JP3532044B2 - Oxide catalyst material for removing nitrogen oxides and method for removing nitrogen oxides - Google Patents
Oxide catalyst material for removing nitrogen oxides and method for removing nitrogen oxidesInfo
- Publication number
- JP3532044B2 JP3532044B2 JP29039396A JP29039396A JP3532044B2 JP 3532044 B2 JP3532044 B2 JP 3532044B2 JP 29039396 A JP29039396 A JP 29039396A JP 29039396 A JP29039396 A JP 29039396A JP 3532044 B2 JP3532044 B2 JP 3532044B2
- Authority
- JP
- Japan
- Prior art keywords
- nitrogen oxides
- removing nitrogen
- catalyst material
- oxide
- exhaust gas
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Fee Related
Links
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 title claims description 135
- 239000003054 catalyst Substances 0.000 title claims description 31
- 239000000463 material Substances 0.000 title claims description 20
- 238000000034 method Methods 0.000 title claims description 19
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 claims description 53
- 239000007789 gas Substances 0.000 claims description 36
- 239000002131 composite material Substances 0.000 claims description 17
- 229910052760 oxygen Inorganic materials 0.000 claims description 17
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 16
- 239000001301 oxygen Substances 0.000 claims description 16
- 230000002950 deficient Effects 0.000 claims description 12
- 229910052751 metal Inorganic materials 0.000 claims description 12
- 229910052733 gallium Inorganic materials 0.000 claims description 11
- 229910052759 nickel Inorganic materials 0.000 claims description 11
- 229910052596 spinel Inorganic materials 0.000 claims description 11
- 239000011029 spinel Substances 0.000 claims description 11
- 230000001603 reducing effect Effects 0.000 claims description 9
- 239000006104 solid solution Substances 0.000 claims description 9
- 229910052799 carbon Inorganic materials 0.000 claims description 6
- GYHNNYVSQQEPJS-UHFFFAOYSA-N Gallium Chemical compound [Ga] GYHNNYVSQQEPJS-UHFFFAOYSA-N 0.000 claims description 5
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 4
- 230000001590 oxidative effect Effects 0.000 claims description 4
- 238000011156 evaluation Methods 0.000 description 11
- 230000009467 reduction Effects 0.000 description 10
- 239000000843 powder Substances 0.000 description 8
- 239000013078 crystal Substances 0.000 description 7
- 238000010438 heat treatment Methods 0.000 description 7
- 239000002184 metal Substances 0.000 description 6
- 239000012071 phase Substances 0.000 description 5
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 5
- 239000000126 substance Substances 0.000 description 4
- PNEYBMLMFCGWSK-UHFFFAOYSA-N Alumina Chemical compound [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 3
- KDLHZDBZIXYQEI-UHFFFAOYSA-N Palladium Chemical compound [Pd] KDLHZDBZIXYQEI-UHFFFAOYSA-N 0.000 description 3
- 229910002091 carbon monoxide Inorganic materials 0.000 description 3
- 238000004519 manufacturing process Methods 0.000 description 3
- BASFCYQUMIYNBI-UHFFFAOYSA-N platinum Chemical compound [Pt] BASFCYQUMIYNBI-UHFFFAOYSA-N 0.000 description 3
- 239000010457 zeolite Substances 0.000 description 3
- 229910018072 Al 2 O 3 Inorganic materials 0.000 description 2
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- 238000004438 BET method Methods 0.000 description 2
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 2
- 230000010757 Reduction Activity Effects 0.000 description 2
- 238000002441 X-ray diffraction Methods 0.000 description 2
- 229910021536 Zeolite Inorganic materials 0.000 description 2
- 230000003197 catalytic effect Effects 0.000 description 2
- 239000003153 chemical reaction reagent Substances 0.000 description 2
- 238000002485 combustion reaction Methods 0.000 description 2
- 230000000052 comparative effect Effects 0.000 description 2
- 230000003247 decreasing effect Effects 0.000 description 2
- 230000007812 deficiency Effects 0.000 description 2
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 description 2
- 229930195733 hydrocarbon Natural products 0.000 description 2
- 150000002430 hydrocarbons Chemical class 0.000 description 2
- 229910052914 metal silicate Inorganic materials 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- 230000008569 process Effects 0.000 description 2
- 238000000746 purification Methods 0.000 description 2
- 239000002994 raw material Substances 0.000 description 2
- 239000012495 reaction gas Substances 0.000 description 2
- 239000010948 rhodium Substances 0.000 description 2
- 238000001179 sorption measurement Methods 0.000 description 2
- 238000003756 stirring Methods 0.000 description 2
- 238000012360 testing method Methods 0.000 description 2
- VHUUQVKOLVNVRT-UHFFFAOYSA-N Ammonium hydroxide Chemical compound [NH4+].[OH-] VHUUQVKOLVNVRT-UHFFFAOYSA-N 0.000 description 1
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 1
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 description 1
- JPVYNHNXODAKFH-UHFFFAOYSA-N Cu2+ Chemical group [Cu+2] JPVYNHNXODAKFH-UHFFFAOYSA-N 0.000 description 1
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 description 1
- 150000001242 acetic acid derivatives Chemical class 0.000 description 1
- 238000003915 air pollution Methods 0.000 description 1
- 150000004703 alkoxides Chemical class 0.000 description 1
- QGZKDVFQNNGYKY-UHFFFAOYSA-N ammonia Natural products N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 1
- 150000004649 carbonic acid derivatives Chemical class 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 238000009694 cold isostatic pressing Methods 0.000 description 1
- 230000008094 contradictory effect Effects 0.000 description 1
- 229910052802 copper Inorganic materials 0.000 description 1
- 239000010949 copper Substances 0.000 description 1
- 229910001431 copper ion Inorganic materials 0.000 description 1
- 229910052878 cordierite Inorganic materials 0.000 description 1
- 238000002425 crystallisation Methods 0.000 description 1
- 230000008025 crystallization Effects 0.000 description 1
- 238000000280 densification Methods 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- JSKIRARMQDRGJZ-UHFFFAOYSA-N dimagnesium dioxido-bis[(1-oxido-3-oxo-2,4,6,8,9-pentaoxa-1,3-disila-5,7-dialuminabicyclo[3.3.1]nonan-7-yl)oxy]silane Chemical compound [Mg++].[Mg++].[O-][Si]([O-])(O[Al]1O[Al]2O[Si](=O)O[Si]([O-])(O1)O2)O[Al]1O[Al]2O[Si](=O)O[Si]([O-])(O1)O2 JSKIRARMQDRGJZ-UHFFFAOYSA-N 0.000 description 1
- 239000012153 distilled water Substances 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 230000001747 exhibiting effect Effects 0.000 description 1
- 239000000446 fuel Substances 0.000 description 1
- 238000004817 gas chromatography Methods 0.000 description 1
- 230000002209 hydrophobic effect Effects 0.000 description 1
- 229910052738 indium Inorganic materials 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 238000005259 measurement Methods 0.000 description 1
- 230000007246 mechanism Effects 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 150000002823 nitrates Chemical class 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 229910000510 noble metal Inorganic materials 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 229910052763 palladium Inorganic materials 0.000 description 1
- 229910052697 platinum Inorganic materials 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 239000002244 precipitate Substances 0.000 description 1
- 238000003825 pressing Methods 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 229910052703 rhodium Inorganic materials 0.000 description 1
- MHOVAHRLVXNVSD-UHFFFAOYSA-N rhodium atom Chemical compound [Rh] MHOVAHRLVXNVSD-UHFFFAOYSA-N 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
- 238000003980 solgel method Methods 0.000 description 1
- 238000003746 solid phase reaction Methods 0.000 description 1
- 239000000243 solution Substances 0.000 description 1
- 238000010792 warming Methods 0.000 description 1
Landscapes
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
- Catalysts (AREA)
Description
【0001】[0001]
【発明の属する技術分野】本発明は、窒素酸化物を還元
除去することができる新規な酸化物触媒材料並びにこれ
を用いて排気ガス中の窒素酸化物を除去する方法に関す
るもので、とりわけ排気ガス中に過剰の酸素が存在する
リーンバーンエンジンやディーゼルエンジン等の自動車
排気ガス浄化用として好適な窒素酸化物除去用酸化物触
媒材料並びに該酸化物触媒材料を用いて過剰酸素共存下
の排気ガス中の窒素酸化物(NOx)を除去する方法に
関するものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a novel oxide catalyst material capable of reducing and removing nitrogen oxides, and a method for removing nitrogen oxides in exhaust gas using the same. Oxide catalyst material for removing nitrogen oxides suitable for purifying automobile exhaust gas such as lean burn engines and diesel engines in which excess oxygen is present, and the use of the oxide catalyst material in exhaust gas in the presence of excess oxygen And a method for removing nitrogen oxides (NO x ).
【0002】[0002]
【従来の技術】近年、各種汚染物質による大気の汚れが
大きな社会問題となり、その中でも大気汚染の移動発生
源となっている自動車の排気ガスに含まれるNOx、C
Ox等の有害物質を分解、除去する方法の開発が急務と
なっている。2. Description of the Related Art In recent years, pollution of the air by various pollutants has become a major social problem. Among them, NO x and C contained in exhaust gas of automobiles, which are sources of movement of air pollution.
Decomposing harmful substances O x or the like, the development of a method for removing is a pressing need.
【0003】従来より、自動車の排気ガス中のNOx、
COx等の有害物質を分解、除去する方法としては、排
気ガス中に残存する未燃の一酸化炭素及び炭化水素の酸
化と、窒素酸化物の還元を同時に行う三元触媒が汎用さ
れてきた。[0003] Conventionally, NO x in exhaust gas of automobiles,
As a method for decomposing and removing harmful substances such as CO x, a three-way catalyst has been widely used which simultaneously oxidizes unburned carbon monoxide and hydrocarbons remaining in exhaust gas and reduces nitrogen oxides. .
【0004】そのような方法に用いられる三元触媒とし
ては、パラジウム(Pd)、白金(Pt)、ロジウム
(Rh)等の貴金属をγ−アルミナ(Al2O3)で被
覆したコージェライト等の耐火性担体に担持したものが
用いられていた。The three-way catalyst used in such a method includes cordierite and the like, in which a noble metal such as palladium (Pd), platinum (Pt), and rhodium (Rh) is coated with γ-alumina (Al 2 O 3 ). What was carried on the refractory carrier was used.
【0005】しかしながら、前記三元触媒は、およそ
0.5%程度の低酸素濃度においては前記排気ガスの浄
化を効率良く行うことができるものの、該排気ガス中の
酸素濃度が1%を越えるような高濃度雰囲気中では有効
に働かなくなるという欠点があった。[0005] However, the three-way catalyst can efficiently purify the exhaust gas at a low oxygen concentration of about 0.5%, but the oxygen concentration in the exhaust gas exceeds 1%. There is a disadvantage that it does not work effectively in an extremely high concentration atmosphere.
【0006】一方、前記欠点を回避するために、排気ガ
ス中の酸素濃度を測定し、常にCO及びCxHy、NO
xを高い還元率で処理し得る理論等量値に近い範囲の空
燃比となるように制御することも行われているが、前記
CO及びCxHyとNOxの発生メカニズムが相反する
特性を有することから、限られた状態での燃焼を維持し
なければならず、前記のような高い酸素濃度中での排気
ガス浄化はほとんどできていないのが現状である。On the other hand, in order to avoid the above-mentioned drawback, the oxygen concentration in the exhaust gas is measured, and CO, C x H y , NO
is also being done to control such that the air-fuel ratio close range to the theoretical equivalent value which may be treated with x with a high reduction ratio, the generation mechanism of the CO and C x H y and NO x are contradictory properties Therefore, combustion in a limited state must be maintained, and at present, exhaust gas purification in a high oxygen concentration as described above has hardly been performed.
【0007】そこで、係る高濃度の酸素共存下でも窒素
酸化物を効率良く除去できる触媒として、金属を担持し
た疎水性ゼオライト等の銅イオン交換ゼオライト、ある
いはメタルシリケート、アルミナ触媒等が提案されてい
る(特開平4−349938号公報参照)。Therefore, as a catalyst capable of efficiently removing nitrogen oxides even in the presence of such a high concentration of oxygen, a metal ion-supported copper ion-exchanged zeolite such as a hydrophobic zeolite, a metal silicate, an alumina catalyst, and the like have been proposed. (See JP-A-4-349938).
【0008】[0008]
【発明が解決しようとする課題】しかしながら、前記提
案の銅イオン交換ゼオライトやメタルシリケート、ある
いはアルミナ触媒等は、いずれも耐熱性に劣るため、長
時間運転での構造破壊による性能低下、あるいは耐SV
(空間速度)性が悪く、SV値が200000/hr.
以上の高速を示す実際のエンジン排気ガスの条件下で
は、窒素酸化物の還元能が著しく低下するという課題が
あり、そのままでは効果的な窒素酸化物の浄化が難しい
という課題があった。However, the copper ion exchanged zeolites, metal silicates, alumina catalysts and the like proposed above are all inferior in heat resistance.
(Space velocity) property is poor, and the SV value is 200000 / hr.
Under the conditions of the actual engine exhaust gas exhibiting the above high speed, there is a problem that the reducing ability of nitrogen oxides is remarkably reduced, and there is a problem that it is difficult to effectively purify nitrogen oxides as it is.
【0009】[0009]
【発明の目的】本発明は、ディーゼルエンジンをはじめ
とする各種自動車用エンジン等の水分を含む酸素濃度の
高い排気ガスを、該排気ガスの流速がSV値で2000
00/hr.以上の高速であっても、高い窒素酸化物の
還元作用を示し、有効に排気ガス中の窒素酸化物を還元
することができる有用な触媒材料並びにそれを用いた窒
素酸化物除去方法を提供するものである。SUMMARY OF THE INVENTION The present invention relates to an exhaust gas having a high oxygen concentration containing water, such as a diesel engine and various automobile engines, having an SV value of 2000.
00 / hr. Provided is a useful catalyst material which exhibits a high nitrogen oxide reducing action even at the above high speed and can effectively reduce nitrogen oxides in exhaust gas, and a nitrogen oxide removing method using the same. Things.
【0010】[0010]
【課題を解決するための手段】本発明は、前記課題に鑑
みなされたもので、Ni及びGaを主たる金属元素とし
て含有するスピネル型結晶性複合酸化物で、Ni1−X
Ga2O4(但し、0.2≦X<0.6)で表されるN
i欠損型固溶体が、高酸素濃度雰囲気下でも高い触媒活
性を長期にわたり有し、有効に排気ガス中の窒素酸化物
を還元することができることを見出したものである。SUMMARY OF THE INVENTION The present invention has been made in view of the above problems, the spinel crystalline composite oxide containing Ni and Ga as the main metal element, Ni 1-X
N represented by Ga 2 O 4 (where 0.2 ≦ X <0.6)
It has been found that an i-deficient solid solution has high catalytic activity for a long period of time even in a high oxygen concentration atmosphere and can effectively reduce nitrogen oxides in exhaust gas.
【0011】即ち、本発明の窒素酸化物除去用酸化物触
媒材料は、ニッケル(Ni)とガリウム(Ga)を主た
る金属元素として含有するスピネル型構造の複合酸化物
で、 Ni 1−XGa 2O 4(但し、0.2≦X<0.6) で表されるNi欠損型固溶体から成り、真密度が5.5
54〜5.933g/ccであることを特徴とするもの
である。 That is, the oxide catalyst material for removing nitrogen oxides of the present invention mainly comprises nickel (Ni) and gallium (Ga).
Oxides with spinel structure as metal elements
In, Ni 1-X Ga 2 O 4 ( where, 0.2 ≦ X <0.6) consists Ni deficient solid solution represented by the true density 5.5
54 to 5.933 g / cc
It is.
【0012】更に、本発明の窒素酸化物除去方法は、高
濃度の酸素と、還元性を有する炭素含有ガスが存在する
酸化雰囲気中で、ニッケル(Ni)とガリウム(Ga)
を主たる金属元素として含有するスピネル型構造の複合
酸化物で、 Ni 1−XGa 2O 4(但し、0.2≦X<0.6) で表されるNi欠損型固溶体から成り、真密度が5.5
54〜5.933g/ccである窒素酸化物除去用酸化
物触媒材料を、窒素酸化物を含む排気ガスと接触させる
ことを特徴とする
ものである。Furthermore, the nitrogen oxide removal method of the present invention are
Concentration of oxygen and reducing carbon-containing gas are present
Nickel (Ni) and gallium (Ga) in an oxidizing atmosphere
Of spinel-type structure containing iron as main metal element
The oxide is an Ni-deficient solid solution represented by Ni 1-X Ga 2 O 4 (where 0.2 ≦ X <0.6) and has a true density of 5.5.
Oxidation for removing nitrogen oxides of 54 to 5.933 g / cc
Catalyst material in contact with exhaust gas containing nitrogen oxides
It is characterized by the following.
【0013】[0013]
【作用】本発明の窒素酸化物除去用酸化物触媒材料並び
に窒素酸化物除去方法によれば、本発明の酸化物触媒材
料はNi及びGaを金属元素として含有するスピネル型
結晶性複合酸化物で、Ni欠損型固溶体(Ni/Ga原
子比nが0.20<n≦0.40)であることにより、
主たる結晶相が定比のスピネル型(AB2O4)構造の
NiGa2O4のAサイトからNiの欠損を許容し、こ
れにより金属元素の周囲に生じる電子状態の差により、
窒素酸化物の還元作用で高い特性を示すように作用する
ものと考えられる。According to the oxide catalyst material for removing nitrogen oxides and the method for removing nitrogen oxides of the present invention, the oxide catalyst material of the present invention is a spinel crystalline composite oxide containing Ni and Ga as metal elements. , Ni-deficient solid solution (Ni / Ga atomic ratio n is 0.20 <n ≦ 0.40 ),
The main crystal phase allows the deficiency of Ni from the A site of NiGa 2 O 4 having a stoichiometric spinel type (AB 2 O 4 ) structure.
It is considered that the nitrogen oxide acts to show high characteristics by the reducing action of the nitrogen oxide.
【0014】[0014]
【発明の実施の形態】以下、本発明の窒素酸化物除去用
酸化物触媒材料並びに窒素酸化物除去方法について詳述
する。BEST MODE FOR CARRYING OUT THE INVENTION Hereinafter, an oxide catalyst material for removing nitrogen oxides and a method for removing nitrogen oxides according to the present invention will be described in detail.
【0015】本発明の複合酸化物は、主たる金属元素と
してNi及びGaを含有し、Ni/Ga原子比nが0.
20<n≦0.40の比率から成るNi欠損型のスピネ
ル型複合酸化物であり、Ni1−XGa2O4(但し、
0.2≦X<0.6)の一般式で表されるものである。The composite oxide of the present invention contains Ni and Ga as main metal elements, and has a Ni / Ga atomic ratio n of 0.1.
A Ni-deficient spinel-type composite oxide having a ratio of 20 <n ≦ 0.40 , and Ni 1-X Ga 2 O 4 (provided that
0.2 ≦ X <0.6).
【0016】また、本発明で用いられる複合酸化物は、
前記一般式のX値をNi/Ga原子比nで表記した場
合、Ni/Ga原子比nの値が0.20<n≦0.40
の範囲を逸脱すると触媒活性が低下するため、前記範囲
に特定され、とりわけ窒素酸化物の還元能を考慮すると
n=0.25〜0.40が最も望ましいものである。The composite oxide used in the present invention is:
When the X value of the general formula is represented by the Ni / Ga atomic ratio n, the value of the Ni / Ga atomic ratio n is 0.20 <n ≦ 0.40.
If the value is outside the range, the catalytic activity is reduced. Therefore, the value is specified in the above range, and n = 0.25 to 0.40 is most preferable in consideration of the ability to reduce nitrogen oxides.
【0017】次に、本発明の窒素酸化物除去用酸化物触
媒材料の製造方法について一例を詳述する。Next, an example of the method for producing the oxide catalyst material for removing nitrogen oxides of the present invention will be described in detail.
【0018】本発明の複合酸化物は、Ni及びGaを主
たる金属元素として含有する原料粉末を、Ni/Gaの
原子比nが0.20<n≦0.40となるように秤量
し、十分に撹袢混合した後、酸化雰囲気中、700〜1
200℃の温度で5〜30時間熱処理した後、更に、そ
の降温過程において600〜650℃の温度で10時間
保持することにより、主たる金属元素としてNi及びG
aを含有するスピネル型構造の複合酸化物で、Ni欠損
型の固溶体を主結晶相とする複合酸化物粉末が得られ
る。In the composite oxide of the present invention, a raw material powder containing Ni and Ga as main metal elements is weighed so that the atomic ratio n of Ni / Ga satisfies 0.20 <n ≦ 0.40, and After stirring and mixing in an oxidizing atmosphere,
After heat-treating at a temperature of 200 ° C. for 5 to 30 hours, it is further held at a temperature of 600 to 650 ° C. for 10 hours in the process of lowering the temperature so that Ni and G
A composite oxide powder having a spinel-type structure containing a and having a Ni-deficient solid solution as a main crystal phase can be obtained.
【0019】前記原料粉末としては、例えば、Ni及び
Gaの酸化物や、熱処理により酸化物を生成するそれら
の炭酸塩、硝酸塩、酢酸塩等を用いることができる。As the raw material powder, for example, oxides of Ni and Ga, and their carbonates, nitrates, acetates, etc., which form oxides by heat treatment, can be used.
【0020】また前記複合酸化物は、前記以外に酸化物
や他の金属塩による固相反応法や、金属アルコキシド等
のゾル−ゲル法等によっても合成できるものであり、何
等これら製造方法に限定されるものではない。The composite oxide can be synthesized by a solid-phase reaction method using an oxide or another metal salt, or a sol-gel method such as a metal alkoxide. It is not done.
【0021】前記製造方法において、いずれも熱処理
は、その熱処理温度が700℃より低いと結晶化が不十
分となり、逆に1200℃を越えると緻密化してしまう
ため、酸化雰囲気中、700〜1200℃の温度で5〜
30時間行うが、特に低い温度で熱処理することが粉末
の比表面積を高める上で有効であり、実用的には、比表
面積が35m2/g以上となるように設定することが望
ましい。In any of the above-mentioned manufacturing methods, the crystallization becomes insufficient when the heat treatment temperature is lower than 700.degree. C., whereas the densification occurs when the heat treatment temperature exceeds 1200.degree. At the temperature of 5
Although the heat treatment is performed for 30 hours, heat treatment at a particularly low temperature is effective in increasing the specific surface area of the powder, and practically, it is desirable to set the specific surface area to be 35 m 2 / g or more.
【0022】尚、前記Ni欠損型のスピネル型結晶を主
結晶相とする複合酸化物を得る製造方法では、特に、前
記熱処理中、降温過程で600〜650℃の温度で10
時間程度、保持することが肝要である。In the method for producing a composite oxide having a Ni-deficient spinel type crystal as a main crystal phase, particularly, during the heat treatment, a temperature of 600 to 650.degree.
It is important to hold for about an hour.
【0023】また、本発明のスピネル型複合酸化物は、
窒素酸化物を含有する排気ガスと接触させることによ
り、排気ガス中に含有される酸素濃度が3%以上の高濃
度であっても、その上、水蒸気が存在する雰囲気下であ
っても、広い温度範囲で優れた窒素酸化物の還元性能を
有するものである。Further, the spinel-type composite oxide of the present invention comprises:
By contact with the exhaust gas containing nitrogen oxides, even if the concentration of oxygen contained in the exhaust gas is as high as 3% or more, and even in an atmosphere where water vapor is present, it can be widely used. It has excellent nitrogen oxide reduction performance in the temperature range.
【0024】更に、前記排気ガス雰囲気中に、還元剤と
してC2H4、C3H6、C3H8等の炭化水素、CH
3OH、C2H5OH等のアルコール、CO等の還元性
を有する炭素含有ガス等を混在させて、前記複合酸化物
から成る触媒材料と接触させると、窒素酸化物の還元性
能は更に高くなる。Furthermore, in the exhaust gas atmosphere, hydrocarbons such as C 2 H 4 , C 3 H 6 , C 3 H 8 , CH 3
When an alcohol such as 3 OH and C 2 H 5 OH and a carbon-containing gas having a reducing property such as CO are mixed and brought into contact with the catalyst material comprising the composite oxide, the reducing performance of the nitrogen oxide is further improved. Become.
【0025】[0025]
【実施例】次に、本発明の窒素酸化物除去用酸化物触媒
材料並びに窒素酸化物除去方法について、以下に詳述す
るようにして評価した。EXAMPLES Next, the oxide catalyst material for removing nitrogen oxides and the method for removing nitrogen oxides of the present invention were evaluated as described in detail below.
【0026】先ず、出発原料としてNi(NO3)2・
6H2O、及びGa(NO3)2・9H2Oの試薬を用
い、前記一般式Ni1−XGa2O4(但し、0<X<
0.6)で表した時のXの値を表1に示すように設定
し、具体的にはNi/Gaのモル比を種々設定して秤量
し、これらの試薬を蒸留水中に溶解させ、撹拌しながら
アンモニア水で中和し、この時、生成した沈殿物を濾
過、洗浄し、凍結乾燥させた。First, Ni (NO 3 ) 2.
6H 2 O, and Ga (NO 3) with reagents 2 · 9H 2 O, the formula Ni 1-X Ga 2 O 4 ( where, 0 <X <
0.6) is set as shown in Table 1, specifically, the molar ratio of Ni / Ga is variously set and weighed, and these reagents are dissolved in distilled water. The mixture was neutralized with aqueous ammonia with stirring, and the precipitate formed at this time was filtered, washed, and freeze-dried.
【0027】かくして得られた乾燥粉末を大気中、70
0〜1200℃の範囲内の温度で30時間熱処理した
後、その降温過程で650℃又は600℃の温度で10
時間保持して比表面積が40〜50m2/gのNi欠損
型スピネル型結晶性複合酸化物粉末を得た。The dry powder thus obtained is placed in air at 70
After heat treatment at a temperature within the range of 0 to 1200 ° C. for 30 hours, the temperature is lowered at 650 ° C. or 600 ° C. for 10 hours.
After holding for a time, a Ni-deficient spinel-type crystalline composite oxide powder having a specific surface area of 40 to 50 m 2 / g was obtained.
【0028】次いで、前記スピネル型複合酸化物粉末を
金型プレスにより成形し、更に冷間静水圧成形法により
圧縮してから該成形物を解砕して篩別し、500μmを
越え、700μm以下に整粒して評価用試料を調製し
た。Next, the spinel-type composite oxide powder is molded by a mold press, and further compressed by a cold isostatic pressing method, and then the molded product is crushed and sieved, and exceeds 500 μm to 700 μm or less. To prepare an evaluation sample.
【0029】尚、前記降温過程で所定温度、時間の保持
処理を施さないで作製した複合酸化物を比較例とした。A composite oxide prepared without performing a holding treatment at a predetermined temperature and for a predetermined time in the temperature decreasing process was used as a comparative example.
【0030】かくして得られた評価用試料の粉末を用い
てX線回折測定(XRD)により結晶相を同定し、該結
晶相がスピネル結晶から成ることを確認した。Using the powder of the evaluation sample thus obtained, a crystal phase was identified by X-ray diffraction measurement (XRD), and it was confirmed that the crystal phase consisted of spinel crystals.
【0031】また、前記評価用試料の真密度と表面積を
それぞれガス置換法とBET法により測定し、前記ガス
置換法では純度99.999%のHeガスを使用して9
回測定した結果を平均し、標準サンプルにAl2O3を
測定して校正するとともに、BET法では、吸着ガスに
液体窒素を用いて吸着量を測定することにより表面積を
決定した。Further, the true density and the surface area of the evaluation sample were measured by a gas replacement method and a BET method, respectively, and the gas replacement method was performed by using He gas having a purity of 99.999%.
The measurement results were averaged, Al 2 O 3 was measured as a standard sample, and calibration was performed. In the BET method, the surface area was determined by measuring the amount of adsorption using liquid nitrogen as the adsorption gas.
【0032】一方、模擬排気ガスには窒素酸化物として
NOを用い、該NOが1000ppm、O2が10%、
C3H6が666ppm、残部がHeから成る反応ガス
を、該反応ガスと触媒材料が接触する条件として、空間
速度(SV)を200000/hr.に設定して前記評
価用試料を充填した触媒層に流し、300〜500℃の
温度範囲で触媒層を通過して生成したN2ガスをガスク
ロマトグラフで測定した。On the other hand, NO was used as a nitrogen oxide in the simulated exhaust gas, the NO being 1000 ppm, the O 2 being 10%,
A reaction gas consisting of 666 ppm of C 3 H 6 and the balance of He was used as a condition for contacting the reaction gas with the catalyst material, and a space velocity (SV) of 200,000 / hr. Was passed through the catalyst layer filled with the evaluation sample, and the N 2 gas generated by passing through the catalyst layer in a temperature range of 300 to 500 ° C. was measured by gas chromatography.
【0033】触媒のNO還元分解能は、触媒層出口側の
N2濃度(ppm)の2倍の値を、触媒層入口側のNO
濃度(ppm)で除した百分率をNO還元率(%)と
し、450℃におけるNO還元率を求めて窒素酸化物還
元活性として評価した。The NO reduction ability of the catalyst is determined to be twice the value of the N 2 concentration (ppm) at the catalyst layer outlet side, and to the NO at the catalyst layer inlet side.
The percentage divided by the concentration (ppm) was defined as the NO reduction rate (%), and the NO reduction rate at 450 ° C. was obtained and evaluated as the nitrogen oxide reduction activity.
【0034】[0034]
【表1】 [Table 1]
【0035】また、表1の結果に基づき、本発明に係る
評価用試料のNi/Ga原子比と真密度の関係を図1に
示した。FIG. 1 shows the relationship between the Ni / Ga atomic ratio and the true density of the evaluation sample according to the present invention based on the results shown in Table 1.
【0036】図1から分かるように、Ni/Ga原子比
と真密度は直線的な関係が得られており、スピネル量論
組成のNi/Ga原子比が0.50の時、前記関係の延
長線上の理論密度が6.175g/ccの点を通ること
から、本発明に係る評価用試料は、スピネル型(AB2
O3)構造のNiGa2O4のAサイトからNiの欠損
を許容したNi欠損型固溶体であることが分かる。As can be seen from FIG. 1, a linear relationship is obtained between the atomic ratio of Ni / Ga and the true density. When the atomic ratio of Ni / Ga in the stoichiometric spinel composition is 0.50, the relationship is extended. Since the theoretical density on the line passes through a point of 6.175 g / cc, the evaluation sample according to the present invention has a spinel type (AB 2
From the A site of NiGa 2 O 4 having an O 3 ) structure, it can be seen that the Ni solution is a Ni-deficient solid solution that allows Ni deficiency.
【0037】一方、表から明らかなように、比較例であ
る試料番号12、14は、NO還元率が著しく低く、ま
た、本発明の請求範囲外である試料番号1、2、3、
9、10、11、13、でもNO還元率が低く、実用的
でないことが明らかとなった。On the other hand, as is clear from the table, Sample Nos. 12 and 14, which are comparative examples, have remarkably low NO reduction rates, and Sample Nos. 1, 2, 3, and 4 which are outside the scope of the present invention .
Even in 9, 10, 11, and 13, it became clear that the NO reduction rate was low and not practical.
【0038】それに対して、0.2≦X<0.6、真密
度が5.554〜5.933g/cc、比表面積が45
m 2 /g以上である本発明ではいずれも450℃で49
%以上と十分なNO還元率を示していることが分かる。[0038] On the other hand, 0.2 ≦ X <0.6, true tight
The degree is 5.554-5.933 g / cc and the specific surface area is 45.
m 2 / g is more than 49 at 450 ° C. Both the present invention
% Or more, which indicates a sufficient NO reduction rate.
【0039】また、本発明の前記評価用試料は、いずれ
もSV値が300000/hr.まで、酸素濃度は15
%まで、前記評価特性の著しい低下はなく、一方、35
0℃の温度で連続して100時間、前記模擬排気ガスと
接触させて反応させた後においても前記評価特性に大き
な変化は認められなかった。The samples for evaluation of the present invention all have an SV value of 300,000 / hr. Until the oxygen concentration is 15
%, There is no significant decrease in the evaluation characteristics, while 35
No significant change was observed in the evaluation characteristics even after contacting with the simulated exhaust gas for a reaction at a temperature of 0 ° C. for 100 hours for 100 hours.
【0040】更に、前記評価用試料を4気筒のディーゼ
ルエンジン台上試験装置の排気管に取り付け、該ディー
ゼルエンジンを最高回転数、全負荷の条件で100時間
運転する耐久試験を実施し、試験後の評価用試料につい
て前記同様にして窒素酸化物の還元活性を評価したが、
NO還元率はほとんど低下していないことが確認でき、
耐水性、耐熱性ともに優れていることが証明された。Further, the evaluation sample was attached to an exhaust pipe of a 4-cylinder diesel engine bench test apparatus, and a durability test was performed in which the diesel engine was operated at the maximum rotation speed and full load for 100 hours. The evaluation sample was evaluated for nitrogen oxide reduction activity in the same manner as described above.
It can be confirmed that the NO reduction rate has hardly decreased,
It was proved that both water resistance and heat resistance were excellent.
【0041】[0041]
【発明の効果】以上、詳述したように本発明の窒素酸化
物除去用酸化物触媒材料並びに窒素酸化物除去方法によ
れば、該酸化物触媒材料はニッケル(Ni)とガリウム
(Ga)を主たる金属元素として含有するスピネル型結
晶性複合酸化物で、Ni1−XGa2O4(但し、0.
2≦X<0.6)で表されるNi欠損型固溶体から成
り、真密度が5.554〜5.933g/ccであるも
ので、高濃度の酸素と還元性を有する炭素含有ガスが存
在する酸化雰囲気中で前記酸化物触媒材料と窒素酸化物
を含有する排気ガスを接触させることから、水蒸気が存
在する雰囲気は勿論、排気ガス中の酸素濃度が3%以上
の高酸素濃度雰囲気下であっても、その上、ガスの流速
が高速度であっても、優れた窒素酸化物の還元性能を有
し、排気ガス中に含有される窒素酸化物を有効に還元す
ることができる。As described above, according to the oxide catalyst material for removing nitrogen oxides and the method for removing nitrogen oxides of the present invention, the oxide catalyst material contains nickel (Ni) and gallium (Ga). in spinel crystalline composite oxide containing as a main metal element, Ni 1-X Ga 2 O 4 ( where 0.
From Ni-deficient solid solution represented by 2 ≦ X <0.6) formed
And the true density is 5.554 to 5.933 g / cc, so that the oxide catalyst material and the nitrogen oxide are mixed in an oxidizing atmosphere in which a high concentration of oxygen and a carbon-containing gas having a reducing property are present. Since the exhaust gas containing substances is brought into contact with the exhaust gas, not only in an atmosphere in which water vapor is present but also in a high oxygen concentration atmosphere in which the oxygen concentration in the exhaust gas is 3% or more, the gas flow rate is high. Even so, it has excellent nitrogen oxide reduction performance, and can effectively reduce nitrogen oxides contained in exhaust gas.
【0042】その結果、省エネルギー、省資源及び地球
温暖化防止を目標として開発される今後のディーゼルエ
ンジンやリーンバーンエンジン等の各種内燃機関の排気
ガスをはじめ、窒素酸化物を含有する各種有害物質の浄
化に極めて有用なものとなる。As a result, various types of harmful substances containing nitrogen oxides, including exhaust gas from various internal combustion engines such as diesel engines and lean burn engines, which will be developed with the aim of saving energy and resources and preventing global warming, are developed. It will be very useful for purification.
【図1】本発明の窒素酸化物除去用酸化物触媒材料のN
i/Ga原子比と真密度の関係図である。FIG. 1 shows N of an oxide catalyst material for removing nitrogen oxides according to the present invention.
FIG. 4 is a diagram illustrating a relationship between an i / Ga atomic ratio and a true density.
フロントページの続き (56)参考文献 特開 平7−265703(JP,A) 特開 平8−24650(JP,A) 特開 平8−150338(JP,A) 特開 平8−1002(JP,A) 特開 平9−225267(JP,A) (58)調査した分野(Int.Cl.7,DB名) B01J 21/00 - 38/74 B01D 53/86,53/94 Continuation of the front page (56) References JP-A-7-265703 (JP, A) JP-A-8-24650 (JP, A) JP-A 8-150338 (JP, A) JP-A 8-10002 (JP) , A) JP-A-9-225267 (JP, A) (58) Fields investigated (Int. Cl. 7 , DB name) B01J 21/00-38/74 B01D 53/86, 53/94
Claims (2)
たる金属元素として含有するスピネル型構造の複合酸化
物で、 Ni1−XGa2O4(但し、0.2≦X<0.6) で表されるNi欠損型固溶体から成り、真密度が5.5
54〜5.673g/cc、比表面積が45m 2 /g以
上であることを特徴とする窒素酸化物除去用酸化物触媒
材料。1. A composite oxide having a spinel structure containing nickel (Ni) and gallium (Ga) as main metal elements, wherein Ni 1-X Ga 2 O 4 (where 0.2 ≦ X <0.6) ) Ri consists Ni deficient solid solution represented by the true density 5.5
54 to 5.673 g / cc, specific surface area of 45 m 2 / g or less
An oxide catalyst material for removing nitrogen oxides, which is characterized by the above .
ガスが存在する酸化雰囲気中で、ニッケル(Ni)とガ
リウム(Ga)を主たる金属元素として含有するスピネ
ル型構造の複合酸化物で、 Ni1−XGa2O4(但し、0.2≦X<0.6) で表されるNi欠損型固溶体から成り、真密度が5.5
54〜5.673g/ccである窒素酸化物除去用酸化
物触媒材料を、窒素酸化物を含む排気ガスと接触させる
ことを特徴とする窒素酸化物除去方法。2. A composite oxide having a spinel structure containing nickel (Ni) and gallium (Ga) as main metal elements in an oxidizing atmosphere in which a high concentration of oxygen and a carbon-containing gas having a reducing property are present. , Ni 1-X Ga 2 O 4 ( where, 0.2 ≦ X <0.6) Ri consists Ni deficient solid solution represented by the true density 5.5
A method for removing nitrogen oxides, comprising contacting an oxide catalyst material for removing nitrogen oxides of 54 to 5.673 g / cc with an exhaust gas containing nitrogen oxides.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP29039396A JP3532044B2 (en) | 1996-10-31 | 1996-10-31 | Oxide catalyst material for removing nitrogen oxides and method for removing nitrogen oxides |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP29039396A JP3532044B2 (en) | 1996-10-31 | 1996-10-31 | Oxide catalyst material for removing nitrogen oxides and method for removing nitrogen oxides |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH10128119A JPH10128119A (en) | 1998-05-19 |
JP3532044B2 true JP3532044B2 (en) | 2004-05-31 |
Family
ID=17755437
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP29039396A Expired - Fee Related JP3532044B2 (en) | 1996-10-31 | 1996-10-31 | Oxide catalyst material for removing nitrogen oxides and method for removing nitrogen oxides |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP3532044B2 (en) |
Families Citing this family (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109216047B (en) * | 2017-07-03 | 2020-11-06 | 澳门大学 | Electrochemical electrode, preparation method thereof and supercapacitor |
-
1996
- 1996-10-31 JP JP29039396A patent/JP3532044B2/en not_active Expired - Fee Related
Also Published As
Publication number | Publication date |
---|---|
JPH10128119A (en) | 1998-05-19 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
JP5526410B2 (en) | Method for removing nitrogen oxides in exhaust gas | |
BR112017028424B1 (en) | NITROUS OXIDE REMOVAL CATALYST COMPOSITE, EMISSION TREATMENT SYSTEM, AND, METHOD TO TREAT EXHAUST GASES | |
JPH07155614A (en) | Production of exhaust gas purifying catalyst | |
WO2007122917A1 (en) | Exhaust gas purifying catalyst and method for producing same | |
WO2005084796A1 (en) | Exhaust gas purifying catalyst, metal oxide particle and production process thereof | |
JP3532044B2 (en) | Oxide catalyst material for removing nitrogen oxides and method for removing nitrogen oxides | |
JP2851773B2 (en) | Oxide catalyst material for removing nitrogen oxides and method for removing nitrogen oxides | |
JP3199562B2 (en) | Oxide catalyst material for removing nitrogen oxides and method for removing nitrogen oxides | |
JP3346665B2 (en) | Oxide catalyst material for removing nitrogen oxides and method for removing nitrogen oxides | |
JPH0859236A (en) | Highly heat-resistant copper-alumina double oxide and cleaning method of exhaust gas | |
JP3346653B2 (en) | Oxide catalyst material for removing nitrogen oxides and method for removing nitrogen oxides | |
JP3309024B2 (en) | Oxide catalyst material for removing nitrogen oxides and method for removing nitrogen oxides | |
JPH09141102A (en) | Oxide catalyst material for removing nitrogen oxide and removal of nitrogen oxide | |
JP3199561B2 (en) | Oxide catalyst material for removing nitrogen oxides and method for removing nitrogen oxides | |
JP3298133B2 (en) | Method for producing zeolite containing cobalt and palladium and method for purifying exhaust gas | |
JPH10180105A (en) | Oxide catalyst material for removing nitrogen oxide and method for removing nitrogen oxide | |
JPH0975733A (en) | Oxide catalytic material for removal of nox and method for removing nox | |
JPH10180103A (en) | Oxide catalyst material for removing nitrogen oxide and its preparation | |
JP2851769B2 (en) | Oxide catalyst material for removing nitrogen oxides and method for removing nitrogen oxides | |
JP2922759B2 (en) | Oxide catalyst material for removing nitrogen oxides and method for removing nitrogen oxides | |
JPH09313941A (en) | Oxide catalyst material for removing nitrogen oxide and removal of nitrogen oxide | |
JP3221706B2 (en) | Nitrogen oxide removal catalyst and exhaust gas purification method using the same | |
JPH09141103A (en) | Oxide catalyst material for removing nitrogen oxide and removal of nitrogen oxide | |
JPH08323204A (en) | Oxide catalyst material and method for removing nitrogen oxide | |
JPH0524907A (en) | Phosphoric acid-based composition and catalyst for reduction cracking of nox using this composition |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
TRDD | Decision of grant or rejection written | ||
A01 | Written decision to grant a patent or to grant a registration (utility model) |
Free format text: JAPANESE INTERMEDIATE CODE: A01 Effective date: 20040224 |
|
A61 | First payment of annual fees (during grant procedure) |
Free format text: JAPANESE INTERMEDIATE CODE: A61 Effective date: 20040302 |
|
R150 | Certificate of patent or registration of utility model |
Free format text: JAPANESE INTERMEDIATE CODE: R150 |
|
FPAY | Renewal fee payment (event date is renewal date of database) |
Free format text: PAYMENT UNTIL: 20090312 Year of fee payment: 5 |
|
LAPS | Cancellation because of no payment of annual fees |