JP2014113580A - Catalyst for exhaust gas purification and method for producing the same - Google Patents

Catalyst for exhaust gas purification and method for producing the same Download PDF

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JP2014113580A
JP2014113580A JP2012271595A JP2012271595A JP2014113580A JP 2014113580 A JP2014113580 A JP 2014113580A JP 2012271595 A JP2012271595 A JP 2012271595A JP 2012271595 A JP2012271595 A JP 2012271595A JP 2014113580 A JP2014113580 A JP 2014113580A
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Rui Imoto
瑠伊 井元
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Toyota Motor Corp
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Abstract

PROBLEM TO BE SOLVED: To provide an exhaust gas catalyst using an aluminum phosphate fired body and having more excellent performance, and a method for producing the same.SOLUTION: Provided is a catalyst for exhaust gas purification obtained by carrying at least one kind of platinum group metal selected from the group consisting of Pt, Rh and Pd onto a carrier of tridymite type aluminum phosphate fired body, in which the ratio x of a base content to an acid content in the carrier measured by a temperature rising desorption method satisfies 0.5%≤x≤1.0%, and also, the CO(probe gas) desorption peak temperature from the base point of the carrier is 600°C or higher.

Description

本発明は排気ガス浄化用触媒及びその製造方法に関し、さらに特に、排気ガス浄化用白金族金属および卑金属担持リン酸アルミニウム触媒、例えば、自動車等の内燃機関から排出される排ガスに含まれる有害成分を浄化する白金族金属および卑金属担持リン酸アルミニウム触媒、およびその製造方法に関する。   The present invention relates to an exhaust gas purifying catalyst and a method for producing the same, and more particularly, a platinum group metal for exhaust gas purifying and a base metal-supported aluminum phosphate catalyst, for example, harmful components contained in exhaust gas discharged from an internal combustion engine such as an automobile. The present invention relates to a platinum group metal and base metal-supported aluminum phosphate catalyst to be purified, and a method for producing the same.

近年、地球環境保護の観点から、排ガス規制が世界的に年々強化されている。
この対応策として、内燃機関においては、排ガス浄化用触媒が用いられる。この排ガス浄化用触媒において、排ガス中のハイドロカーボン(以下、HCと略記することもある。)、COおよび窒素酸化物を効率的に浄化するために、触媒成分としてPt、Pd、Rh等の白金族元素などを含め種々の触媒が使用されている。
In recent years, exhaust gas regulations have been strengthened worldwide year by year from the viewpoint of protecting the global environment.
As a countermeasure, an exhaust gas purifying catalyst is used in an internal combustion engine. In this exhaust gas purification catalyst, platinum such as Pt, Pd, and Rh is used as a catalyst component in order to efficiently purify hydrocarbons (hereinafter sometimes abbreviated as HC), CO, and nitrogen oxides in the exhaust gas. Various catalysts including group elements are used.

特許文献1は、トリディマイト型結晶構造を有し、BET比表面積が50〜150m/gである耐熱性AlPO化合物と、該AlPO化合物に担持されているPt、Pd及びRhからなる群から選択される少なくとも1種の貴金属成分とからなることを特徴とする排気ガス浄化用触媒(特許文献1の請求項1)を記載する。 Patent Document 1 includes a heat-resistant AlPO 4 compound having a tridymite crystal structure and a BET specific surface area of 50 to 150 m 2 / g, and a group consisting of Pt, Pd, and Rh supported on the AlPO 4 compound. An exhaust gas purifying catalyst (Claim 1 of Patent Document 1) characterized by comprising at least one selected precious metal component is described.

国際公開第2009−142180A1号パンフレットInternational Publication No. 2009-142180A1 Pamphlet

排ガス浄化触媒中に含まれる貴金属の量を減らすこと、ならびにエンジンから排出される熱、および燃料に含まれる硫黄成分などによって劣化しにくい排ガス浄化触媒が求められている。   There is a need for an exhaust gas purification catalyst that reduces the amount of noble metal contained in the exhaust gas purification catalyst, and that does not easily deteriorate due to heat exhausted from the engine, sulfur components contained in fuel, and the like.

しかし、従来技術に示される排ガス浄化用触媒は、硫黄被毒、すなわち燃料中の硫黄酸化物等による触媒の被毒により触媒活性が大きく低下していた。また、シンタリング、すなわち触媒の活性点である貴金属の粒成長によっても、活性が大きく低下しており、活性を高めるために改善の余地があった。   However, the catalyst for exhaust gas purification shown in the prior art has been greatly reduced in catalytic activity due to sulfur poisoning, that is, poisoning of the catalyst by sulfur oxides in fuel and the like. Also, the activity is greatly reduced by sintering, that is, noble metal grain growth which is an active point of the catalyst, and there is room for improvement in order to increase the activity.

本発明者らは、鋭意努力した結果、トリディマイト型結晶構造を有するAlPOを担体とした白金族金属を担持する触媒において、昇温脱離法により測定した担体の酸量に対する塩基量の割合を一定範囲に制御し、さらに担体塩基点のCO脱離ピーク温度を一定温度以上にすることによって、上記2つの課題を一度に解決することができ、非常に優れた結果を得ることができることを見いだした。 As a result of diligent efforts, the present inventors have determined the ratio of the amount of base to the amount of acid of the carrier measured by the temperature programmed desorption method in a catalyst supporting a platinum group metal using AlPO 4 having a tridymite crystal structure as a carrier. By controlling the CO 2 desorption peak temperature of the carrier base point to a certain temperature or more by controlling to a certain range, the above two problems can be solved at once, and very excellent results can be obtained. I found it.

本発明の態様は、以下のようである。
(1)トリディマイト型リン酸アルミニウム焼成体の担体上に、Pt、Rh、Pdからなる群から選択される少なくとも1種の白金族金属を担持してなる、排ガス浄化用触媒であって、昇温脱離法により測定した前記担体の酸量に対する塩基量の割合xが、0.5%≦x≦1.0%、かつ前記担体の塩基点からのCO(プローブガス)脱離ピーク温度が600℃以上である、排ガス浄化用触媒。
(2)前記白金族金属がPdである、(1)に記載の排ガス浄化用触媒。
(3)pHが3.5〜4.5になるように調整した水溶液から得たリン酸アルミニウムを1000℃〜1200℃の温度で2時間以上焼成してリン酸アルミニウム焼成体を得る工程と、
前記リン酸アルミニウム焼成体の担体上に、Pt、Rh、Pdからなる群から選択される少なくとも1種の白金族金属を担持させる工程と、
を含んでなる、排ガス用浄化触媒の製造方法であって、昇温脱離法により測定した前記担体の酸量に対する塩基量の割合xが、0.5%≦x≦1.0%、かつ前記担体の塩基点からのCO(プローブガス)脱離ピーク温度が600℃以上である、排ガス浄化用触媒の製造方法。
(4)前記白金族金属がPdである、(3)に記載の排ガス浄化触媒の製造方法。
Aspects of the present invention are as follows.
(1) An exhaust gas purifying catalyst comprising at least one platinum group metal selected from the group consisting of Pt, Rh, and Pd on a carrier of a tridymite type aluminum phosphate fired body, The ratio x of the base amount to the acid amount of the carrier measured by the desorption method is 0.5% ≦ x ≦ 1.0%, and the CO 2 (probe gas) desorption peak temperature from the base point of the carrier is An exhaust gas purifying catalyst having a temperature of 600 ° C. or higher.
(2) The exhaust gas-purifying catalyst according to (1), wherein the platinum group metal is Pd.
(3) A step of baking an aluminum phosphate obtained from an aqueous solution adjusted to have a pH of 3.5 to 4.5 at a temperature of 1000 ° C. to 1200 ° C. for 2 hours or more to obtain an aluminum phosphate fired body,
Supporting at least one platinum group metal selected from the group consisting of Pt, Rh, and Pd on the carrier of the aluminum phosphate fired body;
The ratio x of the base amount to the acid amount of the carrier measured by the temperature-programmed desorption method is 0.5% ≦ x ≦ 1.0%, A method for producing an exhaust gas purifying catalyst, wherein a CO 2 (probe gas) desorption peak temperature from a base point of the carrier is 600 ° C or higher.
(4) The method for producing an exhaust gas purification catalyst according to (3), wherein the platinum group metal is Pd.

本発明に係る排ガス浄化触媒は、排ガス浄化用触媒の熱耐久による活性点の粒成長の問題と、白金族触媒の硫黄被毒の問題とを同時に解決することによって、触媒の活性低下を抑制し、熱耐久処理・硫黄被毒処理後であっても、非常にすぐれた触媒活性を発現できるだけでなく、従来の触媒よりもさらなる高活性を示すことができるものである。   The exhaust gas purification catalyst according to the present invention suppresses a decrease in the activity of the catalyst by simultaneously solving the problem of grain growth of active sites due to the thermal durability of the exhaust gas purification catalyst and the problem of sulfur poisoning of the platinum group catalyst. Even after heat endurance treatment / sulfur poisoning treatment, the catalyst can exhibit not only excellent catalytic activity but also higher activity than conventional catalysts.

図1は、実施例1のサンプルについて、温度に対し酸量、および塩基量を測定した結果を示すグラフである。FIG. 1 is a graph showing the results of measuring the amount of acid and the amount of base with respect to temperature for the sample of Example 1. 図2は、各担体上における酸点および塩基点の様子を示すイメージ図である。FIG. 2 is an image diagram showing the state of acid points and base points on each carrier. 図3は、塩基量・塩基強度および酸量・酸強度の測定パターンを示すグラフである。FIG. 3 is a graph showing measurement patterns of base amount / base strength and acid amount / acid strength. 図4は、触媒の熱耐久・硫黄被毒処理のパターンを示すグラフである。FIG. 4 is a graph showing a pattern of heat endurance / sulfur poisoning treatment of the catalyst. 図5は、触媒の活性評価の測定パターンを示すグラフである。FIG. 5 is a graph showing a measurement pattern for evaluating the activity of the catalyst. 図6は、触媒の活性評価のイメージ図である。FIG. 6 is a conceptual diagram of catalyst activity evaluation.

なお、本明細書中において、無機物の化合物の名称、または(下記に例示するような)含有される金属の比を用いた表記により、これらの組成を有するように生成させても、不純物などを含めて現実的に生成してしまう組成をも含むものとする。したがって、無機物の化合物の名称または含有される金属の比を用いた表記により、例えば、無機化合物の構造中において、例えば、酸素、水素、窒素などの元素が、化学式中±1原子数以下で過剰または過少に存在している組成の無機化合物、すなわち、例えば、リン酸アルミニウムの場合、AlPO中で、例えば酸素の数が±1の場合のAlPO〜AlPOをも含み、またAl/Pの比率が1±約0.3のものも含み、さらに化合物中に表記されていない水素を不純物として有するものなどをも含むものである。 Note that in this specification, impurities or the like may be generated even if they are generated so as to have these compositions by the name of the inorganic compound or the notation using the ratio of the contained metal (as exemplified below). Including a composition that is actually generated. Therefore, according to the notation using the name of the inorganic compound or the ratio of the contained metal, for example, in the structure of the inorganic compound, for example, elements such as oxygen, hydrogen, and nitrogen are excessive in the chemical formula within ± 1 atom number or less. Or an inorganic compound with an under-existing composition, that is, for example, in the case of aluminum phosphate, AlPO 4 also contains, for example, AlPO 2 to AlPO 5 when the number of oxygen is ± 1, and Al / P The ratio of 1 ± about 0.3 is also included, and further, those having hydrogen not represented in the compound as an impurity are included.

本発明に係るリン酸アルミニウム焼成体は、トリディマイト型結晶構造を有するものである。ただし、トリディマイト型結晶構造の他に、バーリナイト型結晶構造、クリストバライト型結晶構造、またはアモルファスを含むこともできる。   The aluminum phosphate fired body according to the present invention has a tridymite crystal structure. However, in addition to the tridymite type crystal structure, a burrinite type crystal structure, a cristobalite type crystal structure, or an amorphous structure may be included.

本発明に係るリン酸アルミニウム焼成体としては、公知の方法により得られたリン酸アルミニウム焼成体を、特に制限なく用いることができる。   As the aluminum phosphate fired body according to the present invention, an aluminum phosphate fired body obtained by a known method can be used without particular limitation.

そして本発明に係る浄化触媒の担体は、一定範囲の酸量に対する塩基量の割合を有するものである。昇温脱離法により測定したこの担体の酸量に対する塩基量の割合xは、約0.40%以上、約0.45%以上、約0.50%以上、約0.55%以上、約0.60%以上、約1.15%以下、約1.10%以下、約1.05%以下、約1.00%以下、約0.95%以下、約0.90%以下、約0.85%以下であることができる。
下記で説明するように、SOxによる被毒および熱による活性点のシンタリングを抑制する点から、xは、約0.50以上、約1.0%以下であることが好ましい。
And the support | carrier of the purification catalyst which concerns on this invention has the ratio of the amount of bases with respect to the acid amount of a fixed range. The ratio x of the base amount to the acid amount of the carrier measured by the temperature programmed desorption method is about 0.40% or more, about 0.45% or more, about 0.50% or more, about 0.55% or more, about 0.60% or more, about 1.15% or less, about 1.10% or less, about 1.05% or less, about 1.00% or less, about 0.95% or less, about 0.90% or less, about 0 .85% or less.
As described below, x is preferably about 0.50 or more and about 1.0% or less from the viewpoint of suppressing poisoning by SOx and sintering of active sites due to heat.

さらに本発明に係る浄化触媒の担体は、担体の塩基点からのCO(プローブガス)脱離ピーク温度が一定の値以上であるものである。この担体の塩基点からのCO(プローブガス)脱離ピーク温度は、約550℃以上、約580℃以上、約590℃以上、約600℃以上、約605℃以上、約610℃以上、約615℃以上、約620℃以上、約630℃以上、約640℃以上、約1200℃以下であることできる。
下記で説明するように、600℃近辺で顕著となるSOx被毒による触媒の活性低下を防止する点から、この担体の塩基点からのCO(プローブガス)脱離ピーク温度は、約600℃以上であることが好ましい。
Furthermore, the carrier of the purification catalyst according to the present invention is such that the CO 2 (probe gas) desorption peak temperature from the base point of the carrier is a certain value or more. The CO 2 (probe gas) desorption peak temperature from the base point of this carrier is about 550 ° C. or higher, about 580 ° C. or higher, about 590 ° C. or higher, about 600 ° C. or higher, about 605 ° C. or higher, about 610 ° C. or higher, about It can be 615 ° C. or higher, about 620 ° C. or higher, about 630 ° C. or higher, about 640 ° C. or higher, and about 1200 ° C. or lower.
As will be described below, the CO 2 (probe gas) desorption peak temperature from the base point of this carrier is about 600 ° C. in order to prevent the catalyst activity from decreasing due to SOx poisoning that becomes noticeable around 600 ° C. The above is preferable.

リン酸アルミニウム焼成体の製造方法は特に限定されず、中和法などの公知の方法を採用することができる。例えば、Al含有化合物の水溶液中に、Alに対するPのモル比がほぼ当量になるようにリン酸水溶液を加え、さらにアンモニア水を加えてpHを調整して得られた沈殿物を分離して乾燥後、上記の焼成温度で焼成する方法が挙げられる。Al含有化合物としては、例えば、水酸化物、硝酸化物等金属塩が挙げられ、具体的には、Al(OH)、Al(NO等が挙げられる。 The production method of the aluminum phosphate fired body is not particularly limited, and a known method such as a neutralization method can be employed. For example, in an aqueous solution of an Al-containing compound, a phosphoric acid aqueous solution is added so that the molar ratio of P to Al is approximately equivalent, and further, ammonia water is added to adjust the pH, and the resulting precipitate is separated and dried. Then, the method of baking at said baking temperature is mentioned. Examples of the Al-containing compound include metal salts such as hydroxide and nitrate, and specifically include Al (OH) 3 , Al (NO 3 ) 3 and the like.

上記のアルミニウム塩とリン酸を含む混合溶液において用いられる溶媒としては、アルミニウム含有化合物とリン酸を溶解させることができる任意の溶媒、例えば、水などの水性溶媒や有機溶媒等を使用することができる。   As the solvent used in the mixed solution containing the aluminum salt and phosphoric acid, any solvent that can dissolve the aluminum-containing compound and phosphoric acid, for example, an aqueous solvent such as water, an organic solvent, or the like can be used. it can.

そして本発明に係るリン酸アルミニウム焼成体は、トリディマイト型結晶構造を有し、例えば、
(a)所定のpHのリン酸アルミニウム水溶液から得たリン酸アルミニウムを所定の温度で所定の時間焼成する方法、
(b)リン酸アルミニウム焼成体を製造するに際して、アルミニウムイオンに対して、リン酸イオンを過剰量加えて、未反応のリン酸イオンを生成物中に残留させる方法、
(c)リン酸アルミニウム焼成体の製造原料中に、所望の細孔径を生成できる直径を有するオレフィン系樹脂等の熱可塑性樹脂、フェノール系樹脂等の熱可塑性樹脂などの発泡剤を混合させて、焼成工程で発泡剤を焼失させる方法など、広範な方法により得られたものを用いることができる。
And the aluminum phosphate sintered body according to the present invention has a tridymite type crystal structure, for example,
(A) a method of firing an aluminum phosphate obtained from an aqueous aluminum phosphate solution having a predetermined pH at a predetermined temperature for a predetermined time;
(B) a method of adding an excessive amount of phosphate ions to aluminum ions and producing unreacted phosphate ions in the product when producing an aluminum phosphate fired body,
(C) A foaming agent such as a thermoplastic resin such as an olefin resin having a diameter capable of generating a desired pore diameter, a thermoplastic resin such as a phenol resin, or the like is mixed in the raw material for producing the aluminum phosphate fired body, Those obtained by a wide range of methods such as a method of burning off the foaming agent in the firing step can be used.

ここで、上記(a)における、リン酸アルミニウム生成時の水溶液pH、焼成温度、焼成時間は、トリディマイト型結晶構造に悪影響を与えなければ、特に制限無く、それぞれ約3.0〜約10.0、約1000℃〜1200℃、約1時間〜約10時間の範囲内などの通常使用される条件を使用できる。   Here, the pH of the aqueous solution, the firing temperature, and the firing time during the formation of aluminum phosphate in the above (a) are not particularly limited as long as they do not adversely affect the tridymite crystal structure, and about 3.0 to about 10.0, respectively. Usually used conditions such as in the range of about 1000 ° C. to 1200 ° C., about 1 hour to about 10 hours can be used.

本発明に係る浄化触媒は、上記リン酸アルミニウム焼成体に、白金(Pt)、ロジウム(Rh)、パラジウム(Pd)からなる群から選択される少なくとも1種の白金族金属を担持させて成るものである。担持の形態については、特に制限なく、焼成体上に白金族金属がおおよそ一様に担持されていればよい。   A purification catalyst according to the present invention is obtained by supporting at least one platinum group metal selected from the group consisting of platinum (Pt), rhodium (Rh), and palladium (Pd) on the aluminum phosphate fired body. It is. There is no particular limitation on the form of loading, as long as the platinum group metal is supported substantially uniformly on the fired body.

担持される白金族金属ナノ粒子の粒径は、約0.40nm以上、約0.50nm以上、約0.60nm以上、約0.70nm以上、約0.80nm以上、約0.90nm以上、約1.0nm以上であることができ、約2.2nm以下、約2.1nm以下、約2.0nm以下、約1.9nm以下、約1.8nm以下、約1.7nm以下、約1.6nm以下、約1.5nm以下、約1.4nm以下、約1.3nm以下、約1.2nm以下、約1.1nm以下であることができる。   The supported platinum group metal nanoparticles have a particle size of about 0.40 nm or more, about 0.50 nm or more, about 0.60 nm or more, about 0.70 nm or more, about 0.80 nm or more, about 0.90 nm or more, about 1.0 nm or more, about 2.2 nm or less, about 2.1 nm or less, about 2.0 nm or less, about 1.9 nm or less, about 1.8 nm or less, about 1.7 nm or less, about 1.6 nm The thickness may be about 1.5 nm or less, about 1.4 nm or less, about 1.3 nm or less, about 1.2 nm or less, or about 1.1 nm or less.

白金族金属のリン酸アルミニウム焼成体に対する量は、約0.0001wt%以上、約0.001wt%以上、約0.01wt%以上、約0.1wt%以上、約0.20wt%以上、約0.30wt%以上であることができ、約2.0wt%以下、約1.9wt%以下、約1.8wt%以下、約1.7wt%以下、約1.6wt%以下、約1.5wt%以下、約1.4wt%以下、約1.3wt%以下、約1.2wt%以下、約1.1wt%以下、約1.0wt%以下、約0.90wt%以下、約0.80wt%以下、約0.70wt%以下、約0.60wt%以下、約0.50wt%以下、約0.40wt%以下であることができる。
担持の形態については、特に制限なく、焼成体の担体上に白金族金属がおおよそ一様に担持されていればよい。
The amount of platinum group metal with respect to the aluminum phosphate fired body is about 0.0001 wt% or more, about 0.001 wt% or more, about 0.01 wt% or more, about 0.1 wt% or more, about 0.20 wt% or more, about 0 30 wt% or less, about 2.0 wt% or less, about 1.9 wt% or less, about 1.8 wt% or less, about 1.7 wt% or less, about 1.6 wt% or less, about 1.5 wt% Below, about 1.4 wt% or less, about 1.3 wt% or less, about 1.2 wt% or less, about 1.1 wt% or less, about 1.0 wt% or less, about 0.90 wt% or less, about 0.80 wt% or less About 0.70 wt% or less, about 0.60 wt% or less, about 0.50 wt% or less, or about 0.40 wt% or less.
There is no particular limitation on the form of loading, as long as the platinum group metal is supported substantially uniformly on the carrier of the fired body.

白金族金属ナノ粒子をリン酸アルミニウム焼成体に担持させる方法としては、リン酸アルミニウム焼成体に悪影響を与えなければ、特に制限なく、含浸担持法、表面析出法等、一般的な方法を用いることができる。   As a method for supporting the platinum group metal nanoparticles on the aluminum phosphate fired body, there is no particular limitation as long as it does not adversely affect the aluminum phosphate fired body. Can do.

白金族金属ナノ粒子の粒径を揃えるために、所望の粒径の白金族金属の粒子を提供できる白金族金属のコロイドを用いることもできる。他の白金族金属源、例えば酢酸白金族金属化合物、硝酸白金族金属化合物、塩化白金族金属化合物、これらから合成した白金族金属ナノ粒子を用いてもよい。ただし、リン酸アルミニウムは、強酸に易溶であるため、硝酸イオン、塩化物イオン等を含まないことが好ましい。   In order to equalize the particle size of the platinum group metal nanoparticles, a platinum group metal colloid that can provide platinum group metal particles having a desired particle size can be used. Other platinum group metal sources such as platinum acetate metal compounds, platinum nitrate metal compounds, platinum chloride metal compounds, and platinum group metal nanoparticles synthesized from these may also be used. However, since aluminum phosphate is easily soluble in a strong acid, it is preferable not to contain nitrate ions, chloride ions, and the like.

本発明に係る触媒では、下記実施例1〜3に示すように、リン酸アルミニウム中の酸量に対する塩基量の割合xが、0.5%≦x≦1.0%にあること、および担体の塩基点からのCO脱離ピーク温度が、600℃以上であることにより、白金族金属、特にPd粒子を含浸法により担持したAlPO触媒では、熱耐久処理・SO等による硫黄被毒処理後でも、600℃でNOxなどの排ガスに対して60%以上もの浄化能であって、40%以下の浄化率しか示さない従来触媒(比較例1〜7)よりも遙かにすぐれた浄化能を有することが判明した。 In the catalyst according to the present invention, as shown in Examples 1 to 3 below, the ratio x of the base amount to the acid amount in the aluminum phosphate is 0.5% ≦ x ≦ 1.0%, and the carrier When the CO 2 desorption peak temperature from the base point of the catalyst is 600 ° C. or higher, an AlPO 4 catalyst carrying a platinum group metal, particularly Pd particles by an impregnation method, is subjected to heat endurance treatment, sulfur poisoning by SO 2 and the like. Even after the treatment, the purification performance is 60% or more with respect to the exhaust gas such as NOx at 600 ° C., which is much better than the conventional catalysts (Comparative Examples 1 to 7) that show only a purification rate of 40% or less. It was found to have the ability.

ここで酸量に対する塩基量の割合xとは、例えば実施例1における酸・塩基量は、図1に示す実線のグラフのように約200℃近辺において、最大値を示し、温度がそれより高いか低くなるにつれて共に少なくなるが、酸量の塩基量に対する比率は、左軸および右軸から算出されるように、約0.8となっているものである。さらに図1の右側にピークのある幅広線に示されているように、担体の塩基点からのCO脱離ピーク温度が約600℃以上であるものである。 Here, the ratio x of the amount of base to the amount of acid is, for example, that the amount of acid / base in Example 1 shows a maximum value in the vicinity of about 200 ° C. as shown by the solid line graph in FIG. 1, and the temperature is higher than that. Although both decrease as the value decreases, the ratio of the acid amount to the base amount is about 0.8 as calculated from the left and right axes. Further, as shown by the wide line having a peak on the right side of FIG. 1, the CO 2 desorption peak temperature from the base point of the carrier is about 600 ° C. or higher.

何らかの理論に拘束されることを望まないが、担体であるリン酸アルミニウム担体上において、塩基量が少なく酸量が多いと酸性のSOxの担体への吸着を抑制でき、一方、塩基量が多く酸量が少ないと、活性点、すなわち担持された白金族金属ナノ粒子と担体との相互作用が強まって、熱耐久による活性点の粒成長を抑制することができると考えられる。
また、担体に吸着したSOxは、排ガス温度が上昇するか、またはリッチ雰囲気になると、活性点上に移動し、硫黄被毒した触媒は600℃付近で活性低下が顕著となることから、担体の塩基点で約600℃までSOxを吸着保持できると、硫黄被毒による活性点の失活を防げると考えられる。
Although not wishing to be bound by any theory, it is possible to suppress the adsorption of acidic SOx on the carrier when the amount of the base is small and the amount of acid is large on the aluminum phosphate carrier, which is the carrier, while the amount of the base is high and the acid is high. When the amount is small, the interaction between the active sites, that is, the supported platinum group metal nanoparticles and the carrier is strengthened, and it is considered that the growth of active sites due to thermal durability can be suppressed.
In addition, SOx adsorbed on the carrier moves to the active point when the exhaust gas temperature rises or becomes a rich atmosphere, and the sulfur-poisoned catalyst has a significant decrease in activity around 600 ° C. If SOx can be adsorbed and held up to about 600 ° C. at the base point, it is considered that the deactivation of the active point due to sulfur poisoning can be prevented.

下記比較例1に示すゼオライトは、塩基点に対し酸点が充分に多い(図2(b))ため、燃料中の硫黄化合物(SOx)が担体に付着し難いと考えられる。しかし、塩基点の強度が弱い、すなわちCO脱離温度が低いことからSOx吸着力が弱く、担体に吸着したSOxが、排ガスの雰囲気のリッチへの変動や温度上昇等によって、活性点に移動して活性点を被毒して活性を低下させていると考えられる。さらに、ゼオライトは、担体自体の耐熱性が低く、熱による担体の収縮により、活性点が凝集してしまい活性が大きく低下すると考えられる。 The zeolite shown in Comparative Example 1 below has a sufficiently large number of acid points relative to the base point (FIG. 2B), so it is considered that the sulfur compound (SOx) in the fuel is difficult to adhere to the carrier. However, the strength of the base point is weak, that is, the SOx adsorption power is weak because the CO 2 desorption temperature is low, and the SOx adsorbed on the carrier moves to the active point due to the rich change of the exhaust gas atmosphere, the temperature rise, etc. Therefore, it is considered that the activity is decreased by poisoning the active sites. Further, zeolite has low heat resistance of the carrier itself, and it is considered that active sites are aggregated due to shrinkage of the carrier due to heat, and the activity is greatly reduced.

下記比較例2に示すSiOは、塩基点に対し酸点が充分に多い(図2中(c))ため、燃料中の硫黄化合物(SOx)が担体に付着し難く、そして塩基点の強度も強い(CO脱離温度が高い)ので、活性点の硫黄被毒も大幅に抑制されると考えられる。しかし、担体の酸性度が大きすぎるために、担体と活性点の相互作用が小さくなって、熱耐久により活性点が移動・凝集してしまい活性が低下すると考えられる。 Since SiO 2 shown in Comparative Example 2 below has a sufficiently high acid point relative to the base point ((c) in FIG. 2), the sulfur compound (SOx) in the fuel is difficult to adhere to the carrier, and the strength of the base point Is also strong (CO 2 desorption temperature is high), and it is considered that sulfur poisoning at the active site is also greatly suppressed. However, since the acidity of the carrier is too high, the interaction between the carrier and the active sites is reduced, and the active sites are considered to move and aggregate due to thermal durability, resulting in a decrease in activity.

下記比較例3に示すAlは、塩基点を多く有する(図2中(d))ことから、担体と活性点との相互作用が大きく、熱耐久による活性点の粒成長を抑制できている反面、SOxの吸着が促進されるため、硫黄被毒を受けやすくなっていると考えられる。 Since Al 2 O 3 shown in Comparative Example 3 below has many basic points ((d) in FIG. 2), the interaction between the support and the active points is large, and the grain growth of the active points due to thermal endurance can be suppressed. On the other hand, since SOx adsorption is promoted, it is thought that it is easy to receive sulfur poisoning.

これらの材質に対し、本発明に係る、実施例1〜3に示すリン酸アルミニウム担体は、0.5%≦x≦1.0%と、多量の酸点に加え、微量の強塩基点を有する(図2(a))ことによる硫黄化合物の担体への付着しにくさと、担体と活性点との相互作用の大きさのバランスが取れていることが、硫黄被毒抑制と活性点の粒成長抑制に好都合であるだけでなく、担体の塩基点で約600℃までSOxを吸着保持すること(図1)により、SOxの移動による硫黄被毒および活性低下を抑制できるという優れた特性を有するものである。   With respect to these materials, the aluminum phosphate carrier shown in Examples 1 to 3 according to the present invention has 0.5% ≦ x ≦ 1.0%, in addition to a large amount of acid sites, a small amount of strong base sites. It is difficult to adhere to the support of the sulfur compound by having (FIG. 2 (a)) and the magnitude of the interaction between the support and the active site is balanced. Not only is it advantageous for suppressing grain growth, but also has excellent characteristics that it can suppress sulfur poisoning and decrease in activity due to SOx migration by adsorbing and holding SOx up to about 600 ° C. at the base point of the carrier (FIG. 1). It is what you have.

以下、本発明を実施例により更に具体的に説明するが、本発明はこれら実施例に限定されるものではない。   EXAMPLES Hereinafter, the present invention will be described more specifically with reference to examples, but the present invention is not limited to these examples.

<合成例1:AlPOの合成>
工程1−1:室温下で、ビーカーにイオン交換水50mlを加え、撹拌子を入れ、撹拌した。
工程1−2:0.1molの硝酸アルミニウム9水和物(ナカライテスク製)を秤量し、上記イオン交換水に加え、撹拌しながら溶解させた。
工程1−3:別のビーカーに85wt%のリン酸(ナカライテスク製)をリン酸量換算で0.1mol秤量し、工程1−2の水に加え、攪拌速度300回転/分で撹拌を続けた(ビーカーに残ったリン酸は、イオン交換水を用いて、混合液のビーカーに加えた)。
工程1−4:混合液のビーカーに、28wt%アンモニア水(ナカライテスク製)を、ピペットを用いて少量ずつ滴下し、pHが4.3となるように調整した。
工程1−5:混合液のビーカーに蓋をして12時間室温で撹拌した。
工程1−6:混合液を遠心分離機(3000回転/分、10分間)にかけ、沈殿物と上澄みに分けた。
工程1−7:沈殿物にイオン交換水を適量加え、もう一度遠心分離機にかけた(洗浄工程)。
工程1−8:沈殿物を120℃の乾燥機で12時間乾燥させた。
工程1−9:乾燥物を乳鉢に入れ、乳棒を使って解砕し、粉末状にした。
工程1−10:粉末を電気炉中1100℃で5時間焼成し、約12gの粉末を得た。
<製造例1:Pd担持体の製造>
工程2−1:室温下で、AlPO4粉末を6g秤量し、イオン交換水30mlと撹拌子を入れたビーカーに入れ、撹拌した。
工程2−2:Pd粒子の粒径0.7nmの硝酸パラジウム水溶液を、Pd担持量が0.50wt%となるよう秤量し、工程2−1のビーカーに加え、撹拌した。
工程2−3:工程2−2のビーカーを加熱撹拌し、水分がなくなるまで蒸発乾固させた。
工程2−4:工程2−3の乾固物を120℃の乾燥機中で12時間乾燥させた。
工程2−5:乾燥物を乳鉢に入れ、乳棒を使って解砕し、粉末状にした。
工程2−6:この担持粉末を電気炉中500℃で3時間焼成した。
工程2−7:焼成後の粉末をペレット状に成型した。
<Synthesis Example 1: Synthesis of AlPO 4 >
Step 1-1: 50 ml of ion-exchanged water was added to a beaker at room temperature, and a stir bar was added and stirred.
Step 1-2: 0.1 mol of aluminum nitrate nonahydrate (manufactured by Nacalai Tesque) was weighed, added to the ion-exchanged water, and dissolved while stirring.
Step 1-3: Weigh 0.1 mol of phosphoric acid (manufactured by Nacalai Tesque) in a separate beaker in terms of the amount of phosphoric acid, add it to the water in Step 1-2, and continue stirring at a stirring speed of 300 rpm. (The phosphoric acid remaining in the beaker was added to the mixed solution beaker using ion-exchanged water).
Step 1-4: 28 wt% aqueous ammonia (manufactured by Nacalai Tesque) was added dropwise to the beaker of the mixed solution little by little using a pipette, and the pH was adjusted to 4.3.
Step 1-5: The mixed solution beaker was covered and stirred at room temperature for 12 hours.
Step 1-6: The mixture was centrifuged (3000 rpm / min, 10 minutes), and separated into a precipitate and a supernatant.
Step 1-7: An appropriate amount of ion-exchanged water was added to the precipitate, and it was centrifuged again (washing step).
Step 1-8: The precipitate was dried with a dryer at 120 ° C. for 12 hours.
Step 1-9: The dried product was put in a mortar and crushed using a pestle to form a powder.
Step 1-10: The powder was fired at 1100 ° C. for 5 hours in an electric furnace to obtain about 12 g of powder.
<Production Example 1: Production of Pd carrier>
Step 2-1: At room temperature, 6 g of AlPO 4 powder was weighed, placed in a beaker containing 30 ml of ion-exchanged water and a stirring bar, and stirred.
Step 2-2: A palladium nitrate aqueous solution having a Pd particle diameter of 0.7 nm was weighed so that the amount of Pd supported was 0.50 wt%, added to the beaker in Step 2-1, and stirred.
Step 2-3: The beaker of Step 2-2 was heated and stirred and evaporated to dryness until there was no water.
Step 2-4: The dried product of Step 2-3 was dried in a dryer at 120 ° C. for 12 hours.
Step 2-5: The dried product was put in a mortar and crushed using a pestle to form a powder.
Step 2-6: This supported powder was baked in an electric furnace at 500 ° C. for 3 hours.
Step 2-7: The powder after firing was molded into a pellet.

(実施例1)
上記<合成例1>および<製造例1>の手順により、粒径2.0nmのPd担持AlPO4触媒を得た。
(実施例2、3)
工程1−4において、pHが、それぞれ、4.0、10.0になるように調整したことを除き、(実施例1)と同様の手順で、触媒粉末(実施例2、実施例3)を得た。
(比較例1〜3)
担体として、それぞれ、フェリエライト型ゼオライト(東ソー製、SiO:Al=質量比で、18:1、品番:HSZ−700シリーズ720KOA)、SiO ナノテックシリカ(シーアイ化成製)、Al ナノテックアルミナ(シーアイ化成製)を用いたことを除き、(実施例1)と同様の手順で、触媒粉末(比較例1〜3)を得た。
(比較例4〜5)
工程1−3において、それぞれ、攪拌子の回転速度を100回転/分、500回転/分としたことを除き、(実施例1)と同様の手順で、触媒粉末(比較例4、比較例5)を得た。
(比較例6〜7)
工程1−10において、それぞれ、焼成温度を1000℃、1300℃としたことを除き、(実施例1)と同様の手順で、触媒粉末(比較例6,比較例7)を得た。
Example 1
A Pd-supported AlPO 4 catalyst having a particle size of 2.0 nm was obtained by the procedures of <Synthesis Example 1> and <Production Example 1>.
(Examples 2 and 3)
The catalyst powder (Example 2, Example 3) was prepared in the same procedure as in (Example 1) except that the pH was adjusted to 4.0 and 10.0 in Steps 1-4, respectively. Got.
(Comparative Examples 1-3)
As carriers, ferrierite-type zeolite (manufactured by Tosoh, SiO 2 : Al 2 O 3 = mass ratio, 18: 1, product number: HSZ-700 series 720KOA), SiO 2 nanotech silica (manufactured by C-I Kasei), Al 2, respectively. Catalyst powders (Comparative Examples 1 to 3) were obtained in the same procedure as in (Example 1) except that O 3 nanotech alumina (manufactured by C-I Kasei) was used.
(Comparative Examples 4-5)
In Step 1-3, the catalyst powders (Comparative Example 4 and Comparative Example 5) were prepared in the same manner as in (Example 1) except that the rotation speed of the stirrer was 100 rpm / 500 rpm. )
(Comparative Examples 6-7)
In Step 1-10, catalyst powders (Comparative Example 6 and Comparative Example 7) were obtained in the same procedure as in (Example 1) except that the firing temperature was 1000 ° C. and 1300 ° C., respectively.

<XPSによる光電子エネルギーおよび結晶構造の測定>
試料水平型強力X線回析装置 RINT−TTRIII(メーカー名:(株)リガク)を用いてX線を照射し、生じる光電子のエネルギーを測定し、さらに結晶構造を観察した。
<Measurement of photoelectron energy and crystal structure by XPS>
A sample horizontal strong X-ray diffraction apparatus RINT-TTRIII (manufacturer name: Rigaku Co., Ltd.) was used to irradiate X-rays, measure the energy of the generated photoelectrons, and observe the crystal structure.

<白金族金属ナノ粒子の粒径の測定>
白金族金属ナノ粒子の粒径は、試料水平型強力X線回析装置 RINT−TTRIII(メーカー名:(株)リガク)を用いて測定した。
結晶子径の算出には2θ=40.0〜40.2°付近をPdのピークとして使用した。
<Measurement of particle size of platinum group metal nanoparticles>
The particle size of the platinum group metal nanoparticles was measured using a sample horizontal intense X-ray diffraction apparatus RINT-TTRIII (manufacturer name: Rigaku Corporation).
For calculation of the crystallite diameter, the vicinity of 2θ = 40.0 to 40.2 ° was used as the peak of Pd.

(触媒評価法)
触媒粉末を2tの圧力を加えて圧縮成形した後、これを粉砕し直径1.0mm程度のペレットに圧縮成形したものを評価サンプルとした。
<塩基量・塩基強度測定(CO昇温脱離法)>
図3に示す以下の工程3−1〜工程3−7に従って、触媒用吸着脱離ガス分析装置(型番:RE−202、メーカー名:日本真空技術株式会社)により、測定した。
サンプル量は各1.0gとし、ガス流量は100cc/分とした。
工程3−1:室温から500℃まで30℃/分の昇温速度で15分掛けて、サンプルの温度を昇温しながら、Heを流した。
工程3−2:サンプルを500℃で10分間保持しながら、Heを流した。
工程3−3:500℃から100℃まで、20℃/分の降温速度で、20分掛けて、サンプルの温度を昇温しながら、Heを流した。
工程3−4:サンプルを100℃で5分間保持しながら、Heを流した。
工程3−5:サンプルを100℃で15分間保持しながら、sccm比、すなわち体積比で、90:10のHe:COを流した。
工程3−6:サンプルを100℃で90分間保持しながら、Heを流した。
工程3−7:100℃から800℃まで、20℃/分の昇温速度で35分掛けて、サンプルの温度を昇温しながら、Heを流した。
(Catalyst evaluation method)
The catalyst powder was compression-molded by applying a pressure of 2 t, then pulverized and compression-molded into pellets having a diameter of about 1.0 mm as an evaluation sample.
<Measurement of base amount and base strength (CO 2 temperature programmed desorption method)>
According to the following steps 3-1 to 3-7 shown in FIG. 3, the measurement was performed using a catalyst adsorption / desorption gas analyzer (model number: RE-202, manufacturer: Nippon Vacuum Technology Co., Ltd.).
The sample amount was 1.0 g each, and the gas flow rate was 100 cc / min.
Step 3-1: He was allowed to flow while increasing the temperature of the sample from room temperature to 500 ° C. at a rate of temperature increase of 30 ° C./min over 15 minutes.
Step 3-2: He was allowed to flow while holding the sample at 500 ° C. for 10 minutes.
Step 3-3: He was allowed to flow while raising the temperature of the sample from 500 ° C. to 100 ° C. at a rate of temperature decrease of 20 ° C./min over 20 minutes.
Step 3-4: He was allowed to flow while holding the sample at 100 ° C. for 5 minutes.
Step 3-5: While maintaining the sample at 100 ° C. for 15 minutes, 90:10 He: CO 2 was flowed at a sccm ratio, that is, a volume ratio.
Step 3-6: He was allowed to flow while holding the sample at 100 ° C. for 90 minutes.
Step 3-7: He was allowed to flow from 100 ° C. to 800 ° C. at a rate of temperature increase of 20 ° C./min for 35 minutes while increasing the temperature of the sample.

<酸量・酸強度測定(NH昇温脱離法)>
工程3−5において、He:COの代わりに、sccmの比、すなわち体積比で、90:10のHe:NHを流した以外は、<塩基量・塩基強度測定(CO昇温脱離法)>と同様の手順により行った。
<熱耐久処理・硫黄被毒処理>
工程4−1:白金属金属を担持したペレット1.0gを、アルミナ製反応管に入れた。次に、図4に示すように、以下の工程4−2〜工程4−6により触媒に熱耐久・硫黄被毒処理を行った。なお、工程4−2〜工程4−5において、ガス流量はいずれも5リットル/分である。
工程4−2:反応管内の温度を、電気炉で室温から1000℃まで、5℃/分の昇温速度で180分間加熱しながら、反応管内に100体積%のNを流した。
工程4−3:反応管内の温度を1000℃に保ったまま、300分間の間、3体積%のCO(残余N)のガスと、5体積%のO(残余N)のガスとを2分間隔で交互に流通させた。
工程4−4:反応管内の温度を、3℃/分の速度で400℃まで200分間降温しながら、反応管内に100体積%のNを流した。
工程4−5:反応管内の温度を400℃に保ったまま、90分間の間、体積でNO:0.1%、CO:0.65%、C:0.1%、CO:10%、O:0.725%、HO:3%、SO:0.05%、N:残余のガスを流した。
工程4−6:自然放冷により室温まで冷却した。
<Measurement of acid amount and acid strength (NH 3 temperature programmed desorption method)>
In Step 3-5, instead of He: CO 2 , the ratio of sccm, that is, volume ratio, except that 90:10 He: NH 3 was flowed, <base amount / base strength measurement (CO 2 temperature rising desorption) Separation procedure)>.
<Heat endurance treatment / sulfur poisoning treatment>
Step 4-1: 1.0 g of pellets carrying a white metal metal was placed in an alumina reaction tube. Next, as shown in FIG. 4, the catalyst was subjected to heat durability and sulfur poisoning by the following steps 4-2 to 4-6. In Steps 4-2 to 4-5, the gas flow rate is 5 liters / minute.
Step 4-2: While the temperature in the reaction tube was heated from room temperature to 1000 ° C. in an electric furnace at a rate of temperature increase of 5 ° C./min for 180 minutes, 100% by volume of N 2 was allowed to flow into the reaction tube.
Step 4-3: While maintaining the temperature in the reaction tube at 1000 ° C., for 3 minutes, 3% by volume of CO (residual N 2 ) gas and 5% by volume of O 2 (residual N 2 ) gas Were circulated alternately at intervals of 2 minutes.
Step 4-4: While the temperature in the reaction tube was lowered to 400 ° C. for 200 minutes at a rate of 3 ° C./min, 100% by volume of N 2 was allowed to flow into the reaction tube.
Step 4-5: While maintaining the temperature in the reaction tube at 400 ° C., NO is 0.1%, CO is 0.65%, C 3 H 6 is 0.1%, and CO 2 by volume for 90 minutes. : 10%, O 2 : 0.725%, H 2 O: 3%, SO 2 : 0.05%, N 2 : The remaining gas was allowed to flow.
Process 4-6: It cooled to room temperature by natural cooling.

<触媒の活性評価>
熱耐久処理・硫黄被毒処理後の触媒の活性評価を、図5に示す以下の工程5−1〜工程5−5に従って、ガス流通式の触媒評価装置を用いて浄化率を測定することにより行った。
サンプル量は、各3.0gとした。
工程5−1:室温から150℃まで20℃/分の昇温速度で、サンプルの温度を昇温させた。
工程5−2:サンプルを150℃で5分間保持した。
工程5−3:150℃から600℃まで20℃/分の昇温速度で、サンプルの温度を昇温させた。
工程5−4:サンプルの温度を600℃保持しながら、評価ガスとして、体積で、CO:0.65%、C:3000ppmC、NO:1500ppm、O:0.7%、HO:3%、CO:10%、N:残余のモデルガスを、ガス流量15L/分、SV約300,000時間−1で、3分間流して、浄化率を測定した。
浄化率測定は、図6に示すように、評価ガスをサンプルに通過させた後のガス組成を、赤外分光計(メーカー名:(株)堀場製作所、型番:MEXA−6000FT)を用いて測定し、この測定値から下記の式により浄化率を算出した。
浄化率(%)=(触媒の入りガス濃度(体積%)−触媒の出ガス濃度(体積%))/触媒の入りガス濃度(体積%)×100
工程5−5:自然放冷により室温まで冷却した。
<Evaluation of catalyst activity>
By evaluating the activity of the catalyst after the heat endurance treatment / sulfur poisoning treatment by measuring the purification rate using a gas flow-type catalyst evaluation device according to the following steps 5-1 to 5-5 shown in FIG. went.
Each sample amount was 3.0 g.
Step 5-1: The temperature of the sample was raised from room temperature to 150 ° C. at a rate of temperature increase of 20 ° C./min.
Step 5-2: The sample was held at 150 ° C. for 5 minutes.
Step 5-3: The temperature of the sample was increased from 150 ° C. to 600 ° C. at a rate of temperature increase of 20 ° C./min.
Step 5-4: While maintaining the temperature of the sample at 600 ° C., by volume, as an evaluation gas, CO: 0.65%, C 3 H 6 : 3000 ppmC, NO: 1500 ppm, O 2 : 0.7%, H 2 O: 3%, CO 2 : 10%, N 2 : The remaining model gas was allowed to flow for 3 minutes at a gas flow rate of 15 L / min and SV of about 300,000 hours −1 to measure the purification rate.
As shown in FIG. 6, the purification rate is measured using an infrared spectrometer (manufacturer name: HORIBA, Ltd., model number: MEXA-6000FT) after passing the evaluation gas through the sample. The purification rate was calculated from the measured value by the following formula.
Purification rate (%) = (catalyst gas concentration (volume%) − catalyst gas concentration (volume%)) / catalyst gas concentration (volume%) × 100
Step 5-5: Cooled to room temperature by natural cooling.

(結果)
実施例1〜3および比較例1〜7で得られた、担体ごとの、酸量に対する塩基量の割合(%)、塩基点からのCO脱離ピーク温度(℃)、熱耐久・硫黄比被毒後の600℃でのNOx浄化率(%)を表1に示す。
酸量に対する塩基量の割合は、両者の検量線と、ピーク面積から算出した。
(result)
The ratio of base amount to acid amount (%), CO 2 desorption peak temperature from base point (° C.), heat endurance / sulfur ratio, obtained for each of Examples 1 to 3 and Comparative Examples 1 to 7 Table 1 shows the NOx purification rate (%) at 600 ° C. after poisoning.
The ratio of the amount of base to the amount of acid was calculated from both calibration curves and the peak area.

Figure 2014113580
Figure 2014113580

酸量に対する塩基量の割合xが、0.8%(実施例1)、0.5%(実施例2)、1.0%(実施例3)であり、かつ塩基点からのCO脱離ピーク温度が、640℃、620℃、650℃である本発明に係る触媒では、600℃でのNOについて熱耐久・硫黄被毒処理後でも、驚いたことに、浄化率がそれぞれ65%、58%、60%と、従来の浄化率18%〜40(比較例1〜7)に比べて、格段の性能を示した。 The ratio x of the amount of base to the amount of acid is 0.8% (Example 1), 0.5% (Example 2), 1.0% (Example 3), and CO 2 desorption from the base point. In the catalyst according to the present invention having separation peak temperatures of 640 ° C., 620 ° C., and 650 ° C., surprisingly, the purification rate was 65% for NO at 600 ° C. even after heat endurance and sulfur poisoning treatment. Compared with conventional purification rates of 18% to 40 (Comparative Examples 1 to 7), 58% and 60%, markedly higher performance was exhibited.

比較例1のゼオライトは、塩基点に対し酸点が充分に多いことから、燃料中の硫黄化合物(SOx)が担体に付着し難いと考えられるものの、塩基点からのCO離脱ピーク温度が170℃、340℃と低いことから、塩基点の強度が弱いようであることが判明した。
さらに、熱耐久・硫黄被毒後の600℃におけるNOx浄化率が18%と低いのは、ゼオライト担体自体の耐熱性が低く、熱による担体の収縮により、活性点が凝集してしまって活性が大きく低下してしまったことによると考えられる。
Since the zeolite of Comparative Example 1 has a sufficiently high acid point relative to the base point, it is considered that the sulfur compound (SOx) in the fuel is difficult to adhere to the carrier, but the CO 2 desorption peak temperature from the base point is 170. Since it was as low as 340 ° C., it was found that the strength of the base point seems to be weak.
Furthermore, the NOx purification rate at 600 ° C. after heat endurance and sulfur poisoning is as low as 18% because the heat resistance of the zeolite carrier itself is low, and the active sites are aggregated due to the shrinkage of the carrier due to heat, and the activity is increased. This is thought to be due to a large drop.

比較例2のSiOは、塩基点に対し酸点が充分に多いことから、燃料中の硫黄化合物(SOx)が担体に付着し難いと考えられ、塩基点からのCO離脱ピーク温度も680℃であることから、塩基点の強度も強いと考えられる。
しかし、担体の酸性度が大きすぎるために、担体と活性点の相互作用が小さくなって、熱耐久により活性点が移動・凝集して、熱耐久・硫黄被毒後の600℃におけるNOx浄化率が35%と低下してしまったと考えられる。
Since SiO 2 of Comparative Example 2 has a sufficiently large acid point relative to the base point, it is considered that the sulfur compound (SOx) in the fuel is difficult to adhere to the carrier, and the CO 2 desorption peak temperature from the base point is also 680. Since it is ° C., it is considered that the strength of the base point is also strong.
However, since the acidity of the carrier is too large, the interaction between the carrier and the active point is reduced, and the active point moves and aggregates due to heat endurance, and the NOx purification rate at 600 ° C. after heat endurance and sulfur poisoning Is considered to have fallen to 35%.

比較例3のAlは、塩基点を多く有することから、担体と活性点との相互作用が大きいと考えられる。しかし、この塩基点の多さにより酸性のSOxの吸着が促進されて硫黄被毒により、熱耐久・硫黄被毒後の600℃におけるNOx浄化率が30%と低下してしまったと考えられる。 Al 2 O 3 of Comparative Example 3, since it has many basic sites is believed that a large interaction between the carrier and the active sites. However, it is considered that the adsorption of acidic SOx was promoted by the large number of base points, and the NOx purification rate at 600 ° C. after heat endurance / sulfur poisoning was reduced to 30% due to sulfur poisoning.

また、トリディマイト型結晶を有するリン酸アルミニウムを用いても、酸量に対する塩基量の割合xが1.0%を超えた、1.2%(比較例5)、2.0%(比較例7)では、xが大きくなる程、熱耐久・硫黄被毒後の600℃におけるNOx浄化率が40%(比較例5)、18%(比較例7)とより低下してしまうことが判明した。   Further, even when aluminum phosphate having tridymite type crystals was used, the ratio x of the base amount to the acid amount exceeded 1.0%, 1.2% (Comparative Example 5), 2.0% (Comparative Example 7) ), It was found that as x increased, the NOx purification rate at 600 ° C. after heat endurance / sulfur poisoning decreased to 40% (Comparative Example 5) and 18% (Comparative Example 7).

さらに、リン酸アルミニウム担体の焼成条件が、1000℃だと、アモルファス構造のリン酸アルミニウムが生成する。アモルファス構造のリン酸アルミニウムは、白金属金属を担持する際に担持薬液の酸成分によって構造が壊れるため、担体上に白金属金属がうまく担持されず、熱耐久後にシンタリングすると考えられ、xが0.8%であっても、熱耐久・硫黄被毒後の600℃におけるNOx浄化率が24%(比較例6)と低下してしまうことが判明した。   Further, when the baking condition of the aluminum phosphate carrier is 1000 ° C., amorphous aluminum phosphate is generated. It is considered that the amorphous aluminum phosphate having an amorphous structure breaks the structure due to the acid component of the supporting chemical solution when supporting the white metal metal, so that the white metal metal is not well supported on the support and is sintered after the heat endurance. Even at 0.8%, it has been found that the NOx purification rate at 600 ° C. after heat endurance and sulfur poisoning decreases to 24% (Comparative Example 6).

上記のように、本発明の態様に係る触媒と、比較例および従来の触媒との性能差には、アモルファスを含まないトリディマイト型リン酸アルミニウム焼成体であること、昇温脱離法により測定した前記担体の酸量に対する塩基量の割合xが、0.5%≦x≦1.0%であること、および前記担体の塩基点からのCO(プローブガス)脱離ピーク温度が600℃以上であることが、大きく影響することが明らかになった。 As described above, the performance difference between the catalyst according to the embodiment of the present invention, the comparative example, and the conventional catalyst is a tridymite-type aluminum phosphate fired body that does not contain an amorphous material, measured by a temperature programmed desorption method. The ratio x of the base amount to the acid amount of the carrier is 0.5% ≦ x ≦ 1.0%, and the CO 2 (probe gas) desorption peak temperature from the base point of the carrier is 600 ° C. or higher. It has become clear that this has a significant effect.

以上のように、本発明に係る排ガス浄化触媒は、熱耐久処理・硫黄被毒処理後であっても、排ガス浄化触媒として良好な性能を有するものである。こうしたことから、本発明に係る酸化触媒の用途は、排ガス浄化触媒に限られず、広い分野において様々な用途に利用することができる。   As described above, the exhaust gas purification catalyst according to the present invention has good performance as an exhaust gas purification catalyst even after the heat endurance treatment and sulfur poisoning treatment. For these reasons, the use of the oxidation catalyst according to the present invention is not limited to the exhaust gas purification catalyst, and can be used for various applications in a wide field.

Claims (4)

トリディマイト型リン酸アルミニウム焼成体の担体上に、Pt、Rh、Pdからなる群から選択される少なくとも1種の白金族金属を担持してなる、排ガス浄化用触媒であって、昇温脱離法により測定した前記担体の酸量に対する塩基量の割合xが、0.5%≦x≦1.0%、かつ前記担体の塩基点からのCO(プローブガス)脱離ピーク温度が600℃以上である、排ガス浄化用触媒。 A catalyst for purifying exhaust gas, comprising at least one platinum group metal selected from the group consisting of Pt, Rh, and Pd on a carrier of a tridymite-type aluminum phosphate fired body, The ratio x of the base amount to the acid amount of the carrier measured by the above is 0.5% ≦ x ≦ 1.0%, and the CO 2 (probe gas) desorption peak temperature from the base point of the carrier is 600 ° C. or higher A catalyst for exhaust gas purification. 前記白金族金属がPdである、請求項1に記載の排ガス浄化用触媒。   The exhaust gas-purifying catalyst according to claim 1, wherein the platinum group metal is Pd. pHが3.5〜4.5になるように調整した水溶液から得たリン酸アルミニウムを1000℃〜1200℃の温度で2時間以上焼成してリン酸アルミニウム焼成体を得る工程と、
前記リン酸アルミニウム焼成体の担体上に、Pt、Rh、Pdからなる群から選択される少なくとも1種の白金族金属を担持させる工程と、
を含んでなる、排ガス用浄化触媒の製造方法であって、昇温脱離法により測定した前記担体の酸量に対する塩基量の割合xが、0.5%≦x≦1.0%、かつ前記担体の塩基点からのCO(プローブガス)脱離ピーク温度が600℃以上である、排ガス浄化用触媒の製造方法。
a step of calcining an aluminum phosphate obtained from an aqueous solution adjusted to have a pH of 3.5 to 4.5 at a temperature of 1000 ° C. to 1200 ° C. for 2 hours or more to obtain a calcined aluminum phosphate,
Supporting at least one platinum group metal selected from the group consisting of Pt, Rh, and Pd on the carrier of the aluminum phosphate fired body;
The ratio x of the base amount to the acid amount of the carrier measured by the temperature-programmed desorption method is 0.5% ≦ x ≦ 1.0%, A method for producing an exhaust gas purifying catalyst, wherein a CO 2 (probe gas) desorption peak temperature from a base point of the carrier is 600 ° C or higher.
前記白金族金属がPdである、請求項3に記載の排ガス浄化触媒の製造方法。   The method for producing an exhaust gas purification catalyst according to claim 3, wherein the platinum group metal is Pd.
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EP2799133A1 (en) * 2011-12-26 2014-11-05 Toyota Jidosha Kabushiki Kaisha Exhaust gas purifying catalyst and method for producing same
US9498771B2 (en) 2012-09-12 2016-11-22 Toyota Jidosha Kabushiki Kaisha Catalyst for exhaust gas purification, and method for producing same

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WO2009142180A1 (en) * 2008-05-22 2009-11-26 三井金属鉱業株式会社 Exhaust gas purifying catalyst and method for producing the same

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP2799133A1 (en) * 2011-12-26 2014-11-05 Toyota Jidosha Kabushiki Kaisha Exhaust gas purifying catalyst and method for producing same
US9498771B2 (en) 2012-09-12 2016-11-22 Toyota Jidosha Kabushiki Kaisha Catalyst for exhaust gas purification, and method for producing same

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