CN102179243A - Catalyst for selective catalytic reduction of nitrogen oxide in moderate/low temperature environment - Google Patents
Catalyst for selective catalytic reduction of nitrogen oxide in moderate/low temperature environment Download PDFInfo
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- CN102179243A CN102179243A CN 201110088471 CN201110088471A CN102179243A CN 102179243 A CN102179243 A CN 102179243A CN 201110088471 CN201110088471 CN 201110088471 CN 201110088471 A CN201110088471 A CN 201110088471A CN 102179243 A CN102179243 A CN 102179243A
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Abstract
The invention belongs to the field of end gas decontamination of diesel cars, and in particular relates to a MnOx-Wo3/TiO3 catalyst for selective catalytic reduction of nitrogen oxide, which is used for treating NOx in the end gas of diesel cars in moderate/low temperature environment (120-300 DEG C) and prepared by an immersion method. The catalyst adopts a common metal oxide MnOx as an active component, the raw materials are low-cost and easily obtained, the use condition is simple, and the catalyst can be mass produced. The catalyst disclosed by the invention can be used for catalyzing ammonia selective reduction nitric oxides to be harmless nitrogen and water in the low temperature environment of 120 DEG C, and the high conversion rate of the catalyst can be kept at about 300 DEG C.
Description
Technical field
The invention belongs to the diesel car tail gas refining field, be specifically related in a kind of processing under the low temperature environment NO in (120 ℃~300 ℃) exhaust gas from diesel vehicle
xThe catalyst of selective catalyst reduction of nitrogen oxides.
Background technology
Motor-vehicle tail-gas was one of the most serious pollution sources in recent years, in the big city because a large amount of buses and diesel-powered trucks of using, pollute very serious, research report according to internal authority mechanism shows, in 150 big cities, the world, Beijing of China, Shanghai, Guangzhou, Xi'an, Shenyang five big city air pollutions come top 10, carry out the research of diesel engine vent gas purification techniques and become to need badly with Study of Catalyst work.The emission of exhaust gas from diesel vehicle mainly is NO
x(mainly being NO) and soot (PM), the discharging of CO and HC is starkly lower than gasoline engine, so Exhaust Control for Diesel Engine focus on PM and NO
xControl.For NO under the excess oxygen
xRemove ammine selectivity catalytic reduction method (NH
3-SCR) be considered to one of effective method.
External practicability the SCR technology with V
2O
5-WO
3/ TiO
2Catalyst is a catalyst system and catalyzing, has good NO in 300 ℃~400 ℃ temperature range
xClean-up effect.But still there are some problems in actual applications in this technology: the one, and the catalyst cost is higher; The 2nd, vanadic anhydride itself is exactly a kind of noxious material; The 3rd, the catalyst temperature active window is narrower, when temperature is lower than 300 ℃, NO
xConversion ratio obviously descends, even less than 50%.For MnO
x-TiO
2Catalyst system and catalyzing has good NO in low temperature range
xConversion ratio, but when temperature surpasses 200 ℃, catalyst can be because heat endurance be not good and sintering etc. is former thereby cause NO
xConversion ratio descends.Tungsten oxide can improve the heat endurance of catalyst as important transition metal oxide, and can provide extra catalytic active center (
The acid position), help NH
3-SCR reaction.Therefore, we are with WO
3Be incorporated into MnO
x-TiO
2Catalyst system and catalyzing is to MnO
x-WO
3/ TiO
2Catalyst has carried out the research in a dark step.
Summary of the invention
The objective of the invention is to overcome the deficiency of above-mentioned two kinds of catalyst, seek and a kind ofly can in middle low temperature range, (120 ℃~300 ℃) have higher NO
xThe NH of conversion ratio
3-SCR catalysts.This catalyst can be widely used in gently, heavy-duty diesel oil car engine and other small-sized universal engine tail gas catalytic purification.
The present invention uses infusion process to make MnO
x-WO
3/ TiO
2Catalyst, its step is as follows:
(1) particle size range had the TiO of single anatase phase at 30~40nm
2Powder mixes stirring at normal temperatures with deionized water, makes TiO
2Slurries, TiO
2Mass concentration be 4~10%;
(2) with tungstic acid hydrate ammonia (traditional Chinese medicines group produces, analyze pure, molecular formula: H
40N
10O
41W
12YH
2O) be dissolved in the oxalic acid solution, heating is stirred to tungstic acid hydrate ammonia and all dissolves, and then the solution that obtains is joined the TiO of step (1)
2In the slurries, tungstic acid hydrate ammonium and TiO
2Mol ratio be 0.007~0.009: 1, continue to stir after 2~5 hours and obtain mixed solution;
(3) mixed solution is continued stir in 85~95 ℃ water-bath, become thickly until mixed solution, take out to be positioned in the baking oven then and under 120~130 ℃ of temperature conditions, dry, make WO
3/ TiO
2The catalyst precursor;
(4) with WO
3/ TiO
2The catalyst precursor is ground to 80 orders~100 orders;
(5) WO after will grinding
3/ TiO
2450~550 ℃ of calcinings 3~6 hours under excess oxygen of catalyst precursor are treated that Muffle furnace naturally cools to take out after the room temperature to be ground to 80 orders~100 orders;
(6) with mass concentration be 50~65% Mn (NO
3)
2Solution dilutes according to 1: 4~8 volume ratio with deionized water, adds the WO in the step (5)
3/ TiO
2Stirred 2~4 hours Mn (NO behind the catalyst precursor powder again
3)
2With TiO
2Mass ratio be 0.4~3: 1; The mixed liquor of above-mentioned steps is continued to stir in 85~95 ℃ water-bath, become thickly until mixed liquor, take out to be positioned in the baking oven then and under 120~130 ℃ of temperature conditions, dry, make MnO
x-WO
3/ TiO
2Catalyst precursor (X=3 or X=4);
(7) with MnO
x-WO
3/ TiO
2The catalyst precursor is ground to 80 orders~100 orders;
(8) MnO after will grinding
x-WO
3/ TiO
2450~550 ℃ of calcinings 3~6 hours under excess oxygen of catalyst precursor are treated that Muffle furnace naturally cools to take out after the room temperature to be ground to 80 orders~100 orders, thereby are made MnO
x-WO
3/ TiO
2Catalyst.
Preparation process of the present invention is simple, and is easy to operate.Compare with existing technology, the present invention has following advantage:
(1) catalyst of the present invention is selected common metal oxide MnO for use
xBe active constituent, raw material is cheap is easy to get in preparation, and service condition is simple, can produce in batches;
(2) catalyst of the present invention can the catalysis ammonia selective reducing nitrogen oxide be harmless nitrogen G﹠W just under 120 ℃ cryogenic conditions, and this high conversion can be remained to about 300 ℃.
Description of drawings
Fig. 1: different MnO
xThe MnO of content
x-WO
3/ TiO
2The XRD spectra of catalyst.From XRD spectra as can be seen, TiO in four general lines
2Have only single Detitanium-ore-type crystalline phase diffraction maximum, use among the figure
Mark; Also all detected WO in four spectral lines simultaneously
3Characteristic diffraction peak, mark with " ◇ " among the figure; And MnO
2Characteristic diffraction peak (marking) with " " only at MnO
x(0.4)-WO
3(0.1)/TiO
2, MnO
x(0.6)-WO
3(0.1)/TiO
2Detect in two kinds of pairing XRD spectral lines of catalyst, at MnO
x(0.1)-WO
3(0.1)/TiO
2, MnO
x(0.2)-WO
3(0.1)/TiO
2Two kinds of corresponding XRD spectral lines of catalyst but do not detect, and the oxide that manganese is described is at WO
3(0.1)/TiO
2Apparent height disperses.
Fig. 2: different MnO
xThe MnO of content
x-WO
3/ TiO
2The ESEM picture of catalyst.As can be seen, sintering phenomenon does not all take place in catalyst, and particle size distribution is even from four width of cloth SEM pictures.
The specific embodiment
In order to be illustrated more clearly in the present invention, enumerate following examples, but it there is not any restriction to scope of the present invention.
Embodiment 1~4:
Take by weighing the 8g particle size range has single anatase phase at 30~40nm TiO
2Powder mixes stirring with the 40ml deionized water, makes TiO
2Fully mix with water, obtain TiO
2Slurries.Take by weighing 2.54g tungstic acid hydrate ammonia and be dissolved in the solution that 30ml contains 5g oxalic acid, heating all joins TiO after the dissolving until tungstic acid hydrate ammonia
2In the slurries, continue to stir 2 hours, in 90 ℃ water-bath, continue to stir evaporate to dryness then, become the taking-up of thick back until mixed liquor and be positioned over 120 ℃ of oven dry in the baking oven, be ground to 80 orders~100 orders, 500 ℃ of calcinings 5 hours under air conditions are then treated that Muffle furnace naturally cools to take out after the room temperature to be ground to 80 orders~100 orders, obtain 10.34g WO
3/ TiO
2Carrier, wherein WO
3With TiO
2Mol ratio be 0.1: 1, be expressed as WO
3(0.1)/TiO
2
The mass concentration that takes by weighing 3.58g then is 50% Mn (NO
3)
2Solution is with the dilution of 80ml deionized water, then with 10.34g WO
3(0.1)/TiO
2Carrier adds wherein, continue to stir 2 hours, in 90 ℃ water-bath, continue to stir evaporate to dryness then, become the taking-up of thick back until mixed liquor and be positioned over 120 ℃ of oven dry in the baking oven, be ground to 80 orders~100 orders, 500 ℃ of calcinings 5 hours under air conditions are then treated that Muffle furnace naturally cools to take out after the room temperature to grind, and obtain 11g MnO
X(0.1)-WO
3(0.1)/TiO
2Catalyst.Change the consumption of nitrate, make to use the same method, obtain catalyst MnO respectively
X(0.2)-WO
3(0.1)/TiO
2, MnO
X(0.4)-WO
3(0.1)/TiO
2And MnO
X(0.6)-WO
3(0.1)/TiO
2The each component raw material uses and sees Table 1.In this example, X=3 or X=4.The catalyst of 0.5ml embodiment 1~4 preparation is positioned over respectively in the quartz tube type fixed bed reactors reacts, experiment condition is as follows:
Reaction condition is NO:500ppm, NH
3: 500ppm, O
2: 2% (volumetric concentration), N
2Be balance gas, total tolerance 400ml/min, reaction velocity (GHSV) is 40000h
-1The reaction temperature interval uses flue gas analyzer (KM9106 Quintox Kane International Limited) every 20 ℃ of real-time NO of record from 80 ℃ to 300 ℃
x(NO and NO
2) concentration, use infrared gas analyser (QGS-08C, north, Beijing is divided) to measure NH
3Concentration, experimental result sees Table 2.
Table 1: raw material use amount
TiO 2 | Tungstic |
50%Mn(NO 3) 2 | ||
Embodiment 1 | Mn?O x(0.1)-WO 3(0.1)/TiO 2 | 8g | 2.54g | 3.58g |
Embodiment 2 | Mn?O x(0.2)-WO 3(0.1)/TiO 2 | 8g | 2.54g | 7.16g |
Embodiment 3 | Mn?O x(0.4)-WO 3(0.1)/TiO 2 | 8g | 2.54g | 14.42g |
Embodiment 4 | Mn?O x(0.6)-WO 3(0.1)/TiO 2 | 8g | 2.54g | 21.48g |
Table 2: the activity of catalyst nitrogen oxides reduction under the differential responses temperature
From above table as can be seen the catalyst the embodiment 1 in 120~300 ℃ temperature range, be 74.9% to the average removal efficiency of nitrogen oxide, catalyst among the embodiment 2 is 98.74% to the average removal efficiency of nitrogen oxide in 120~300 ℃ temperature range, catalyst among the embodiment 3 is 94.53% to the average removal efficiency of nitrogen oxide in 120~300 ℃ temperature range, and the catalyst among the embodiment 4 is 86.2% to the average removal efficiency of nitrogen oxide in 120~300 ℃ temperature range.
Claims (4)
1. the catalyst of selective catalyst reduction of nitrogen oxides under the low temperature environment in a kind, it is prepared by following steps:
1) particle size range had the TiO of single anatase phase at 30~40nm
2Powder mixes stirring at normal temperatures with deionized water, makes TiO
2Slurries;
2) tungstic acid hydrate ammonia is dissolved in the oxalic acid solution, heating is stirred to tungstic acid hydrate ammonia and all dissolves, and then the solution that obtains is joined the TiO of step 1)
2In the slurries, continue stirring and obtain mixed solution after 2~5 hours;
3) mixed solution is continued stir in 85~95 ℃ water-bath, become thickly until mixed solution, take out to be positioned in the baking oven then and under 120~130 ℃ of temperature conditions, dry, make WO
3/ TiO
2The catalyst precursor;
4) with WO
3/ TiO
2The catalyst precursor is ground to 80 orders~100 orders;
5) WO after will grinding
3/ TiO
2450~550 ℃ of calcinings 3~6 hours under excess oxygen of catalyst precursor are treated that Muffle furnace naturally cools to take out after the room temperature to be ground to 80 orders~100 orders;
6) with mass concentration be 50~65% Mn (NO
3)
2Solution dilutes according to 1: 4~8 volume ratio with deionized water, adds the WO in the step 5)
3/ TiO
2Stirred again 2~4 hours behind the catalyst precursor powder; The mixed liquor of above-mentioned steps is continued to stir in 85~95 ℃ water-bath, become thickly until mixed liquor, take out to be positioned in the baking oven then and under 120~130 ℃ of temperature conditions, dry, make MnO
x-WO
3/ TiO
2Catalyst precursor, wherein X=3 or X=4;
7) with MnO
x-WO
3/ TiO
2The catalyst precursor is ground to 80 orders~100 orders;
8) MnO after will grinding
x-WO
3/ TiO
2450~550 ℃ of calcinings 3~6 hours under excess oxygen of catalyst precursor are treated that Muffle furnace naturally cools to take out after the room temperature to be ground to 80 orders~100 orders, thereby are made MnO
x-WO
3/ TiO
2Catalyst.
2. the catalyst of selective catalyst reduction of nitrogen oxides is characterised in that: TiO in the step 1) altogether under a kind of middle low temperature environment as claimed in claim 1
2Mass concentration be 4~10%.
3. the catalyst of selective catalyst reduction of nitrogen oxides is characterised in that: step 2 altogether under a kind of middle low temperature environment as claimed in claim 1) middle tungstic acid hydrate ammonium and TiO
2Mol ratio be 0.007~0.009: 1.
4. the catalyst of selective catalyst reduction of nitrogen oxides is characterised in that: Mn (NO in the step 6) altogether under a kind of middle low temperature environment as claimed in claim 1
3)
2With TiO
2Mass ratio be 0.4~3: 1.
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Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102814192A (en) * | 2012-07-24 | 2012-12-12 | 中国科学院长春应用化学研究所 | Cerium/molecular sieve catalyst used for selective catalytic reduction of nitrogen oxides and preparation method thereof |
CN104162421A (en) * | 2014-08-18 | 2014-11-26 | 南京理工大学 | Preparation method of high temperature resistant vanadium tungsten titanium oxide catalyst |
CN105688932A (en) * | 2016-03-16 | 2016-06-22 | 南京工业大学 | Catalyst for purifying diesel engine tail gas NOX, CO and HC for vehicle and preparation method thereof |
CN113713608A (en) * | 2021-08-26 | 2021-11-30 | 复旦大学 | For CO and NOxSimultaneous removal catalyst combination |
Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US5326735A (en) * | 1992-07-10 | 1994-07-05 | N.E. Chemcat Corporation | Iridium catalysts for purifying exhaust gas |
CN101284238A (en) * | 2008-05-29 | 2008-10-15 | 国电环境保护研究院 | Stationary source ammine selectivity catalytic reduction nitrous oxides series catalysts |
CN101912775A (en) * | 2010-09-03 | 2010-12-15 | 中国汽车技术研究中心 | Selective catalyst for removing oxynitrides from tail gases of diesel vehicles and preparation method thereof |
-
2011
- 2011-04-11 CN CN2011100884719A patent/CN102179243B/en not_active Expired - Fee Related
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US5326735A (en) * | 1992-07-10 | 1994-07-05 | N.E. Chemcat Corporation | Iridium catalysts for purifying exhaust gas |
CN101284238A (en) * | 2008-05-29 | 2008-10-15 | 国电环境保护研究院 | Stationary source ammine selectivity catalytic reduction nitrous oxides series catalysts |
CN101912775A (en) * | 2010-09-03 | 2010-12-15 | 中国汽车技术研究中心 | Selective catalyst for removing oxynitrides from tail gases of diesel vehicles and preparation method thereof |
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102814192A (en) * | 2012-07-24 | 2012-12-12 | 中国科学院长春应用化学研究所 | Cerium/molecular sieve catalyst used for selective catalytic reduction of nitrogen oxides and preparation method thereof |
CN102814192B (en) * | 2012-07-24 | 2014-07-23 | 中国科学院长春应用化学研究所 | Cerium/molecular sieve catalyst used for selective catalytic reduction of nitrogen oxides and preparation method thereof |
CN104162421A (en) * | 2014-08-18 | 2014-11-26 | 南京理工大学 | Preparation method of high temperature resistant vanadium tungsten titanium oxide catalyst |
CN105688932A (en) * | 2016-03-16 | 2016-06-22 | 南京工业大学 | Catalyst for purifying diesel engine tail gas NOX, CO and HC for vehicle and preparation method thereof |
CN113713608A (en) * | 2021-08-26 | 2021-11-30 | 复旦大学 | For CO and NOxSimultaneous removal catalyst combination |
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