JPH07213906A - Exhaust gas purifying catalyst - Google Patents
Exhaust gas purifying catalystInfo
- Publication number
- JPH07213906A JPH07213906A JP6031828A JP3182894A JPH07213906A JP H07213906 A JPH07213906 A JP H07213906A JP 6031828 A JP6031828 A JP 6031828A JP 3182894 A JP3182894 A JP 3182894A JP H07213906 A JPH07213906 A JP H07213906A
- Authority
- JP
- Japan
- Prior art keywords
- catalyst
- exhaust gas
- atmosphere
- nitrogen oxides
- transition metal
- 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.)
- Pending
Links
- 239000003054 catalyst Substances 0.000 title claims abstract description 55
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 claims abstract description 46
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims abstract description 24
- 229910002091 carbon monoxide Inorganic materials 0.000 claims abstract description 24
- 229930195733 hydrocarbon Natural products 0.000 claims abstract description 19
- 150000002430 hydrocarbons Chemical class 0.000 claims abstract description 19
- 239000007789 gas Substances 0.000 claims abstract description 15
- 229910000314 transition metal oxide Inorganic materials 0.000 claims abstract description 10
- 229910000510 noble metal Inorganic materials 0.000 claims description 18
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 abstract description 14
- 239000001301 oxygen Substances 0.000 abstract description 14
- 229910052760 oxygen Inorganic materials 0.000 abstract description 14
- 238000002485 combustion reaction Methods 0.000 abstract description 6
- 239000003208 petroleum Substances 0.000 abstract description 2
- 239000010970 precious metal Substances 0.000 abstract description 2
- BASFCYQUMIYNBI-UHFFFAOYSA-N platinum Chemical compound [Pt] BASFCYQUMIYNBI-UHFFFAOYSA-N 0.000 description 23
- 229910052697 platinum Inorganic materials 0.000 description 12
- 238000000746 purification Methods 0.000 description 12
- 229910020599 Co 3 O 4 Inorganic materials 0.000 description 10
- 230000000052 comparative effect Effects 0.000 description 9
- 238000000034 method Methods 0.000 description 9
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 description 6
- 239000007864 aqueous solution Substances 0.000 description 6
- UFMZWBIQTDUYBN-UHFFFAOYSA-N cobalt dinitrate Chemical compound [Co+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O UFMZWBIQTDUYBN-UHFFFAOYSA-N 0.000 description 6
- 229910001981 cobalt nitrate Inorganic materials 0.000 description 6
- GPNDARIEYHPYAY-UHFFFAOYSA-N palladium(ii) nitrate Chemical compound [Pd+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O GPNDARIEYHPYAY-UHFFFAOYSA-N 0.000 description 6
- 229910052723 transition metal Inorganic materials 0.000 description 6
- KDLHZDBZIXYQEI-UHFFFAOYSA-N Palladium Chemical compound [Pd] KDLHZDBZIXYQEI-UHFFFAOYSA-N 0.000 description 5
- 230000000694 effects Effects 0.000 description 5
- 238000007254 oxidation reaction Methods 0.000 description 5
- 150000003839 salts Chemical class 0.000 description 5
- 150000003624 transition metals Chemical class 0.000 description 5
- 229910052751 metal Inorganic materials 0.000 description 4
- 239000002184 metal Substances 0.000 description 4
- 230000003647 oxidation Effects 0.000 description 4
- 239000000843 powder Substances 0.000 description 4
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 4
- 229910018072 Al 2 O 3 Inorganic materials 0.000 description 3
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 description 3
- 238000006722 reduction reaction Methods 0.000 description 3
- 229910000029 sodium carbonate Inorganic materials 0.000 description 3
- 239000000243 solution Substances 0.000 description 3
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 2
- GWEVSGVZZGPLCZ-UHFFFAOYSA-N Titan oxide Chemical compound O=[Ti]=O GWEVSGVZZGPLCZ-UHFFFAOYSA-N 0.000 description 2
- MCMNRKCIXSYSNV-UHFFFAOYSA-N Zirconium dioxide Chemical compound O=[Zr]=O MCMNRKCIXSYSNV-UHFFFAOYSA-N 0.000 description 2
- 238000011156 evaluation Methods 0.000 description 2
- 239000000446 fuel Substances 0.000 description 2
- VCJMYUPGQJHHFU-UHFFFAOYSA-N iron(3+);trinitrate Chemical compound [Fe+3].[O-][N+]([O-])=O.[O-][N+]([O-])=O.[O-][N+]([O-])=O VCJMYUPGQJHHFU-UHFFFAOYSA-N 0.000 description 2
- 229910052763 palladium Inorganic materials 0.000 description 2
- 239000008188 pellet Substances 0.000 description 2
- 239000010948 rhodium Substances 0.000 description 2
- ATRRKUHOCOJYRX-UHFFFAOYSA-N Ammonium bicarbonate Chemical compound [NH4+].OC([O-])=O ATRRKUHOCOJYRX-UHFFFAOYSA-N 0.000 description 1
- 101100433727 Caenorhabditis elegans got-1.2 gene Proteins 0.000 description 1
- 239000004215 Carbon black (E152) Substances 0.000 description 1
- 229910021503 Cobalt(II) hydroxide Inorganic materials 0.000 description 1
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 description 1
- 101100489867 Mus musculus Got2 gene Proteins 0.000 description 1
- 229910002651 NO3 Inorganic materials 0.000 description 1
- NHNBFGGVMKEFGY-UHFFFAOYSA-N Nitrate Chemical compound [O-][N+]([O-])=O NHNBFGGVMKEFGY-UHFFFAOYSA-N 0.000 description 1
- 229910021536 Zeolite Inorganic materials 0.000 description 1
- 239000001099 ammonium carbonate Substances 0.000 description 1
- 235000012501 ammonium carbonate Nutrition 0.000 description 1
- 239000011230 binding agent Substances 0.000 description 1
- 238000001354 calcination Methods 0.000 description 1
- 239000001569 carbon dioxide Substances 0.000 description 1
- 229910002092 carbon dioxide Inorganic materials 0.000 description 1
- 230000003197 catalytic effect Effects 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 229940011182 cobalt acetate Drugs 0.000 description 1
- UBEWDCMIDFGDOO-UHFFFAOYSA-N cobalt(2+);cobalt(3+);oxygen(2-) Chemical compound [O-2].[O-2].[O-2].[O-2].[Co+2].[Co+3].[Co+3] UBEWDCMIDFGDOO-UHFFFAOYSA-N 0.000 description 1
- QAHREYKOYSIQPH-UHFFFAOYSA-L cobalt(II) acetate Chemical compound [Co+2].CC([O-])=O.CC([O-])=O QAHREYKOYSIQPH-UHFFFAOYSA-L 0.000 description 1
- ASKVAEGIVYSGNY-UHFFFAOYSA-L cobalt(ii) hydroxide Chemical compound [OH-].[OH-].[Co+2] ASKVAEGIVYSGNY-UHFFFAOYSA-L 0.000 description 1
- 229910052802 copper Inorganic materials 0.000 description 1
- 239000010949 copper Substances 0.000 description 1
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 description 1
- 238000002474 experimental method Methods 0.000 description 1
- 238000010304 firing Methods 0.000 description 1
- 230000003301 hydrolyzing effect Effects 0.000 description 1
- 238000005342 ion exchange Methods 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- 238000005259 measurement Methods 0.000 description 1
- 229910001510 metal chloride Inorganic materials 0.000 description 1
- 239000011259 mixed solution Substances 0.000 description 1
- KBJMLQFLOWQJNF-UHFFFAOYSA-N nickel(ii) nitrate Chemical compound [Ni+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O KBJMLQFLOWQJNF-UHFFFAOYSA-N 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 238000011160 research Methods 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
- 230000000630 rising effect Effects 0.000 description 1
- RMAQACBXLXPBSY-UHFFFAOYSA-N silicic acid Chemical compound O[Si](O)(O)O RMAQACBXLXPBSY-UHFFFAOYSA-N 0.000 description 1
- 239000002002 slurry Substances 0.000 description 1
- 239000006104 solid solution Substances 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 239000000758 substrate Substances 0.000 description 1
- 230000009897 systematic effect Effects 0.000 description 1
- -1 transition metal salt Chemical class 0.000 description 1
- 239000010457 zeolite Substances 0.000 description 1
Landscapes
- Exhaust Gas Treatment By Means Of Catalyst (AREA)
- Catalysts (AREA)
Abstract
(57)【要約】
【目的】 本発明は、自動車等の内燃機関、石油ストー
ブあるいは工場等から排出される窒素酸化物を酸素過剰
の雰囲気下において300℃〜600℃の広い温度範囲
において効率良く除去することができる触媒を提供す
る。
【構成】 酸素過剰の雰囲気において排気ガス中の炭化
水素、一酸化炭素および窒素酸化物を浄化するための触
媒であって、多孔質担体と、この多孔質担体に担持した
遷移金属酸化物から選択さた1種以上と貴金属から選択
された1種以上とからなることを特徴とする。(57) [Abstract] [Purpose] The present invention efficiently makes nitrogen oxides discharged from an internal combustion engine such as an automobile, a petroleum stove, or a factory in a wide temperature range of 300 ° C to 600 ° C in an atmosphere of excess oxygen. Provided is a catalyst that can be removed. [Composition] A catalyst for purifying hydrocarbons, carbon monoxide and nitrogen oxides in exhaust gas in an atmosphere of excess oxygen, which is selected from a porous carrier and a transition metal oxide supported on the porous carrier. It is characterized in that it is composed of one or more kinds and one or more kinds selected from precious metals.
Description
【0001】[0001]
【産業上の利用分野】本発明は自動車等の内燃機関、石
油ストーブあるいは工場等から排出される炭化水素(C
H)、一酸化炭素(CO)および窒素酸化物(NOx)
を酸素過剰の雰囲気下において300℃〜600℃の広
い温度範囲において効率良く除去する触媒に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to hydrocarbons (C) discharged from internal combustion engines such as automobiles, oil stoves or factories.
H), carbon monoxide (CO) and nitrogen oxides (NO x ).
The present invention relates to a catalyst that efficiently removes R in a wide temperature range of 300 ° C to 600 ° C in an atmosphere of excess oxygen.
【0002】[0002]
【従来技術】最近、自然環境の維持が特に重視されつつ
あり、自動車等の排気ガスの規制が強化される傾向にあ
る。そこで燃焼排気ガス中の炭化水素(HC)、一酸化
炭素(CO)等の発生を抑制するための一手段として酸
素過剰の雰囲気下において希薄燃焼させるリーンバーン
エンジンが有望視されている。このリーンバーンは燃費
が向上するため燃料の使用量が低減され、その結果排気
ガス中の二酸化炭素(CO2 )等の発生を抑制させるこ
とができる。しかし、前記リーンバーンエンジンから排
出される酸素過剰の排気ガス中には窒素酸化物(NOx)
が多量に含有されている。そこで酸素過剰の雰囲気下
において窒素酸化物(NOx) を充分に還元浄化できる
触媒の開発が広範囲に実施されている。2. Description of the Related Art Recently, the importance of maintaining the natural environment has been particularly emphasized, and the regulation of exhaust gas from automobiles has tended to be tightened. Therefore, a lean burn engine that burns lean in an oxygen-rich atmosphere is regarded as promising as one means for suppressing the generation of hydrocarbons (HC), carbon monoxide (CO), etc. in the combustion exhaust gas. Since the lean burn improves fuel consumption, the amount of fuel used is reduced, and as a result, generation of carbon dioxide (CO 2 ) and the like in exhaust gas can be suppressed. However, nitrogen oxides (NO x ) are present in the oxygen-excessive exhaust gas discharged from the lean burn engine.
Is contained in a large amount. Therefore, a catalyst capable of sufficiently reducing and purifying nitrogen oxides (NO x ) under an atmosphere of excess oxygen has been extensively developed.
【0003】このような触媒として銅等の遷移金属を
イオン交換によりゼオライトに担持した触媒(特開平1
ー139145号公報)、白金等の貴金属をアルミナ
等の多孔質担体に担持した触媒(特開平5ー16886
0号公報)がある。As such a catalyst, a catalyst in which a transition metal such as copper is supported on zeolite by ion exchange (JP-A-1
No. 139145), a catalyst in which a noble metal such as platinum is supported on a porous carrier such as alumina (Japanese Patent Laid-Open No. 16886/1993).
No. 0).
【0004】[0004]
【発明が解決しょうとする課題】しかし、の触媒は、
耐久性が劣っているという問題がある。また、の触媒
では、窒素酸化物浄化開始温度が200℃と低く、かつ
窒素酸化物を充分に浄化し得る温度域が250〜350
℃と狭いため、特に自動車の内燃機関から排出される排
気ガス中の窒素酸化物の浄化には適していない。[Problems to be Solved by the Invention] However, the catalyst of
There is a problem of poor durability. In addition, in the catalyst of 1, the nitrogen oxide purification start temperature is as low as 200 ° C., and the temperature range in which the nitrogen oxides can be sufficiently purified is 250 to 350.
Since it is as low as ℃, it is not suitable for purifying nitrogen oxides in exhaust gas discharged from internal combustion engines of automobiles.
【0005】本発明者等は上記問題点を解決すべく研究
し各種の系統的実験を重ね、本発明をなすに至ったもの
である。本発明者等は従来酸化触媒として使用されてき
た酸化コバルト(Co3 O4 )および白金に着目した。
リーンバーンエンジンから排出される排気ガス中には酸
素が過剰に存在するため前記酸化触媒を使用した場合に
は酸化反応が一層進行し、酸化触媒の使用によって窒素
酸化物(NOx) を還元し得るとは当業者は考えないの
が常識であった。本発明者等は、酸素過剰の雰囲気下に
おいてあえて前記酸化触媒を使用し、窒素酸化物(NO
x) を選択的に還元し得ることを見出し本発明をなした
のである。The present inventors have conducted research to solve the above-mentioned problems and conducted various systematic experiments to complete the present invention. The present inventors have focused on cobalt oxide (Co 3 O 4 ) and platinum, which have been conventionally used as oxidation catalysts.
Oxygen is excessively present in the exhaust gas discharged from the lean burn engine, so that when the above-mentioned oxidation catalyst is used, the oxidation reaction further progresses, and the use of the oxidation catalyst reduces nitrogen oxides (NO x ). It was common sense that a person skilled in the art would not obtain it. The inventors of the present invention dare to use the above-mentioned oxidation catalyst in an atmosphere of excess oxygen to remove nitrogen oxide (NO
The present invention has been made based on the finding that x ) can be selectively reduced.
【0006】本発明は自動車等の内燃機関、石油ストー
ブあるいは工場等から排出される炭化水素、一酸化炭素
および窒素酸化物を酸素過剰の雰囲気下において300
℃〜600℃の広い温度範囲において効率良く除去する
ことができる触媒を提供することを目的とする。[0006] The present invention is designed to remove hydrocarbons, carbon monoxide and nitrogen oxides discharged from internal combustion engines such as automobiles, petroleum stoves or factories in an atmosphere of excess oxygen.
An object of the present invention is to provide a catalyst that can be efficiently removed in a wide temperature range of ℃ to 600 ℃.
【0007】[0007]
【課題を解決するための手段】本発明の排気ガス浄化用
触媒は、酸素過剰の雰囲気において排気ガス中の炭化水
素、一酸化炭素および窒素酸化物を浄化するための触媒
であって、多孔質担体と、この多孔質担体に担持した遷
移金属酸化物の1種以上と貴金属の1種以上とからな
る。The exhaust gas purifying catalyst of the present invention is a catalyst for purifying hydrocarbons, carbon monoxide and nitrogen oxides in exhaust gas in an oxygen-excess atmosphere, and is porous. It comprises a carrier and one or more kinds of transition metal oxides and one or more kinds of noble metals supported on the porous carrier.
【0008】[0008]
【作用】本触媒によれば酸素過剰の雰囲気中、300〜
600℃という広い温度域において炭化水素(HC)、
一酸化炭素(CO)および窒素酸化物(NOx )を効率
良く浄化できる。特に従来の触媒では充分に浄化できな
かったNOx の浄化を可能とした。[Function] According to the present catalyst, in an atmosphere of excess oxygen,
Hydrocarbon (HC) in a wide temperature range of 600 ° C,
Carbon monoxide (CO) and nitrogen oxides (NO x ) can be efficiently purified. In particular, it has made it possible to purify NO x , which could not be sufficiently purified by the conventional catalyst.
【0009】本触媒のかかる作用は明確ではないが以下
のように考えられる。従来の三元触媒は排気ガス中の有
害成分であるHC、CO、NOx を貴金属上に吸着し、
以下に示すような反応によって除去するものである。 CO + 1/2O2 → CO2 …… NO + H2 → 1/2N2 +H2 O …… NO + CO → CO2 +1/2N2 …… Cn Hm +(n+m/4)O2 → nCO2 +m/2H2 O ……Although the action of the catalyst is not clear, it is considered as follows. A conventional three-way catalyst adsorbs HC, CO, and NO x , which are harmful components in exhaust gas, on a precious metal,
It is removed by the reaction shown below. CO + 1 / 2O 2 → CO 2 …… NO + H 2 → 1 / 2N 2 + H 2 O …… NO + CO → CO 2 + 1 / 2N 2 …… C n H m + (n + m / 4) O 2 → nCO 2 + m / 2H 2 O ...
【0010】本発明の触媒は、従来の三元触媒とは異な
り、NOx をCOおよびH2 以外に式のごとくHCと
反応させN2 にまで還元する作用があり、また、このN
Ox還元反応を酸素過剰のリーン雰囲気(A/F>1
4.6、好ましくは17≦A/F≦23)において進行
せしめる作用を有している点に特徴がある。 (2 n+m/2 )NO + Cn Hm → (n+m/4 )N2 +nCO2 +m/2 H2 O ……Unlike the conventional three-way catalyst, the catalyst of the present invention has an action of reacting NO x with HC in addition to CO and H 2 as shown in the formula to reduce it to N 2.
Ox reduction reaction was performed in a lean atmosphere with excess oxygen (A / F> 1).
It is characterized in that it has an action of advancing at 4.6, preferably 17 ≦ A / F ≦ 23). (2 n + m / 2) NO + C n H m → (n + m / 4) N 2 + nCO 2 + m / 2 H 2 O ......
【0011】さらに、前記NOx 還元反応は貴金属単独
あるいは遷移金属単独では起こらず貴金属と遷移金属と
が共存してはじめて現出するものである。したがって、
貴金属と遷移金属とが相互作用を及ぼし合うように多く
の界面が存在することが望ましい。Further, the NO x reduction reaction does not occur with the noble metal alone or the transition metal alone, and appears only when the noble metal and the transition metal coexist. Therefore,
It is desirable that there are many interfaces so that the noble metal and the transition metal interact with each other.
【0012】[0012]
【発明の効果】本発明の排気ガス浄化用触媒によれば、
自動車等の内燃機関、石油ストーブあるいは工場等から
排出される炭化水素(HC)、一酸化炭素(CO)およ
び窒素酸化物(NOx) を酸素過剰の雰囲気下において
300℃〜600℃の広い温度範囲において効率良く除
去することができる。According to the exhaust gas purifying catalyst of the present invention,
Hydrocarbons (HC), carbon monoxide (CO), and nitrogen oxides (NO x ) emitted from internal combustion engines such as automobiles, oil stoves, or factories, etc., in a wide temperature range of 300 ° C to 600 ° C in an atmosphere of excess oxygen It can be removed efficiently in the range.
【0013】(その他の発明の説明)本発明において使
用する遷移金属酸化物は、Co3O4、NiO、Fe
2 O3 、Cr2 O3 、Mn2 O3 等が挙げられるが、こ
れらは例示にすぎない。これらの1種以上を用いる。遷
移金属酸化物の大きさは2000Å以下、また、比表面
積は0.2〜200m2 /gで用いる。この範囲を超え
ると良好な浄化活性を発揮できない。望ましくは100
Å以下、50m2 /g〜200m2 /gが良い。(Description of Other Inventions) The transition metal oxide used in the present invention is Co 3 O 4, NiO, Fe.
2 O 3 , Cr 2 O 3 , Mn 2 O 3 and the like can be mentioned, but these are merely examples. One or more of these are used. The size of the transition metal oxide is 2000 Å or less, and the specific surface area is 0.2 to 200 m 2 / g. If it exceeds this range, good purification activity cannot be exhibited. Preferably 100
Å below, 50m 2 / g~200m 2 / g is good.
【0014】貴金属はロジウム(Rh)、白金(P
t)、パラジウム(Pd)の1種以上を用いる。貴金属
の量は遷移金属酸化物の金属成分に対し2〜20at%
とする。2at%以下だと浄化活性が発揮されず、逆に
20at%以上だと貴金属の量が多すぎて互いに凝集し
てしまい活性が低下することになる。望ましくは2〜1
0at%が良い。貴金属の粒径は500Å以下とするの
が望ましい。Noble metals are rhodium (Rh), platinum (P
One or more of t) and palladium (Pd) are used. The amount of noble metal is 2 to 20 at% with respect to the metal component of the transition metal oxide.
And If it is 2 at% or less, the purifying activity will not be exhibited, and conversely, if it is 20 at% or more, the amount of noble metals will be too large and they will aggregate with each other, resulting in a decrease in activity. Desirably 2 to 1
0at% is good. It is desirable that the particle size of the noble metal be 500 Å or less.
【0015】これら遷移金属酸化物と貴金属とは混合し
て用いる。HC等を貴金属表面で浄化して除去するため
には貴金属と遷移金属酸化物とが密接して存在している
ことが必要なためである。またこれら両物質が接触する
界面は固溶し合っている方が良好な浄化特性を発揮す
る。These transition metal oxides and noble metals are mixed and used. This is because it is necessary that the noble metal and the transition metal oxide are in close contact with each other in order to remove and remove HC and the like on the surface of the noble metal. Further, if the interface where these two substances are in contact with each other is in solid solution, good purification characteristics are exhibited.
【0016】また、本発明の遷移金属酸化物と貴金属と
から構成される触媒は、酸素過剰のリーン雰囲気におい
て、かつ高空間速度下(SV=200000hr-1)で
も、NOx の還元反応を進行せしめる特徴を有する。Further, the catalyst composed of the transition metal oxide and the noble metal of the present invention progresses the NO x reduction reaction even in a lean atmosphere with excess oxygen and under a high space velocity (SV = 200000 hr −1 ). It has a characteristic that makes it attractive.
【0017】本発明に係る触媒は以下に示す方法によっ
て製造する。従来公知の方法、遷移金属の硝酸金属
塩、有機金属塩または金属塩化物を熱分解したものに貴
金属塩の水溶液を含浸して製造する方法、上記各種金
属塩を加水分解し、得られた水酸化物を焼成後、貴金属
を担持する方法、遷移金属塩と貴金属塩とからなる混
合溶液から共沈して製造する方法等のいずれを用いても
よい。The catalyst according to the present invention is manufactured by the following method. A conventionally known method, a method of impregnating a nitrate metal salt of a transition metal, an organic metal salt or a metal chloride thermally decomposed with an aqueous solution of a noble metal salt, and hydrolyzing the various metal salts to obtain water. Any of a method of supporting a noble metal after firing an oxide, a method of coprecipitating from a mixed solution of a transition metal salt and a noble metal salt, and the like may be used.
【0018】遷移金属酸化物と貴金属とからなる触媒
は、粉状、ペレット状、ハニカム状等その形状・構造は
問わない。また粉末状の触媒にアルミナゾルやシリカゾ
ル、ジルコニアゾル、チタニアゾル等のバインダーを添
加して、所定の形状に成形したり、水を加えて、スラリ
ー状としてハニカム等の形状のアルミナ等の耐火性基体
に塗布してもよい。The catalyst composed of a transition metal oxide and a noble metal may have any shape and structure such as powder, pellets and honeycomb. Further, a binder such as alumina sol, silica sol, zirconia sol, titania sol, etc. is added to the powdery catalyst to form it into a predetermined shape, or water is added to form a slurry into a refractory substrate such as alumina in the shape of a honeycomb or the like. You may apply.
【0019】[0019]
【実施例】本発明に係る触媒を製造し、該触媒について
酸素過剰雰囲気のモデルガスを用い、NOx 、CO、HC
に対する浄化活性評価を行った。また比較触媒について
も同様の活性評価を行った。EXAMPLES to produce a catalyst according to the present invention, using a model gas of oxygen-rich atmosphere for the catalyst, NO x, CO, HC
The purification activity was evaluated. The same activity evaluation was performed for the comparative catalyst.
【0020】(実施例1)硝酸コバルト・6水溶液54
gと硝酸パラジウム0.866gとを、イオン交換水2
lに溶かしたもの(原子比Pd:Co=1:50)を室
温下で、分液ロートより約0.6ml/secの速度
で、炭酸ナトリウム50gをイオン交換水2lに溶かし
たアルカリ性水溶液に滴下、撹拌する。この溶液を一時
間放置した後、ろ過か、洗浄し、減圧乾燥する。そして
得られた粉末を空気中で350℃、3時間焼成した。こ
の焼成物を約2〜3mmのサイコロ状に圧粉成型し、P
dとCo3O4とからなる実施例触媒No.1を得た。Example 1 Cobalt Nitrate / 6 Aqueous Solution 54
g and 0.866 g of palladium nitrate, ion-exchanged water 2
What was dissolved in 1 (atomic ratio Pd: Co = 1: 50) was dripped at room temperature from a separating funnel at a rate of about 0.6 ml / sec into an alkaline aqueous solution prepared by dissolving 50 g of sodium carbonate in 2 l of ion-exchanged water. , Stir. The solution is left for one hour, then filtered or washed and dried under reduced pressure. Then, the obtained powder was fired in air at 350 ° C. for 3 hours. This fired product is pressed into a die shape of about 2 to 3 mm, and P
Example catalyst No. 1 composed of d and Co 3 O 4 . Got 1.
【0021】(実施例2)実施例1の方法において、硝
酸パラジウムの代わりにジニトロジアミノPtを用い
(PtとCoとの原子比は1:50と同一)、アルカリ
性水溶液として炭酸ナトリウムを用いた以外は同一の条
件でPtとCo3O4とからなる実施例触媒No.2を得
た。(Example 2) In the same manner as in Example 1, except that dinitrodiamino Pt was used instead of palladium nitrate (atomic ratio of Pt to Co was the same as 1:50) and sodium carbonate was used as the alkaline aqueous solution. Is an example catalyst consisting of Pt and Co 3 O 4 under the same conditions. Got 2.
【0022】(実施例3)実施例1の方法において、硝
酸パラジウムの代わりにジニトロジアミノPtを用い
(PtとCoとの原子比は1:50と同一)アルカリ性
水溶液として炭酸アンモニウムを用いた以外は同一の条
件でPtとCo3O4とからなる実施例触媒No.3を得
た。Example 3 In the method of Example 1, except that dinitrodiamino Pt was used instead of palladium nitrate (the atomic ratio of Pt and Co was the same as 1:50), ammonium carbonate was used as the alkaline aqueous solution. Example catalyst No. consisting of Pt and Co 3 O 4 under the same conditions. Got 3.
【0023】(実施例4)硝酸コバルト水溶液(54g
/l)を、炭酸ナトリウム水溶液(50g/l)に滴下
して撹拌し、水酸化コバルトを沈澱させた後、ろ過、洗
浄し、さらに減圧乾燥し、その後空気中で350℃、3
hr焼成して得た粉末にジニトロジアミノPtをPt含
有量として2at%含浸し、その後空気中350℃で焼
成した。この焼成物を2〜3mmのサイコロ状に圧粉成
型し、PtとCo3O4とからなる実施例触媒No.4を得
た。Example 4 Aqueous cobalt nitrate solution (54 g
/ L) was added dropwise to an aqueous solution of sodium carbonate (50 g / l) and stirred to precipitate cobalt hydroxide, which was then filtered, washed and dried under reduced pressure, and then 350 ° C. in air for 3 days.
The powder obtained by the hr calcination was impregnated with dinitrodiamino Pt at a Pt content of 2 at% and then calcinated in air at 350 ° C. The calcined product was compacted into a die having a diameter of 2 to 3 mm, and the catalyst of Example No. 1 composed of Pt and Co 3 O 4 was used. Got 4.
【0024】(実施例5)硝酸コバルトを600℃で空
気中5hr焼成し、熱分解させCo3 O4 を得る。この
Co3 O4 粉末に硝酸パラジウム含有量3.5at%に
なるように含浸し、その後空気中で350℃、3hr焼
成した。この焼成物を2〜3mmのサイコロ状に圧粉成
型し、PdとCo3O4とからなる実施例触媒No.5を得
た。(Example 5) Co 3 O 4 was obtained by burning cobalt nitrate at 600 ° C for 5 hours in air and thermally decomposing it. This Co 3 O 4 powder was impregnated so that the content of palladium nitrate was 3.5 at%, and then calcined in air at 350 ° C. for 3 hours. The calcined product was compacted into a die having a diameter of 2 to 3 mm, and the catalyst of Example No. 1 containing Pd and Co 3 O 4 was used. Got 5.
【0025】(実施例6)実施例5の方法において、硝
酸パラジウムの代わりにジニトロジアミノPtを用いた
以外は同一の条件でPtとCo3O4とからなる実施例触
媒No.6を得た。(Example 6) In Example 5, except that dinitrodiamino Pt was used in place of palladium nitrate, the catalyst No. No. of Pt and Co 3 O 4 was used under the same conditions. Got 6.
【0026】(実施例7)実施例5の方法において、硝
酸コバルトの代わりに酢酸コバルトを用いた以外は同一
の条件でPtとCo3O4とからなる実施例触媒No.7を
得た。(Example 7) In Example 5, except that cobalt acetate was used in place of cobalt nitrate, Example catalyst No. 3 containing Pt and Co 3 O 4 was used under the same conditions. Got 7.
【0027】(実施例8)実施例5の方法において、硝
酸コバルトの代わりに硝酸ニッケルを用いた以外は同一
の条件でPtとNiOとからなる実施例触媒No.8を得
た。(Embodiment 8) An embodiment catalyst No. consisting of Pt and NiO was used under the same conditions except that nickel nitrate was used instead of cobalt nitrate in the method of Embodiment 5. Got 8.
【0028】(実施例9)実施例5の方法において、硝
酸コバルトの代わりに硝酸第二鉄を用いた以外は同一の
条件で、PtとFe2O3 とからなる実施例触媒No.9を
得た。(Embodiment 9) In the method of Embodiment 5, the catalyst No. of the embodiment of Pt and Fe 2 O 3 was used under the same conditions except that ferric nitrate was used instead of cobalt nitrate. Got 9.
【0029】(比較例1)実施例1の方法において、硝
酸パラジウムを加えないでそれ以外は同一の条件でCo
3O4のみからなる比較例触媒No.C1を得た。(Comparative Example 1) In the method of Example 1, palladium nitrate was not added, and Co
Comparative example catalyst consisting of 3 O 4 only C1 was obtained.
【0030】(比較例2)比表面積約140m2 /gの
γ−Al2O3ペレット担体(2〜3mmφ)をジニトロ
ジアミノPt水溶液に浸漬し、γ−Al2O3重量に対し
Pt量が0.14wt%になる様に含浸し、空気中11
0℃、5hr乾燥し、600℃空気中3hr焼成した。この焼
成物を約2〜3mmのサイコロ状に圧粉成型し、Ptと
Al2O3 とからなる比較例触媒No.C2を得た。(Comparative Example 2) A γ-Al 2 O 3 pellet carrier ( 2 to 3 mmφ) having a specific surface area of about 140 m 2 / g was immersed in an aqueous dinitrodiamino Pt solution, and the amount of Pt was adjusted with respect to the weight of γ-Al 2 O 3. Impregnated to 0.14 wt% in air 11
It was dried at 0 ° C. for 5 hours and calcined in air at 600 ° C. for 3 hours. The calcined product was compacted into a dice shape of about 2 to 3 mm, and the catalyst of Comparative Example No. 1 composed of Pt and Al 2 O 3 was used. C2 was obtained.
【0031】(触媒活性評価)サイコロ状とした本実施
例触媒No.1〜9および比較例触媒No.C1〜C2を用
い、表1に示した酸素過剰雰囲気のモデルガス中、SV
=200000hr-1での100℃〜600℃における
各成分(NO、CO、HC)の昇温浄化特性を測定し
た。その結果のうち、実施例触媒No.3を図1に、比較
例触媒No.C1を図2に、比較例触媒No.C2を図3に
示した。(Evaluation of Catalytic Activity) The catalyst No. of this example in the form of a dice. 1 to 9 and Comparative Example Catalyst No. Using C1 to C2, SV in the model gas in the oxygen excess atmosphere shown in Table 1
= 200,000 hr -1 at 100 ° C to 600 ° C, the temperature rising purification characteristics of each component (NO, CO, HC) were measured. Among the results, Example catalyst No. No. 3 is shown in FIG. C1 is shown in FIG. C2 is shown in FIG.
【0032】[0032]
【表1】 [Table 1]
【0033】実施例触媒No.3は270℃〜600℃に
おいてCO、HCをほぼ100%で、NOを30〜80
%の高浄化率で浄化することができる。しかし、 比較例
触媒No.ClおよびNo.C2は、NO浄化率が最大でも
20%程度の低い値を示すにすぎない。Example catalyst No. 3 is approximately 100% for CO and HC and 30 to 80 for NO at 270 ° C to 600 ° C.
It can be purified with a high purification rate of%. However, the comparative catalyst No. Cl and No. C2 shows only a low value of about 20% in the NO purification rate at the maximum.
【0034】また、上記各触媒の測定結果をNO、CO、
HCの400℃における浄化率を整理して表2に示し
た。実施例触媒は、NO、CO、HCすべての成分につい
て優れた浄化特性を示している。The measurement results of each of the above catalysts are shown as NO, CO,
The purification rates of HC at 400 ° C. are summarized and shown in Table 2. The example catalysts show excellent purification characteristics for all NO, CO and HC components.
【0035】[0035]
【表2】 [Table 2]
【0036】また、実施例触媒は、250℃において
も、400℃と同様な優れた浄化特性を示した。Further, the catalysts of Examples showed excellent purifying characteristics at 250 ° C. as well as at 400 ° C.
【図1】実施例触媒No.3についての温度に対する浄化
率の関係を示す図である。FIG. 1 Example catalyst No. It is a figure which shows the relationship of the purification rate with respect to the temperature about 3.
【図2】比較例触媒No.C1についての温度に対する浄
化率の関係を示す図である。FIG. 2 Comparative catalyst No. It is a figure which shows the relationship of the purification rate with respect to the temperature about C1.
【図3】比較例触媒No.C2についての温度に対する浄
化率の関係を示す図である。FIG. 3 Comparative example catalyst No. It is a figure which shows the relationship of the purification rate with respect to the temperature about C2.
Claims (1)
炭化水素、一酸化炭素および窒素酸化物を浄化するため
の触媒であって、多孔質担体と、この多孔質担体に担持
した遷移金属酸化物から選択された1種以上と貴金属か
ら選択された1種以上とからなることを特徴とする排気
ガス浄化用触媒。1. A catalyst for purifying hydrocarbons, carbon monoxide, and nitrogen oxides in exhaust gas in an oxygen-excess atmosphere, which is a porous carrier and a transition metal oxide supported on the porous carrier. An exhaust gas purifying catalyst comprising one or more kinds selected from among and one or more kinds selected from noble metals.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP6031828A JPH07213906A (en) | 1994-02-02 | 1994-02-02 | Exhaust gas purifying catalyst |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP6031828A JPH07213906A (en) | 1994-02-02 | 1994-02-02 | Exhaust gas purifying catalyst |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH07213906A true JPH07213906A (en) | 1995-08-15 |
Family
ID=12341943
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP6031828A Pending JPH07213906A (en) | 1994-02-02 | 1994-02-02 | Exhaust gas purifying catalyst |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH07213906A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2001048529A (en) * | 1999-08-04 | 2001-02-20 | Toyota Central Res & Dev Lab Inc | Spinel powder and spinel slurry |
-
1994
- 1994-02-02 JP JP6031828A patent/JPH07213906A/en active Pending
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2001048529A (en) * | 1999-08-04 | 2001-02-20 | Toyota Central Res & Dev Lab Inc | Spinel powder and spinel slurry |
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