[go: up one dir, main page]

CN111408365A - A kind of preparation method of monolithic manganese-based catalyst for low-temperature denitration - Google Patents

A kind of preparation method of monolithic manganese-based catalyst for low-temperature denitration Download PDF

Info

Publication number
CN111408365A
CN111408365A CN202010431506.3A CN202010431506A CN111408365A CN 111408365 A CN111408365 A CN 111408365A CN 202010431506 A CN202010431506 A CN 202010431506A CN 111408365 A CN111408365 A CN 111408365A
Authority
CN
China
Prior art keywords
manganese
catalyst
low
monolithic
carrier
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN202010431506.3A
Other languages
Chinese (zh)
Inventor
上官文峰
李咸伟
陶善龙
石洪志
石琎
张志翔
刘道清
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.)
Baoshan Iron and Steel Co Ltd
Shanghai Jiao Tong University
Original Assignee
Baoshan Iron and Steel Co Ltd
Shanghai Jiao Tong University
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 Baoshan Iron and Steel Co Ltd, Shanghai Jiao Tong University filed Critical Baoshan Iron and Steel Co Ltd
Publication of CN111408365A publication Critical patent/CN111408365A/en
Pending legal-status Critical Current

Links

Images

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/50Catalysts, in general, characterised by their form or physical properties characterised by their shape or configuration
    • B01J35/56Foraminous structures having flow-through passages or channels, e.g. grids or three-dimensional monoliths
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/86Catalytic processes
    • B01D53/8621Removing nitrogen compounds
    • B01D53/8625Nitrogen oxides
    • B01D53/8628Processes characterised by a specific catalyst
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/002Mixed oxides other than spinels, e.g. perovskite
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/16Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
    • B01J23/32Manganese, technetium or rhenium
    • B01J23/34Manganese
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/70Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
    • B01J23/76Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/84Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36 with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
    • B01J23/889Manganese, technetium or rhenium
    • B01J23/8892Manganese
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2258/00Sources of waste gases
    • B01D2258/02Other waste gases
    • B01D2258/0283Flue gases
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2523/00Constitutive chemical elements of heterogeneous catalysts

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Materials Engineering (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Organic Chemistry (AREA)
  • Environmental & Geological Engineering (AREA)
  • Health & Medical Sciences (AREA)
  • Biomedical Technology (AREA)
  • Analytical Chemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Catalysts (AREA)
  • Exhaust Gas Treatment By Means Of Catalyst (AREA)

Abstract

The invention discloses a preparation method of an integral manganese-based catalyst for low-temperature denitration, and relates to the technical field of environmental catalysis. The method comprises the following steps: A. soaking the honeycomb ceramic catalyst carrier in an oxidizing solvent, washing to be neutral and drying; B. dissolving manganese salt, ferric salt or manganese salt and cerium salt in a solvent to obtain a mixed solution, adding an organic compound, and heating and stirring in a water bath; C. drying and roasting the catalyst precursor solution to obtain catalyst powder, mixing the catalyst powder with deionized water and a complexing binder, and coating the mixture on a pretreatment carrier; or directly adding the pretreatment carrier into the catalyst precursor solution, and drying and roasting the pretreatment carrier coated with the catalyst precursor solution to obtain the monolithic manganese-based catalyst for low-temperature denitration. The method is simple and efficient, nontoxic and harmless, the prepared product is uniform in dispersion, firm in combination and high in activity, the NOx removal efficiency can reach 70% -96%, the flue gas denitration effect is obvious, and the method has a wide application prospect.

Description

一种用于低温脱硝的整体型锰基催化剂的制备方法A kind of preparation method of monolithic manganese-based catalyst for low-temperature denitration

技术领域technical field

本发明涉及环境催化技术领域,尤其涉及一种用于低温脱硝的整体型锰基催化剂及其制备方法,具体涉及一种基于锰基复合氧化物并应用于烧结烟气低温脱硝的整体型催化剂及其制备方法。The invention relates to the technical field of environmental catalysis, in particular to a monolithic manganese-based catalyst for low-temperature denitration and a preparation method thereof, in particular to a monolithic catalyst based on manganese-based composite oxide and applied to low-temperature denitration of sintering flue gas and its preparation method.

背景技术Background technique

随着钢铁工业的发展,烧结烟气中氮氧化物的排放成为阻碍钢铁企业绿色发展的主要阻力之一。这些污染不但对大气环境造成破坏(臭氧层空洞,酸雨和光化学烟雾等),更严重危害人类的健康。使用适当的催化剂,在一定温度下,利用含氮还原剂例如氨(NH3)将烟气中的氮氧化物(NOx)选择性催化还原转化成氮气,即选择性催化还原(SCR)是目前烧结烟气脱硝的主要方法。With the development of the iron and steel industry, the emission of nitrogen oxides in sintering flue gas has become one of the main obstacles hindering the green development of iron and steel enterprises. These pollutions not only cause damage to the atmospheric environment (the hole in the ozone layer, acid rain and photochemical smog, etc.), but also seriously endanger human health. Selective catalytic reduction (SCR) of nitrogen oxides (NOx) in flue gas by selective catalytic reduction of nitrogen oxides (NOx) into nitrogen at a certain temperature with a nitrogen-containing reductant such as ammonia (NH 3 ) using an appropriate catalyst The main method of sintering flue gas denitrification.

当前工业界应用于SCR过程最成熟的催化剂体系是钒钨钛催化剂,但由于其活性温度较高,脱硝反应器需安装在脱硫装置、静电除尘器与空气预热器之前,因此极易造成飞灰堵塞催化剂床层以及催化剂SO2中毒。除此之外,钒氧化物的前驱体毒性较大,易造成环境污染。因此亟需开发新型的低温SCR催化剂,将催化剂活性温度降至120℃-160℃,从而实现脱硝装置后移.At present, the most mature catalyst system used in the SCR process in the industry is vanadium-tungsten-titanium catalyst. However, due to its high activity temperature, the denitration reactor needs to be installed before the desulfurization device, electrostatic precipitator and air preheater, so it is easy to cause flying Ash clogging the catalyst bed and catalyst SO2 poisoning. In addition, the precursors of vanadium oxides are highly toxic and easily cause environmental pollution. Therefore, it is urgent to develop new low-temperature SCR catalysts to reduce the catalyst activity temperature to 120 °C-160 °C, so as to realize the backward shift of the denitrification device.

锰基催化剂是当前应用于SCR过程的新型高效催化剂,例如,Mn3O4可以实现对于NO的高效吸附并将其转化为吸附态的NO,而其表面的氧空位可以有效捕捉氧分子并使其成为活化,继而完成NO到NO2的反应过程。由此更易实现NO:NO2=1:1的“快速SCR反应”。Manganese-based catalysts are new high-efficiency catalysts currently used in SCR processes . For example, Mn3O4 can achieve efficient adsorption of NO and convert it into adsorbed NO, while the oxygen vacancies on its surface can effectively capture oxygen molecules and enable It becomes activated, which in turn completes the NO to NO2 reaction process. This makes it easier to achieve a "fast SCR reaction" of NO:NO 2 =1:1.

公告号为107126955A的中国发明专利“一种炭基低温烧结烟气脱硝催化剂及其制备方法”公开了一种以改性生物质焦为载体,MnO2为活性组分,CeO2为助催化剂组分的粉末状催化剂,在固定床脱硝测试中表现出优异的性能,100℃-200℃区间内脱硝率均可达到90%以上。此外,公开号为108671965A的中国发明专利“一种半焦低温SCR脱硝催化剂及其制备方法”提出了以半焦制备活性炭载体,再利用三聚氰胺作为还原剂,通过浸渍焙烧负载锰氧化物活性组分,得到的催化剂在175℃-300℃范围内脱硝效率可以达到90%以上。但考虑到实际应用中需将催化剂成分涂覆至大规格成型载体上,且实际工况的空速较低,如何制备高效的整体型催化剂有待进一步探索。Chinese invention patent No. 107126955A "A carbon-based low-temperature sintering flue gas denitration catalyst and its preparation method" discloses a kind of modified biomass coke as a carrier, MnO 2 as an active component, and CeO 2 as a co-catalyst group. The different powder catalysts show excellent performance in the fixed bed denitration test, and the denitration rate can reach more than 90% in the range of 100℃-200℃. In addition, the Chinese invention patent with publication number 108671965A "A semi-coke low-temperature SCR denitration catalyst and its preparation method" proposes to prepare an activated carbon carrier with semi-coke, and then use melamine as a reducing agent to support manganese oxide active components by impregnation and roasting. , the denitration efficiency of the obtained catalyst can reach more than 90% in the range of 175℃-300℃. However, considering that the catalyst components need to be coated on a large-sized shaped carrier in practical applications, and the space velocity of the actual working condition is low, how to prepare an efficient monolithic catalyst needs to be further explored.

公告号为105854874A的中国发明专利“脱硝催化剂及其制备方法和在烟气脱硝中的应用”公开了一种低温自蔓延燃烧涂覆法制备得到低温脱硝催化剂,主要利用甘氨酸、尿素等物质对胶状溶液引燃,使Mn、Ce及Al等活性组分均匀负载在载体上.得到的整体型催化剂在250℃下NO转换率可以到达80%左右,但是仍然达不到当下的要求。The Chinese invention patent "Denitration catalyst and its preparation method and application in flue gas denitration" with the announcement number of 105854874A discloses a low-temperature self-propagating combustion coating method to prepare a low-temperature denitration catalyst, mainly using glycine, urea and other substances to The state solution is ignited, so that the active components such as Mn, Ce and Al are evenly supported on the carrier. The obtained monolithic catalyst can achieve a NO conversion rate of about 80% at 250 °C, but it still cannot meet the current requirements.

公告号为101879452A的中国发明专利“一种锰基低温脱硝催化剂及其制备方法”公开了一种含有锰、铁、铈、锡四种元素的低温脱硝催化剂,得到的200mg粉末样品在30000h-1空速下、110℃-200℃区间内的NO转换率可以达到95%以上。该专利主要通过逐滴添加铵盐溶液至前驱体溶液中使锰及其它元素沉淀,继而焙烧得到锰及其它元素的氧化复合物。但是多种活性成分的组合提高了制造成本,在达到减排标准的前提下降低原料成本、优化制备工艺以进一步满足实际生产就显得尤为重要。Chinese invention patent No. 101879452A "A manganese-based low-temperature denitration catalyst and its preparation method" discloses a low-temperature denitration catalyst containing four elements of manganese, iron, cerium and tin, and the obtained 200mg powder sample is at 30000h -1 Under the space velocity, the NO conversion rate in the range of 110℃-200℃ can reach more than 95%. In this patent, manganese and other elements are precipitated by dropwise addition of ammonium salt solution to the precursor solution, followed by calcination to obtain oxide complexes of manganese and other elements. However, the combination of various active ingredients increases the manufacturing cost, and it is particularly important to reduce the cost of raw materials and optimize the preparation process to further meet the actual production requirements under the premise of meeting emission reduction standards.

发明内容SUMMARY OF THE INVENTION

有鉴于此,本发明目的在于克服上述现有技术存在的不足,提出一种用于低温脱硝的整体型锰基催化剂的制备方法。本发明所制备的整体型催化剂可应用于通过氨选择性催化还原除氮氧化物,从而实现烧结烟气脱硝处理。In view of this, the purpose of the present invention is to overcome the above-mentioned deficiencies of the prior art, and to propose a preparation method of a monolithic manganese-based catalyst for low-temperature denitration. The monolithic catalyst prepared by the invention can be applied to the removal of nitrogen oxides through selective catalytic reduction of ammonia, so as to realize the denitration treatment of sintered flue gas.

本发明的目的是通过以下技术方案实现的:一种用于低温脱硝的整体型锰基催化剂的制备方法,包括如下步骤:The object of the present invention is achieved through the following technical solutions: a preparation method of a monolithic manganese-based catalyst for low-temperature denitration, comprising the following steps:

A、预处理载体:将蜂窝陶瓷催化剂载体浸渍在氧化性溶剂中,洗涤至显中性,干燥备用;A. Pretreatment carrier: The honeycomb ceramic catalyst carrier is immersed in an oxidizing solvent, washed to become neutral, and dried for later use;

B、制备催化剂前驱体溶液:将锰盐、铁盐或锰盐、铈盐溶于溶剂中得到混合溶液,加入有机化合物,水浴加热搅拌;B. Preparation of catalyst precursor solution: dissolving manganese salt, iron salt or manganese salt and cerium salt in a solvent to obtain a mixed solution, adding an organic compound, heating and stirring in a water bath;

C、制备整体型催化剂:将催化剂前驱体溶液干燥并焙烧得到催化剂粉末,将催化剂粉末与去离子水、络合粘结剂混合涂覆至预处理载体上;或直接添加预处理载体至催化剂前驱体溶液中,将涂覆有催化剂前驱体溶液的预处理载体干燥、焙烧,即得所述用于低温脱硝的整体型锰基催化剂,所述用于低温脱硝的整体型锰基催化剂负载的锰基活性组分的质量百分比含量为6%~14%。C. Preparation of monolithic catalyst: drying and calcining the catalyst precursor solution to obtain catalyst powder, mixing the catalyst powder with deionized water and complex binder and coating it on the pretreatment carrier; or directly adding the pretreatment carrier to the catalyst precursor In the bulk solution, the pretreatment carrier coated with the catalyst precursor solution is dried and calcined to obtain the monolithic manganese-based catalyst for low-temperature denitration, and the manganese supported by the monolithic manganese-based catalyst for low-temperature denitration The mass percentage content of the base active component is 6% to 14%.

当所述用于低温脱硝的整体型锰基催化剂负载的锰基活性组分的质量百分比含量低于6%时,由于活性组分偏少,无法达到优异的低温脱硝性能;当所述用于低温脱硝的整体型锰基催化剂负载的锰基活性组分的质量百分比含量高于14%时,由于金属元素含量过高,导致团聚形成大量的氧化物颗粒,增加了气相扩散阻力,降低了催化剂的活性。与此同时,活性组分含量过高同时也会提高单位体积整体型催化剂的生产成本。When the mass percentage of manganese-based active components supported by the monolithic manganese-based catalyst for low-temperature denitration is less than 6%, excellent low-temperature denitration performance cannot be achieved due to the lack of active components; When the mass percentage content of the manganese-based active component supported by the monolithic manganese-based catalyst for low-temperature denitration is higher than 14%, due to the excessively high metal element content, agglomeration forms a large number of oxide particles, which increases the gas phase diffusion resistance and reduces the catalyst. activity. At the same time, an excessively high content of active components will also increase the production cost of the monolithic catalyst per unit volume.

优选的,步骤A中所述蜂窝陶瓷催化剂载体包括氧化铝陶瓷、堇青石陶瓷中的一种或多种。Preferably, the honeycomb ceramic catalyst carrier in step A includes one or more of alumina ceramics and cordierite ceramics.

优选的,步骤A中所述氧化性溶剂包括质量百分浓度为20%-40%的磷酸溶液或质量百分浓度为15%-30%的过氧化氢溶液。Preferably, the oxidizing solvent in step A includes a phosphoric acid solution with a concentration of 20%-40% by mass or a hydrogen peroxide solution with a concentration of 15%-30% by mass.

优选的,步骤A中所述蜂窝陶瓷催化剂载体浸渍在氧化性溶剂的浸渍时间为4-8h,干燥温度在80-120℃。Preferably, in step A, the impregnation time of the honeycomb ceramic catalyst carrier in the oxidizing solvent is 4-8h, and the drying temperature is 80-120°C.

优选的,步骤B中所述锰盐包括硝酸锰、醋酸锰中的一种或多种;所述铁盐包括硝酸铁、草酸氨铁、醋酸铁,柠檬酸铁中的一种或多种;所述铈盐包括硝酸铈、草酸铈胺中的一种或多种;所述溶剂包括去离子水、甲醇、乙醇中的一种或多种。Preferably, the manganese salt in step B includes one or more of manganese nitrate and manganese acetate; the iron salt includes one or more of ferric nitrate, ferric ammonia oxalate, ferric acetate, and ferric citrate; The cerium salt includes one or more of cerium nitrate and ceric amine oxalate; the solvent includes one or more of deionized water, methanol, and ethanol.

更加优选的,步骤B中所述锰盐优选为硝酸锰。More preferably, the manganese salt in step B is preferably manganese nitrate.

优选的,步骤B中所述有机化合物包括尿素、柠檬酸、甘氨酸中的一种或多种。Preferably, the organic compound in step B includes one or more of urea, citric acid, and glycine.

优选的,步骤B所述混合溶液中锰元素与铁元素的摩尔比为(0.5-1.5):1;锰元素与铈元素的摩尔比为(1-5):(5-9),所述有机化合物与锰元素摩尔比为(0.5-5):1;更加优选的所述尿素与锰元素摩尔比为(3-5):1。Preferably, the molar ratio of manganese element and iron element in the mixed solution described in step B is (0.5-1.5): 1; the molar ratio of manganese element and cerium element is (1-5): (5-9), the said The molar ratio of the organic compound to the manganese element is (0.5-5):1; more preferably, the molar ratio of the urea to the manganese element is (3-5):1.

锰铁元素比例以及锰铈元素比例中,锰元素过少,铁或者铈过多时,会造成活性下降。有机物过少,会造成硝酸盐氧化不充分,催化剂产率以及活性下降;有机物过多,会造成硝酸盐过度氧化,甚至烧结,造成催化剂活性下降。In the ratio of ferromanganese and manganese to cerium, too little manganese and too much iron or cerium will cause the activity to decrease. Too little organic matter will cause insufficient oxidation of nitrate, resulting in decreased catalyst yield and activity; too much organic matter will cause excessive oxidation of nitrate, or even sintering, resulting in decreased catalyst activity.

优选的,步骤B中所述水浴的加热温度为70℃-90℃,加热时间为1h-4h。Preferably, the heating temperature of the water bath in step B is 70°C-90°C, and the heating time is 1h-4h.

更加优选的,步骤B中加入有机化合物之前还添加有TiO(NO3)前驱液,所述TiO(NO3)前驱液为锰元素摩尔量的2倍;所述TiO(NO3)前驱液的制备方法为:将相当于锰元素摩尔量2倍的钛酸四丁酯作为二氧化钛的前驱体,向盛有适量钛酸四丁酯的烧杯中先缓慢滴加无水乙醇进行醇解,在室温下用磁力搅拌,再将醇解溶液以同样方式滴加去离子水使其水解生成TiO(OH)2沉淀,而后滴入适量硝酸溶解沉淀,得到澄清透明的TiO(NO3)前驱液。More preferably, before adding the organic compound in step B, a TiO(NO 3 ) precursor solution is added, and the TiO(NO 3 ) precursor solution is twice the molar amount of manganese ; The preparation method is as follows: using tetrabutyl titanate equivalent to twice the molar amount of manganese element as the precursor of titanium dioxide, slowly adding anhydrous ethanol dropwise to a beaker containing an appropriate amount of tetrabutyl titanate for alcoholysis, and at room temperature Magnetic stirring was performed under the same method, and deionized water was added dropwise to the alcoholysis solution in the same way to hydrolyze to form TiO(OH) 2 precipitation, and then an appropriate amount of nitric acid was added to dissolve the precipitation to obtain a clear and transparent TiO(NO 3 ) precursor solution.

优选的,所述步骤C具体包括如下步骤:Preferably, the step C specifically includes the following steps:

将催化剂前驱体溶液在80℃-120℃下干燥6h-12h并在450℃-650℃下焙烧4h-6h,得到催化剂粉末后再混合离子水以及络合粘结剂,利用压缩机喷枪喷涂预处理后的载体1min-5min,80℃-120℃下干燥1h-3h,重复若干次,即得所述用于低温脱硝的整体型锰基催化剂,其中预处理载体质量与去离子水、络合粘结剂的质量比为1:(0.75-1.25):(0.05-0.2);The catalyst precursor solution was dried at 80°C-120°C for 6h-12h and calcined at 450°C-650°C for 4h-6h to obtain catalyst powder, then mixed with ionized water and complex binder, and sprayed with a compressor spray gun for pre-treatment. The treated carrier is dried for 1min-5min at 80℃-120℃ for 1h-3h, and repeated several times to obtain the monolithic manganese-based catalyst for low-temperature denitration, wherein the quality of the pretreated carrier is combined with deionized water, complexed The mass ratio of the binder is 1:(0.75-1.25):(0.05-0.2);

或将预处理载体添加至催化剂前驱体溶液中,超声浸渍10min-60min,再将涂覆有催化剂前驱体溶液的预处理载体首先在150℃-350℃下干燥1h,然后在450℃-650℃下焙烧5h-6h,即得所述用于低温脱硝的整体型锰基催化剂;更加优选的超声浸渍的时间为35-60min。Or add the pretreated carrier to the catalyst precursor solution, ultrasonically immerse it for 10min-60min, and then dry the pretreated carrier coated with the catalyst precursor solution at 150℃-350℃ for 1h, then at 450℃-650℃ After calcining for 5h-6h, the monolithic manganese-based catalyst for low-temperature denitration can be obtained; the more preferred ultrasonic impregnation time is 35-60min.

当焙烧温度过高会造成过度氧化,产生过多催化剂晶格畸变等,活性降低;如果焙烧温度过低,前驱体硝酸盐氧化不充分,活性同样降低。When the calcination temperature is too high, it will cause excessive oxidation, resulting in excessive catalyst lattice distortion, etc., and the activity will decrease; if the calcination temperature is too low, the oxidation of the precursor nitrate will be insufficient, and the activity will also decrease.

优选的,所述络合粘结剂包括硅溶胶、铝溶胶、甲基纤维素中的一种或多种。Preferably, the complex binder includes one or more of silica sol, aluminum sol, and methyl cellulose.

综上所述,与现有技术相比,本发明具有如下的有益效果:To sum up, compared with the prior art, the present invention has the following beneficial effects:

(1)本发明主要利用锰基氧化物复合铁元素或者铈元素制备催化剂,原料成分简单,无毒无害,制备流程快捷,有利于进一步实现大规模生产试验;(1) The present invention mainly utilizes manganese-based oxide composite iron element or cerium element to prepare catalyst, the raw material composition is simple, non-toxic and harmless, and the preparation process is fast, which is conducive to further realizing large-scale production test;

(2)本发明所述催化剂负载方法中载体涂覆活性组分含量范围主要在6%-14%之间。针对相同前驱体,优化工艺制备得到的负载低含量活性组分整体型催化剂具有较高的比活性。由此可以提高前驱体溶液重复利用率,降低生产成本;(2) In the catalyst loading method of the present invention, the content of the active components of the carrier coating is mainly in the range of 6%-14%. For the same precursor, the monolithic catalyst with low content of active components prepared by the optimized process has higher specific activity. Thereby, the reuse rate of the precursor solution can be improved, and the production cost can be reduced;

(3)本发明在粉末催化剂以及蜂窝陶瓷载体的基础上实现了高效涂覆制备,优化活性组分在蜂窝陶瓷载体上的分散性,从而改善气固两相反应时反应物扩散条件并降低脱硝反应活性温度,使得催化剂在8000h-1以下的低空速条件下,针对110℃-160℃温度区间内的NO转换率可以达到90%以上,性能优于一般成型及粉末体系锰基催化剂。(3) The present invention realizes efficient coating preparation on the basis of powder catalyst and honeycomb ceramic carrier, optimizes the dispersibility of active components on the honeycomb ceramic carrier, thereby improving the diffusion conditions of reactants during gas-solid two-phase reaction and reducing denitrification The reaction activity temperature enables the catalyst to achieve a NO conversion rate of more than 90% in the temperature range of 110℃-160℃ under the condition of low space velocity below 8000h -1 , and its performance is better than that of general molding and powder system manganese-based catalysts.

附图说明Description of drawings

通过阅读参照以下附图对非限制性实施例所作的详细描述,本发明的其它特征、目的和优点将会变得更明显:Other features, objects and advantages of the present invention will become more apparent by reading the detailed description of non-limiting embodiments with reference to the following drawings:

图1为实施例1-7中用于低温脱硝的整体型锰基催化剂的催化剂在NH3-SCR脱硝过程中NO转化率折线图。FIG. 1 is a broken line graph of NO conversion rate of the catalysts of the monolithic manganese-based catalysts used for low-temperature denitration in the NH 3 -SCR denitration process in Examples 1-7.

具体实施方式Detailed ways

以下实施例将有助于本领域的技术人员进一步理解本发明,但不以任何形式限制本发明。对本领域的普通技术人员来说,在不脱离本发明构思的前提下,还可以做出若干变化和改进,这些都属于本发明的保护范围。在本文中所披露的范围的端点和任何值都不限于该精确的范围或值,这些范围或值应当理解为包含接近这些范围或值的值。对于数值范围来说,各个范围的端点值之间、各个范围的端点值和单独的点值之间,以及单独的点值之间可以彼此组合而得到一个或多个新的数值范围,这些数值范围应被视为在本文中具体公开,下面结合具体实施例对本发明进行详细说明:The following examples will help those skilled in the art to further understand the present invention, but do not limit the present invention in any form. For those skilled in the art, on the premise of not departing from the concept of the present invention, several changes and improvements can also be made, which all belong to the protection scope of the present invention. The endpoints of ranges and any values disclosed herein are not limited to the precise ranges or values, which are to be understood to encompass values proximate to those ranges or values. For ranges of values, the endpoints of each range, the endpoints of each range and the individual point values, and the individual point values can be combined with each other to yield one or more new ranges of values that The scope should be considered to be specifically disclosed herein, and the present invention will be described in detail below in conjunction with specific embodiments:

实施例1Example 1

一种用于低温脱硝的整体型锰基催化剂的制备方法,包括以下步骤:A preparation method of a monolithic manganese-based catalyst for low-temperature denitration, comprising the following steps:

A、将底面直径为11mm,高为24mm的圆柱型氧化铝蜂窝陶瓷催化剂载体浸渍在装有质量浓度30%过氧化氢溶液的容器中,在室温下静置6h,再反复水洗干燥直至显中性,放入烘箱中80℃下干燥12h得到预处理后的氧化铝蜂窝陶瓷催化剂载体;A. Immerse the cylindrical alumina honeycomb ceramic catalyst carrier with a bottom diameter of 11mm and a height of 24mm in a container with a mass concentration of 30% hydrogen peroxide solution, let stand for 6h at room temperature, and then repeatedly wash and dry until it becomes clear properties, put it in an oven to dry at 80°C for 12h to obtain the pretreated alumina honeycomb ceramic catalyst carrier;

B、用硝酸锰作为锰源,使用去离子水和甲醇两者混合物作为溶剂。将一定量四水硝酸锰及九水硝酸铁(锰铁元素摩尔比=1:1)分别溶解于适量溶剂中,搅拌至完全溶解后混合均匀,在上述溶液中加入锰元素5倍摩尔比的尿素,搅拌分散,将样品溶液在80℃水浴中充分搅拌2h。B. Use manganese nitrate as manganese source, and use a mixture of deionized water and methanol as solvent. A certain amount of manganese nitrate tetrahydrate and ferric nitrate nonahydrate (molar ratio of ferromanganese element = 1:1) are respectively dissolved in an appropriate amount of solvent, stirred until completely dissolved and mixed evenly, and 5 times the molar ratio of manganese element is added to the above solution. Urea, stir and disperse, and fully stir the sample solution in a water bath at 80°C for 2h.

C、置于烘箱中110℃干燥12h,最后将粉末固体样放入体积为100mL的刚玉坩埚中,然后将装样的坩埚置于马弗炉中,以5℃/min的速度升温至550℃,保温4h。冷却后取出置于玛瑙研钵中研磨,获得目标物;C. Put it in an oven to dry at 110°C for 12h, and finally put the powder solid sample into a corundum crucible with a volume of 100mL, then place the sample crucible in a muffle furnace, and heat it up to 550°C at a rate of 5°C/min , keep warm for 4h. After cooling, take it out and grind it in an agate mortar to obtain the target;

将研磨得到的催化剂粉末以及一定量的硅溶胶溶解在适量的去离子水中,其中预处理载体质量与去离子水、络合粘结剂的质量比为1:1:0.125,得到催化剂浆液。利用压缩机喷枪喷涂预处理后的载体3min,100℃下干燥2h,重复若干次,即得所述用于低温脱硝的整体型锰基催化剂;Dissolve the ground catalyst powder and a certain amount of silica sol in an appropriate amount of deionized water, wherein the mass ratio of the pretreated carrier to deionized water and complex binder is 1:1:0.125 to obtain a catalyst slurry. The pretreated carrier was sprayed with a compressor spray gun for 3 minutes, dried at 100°C for 2 hours, and repeated several times to obtain the monolithic manganese-based catalyst for low-temperature denitration;

制备得到的锰铁低温脱硝整体催化剂中活性组分占比约为10%,在反应温度110℃-160℃内、NO流量为6mL/min,NO流量为6mL/min、O2流量为15mL/min、N2流量为129mL/min、空速为4000h-1的条件下,所得催化剂在NH3-SCR脱硝过程中NO转化率如图1。The proportion of active components in the prepared ferromanganese low-temperature denitration monolithic catalyst is about 10%. Within the reaction temperature of 110℃-160℃, the NO flow rate is 6mL/min, the NO flow rate is 6mL/min, and the O 2 flow rate is 15mL/min. min, N 2 flow rate of 129 mL/min, and space velocity of 4000 h -1 , the NO conversion rate of the obtained catalyst in the NH 3 -SCR denitration process is shown in Figure 1.

实施例2Example 2

一种用于低温脱硝的整体型锰基催化剂的制备方法,包括以下步骤:A preparation method of a monolithic manganese-based catalyst for low-temperature denitration, comprising the following steps:

A、将底面直径为11mm,高为24mm的圆柱型氧化铝蜂窝陶瓷催化剂载体浸渍在装有质量浓度30%过氧化氢溶液的容器中,在室温下静置6h,再反复水洗干燥直至显中性,放入烘箱中80℃下干燥12h得到预处理后的氧化铝蜂窝陶瓷催化剂载体;A. Immerse the cylindrical alumina honeycomb ceramic catalyst carrier with a bottom diameter of 11mm and a height of 24mm in a container with a mass concentration of 30% hydrogen peroxide solution, let stand for 6h at room temperature, and then repeatedly wash and dry until it becomes clear properties, put it in an oven to dry at 80°C for 12h to obtain the pretreated alumina honeycomb ceramic catalyst carrier;

B、用硝酸锰作为锰源,使用无水甲醇或者乙醇作为溶剂。将一定量四水硝酸锰及九水硝酸铁(锰铁元素摩尔比=1:1)分别溶解于适量溶剂中,搅拌至完全溶解后混合均匀。将相当于锰元素摩尔量2倍的钛酸四丁酯作为二氧化钛的前驱体,向盛有适量钛酸四丁酯的烧杯中先缓慢滴加无水乙醇进行醇解,在室温下用磁力搅拌,再将醇解溶液以同样方式滴加去离子水使其水解生成TiO(OH)2沉淀,而后滴入适量硝酸溶解沉淀,得到澄清透明的TiO(NO3)前驱液;将上述溶液混合均匀,加入相当于锰元素摩尔量5倍的尿素,搅拌分散,并样品溶液在80℃水浴中充分搅拌2h。B. Use manganese nitrate as manganese source, and use anhydrous methanol or ethanol as solvent. A certain amount of manganese nitrate tetrahydrate and ferric nitrate nonahydrate (molar ratio of manganese-iron element = 1:1) are respectively dissolved in an appropriate amount of solvent, stirred until completely dissolved, and then mixed evenly. Use tetrabutyl titanate equivalent to twice the molar amount of manganese as the precursor of titanium dioxide, slowly add anhydrous ethanol dropwise to a beaker containing an appropriate amount of tetrabutyl titanate for alcoholysis, and use magnetic stirring at room temperature. , and then add deionized water dropwise to the alcoholysis solution in the same way to make it hydrolyze to form TiO(OH) 2 precipitation, and then drop an appropriate amount of nitric acid to dissolve the precipitation to obtain a clear and transparent TiO(NO 3 ) precursor solution; Mix the above solutions evenly , add urea equivalent to 5 times the molar amount of manganese, stir and disperse, and fully stir the sample solution in a water bath at 80°C for 2h.

C、置于烘箱中110℃干燥12h,最后将粉末固体样放入体积为100mL的刚玉坩埚中,然后将装样的坩埚置于马弗炉中,以5℃/min的速度升温至450℃,保温4h。冷却后取出置于玛瑙研钵中研磨,获得目标物;C. Put it in an oven to dry at 110°C for 12h, and finally put the powder solid sample into a corundum crucible with a volume of 100mL, then place the sample crucible in a muffle furnace, and heat it up to 450°C at a rate of 5°C/min , keep warm for 4h. After cooling, take it out and grind it in an agate mortar to obtain the target;

将研磨得到的催化剂粉末以及一定量的硅溶胶溶解在适量的去离子水中,其中预处理载体质量与去离子水、络合粘结剂的质量比为1:1.25:0.2,得到催化剂浆液。利用压缩机喷枪喷涂预处理后的载体5min,110℃下干燥3h,重复若干次,即得所述用于低温脱硝的整体型锰基催化剂;Dissolve the ground catalyst powder and a certain amount of silica sol in an appropriate amount of deionized water, wherein the mass ratio of the pretreatment carrier to deionized water and complex binder is 1:1.25:0.2 to obtain a catalyst slurry. The pretreated carrier was sprayed with a compressor spray gun for 5 minutes, dried at 110° C. for 3 hours, and repeated several times to obtain the monolithic manganese-based catalyst for low-temperature denitration;

制备得到的锰铁/二氧化钛低温脱硝整体催化剂中活性组分占比约为10%,在反应温度110℃-160℃内、NO流量为6mL/min,NO流量为6mL/min、O2流量为15mL/min、N2流量为129mL/min、空速为4000h-1的条件下,所得催化剂在NH3-SCR脱硝过程中NO转化率见图1。The proportion of active components in the prepared ferromanganese/titania low-temperature denitration monolith catalyst is about 10%. Within the reaction temperature of 110℃-160℃, the NO flow rate is 6mL/min, the NO flow rate is 6mL/min, and the O 2 flow rate is Under the conditions of 15 mL/min, N 2 flow rate of 129 mL/min, and space velocity of 4000 h -1 , the NO conversion rate of the obtained catalyst in the NH 3 -SCR denitration process is shown in Figure 1.

实施例3Example 3

一种用于低温脱硝的整体型锰基催化剂的制备方法,包括以下步骤:A preparation method of a monolithic manganese-based catalyst for low-temperature denitration, comprising the following steps:

A、将11mm*11mm*48mm的立方体型氧化铝蜂窝陶瓷催化剂载体浸渍在装有质量浓度30%过氧化氢溶液的容器中,在室温下静置6h,再反复水洗干燥直至显中性,放入烘箱中80℃下干燥12h得到预处理后的氧化铝蜂窝陶瓷催化剂载体;A. Immerse the 11mm*11mm*48mm cube-shaped alumina honeycomb ceramic catalyst carrier in a container with a mass concentration of 30% hydrogen peroxide solution, let it stand for 6 hours at room temperature, and then repeatedly wash and dry until it is neutral. The pretreated alumina honeycomb ceramic catalyst carrier was obtained by drying at 80°C for 12h in an oven;

B、将一定量四水硝酸锰以及九水硝酸铁(锰铁元素摩尔比=1:1)分别溶解于适量的去离子水中,搅拌至完全溶解后混合均匀,然后加入相当于锰元素摩尔量2倍的尿素,并在80℃水浴中充分搅拌2h。B. Dissolve a certain amount of manganese nitrate tetrahydrate and ferric nitrate nonahydrate (molar ratio of ferromanganese element = 1:1) in an appropriate amount of deionized water, stir until completely dissolved, and mix evenly, and then add a molar amount equivalent to manganese element. 2 times of urea, and fully stirred in a water bath at 80 °C for 2 h.

C、将预处理后的陶瓷载体浸渍在得到的混合溶液中,超声浸渍35min,再将涂覆有催化剂前驱体溶液的预处理载体首先在350℃下干燥1h,然后在450℃下焙烧5h,即得所述用于低温脱硝的整体型锰基催化剂;C. Immerse the pretreated ceramic carrier in the obtained mixed solution, ultrasonically impregnate it for 35 minutes, and then dry the pretreated carrier coated with the catalyst precursor solution at 350 °C for 1 hour, and then bake it at 450 °C for 5 hours. to obtain the monolithic manganese-based catalyst for low-temperature denitration;

制备得到的锰铁低温脱硝整体催化剂中活性组分占比约为6%,在反应温度110℃-160℃内、NO流量为6mL/min,NO流量为6mL/min、O2流量为15mL/min、N2流量为129mL/min、空速为1625h-1的条件下,所得催化剂在NH3-SCR脱硝过程中NO转化率见图1。The proportion of active components in the prepared ferromanganese low-temperature denitration monolithic catalyst is about 6%. Within the reaction temperature of 110℃-160℃, the NO flow rate is 6mL/min, the NO flow rate is 6mL/min, and the O 2 flow rate is 15mL/min. Under the conditions of min, N 2 flow rate of 129 mL/min, and space velocity of 1625 h -1 , the NO conversion rate of the obtained catalyst in the NH 3 -SCR denitration process is shown in Figure 1.

实施例4Example 4

一种用于低温脱硝的整体型锰基催化剂的制备方法,包括以下步骤:A preparation method of a monolithic manganese-based catalyst for low-temperature denitration, comprising the following steps:

A、将6mm*6mm*28mm的立方体型氧化铝蜂窝陶瓷催化剂载体浸渍在装有质量浓度30%过氧化氢溶液的容器中,在室温下静置6h,再反复水洗干燥直至显中性,放入烘箱中80℃下干燥12h得到预处理后的氧化铝蜂窝陶瓷催化剂载体;A. Immerse the 6mm*6mm*28mm cube-shaped alumina honeycomb ceramic catalyst carrier in a container with a mass concentration of 30% hydrogen peroxide solution, let it stand for 6 hours at room temperature, and then repeatedly wash and dry until it is neutral. The pretreated alumina honeycomb ceramic catalyst carrier was obtained by drying at 80°C for 12h in an oven;

B、将一定量四水硝酸锰以及九水硝酸铁(锰铁元素摩尔比=1:1)分别溶解于适量的去离子水中,搅拌至完全溶解后混合均匀,然后加入相当于锰元素摩尔量4倍的尿素,并在80℃水浴中充分搅拌2h。B. Dissolve a certain amount of manganese nitrate tetrahydrate and ferric nitrate nonahydrate (molar ratio of ferromanganese element = 1:1) in an appropriate amount of deionized water, stir until completely dissolved, and mix evenly, and then add a molar amount equivalent to manganese element. 4 times of urea, and fully stirred in a water bath at 80 °C for 2 h.

C、将预处理后的陶瓷载体浸渍在得到的混合溶液中,超声浸渍35min,再将涂覆有催化剂前驱体溶液的预处理载体首先在250℃下干燥1h,然后在550℃下焙烧5.5h,即得所述用于低温脱硝的整体型锰基催化剂;C. Immerse the pretreated ceramic carrier in the obtained mixed solution, ultrasonically impregnate it for 35 minutes, and then dry the pretreated carrier coated with the catalyst precursor solution at 250 °C for 1 h, and then bake it at 550 °C for 5.5 h , that is, the monolithic manganese-based catalyst for low-temperature denitration is obtained;

制备得到的锰铁低温脱硝整体催化剂中活性组分占比约为6%,在反应温度110℃-160℃内、NO流量为6mL/min,NO流量为6mL/min、O2流量为15mL/min、N2流量为129mL/min、空速为8000h-1的条件下,所得催化剂在NH3-SCR脱硝过程中NO转化率见图1。The proportion of active components in the prepared ferromanganese low-temperature denitration monolithic catalyst is about 6%. Within the reaction temperature of 110℃-160℃, the NO flow rate is 6mL/min, the NO flow rate is 6mL/min, and the O 2 flow rate is 15mL/min. Under the conditions of min, N 2 flow rate of 129 mL/min, and space velocity of 8000 h -1 , the NO conversion rate of the obtained catalyst in the NH 3 -SCR denitration process is shown in Figure 1.

实施例5Example 5

一种用于低温脱硝的整体型锰基催化剂的制备方法,包括以下步骤:A preparation method of a monolithic manganese-based catalyst for low-temperature denitration, comprising the following steps:

A、将6mm*6mm*28mm的立方体型氧化铝蜂窝陶瓷催化剂载体浸渍在装有质量浓度30%过氧化氢溶液的容器中,在室温下静置6h,再反复水洗干燥直至显中性,放入烘箱中80℃下干燥12h得到预处理后的氧化铝蜂窝陶瓷催化剂载体。A. Immerse the 6mm*6mm*28mm cube-shaped alumina honeycomb ceramic catalyst carrier in a container with a mass concentration of 30% hydrogen peroxide solution, let it stand for 6 hours at room temperature, and then repeatedly wash and dry until it is neutral. The pretreated alumina honeycomb ceramic catalyst carrier was obtained by drying in an oven at 80 °C for 12 h.

B、将一定量四水醋酸锰及硝酸铈(锰铈元素摩尔比=1:1)分别溶解于适量的去离子水中,搅拌至完全溶解后混合均匀,然后加入相当于锰元素摩尔量0.7倍的柠檬酸并在80℃水浴中充分搅拌2h。B. Dissolve a certain amount of manganese acetate tetrahydrate and cerium nitrate (molar ratio of manganese-cerium element = 1:1) in an appropriate amount of deionized water respectively, stir until completely dissolved and mix evenly, then add 0.7 times the molar amount of manganese element citric acid and fully stirred in a water bath at 80 °C for 2 h.

C、将预处理后的陶瓷载体浸渍在得到的混合溶液中,超声浸渍10min,再将涂覆有催化剂前驱体溶液的预处理载体首先在150℃下干燥1h,然后在650℃下焙烧5h,即得所述用于低温脱硝的整体型锰基催化剂;C. Immerse the pretreated ceramic carrier in the obtained mixed solution, ultrasonically impregnate it for 10 minutes, and then dry the pretreated carrier coated with the catalyst precursor solution at 150 °C for 1 hour, and then bake it at 650 °C for 5 hours. to obtain the monolithic manganese-based catalyst for low-temperature denitration;

制备得到的锰铈低温脱硝整体催化剂中活性组分占比约为8%,在反应温度110℃-160℃内、NO流量为6mL/min,NO流量为6mL/min、O2流量为15mL/min、N2流量为129mL/min、空速为8000h-1的条件下,所得催化剂在NH3-SCR脱硝过程中NO转化率见图1。The proportion of active components in the prepared manganese-cerium low-temperature denitration monolith catalyst is about 8%. At the reaction temperature of 110℃-160℃, the NO flow rate is 6mL/min, the NO flow rate is 6mL/min, and the O 2 flow rate is 15mL/min. Under the conditions of min, N 2 flow rate of 129 mL/min, and space velocity of 8000 h -1 , the NO conversion rate of the obtained catalyst in the NH 3 -SCR denitration process is shown in Figure 1.

实施例6Example 6

一种用于低温脱硝的整体型锰基催化剂的制备方法,包括以下步骤:A preparation method of a monolithic manganese-based catalyst for low-temperature denitration, comprising the following steps:

A、将6mm*6mm*28mm的立方体型氧化铝蜂窝陶瓷催化剂载体浸渍在装有质量浓度30%过氧化氢溶液的容器中,在室温下静置6h,再反复水洗干燥直至显中性,放入烘箱中80℃下干燥12h得到预处理后的氧化铝蜂窝陶瓷催化剂载体。A. Immerse the 6mm*6mm*28mm cube-shaped alumina honeycomb ceramic catalyst carrier in a container with a mass concentration of 30% hydrogen peroxide solution, let it stand for 6 hours at room temperature, and then repeatedly wash and dry until it is neutral. The pretreated alumina honeycomb ceramic catalyst carrier was obtained by drying in an oven at 80 °C for 12 h.

B、将一定量四水硝酸锰及硝酸铈(锰铈元素摩尔比=1:1)分别溶解于适量的去离子水中,搅拌至完全溶解后混合均匀,然后加入相当于锰元素摩尔量0.7倍的柠檬酸并在80℃水浴中充分搅拌2h。B. Dissolve a certain amount of manganese nitrate tetrahydrate and cerium nitrate (molar ratio of manganese-cerium element = 1:1) in an appropriate amount of deionized water respectively, stir until completely dissolved and mix evenly, then add 0.7 times the molar amount of manganese element citric acid and fully stirred in a water bath at 80 °C for 2 h.

C、将预处理后的陶瓷载体浸渍在得到的混合溶液中,超声浸渍60min,再将涂覆有催化剂前驱体溶液的预处理载体首先在350℃下干燥1h,然后在450℃下焙烧5h,即得所述用于低温脱硝的整体型锰基催化剂。C. Immerse the pretreated ceramic carrier in the obtained mixed solution, ultrasonically impregnate it for 60 minutes, and then dry the pretreated carrier coated with the catalyst precursor solution at 350 °C for 1 h, and then bake it at 450 °C for 5 h, That is, the monolithic manganese-based catalyst for low-temperature denitration is obtained.

制备得到的锰铈低温脱硝整体催化剂中活性组分占比约为6.39%,在反应温度110℃-160℃内、NO流量为6mL/min,NO流量为6mL/min、O2流量为15mL/min、N2流量为129mL/min、空速为8000h-1的条件下,所得催化剂在NH3-SCR脱硝过程中NO转化率见图1。The proportion of active components in the prepared manganese-cerium low-temperature denitration monolith catalyst is about 6.39%. Within the reaction temperature of 110℃-160℃, the NO flow rate is 6mL/min, the NO flow rate is 6mL/min, and the O 2 flow rate is 15mL/min. Under the conditions of min, N 2 flow rate of 129 mL/min, and space velocity of 8000 h -1 , the NO conversion rate of the obtained catalyst in the NH 3 -SCR denitration process is shown in Figure 1.

实施例7Example 7

一种用于低温脱硝的整体型锰基催化剂的制备方法,包括以下步骤:A preparation method of a monolithic manganese-based catalyst for low-temperature denitration, comprising the following steps:

A、将6mm*6mm*28mm的立方体型氧化铝蜂窝陶瓷催化剂载体浸渍在装有质量浓度30%过氧化氢溶液的容器中,在室温下静置6h,再反复水洗干燥直至显中性,放入烘箱中80℃下干燥12h得到预处理后的氧化铝蜂窝陶瓷催化剂载体。A. Immerse the 6mm*6mm*28mm cube-shaped alumina honeycomb ceramic catalyst carrier in a container with a mass concentration of 30% hydrogen peroxide solution, let it stand for 6 hours at room temperature, and then repeatedly wash and dry until it is neutral. The pretreated alumina honeycomb ceramic catalyst carrier was obtained by drying in an oven at 80 °C for 12 h.

B、将一定量的四水硝酸锰及硝酸铈(锰铈元素摩尔比=3:7)分别溶解于适量的去离子水中,搅拌至完全溶解后混合均匀,然后加入相当于锰元素摩尔量0.7倍的柠檬酸并在80℃水浴中充分搅拌1h。B, a certain amount of manganese nitrate tetrahydrate and cerium nitrate (molar ratio of manganese-cerium element = 3:7) are dissolved in an appropriate amount of deionized water respectively, stirred to be completely dissolved and mixed uniformly, and then added equivalent to 0.7 mole of manganese element times of citric acid and fully stirred in a water bath at 80 °C for 1 h.

C、将预处理后的陶瓷载体浸渍在得到的混合溶液中,超声浸渍35min,再将涂覆有催化剂前驱体溶液的预处理载体首先在150℃下干燥1h,然后在650℃下焙烧5h,即得所述用于低温脱硝的整体型锰基催化剂。C. Immerse the pretreated ceramic carrier in the obtained mixed solution, ultrasonically impregnate it for 35 minutes, and then dry the pretreated carrier coated with the catalyst precursor solution at 150 °C for 1 h, and then bake it at 650 °C for 5 h. That is, the monolithic manganese-based catalyst for low-temperature denitration is obtained.

制备得到的锰铈低温脱硝整体催化剂中活性组分占比约为13.6%,在反应温度110℃-160℃内、NO流量为6mL/min,NO流量为6mL/min、O2流量为15mL/min、N2流量为129mL/min、空速为8000h-1的条件下,所得催化剂在NH3-SCR脱硝过程中NO转化率见图1。The proportion of active components in the prepared manganese-cerium low-temperature denitration monolithic catalyst is about 13.6%. Within the reaction temperature of 110℃-160℃, the NO flow rate is 6mL/min, the NO flow rate is 6mL/min, and the O 2 flow rate is 15mL/min. Under the conditions of min, N 2 flow rate of 129 mL/min, and space velocity of 8000 h -1 , the NO conversion rate of the obtained catalyst in the NH 3 -SCR denitration process is shown in Figure 1.

实施例8Example 8

一种用于低温脱硝的整体型锰基催化剂的制备方法,与实施例1的不同之处在于,步骤A具体包括如下步骤:将底面直径为11mm,高为24mm的圆柱型堇青石陶瓷催化剂载体浸渍在装有质量浓度20%的磷酸溶液的容器中,在室温下静置8h,再反复水洗干燥直至显中性,放入烘箱中120℃下干燥12h得到预处理后的堇青石陶瓷催化剂载体;步骤B中样品溶液锰元素与铁元素的摩尔比为0.5:1,有机化合物与锰元素摩尔比为0.5:1。其余操作与实施例1相同。A preparation method of a monolithic manganese-based catalyst for low-temperature denitration, the difference from Example 1 is that step A specifically includes the following steps: a cylindrical cordierite ceramic catalyst carrier with a bottom diameter of 11 mm and a height of 24 mm It was immersed in a container containing a phosphoric acid solution with a mass concentration of 20%, left standing at room temperature for 8 hours, washed and dried repeatedly until it became neutral, and was dried in an oven at 120 ° C for 12 hours to obtain a pretreated cordierite ceramic catalyst carrier. ; In step B, the molar ratio of manganese element and iron element in the sample solution is 0.5:1, and the molar ratio of organic compound and manganese element is 0.5:1. The rest of the operations are the same as in Example 1.

实施例9Example 9

一种用于低温脱硝的整体型锰基催化剂的制备方法,与实施例1的不同之处在于,步骤A具体包括如下步骤:将底面直径为11mm,高为24mm的圆柱型堇青石陶瓷催化剂载体浸渍在装有质量浓度40%的磷酸溶液的容器中,在室温下静置4h,再反复水洗干燥直至显中性,放入烘箱中90℃下干燥12h得到预处理后的堇青石陶瓷催化剂载体;步骤B中样品溶液锰元素与铁元素的摩尔比为1.5:1,有机化合物与锰元素摩尔比为1:1;其余操作与实施例1相同。A preparation method of a monolithic manganese-based catalyst for low-temperature denitration, the difference from Example 1 is that step A specifically includes the following steps: a cylindrical cordierite ceramic catalyst carrier with a bottom diameter of 11 mm and a height of 24 mm Immerse in a container containing a phosphoric acid solution with a mass concentration of 40%, let stand for 4 hours at room temperature, and then repeatedly wash and dry until it becomes neutral, put it in an oven and dry at 90 ° C for 12 hours to obtain the pretreated cordierite ceramic catalyst carrier In step B, the molar ratio of manganese element and iron element in the sample solution is 1.5:1, and the molar ratio of organic compound and manganese element is 1:1; the remaining operations are the same as those in Example 1.

实施例10Example 10

一种用于低温脱硝的整体型锰基催化剂的制备方法,与实施例5的不同之处在于,步骤A具体包括如下步骤,将底面直径为11mm,高为24mm的圆柱型氧化铝陶瓷催化剂载体浸渍在装有质量浓度20%的过氧化氢溶液的容器中,在室温下静置8h,再反复水洗干燥直至显中性,放入烘箱中120℃下干燥12h得到预处理后的氧化铝陶瓷催化剂载体。步骤B中样品溶液锰元素与铈元素的摩尔比为1:7,有机化合物与锰元素摩尔比为2:1。步骤C中将预处理后的陶瓷载体浸渍在得到的混合溶液中,超声浸渍60min,再将涂覆有催化剂前驱体溶液的预处理载体首先在350℃下干燥1h,然后在550℃下焙烧6h,即得所述用于低温脱硝的整体型锰基催化剂。其余操作与实施例1相同其余操作与实施例5相同。A preparation method of a monolithic manganese-based catalyst for low-temperature denitration, which differs from Example 5 in that step A specifically includes the following steps: a cylindrical alumina ceramic catalyst carrier with a bottom diameter of 11 mm and a height of 24 mm Immerse in a container with a hydrogen peroxide solution with a mass concentration of 20%, let stand for 8 hours at room temperature, and then repeatedly wash and dry until it becomes neutral, put it in an oven and dry at 120 ° C for 12 hours to obtain pretreated alumina ceramics catalyst carrier. In step B, the molar ratio of manganese element to cerium element in the sample solution is 1:7, and the molar ratio of organic compound to manganese element is 2:1. In step C, the pretreated ceramic carrier is immersed in the obtained mixed solution, ultrasonically immersed for 60 min, and then the pretreated carrier coated with the catalyst precursor solution is first dried at 350 ° C for 1 h, and then calcined at 550 ° C for 6 h , that is, the monolithic manganese-based catalyst for low-temperature denitration is obtained. The rest of the operations are the same as in Example 1 and the rest of the operations are the same as those in Example 5.

实施例11Example 11

一种用于低温脱硝的整体型锰基催化剂的制备方法,与实施例5的不同之处在于,步骤A具体包括如下步骤,将底面直径为11mm,高为24mm的圆柱型氧化铝陶瓷催化剂载体浸渍在装有质量浓度30%的磷酸溶液的容器中,在室温下静置4h,再反复水洗干燥直至显中性,放入烘箱中90℃下干燥12h得到预处理后的氧化铝陶瓷催化剂载体;步骤B中样品溶液锰元素与铈元素的摩尔比为2:9,有机化合物与锰元素摩尔比为2:1。步骤C中将预处理后的陶瓷载体浸渍在得到的混合溶液中,超声浸渍60min,再将涂覆有催化剂前驱体溶液的预处理载体首先在250℃下干燥1h,然后在500℃下焙烧6h,即得所述用于低温脱硝的整体型锰基催化剂。其余操作与实施例1相同其余操作与实施例5相同。A preparation method of a monolithic manganese-based catalyst for low-temperature denitration, which differs from Example 5 in that step A specifically includes the following steps: a cylindrical alumina ceramic catalyst carrier with a bottom diameter of 11 mm and a height of 24 mm It was immersed in a container containing a phosphoric acid solution with a mass concentration of 30%, stood at room temperature for 4 hours, washed and dried repeatedly until it became neutral, and was dried in an oven at 90 °C for 12 hours to obtain the pretreated alumina ceramic catalyst carrier. In step B, the molar ratio of manganese element and cerium element in the sample solution is 2:9, and the molar ratio of organic compound and manganese element is 2:1. In step C, the pretreated ceramic carrier is immersed in the obtained mixed solution, ultrasonically immersed for 60 min, and then the pretreated carrier coated with the catalyst precursor solution is first dried at 250 ° C for 1 h, and then calcined at 500 ° C for 6 h , that is, the monolithic manganese-based catalyst for low-temperature denitration is obtained. The rest of the operations are the same as in Example 1 and the rest of the operations are the same as those in Example 5.

以上对本发明的具体实施例进行了描述。需要理解的是,本发明并不局限于上述特定实施方式,本领域技术人员可以在权利要求的范围内做出各种变化或修改,这并不影响本发明的实质内容。在不冲突的情况下,本申请的实施例和实施例中的特征可以任意相互组合。Specific embodiments of the present invention have been described above. It should be understood that the present invention is not limited to the above-mentioned specific embodiments, and those skilled in the art can make various changes or modifications within the scope of the claims, which do not affect the essential content of the present invention. The embodiments of the present application and features in the embodiments may be combined with each other arbitrarily, provided that there is no conflict.

Claims (10)

1.一种用于低温脱硝的整体型锰基催化剂的制备方法,其特征在于:包括如下步骤:1. a preparation method for the monolithic manganese-based catalyst for low temperature denitration, is characterized in that: comprise the steps: A、预处理载体:将蜂窝陶瓷催化剂载体浸渍在氧化性溶剂中,洗涤至显中性,干燥备用;A. Pretreatment carrier: The honeycomb ceramic catalyst carrier is immersed in an oxidizing solvent, washed to become neutral, and dried for later use; B、制备催化剂前驱体溶液:将锰盐、铁盐或锰盐、铈盐溶于溶剂中得到混合溶液,加入有机化合物,水浴加热搅拌;B. Preparation of catalyst precursor solution: dissolving manganese salt, iron salt or manganese salt and cerium salt in a solvent to obtain a mixed solution, adding an organic compound, heating and stirring in a water bath; C、制备整体型催化剂:将催化剂前驱体溶液干燥并焙烧得到催化剂粉末,将催化剂粉末与去离子水、络合粘结剂混合涂覆至预处理载体上;或直接添加预处理载体至催化剂前驱体溶液中,将涂覆有催化剂前驱体溶液的预处理载体干燥、焙烧,即得所述用于低温脱硝的整体型锰基催化剂,所述用于低温脱硝的整体型锰基催化剂负载的锰基活性组分的质量百分比含量为6%~14%。C. Preparation of monolithic catalyst: drying and calcining the catalyst precursor solution to obtain catalyst powder, mixing the catalyst powder with deionized water and complex binder and coating it on the pretreatment carrier; or directly adding the pretreatment carrier to the catalyst precursor In the bulk solution, the pretreatment carrier coated with the catalyst precursor solution is dried and calcined to obtain the monolithic manganese-based catalyst for low-temperature denitration, and the manganese supported by the monolithic manganese-based catalyst for low-temperature denitration The mass percentage content of the base active component is 6% to 14%. 2.根据权利要求1所述的用于低温脱硝的整体型锰基催化剂的制备方法,其特征在于,步骤A中所述蜂窝陶瓷催化剂载体包括氧化铝陶瓷、堇青石陶瓷中的一种或多种。2. The preparation method of the monolithic manganese-based catalyst for low-temperature denitration according to claim 1, wherein the honeycomb ceramic catalyst carrier described in step A comprises one or more of alumina ceramics and cordierite ceramics. kind. 3.根据权利要求1所述的用于低温脱硝的整体型锰基催化剂的制备方法,其特征在于,步骤A中所述氧化性溶剂包括质量百分浓度为20%-40%的磷酸溶液或质量百分浓度为15%-30%的过氧化氢溶液。3. The preparation method of the monolithic manganese-based catalyst for low-temperature denitration according to claim 1, wherein the oxidizing solvent in step A comprises a phosphoric acid solution with a mass percentage concentration of 20%-40% or Hydrogen peroxide solution with mass percentage concentration of 15%-30%. 4.根据权利要求1所述的用于低温脱硝的整体型锰基催化剂的制备方法,其特征在于,步骤A中所述蜂窝陶瓷催化剂载体浸渍在氧化性溶剂的浸渍时间为4-8h,干燥温度在80-120℃。4. The preparation method of the monolithic manganese-based catalyst for low-temperature denitration according to claim 1, wherein the dipping time of the honeycomb ceramic catalyst carrier in the step A is 4-8h, and the drying time is 4-8h. The temperature is 80-120℃. 5.根据权利要求1所述的用于低温脱硝的整体型锰基催化剂的制备方法,其特征在于,步骤B中所述锰盐包括硝酸锰、醋酸锰中的一种或多种;所述铁盐包括硝酸铁、草酸氨铁、醋酸铁,柠檬酸铁中的一种或多种;所述铈盐包括硝酸铈、草酸铈胺中的一种或多种;所述溶剂包括去离子水、甲醇、乙醇中的一种或多种。5. The preparation method of the monolithic manganese-based catalyst for low-temperature denitration according to claim 1, wherein the manganese salt in step B comprises one or more of manganese nitrate and manganese acetate; the described The iron salt includes one or more of ferric nitrate, ferric ammonia oxalate, ferric acetate, and ferric citrate; the cerium salt includes one or more of cerium nitrate and ceric amine oxalate; the solvent includes deionized water , one or more of methanol and ethanol. 6.根据权利要求1所述的用于低温脱硝的整体型锰基催化剂的制备方法,其特征在于,步骤B中所述所述有机化合物包括尿素、柠檬酸、甘氨酸中的一种或多种。6. The method for preparing a monolithic manganese-based catalyst for low-temperature denitration according to claim 1, wherein the organic compound described in step B comprises one or more of urea, citric acid, and glycine . 7.根据权利要求1所述的用于低温脱硝的整体型锰基催化剂的制备方法,其特征在于,步骤B所述混合溶液中锰元素与铁元素的摩尔比为(0.5-1.5):1;锰元素与铈元素的摩尔比为(1-5):(5-9),所述有机化合物与锰元素摩尔比为(0.5-5):1。7. the preparation method of the monolithic manganese-based catalyst for low-temperature denitration according to claim 1, is characterized in that, in the described mixed solution of step B, the mol ratio of manganese element and iron element is (0.5-1.5): 1 ; The molar ratio of manganese element and cerium element is (1-5): (5-9), and the molar ratio of described organic compound and manganese element is (0.5-5): 1. 8.根据权利要求1所述的用于低温脱硝的整体型锰基催化剂的制备方法,其特征在于,步骤B中所述水浴的加热温度为70℃-90℃,加热时间为1h-4h。8 . The method for preparing a monolithic manganese-based catalyst for low-temperature denitration according to claim 1 , wherein the heating temperature of the water bath in step B is 70°C-90°C, and the heating time is 1h-4h. 9 . 9.根据权利要求1所述的用于低温脱硝的整体型锰基催化剂的制备方法,其特征在于,所述步骤C具体包括如下步骤:9. The preparation method of the monolithic manganese-based catalyst for low-temperature denitration according to claim 1, wherein the step C specifically comprises the following steps: 将催化剂前驱体溶液在80℃-120℃下干燥6h-12h并在450℃-650℃下焙烧4h-6h,得到催化剂粉末后再混合离子水以及络合粘结剂,利用压缩机喷枪喷涂预处理后的载体1min-5min,80℃-120℃下干燥1h-3h,重复若干次,即得所述用于低温脱硝的整体型锰基催化剂,其中预处理载体质量与去离子水、络合粘结剂的质量比为1:(0.75-1.25):(0.05-0.2);The catalyst precursor solution was dried at 80°C-120°C for 6h-12h and calcined at 450°C-650°C for 4h-6h to obtain catalyst powder, then mixed with ionized water and complex binder, and sprayed with a compressor spray gun for pre-treatment. The treated carrier is dried for 1min-5min at 80℃-120℃ for 1h-3h, and repeated several times to obtain the monolithic manganese-based catalyst for low-temperature denitration, wherein the quality of the pretreated carrier is combined with deionized water, complexed The mass ratio of the binder is 1:(0.75-1.25):(0.05-0.2); 或将预处理载体添加至催化剂前驱体溶液中,超声浸渍10min-60min,再将涂覆有催化剂前驱体溶液的预处理载体首先在150℃-350℃下干燥1h,然后在450℃-650℃下焙烧5h-6h,即得所述用于低温脱硝的整体型锰基催化剂。Or add the pretreated carrier to the catalyst precursor solution, ultrasonically immerse it for 10min-60min, and then dry the pretreated carrier coated with the catalyst precursor solution at 150℃-350℃ for 1h, then at 450℃-650℃ After calcining for 5h-6h, the monolithic manganese-based catalyst for low-temperature denitration can be obtained. 10.根据权利要求9所述的用于低温脱硝的整体型锰基催化剂的制备方法,其特征在于,所述络合粘结剂包括硅溶胶、铝溶胶、甲基纤维素中的一种或多种。10 . The method for preparing a monolithic manganese-based catalyst for low-temperature denitration according to claim 9 , wherein the complex binder comprises one of silica sol, aluminum sol, and methyl cellulose. 11 . variety.
CN202010431506.3A 2020-03-30 2020-05-20 A kind of preparation method of monolithic manganese-based catalyst for low-temperature denitration Pending CN111408365A (en)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
CN2020102392421 2020-03-30
CN202010239242 2020-03-30

Publications (1)

Publication Number Publication Date
CN111408365A true CN111408365A (en) 2020-07-14

Family

ID=71486002

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202010431506.3A Pending CN111408365A (en) 2020-03-30 2020-05-20 A kind of preparation method of monolithic manganese-based catalyst for low-temperature denitration

Country Status (1)

Country Link
CN (1) CN111408365A (en)

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111762782A (en) * 2020-07-15 2020-10-13 成都云白环境设备制造有限公司 Preparation method of desulfurization and denitrification activated carbon
CN112371134A (en) * 2020-12-04 2021-02-19 上海交通大学 Preparation method of expanded graphite-based carrier-loaded low-temperature denitration catalyst
CN112892548A (en) * 2021-01-25 2021-06-04 天津大学 Preparation method of manganese-based catalyst for sewage treatment and manganese-based catalyst
CN113101966A (en) * 2021-03-01 2021-07-13 华南理工大学 SCR flue gas denitration catalyst and preparation method thereof
CN113522304A (en) * 2021-08-04 2021-10-22 安徽科浦环保科技有限公司 Preparation method of wide-temperature selective trapping reduction denitration material
CN113908842A (en) * 2021-10-19 2022-01-11 石河子大学 A kind of denitration catalyst for CO-SCR flue gas denitration and preparation method thereof
CN114192176A (en) * 2021-12-29 2022-03-18 安徽元琛环保科技股份有限公司 Carbon-doped graphite-phase carbon nitride-loaded iron-manganese denitration catalyst and preparation method and application thereof
CN115069231A (en) * 2022-07-22 2022-09-20 中国矿业大学(北京) Integral SCR catalyst for back corona catalytic component and preparation method thereof
CN115888693A (en) * 2022-10-25 2023-04-04 浙江大学 Supported manganese/cerium low-temperature honeycomb denitration catalyst and preparation method thereof

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102114424A (en) * 2010-12-29 2011-07-06 国电科学技术研究院 Low-temperature smoke denitration SCR (silicon controlled rectifier) catalyst and preparation method
CN103933971A (en) * 2014-04-23 2014-07-23 中国科学院山西煤炭化学研究所 Low-temperature denitration catalyst as well as preparation method and application thereof
CN105618032A (en) * 2016-01-19 2016-06-01 中国建筑材料科学研究总院 Supported manganese based low-temperature denitration catalyst and preparation method thereof
CN105727985A (en) * 2016-01-27 2016-07-06 中国建筑材料科学研究总院 Honeycomb integral type low temperature denitrifying catalyst and preparation method thereof
CN105854874A (en) * 2016-05-12 2016-08-17 石河子大学 Denitrification catalyst, preparation method of denitrification catalyst and application of denitrification catalyst in flue gas denitrification
CN110605122A (en) * 2018-06-14 2019-12-24 中国石油化工股份有限公司 Low-temperature flue gas denitration catalyst and preparation method and application thereof

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102114424A (en) * 2010-12-29 2011-07-06 国电科学技术研究院 Low-temperature smoke denitration SCR (silicon controlled rectifier) catalyst and preparation method
CN103933971A (en) * 2014-04-23 2014-07-23 中国科学院山西煤炭化学研究所 Low-temperature denitration catalyst as well as preparation method and application thereof
CN105618032A (en) * 2016-01-19 2016-06-01 中国建筑材料科学研究总院 Supported manganese based low-temperature denitration catalyst and preparation method thereof
CN105727985A (en) * 2016-01-27 2016-07-06 中国建筑材料科学研究总院 Honeycomb integral type low temperature denitrifying catalyst and preparation method thereof
CN105854874A (en) * 2016-05-12 2016-08-17 石河子大学 Denitrification catalyst, preparation method of denitrification catalyst and application of denitrification catalyst in flue gas denitrification
CN110605122A (en) * 2018-06-14 2019-12-24 中国石油化工股份有限公司 Low-temperature flue gas denitration catalyst and preparation method and application thereof

Cited By (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111762782A (en) * 2020-07-15 2020-10-13 成都云白环境设备制造有限公司 Preparation method of desulfurization and denitrification activated carbon
CN112371134A (en) * 2020-12-04 2021-02-19 上海交通大学 Preparation method of expanded graphite-based carrier-loaded low-temperature denitration catalyst
CN112371134B (en) * 2020-12-04 2022-04-08 上海交通大学 Preparation method of expanded graphite-based carrier-loaded low-temperature denitration catalyst
CN112892548A (en) * 2021-01-25 2021-06-04 天津大学 Preparation method of manganese-based catalyst for sewage treatment and manganese-based catalyst
CN113101966A (en) * 2021-03-01 2021-07-13 华南理工大学 SCR flue gas denitration catalyst and preparation method thereof
CN113522304A (en) * 2021-08-04 2021-10-22 安徽科浦环保科技有限公司 Preparation method of wide-temperature selective trapping reduction denitration material
CN113908842A (en) * 2021-10-19 2022-01-11 石河子大学 A kind of denitration catalyst for CO-SCR flue gas denitration and preparation method thereof
CN113908842B (en) * 2021-10-19 2024-04-16 石河子大学 Denitration catalyst for CO-SCR flue gas denitration and preparation method thereof
CN114192176A (en) * 2021-12-29 2022-03-18 安徽元琛环保科技股份有限公司 Carbon-doped graphite-phase carbon nitride-loaded iron-manganese denitration catalyst and preparation method and application thereof
CN114192176B (en) * 2021-12-29 2023-11-10 安徽元琛环保科技股份有限公司 Carbon-doped graphite-phase carbon nitride-loaded iron-manganese denitration catalyst and preparation method and application thereof
CN115069231A (en) * 2022-07-22 2022-09-20 中国矿业大学(北京) Integral SCR catalyst for back corona catalytic component and preparation method thereof
CN115888693A (en) * 2022-10-25 2023-04-04 浙江大学 Supported manganese/cerium low-temperature honeycomb denitration catalyst and preparation method thereof

Similar Documents

Publication Publication Date Title
CN111408365A (en) A kind of preparation method of monolithic manganese-based catalyst for low-temperature denitration
CN109999829A (en) A kind of bimetallic manganese iron low temperature SCR denitration catalyst, preparation method and applications
WO2015161627A1 (en) Honeycomb denitration catalyst for flue gas at 400°c-600°c and preparation method therefor
CN110605114B (en) Application of mullite oxide supported catalyst in low-temperature selective catalytic reduction denitration
CN102019187A (en) Low-temperature flue gas SCR (Selective Catalytic Reduction) denitrating catalyst and preparation method and application thereof
CN106732799A (en) A kind of new type low temperature denitration MOF catalyst and preparation method thereof
CN105413715A (en) Composite support loaded type sulfated Mn-Co-Ce sulfur-tolerant catalyst for low-temperature flue gas denitration and preparation method of sulfur-tolerant catalyst
CN106076318A (en) A kind of preparation method of integral catalyzer
CN110314681A (en) One kind is based on kaolinic low temperature SCR denitration catalyst and preparation method thereof
CN112371134B (en) Preparation method of expanded graphite-based carrier-loaded low-temperature denitration catalyst
CN110252317A (en) A Ce-Fe-Based Catalyst for Nitrogen Oxide Removal at Low Temperature and High Efficiency
CN105233814A (en) Cerium oxide catalyst for catalyzing and purifying nitric oxides, preparation method and application
CN113694933A (en) High-entropy co-doped low-temperature SCR denitration catalyst and preparation method and application thereof
CN102008955B (en) Selective catalytic reduction catalyst for diesel vehicle exhaust purification and preparation method thereof
CN116351427A (en) A kind of denitrification catalyst for synthetic flue gas denitrification and its preparation method and application
CN114308053B (en) Denitration catalyst taking high-entropy oxide as active component and preparation and application thereof
CN114210372B (en) An Fe-based denitrification ammonia synthesis catalyst and its preparation method and application
CN115245820A (en) A kind of spinel catalyst, its preparation method and application
CN107185523A (en) Preparation method of denitrating catalyst that a kind of holmium is modified and products thereof
CN110548521A (en) high-performance low-temperature NH 3 -SCR catalyst and preparation method and application thereof
CN105879869A (en) Catalyst used for hydrogen selective reduction of nitric oxide as well as preparation method and application thereof
CN109745997A (en) Preparation method of spherical low-temperature denitration catalyst, spherical low-temperature denitration catalyst prepared by the method and application thereof
CN118204091A (en) A hydrophobic transition metal composite catalyst and its preparation method and application
CN115591575B (en) A denitration catalyst and its preparation method and application
CN117599781A (en) Noble metal @ TiO 2 /TiO 2 Catalyst, preparation method and application thereof

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication

Application publication date: 20200714

RJ01 Rejection of invention patent application after publication