CN111215049A - Mn doped with Cr ions3O4Thermal catalytic material and preparation method and application thereof - Google Patents

Mn doped with Cr ions3O4Thermal catalytic material and preparation method and application thereof Download PDF

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CN111215049A
CN111215049A CN202010141692.7A CN202010141692A CN111215049A CN 111215049 A CN111215049 A CN 111215049A CN 202010141692 A CN202010141692 A CN 202010141692A CN 111215049 A CN111215049 A CN 111215049A
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chromium
catalytic material
ion doped
thermal
alkali
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CN111215049B (en
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范晓星
杨媛
成祥祥
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Liaoning University
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    • 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
    • B01D53/86Catalytic processes
    • B01D53/8668Removing organic compounds not provided for in B01D53/8603 - B01D53/8665

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Abstract

The invention discloses a Cr ion doped Mn3O4A thermal catalytic material, a preparation method and application thereof. Adding chromium salt or chromium alkali into aqueous solution of manganese salt, adding the mixed solution into aqueous alkali, performing ultrasonic treatment, centrifuging, drying and cooling to obtain precursor, grinding the precursor, and performing high-temperature calcination treatment to obtain Cr-Mn3O4. The Cr ion prepared by the method of the invention is doped with Mn3O4Thermal catalytic material, improved Mn3O4Under the dark condition, the defect of low thermal response at low temperature is overcome, the movement of lattice oxygen in the lattice is improved, the initial temperature required by the reaction is reduced, the thermal degradation rate is improved, and the thermal catalytic activity can be effectively improved. By usingWhich can degrade organic contaminants by heating under dark conditions.

Description

Mn doped with Cr ions3O4Thermal catalytic material and preparation method and application thereof
Technical Field
The invention relates to a preparation method of a doped material and application of thermal catalytic performance in the technical field of degradation of volatile organic pollutants under dark conditions, in particular to Cr ion doped Mn3O4A thermal catalytic material, a preparation method and application thereof.
Background
With the development of human society, the burning of fossil fuels has caused a series of serious environmental problems, and the acquisition and conversion of solar energy into usable energy has become a key problem of human society. In recent years, the photocatalytic degradation of organic pollutants has attracted more and more attention due to its advantages of no pollution, mild reaction conditions, and the like. However, due to the effect of the photocatalytic material on its own bandwidth, the larger the bandwidth, the smaller the photoresponse range, and the lower the photocatalytic efficiency. On the basis, the thermocatalysis material under different temperatures in a dark condition is provided, and the thermocatalysis technology is sustainable development and environment-friendly, and has the characteristics of no secondary pollution, cyclic regeneration and the like. The thermocatalytic mechanism is generally that the contaminants are oxidized by the crystal lattice in the catalyst, creating oxygen vacancies and active oxygen catalyst. Subsequently, the oxygen vacancies and oxygen generate lattice oxygen. Doping is an effective and simple method for improving the thermocatalytic performance, because the doping can cause the change of the specific surface area, and the doping of doping ions can generate lattice defects, so that oxygen atoms in lattices are easier to migrate, the initial temperature of the reaction is reduced, and the thermocatalytic reaction efficiency is improved.
Disclosure of Invention
The invention aims to provide a Cr ion doped Mn3O4The method is easy to operate, simple, convenient, low in cost, mild in condition and beneficial to large-scale production.
In order to achieve the purpose, the invention adopts the technical scheme that: mn doped with Cr ions3O4The preparation method of the thermal catalytic material comprises the following steps:
1) preparing an aqueous solution of manganese salt; preparing an alkali solution;
2) adding chromium salt or chromium alkali into the aqueous solution of manganese salt, and performing ultrasonic treatment to uniformly mix the chromium salt or chromium alkali with the aqueous solution of manganese salt;
3) adding the mixed solution obtained in the step 2) into an alkali solution; ultrasonically mixing the mixture evenly; centrifuging to obtain a precipitate, drying and cooling to obtain a precursor;
4) and 3) carrying out high-temperature calcination treatment on the precursor obtained in the step 3) to obtain a target product.
Preferably, the Cr ions mentioned above are doped with Mn3O4The thermal catalysis material is prepared by using manganese salt as a manganese acetate, manganese nitrate or manganese chloride in the step 1).
Preferably, the Cr ions mentioned above are doped with Mn3O4The thermal catalytic material is prepared by the step 1), wherein the alkali solution is sodium hydroxide aqueous solution, potassium hydroxide aqueous solution or ammonium hydroxide aqueous solution.
Preferably, the Cr ions mentioned above are doped with Mn3O4The thermal catalysis material is prepared by the step 2) that the chromium salt is chromium nitrate and the chromium base is chromium hydroxide.
Preferably, the Cr ions mentioned above are doped with Mn3O4Thermocatalytic material, step 2), in molar ratio, Mn2+:Cr3+=1:0.01-0.2。
Preferably, the Cr ions mentioned above are doped with Mn3O4Thermocatalytic material, step 2), in molar ratio, Mn2+: OH in alkali-=1:2-4。
Preferably, the Cr ions mentioned above are doped with Mn3O4The thermal catalysis material, in the step 3), the drying temperature is 50-100 ℃.
Preferably, the Cr ions mentioned above are doped with Mn3O4And (3) carrying out high-temperature calcination treatment on the thermal catalytic material in the step 4), wherein the temperature is 300-600 ℃, and the time is 2-3 h.
The above-mentioned Cr ion-doped Mn3O4The application of the thermal catalytic material in catalytic degradation of gaseous pollutants under dark heating conditions.
Preferably, for the above-mentioned application, the gaseous contaminant is isopropanol.
The invention has the beneficial effects that:
1. the invention provides Cr ion doped Mn3O4The preparation method of the thermal catalytic material successfully constructs a doped structure, and the structure can more easily move lattice oxygen and effectively improve the thermal catalytic activity.
2. The preparation method provided by the invention has the advantages of cheap and easily available raw materials, simple and convenient operation, greatly reduced cost, no toxicity, no pollution to the environment and realization of green chemistry.
3. The invention provides Cr ion doped Mn3O4The thermal catalytic material, chromium doped mangano-manganic oxide can generate lattice defects, so that oxygen atoms in the lattice can be more easily transferred, the thermal catalytic activity can be promoted, and the Cr ion doped Mn-doped thermal catalytic material provided by the invention has an important effect on improving the thermal catalytic material3O4The degradation rate of the thermal catalytic material for degrading the isopropanol is far higher than that of Mn under the dark heating condition3O4
Drawings
FIG. 1 shows pure Mn prepared in example 13O4And Cr ion doped Mn3O4XRD contrast patterns of the thermocatalytic materials.
FIG. 2a shows Cr-Mn3O4(10%) EDS energy spectrum of the sample.
FIG. 2b shows Cr-Mn3O4(10%) topography of the sample.
FIG. 2c shows Cr-Mn3O4(10%) distribution of elemental O on the surface of the sample.
FIG. 2d shows Cr-Mn3O4(10%) distribution of Mn element on the surface of the sample.
FIG. 2e shows Cr-Mn3O4(10%) distribution of Cr element on the surface of the sample.
FIG. 3 is a graph comparing the degradation rate of the thermo-catalytic material prepared in example 1 to degrade isopropanol.
FIG. 4 is a graph showing the thermal catalytic stability of the thermal catalytic material prepared in example 1 in degrading isopropanol.
Detailed Description
Example 1
(I) doping of Cr ions with Mn3O4Thermo-catalytic material Cr-Mn3O4
The preparation method comprises the following steps:
1) adding 2.86g of 50% manganese nitrate into a beaker filled with 10ml of deionized water, and stirring for 15min to fully dissolve the manganese nitrate;
2) adding 0.64g of sodium hydroxide into a beaker containing 10ml of deionized water, and stirring for 15min to fully dissolve the sodium hydroxide;
3) adding 1.28g of chromium nitrate nonahydrate (the molar weight of Cr is 10 percent of the molar weight of Mn) into the manganese salt solution obtained in the step 1), and uniformly mixing by ultrasonic waves;
4) dripping the mixed solution obtained in the step 3) into a sodium hydroxide solution, and carrying out ultrasonic treatment for 30 minutes until the solution is uniformly mixed;
5) putting the solution obtained in the step 4) into a centrifuge, and centrifuging to obtain a precipitate.
6) Putting the mixed solution obtained in the step 5) into an oven, drying at 60 ℃, and naturally cooling to obtain a precursor;
7) grinding the precursor obtained in the step 6), heating to 400 ℃ at the heating rate of 5 ℃/min, and calcining for 2h to obtain the Cr ion doped Mn3O4Thermo-catalytic material Cr-Mn3O4
Comparative example (II) pure Mn3O4Thermal catalytic material
The preparation method comprises the following steps: pouring 2.86g of 50% manganese nitrate into a beaker containing 10ml of aqueous solution, adding 0.64g of sodium hydroxide into the beaker containing 10ml of deionized water, dropwise adding the manganese nitrate solution into the sodium hydroxide solution, and carrying out ultrasonic treatment for 30 minutes to fully dissolve the manganese nitrate solution; then placing the mixture in an oven to be dried at 60 ℃ to obtain a precursor; heating the obtained precursor to 450 ℃ at the heating rate of 5 ℃/min, and calcining for 2h to obtain pure Mn3O4A thermocatalytic material.
(III) detection
FIG. 1 shows the preparation of Cr ion doped Mn3O4Thermocatalytic material and pure Mn3O4XRD test pattern of the thermocatalytic material, as can be seen from FIG. 1, pure Mn3O4The diffraction peak of the photocatalytic material sample is completely consistent with the peak spectrum of the manganomanganic oxide standard card, which indicates that the prepared pure Mn3O4The thermo-catalytic material is indeed trimanganese tetroxide. Prepared Mn with 10 percent of Cr ion doping amount3O4The sample of the thermocatalytic material had Mn3O4Diffraction peaks whose peak spectra completely coincide. Because the doping amount is very small, XRD can not clearly scan a diffraction peak related to Cr ions, so that the C is subjected tor-Mn3O4(10%) the samples were subjected to elemental analysis, as shown in fig. 2 c-2 e, which showed that elements such as oxygen, manganese, chromium, etc. had significant strong signals and were uniformly distributed. As shown in FIG. 2a, no additional residual element was found in the EDS results, demonstrating that the Cr ion doped Mn prepared by the present invention3O4The thermal catalytic material is doped with Cr ions.
Example 2 application
(one) influence of different catalytic materials on catalytic degradation rate of isopropanol at different temperatures
The test process is as follows: 0.1g of pure Mn from example 1 were each taken3O4And 10% of Cr doping amount3O4The thermocatalyst was separately loaded into a quartz flow reactor, which was then placed in a thermostat and then connected to flowing isopropanol, and the flow rate was adjusted to 1.37 ml/s. The isopropanol was subjected to thermocatalytic degradation under dark conditions at different temperatures and the peak areas of the degraded isopropanol and the initial isopropanol were recorded. The amount of degraded isopropyl alcohol and the amount of initial isopropyl alcohol were calculated, and as shown in FIG. 3, Cr ion-doped Cr-Mn according to the present invention3O4Mn with higher thermo-catalytic degradation rate than pure Mn in composite thermo-catalytic material3O4The effect is good. Comparative pure Mn at 120 deg.C3O4,Cr-Mn3O4The degradation rate of the composite material is improved by 60 percent.
(II) influence of different time on catalytic degradation rate of isopropanol
The test process is as follows: Cr-Mn prepared with a 10% Cr doping amount of 0.1g prepared in example 13O4The thermocatalytic material was loaded into a quartz flow reactor, which was then placed in a thermostat and then connected to flowing isopropanol, and the flow rate was adjusted to 1.37 ml/s. The isopropanol was subjected to thermocatalytic degradation under dark conditions at 200 ℃ and the peak areas of degraded isopropanol and initial isopropanol at different reaction times were recorded. The amount of degraded isopropanol and the amount of initial isopropanol were calculated. As shown in FIG. 4, the degradation rate of isopropyl alcohol at 200 ℃ was varied with the reaction time within the allowable range of error, and it can be seen that Cr-Mn was produced according to the present invention3O4Composite heatThe catalytic material is very stable. The degradation rate reaches about 97.4 percent at 200 ℃.

Claims (10)

  1. Doping of Cr ions with Mn3O4The thermal catalytic material is characterized by comprising the following preparation methods:
    1) preparing an aqueous solution of manganese salt; preparing an alkali solution;
    2) adding chromium salt or chromium alkali into the aqueous solution of manganese salt, and performing ultrasonic treatment to uniformly mix the chromium salt or chromium alkali with the aqueous solution of manganese salt;
    3) adding the mixed solution obtained in the step 2) into an alkali solution, performing ultrasonic treatment to uniformly mix the mixed solution, centrifuging the mixed solution to obtain a precipitate, and drying and cooling the precipitate to obtain a precursor;
    4) grinding the precursor obtained in the step 3), and then carrying out high-temperature calcination treatment to obtain a target product.
  2. 2. The Cr ion doped Mn of claim 13O4The thermal catalytic material is characterized in that in the step 1), the manganese salt is manganese acetate, manganese nitrate or manganese chloride.
  3. 3. The Cr ion doped Mn of claim 13O4The thermal catalytic material is characterized in that in the step 1), the alkali solution is a sodium hydroxide aqueous solution, a potassium hydroxide aqueous solution or an ammonium hydroxide aqueous solution.
  4. 4. The Cr ion doped Mn of claim 13O4The thermal catalytic material is characterized in that in the step 2), the chromium salt is chromium nitrate and the chromium base is chromium hydroxide.
  5. 5. The Cr ion doped Mn of claim 13O4The thermal catalytic material is characterized in that in the step 2), Mn is used according to the molar ratio2+:Cr3+=1:0.01-0.2。
  6. 6. The Cr ion doped Mn of claim 13O4A thermocatalytic material characterized in that, in step 3), the molar ratio is,Mn2+: OH in alkali-=1:2-4。
  7. 7. The Cr ion doped Mn of claim 13O4The thermal catalysis material is characterized in that in the step 3), the drying temperature is 50-100 ℃.
  8. 8. The Cr ion doped Mn of claim 13O4The thermal catalytic material is characterized in that in the step 4), the high-temperature calcination treatment is carried out at the temperature of 300-600 ℃ for 2-3 h.
  9. 9. Cr ion doped Mn as set forth in claim 13O4The application of the thermal catalytic material in catalytic degradation of gaseous pollutants under dark heating conditions.
  10. 10. The use of claim 9, wherein the gaseous contaminant is isopropanol.
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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN115845863A (en) * 2023-01-09 2023-03-28 辽宁大学 Chromium-doped cobaltosic oxide photocatalyst and preparation method and application thereof

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CN108212147A (en) * 2018-01-31 2018-06-29 东北大学秦皇岛分校 A kind of rare-earth-doped modification mangano-manganic oxide and its preparation method and application

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US20030215712A1 (en) * 2001-06-01 2003-11-20 Feddrix Frank H Doped manganese dioxides
CN104512932A (en) * 2013-09-26 2015-04-15 天津神能科技有限公司 Preparation method of mesoporous manganic manganous oxide
CN108212147A (en) * 2018-01-31 2018-06-29 东北大学秦皇岛分校 A kind of rare-earth-doped modification mangano-manganic oxide and its preparation method and application

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A.NALLATHAMBI ET AL.: "Structural, photoluminescence and magnetic properties of chromium (Cr) doped manganese oxide (Mn3O4) hexagonal particles", 《PHYSICA E: LOW-DIMENSIONAL SYSTEMS AND NANOSTRUCTURES》 *
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Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN115845863A (en) * 2023-01-09 2023-03-28 辽宁大学 Chromium-doped cobaltosic oxide photocatalyst and preparation method and application thereof
CN115845863B (en) * 2023-01-09 2024-03-22 辽宁大学 Chromium-doped tricobalt tetraoxide photocatalyst and preparation method and application thereof

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