CN113648992A - Preparation method of catalyst for catalyzing ozone to oxidize chlorine-containing volatile organic compounds - Google Patents

Preparation method of catalyst for catalyzing ozone to oxidize chlorine-containing volatile organic compounds Download PDF

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CN113648992A
CN113648992A CN202111056682.4A CN202111056682A CN113648992A CN 113648992 A CN113648992 A CN 113648992A CN 202111056682 A CN202111056682 A CN 202111056682A CN 113648992 A CN113648992 A CN 113648992A
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manganese
cerium
catalyst
solid solution
hours
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徐仲均
庄院院
陈少博
张喜荣
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Beijing University of Chemical Technology
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Beijing University of Chemical Technology
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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
    • B01D53/8671Removing components of defined structure not provided for in B01D53/8603 - B01D53/8668
    • 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
    • B01J37/0009Use of binding agents; Moulding; Pressing; Powdering; Granulating; Addition of materials ameliorating the mechanical properties of the product catalyst
    • B01J37/0018Addition of a binding agent or of material, later completely removed among others as result of heat treatment, leaching or washing,(e.g. forming of pores; protective layer, desintegrating by heat)
    • 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
    • B01J37/02Impregnation, coating or precipitation
    • B01J37/0201Impregnation
    • 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
    • B01J37/08Heat treatment
    • B01J37/082Decomposition and pyrolysis
    • B01J37/088Decomposition of a metal salt

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  • Engineering & Computer Science (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Materials Engineering (AREA)
  • Organic Chemistry (AREA)
  • Environmental & Geological Engineering (AREA)
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Abstract

The invention discloses a preparation method of a catalyst for catalyzing ozone to oxidize chlorine-Containing Volatile Organic Compounds (CVOCs). The catalyst mainly comprises MnCeOxIs prepared from active component through template process and vacuum drying process. The preparation process is simple, the raw materials are easy to obtain, and the method can effectively utilize the template agent to enable the manganese-cerium solid solution to form a specific structure and increase the specific surface area of the manganese-cerium solid solution; the surface and even the inner part of the two transition metal oxides can be improvedUniformity of the cloth, more Mn-Ce-O bonds are formed, chlorine species are made to react with HCl and Cl2Is removed in the form of (1). The catalyst prepared by the invention can catalyze ozone to oxidize CVOCs into CO at room temperature2、H2O、HCl、Cl2And the like, has excellent low-temperature redox activity, chlorine poisoning resistance and higher CO2And (4) selectivity.

Description

Preparation method of catalyst for catalyzing ozone to oxidize chlorine-containing volatile organic compounds
Technical Field
The invention relates to the technical field of environment, in particular to a preparation method of a catalyst for catalyzing ozone to oxidize chlorine-containing volatile organic compounds.
Background
Volatile Organic Compounds (VOCs) are organic chemical substances with high vapor pressure and volatility at normal temperature and normal pressure, and are important precursors for forming atmospheric pollution such as haze, photochemical smog and the like. chlorine-Containing Volatile Organic Compounds (CVOCs) are a class with a high content of VOCs and are widely used as production raw materials, solvents, refrigerants and the like. Most CVOCs have the characteristics of strong volatility, poor degradability, high toxicity and the like, and partial CVOCs even have the effect of causing three causes, so that the environmental quality is seriously influenced, and the human health is also greatly threatened. Therefore, it is urgent to find a practical and effective technique for controlling CVOCs.
The chlorine-containing volatile organic compounds have chlorine atoms which are difficult to convert in the environment, and are liable to cause catalyst poisoning and deactivation. In order to solve the problem of chlorine poisoning of the catalyst, scholars at home and abroad make a great deal of research work and develop a series of composite metal (or oxide) chlorine-resistant catalysts. CN 112588289A discloses a high CO2The selective CVOCs removing catalyst is prepared with titanium oxide as carrier, transition metal oxide as active component and noble metal Pd as modifying component. CN 101402047A discloses a catalyst for CVOCs catalytic combustion and a preparation method thereof, the cerium titanium nanotube catalyst prepared by the method can effectively remove dichloroethane and has strong chlorine poisoning resistance.
In recent years, the technology of catalyzing ozone to oxidize VOCs has attracted much attention because of the advantages of high purification efficiency, no secondary pollution, no need of auxiliary heating, etc. However, few studies on this technology have been reported to deal with CVOCs. The invention prepares a mesoporous manganese-cerium solid solution catalyst by utilizing a template method and a vacuum drying method. The preparation process is simple, the raw materials are easy to obtain, and the method can effectively utilize the template agent to enable the manganese-cerium solid solution to form a specific structure and increase the specific surface area of the manganese-cerium solid solution; can also improve the uniformity of the surface and even internal distribution of two transition metal oxides, form more Mn-Ce-O bonds, and make chlorine species adopt HCl and Cl2Is removed in the form of (1). Catalyst prepared by the inventionThe oxidant can catalyze ozone to oxidize CVOCs into CO at room temperature2、H2O、HCl、Cl2And the like, has excellent low-temperature redox activity, chlorine poisoning resistance and higher CO2And (4) selectivity.
Disclosure of Invention
The invention discloses a preparation method of a catalyst for catalyzing ozone to oxidize chlorine-containing volatile organic compounds. Aims to degrade CVOCs into CO by improving the deep oxidation of ozone to the CVOCs and the chlorine poisoning resistance of the catalyst2、H2O、HCl、Cl2And the like.
The preparation method of the manganese-cerium solid solution catalyst comprises the following steps:
(1) adding manganese salt and cerium salt into pure water, and stirring and dissolving to obtain manganese-cerium salt mixed solution;
(2) soaking the mesoporous silicon template agent in a manganese-cerium salt mixed solution, and then centrifuging to remove a soaking solution;
(3) drying the impregnated product obtained in the step (2) in vacuum and then calcining to obtain a manganese-cerium solid solution precursor;
(4) adopting an alkali solution to dip the manganese-cerium solid solution precursor obtained in the step (3), dissolving a template agent in the manganese-cerium solid solution precursor, filtering, and washing a filter cake to be neutral by pure water;
(5) and drying the filter cake in vacuum to obtain the mesoporous manganese-cerium solid solution catalyst.
In the preparation method, the manganese salt in the step (1) is one or a mixture of more of manganese chloride, manganese sulfate, manganese acetate and manganese nitrate; the cerium salt is one or a mixture of cerium chloride, cerium sulfate and cerium nitrate; the molar ratio of manganese to cerium is from 1:4 to 4: 1.
In the preparation method, the template agent in the step (2) is one or a mixture of more of SBA-15, SBA-16, KIT-6 and MCM-41, and the mass ratio of the template agent to the transition metal salt is 5:4 to 5: 1; the dipping condition is magnetic stirring for 4-10 hours.
In the step (3), the vacuum drying temperature is 60-100 ℃, and the time is 5-14 hours; the calcination temperature is 200-600 ℃ and the calcination time is 4-10 hours.
The alkali solution in the step (4) of the preparation method is one or two mixed solutions of sodium hydroxide and potassium hydroxide, and the concentration is 1-3 mol/L; the dipping condition is magnetic stirring for 4-10 hours.
In the step (5), the vacuum drying temperature is 60-100 ℃, and the time is 5-14 hours.
Drawings
Fig. 1 is a flowchart of a method for preparing a mesoporous manganese-cerium solid solution catalyst according to an embodiment of the present invention;
FIG. 2 is a transmission electron micrograph of a catalyst made according to an embodiment of the invention.
Detailed Description
Example 1: 20g of 50% manganese nitrate solution and 12g of cerium nitrate hexahydrate were dissolved in 130ml of pure water by thoroughly stirring for 30 min. Adding 6g of SBA-15 template agent into the manganese-cerium salt mixed solution, magnetically stirring and soaking at room temperature for 10 hours, and centrifuging to obtain a white solid. And (3) putting the white solid in a vacuum drying oven, drying for 12 hours at the temperature of 60 ℃, and then calcining for 4 hours in a muffle furnace at the temperature of 400 ℃ to obtain a brown manganese-cerium solid solution precursor. Dissolving the manganese-cerium solid solution precursor in 150ml of 2mol/L sodium hydroxide solution, stirring, soaking for 6 hours, filtering, washing a filter cake to pH 7 with pure water, and drying the filter cake in a vacuum drying oven at 60 ℃ for 12 hours to obtain the mesoporous manganese-cerium solid solution catalyst for catalyzing ozone oxidation CVOCs. Evaluation of catalyst Performance: the mass of the catalyst was 0.5g, the gas flow was 125ml/min, and the inlet concentration of dichloroethane was 150mg/m3The ozone concentration at the inlet is 1000mg/m3When the purification rate of dichloroethane is 85%, the selectivity of carbon dioxide is 70%, no ozone is detected at the outlet, the operation lasts for 15 hours, and the performance of the catalyst is stable.
Example 2: 10g of 50% manganese nitrate solution and 24g of cerium nitrate hexahydrate were dissolved in 130ml of pure water by thoroughly stirring for 30 min. Soaking 6g of SBA-15 template agent in the manganese-cerium salt mixed solution, magnetically stirring and soaking at room temperature for 10 hours, and centrifuging to obtain a white solid. The white solid was dried in a vacuum oven at 60 ℃ for 12 hours and then calcined in a muffle furnace at 400 ℃ for 4 hours to give a brown colorThe precursor of manganese-cerium solid solution. Dissolving the manganese-cerium solid solution precursor in 150ml of 2mol/L sodium hydroxide solution, stirring, soaking for 6 hours, filtering, washing a filter cake to pH 7 with pure water, and drying the filter cake in a vacuum drying oven at 60 ℃ for 12 hours to obtain the mesoporous manganese-cerium solid solution catalyst for catalyzing ozone oxidation CVOCs. Evaluation of catalyst Performance: the mass of the catalyst was 0.5g, the gas flow was 125ml/min, and the inlet concentration of dichloroethane was 150mg/m3The ozone concentration at the inlet is 1000mg/m3The measured dichloroethane purification rate is 96%, the carbon dioxide selectivity is 82%, no ozone is detected at the outlet, the operation is carried out for 15 hours, and the catalyst performance is stable.

Claims (6)

1. A preparation method of a catalyst for catalyzing ozone oxidation of chlorine-containing volatile organic compounds is characterized in that the catalyst is of a mesoporous manganese-cerium solid solution structure and is prepared by adopting a template method-vacuum drying method, and the preparation method comprises the following steps:
(1) adding manganese salt and cerium salt into pure water, and stirring and dissolving to obtain manganese-cerium salt mixed solution;
(2) soaking the mesoporous silicon template agent in a manganese-cerium salt mixed solution, and then centrifuging to remove a soaking solution;
(3) drying the impregnated product obtained in the step (2) in vacuum and then calcining to obtain a manganese-cerium solid solution precursor;
(4) adopting an alkali solution to dip the manganese-cerium solid solution precursor obtained in the step (3), dissolving a template agent in the manganese-cerium solid solution precursor, filtering, and washing a filter cake to be neutral by pure water;
(5) and drying the filter cake in vacuum to obtain the mesoporous manganese-cerium solid solution catalyst.
2. The preparation method of the catalyst according to claim 1, wherein the manganese salt in the step (1) is one or more of manganese chloride, manganese sulfate, manganese acetate and manganese nitrate; the cerium salt is one or a mixture of cerium chloride, cerium sulfate and cerium nitrate; the molar ratio of manganese to cerium is from 1:4 to 4: 1.
3. The method for preparing the catalyst according to claim 1, wherein the template in the step (2) is one or more of SBA-15, SBA-16, KIT-6 and MCM-41, and the mass ratio of the template to the transition metal salt is 5:4 to 5: 1; the dipping condition is magnetic stirring for 4-10 hours.
4. The method for preparing a catalyst according to claim 1, wherein the vacuum drying temperature in the step (3) is 60 to 100 ℃ for 5 to 14 hours; the calcination temperature is 200-600 ℃ and the calcination time is 4-10 hours.
5. The method for preparing the catalyst according to claim 1, wherein the alkali solution in the step (4) is one or a mixture of sodium hydroxide and potassium hydroxide, and the concentration is 1-3 mol/L; the dipping condition is magnetic stirring for 4-10 hours.
6. The method for preparing a catalyst according to claim 1, wherein the vacuum drying temperature in the step (5) is 60 to 100 ℃ for 5 to 14 hours.
CN202111056682.4A 2021-09-09 2021-09-09 Preparation method of catalyst for catalyzing ozone to oxidize chlorine-containing volatile organic compounds Pending CN113648992A (en)

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Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102218312A (en) * 2011-04-13 2011-10-19 北京航空航天大学 Manganese-cerium composite oxide catalyst for removing medium-low concentration benzene series in air and preparation method thereof
CN102941084A (en) * 2012-11-22 2013-02-27 大连理工大学 Method for preparing double-component metallic oxide catalytic ozonation catalyst
CN109107567A (en) * 2018-09-25 2019-01-01 南京信息工程大学 A kind of M-MnOx-CeO2Catalyst and its application
CN111774069A (en) * 2020-07-08 2020-10-16 上海纳米技术及应用国家工程研究中心有限公司 Manganese-cerium solid solution loaded cobalt catalyst for catalyzing and oxidizing volatile organic compounds by ozone and preparation method and application thereof
CN112495371A (en) * 2019-09-16 2021-03-16 北京化工大学 Preparation method of catalyst for catalyzing ozone to oxidize volatile organic compounds
CN112547047A (en) * 2019-09-25 2021-03-26 北京化工大学 Method for preparing nano manganese dioxide catalyst by freeze drying method

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102218312A (en) * 2011-04-13 2011-10-19 北京航空航天大学 Manganese-cerium composite oxide catalyst for removing medium-low concentration benzene series in air and preparation method thereof
CN102941084A (en) * 2012-11-22 2013-02-27 大连理工大学 Method for preparing double-component metallic oxide catalytic ozonation catalyst
CN109107567A (en) * 2018-09-25 2019-01-01 南京信息工程大学 A kind of M-MnOx-CeO2Catalyst and its application
CN112495371A (en) * 2019-09-16 2021-03-16 北京化工大学 Preparation method of catalyst for catalyzing ozone to oxidize volatile organic compounds
CN112547047A (en) * 2019-09-25 2021-03-26 北京化工大学 Method for preparing nano manganese dioxide catalyst by freeze drying method
CN111774069A (en) * 2020-07-08 2020-10-16 上海纳米技术及应用国家工程研究中心有限公司 Manganese-cerium solid solution loaded cobalt catalyst for catalyzing and oxidizing volatile organic compounds by ozone and preparation method and application thereof

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* Cited by examiner, † Cited by third party
Title
曾小岚等: "Mn的氧化价态对Mn/γ-Al2O3催化剂催化臭氧氧化气相低浓度甲苯的影响", 《环境工程学报》 *

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Application publication date: 20211116