KR100429825B1 - Catalyst for purifying exhaust gas of automobil and method for manufacturing the same - Google Patents
Catalyst for purifying exhaust gas of automobil and method for manufacturing the same Download PDFInfo
- Publication number
- KR100429825B1 KR100429825B1 KR1019960080118A KR19960080118A KR100429825B1 KR 100429825 B1 KR100429825 B1 KR 100429825B1 KR 1019960080118 A KR1019960080118 A KR 1019960080118A KR 19960080118 A KR19960080118 A KR 19960080118A KR 100429825 B1 KR100429825 B1 KR 100429825B1
- Authority
- KR
- South Korea
- Prior art keywords
- catalyst
- exhaust gas
- automobile exhaust
- carrier
- porous body
- Prior art date
Links
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J23/00—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
- B01J23/70—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
- B01J23/89—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with noble metals
- B01J23/8906—Iron and noble metals
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J37/00—Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
- B01J37/0009—Use of binding agents; Moulding; Pressing; Powdering; Granulating; Addition of materials ameliorating the mechanical properties of the product catalyst
- B01J37/0027—Powdering
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J37/00—Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
- B01J37/0081—Preparation by melting
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J37/00—Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
- B01J37/02—Impregnation, coating or precipitation
- B01J37/0201—Impregnation
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J37/00—Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
- B01J37/08—Heat treatment
Abstract
Description
본 발명은 자동차 배기가스 정화용 촉매 및 그 제조방법에 관한 것으로서, 보다 상세하게는 디젤 엔진이 작동을 개시하는 낮은 온도 범위에서도 질소산화물에 대한 정화능력이 우수한 촉매 및 그 제조방법에 관한 것이다.The present invention relates to a catalyst for automobile exhaust gas purification and a method for manufacturing the same, and more particularly, to a catalyst having excellent purification ability for nitrogen oxide even in a low temperature range in which a diesel engine starts operation, and a method for manufacturing the same.
최근들어 전세계적으로 환경파괴에 대한 우려와 함께 환경보호에 대한 관심이 높아지고 있는데, 환경오염은 대기오염, 수질오염, 토양오염 등으로 대별될 수 있다.In recent years, there has been a growing concern about environmental protection along with concerns about environmental destruction. Environmental pollution can be roughly classified into air pollution, water pollution, and soil pollution.
이중, 특히 대기오염에 의한 현상으로는 염화불화수소 (CFC)의 사용으로 인한 오존층의 파괴, 화석 연료를 사용할 때 발생하는 이산화탄소에 의한 지구 온실화 등을 들 수 있다. 또한, 각종 오염물질 배출시설로부터 배출되는 황산화물, 질소산화물, 탄화수소 등은 동식물에 각종 질병을 유발한다.In particular, the phenomenon due to air pollution includes the destruction of the ozone layer due to the use of hydrogen fluoride (CFC), and the global greenhouse effect due to carbon dioxide generated when using fossil fuels. In addition, sulfur oxides, nitrogen oxides, hydrocarbons, and the like emitted from various pollutant discharge facilities cause various diseases to animals and plants.
대기오염은 주로 연소체로부터 발생되므로 연소체의 배출시설 구조와 작동방법, 그리고 외부 기상조건 등에 의해 피해의 경중이 결정된다. 대표적인 연소체로는 자동차를 들 수 있다.Since air pollution mainly comes from the combustion body, the magnitude of the damage is determined by the structure of the combustion facility, the method of operation, and external weather conditions. Representative combustion bodies include automobiles.
자동차는 다른 대기오염 배출시설과는 달리 움직이면서 오염물질을 배출한다는 특징을 가지고 있는데, 생활수준이 향상되면서 자동차 사용이 급속하게 증가됨에 따라 자동차로 인한 대기오염 문제가 심각해지고 있다.Unlike other air pollution emission facilities, cars emit pollutants while moving, and as the use of automobiles increases rapidly as living standards improve, the air pollution problem caused by cars becomes serious.
자동차 배기가스의 성분과 배출량은 엔진의 온도, 압력 및 공기의 비율에 관계된다. 즉, 엔진의 공연비 (air/fuel ratio)를 적절히 조절함으로써 배기가스 정화효율을 높일 수 있다. 또한 배기가스 성분과 배출량은 사용되는 연료원과 정화장치의 종류에 의해서도 크게 좌우된다.The composition and emissions of automobile exhaust are related to the engine's temperature, pressure and proportion of air. That is, by properly adjusting the air / fuel ratio of the engine, it is possible to increase the exhaust gas purification efficiency. Exhaust gas components and emissions also depend largely on the type of fuel source and purification equipment used.
가솔린을 연료원으로 사용하는 스파크 점화식 엔진에 의해 구동되는 자동차에 대해서는 삼원 촉매와 같은 배기가스 제거 기술이 많이 개발되고 있어서, 가솔린 차량에 의한 오염물질의 배출은 현저하게 감소되고 있다.For automobiles driven by spark ignition engines using gasoline as a fuel source, many exhaust gas removal technologies such as three-way catalysts have been developed, and emissions of pollutants by gasoline vehicles have been significantly reduced.
이에 반해, 경유를 연료원으로 사용하는 디젤식 엔진은 열효율은 좋은 반면 악성 오염물질을 다량 배출하기 때문에 선진국에서는 그 사용을 엄격하게 규제하고 있다. 그러나, 아직도 많은 나라에서 트럭과 같은 대형차에 이러한 디젤식 엔진을 많이 채용하고 있다. 그럼에도 불구하고, 가솔린 자동차에 비해 디젤 엔진을 채용하는 경유 자동차의 배기가스를 정화시키는 기술은 매우 낙후된 상태이다. 따라서 경유 자동차에 대한 대기오염의 심각도가 더해지고 있어 전세계적으로 이에 대한 규제가 강화되고 있는 실정이고 우리나라에서도 규제가 시작되고 있어서 디젤 자동차의 배기가스 정화장치에 대한 개발이 시급하게 요구되고 있는 실정이다.On the other hand, diesel engines using diesel as a fuel source have good thermal efficiency but emit large amounts of harmful pollutants, so developed countries strictly regulate their use. However, many diesel engines are still adopted in large countries such as trucks in many countries. Nevertheless, the technology for purifying the exhaust gas of diesel vehicles employing diesel engines is very low compared to gasoline automobiles. Therefore, the severity of air pollution on diesel vehicles is increasing, and the regulations on these are being tightened around the world, and the regulations are starting in Korea. Therefore, the development of exhaust gas purification equipment for diesel vehicles is urgently required. .
디젤 자동차의 배기가스 중에는 일산화탄소, 탄화수소, 질소산화물 (NOX), 황산화물 및 입자성 물질 (particle matter)이 포함되어 있다. 이중, 상기 입자성 물질은 시야 장애의 원인이 되는 광화학 스모그 현상 및 부유분진의 발생을 가중시키며, 질소산화물은 태양광선의 작용을 받아 공기 중의 산소와 결합하여 호흡기 질환, 및 체내 단백질의 변성과 지방의 과산화 반응과 같은 생체 화학적 반응의 원인이 되는 오존을 생성한다.Exhaust gases of diesel vehicles include carbon monoxide, hydrocarbons, nitrogen oxides (NOX), sulfur oxides and particle matter. Among them, the particulate matter increases the photochemical smog phenomenon and the generation of suspended dust, which causes vision disturbances, and nitrogen oxides are combined with oxygen in the air under the action of sunlight to cause respiratory diseases, protein denaturation and fat in the body. Ozone is the cause of biochemical reactions such as peroxidation.
따라서, 상기 입자성 물질과 질소산화물을 동시에 제거할 수 있다면 바람직하겠으나, 이들에 대한 정화방법이 서로 상반되기 때문에 현재의 기술로는 이들을 동시에 제거하는 것이 불가능하다 하겠다.Therefore, it would be desirable if the particulate matter and the nitrogen oxide can be removed at the same time, but since the purification methods for them are mutually opposite to each other, it is impossible to remove them simultaneously with the current technology.
특히, 디젤 자동차에서 배출되는 오염물질 중에 다량 포함되어 있는 산소 및 황산화물이 질소산화물의 정화를 저해하기 때문에 정화 능력 향상에 어려움이 많다. 또한, 공지된 바 있는 대부분의 질소산화물 제거 시스템이 300℃ 전후의 온도에서 최대 활성을 나타내다가 이후에는 급격하게 활성이 저하된다는 단점이 있다. 그러므로 300℃보다 낮은 온도에서의 촉매활성이 개선되고 고온에서도 활성의 급격한 저하가 일어나지 않는 자동차 배기가스 정화용 촉매에 대한 요구가 증대되고 있다.In particular, since oxygen and sulfur oxides contained in a large amount of pollutants emitted from diesel vehicles inhibit the purification of nitrogen oxides, it is difficult to improve the purification ability. In addition, most of the known nitrogen oxide removal system exhibits a maximum activity at a temperature of about 300 ° C., and thereafter, there is a disadvantage in that the activity rapidly decreases. Therefore, there is an increasing demand for a catalyst for automobile exhaust gas purification which improves catalytic activity at temperatures lower than 300 ° C. and does not cause a sharp drop in activity even at high temperatures.
본 발명이 이루고자 하는 기술적 과제는 낮은 온도 범위에서도 질소산화물에 대하여 우수한 활성을 나타내며 고온에서 질소산화물 제거능력이 급격하게 저하되지 않는 자동차 배기가스 정화용 촉매를 제공하는 것이다.SUMMARY OF THE INVENTION The present invention has been made in an effort to provide a catalyst for automobile exhaust gas purification, which exhibits excellent activity against nitrogen oxides even in a low temperature range and does not sharply degrade nitrogen oxide removal capability at high temperatures.
또한, 본 발명이 이루고자 하는 다른 기술적 과제는 낮은 온도 범위에서도 질소산화물에 대하여 우수한 활성을 나타내며 고온에서 질소산화물 제거능력이 급격하게 저하되지 않는 자동차 배기가스 정화용 촉매의 제조방법을 제공하는 것이다.In addition, another technical problem to be achieved by the present invention is to provide a method for producing a catalyst for the purification of automobile exhaust gas exhibits excellent activity against nitrogen oxides even in a low temperature range and does not rapidly decrease the ability to remove nitrogen oxides at high temperatures.
도 1은 본 발명에 따른 자동차 배기가스 정화용 촉매의 활성을 종래의 촉매의 활성과 비교하여 나타낸 그래프이다.1 is a graph showing the activity of the catalyst for automobile exhaust purification according to the present invention compared with the activity of a conventional catalyst.
본 발명의 기술적 과제는 전이금속을 다공체에 담지시켜 얻은 담체, 및 상기 담체에 담지된 귀금속을 포함하는 자동차 배기가스 정화용 촉매에 의하여 달성될 수 있다.The technical problem of the present invention can be achieved by a carrier obtained by supporting a transition metal in a porous body, and a catalyst for automobile exhaust gas purification comprising a noble metal supported on the carrier.
본 발명의 자동차 배기가스 정화용 촉매에 있어서, 상기 전이금속은 철이고, 상기 다공체는 알루미나, 지로코니아, 이산화티탄, 제올라이트 또는 모데나이트이며, 상기 전이금속과 다공체의 혼합몰비는 1:10-1:20이다. 또한, 상기 담체상에 담지된 귀금속의 담지량은 담체의 총중량을 기준으로 하여 1-1.5중량%이며, 상기 귀금속으로는 팔라듐 및 백금의 혼합물이 바람직하다.In the catalyst for automobile exhaust gas purification of the present invention, the transition metal is iron, the porous body is alumina, zirconia, titanium dioxide, zeolite or mordenite, and the mixed molar ratio of the transition metal and the porous body is 1: 10-1: 20. The amount of the noble metal supported on the carrier is 1-1.5% by weight based on the total weight of the carrier, and a mixture of palladium and platinum is preferred as the noble metal.
본 발명의 다른 기술적 과제는 (a) 다공체 및 철염 수화물을 물속에서 교반한 다음, 건조 및 소성시켜서 전이금속이 다공체에 함침된 담체를 제조하는 단계; (b) 팔라듐염 및 백금착화물을 각각 폴리올에 용해시켜 용액 (1) 및 용액 (2)를 제조하는 단계; (c) 상기 단계 (a)에서 제조된 담체를 상기 단계 (b)에서 제조된 용액 (1) 및 (2)에 넣어 팔라듐 및 백금을 상기 담체에 담지하는 단계; (d) 상기 단계 (c)의 결과물을 건조 및 분쇄하는 단계; 및 (e) 상기 단계 (d)의 결과물을 열처리하는 단계를 포함하는 것을 특징으로 하는 자동차 배기가스 정화용 촉매의 제조방법에 의하여 달성될 수 있다.Another technical problem of the present invention is to prepare a carrier having a transition metal impregnated into a porous body by (a) stirring the porous body and iron salt hydrate in water, and then drying and calcining; (b) dissolving palladium salts and platinum complexes in polyols, respectively, to prepare solution (1) and solution (2); (c) adding the carrier prepared in step (a) to the solutions (1) and (2) prepared in step (b) to support palladium and platinum on the carrier; (d) drying and grinding the product of step (c); And (e) it can be achieved by a method for producing a catalyst for automobile exhaust gas purification comprising the step of heat-treating the product of step (d).
본 발명의 자동차 배기가스 정화용 촉매의 제조방법에 있어서, 상기 다공체로는 알루미나, 지로코늄, 이산화티탄, 제올라이트 또는 모데나이트가 바람직하며, 상기 철염수화물 및 다공체의 혼합비율은 1:10-1:20인 것이 바람직하다. 또한, 바람직하게는 상기 팔라듐염 용액중의 팔라듐 함유량 및 상기 백금착화물 중의 백금 함유량은 상기 담체의 총중량을 기준으로 하여 각각 0.75-1중량% 및 0.25-0.5중량%이며, 상기 폴리올로는 에틸렌글리콜 또는 프로필렌글리콜이 사용된다. 또한, 상기 단계 (e)는 400-600℃에서 2-5시간 동안 실시된다.In the method for preparing a catalyst for automobile exhaust gas purification of the present invention, the porous body is preferably alumina, zirconium, titanium dioxide, zeolite or mordenite, and the mixing ratio of the iron chloride and the porous body is 1: 10-1: 20. Is preferably. Preferably, the palladium content in the palladium salt solution and the platinum content in the platinum complex are 0.75-1% by weight and 0.25-0.5% by weight, respectively, based on the total weight of the carrier, and the polyol is ethylene glycol. Or propylene glycol is used. In addition, the step (e) is carried out for 2-5 hours at 400-600 ℃.
본 발명의 제조방법에 따라 제조된 자동차 배기가스 정화용 촉매는 종래의 촉매에 비하여 300℃ 이하의 저온에서 질소산화물의 전환율이 상당히 개선되며 300℃ 이상의 고온에서도 질소산화물 전환율이 급격하게 떨어지지 않는다.The catalyst for purifying automobile exhaust gas prepared according to the production method of the present invention is significantly improved in conversion of nitrogen oxide at a low temperature of 300 ° C. or lower as compared with the conventional catalyst, and does not drop rapidly in a high temperature of 300 ° C. or higher.
이하, 실시예를 들어 본 발명을 보다 상세하게 설명할 것이나, 본 발명이 이에 한정되지는 않는다.Hereinafter, the present invention will be described in more detail with reference to Examples, but the present invention is not limited thereto.
<실시예><Example>
132.22g의 ZrO2 및 34.19g의 Fe(NO3)2·9H2O를 물 0.2ℓ에 넣고 2시간 동안 교반하였다. 이어서 물을 증발시키고 오븐에서 건조한 다음, 500℃에서 2시간 동안 소성하여 전이금속 및 다공체를 포함하는 담체인 Fe-ZrO2를 합성하였다. 이어서, Pd(NO3)3 용액 (0.15g의 팔라듐 함유)을 6㎖의 에틸렌글리콜에 용해시켜 팔라듐의 에틸렌글리콜 용액을 제조한 다음, Pt(NH3)4Cl2·H2O (0.05g의 백금 함유)을 2㎖의에틸렌글리콜에 용해시켜서 백금의 에틸렌글리콜 용액을 제조하였다.132.22 g of ZrO 2 and 34.19 g of Fe (NO 3) 2 .9H 2 O were added to 0.2 L of water and stirred for 2 hours. Subsequently, water was evaporated, dried in an oven, and calcined at 500 ° C. for 2 hours to synthesize Fe-ZrO 2, a carrier including a transition metal and a porous body. Subsequently, a Pd (NO 3) 3 solution (containing 0.15 g of palladium) was dissolved in 6 ml of ethylene glycol to prepare an ethylene glycol solution of palladium, followed by Pt (NH 3) 4 Cl 2 .H 2 O (containing 0.05 g of platinum). It was dissolved in ml of ethylene glycol to prepare a solution of platinum ethylene glycol.
계속하여, 백금의 에틸렌글리콜 용액과 팔라듐의 에틸렌글리콜 용액을 전술한 바와 같이 제조된 담체 (Fe-ZrO2) 20g에 스며들도록 조금씩 가해서 백금 및 팔라듐이 담지된 0.75Pd0.25Pt/Fe-ZrO2를 제조하였다. 이 생성물을 80℃의 오븐에 넣어 건조시킨 다음, 유발에서 분쇄하고 다시 전기로에 넣어 500℃에서 2시간 동안 열처리하여 분말화시켰다. 이 분말을 펠렛 형태로 만든 다음, 체를 이용하여 크기가 약 1-2㎜인 것만 선택하였다. 상기와 같이 만들어진 펠렛형 촉매 2㎖을 반응기에 넣고 질소산화물에 대한 촉매 활성을 측정하였다. 측정시의 배기가스 조성 및 반응조건은 하기와 같다:Subsequently, 0.75 Pd 0.25 Pt / Fe-ZrO 2 supported with platinum and palladium was prepared by gradually adding platinum ethylene glycol solution and palladium ethylene glycol solution to 20 g of the carrier (Fe-ZrO 2) prepared as described above. . The product was put into an oven at 80 ° C. and dried, then ground in a mortar and put into an electric furnace to be powdered by heat treatment at 500 ° C. for 2 hours. The powder was made into pellets, and then only those with a size of about 1-2 mm were selected using a sieve. 2 ml of the pellet-type catalyst prepared as described above was placed in a reactor, and catalytic activity of nitrogen oxide was measured. The exhaust gas composition and reaction conditions in the measurement are as follows:
NO: 500ppm, C3H6: 800ppm, O2: 8%, CO2: 14%, CO: 0.2%, SO2: 200ppmNO: 500 ppm, C3H6: 800 ppm, O2: 8%, CO2: 14%, CO: 0.2%, SO2: 200 ppm
반응온도: 200-600℃Reaction temperature: 200-600 ℃
공간속도: 40,000h-1.Space velocity: 40,000 h-1.
촉매활성 측정 결과를 도 1의 그래프에 나타내었다 (a).The catalytic activity measurement results are shown in the graph of FIG. 1 (a).
<비교예>Comparative Example
담체로서 지르코니아 (ZrO2)를 사용한 것을 제외하고는 실시예 1에서와 동일한 방법을 이용하여 촉매인 0.75Pd0.25Pt/ZrO2를 제조하였다. 이렇게 제조된 촉매에 대하여 실시예 1에서와 동일한 건조, 분쇄 및 열처리 공정을 실시하여 분말 형태로 만든 다음, 이것을 다시 펠렛 형태로 만들었다. 이 펠렛 형태의 촉매에 대한 촉매활성을 실시예 1에서와 동일한 배기가스 조성 및 반응 조건하에서 실시하였다. 그 결과를 도 1에 나타내었다 (b).A catalyst of 0.75 Pd 0.25 Pt / ZrO 2 was prepared in the same manner as in Example 1, except that zirconia (ZrO 2) was used as the carrier. The catalyst thus prepared was subjected to the same drying, grinding and heat treatment processes as in Example 1 to form a powder, which was then pelletized. Catalytic activity for this pellet type catalyst was carried out under the same exhaust gas composition and reaction conditions as those in Example 1. The results are shown in Figure 1 (b).
도 1의 결과로부터 알 수 있듯이, 귀금속을 통상의 촉매에 담지시킨 종래의 촉매 (b)는 300℃ 정도의 온도에서는 높은 질소산화물 전환율을 나타내지만 300℃ 미만의 저온에서는 전환율이 저조하고 반대로 300℃를 초과하는 온도에서는 전환율이 급격하게 저하되는 것으로 나타났다. 이에 반하여, 전이금속이 포함된 담체를 사용하는 본 발명의 촉매 (a)는 저온에서도 비교적 높은 질소산화물 전환율을 나타낼 뿐 아니라 고온에서도 전환율의 급격한 저하를 나타내지 않는다.As can be seen from the results of FIG. 1, the conventional catalyst (b) having a noble metal supported on a conventional catalyst shows high nitrogen oxide conversion at a temperature of about 300 ° C., but has a low conversion rate at a low temperature of less than 300 ° C., and conversely, 300 ° C. It was found that the conversion rate dropped sharply at temperatures exceeding. In contrast, the catalyst (a) of the present invention using a carrier containing a transition metal not only shows a relatively high nitrogen oxide conversion even at low temperatures but also does not show a sharp decrease in the conversion even at high temperatures.
본 발명에 따른 자동차 배기가스 정화용 촉매는 300℃ 이하의 저온에서 촉매활성이 종래의 자동차 배기가스 촉매보다 전반적으로 높으며, 고온에서의 활성 저하도 급격하게 일어나지 않고 비교적 고른 분포의 촉매활성을 나타낸다. 이로부터 알 수 있듯이, 본 발명의 촉매는 종래의 촉매에 비하여 촉매활성이 전반적으로 크게 개선되는 효과를 나타낸다.The catalyst for automobile exhaust gas purification according to the present invention has a higher catalytic activity than a conventional automobile exhaust gas catalyst at a low temperature of 300 ° C. or lower, and shows a relatively even distribution of catalytic activity without a sharp decrease in activity at high temperatures. As can be seen from this, the catalyst of the present invention exhibits the effect of greatly improving the catalytic activity as a whole compared to the conventional catalyst.
Claims (11)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
KR1019960080118A KR100429825B1 (en) | 1996-12-31 | 1996-12-31 | Catalyst for purifying exhaust gas of automobil and method for manufacturing the same |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
KR1019960080118A KR100429825B1 (en) | 1996-12-31 | 1996-12-31 | Catalyst for purifying exhaust gas of automobil and method for manufacturing the same |
Publications (2)
Publication Number | Publication Date |
---|---|
KR19980060752A KR19980060752A (en) | 1998-10-07 |
KR100429825B1 true KR100429825B1 (en) | 2004-06-16 |
Family
ID=37335261
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
KR1019960080118A KR100429825B1 (en) | 1996-12-31 | 1996-12-31 | Catalyst for purifying exhaust gas of automobil and method for manufacturing the same |
Country Status (1)
Country | Link |
---|---|
KR (1) | KR100429825B1 (en) |
Families Citing this family (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN113713852B (en) * | 2021-08-03 | 2024-05-03 | 浙江三元龙兴科技股份有限公司 | Catalyst for meeting low NOx emission of diesel vehicle and production method thereof |
Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR940003609A (en) * | 1992-08-28 | 1994-03-12 | 카렌 엘.존슨 | Catalysts for treating exhaust gases from internal combustion and stationary supply lines |
KR940003611A (en) * | 1992-08-18 | 1994-03-12 | 이헌조 | Method for producing catalyst for exhaust gas purification |
JPH0788335A (en) * | 1993-09-22 | 1995-04-04 | Nippon Steel Corp | Method for denitrating low-temperature waste gas |
-
1996
- 1996-12-31 KR KR1019960080118A patent/KR100429825B1/en not_active IP Right Cessation
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR940003611A (en) * | 1992-08-18 | 1994-03-12 | 이헌조 | Method for producing catalyst for exhaust gas purification |
KR940003609A (en) * | 1992-08-28 | 1994-03-12 | 카렌 엘.존슨 | Catalysts for treating exhaust gases from internal combustion and stationary supply lines |
JPH0788335A (en) * | 1993-09-22 | 1995-04-04 | Nippon Steel Corp | Method for denitrating low-temperature waste gas |
Also Published As
Publication number | Publication date |
---|---|
KR19980060752A (en) | 1998-10-07 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
EP0761289A2 (en) | Exhaust gas cleaner and method for cleaning exhaust gas | |
KR100213183B1 (en) | Catalyst for purifying exhaust gases of automobile and preparing method thereof | |
EP0664149B1 (en) | Method of purifying exhaust gas | |
JPH0938464A (en) | Catalyst for purification of exhaust gas and purifying method of exhaust gas | |
JPH0884911A (en) | Catalyst for decomposing nitrogen oxide and method for purifying diesel engine exhaust using the same | |
KR100429825B1 (en) | Catalyst for purifying exhaust gas of automobil and method for manufacturing the same | |
US5955046A (en) | Catalytic material for removing nitrogen oxides apparatus for treating nitrogen oxides using the material, and method of removing nitrogen oxides | |
EP0499087B1 (en) | Process for purifying exhaust gas | |
KR100408511B1 (en) | Catalyst for purifying exhaust gas of automobile and method for manufacturing the same | |
WO2002055194A1 (en) | Catalyst for clarification of nitrogen oxides | |
JP2506598B2 (en) | Nitrogen oxide removal method | |
KR0166465B1 (en) | Preparation of catalyst for cleaning exhaust gases | |
KR100446600B1 (en) | Catalyst system for purifying exhaust gas from diesel automobile and manufacturing method thereof | |
JP3398159B2 (en) | Nitrogen oxide removal method | |
KR100408503B1 (en) | Catalyst for purifying exhaus gas of vehicle | |
JP4588134B2 (en) | Nitrogen oxide purification catalyst | |
JPH0751542A (en) | Purification of exhaust gas | |
KR100408502B1 (en) | Catalyst for purifying exhaust gas of vehicle | |
KR0183620B1 (en) | Nitrogen oxide reducing catalyst | |
JP3686753B2 (en) | Oxide catalyst material for decomposing nitrogen oxide and method for decomposing and removing nitrogen oxide | |
KR100384016B1 (en) | High durable Pd-Rh three way catalyst for NOx reduction | |
JP3423703B2 (en) | Nitrogen oxide removal catalyst | |
JPH1033944A (en) | Catalyst for catalytic reduction and removal of nitrogen oxide and method therefor | |
JPH1190225A (en) | Oxide catalytic material for removing nitrogen oxide and removing method therefor | |
JPH1133401A (en) | Oxide catalytic material for removal of nox, and method for removing nox |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
A201 | Request for examination | ||
E902 | Notification of reason for refusal | ||
AMND | Amendment | ||
E601 | Decision to refuse application | ||
AMND | Amendment | ||
J201 | Request for trial against refusal decision | ||
B90T | Transfer of trial file for re-examination | ||
B701 | Decision to grant | ||
GRNT | Written decision to grant | ||
FPAY | Annual fee payment |
Payment date: 20130403 Year of fee payment: 10 |
|
FPAY | Annual fee payment |
Payment date: 20140325 Year of fee payment: 11 |
|
LAPS | Lapse due to unpaid annual fee |