhaust gas purification catalyst that exhibits excellent purification performance for a long time, for example, an exhaust gas purification catalyst that exhibits excellent purification performance for a long time in an exhaust gas atmosphere of an internal combustion engine such as a motorcycle.
自動車等の内燃機関から排出される排気ガス中には炭化水素(HC)、一酸化炭素(CO)、窒素酸化物(NOx)等の有害成分が含まれている。それで、従来から、これら有害成分を浄化して無害化する三元触媒が用いられている。 The exhaust gas discharged from an internal combustion engine such as an automobile contains harmful components such as hydrocarbon (HC), carbon monoxide (CO), and nitrogen oxide (NO x ). Therefore, conventionally, a three-way catalyst for purifying and detoxifying these harmful components has been used.
このような三元触媒として、Pt、Pd、Rh等の貴金属とアルミナ、セリア、ジルコニア又はこれらの複合酸化物とを任意に組み合わせてセラミックス又は金属等のハニカム担体上に塗布したものがある。例えば、アパタイト型構造を有する複合酸化物を含む排ガス浄化用触媒が提案されている(例えば、特許文献1及び2参照)。 As such a three-way catalyst, there is one in which a noble metal such as Pt, Pd, or Rh and an alumina, ceria, zirconia, or a composite oxide thereof are arbitrarily combined and coated on a honeycomb carrier such as ceramics or metal. For example, an exhaust gas purification catalyst containing a composite oxide having an apatite structure has been proposed (see, for example, Patent Documents 1 and 2).
しかしながら、ステンレススチール等の金属材料からなる担体に直接に担持させると温度変化、振動等により剥離しやすいという問題がある。その対策として、例えば、微粒子の存在下で機械的エネルギーを金属担体に付与することで、金属担体の表面に耐酸化性を有する表面層を形成させて触媒層と金属担体との接触を抑え、さらに、金属担体の表面を凹凸状に形成させて表面層上に形成される触媒層との界面を凹凸状とし、両者の剥離が生じにくくすることが提案されている(例えば、特許文献3参照)。 However, when it is directly supported on a carrier made of a metal material such as stainless steel, there is a problem that it is easily peeled off due to temperature change, vibration or the like. As a countermeasure, for example, by applying mechanical energy to the metal support in the presence of fine particles, a surface layer having oxidation resistance is formed on the surface of the metal support to suppress contact between the catalyst layer and the metal support, Furthermore, it has been proposed that the surface of the metal carrier is formed in a concavo-convex shape so that the interface with the catalyst layer formed on the surface layer is formed in a concavo-convex shape so that the separation of both is less likely to occur (for example, see Patent Document 3) ).
本発明は金属材料からなる担体上に直接に設けられているが耐剥離性に優れていることにより過酷な熱条件下及び振動条件下でも長時間にわたって優れた浄化性能を発揮する排気ガス浄化用触媒の製造方法を提供することを目的とする。 Although the present invention is provided directly on a carrier made of a metal material, it has an excellent resistance to peeling, and exhibits excellent purification performance for a long time even under severe heat and vibration conditions. It aims at providing the manufacturing method of a catalyst.
本発明者等は上記目的を達成するために鋭意検討した結果、固形分の平均粒子径が特定範囲内にあり且つ粘度が特定範囲内にあるスラリーを金属材料からなる担体上に直接に塗布することにより上記目的が達成されることを見いだし、本発明を完成した。 As a result of intensive studies to achieve the above object, the present inventors directly apply a slurry having an average particle size of solid content within a specific range and a viscosity within a specific range onto a carrier made of a metal material. The present invention has been completed by finding that the above object can be achieved.
即ち、本発明の排気ガス浄化用触媒の製造方法は、耐熱性アルミナ、セリア−ジルコニア複合酸化物、バインダー、粘度調整剤及び水からなり、固形分の平均粒子径が3〜10μmであり且つ粘度が300〜2000mPa・sであるスラリーを金属材料からなる担体上に直接に塗布し、乾燥させ、焼成し、次いでこの焼成物を貴金属触媒成分含有溶液中に浸漬し、乾燥させ、焼成することを特徴とする。 That is, the method for producing an exhaust gas purifying catalyst of the present invention comprises heat-resistant alumina, ceria-zirconia composite oxide, a binder, a viscosity modifier and water, and has an average solid particle size of 3 to 10 μm and a viscosity. Is applied directly on a support made of a metal material, dried and fired, and then the fired product is immersed in a solution containing a precious metal catalyst component, dried and fired. Features.
本発明の排気ガス浄化用触媒の製造方法により得られる排気ガス浄化用触媒は、金属材料からなる担体上に直接に設けられているが耐剥離性に優れており、室温−−900℃以上の高温−−室温の熱処理サイクルを繰り返しても剥離脱落量が少ないので、過酷な熱条件下及び振動条件下でも長時間にわたって優れた浄化性能を発揮する。 The exhaust gas purifying catalyst obtained by the method for producing an exhaust gas purifying catalyst of the present invention is directly provided on a carrier made of a metal material, but has excellent peeling resistance and has a room temperature of −900 ° C. or higher. High temperature--Since the amount of peeling off is small even after repeated heat treatment cycles at room temperature, excellent purification performance is exhibited over a long period of time even under severe thermal conditions and vibration conditions.
本発明の排気ガス浄化用触媒の製造方法(以下、本発明の製造方法と記載する)で用いるスラリーは、耐熱性アルミナ、酸素貯蔵剤として機能するセリア−ジルコニア複合酸化物、バインダー、粘度調整剤及び水からなり、固形分の平均粒子径が3〜10μmであり且つ粘度が300〜2000mPa・sであるものである。 The slurry used in the method for producing an exhaust gas purifying catalyst of the present invention (hereinafter referred to as the production method of the present invention) is a heat-resistant alumina, a ceria-zirconia composite oxide that functions as an oxygen storage agent, a binder, and a viscosity modifier. And having an average particle diameter of 3 to 10 μm and a viscosity of 300 to 2000 mPa · s.
耐熱性アルミナ、セリア−ジルコニア複合酸化物、バインダー、粘度調整剤及び水からなるが、スラリー中の固形分の平均粒子径が3μm未満であるか又は10μmを超えるスラリーや、スラリーの粘度が300mPa・s未満であるか又は2000mPa・sを超えるスラリーを金属材料からなる担体上に直接に塗布すると、得られる排気ガス浄化用触媒の層の耐剥離性が改良されず、過酷な熱条件下又は振動条件下で使用すると剥離脱落が生じ、優れた浄化性能を発揮することはできない。従って、本発明の製造方法においては、耐熱性アルミナ、セリア−ジルコニア複合酸化物、バインダー、粘度調整剤及び水からなり、固形分の平均粒子径が3〜10μmであり且つ粘度が300〜2000mPa・sであるスラリーを用いる。 It consists of heat-resistant alumina, ceria-zirconia composite oxide, binder, viscosity modifier and water, but the average particle size of the solid content in the slurry is less than 3 μm or more than 10 μm, and the viscosity of the slurry is 300 mPa · If a slurry of less than s or more than 2000 mPa · s is applied directly onto a support made of a metal material, the resulting stripping resistance of the exhaust gas purifying catalyst layer is not improved, and it is under severe thermal conditions or vibrations. When used under conditions, peeling off occurs, and excellent purification performance cannot be exhibited. Therefore, in the production method of the present invention, it comprises a heat-resistant alumina, a ceria-zirconia composite oxide, a binder, a viscosity modifier, and water, and has an average particle size of 3 to 10 μm and a viscosity of 300 to 2000 mPa · The slurry which is s is used.
固形分の平均粒子径が3〜10μmであるスラリーは、平均粒子径が3〜10μmである耐熱性アルミナ粒子及び平均粒子径が3〜10μmであるセリア−ジルコニア複合酸化物粒子を用いてスラリーを調製することにより得ることができるが、耐熱性アルミナ粒子及びセリア−ジルコニア複合酸化物粒子の何れか一方又は両方の平均粒子径が10μmよりも大きいものを用い、それらとバインダー及び水からなる混合物を湿式粉砕して固形分の平均粒子径を3〜10μmとし、且つ粘度調整剤を添加して粘度を300〜2000mPa・sとすることにより得ることもできる。 The slurry having an average particle size of 3 to 10 μm is obtained by using heat-resistant alumina particles having an average particle size of 3 to 10 μm and ceria-zirconia composite oxide particles having an average particle size of 3 to 10 μm. Although it can be obtained by preparing, one having either one or both of heat-resistant alumina particles and ceria-zirconia composite oxide particles having an average particle diameter larger than 10 μm is used, and a mixture comprising them, a binder and water is used. It can also be obtained by wet-grinding to make the average particle size of solids 3 to 10 μm and adding a viscosity modifier to make the viscosity 300 to 2000 mPa · s.
本発明の製造方法においては、好ましくは、耐熱性アルミナ:セリア−ジルコニア複合酸化物:バインダーの質量比が20〜80質量%:10〜50質量%:10〜30質量%であるスラリーを用いる。この配合比から外れる場合には排気ガス浄化用触媒の性能、耐剥離性等が低下する傾向がある。 In the production method of the present invention, a slurry in which the mass ratio of heat-resistant alumina: ceria-zirconia composite oxide: binder is 20 to 80% by mass: 10 to 50% by mass: 10 to 30% by mass is preferably used. When it is out of this blending ratio, the performance of the exhaust gas purifying catalyst, peeling resistance and the like tend to be lowered.
本発明の製造方法においては、バインダーとして排気ガス浄化用触媒の製造に用いられている任意のバインダーを用いることができる。 In the production method of the present invention, any binder used for producing an exhaust gas purifying catalyst can be used as a binder.
本発明の製造方法においては、スラリーの粘度を300〜2000mPa・sに調整することができるものであればいかなる粘度調整剤も用いることができるが、粘度調整剤として界面活性剤をスラリーの0.1〜10質量%を占める量で用いることが好ましい。 In the production method of the present invention, any viscosity adjusting agent can be used as long as the viscosity of the slurry can be adjusted to 300 to 2000 mPa · s, but a surfactant is used as the viscosity adjusting agent. It is preferably used in an amount occupying 1 to 10% by mass.
本発明の製造方法においては、ステンレス等の金属材料からなる担体を用いるが、金属材料からなる担体を用いることが必須と言うよりも金属材料からなる担体を用いる場合に問題となる耐剥離性を改善することが本発明の目的である。本発明の製造方法で用いる担体の形状は、特に限定されるものではなく、一般的にはハニカム、板、ペレット、針金等の形状であり、好ましくはハニカム形状である。 In the production method of the present invention, a carrier made of a metal material such as stainless steel is used. However, it is necessary to use a carrier made of a metal material rather than using a carrier made of a metal material. It is an object of the present invention to improve. The shape of the carrier used in the production method of the present invention is not particularly limited, and is generally a shape of a honeycomb, a plate, a pellet, a wire, or the like, and preferably a honeycomb shape.
本発明の製造方法においては、上記のようなスラリーを金属材料からなる担体上に直接に塗布し、乾燥させ、例えば300〜600℃で0.5〜5時間焼成する。このことにより耐熱性アルミナ及びセリア−ジルコニア複合酸化物が金属材料からなる担体に強固に担持される。 In the production method of the present invention, the slurry as described above is directly applied onto a carrier made of a metal material, dried, and baked, for example, at 300 to 600 ° C. for 0.5 to 5 hours. As a result, the heat-resistant alumina and the ceria-zirconia composite oxide are firmly supported on the carrier made of the metal material.
本発明の製造方法においては、貴金属触媒成分としてPt、Pd、Rh等を用いることができるが、より良い触媒性能を達成するために貴金属触媒成分としてPt及びPdの少なくとも1種とRhとを(Pt+Pd)/Rhの質量比で1/1〜20/1となる量で用いることが好ましい。 In the production method of the present invention, Pt, Pd, Rh or the like can be used as the noble metal catalyst component. However, in order to achieve better catalyst performance, at least one of Pt and Pd and Rh are used as the noble metal catalyst component ( Pt + Pd) / Rh is preferably used in an amount of 1/1 to 20/1.
本発明の製造方法においては、上記の耐熱性アルミナ及びセリア−ジルコニア複合酸化物を担持している金属材料からなる担体を、貴金属触媒成分含有溶液中に浸漬し、乾燥させ、例えば300〜600℃で0.5〜5時間焼成する。 In the production method of the present invention, a support made of a metal material carrying the above heat-resistant alumina and ceria-zirconia composite oxide is immersed in a noble metal catalyst component-containing solution and dried, for example, 300 to 600 ° C. Baked for 0.5 to 5 hours.
本発明の製造方法で得られる排気ガス浄化用触媒は耐剥離性に優れていることにより過酷な熱条件下及び振動条件下でも長時間にわたって優れた浄化性能を発揮し、また、例えば1000℃で5時間熱処理した後においてもBET比表面積の低下の程度が小さいので高い排ガス浄化性能を維持することができる。 The exhaust gas purification catalyst obtained by the production method of the present invention exhibits excellent purification performance over a long period of time even under severe thermal conditions and vibration conditions due to its excellent peeling resistance. Even after the heat treatment for 5 hours, the degree of decrease in the BET specific surface area is small, so that high exhaust gas purification performance can be maintained.
以下に、実施例及び比較例に基づいて本発明を説明する。
実施例1
BET比表面積が120m2/gで平均粒子径が30μmである耐熱性アルミナ(Al2O3換算で純度95%以上)55g、BET比表面積が60m2/gで平均粒子径が10μmであるセリアージルコニア複合酸化物粒子30g、アルミナコロイドを主成分とするバインダー(アルミナ酸化物換算で)15g及び蒸留水180gをボールミルに入れ、8時間湿式粉砕し、更にノニオン表面活性剤5.0gを加えて均一に混合してウオシュコート液を得た。このウオシュコート液中の固形分の平均粒子径は8.5μmであり、粘度は700mPa・sであった。
Below, this invention is demonstrated based on an Example and a comparative example.
Example 1
55 g of heat-resistant alumina having a BET specific surface area of 120 m 2 / g and an average particle diameter of 30 μm (purity of 95% or more in terms of Al 2 O 3 ), a BET specific surface area of 60 m 2 / g and an average particle diameter of 10 μm Add 30 g of Arzirconia composite oxide particles, 15 g of binder mainly composed of alumina colloid (in terms of alumina oxide) and 180 g of distilled water into a ball mill, wet pulverize for 8 hours, and add 5.0 g of nonionic surfactant. A washcoat solution was obtained by uniformly mixing. The average particle size of the solid content in the washcoat solution was 8.5 μm, and the viscosity was 700 mPa · s.
ステンレス製ハニカム担体(300セル、容量150cc)を上記のウオシュコート液に浸漬した後、エアブローでハニカム担体のセル中の余分のウオシュコート液を除去し、乾燥させ、520℃で1時間焼成した。この処理によってステンレス製ハニカム担体に担持された無機物の量は完成触媒1リッター当たり200gであった。次に、塩化白金酸H2PtCl6溶液及び塩化ロジウム溶液を蒸留水で希釈し、この希釈した水溶液中に上記の無機物を担持したハニカム担体を浸漬した後、エアブローでセル中の余分の溶液を除去し、乾燥させ、520℃で1時間焼成して完成触媒を得た。この触媒はPtを1.5g/L、Rhを0.3g/L担持していた。 A stainless steel honeycomb carrier (300 cells, capacity 150 cc) was immersed in the above washcoat solution, and then the excess washcoat solution in the cells of the honeycomb carrier was removed by air blowing, dried, and fired at 520 ° C. for 1 hour. The amount of the inorganic substance supported on the stainless steel honeycomb carrier by this treatment was 200 g per liter of the finished catalyst. Next, after diluting the chloroplatinic acid H 2 PtCl 6 solution and the rhodium chloride solution with distilled water, and immersing the honeycomb carrier supporting the inorganic substance in the diluted aqueous solution, the excess solution in the cell is removed by air blowing. The catalyst was removed, dried, and calcined at 520 ° C. for 1 hour to obtain a finished catalyst. This catalyst supported 1.5 g / L of Pt and 0.3 g / L of Rh.
実施例2
湿式粉砕時間を8時間から16時間に変更した以外は実施例1と同様に処理した。得られたウオシュコート液中の固形分の平均粒子径は5.0μmであり、粘度は1100mPa・sであった。実施例1と同様に処理し得られた触媒はPtを1.5g/L、Rhを0.3g/L担持していた。
Example 2
The same treatment as in Example 1 was conducted except that the wet grinding time was changed from 8 hours to 16 hours. The average particle size of the solid content in the obtained washcoat solution was 5.0 μm, and the viscosity was 1100 mPa · s. The catalyst obtained by the same treatment as in Example 1 supported Pt of 1.5 g / L and Rh of 0.3 g / L.
比較例1
湿式粉砕時間を8時間から32時間に変更した以外は実施例1と同様に処理した。得られたウオシュコート液中の固形分の平均粒子径は2.5μmであり、粘度は2800mPa・sであった。実施例1と同様に処理し得られた触媒はPtを1.5g/L、Rhを0.3g/L担持していた。
Comparative Example 1
The treatment was performed in the same manner as in Example 1 except that the wet grinding time was changed from 8 hours to 32 hours. The average particle size of the solid content in the obtained washcoat solution was 2.5 μm, and the viscosity was 2800 mPa · s. The catalyst obtained by the same treatment as in Example 1 supported Pt of 1.5 g / L and Rh of 0.3 g / L.
比較例2
耐熱性アルミナ54gの代わりに耐熱処理をしていないアルミナ64gを用い、セリアージルコニア複合酸化物粒子を添加しなかった以外は実施例1と同様に処理した。得られたウオシュコート液中の固形分の平均粒子径は12.2μmであり、粘度は280mPa・sであった。実施例1と同様に処理し得られた触媒はPtを1.5g/L、Rhを0.3g/L担持していた。
Comparative Example 2
The treatment was performed in the same manner as in Example 1 except that 64 g of alumina not subjected to heat treatment was used instead of 54 g of heat resistant alumina, and ceria-zirconia composite oxide particles were not added. The average particle diameter of the solid content in the obtained washcoat liquid was 12.2 μm, and the viscosity was 280 mPa · s. The catalyst obtained by the same treatment as in Example 1 supported Pt of 1.5 g / L and Rh of 0.3 g / L.
<耐剥離性試験>
実施例1、2及び比較例1、2で得られた各々の排気ガス浄化用触媒について質量を測定した。次いで800℃に保持された電気炉中で30分間加熱した後、電気炉から取り出し、室温で30分間冷却する加熱−冷却サイクルを2回繰り返した。その後、同じ加熱条件でもう一度加熱した後、電気炉から取り出し、水中に投入して急冷し、その後、純水を張った超音波洗浄機で30分間超音波処理し、200℃で乾燥させた後再び質量を測定し、処理前後の質量の差から剥離量を計算し、耐剥離性を評価した。それらの結果を粉砕時間、平均粒子径、粘度と共に第1表に示す。
<Peel resistance test>
The mass of each exhaust gas purifying catalyst obtained in Examples 1 and 2 and Comparative Examples 1 and 2 was measured. Subsequently, after heating for 30 minutes in the electric furnace hold | maintained at 800 degreeC, it removed from the electric furnace and repeated the heating-cooling cycle which cools at room temperature for 30 minutes twice. Then, after heating again under the same heating conditions, it was taken out from the electric furnace, put into water and quenched, and then sonicated for 30 minutes with an ultrasonic cleaner filled with pure water and dried at 200 ° C. The mass was measured again, the amount of peel was calculated from the difference in mass before and after the treatment, and the peel resistance was evaluated. The results are shown in Table 1 together with the grinding time, average particle size and viscosity.
<排ガス浄化性能試験>
実施例1、2及び比較例1、2で得られた各々の排気ガス浄化用触媒を900℃で10%H2Oの空気雰囲気に保持された電気炉中で25時間加熱した後、電気炉から取り出して室温まで冷却し、次いで、反応器に取り付けて、下記第2表に示す組成のモデルガスを25L/minの速度で流通させ、昇温10℃/min、100〜400℃の温度条件下での排ガス浄化性能を評価した。その結果は下記の第3表に示す通りであった。
<Exhaust gas purification performance test>
Each exhaust gas purifying catalyst obtained in Examples 1 and 2 and Comparative Examples 1 and 2 was heated in an electric furnace maintained at 900 ° C. in an air atmosphere of 10% H 2 O for 25 hours. The sample gas was cooled to room temperature, then attached to the reactor, and a model gas having the composition shown in Table 2 below was circulated at a rate of 25 L / min, and the temperature conditions were 10 ° C / min and 100 to 400 ° C. The exhaust gas purification performance below was evaluated. The results were as shown in Table 3 below.
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JP6106458B2 (en) * | 2013-02-26 | 2017-03-29 | 本田技研工業株式会社 | Exhaust gas catalytic device |
JP5777690B2 (en) * | 2013-12-02 | 2015-09-09 | 田中貴金属工業株式会社 | Exhaust gas purification catalyst and method for producing the same |
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