CN104888845A - Platinum/cerium aluminum-molecular sieve catalyst for catalytic oxidation of ammonia gas and preparation method thereof - Google Patents

Platinum/cerium aluminum-molecular sieve catalyst for catalytic oxidation of ammonia gas and preparation method thereof Download PDF

Info

Publication number
CN104888845A
CN104888845A CN201510306885.2A CN201510306885A CN104888845A CN 104888845 A CN104888845 A CN 104888845A CN 201510306885 A CN201510306885 A CN 201510306885A CN 104888845 A CN104888845 A CN 104888845A
Authority
CN
China
Prior art keywords
cerium
platinum
catalyst
molecular sieve
aluminium
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.)
Granted
Application number
CN201510306885.2A
Other languages
Chinese (zh)
Other versions
CN104888845B (en
Inventor
廖传文
刘小庆
彭鹏
孙浩
李云
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
SICHUAN ZHONGZI EXHAUST PURGE CO Ltd
Original Assignee
SICHUAN ZHONGZI EXHAUST PURGE CO Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by SICHUAN ZHONGZI EXHAUST PURGE CO Ltd filed Critical SICHUAN ZHONGZI EXHAUST PURGE CO Ltd
Priority to CN201510306885.2A priority Critical patent/CN104888845B/en
Publication of CN104888845A publication Critical patent/CN104888845A/en
Application granted granted Critical
Publication of CN104888845B publication Critical patent/CN104888845B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02CCAPTURE, STORAGE, SEQUESTRATION OR DISPOSAL OF GREENHOUSE GASES [GHG]
    • Y02C20/00Capture or disposal of greenhouse gases
    • Y02C20/10Capture or disposal of greenhouse gases of nitrous oxide (N2O)

Abstract

The invention provides a platinum/cerium aluminum-molecular sieve catalyst for catalytic oxidation of an ammonia gas. Cordierite ceramic is utilized as a carrier for the platinum/cerium aluminum-molecular sieve catalyst, the surface of the carrier is coated with a catalyst layer, and the catalytic active site of the catalyst layer consists of a noble metal platinum, a cerium-aluminum composite oxide and a neodymium-modified molecular sieve; the mass ratio of the cerium-aluminum composite oxide to the neodymium-modified molecular sieve to the noble metal platinum is (20-80):(20-80):(0.01-0.1), and the mass ratio of cerium oxide and aluminum oxide in the cerium-aluminum composite oxide is (1-3):(1-5); the mass ratio of neodymium oxide and a molecular sieve in the neodymium-modified molecular sieve is (1-10):(90-100). The platinum/cerium aluminum-molecular sieve catalyst is also capable of achieving wide low-temperature activity window, good catalytic activity and high selectivity even at a high space velocity (SV), and is capable of effectively restraining generation of secondary pollutants of N2O, NO and NO2. The invention further provides a preparation method of the platinum/cerium aluminum-molecular sieve catalyst.

Description

For the platinum/cerium aluminium-molecular sieve catalyst and preparation method thereof of catalytic oxidation ammonia
Technical field
The invention belongs to catalyst technical field, relate to a kind of Catalysts and its preparation method for catalytic oxidation ammonia, particularly a kind of platinum for catalytic oxidation ammonia/cerium aluminium-molecular sieve catalyst and preparation method thereof.
Background technology
Diesel engine obtains applying more and more widely with its low oil consumption, high-power feature, but the HTHP in cylinder of diesel engine can produce a large amount of nitrogen oxide, brings serious environmental problem.At present, China is the nitrogen oxide adopting SCR (SCR) to process diesel engine generation substantially, and wherein applying maximum reducing agents is aqueous solution of urea, and hydrolysis of urea generates ammonia.In order to reach stricter NOx emission standard, the following two kinds of methods of main employing in the world: (1) sprays more urea liquid, and the shortcoming of this method is to cause unnecessary ammonia leakage; (2) use the catalyst of absorbing ammonia, the shortcoming of this method be when diesel vehicle carry out urgency accelerate time, the exhaust temperature of discharge can be made sharply to raise, and the ammonia of desorption exacerbates the leakage of ammonia, causes new secondary environmental pollution.
Ammonia is a kind of colourless and have the gas of intense stimulus stench, and can dissolve each other with any ratio and aqueous phase and separate and highly volatile.It has stimulation and corrosiveness to human respiratory tract, reduces human body to the resistance of disease.People sucks a large amount of ammonias in a short time, may occur shedding tears, pharyngalgia, hoarseness, dizziness, the symptom such as nauseating, uncomfortable in chest, weak, severe patient there will be pulmonary emphysema, also respiratory tract symptom can occur simultaneously.Ammonia is listed in odorant pollutant discharge by China, becomes field of Environment Protection item controlled, must the strict discharge controlling ammonia.
At present, the method removing ammonia mainly contains chemical absorption method, physisorphtion, catalystic pyrolysis, biofiltration process and catalytic oxidation.Although chemical absorption method and physisorphtion simple to operate, need regularly replace adsorbent, easily produce secondary pollution.Catalystic pyrolysis needs could decompose at relatively high temperatures, and permanent plant investment is larger.Biofiltration process, though do not produce secondary pollution, is difficult to realize industrialization because ammonia removal efficiency is low.
Catalytic oxidation is a kind of ideal Treatment process, is under the atmosphere of catalyst and oxygen, ammonia Catalytic Oxygen is changed into free of contamination nitrogen and water.In practical application, need catalyst cryogenic property good, ammonia just can be made farthest to be converted into nitrogen and water, reduce the generation of nitrogen oxide accessory substance.Conventional catalyst system mainly contains following a few class: metal-oxide catalyst, Ion exchange-Size exclusion type catalyst and noble metal type catalyst.Get well and low price although metal-oxide catalyst is selective, its low temperature active is lower, and the conversion ratio 250 DEG C time is only 60%.Although Ion exchange-Size exclusion type catalyst low temperature window is wide, easily produces nitrous oxide at 250 ~ 300 DEG C, cause secondary pollution.
Noble metal type catalyst is that have higher catalytic oxidation activity at 250 ~ 450 DEG C, good low temperature active window, is oxidized the ammonia of leakage by platinum, palladium even load in the inorganic material such as aluminium oxide, and its reaction equation is as shown in the formula shown in (1).
4NH 3+3O 2→2N 2+6H 2O (1)
But current existing noble metal type catalyst is take aluminium oxide as carrier material mostly, noble metal distribution on alumina, causes noble metal catalyst while carrying out ammonia oxidation, easily causes N 2o, NO, NO 2pollutant produces, and therefore seriously limits the application in practice of noble metal type catalyst, specifically reacts as shown in the formula shown in (2) ~ (3).
4NH 3+5O 2→4NO+6H 2O (2)
4NH 3+7O 2→4NO 2+6H 2O (3)
2NH 3+2O 2→N 2O+3H 2O (4)
CN 103476495A discloses a kind of ammoxidation catalyst and employs its waste gas purification apparatus and using method, adopts double-deck coating, and the inorganic material of lower floor's noble metal that has been load, upper strata is molecular sieve catalyst, although at 250 ~ 400 DEG C to NH 3there is higher catalytic oxidation activity, but also create higher concentration N simultaneously 2o and NO x.
Therefore, at use aqueous solution of urea as in SCR (SCR) system of diesel engine reducing agent, develop low-temperature catalytic oxidation ammonia performance good, and effectively can suppress N 2o, NO, NO 2the noble metal type catalyst produced Deng pollutant is very urgent and necessary.
Summary of the invention
The object of the invention is to overcome above-mentioned deficiency existing in prior art, a kind of platinum for catalytic oxidation ammonia/cerium aluminium-molecular sieve catalyst and preparation method thereof is provided.This platinum/cerium aluminium-molecular sieve catalyst take cordierite ceramic as carrier, with noble metal platinum, cerium-aluminium composite oxide (Ce-Al composite oxides) and neodymium modified molecular screen (Nd/ZSM-5) for catalytic active center, noble metal platinum is distributed on cerium-aluminium composite oxide and neodymium modified molecular screen, and regulate its weight, even if it is wide to make described platinum/cerium aluminium-molecular sieve catalyst also can realize low temperature active window under high air speed (SV), catalytic activity is good, selective height, effectively can suppress N 2o, NO, NO 2the generation of secondary pollution.
In order to realize foregoing invention object, the invention provides following technical scheme:
Platinum for catalytic oxidation ammonia of the present invention/cerium aluminium-molecular sieve catalyst, take cordierite ceramic as carrier, carrier surface is coated with catalyst layer, it is characterized in that: the catalytic active center of described catalyst layer is made up of noble metal platinum, cerium-aluminium composite oxide and neodymium modified molecular screen; The weight ratio of described cerium-aluminium composite oxide, neodymium modified molecular screen and noble metal platinum (in Pt) is 20 ~ 80:20 ~ 80:0.01 ~ 0.1; In described cerium-aluminium composite oxide, the weight ratio of cerium oxide and aluminium oxide is 1 ~ 3:1 ~ 5; In described neodymium modified molecular screen, the weight ratio of neodymia and molecular sieve is 1 ~ 10:90 ~ 100.
Platinum/cerium aluminium-the molecular sieve catalyst of catalytic oxidation ammonia of the present invention, noble metal platinum exists with the form of simple substance platinum and platinum oxide.In prior art, usually using precious metal palladium, rhodium or gold as catalytic active center.Wherein, precious metal palladium is not strong to the oxidation susceptibility of ammonia, can not be nitrogen by ammonia complete oxidation, causes generating a large amount of oxynitrides, causes secondary pollution; And the sulfur resistance of palladium is very poor, easily causes sulfur poisoning.Noble Metal Rhodium does not have oxidation susceptibility substantially to ammonia, and its price comparison is expensive.Although gold has good oxidation susceptibility and selective at low temperatures, ageing resistace is poor.Applicant finds through test of many times, is distributed in by noble metal platinum on cerium-aluminium composite oxide and neodymium modified molecular screen, not only can significantly improve the low-temperature catalytic activity of platinum/cerium aluminium-molecular sieve catalyst, and selective height, and ammonia is being oxidized to N 2while effectively inhibit N 2o, NO, NO 2the generation of secondary pollution.Its main mechanism provides active sites for noble metal platinum, ammonia is oxidized to oxynitrides or nitrogen, and oxynitrides is adsorbed on above molecular sieve, provides secondary response, is converted into nitrogen, inhibits N 2o, NO, NO 2the generation of secondary pollution.
In catalyst layer, cerium-aluminium composite oxide, as the carrier of noble metal platinum, makes ammonia react rapidly; The effect of neodymium modified molecular screen, simultaneously can the oxynitrides of adsorption reaction not only as the carrier of noble metal, makes oxynitrides react generation nitrogen further, suppresses N 2o, NO, NO 2the generation of secondary pollution.In the prior art, usually noble metal is directly distributed on the molecular sieve of non-modified, can N be caused 2o, NO, NO 2the generation of secondary pollution; The present invention adopts neodymium to carry out modification to molecular sieve, efficiently avoid this defect.
Preferably, described catalyst carrier surface coated weight according to the dry weight of catalyst layer be 120 ~ 180g/L calculate.Namely catalyst pulp is after carrier surface drying, roasting, and the coated weight on its surface should reach often liter of carrier cordierite ceramic surface coated catalysts 120 ~ 180g.When the dry weight of catalyst layer is less than 120g/L, ammonia oxidation not exclusively, does not reach high conversion ratio; When the dry weight of catalyst layer is greater than 180g/L, the back pressure of diesel engine can be increased, bad impact is caused on the fuel economy of diesel engine.Further preferably, the dry weight of described catalyst layer is 150 ~ 170g/L.Preferably, the dry weight of described catalyst layer is 155 ~ 165g/L to the best.
Preferably, described molecular sieve is ZSM-5 molecular sieve.ZSM-5 molecular sieve basic structural unit is made up of eight five-membered rings, and its crystal structure belongs to orthorhombic system, is beneficial to the absorption of oxynitrides.
Applicant finds through many experiments, and in catalyst layer, the weight ratio of cerium-aluminium composite oxide, neodymium modified molecular screen and noble metal platinum affects platinum/cerium aluminium-molecular sieve catalyst catalytic activity and optionally one of key factor.When the weight ratio of cerium-aluminium composite oxide, neodymium modified molecular screen and noble metal platinum is in the scope of 20 ~ 80:20 ~ 80:0.01 ~ 0.1, platinum/cerium aluminium-molecular sieve catalyst is to ammonia catalytic activity and selective all better.Further preferably, the weight ratio of described cerium-aluminium composite oxide, neodymium modified molecular screen and noble metal platinum is 40 ~ 70:30 ~ 60:0.04 ~ 0.06.Preferably, the weight ratio of described cerium-aluminium composite oxide, neodymium modified molecular screen and noble metal platinum is 50:50:0.0441 to the best.By above preferably, the catalytic activity of platinum/cerium aluminium-molecular sieve catalyst can be made and selectively reach best, while raising catalytic activity, farthest suppressing N 2o, NO, NO 2the generation of secondary pollution.
The preparation method of platinum of the present invention/cerium aluminium-molecular sieve catalyst, is characterized in that, comprise the following steps:
(1) preparation of cerium-aluminium composite oxide
Get the aluminum nitrate solution of 0.1 ~ 0.4g/ml and the cerous nitrate solution of 0.1 ~ 0.4g/ml, mix, join in the citric acid solution of 0.1 ~ 0.3g/ml, stir 1 ~ 2h, evaporating water, dry 20 ~ 24h at 100 ~ 120 DEG C, then roasting, obtains cerium-aluminium composite oxide;
(2) preparation of neodymium modified molecular screen
The neodymium nitrate solution of 0.1 ~ 0.4g/ml is joined in molecular sieve powder, dry 8 ~ 10h at 100 ~ 120 DEG C; Then roasting, obtains neodymium modified molecular screen powder;
(3) preparation of slurry
Cerium-aluminium composite oxide, neodymium modified molecular screen powder, citric acid and platinum salt are joined in deionized water, fully stirs, obtain catalyst pulp;
(4) ground slurry: grind catalyst pulp, until catalyst pulp particle is 2 ~ 5 μm;
(5) slurry is applied: take cordierite ceramic as carrier, be immersed into by cordierite ceramic in the catalyst pulp after grinding, submergence 3 ~ 5min; Then cordierite ceramic is taken out from catalyst pulp, blow remainder catalyst slurry in duct off, obtain the cordierite ceramic that surface is coated with catalyst pulp;
(6) dry and roasting: the cordierite ceramic dry 4 ~ 6h, the then roasting at 100 ~ 120 DEG C that surface are coated with catalyst pulp, be finally cooled to room temperature, obtain platinum/cerium aluminium-molecular sieve catalyst; Wherein the coated weight of catalyst pulp after roasting is 120 ~ 180g/L.
Preparation method's cost of the present invention is low, and toxicity is little, simple to operate, easily controls, and obtained platinum/cerium aluminium-molecular sieve catalyst low-temperature catalytic activity is good, ammonia can be transformed completely at 225 DEG C, and selective height, effectively can suppress N simultaneously 2o, NO, NO 2the generation of secondary pollution.
Preferably, in described step (1), the volume ratio of aluminum nitrate solution and citric acid solution is 1:1 ~ 4.In the preparation process of cerium aluminium compound, the effect of citric acid enters in the duct of cerium-aluminium composite oxide crystal, increases its specific area.When the volume ratio of aluminum nitrate solution and citric acid solution is less than 1:1, the cerium-aluminium composite oxide of preparation has less specific area, is unfavorable for the reaction of ammonia.When the volume ratio of aluminum nitrate solution and citric acid solution is greater than 1:4, excessive citric acid can enter in cerium-aluminium composite oxide crystal, because heat release is large during roasting, can cause the tunnel collapse of a part, cause specific area to reduce equally, be unfavorable for the reaction of ammonia.
Preferably, the roasting in described step (1) is roasting 3 ~ 4h at 550 ~ 650 DEG C.Be less than 3h upon firing, citric acid incomplete combustion can be caused, simultaneously cerium-aluminium composite oxide poor stability.Be greater than 4h upon firing, under causing cerium-aluminium composite oxide to be in the condition of high temperature for a long time, cause cerium-aluminium composite oxide to sinter, reduce its specific area.Preferably, the roasting time in described step (1) is 3h to the best.
Preferably, the roasting in described step (2) is roasting 3 ~ 4h at 550 ~ 650 DEG C.Preferably, the roasting time in described step (2) is 3.5h to the best.
Preferably, the platinum salt in described step (3) is one or more in platinum nitrate, chloroplatinic acid, acetic acid platinum, cyaniding platinum, platinic hydroxide, xenon platinum hexafluoride and ammonium chloroplatinate.
Preferably, in described step (3), the weight ratio of citric acid and cerium-aluminium composite oxide is 1:3 ~ 9.In the preparation process of catalyst pulp, the effect of citric acid is the pH value regulating slurry, changes slurry fluidity.When the weight ratio of citric acid and cerium-aluminium composite oxide is 1:3 ~ 9, can be made by the mode of dipping that slurry is better must be coated in cordierite ceramic surface.Citric acid, in roasting process, can generate carbon dioxide and water with oxygen reaction, can not remain in catalyst coat.Preferably, in described step (3), the weight ratio of citric acid and cerium-aluminium composite oxide is 1:5 ~ 9.Preferably, in described step (3), the weight ratio of citric acid and cerium-aluminium composite oxide is 1:5 to the best.
Preferably, the roasting time in described step (6) is 2 ~ 3h.The platinum obtained/cerium aluminium-molecular sieve catalyst catalytic activity is good, selective height.Preferably, described roasting time is 2.5h to the best.
Beneficial effect of the present invention is:
(1) platinum of the present invention/cerium aluminium-molecular sieve catalyst take cordierite ceramic as carrier, with noble metal platinum, cerium-aluminium composite oxide and neodymium modified molecular screen are catalytic active center, noble metal platinum is distributed on cerium-aluminium composite oxide and neodymium modified molecular screen, and by regulating catalyst layer at the coated weight of carrier surface, and noble metal platinum in catalyst layer, the weight of cerium-aluminium composite oxide and neodymium modified molecular screen, even if it is wide to make described platinum/cerium aluminium-molecular sieve catalyst also can realize low temperature active window under high air speed (SV), catalytic activity is good, ammonia can be transformed completely at 225 DEG C, selective height simultaneously, effectively can suppress N 2o, NO, NO 2the generation of secondary pollution.
(2) preparation method's cost of platinum of the present invention/cerium aluminium-molecular sieve catalyst is low, and toxicity is little, simple to operate, easily controls.
Accompanying drawing explanation
Fig. 1 is the NH of various ammonia VPO catalysts 3conversion ratio chart.
The N of the various ammonia VPO catalysts of Fig. 2 2o discharges concentration chart.
Fig. 3 is the NO of various ammonia VPO catalysts xdischarge concentration chart.
Detailed description of the invention
Below in conjunction with test example and detailed description of the invention, the present invention is described in further detail.But this should be interpreted as that the scope of the above-mentioned theme of the present invention is only limitted to following embodiment, all technology realized based on content of the present invention all belong to scope of the present invention.
In embodiment of the present invention and comparative example, the cordierite ceramic adopted is diameter 25.4mm, the cylindrical cordierite pottery of high 25.4mm.
Embodiment 1
(1) cerium-aluminium composite oxide preparation
Get the aluminum nitrate solution 261.0ml of 0.4g/ml, the cerous nitrate solution 236.7ml of 0.2g/ml, and the citric acid solution 758.7ml of 0.2g/ml mixes; Stir 2h, re-use Rotary Evaporators evaporating water, dry 20h at 120 DEG C, finally put into Muffle furnace, from room temperature to 650 DEG C, and at 650 DEG C roasting 3h, obtain cerium-aluminium composite oxide, in this cerium-aluminium composite oxide, the mass ratio of aluminium oxide and cerium oxide is 1:1.
(2) neodymium modified molecular screen preparation
The neodymium nitrate solution 29.5ml getting 0.2g/ml joins in 47g ZSM-5 molecular sieve powder, then puts into baking oven, dry 10h at 100 DEG C; Then put into Muffle furnace, at 600 DEG C of roasting 3.5h, obtain neodymium modified molecular screen; In this neodymium modified molecular screen, neodymium element exists with the form of neodymia, and the mass ratio of neodymia and ZSM-5 molecular sieve is 6:94.
(3) preparation of catalyst pulp
Get 50g cerium-aluminium composite oxide, 50g neodymium modified molecular screen powder, 10g citric acid, 1.588g platinum nitrate solution (metal platinum 2.78wt%) join in 112.3ml deionized water, stir, obtain catalyst pulp.
(4) ball milling catalyst pulp: ground through planetary ball mill by catalyst pulp, makes pulp particle be 2 ~ 5 μm, obtains catalyst pulp; Wherein the rotating speed of planetary ball mill is 380 ~ 400 revs/min, and milling time is 1 ~ 1.5h.
(5) slurry is applied: be immersed into by cordierite ceramic matrix in the catalyst pulp after grinding, submergence 3 ~ 5min; Taken out from slurry by cordierite ceramic matrix, blow leftover slurry in duct off, obtain the cordierite ceramic being coated with catalyst pulp, wherein the weightening finish of cordierite ceramic surface is 4.42g, and in final catalyst unit volume, Pt content is 2g/ft 3.
(6) dry and roasting: cordierite ceramic surface being coated with catalyst pulp, at 100 DEG C of dry 6h, then puts into Muffle furnace, roasting 2.5h at 600 DEG C, obtains platinum/cerium aluminum molecular screen catalyst, the Pt-1/CA-ZSM namely in accompanying drawing; Wherein the coated weight of catalyst pulp after roasting reaches 155 ~ 165g/L.
Get catalyst pulp 20g prepared by above-mentioned steps (4) and put into Muffle furnace, at 550 ~ 650 DEG C, roasting 1 ~ 2h, is finally cooled to room temperature, weighs, and it is 9.348g that result obtains powder quality, and namely the solid content of catalyst pulp is 46.74%.Take powder 10g more subsequently, after the steps such as dissolving, precipitation, filtration, dissolving, adopt inductively coupled plasma to carry out the mensuration of noble metal platinum content, it is 0.0441 (platinum that result obtains the content of noble metal platinum in powder, g)/100 (powder, g).
From the above, in platinum of the present invention/cerium aluminum molecular screen catalyst, the weight ratio of cerium-aluminium composite oxide, neodymium modified molecular sieve catalyst and noble metal platinum is 50:50:0.0441.
Embodiment 2
(1) cerium-aluminium composite oxide preparation
Get the aluminum nitrate solution 835.3ml of 0.2g/ml, the cerous nitrate solution 252.2ml of 0.3g/ml, and the citric acid solution 1213.6ml of 0.2g/ml mixes; Stir 2h, re-use Rotary Evaporators evaporating water, dry 20h at 120 DEG C, finally put into Muffle furnace, from room temperature to 650 DEG C, and at 650 DEG C roasting 3h, obtain cerium-aluminium composite oxide, in this cerium-aluminium composite oxide, the mass ratio of aluminium oxide and cerium oxide is 4:3.
(2) neodymium modified molecular screen preparation
Get the neodymium nitrate solution 23.6ml of 0.1g/ml, join in 28.8g ZSM-5 molecular sieve powder, then put into baking oven, dry 8h at 120 DEG C; Then put into Muffle furnace, at 650 DEG C of roasting 3h, obtain neodymium modified molecular screen; In this neodymium modified molecular screen, neodymium element exists with the form of neodymia, and the mass ratio of neodymia and ZSM-5 molecular sieve is 4:96.
(3) preparation of catalyst pulp
Get 70g cerium-aluminium composite oxide, 30g neodymium modified molecular screen powder, 10.0g citric acid, 2.054g platinum nitrate solution (metal platinum 2.78wt%) join in 110.8ml deionized water, stir, obtain catalyst pulp.
(4) ball milling catalyst pulp: ground through planetary ball mill by catalyst pulp, makes pulp particle be 2 ~ 5 μm, obtains catalyst pulp; Wherein the rotating speed of planetary ball mill is 380 ~ 400 revs/min, and milling time is 1 ~ 1.5h.
(5) slurry is applied: be immersed into by cordierite ceramic matrix in the catalyst pulp after grinding, submergence 3 ~ 5min; Taken out from slurry by cordierite ceramic matrix, blow leftover slurry in duct off, obtain the cordierite ceramic being coated with catalyst pulp, wherein the weightening finish of cordierite ceramic surface is 3.39g, and in final catalyst unit volume, Pt content is 2g/ft 3.
(6) dry and roasting: cordierite ceramic surface being coated with catalyst pulp, at 120 DEG C of dry 4h, then puts into Muffle furnace, roasting 2h at 650 DEG C, obtains platinum/cerium aluminum molecular screen catalyst, the Pt-2/CA-ZSM namely in accompanying drawing; Wherein the coated weight of catalyst pulp after roasting reaches 120 ~ 130g/L.
Get catalyst pulp 20g prepared by above-mentioned steps (4) and put into Muffle furnace, at 550 ~ 650 DEG C, roasting 1 ~ 2h, is finally cooled to room temperature, weighs, and it is 9.506g that result obtains powder quality, and namely the solid content of catalyst pulp is 47.03%.Take powder 10g more subsequently, after the steps such as dissolving, precipitation, filtration, dissolving, adopt inductively coupled plasma to carry out the mensuration of noble metal platinum content, it is 0.0571 (platinum that result obtains the content of noble metal platinum in powder, g)/100 (powder, g).
From the above, in platinum of the present invention/cerium aluminum molecular screen catalyst, the weight ratio of cerium-aluminium composite oxide, neodymium modified molecular sieve catalyst and noble metal platinum is 70:30:0.0571.
Embodiment 3
(1) cerium-aluminium composite oxide preparation
Get the aluminum nitrate solution 348.0ml of 0.3g/ml, the cerous nitrate solution 71.1ml of 0.4g/ml, and the citric acid solution 664.2ml of 0.2g/ml mixes; Stir 1.5h, re-use Rotary Evaporators evaporating water, dry 24h at 100 DEG C, finally put into Muffle furnace, from room temperature to 550 DEG C, and at 550 DEG C roasting 4h, obtain cerium-aluminium composite oxide, in this cerium-aluminium composite oxide, the mass ratio of aluminium oxide and cerium oxide is 5:3.
(2) neodymium modified molecular screen preparation
Get the neodymium nitrate solution 11.8ml of 0.2g/ml, join in 58.8g ZSM-5 molecular sieve powder, then put into baking oven, dry 8h at 120 DEG C; Then put into Muffle furnace, at 550 DEG C of roasting 4h, obtain neodymium modified molecular screen; In this neodymium modified molecular screen, neodymium element exists with the form of neodymia, and the mass ratio of neodymia and ZSM-5 molecular sieve is 2:98.
(3) preparation of catalyst pulp
Get 40g cerium-aluminium composite oxide, 60g neodymium modified molecular screen powder, 10g citric acid, 1.469g platinum nitrate solution (metal platinum 2.78wt%) join in 115.2ml deionized water, stir, obtain catalyst pulp.
(4) ball milling catalyst pulp: ground through planetary ball mill by catalyst pulp, makes pulp particle be 2 ~ 5 μm, obtains catalyst pulp; Wherein the rotating speed of planetary ball mill is 380 ~ 400 revs/min, and milling time is 1 ~ 1.5h.
(5) slurry is applied: be immersed into by cordierite ceramic matrix in the catalyst pulp after grinding, submergence 3 ~ 5min; Taken out from slurry by cordierite ceramic matrix, blow leftover slurry in duct off, obtain the cordierite ceramic being coated with catalyst pulp, wherein the weightening finish of cordierite ceramic surface is 4.82g, and in final catalyst unit volume, Pt content is 2g/ft 3.
(6) dry and roasting: cordierite ceramic surface being coated with catalyst pulp, at 120 DEG C of dry 4h, then puts into Muffle furnace, roasting 3h at 550 DEG C, obtains platinum/cerium aluminum molecular screen catalyst, the Pt-3/CA-ZSM namely in accompanying drawing; Wherein the coated weight of catalyst pulp after roasting reaches 170 ~ 180g/L.
Get catalyst pulp 20g prepared by above-mentioned steps (4) and put into Muffle furnace, at 550 ~ 650 DEG C, roasting 1 ~ 2h, is finally cooled to room temperature, weighs, and it is 9.23g that result obtains powder quality, and namely the solid content of catalyst pulp is 46.15%.Take powder 10g more subsequently, after the steps such as dissolving, precipitation, filtration, dissolving, adopt inductively coupled plasma to carry out the mensuration of noble metal platinum content, it is 0.0408 (platinum that result obtains the content of noble metal platinum in powder, g)/100 (powder, g).
From the above, in platinum of the present invention/cerium aluminum molecular screen catalyst, the weight ratio of cerium-aluminium composite oxide, neodymium modified molecular sieve catalyst and noble metal platinum is 40:60:0.0408.
Comparative example 1
Step (1) is with embodiment 1.
(2) preparation of catalyst pulp
Get 100g cerium-aluminium composite oxide, 10g citric acid, 1.588g platinum nitrate solution (metal platinum 2.78wt%) join in 107.5ml deionized water, stir, obtain catalyst pulp.
(3) with the step (4) in embodiment 1.
(4) apply slurry: with the step (5) in embodiment 1, the weightening finish of cordierite ceramic surface is 4.31g, and in final catalyst unit volume, Pt content is 2g/ft 3.
(5) dry and roasting: with the step (6) in embodiment 1, obtain ammonia VPO catalysts, the Pt-1/CA-1 namely in accompanying drawing.
Get catalyst pulp 20g prepared by step (4) and put into Muffle furnace, at 550 ~ 650 DEG C, roasting 1 ~ 2h, is finally cooled to room temperature, weighs, and it is 9.569g that result obtains powder quality, and namely the solid content of catalyst pulp is 47.85%.Take powder 10g more subsequently, after the steps such as dissolving, precipitation, filtration, dissolving, adopt ICP to carry out the mensuration of noble metal platinum content, it is 0.0441 platinum that result obtains the content of noble metal platinum in powder, g)/100 (powder, g).
From the above, in platinum of the present invention/cerium aluminum molecular screen catalyst, the weight ratio of cerium-aluminium composite oxide, neodymium modified molecular sieve catalyst and noble metal platinum is 100:0:0.0441.
Comparative example 2
(1) cerium-aluminium composite oxide preparation
With the step (1) in embodiment 1.
(2) preparation of catalyst pulp
Get 100g cerium-aluminium composite oxide, 10g citric acid, 3.113g platinum nitrate solution (metal platinum 2.78wt%) join in 104.6ml deionized water, stir, obtain catalyst pulp.
(3) ball milling catalyst pulp: with the step (4) in embodiment 1.
(4) slurry is applied: be immersed into by cordierite ceramic matrix in the catalyst pulp after grinding, submergence 3 ~ 5min; Taken out from slurry by cordierite ceramic matrix, blow leftover slurry in duct off, obtain the cordierite ceramic being coated with catalyst pulp, wherein the weightening finish of cordierite ceramic surface is 2.18g, and in final catalyst unit volume, Pt content is 2g/ft 3.
(6) dry and roasting: cordierite ceramic surface being coated with catalyst pulp, at 100 DEG C of dry 6h, is then put into Muffle furnace, roasting 2.5h at 600 DEG C, obtained ammonia VPO catalysts, the Pt-1/CA-2 namely in accompanying drawing; Wherein the coated weight of catalyst pulp after roasting reaches 78 ~ 83g/L.
Get catalyst pulp 20g prepared by above-mentioned steps (4) and put into Muffle furnace, at 550 ~ 650 DEG C, roasting 1 ~ 2h, is finally cooled to room temperature, weighs, and it is 9.632g that result obtains powder quality, and namely the solid content of catalyst pulp is 48.16%.Take powder 10g more subsequently, after the steps such as dissolving, precipitation, filtration, dissolving, adopt inductively coupled plasma to carry out the mensuration of noble metal platinum content, it is 0.0865 (platinum that result obtains the content of noble metal platinum in powder, g)/100 (powder, g).
From the above, in platinum of the present invention/cerium aluminum molecular screen catalyst, the weight ratio of cerium-aluminium composite oxide, neodymium modified molecular sieve catalyst and noble metal platinum is 100:0:0.0865.
Comparative example 3
(1) cerium-aluminium composite oxide preparation
With embodiment 1.
(2) preparation of catalyst pulp
Get 50g cerium-aluminium composite oxide, 50g ZSM-5 molecular sieve powder, 10g citric acid, 1.588g platinum nitrate solution join in 113.1ml deionized water, stir, obtain catalyst pulp.
(3) ball milling catalyst pulp: with the step (4) in embodiment 1.
(4) apply slurry: with the step (5) in embodiment 1, wherein the weightening finish of cordierite ceramic surface is 4.35g, and in final catalyst unit volume, Pt content is 2g/ft 3.
(5) dry and roasting: with the step (6) in embodiment 1, obtain ammonia VPO catalysts.Namely the Pt-1/CA-3 in accompanying drawing.
Get catalyst pulp 20g prepared by above-mentioned steps (3) and put into Muffle furnace, at 550 ~ 650 DEG C, roasting 1 ~ 2h, is finally cooled to room temperature, weighs, and it is 9.324g that result obtains powder quality, and namely the solid content of catalyst pulp is 46.62%.Take powder 10g more subsequently, after the steps such as dissolving, precipitation, filtration, dissolving, adopt inductively coupled plasma to carry out the mensuration of noble metal platinum content, it is 0.0441 (platinum that result obtains the content of noble metal platinum in powder, g)/100 (powder, g).
From the above, in platinum of the present invention/cerium aluminum molecular screen catalyst, the weight ratio of cerium-aluminium composite oxide, molecular sieve catalyst and noble metal platinum is 50:50:0.0441.
Experimental example 1
Catalytic performance test is carried out to catalyst prepared by above-described embodiment 1 ~ 3 and comparative example 1 ~ 3.
By the ammonia (NH of 200ppm 3), 10% oxygen (O 2), 7% carbon dioxide (CO 2), 8% steam (H 2o), all the other are nitrogen (N 2) mist pass into model gas experimental rig, reaction velocity is 150000 ~ 160000h -1under 200 DEG C, 225 DEG C, 250 DEG C, 300 DEG C, 350 DEG C, 400 DEG C, 450 DEG C and 500 DEG C of eight temperature conditions, reach set point of temperature and concentration gases circulation start after have passed through 30 minutes after, measure under the concentration of various gas componant is stable state.Metered catalyst entrance and exit place NH respectively 3, NO 2, NO, N 2the gas concentration of O, utilizes NH 3conversion ratio, NOx discharge concentration, N 2o discharges these 3 indexs of concentration and evaluates catalyst (ASC) performance.
Wherein: NH 3conversion ratio %=(entrance NH 3concentration-outlet NH 3concentration)/(entrance NH 3concentration) × 100
(NOx discharges concentration ppm)=(outlet NO concentration ppm)+(outlet NO 2concentration ppm)
Result is as shown in table 1 ~ 3.
Fig. 1 is that each catalyst is to NH 3conversion ratio chart.Known as shown in Figure 1, the catalyst prepared due to the embodiment of the present invention 1 ~ 3 comprises specific cerium-aluminium composite oxide and neodymium modified molecular screen (Nd/ZSM-5) powder as catalyst carrier, namely noble metal platinum is distributed on cerium-aluminium composite oxide and neodymium modified molecular screen, in 225 ~ 500 DEG C of intervals to NH 3conversion ratio all reach more than 90%, NH 3substantially be converted completely.
And catalyst prepared by comparative example 1,2 is not owing to adopting the molecular sieve of neodymium modification, cause NH 3conversion ratio comparatively embodiment 1 ~ 3 have obvious decline, especially 225 DEG C time, to NH 3conversion ratio be only about 70%, when catalyst-coated quantity not sufficient, catalytic performance obviously reduces.
Catalyst prepared by comparative example 3 carries out modification owing to not adopting neodymium to molecular sieve, causes NH 3conversion ratio comparatively embodiment 1 ~ 3 has decline, especially 225 DEG C time, to NH 3low conversion rate in 90%.
Fig. 2 is the N of each catalyst 2o discharges concentration chart.As shown in Figure 2, catalyst prepared by the embodiment of the present invention 1 ~ 3, its exit N 2the discharge concentration of O is very low, within the scope of 200 ~ 500 DEG C, is all less than 30ppm, especially within the scope of 200 ~ 250 DEG C and 400 ~ 500 DEG C, is all less than 15ppm.Show, platinum of the present invention/cerium aluminum molecular screen catalyst is to NH 3while there is the conversion ratio of more than 90%, can also significantly suppress harmful side product N 2the generation of O.
By the N of comparative example 1 ~ 3 2o discharges concentration compared with embodiment 1 ~ 3, within the scope of 200 ~ 500 DEG C, and its N 2the eliminating concentration of O has raising in various degree, especially within the scope of 300 ~ 400 DEG C, improves about 5 ~ 15ppm respectively.
Fig. 3 is the NO of each catalyst xget rid of concentration chart.As shown in Figure 3, catalyst prepared by the embodiment of the present invention 1 ~ 3, its exit NO xdischarge concentration very low, within the scope of 200 ~ 500 DEG C, be all less than 110ppm, especially at 200 ~ 300 DEG C, be all less than 20ppm.Show, platinum of the present invention/cerium aluminum molecular screen catalyst is to NH 3while there is the conversion ratio of more than 90%, can also significantly suppress harmful side product NO xgeneration.This is due to NH 3with NO or NO 2reaction, generates nontoxic N 2and H 2o discharges.
By the NO of comparative example 1 ~ 3 xdischarge concentration compared with embodiment 1 ~ 3, within the scope of 200 ~ 500 DEG C, its NO xeliminating concentration have raising in various degree, and obvious with the eliminating concentration difference of embodiment 1 ~ 3.
From Fig. 1 ~ 3, platinum of the present invention/cerium aluminium-molecular sieve catalyst can obtain the NH higher than prior art 3transformation efficiency, and significantly can suppress N 2o accessory substance and adjoint NH 3the NO that incomplete oxidation causes xthe generation of accessory substance.Therefore, platinum of the present invention/cerium aluminum molecular screen catalyst can be widely used in Diesel engine and leak NH 3purification.
The NH of the platinum again prepared by embodiment 1/cerium aluminium-molecular sieve catalyst 3conversion ratio, N 2o discharges concentration and NO xplatinum/cerium aluminum molecular screen catalyst that discharge concentration is prepared with embodiment 2 and 3 is compared: at 200 ~ 500 DEG C, the NH of embodiment 1 3conversion ratio higher than embodiment 2, only a little less than embodiment 3.But the N of embodiment 1 2o, NO xdischarge concentration compared with embodiment 3, all have and reduce in various degree; And the coated weight of embodiment 3 is larger, cost increases, and affects Fuel Economy.To sum up, embodiment 1 is in preferably effect with less advantage, is optimum implementation of the present invention.

Claims (10)

1. the platinum for catalytic oxidation ammonia/cerium aluminium-molecular sieve catalyst, take cordierite ceramic as carrier, carrier surface is coated with catalyst layer, it is characterized in that: the catalytic active center of described catalyst layer is made up of noble metal platinum, cerium-aluminium composite oxide and neodymium modified molecular screen; The weight ratio of described cerium-aluminium composite oxide, neodymium modified molecular screen and noble metal platinum is 20 ~ 80:20 ~ 80:0.01 ~ 0.1; In described cerium-aluminium composite oxide, the weight ratio of cerium oxide and aluminium oxide is 1 ~ 3:1 ~ 5; In described neodymium modified molecular screen, the weight ratio of neodymia and molecular sieve is 1 ~ 10:90 ~ 100.
2. platinum according to claim 1/cerium aluminium-molecular sieve catalyst, is characterized in that: described catalyst carrier surface coated weight according to the dry weight of catalyst layer be 120 ~ 180g/L calculate.
3. platinum according to claim 1/cerium aluminium-molecular sieve catalyst, is characterized in that: described molecular sieve is ZSM-5 molecular sieve.
4. platinum according to claim 1/cerium aluminium-molecular sieve catalyst, is characterized in that: the weight ratio of described cerium-aluminium composite oxide, neodymium modified molecular screen and noble metal platinum is 40 ~ 70:30 ~ 60:0.04 ~ 0.06.
5. the preparation method of platinum/cerium aluminium-molecular sieve catalyst as described in any one of Claims 1 to 4, is characterized in that, comprise the following steps:
(1) preparation of cerium-aluminium composite oxide
Get the aluminum nitrate solution of 0.1 ~ 0.4g/ml and the cerous nitrate solution of 0.1 ~ 0.4g/ml, mix, join in the citric acid solution of 0.1 ~ 0.3g/ml, stir 1 ~ 2h, evaporating water, then dry, roasting, obtains cerium-aluminium composite oxide;
(2) preparation of neodymium modified molecular screen
Join in molecular sieve powder by the neodymium nitrate solution of 0.1 ~ 0.4g/ml, dry, then roasting, obtains neodymium modified molecular screen powder;
(3) preparation of slurry
Cerium-aluminium composite oxide, neodymium modified molecular screen powder, citric acid and platinum salt are joined in deionized water, fully stirs, obtain catalyst pulp;
(4) ground slurry: grind catalyst pulp, until catalyst pulp particle is 2 ~ 5 μm;
(5) slurry is applied: take cordierite ceramic as carrier, be immersed into by cordierite ceramic in the catalyst pulp after grinding; Then cordierite ceramic is taken out from catalyst pulp, blow remainder catalyst slurry in duct off, obtain the cordierite ceramic that surface is coated with catalyst pulp;
(6) dry and roasting: cordierite ceramic surface being coated with catalyst pulp carries out drying, and then roasting, is finally cooled to room temperature, obtains platinum/cerium aluminium-molecular sieve catalyst; Wherein the coated weight of catalyst pulp after roasting is 120 ~ 180g/L.
6. preparation method according to claim 5, is characterized in that: in described step (1), the volume ratio of aluminum nitrate solution and citric acid solution is 1:1 ~ 4.
7. preparation method according to claim 5, is characterized in that: the roasting in described step (1) is roasting 3 ~ 4h at 550 ~ 650 DEG C.
8. preparation method according to claim 5, is characterized in that: the platinum salt in described step (3) is one or more in platinum nitrate, chloroplatinic acid, acetic acid platinum, cyaniding platinum, platinic hydroxide, xenon platinum hexafluoride and ammonium chloroplatinate.
9. the preparation method according to claim 5 or 8, is characterized in that: in described step (3), the weight ratio of citric acid and cerium-aluminium composite oxide is 1:3 ~ 9.
10. preparation method according to claim 5, is characterized in that: the roasting in described step (6) is roasting 2 ~ 3h at 550 ~ 650 DEG C.
CN201510306885.2A 2015-06-05 2015-06-05 Platinum/cerium aluminum molecular screen catalyst for catalysis oxidation ammonia and preparation method thereof Active CN104888845B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201510306885.2A CN104888845B (en) 2015-06-05 2015-06-05 Platinum/cerium aluminum molecular screen catalyst for catalysis oxidation ammonia and preparation method thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201510306885.2A CN104888845B (en) 2015-06-05 2015-06-05 Platinum/cerium aluminum molecular screen catalyst for catalysis oxidation ammonia and preparation method thereof

Publications (2)

Publication Number Publication Date
CN104888845A true CN104888845A (en) 2015-09-09
CN104888845B CN104888845B (en) 2017-08-25

Family

ID=54022049

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201510306885.2A Active CN104888845B (en) 2015-06-05 2015-06-05 Platinum/cerium aluminum molecular screen catalyst for catalysis oxidation ammonia and preparation method thereof

Country Status (1)

Country Link
CN (1) CN104888845B (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109261200A (en) * 2018-09-30 2019-01-25 无锡威孚环保催化剂有限公司 NH_3 leakage catalyst and preparation method thereof for equivalent burn natural gas engines
CN110075907A (en) * 2019-05-08 2019-08-02 中自环保科技股份有限公司 A kind of ammoxidation catalyst and preparation method thereof for diesel car tail gas refining
CN112547115A (en) * 2019-09-26 2021-03-26 中国石油化工股份有限公司 Multi-effect catalyst for waste gas purification and waste gas purification method
CN113578374A (en) * 2021-07-30 2021-11-02 芜湖美的厨卫电器制造有限公司 Peculiar smell removing catalyst and preparation method and application thereof
CN116139923A (en) * 2022-12-28 2023-05-23 济南大学 Method for preparing Cu-based small-pore molecular sieve catalyst by gradient loading method, obtained product and application
EP4183485A4 (en) * 2021-09-01 2024-01-24 Ningbo Geely Royal Engine Components Co Ltd Ammonia adsorption catalyst, and preparation method therefor and use thereof

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1342520A (en) * 2000-09-14 2002-04-03 中国科学院生态环境研究中心 Catalyst for cleaning tail gas of car and its preparing process
CN101417237A (en) * 2008-11-27 2009-04-29 中国科学院生态环境研究中心 PtX-Fe-ZSM-5 molecular sieve catalyst for ammine selective catalytic oxidation
CN102740966A (en) * 2009-11-19 2012-10-17 Sk新技术株式会社 Catalyst for selective oxidation of nh3 to n2 and method for preparing the same
CN103170330A (en) * 2013-02-26 2013-06-26 四川中自尾气净化有限公司 SOF (Soluble Organic Fractions) high-oxidation catalyst and preparation method thereof
CN103464152A (en) * 2013-09-29 2013-12-25 福州大学 Catalyst for tail gas purification and preparation method thereof
CN104096574A (en) * 2013-04-12 2014-10-15 财团法人工业技术研究院 Catalyst for oxidizing ammonia and method for removing ammonia in gas

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1342520A (en) * 2000-09-14 2002-04-03 中国科学院生态环境研究中心 Catalyst for cleaning tail gas of car and its preparing process
CN101417237A (en) * 2008-11-27 2009-04-29 中国科学院生态环境研究中心 PtX-Fe-ZSM-5 molecular sieve catalyst for ammine selective catalytic oxidation
CN102740966A (en) * 2009-11-19 2012-10-17 Sk新技术株式会社 Catalyst for selective oxidation of nh3 to n2 and method for preparing the same
CN103170330A (en) * 2013-02-26 2013-06-26 四川中自尾气净化有限公司 SOF (Soluble Organic Fractions) high-oxidation catalyst and preparation method thereof
CN104096574A (en) * 2013-04-12 2014-10-15 财团法人工业技术研究院 Catalyst for oxidizing ammonia and method for removing ammonia in gas
CN103464152A (en) * 2013-09-29 2013-12-25 福州大学 Catalyst for tail gas purification and preparation method thereof

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
YI LUO ET AL.: "The adsorption of nitrogen oxides and water on rare-earth ion-exchanged ZSM-5: a density functional study", 《APPLIED SURFACE SCIENCE》 *
张丽等: "CeO2 添加对 Ag/Al2O3催化剂低温氨氧化性能的影响", 《催化学报》 *

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109261200A (en) * 2018-09-30 2019-01-25 无锡威孚环保催化剂有限公司 NH_3 leakage catalyst and preparation method thereof for equivalent burn natural gas engines
CN110075907A (en) * 2019-05-08 2019-08-02 中自环保科技股份有限公司 A kind of ammoxidation catalyst and preparation method thereof for diesel car tail gas refining
CN112547115A (en) * 2019-09-26 2021-03-26 中国石油化工股份有限公司 Multi-effect catalyst for waste gas purification and waste gas purification method
CN113578374A (en) * 2021-07-30 2021-11-02 芜湖美的厨卫电器制造有限公司 Peculiar smell removing catalyst and preparation method and application thereof
EP4183485A4 (en) * 2021-09-01 2024-01-24 Ningbo Geely Royal Engine Components Co Ltd Ammonia adsorption catalyst, and preparation method therefor and use thereof
CN116139923A (en) * 2022-12-28 2023-05-23 济南大学 Method for preparing Cu-based small-pore molecular sieve catalyst by gradient loading method, obtained product and application
CN116139923B (en) * 2022-12-28 2024-04-05 济南大学 Method for preparing Cu-based small-pore molecular sieve catalyst by gradient loading method, obtained product and application

Also Published As

Publication number Publication date
CN104888845B (en) 2017-08-25

Similar Documents

Publication Publication Date Title
CN104888845A (en) Platinum/cerium aluminum-molecular sieve catalyst for catalytic oxidation of ammonia gas and preparation method thereof
JP5373255B2 (en) NOx reduction catalyst, NOx reduction catalyst system, and NOx reduction method
US10179328B2 (en) Low temperature SCR catalyst for denitrating diesel vehicle exhaust, and preparation method thereof
CN102553574B (en) Method for preparing flue gas SCR (Selective Catalytic Reduction) denitration catalyst
CN109092325A (en) A kind of catalyst and the preparation method and application thereof for low-temperature denitration of flue gas
CN103433057A (en) Three-way catalyst used for automobile emission purification and preparation method thereof
CN104338545B (en) A kind of efficient SCR catalyst that is applied to diesel engine vent gas purification of nitrogen oxides
CN109569587A (en) A kind of manganese-based low-temperature catalyst for denitrating flue gas and preparation method thereof
CN106944130A (en) A kind of SCR AOC combination catalysts of purification of diesel tail gas and preparation method thereof
US8252257B2 (en) Method for purifying gas, gas purifying apparatus, and gas purifying catalyst
CN101254464A (en) Composite catalyst flue gas denitrating under low-temperature condition and method of preparing the same
CN106902864A (en) A kind of ammoxidation catalyst for diesel engine vent gas cleaning system and preparation method thereof
JP4090547B2 (en) Exhaust gas purification catalyst
CN105854874A (en) Denitrification catalyst, preparation method of denitrification catalyst and application of denitrification catalyst in flue gas denitrification
CN102259009A (en) Sulfate radical promoted TiO2 carrier based SCR (Selective Catalytic Reduction) flue gas denitration catalyst and preparation method thereof
CN108187665B (en) Denitration catalyst and preparation method thereof
CN106824174A (en) A kind of coccoid catalyst of high-efficient purification nitrogen oxides and preparation method thereof
CN101554589A (en) Copper and iron modified titanium dioxide pillared bentonite catalyst and preparation method thereof
WO2020073667A1 (en) Integrated catalyst system for stoichiometric-burn natural gas vehicles and preparation method therefor
CN111905721B (en) Catalyst for low-temperature denitration and demercuration of titanium dioxide nano array and preparation method thereof
CN103894184B (en) A kind of high-specific surface area vanadium zinc system's modification denitrating catalyst and preparation method
CN104971719A (en) Method for preparing catalyst for RCO-SCR (Regenerative Catalytic Oxidation-Selective Catalytic Reduction) integrated reaction
CN103349980B (en) A kind of cerium base catalyst and preparation method thereof and the application in nitrous oxides selectivity catalysis reduction
CN114146705A (en) High water resistance nano-carrier low-temperature ammonia catalytic oxidation catalyst
CN109225260B (en) Regeneration method of Ce-based SCR denitration catalyst for sulfur poisoning

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
CB02 Change of applicant information

Address after: 611731, No. 88, Nan Jie street, hi tech Zone, Sichuan, Chengdu

Applicant after: SINOCAT ENVIRONMENTAL TECHNOLOGY CO., LTD.

Address before: 611731, No. 88, Nan Jie street, hi tech Zone, Sichuan, Chengdu

Applicant before: Sichuan Zhongzi Exhaust Purge Co., Ltd.

COR Change of bibliographic data
GR01 Patent grant
GR01 Patent grant
PE01 Entry into force of the registration of the contract for pledge of patent right

Denomination of invention: Platinum/cerium aluminum-molecular sieve catalyst for catalytic oxidation of ammonia gas and preparation method thereof

Effective date of registration: 20181012

Granted publication date: 20170825

Pledgee: Chengdu small business financing Company Limited by Guarantee

Pledgor: SINOCAT ENVIRONMENTAL TECHNOLOGY CO., LTD.

Registration number: 2018510000100

PE01 Entry into force of the registration of the contract for pledge of patent right
PC01 Cancellation of the registration of the contract for pledge of patent right

Date of cancellation: 20191021

Granted publication date: 20170825

Pledgee: Chengdu small business financing Company Limited by Guarantee

Pledgor: SINOCAT ENVIRONMENTAL TECHNOLOGY CO., LTD.

Registration number: 2018510000100

PC01 Cancellation of the registration of the contract for pledge of patent right
PE01 Entry into force of the registration of the contract for pledge of patent right

Denomination of invention: Platinum/cerium aluminum-molecular sieve catalyst for catalytic oxidation of ammonia gas and preparation method thereof

Effective date of registration: 20191030

Granted publication date: 20170825

Pledgee: Chengdu small business financing Company Limited by Guarantee

Pledgor: SINOCAT ENVIRONMENTAL TECHNOLOGY CO., LTD.

Registration number: Y2019510000045

PE01 Entry into force of the registration of the contract for pledge of patent right
PC01 Cancellation of the registration of the contract for pledge of patent right

Date of cancellation: 20201105

Granted publication date: 20170825

Pledgee: Chengdu small business financing Company Limited by Guarantee

Pledgor: Sinocat Environmental Technology Co.,Ltd.

Registration number: Y2019510000045

PC01 Cancellation of the registration of the contract for pledge of patent right