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 PDF

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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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catalyst
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CN102179243B (en
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韩炜
张克金
彭悦
张苡铭
曹雅彬
张贺
韩建
周亮
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Jilin University
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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

The catalyst of selective catalyst reduction of nitrogen oxides under the middle low temperature environment
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
Figure BDA0000054577960000021
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 acid hydrate ammonia 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
Figure BDA0000054577960000041
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)

* Cited by examiner, † Cited by third party
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)

* Cited by examiner, † Cited by third party
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

Patent Citations (3)

* Cited by examiner, † Cited by third party
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)

* Cited by examiner, † Cited by third party
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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