CN112547047A - Method for preparing nano manganese dioxide catalyst by freeze drying method - Google Patents

Method for preparing nano manganese dioxide catalyst by freeze drying method Download PDF

Info

Publication number
CN112547047A
CN112547047A CN201910913585.9A CN201910913585A CN112547047A CN 112547047 A CN112547047 A CN 112547047A CN 201910913585 A CN201910913585 A CN 201910913585A CN 112547047 A CN112547047 A CN 112547047A
Authority
CN
China
Prior art keywords
solution
polyvinyl alcohol
catalyst
permanganate
manganese
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
CN201910913585.9A
Other languages
Chinese (zh)
Inventor
徐仲均
袁悦
秦志远
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.)
Beijing University of Chemical Technology
Original Assignee
Beijing University of Chemical Technology
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 Beijing University of Chemical Technology filed Critical Beijing University of Chemical Technology
Priority to CN201910913585.9A priority Critical patent/CN112547047A/en
Publication of CN112547047A publication Critical patent/CN112547047A/en
Pending legal-status Critical Current

Links

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
    • 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
    • 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
    • B01D53/76Gas phase processes, e.g. by using aerosols
    • 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
    • B01D53/864Removing carbon monoxide or hydrocarbons
    • 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
    • B01D53/8678Removing components of undefined structure
    • B01D53/8687Organic components
    • 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
    • B01J35/20Catalysts, in general, characterised by their form or physical properties characterised by their non-solid state
    • B01J35/23Catalysts, in general, characterised by their form or physical properties characterised by their non-solid state in a colloidal state
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/32Freeze drying, i.e. lyophilisation
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2251/00Reactants
    • B01D2251/10Oxidants
    • B01D2251/104Ozone
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2256/00Main component in the product gas stream after treatment
    • B01D2256/22Carbon dioxide
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/70Organic compounds not provided for in groups B01D2257/00 - B01D2257/602
    • B01D2257/702Hydrocarbons
    • B01D2257/7027Aromatic hydrocarbons
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/70Organic compounds not provided for in groups B01D2257/00 - B01D2257/602
    • B01D2257/708Volatile organic compounds V.O.C.'s

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Chemical Kinetics & Catalysis (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)
  • Materials Engineering (AREA)
  • Organic Chemistry (AREA)
  • Dispersion Chemistry (AREA)
  • Catalysts (AREA)

Abstract

The invention provides a preparation method and application of a nano manganese dioxide catalyst. The preparation method of the catalyst comprises the steps of firstly preparing a mixed solution of polyvinyl alcohol and permanganate, then dropwise adding a divalent manganese salt solution into the mixed solution at a constant speed to react to obtain sol, then removing water in the sol by using a vacuum freeze drying technology to obtain black foamy solid mixed by the polyvinyl alcohol and the manganese dioxide, and finally calcining the solid to obtain the product of nano manganese dioxide powder. The preparation process is simple, the raw materials are easy to obtain, the catalyst can be used as a catalyst for catalyzing ozone oxidation, the catalytic activity of the catalyst is high, and the catalyst can be used for catalyzing ozone oxidation of industrial waste gas and indoor air volatile organic compounds.

Description

Method for preparing nano manganese dioxide catalyst by freeze drying method
Technical Field
The invention relates to the technical field of environment inorganic nano materials and environment treatment, in particular to a preparation method of a catalyst for catalyzing ozone to oxidize volatile organic compounds.
Background
Volatile Organic Compounds (VOCs) are a common type of atmospheric pollutants, and the emission of VOCs waste gas causes a series of problems of health, environment, production safety and the like. Therefore, exploring the purification treatment method of VOCs, reducing the discharge of VOCs is beneficial to improving the quality of atmospheric environment, protecting ecological environment and guaranteeing human health, and is also an urgent need for sustainable development of social economy.
In the field of waste gas treatment, catalytic ozonation is an effective method for treating VOCs, for example, CN201510377785.9 discloses a catalyst for catalytic ozonation of VOCs, the catalyst is composed of a metal composite oxide containing manganese, tin, cerium and antimony, the preparation cost of the catalyst is low, and the catalytic activity is high. In addition, CN201810389568.5 also discloses a catalyst for catalyzing ozone to oxidize VOCs, which is composed of an aluminum oxide carrier and a metal composite oxide, and has a large specific surface area and good stability.
Cn201410323516.x discloses a preparation method of porous manganese dioxide, which is a spongy three-dimensional porous structure; CN201410472977.3 discloses a method for preparing manganese dioxide with various structures by using permanganate and ethylene glycol to prepare rod-shaped basic manganese oxide under hydrothermal conditions, and then calcining to prepare nano rod-shaped manganese oxide, but the above patent discloses a method for preparing manganese dioxide with various structures. The common manganese dioxide has larger particle size and smaller specific surface area, and the nano manganese dioxide has finer particles and is well applied in many fields. The nano manganese dioxide catalyst prepared by the vacuum freeze-drying method can be applied to catalytic ozonation of VOCs. The vacuum freeze-drying technology is a technology that a substance containing a large amount of moisture is cooled and frozen into a solid in advance, and then water vapor is directly sublimated from the solid under the vacuum condition, so that a dried product is obtained, and the structure of the substance is not damaged. The nano manganese dioxide prepared by the preparation method has large specific surface area and good chemical stability, and can catalyze ozone to oxidize VOCs and degrade the VOCs into H2O and CO2The redundant ozone can be catalytically decomposed into oxygen, and secondary pollution can not be caused.
Disclosure of Invention
The invention discloses a method for preparing a nano manganese dioxide catalyst by utilizing a freeze-drying method, which aims to improve the deep oxidation of ozone to VOCs (volatile organic compounds) and further degrade the VOCs into CO2And H2O and the like.
The preparation method of the nano manganese dioxide comprises the following steps:
(1) mixing polyvinyl alcohol and deionized water according to a certain mass ratio, heating and stirring to obtain a polyvinyl alcohol aqueous solution;
(2) adding permanganate with certain quality into the polyvinyl alcohol aqueous solution obtained in the step (1) to obtain a mixed solution of polyvinyl alcohol and permanganate;
(3) preparing a manganous salt solution, and dropwise adding the manganous salt solution into the mixed solution of the polyvinyl alcohol and the permanganate in the step (2) at a constant speed to react to obtain sol;
(4) fully pre-freezing the sol obtained in the step (3), and then putting the sol into a vacuum freeze dryer for freeze drying to obtain black foam-like solid mixed by polyvinyl alcohol and manganese dioxide;
(5) and (4) calcining the solid obtained in the step (4) to obtain the nano manganese oxide powder.
In the step (1), the mass ratio of polyvinyl alcohol to water is 0.1-10%.
In the step (2), the permanganate solution is one or a mixture of potassium permanganate solution and sodium permanganate solution, and the mass ratio of the polyvinyl alcohol to the permanganate is 4: 1-1: 2.
In the step (3), the manganous salt solution is one or a mixture of more of a manganese chloride solution, a manganese sulfate solution, a manganese nitrate solution and a manganese acetate solution, and the concentration of the manganous salt solution is 0.01-0.6 mol/L.
In the step (4) of the preparation method, the drying process is a vacuum freeze drying technology.
In the step (5) of the preparation method, the calcining temperature is 200-600 ℃, and the calcining time is 4-10 hours.
Detailed Description
The following will further illustrate the application of the freeze-drying method of the present invention to prepare nano manganese dioxide catalyst and catalyze ozone to oxidize VOCs by specific examples.
Example 1: 6g of polyvinyl alcohol is weighed into a beakerAdding 100ml of pure water, and then putting the beaker into a water bath heating pot at 70 ℃ to heat and stir for 30min to obtain a clear and transparent polyvinyl alcohol aqueous solution. 3.16g of potassium permanganate solid was added to the polyvinyl alcohol solution cooled to room temperature to form a mixed solution of polyvinyl alcohol and potassium permanganate. Weighing 10.74g of a 50% manganese nitrate solution by mass fraction, and fixing the volume to a 100ml volumetric flask to prepare 0.3mol/L manganese nitrate solution. 100ml of manganese nitrate solution is dropwise added into a mixed solution of polyvinyl alcohol and potassium permanganate at a constant speed by using a peristaltic pump to form sol, the sol is fully pre-frozen at a low temperature, and then the sol is placed in a freeze dryer with a cold trap temperature of-50 ℃ and a working pressure of 10 Pa for freeze drying for 12 hours to obtain black foam-shaped solid of the polyvinyl alcohol and the manganese dioxide. And putting the solid into a muffle furnace, and calcining for 4 hours at 400 ℃ to obtain the nano manganese dioxide powder. Evaluation of catalyst Performance: the volume of the catalyst was 0.7mL, the gas flow rate was 125mL/min, and the inlet concentration of toluene was 60mg/m3The inlet concentration of ozone is 1000 mg/m3The measured toluene removal rate is 97%, the carbon dioxide selectivity is 60%, ozone is detected at an outlet, the ozone degradation efficiency is 98%, the operation is carried out for 40 hours, and the catalyst performance is stable.
Example 2: weighing 7g of polyvinyl alcohol and adding 100ml of pure water into a beaker, and then putting the beaker into a 70 ℃ water bath heating pot to heat and stir for 30min to obtain a clear and transparent polyvinyl alcohol aqueous solution. 3.16g of potassium permanganate solid was added to the polyvinyl alcohol solution cooled to room temperature to form a mixed solution of polyvinyl alcohol and potassium permanganate. 4.53g of anhydrous manganese sulfate solid is weighed and dissolved in pure water to prepare 100ml of 0.3mol/L manganese sulfate solution. 100ml of manganese sulfate solution is dropwise added into a mixed solution of polyvinyl alcohol and potassium permanganate at a constant speed by using a peristaltic pump to form sol, the sol is fully pre-frozen at a low temperature, and then the sol is placed in a freeze dryer with a cold trap temperature of-50 ℃ and a working pressure of 10 Pa for freeze drying for 12 hours to obtain black foam-shaped solid of the polyvinyl alcohol and the manganese dioxide. And putting the solid into a muffle furnace, and calcining for 4 hours at 300 ℃ to obtain the nano manganese dioxide powder. Evaluation of catalyst Performance: the volume of the catalyst was 0.7mL, the gas flow rate was 125mL/min, and the inlet concentration of toluene was 60mg/m3The inlet concentration of ozone is 1000 mg/m3The measured toluene purification rate is 94%, the carbon dioxide selectivity is 63%, ozone is detected at an outlet, the ozone degradation efficiency is 97%, the operation is carried out for 40 hours, and the catalyst performance is stable.
Example 3: weighing 8g of polyvinyl alcohol and adding 100ml of pure water into a beaker, and then putting the beaker into a 70 ℃ water bath heating pot to heat and stir for 30min to obtain a clear and transparent polyvinyl alcohol aqueous solution. 3.16g of potassium permanganate solid was added to the polyvinyl alcohol solution cooled to room temperature to form a mixed solution of polyvinyl alcohol and potassium permanganate. 3.78g of anhydrous manganese chloride solid is weighed and dissolved in pure water to prepare 100ml of 0.3mol/L manganese chloride solution. 100ml of manganese chloride solution is dropwise added into a mixed solution of polyvinyl alcohol and potassium permanganate at a constant speed by using a peristaltic pump to form sol, the sol is fully pre-frozen at a low temperature, and then the sol is placed in a freeze dryer with a cold trap temperature of-50 ℃ and a working pressure of 10 Pa for freeze drying for 12 hours to obtain black foam-shaped solid of the polyvinyl alcohol and the manganese dioxide. And putting the solid into a muffle furnace, and calcining for 4 hours at 300 ℃ to obtain the nano manganese dioxide powder. Evaluation of catalyst Performance: the volume of the catalyst was 0.7mL, the gas flow rate was 125mL/min, and the inlet concentration of toluene was 60mg/m3The inlet concentration of ozone is 1000 mg/m3And the measured toluene purification rate is 92%, the carbon dioxide selectivity is 65%, ozone is detected at an outlet, the ozone degradation efficiency is 95%, the operation lasts for 40 hours, and the catalyst performance is stable.

Claims (6)

1. A method for preparing nano manganese dioxide catalyst by utilizing freeze drying method comprises the following steps:
mixing polyvinyl alcohol and deionized water according to a certain mass ratio, heating and stirring to obtain a polyvinyl alcohol aqueous solution;
adding permanganate with certain quality into the polyvinyl alcohol aqueous solution obtained in the step (1) to obtain a mixed solution of polyvinyl alcohol and permanganate;
preparing a divalent manganese salt solution, and dropwise adding the divalent manganese salt solution into the mixed solution of the polyvinyl alcohol and the permanganate in the step (2) at a constant speed to react to obtain sol;
fully pre-freezing the sol obtained in the step (3), and then putting the sol into a vacuum freeze dryer for freeze drying to obtain black foam-like solid mixed by polyvinyl alcohol and manganese dioxide;
and (4) calcining the solid obtained in the step (4) to obtain the nano manganese oxide powder.
2. The method for preparing the catalyst according to claim 1, wherein the mass ratio of the polyvinyl alcohol to the water in the step (1) is 0.1% to 10%.
3. The preparation method of the catalyst according to claim 1, wherein the permanganate solution in step (2) is one or a mixture of potassium permanganate solution and sodium permanganate solution, and the mass ratio of the polyvinyl alcohol to the permanganate is 4: 1-1: 2.
4. The method for preparing the catalyst according to claim 1, wherein the manganous salt solution in the step (3) is one or more of a manganese chloride solution, a manganese sulfate solution, a manganese nitrate solution and a manganese acetate solution, and the concentration of the manganous salt solution is 0.01-0.6 mol/L.
5. The method for preparing a catalyst according to claim 1, wherein the drying process used in step (4) is a vacuum freeze-drying technique.
6. The method of preparing a catalyst according to claim 1, wherein the calcination temperature in the step (5) is 200 to 600 ℃ and the calcination time is 4 to 10 hours.
CN201910913585.9A 2019-09-25 2019-09-25 Method for preparing nano manganese dioxide catalyst by freeze drying method Pending CN112547047A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201910913585.9A CN112547047A (en) 2019-09-25 2019-09-25 Method for preparing nano manganese dioxide catalyst by freeze drying method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201910913585.9A CN112547047A (en) 2019-09-25 2019-09-25 Method for preparing nano manganese dioxide catalyst by freeze drying method

Publications (1)

Publication Number Publication Date
CN112547047A true CN112547047A (en) 2021-03-26

Family

ID=75029489

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201910913585.9A Pending CN112547047A (en) 2019-09-25 2019-09-25 Method for preparing nano manganese dioxide catalyst by freeze drying method

Country Status (1)

Country Link
CN (1) CN112547047A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113648992A (en) * 2021-09-09 2021-11-16 北京化工大学 Preparation method of catalyst for catalyzing ozone to oxidize chlorine-containing volatile organic compounds

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105797704A (en) * 2016-04-28 2016-07-27 北京化工大学常州先进材料研究院 Preparation method and application of nano zinc oxide photocatalyst
CN107537473A (en) * 2017-07-20 2018-01-05 中山大学 A kind of nanometer Mn catalyst of room temperature catalytic oxidation formaldehyde and preparation method thereof
CN108273499A (en) * 2018-02-10 2018-07-13 成都理工大学 A kind of preparation method and application of ultra micro loading gage silver titanium dioxide optical catalyst
CN108417846A (en) * 2018-01-26 2018-08-17 合肥国轩高科动力能源有限公司 Supported oxygen reduction catalyst and application thereof

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105797704A (en) * 2016-04-28 2016-07-27 北京化工大学常州先进材料研究院 Preparation method and application of nano zinc oxide photocatalyst
CN107537473A (en) * 2017-07-20 2018-01-05 中山大学 A kind of nanometer Mn catalyst of room temperature catalytic oxidation formaldehyde and preparation method thereof
CN108417846A (en) * 2018-01-26 2018-08-17 合肥国轩高科动力能源有限公司 Supported oxygen reduction catalyst and application thereof
CN108273499A (en) * 2018-02-10 2018-07-13 成都理工大学 A kind of preparation method and application of ultra micro loading gage silver titanium dioxide optical catalyst

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
曾贵玉 等: "《微纳米含能材料》", 31 May 2015 *

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113648992A (en) * 2021-09-09 2021-11-16 北京化工大学 Preparation method of catalyst for catalyzing ozone to oxidize chlorine-containing volatile organic compounds

Similar Documents

Publication Publication Date Title
CN107398272B (en) Composite carrier catalyst for room-temperature catalysis of formaldehyde and preparation method thereof
CN104056658B (en) Low-temperature sulfur-resistant denitration catalyst and preparing method thereof
CN107362823B (en) Catalytic material for degrading indoor formaldehyde at room temperature and preparation method thereof
CN113042036A (en) Preparation method and application of cerium modified amorphous manganese oxide catalyst
CN108786859A (en) A kind of preparation method of carbon doping iodine oxygen bismuth acid iodide oxygen bismuth heterojunction structure
CN115090332B (en) MOFs photocatalyst capable of removing organic pollutants in high-salt wastewater through visible light catalysis and preparation method and application thereof
CN111018565A (en) Rod-shaped ZnO piezoelectric catalytic porous ceramic material, and method and application thereof
CN115676896B (en) Amorphous manganese oxide composite material and preparation method and application thereof
CN111905751B (en) Modified LaCoO by high-temperature quenching3-δMethod for catalyzing and degrading phenol in water body by using material
CN109364912A (en) Alkaline-earth metal ions replace OMS-2 catalyst and its preparation method and application
CN113731402B (en) Catalyst and preparation method and application thereof
CN113426458B (en) Catalyst for catalytic combustion of halogen-containing volatile organic compounds and application thereof
CN105642333A (en) Multifunctional environment purification composite material, and preparation method and application thereof
CN115212869A (en) CeO preparation based on Ce-MOF precursor 2 /TiO 2 Preparation method of composite thermal catalytic material
CN112547047A (en) Method for preparing nano manganese dioxide catalyst by freeze drying method
WO2024114551A1 (en) Ceramic-based composite material used for low-concentration formaldehyde degradation, and preparation method therefor
CN101693193A (en) Rare earth-Cu-Fe active carbon adsorbent, preparation method and application thereof
CN113262780A (en) High-activity and high-stability manganese-based carbon smoke catalyst and preparation method and application thereof
CN101837300B (en) Photocatalysis coupled catalyst based on ozone and preparation method thereof
CN106390930A (en) Method for preparing silver-loaded activated carbon through glycine and silver nitrate complexation
CN110743501A (en) Metal organic framework material for purifying formaldehyde-polluted air and preparation method thereof
CN115845907A (en) Low-temperature SCR catalyst and preparation method and application thereof
CN115487823A (en) Preparation method and application of high-humidity-resistance ozonolysis catalyst
CN106076305B (en) A kind of grade spheric catalyst and preparation method thereof and its application in denitrating flue gas
CN106563508A (en) Preparation method of iron-cerium-based porous catalyst used for removing organic sulfur

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