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CN113171774A - Alkali metal poisoning resistant VOCs catalytic combustion catalyst and preparation method thereof - Google Patents

Alkali metal poisoning resistant VOCs catalytic combustion catalyst and preparation method thereof Download PDF

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Publication number
CN113171774A
CN113171774A CN202110455289.6A CN202110455289A CN113171774A CN 113171774 A CN113171774 A CN 113171774A CN 202110455289 A CN202110455289 A CN 202110455289A CN 113171774 A CN113171774 A CN 113171774A
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catalyst
alkali metal
mof
sample
catalytic combustion
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沈伟
查凯文
黄镇
徐华龙
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Fudan 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
    • B01J23/70Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
    • B01J23/74Iron group metals
    • B01J23/745Iron
    • 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
    • B01J35/30Catalysts, in general, characterised by their form or physical properties characterised by their physical properties
    • B01J35/396Distribution of the active metal ingredient
    • B01J35/398Egg yolk like
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G7/00Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
    • F23G7/06Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases
    • F23G7/07Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases in which combustion takes place in the presence of catalytic material
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2209/00Specific waste
    • F23G2209/14Gaseous waste or fumes

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Abstract

The invention belongs to the technical field of chemical catalysts, and particularly relates to an alkali metal poisoning resistant VOCs catalytic combustion catalyst and a preparation method thereof. The catalyst of the invention is formed by encapsulating cobalt oxide with catalytic activity in silicon dioxide, and the shell layer of the silicon dioxide provides a confinement effect and a protection function. According to the invention, a nano-casting method of MOF is adopted, siloxane precursor salt is filled into the pore channels of the MOF, the hydrolysis of the siloxane precursor salt is promoted by using an inert gas bubbling method, and a one-dimensional cowpea-shaped catalyst is prepared through carbonization and calcination; the silica shell enables the cobalt oxide with high loading capacity to be well dispersed, has smaller particle size, effectively improves the catalytic activity of the catalyst, enables the cobalt oxide to be free from the influence of alkali metal, and improves the alkali metal poisoning resistance. The catalyst has high activity, good stability and strong alkali metal poisoning resistance, and completely meets the actual requirements.

Description

Alkali metal poisoning resistant VOCs catalytic combustion catalyst and preparation method thereof
Technical Field
The invention belongs to the technical field of chemical catalysts, and particularly relates to an alkali metal poisoning resistant VOCs catalytic combustion catalyst and a preparation method thereof.
Background
Volatile Organic Compounds (VOCs) are a major atmospheric pollutant. The VOCs discharged from automobile exhaust and industrial production process not only cause serious pollution to the environment, but also seriously threaten the health of human beings. Over the past several decades, catalytic combustion processes have become one of the most effective and most widely used techniques for the abatement of various VOCs pollutants. In the VOCs catalytic combustion catalyst, the noble metal-based catalyst has stronger oxidation performance and shows excellent VOCs conversion capability. But the disadvantages of high price, easy poisoning, easy sintering and the like limit the large-scale application of the material. Therefore, it is necessary to develop a high-efficiency catalyst for catalytic combustion of VOCs without noble metals. Among many transition metal oxide catalysts, cobalt-based oxide catalysts have received much attention from researchers because of their environmental friendliness, high cost performance, and good catalytic performance in various redox reactions.
In the practical application process, alkali metals exist in fly ash of coal-fired power plants and diesel vehicles, which can cause serious catalyst poisoning. Alkali metals, a common material from biomass coal and fuel/petroleum additives, are a significant problem that cannot be ignored in the application of VOCs catalytic combustion catalysts (e.g., cobalt-based catalysts). In addition to plugging catalyst channels, alkali metals can also affect adsorption-desorption behavior and normal redox cycling by changing the acid-base properties of the catalyst and binding with active components. Pu-Xian Gao et al (W. Tang, J. Weng, X. Lu, L. Wen, A. Subramanian, C. -Y. Nam, P. -X. Gao. appl. Catl. B: Environ., 2019, 256, 117859-3O4The poisoning effect of alkali metals during the oxidation of propane on the catalyst. They found that alkali metals can reduce the mobility of oxygen by a "blocking effect". In addition, as the reaction proceeds, the alkali metal forms a stable surface carbonate species, thereby sequestering the CO2Desorption of the product had a significant effect. Therefore, after the alkali metal poisoning, the catalyst activity is drastically decreased. Therefore, it is important to improve the alkali metal poisoning resistance of VOCs catalytic combustion catalysts (e.g., cobalt oxide catalysts), but the methods so farThe method yield is not obvious, and the requirement of alkali metal poisoning resistance in the practical application of the VOCs catalytic combustion catalyst cannot be completely met.
Disclosure of Invention
The invention aims to provide a VOCs catalytic combustion catalyst with high activity, good stability and strong alkali metal poisoning resistance and a preparation method thereof aiming at the defects of the existing VOCs catalytic combustion catalyst.
The alkali metal poisoning resistant VOCs catalytic combustion catalyst provided by the invention is of a one-dimensional cowpea-shaped structure, and is formed by encapsulating cobalt oxide with catalytic activity in silicon dioxide, and a silicon dioxide shell layer provides a confinement effect and a protection function. The limiting function can ensure that the cobalt oxide with high load capacity is well dispersed, has smaller particle size and effectively improves the catalytic activity of the catalyst; the protection effect can prevent the cobalt oxide from being influenced by alkali metal, and the alkali metal poisoning resistance is obviously improved.
The molar ratio of the cobalt oxide to the silicon dioxide in the catalyst is 0.2-0.35.
The invention also provides a preparation method of the alkali metal poisoning resistant VOCs catalytic combustion catalyst, siloxane precursor salt is filled into the pore channel of the MOF by adopting a nano-casting method of the MOF, the hydrolysis of the MOF is promoted by utilizing an inert gas bubbling method, and the one-dimensional cowpea-shaped catalyst is prepared by carbonization and calcination; the method comprises the following specific steps:
(1) immersing a certain amount of MOF sample into a certain amount of siloxane precursor salt, and keeping the MOF sample at the temperature of 50-70 ℃ for 12-15 hours; then washing the wet sample for several times by using methanol to remove redundant siloxane precursor salt, and placing the sample in a quartz tube after washing;
(2) bubbling 10-30 mL/min inert gas flow in 0.01-0.1 mol/L solution for hydrolysis, and inducing hydrolysis of siloxane precursor for 24-48 h at 50-70 ℃ by using generated wet gas flow;
(3) after drying for 5-12 h, carbonizing the sample at 600-700 ℃ for 3-5 h in an inert gas flow environment of 150-200 mL/min; and calcining the carbonized sample in an air atmosphere at 500-600 ℃ for 2-5 h to obtain the alkali metal poisoning resistant VOCs catalytic combustion catalyst.
In the step (1), the MOF is MOF of Co metal centers such as Co-CAT-1, Co-ZIF-67 or Co-MOF-74.
In the step (1), the siloxane precursor salt is Tetramethylsiloxane (TMOS) or Tetraethylsiloxane (TEOS).
In the step (2), the inert gas is nitrogen or helium, and the like.
The solution is deionized water, or acid solution or alkali solution, such as HCl.
In the preparation process, the time for immersing the MOF in the siloxane precursor salt is different, the amount of the precursor salt entering the MOF pore channel is different, and the catalytic activity of the finally obtained catalyst is greatly changed.
In the preparation process, the different concentrations of the HCl solution and the different time for inducing the hydrolysis of the siloxane precursor can cause the great change of the shape structure of the finally obtained catalyst, thereby causing the great change of the catalytic activity and the alkali metal poisoning resistance of the catalyst.
In the preparation process, the morphology and the structure of the finally obtained catalyst are greatly changed due to different carbonization temperatures and different carbonization times, so that the catalytic activity and the alkali metal poisoning resistance of the catalyst are greatly changed.
In the preparation process, the concentration of the solution HC is not too high during bubbling hydrolysis, and is kept between 0.01 and 0.1 mol/L. The hydrolysis temperature is not too low or too high and is kept between 50 and 70 ℃; the hydrolysis time is not suitable to be too short or too long and is kept between 24 and 48 hours; otherwise, the framework structure of the MOF is damaged, so that the active components of the catalyst are not dispersed well, and the activity and alkali metal poisoning resistance of the catalyst are affected.
The temperature rising rate of the carbonization and calcination is 1-3 ℃/min, the carbonization time of the sample under the inert gas flow is 3-5 h, the calcination time of the sample under the air atmosphere is 2-5 h, if the temperature rising rate and the temperature rising time exceed the range, the catalyst can be sintered, so that the structure and the surface appearance of the catalyst are damaged, the specific surface area of the catalyst is reduced, and the catalytic activity and the alkali metal poisoning resistance of the calcined catalyst are not facilitated.
Compared with the prior art, the invention has the following advantages:
(1) the catalyst has a special shape structure, and the outer silicon dioxide shell layer provides a complex diffusion migration path for alkali metal, so that the alkali metal is difficult to contact with an active site, and the alkali metal poisoning resistance of the catalyst is obviously improved.
(2) The catalyst has good confinement effect, and can still realize good dispersion of the active component under the condition of high active component loading capacity, so as to obtain nanoparticles with relatively small particle size.
(3) Compared with the traditional supported catalyst, the catalyst has the advantages of high catalytic activity, strong alkali metal poisoning resistance, good stability and the like, the preparation process is relatively simple and stable, and the catalyst can be applied to VOCs catalytic combustion scenes under the condition of alkali metals on a large scale.
Drawings
Fig. 1 is a graph showing the comparison of propane conversion efficiency between the one-dimensional cowpea-like silica encapsulated cobaltosic oxide catalyst obtained in example 1 of the present invention before and after potassium poisoning and the one-dimensional cowpea-like silica supported cobaltosic oxide catalyst before and after potassium poisoning.
Detailed Description
In order to more clearly illustrate the present invention, the following examples are given, but the present invention is not limited to the scope of the examples.
Example 1:
a0.8 g sample of prepared Co-CAT-1 was immersed in 8 mL of Tetramethylsiloxane (TMOS) and held at 60 ℃ for 12 h. The wetted sample was then washed several times with methanol to remove excess TMOS, and after washing was complete the sample was placed in a quartz tube. Using 15 mL/min N2The gas stream was bubbled through a 0.1M HCl solution, and the resulting humidified gas stream induced hydrolysis of TMOS at 50 ℃ for 30 h. After drying for 5 h, the sample was at 150 mL/min N2Carbonizing at 600 deg.C for 4 h in gas flow environment. The obtained sample was calcined at 500 ℃ for 2 hours in an air atmosphere (heating rate 1 ℃/min). Finally obtaining the one-dimensional cowpea-shaped silicon dioxide packaged cobaltosic oxide catalystAn oxidizing agent.
The catalysts described above were tested for catalytic activity and resistance to alkali metal poisoning: taking 0.3 g of the prepared catalyst, putting the catalyst into a fixed bed reactor for activity test, and simulating the composition of reaction gas as follows: 0.2 vol% propane, 2.5 vol% oxygen and nitrogen balance the carrier gas. The total flow rate of the gas is 100 mL/min, and the corresponding test space velocity (GHSV) is 25000 h-1. The catalyst can maintain over 95 percent of propane conversion rate at the reaction temperature of over 240 ℃. After 1 wt% potassium poisoning, the catalyst can maintain a propane conversion of 95% or more at a reaction temperature of 270 ℃ or more.
Example 2:
a0.8 g sample of prepared Co-CAT-1 was immersed in 8 mL of Tetramethylsiloxane (TMOS) and held at 60 ℃ for 12 h. The wetted sample was then washed several times with methanol to remove excess TMOS, and after washing was complete the sample was placed in a quartz tube. Using 15 mL/min N2The gas stream was bubbled through deionized water, and the resulting humidified gas stream induced hydrolysis of TMOS for 30 h at 60 ℃. After drying for 5 h, the sample was at 150 mL/min N2Carbonizing at 600 deg.C for 4 h in gas flow environment. The obtained sample was calcined at 500 ℃ for 2 hours in an air atmosphere (heating rate 1 ℃/min). Finally obtaining the one-dimensional cowpea-shaped silicon dioxide packaged cobaltosic oxide catalyst.
The catalysts described above were tested for catalytic activity and resistance to alkali metal poisoning: taking 0.3 g of the prepared catalyst, putting the catalyst into a fixed bed reactor for activity test, and simulating the composition of reaction gas as follows: 0.2 vol% propane, 2.5 vol% oxygen and nitrogen balance the carrier gas. The total flow rate of the gas is 100 mL/min, and the corresponding test space velocity (GHSV) is 25000 h-1. The catalyst can maintain over 95 percent of propane conversion rate at the reaction temperature of over 250 ℃. After 1 wt% potassium poisoning, the catalyst can maintain a propane conversion of 95% or more at a reaction temperature of 285 ℃ or more.
Example 3:
a0.8 g sample of prepared Co-CAT-1 was immersed in 8 mL of Tetramethylsiloxane (TMOS) and held at 60 ℃ for 12 h. The wet sample was then washed several times with methanolExcess TMOS was removed and after washing the sample was placed in a quartz tube. Using 15 mL/min N2The gas stream was bubbled through a 0.05M HCl solution, and the resulting humidified gas stream induced hydrolysis of TMOS at 50 ℃ for 30 h. After drying for 5 h, the sample was at 150 mL/min N2Carbonizing at 600 deg.C for 3 h in gas flow environment. The obtained sample was calcined at 500 ℃ for 2 hours in an air atmosphere (heating rate 1 ℃/min). Finally obtaining the one-dimensional cowpea-shaped silicon dioxide packaged cobaltosic oxide catalyst.
The catalysts described above were tested for catalytic activity and resistance to alkali metal poisoning: taking 0.3 g of the prepared catalyst, putting the catalyst into a fixed bed reactor for activity test, and simulating the composition of reaction gas as follows: 0.2 vol% propane, 2.5 vol% oxygen and nitrogen balance the carrier gas. The total flow rate of the gas is 100 mL/min, and the corresponding test space velocity (GHSV) is 25000 h-1. The catalyst can maintain over 95 percent of propane conversion rate at the reaction temperature of over 245 ℃. After 1 wt% potassium poisoning, the catalyst can maintain a propane conversion of 95% or more at a reaction temperature of 275 ℃ or more.

Claims (9)

1. The catalyst is characterized by being of a one-dimensional cowpea-shaped structure, and formed by encapsulating cobalt oxide with catalytic activity in silicon dioxide, wherein a silicon dioxide shell layer provides a confinement effect and a protection function.
2. The VOCs catalytic combustion catalyst of claim 1, wherein the molar ratio of cobalt oxide to silica is in the range of 0.2 to 0.35.
3. A method for preparing a catalyst for catalytic combustion of VOCs according to claim 1 or 2, comprising the steps of:
(1) immersing an MOF sample into siloxane precursor salt, and keeping the MOF sample at the temperature of 50-70 ℃ for 12-15 h; then washing the wet sample for several times by using methanol to remove redundant siloxane precursor salt, and placing the sample in a quartz tube after washing;
(2) bubbling 10-30 mL/min inert gas flow in 0.01-0.1 mol/L solution for hydrolysis, and inducing TMOS (tetramethylammonium sulfate) to hydrolyze for 24-48 h at 50-70 ℃ by using generated humid gas flow;
(3) drying the hydrolyzed product for 5-12 h, then placing the product in an inert gas flow environment of 150-200 mL/min, and carbonizing the product for 3-5 h at 600-700 ℃; and calcining the carbonized sample in an air atmosphere at 500-600 ℃ for 2-5 h to obtain the alkali metal poisoning resistant VOCs catalytic combustion catalyst.
4. The method according to claim 3, wherein the MOF in step (1) is a Co-metal-centered MOF selected from the group consisting of Co-CAT-1, Co-ZIF-67 and Co-MOF-74.
5. The method according to claim 3, wherein the siloxane precursor salt in step (1) is Tetramethylsiloxane (TMOS) or Tetraethylsiloxane (TEOS).
6. The method according to claim 3, wherein the inert gas in the step (2) is nitrogen or helium.
7. The method according to claim 3, wherein the solution in the step (2) is deionized water, or an acid solution or an alkali solution.
8. The method according to claim 3, wherein the solution in the bubble hydrolysis in the step (2) is HCl with a concentration of 0.01 to 0.1 mol/L.
9. The method according to claim 3, wherein in the step (3), the temperature increase rate is 1 to 3 ℃/min during the carbonization and calcination.
CN202110455289.6A 2021-04-26 2021-04-26 Alkali metal poisoning resistant VOCs catalytic combustion catalyst and preparation method thereof Pending CN113171774A (en)

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CN113270599A (en) * 2021-05-25 2021-08-17 西安交通大学 Electrode catalyst, composite electrode and preparation process thereof
CN116422363A (en) * 2022-12-06 2023-07-14 有研资源环境技术研究院(北京)有限公司 Preparation method of hydrophobic Pd-based catalyst and hydrophobic Pd-based catalyst

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Publication number Priority date Publication date Assignee Title
CN113270599A (en) * 2021-05-25 2021-08-17 西安交通大学 Electrode catalyst, composite electrode and preparation process thereof
CN113270599B (en) * 2021-05-25 2022-07-12 西安交通大学 Electrode catalyst, composite electrode and preparation process thereof
CN116422363A (en) * 2022-12-06 2023-07-14 有研资源环境技术研究院(北京)有限公司 Preparation method of hydrophobic Pd-based catalyst and hydrophobic Pd-based catalyst

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