CN110302800B - Synthesis process of catalyst activated carbon composite material for decomposing dioxin - Google Patents

Synthesis process of catalyst activated carbon composite material for decomposing dioxin Download PDF

Info

Publication number
CN110302800B
CN110302800B CN201910360394.4A CN201910360394A CN110302800B CN 110302800 B CN110302800 B CN 110302800B CN 201910360394 A CN201910360394 A CN 201910360394A CN 110302800 B CN110302800 B CN 110302800B
Authority
CN
China
Prior art keywords
product
activated carbon
catalyst
stirring
carbon composite
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.)
Active
Application number
CN201910360394.4A
Other languages
Chinese (zh)
Other versions
CN110302800A (en
Inventor
徐卫星
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.)
Hangzhou Xingyu Carbon Technology Green Co ltd
Original Assignee
Hangzhou Xingyu Carbon Technology Green Co ltd
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 Hangzhou Xingyu Carbon Technology Green Co ltd filed Critical Hangzhou Xingyu Carbon Technology Green Co ltd
Priority to CN201910360394.4A priority Critical patent/CN110302800B/en
Publication of CN110302800A publication Critical patent/CN110302800A/en
Application granted granted Critical
Publication of CN110302800B publication Critical patent/CN110302800B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • 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
    • B01D53/8659Removing halogens or halogen compounds
    • B01D53/8662Organic halogen compounds
    • 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
    • B01J23/89Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with noble metals
    • B01J23/8906Iron and noble metals
    • B01J35/61
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2257/00Components to be removed
    • B01D2257/20Halogens or halogen compounds
    • B01D2257/206Organic halogen compounds
    • B01D2257/2064Chlorine

Abstract

The invention discloses a synthesis process of a catalyst activated carbon composite material for decomposing dioxin, which comprises the following steps of A, crushing activated carbon, and sieving to obtain a product A; B. putting the product A into a container filled with concentrated sulfuric acid, introducing nitrogen into the bottom of the container, soaking, washing and drying to obtain a product B; C. adding alcohol and deionized water into product B and metal salt, and stirring to obtain product C; D. adding complexing agent into product C, ultrasonic penetrating, stirring, adjusting pH, and stirring to obtain product D; E. drying product D to obtain gel to obtain product E; F. under the protection of hydrogen, sintering the product E to obtain a product F; G. and removing impurities from the product F, washing and drying to obtain a finished product. According to the invention, the specific surface area of the modified activated carbon is increased, the catalyst is uniformly distributed in the activated carbon, the finished product is not easy to form pores and crack, the catalyst and the activated carbon have compact structures, the removal rate of the finished product on dioxin is higher and stable, and the service life of the finished product is prolonged.

Description

Synthesis process of catalyst activated carbon composite material for decomposing dioxin
Technical Field
The invention relates to the technical field of catalyst composite materials for decomposing dioxin, in particular to a synthesis process of a catalyst active carbon composite material for decomposing dioxin.
Background
In 22 days 5 and 2001, stockholm sweden, more than 90 countries and regional representatives including china have officially signed the stockholm convention on persistent organic pollutants, which aims to reduce and eliminate persistent organic matters in the environment and protect human health and the environment from the harm of persistent organic pollutants, and the first 12 persistent organic pollutants represented by polyazabiphenyl, dioxin and the like become key targets of global chemical pollution control. China is the first contracting country of the "stockholm convention", and the convention formally takes effect on China in 2004 in 11 months and 11 days. According to the requirements of the convention, China compiles and completes the implementation plan that China fulfills < Stockholm convention about persistent organic pollutants > in 2007 as a general guide for the performance work of China. In the last 10 years, along with the acceleration of urbanization, the production amount of municipal domestic waste in China is greatly increased. According to the data provided by the national environmental sanitation society, the annual domestic garbage production of China is 440kg, the annual domestic garbage production of China reaches 1.5 hundred million t, the annual urban garbage production of China increases at the speed of 8-10%, the national annual garbage stock exceeds 60 hundred million t, and about 2/3 cities fall into the garbage surrounding city. Along with the rapid development of domestic waste incineration plants and waste incineration treatment capacity, the problem of dioxin discharged by domestic waste incineration plants also becomes the focus of public attention and debate. In provinces and markets with high popularization rate of waste incineration, such as Guangdong, Zhejiang, Jiangsu, Beijing and the like, public gathering events against waste incineration often occur. The dioxin emission control gradually becomes the key point in the waste incineration pollution control in China.
The traditional dioxin decomposition catalyst has limited improvement on the decomposition efficiency of dioxin and has higher requirements on reaction conditions such as temperature and the like. In recent years, the application of the activated carbon supported metal ion catalyst in degrading organic pollutants is increasing. The common preparation method of the active carbon-supported metal ion catalyst comprises the steps of firstly modifying active carbon, then fixedly supporting the metal ion catalyst in the modified active carbon by a sol-gel method, drying and sintering to obtain the catalyst-activated carbon composite material. In the preparation process of the existing catalyst active carbon composite material, the specific surface area of the modified active carbon is not large enough, the catalyst is not uniformly dispersed in the active carbon during sol-gel reaction, aggregates are easily generated, and the catalyst is easy to crack during drying, so that the performance of a finished product is not uniform, the removal rate of organic pollutants is not high enough and is not stable, and the service life of the finished product is shortened; during the sol-gel reaction, the connection between the catalyst and the activated carbon is not tight enough, pores are easy to form in the finished product prepared by sintering, and the service life of the finished product is shortened; when the gel is sintered, the temperature rise speed is improperly controlled, small air holes in the sol cannot be well eliminated, so that a sintered product is not compact enough and is easy to crack, and the service life of a finished product is shortened. Therefore, in the preparation of the existing catalyst activated carbon composite material, the specific surface area of the modified activated carbon is not large enough, the catalyst is unevenly distributed in the activated carbon, the finished product is easy to form pores and crack, the structure of the catalyst and the activated carbon is not compact enough, so that the removal rate of the finished product to organic pollutants is not high enough and unstable, and the service life of the finished product is short.
Disclosure of Invention
The invention aims to provide a synthesis process of a catalyst activated carbon composite material for decomposing dioxin. According to the invention, the specific surface area of the modified activated carbon is increased, the catalyst is uniformly distributed in the activated carbon, the finished product is not easy to form pores and crack, the catalyst and the activated carbon have compact structures, the removal rate of the finished product on dioxin is higher and stable, and the service life of the finished product is prolonged.
The technical scheme of the invention is as follows: the synthesis process of the catalyst-activated carbon composite material for decomposing dioxin comprises the following steps,
A. crushing the activated carbon, and sieving the crushed activated carbon with a 200-mesh and 300-mesh sieve to obtain a product A;
B. putting the product A into a container filled with concentrated sulfuric acid, introducing nitrogen into the bottom of the container, soaking for 2-3h, washing until the pH value is 6-7, and drying to obtain a product B;
C. taking 3-9 parts of the product B and 3-9 parts of metal salt, adding a mixed solution of 10-30 parts of alcohol and 30-60 parts of deionized water, and stirring to obtain a product C;
D. adding 4-10 parts of complexing agent into product C, performing ultrasonic penetration at 70-90 deg.C, stirring, adding dropwise ammonia water to adjust pH to 6.5-7, and stirring to obtain product D;
E. drying product D to obtain gel to obtain product E;
F. under the protection of hydrogen, sintering the E product at the temperature of 400-800 ℃ for 4-6h at the temperature rising speed of 2-5 ℃/min to obtain an F product;
G. and separating and removing impurities from the F product, washing and drying to obtain a finished product of the catalyst active carbon composite material.
In the synthesis process of the catalyst-activated carbon composite material for decomposing dioxin, in the step B, the flow rate of the nitrogen is 30-80 mL/min.
In the synthesis process of the catalyst activated carbon composite material for decomposing dioxin, in the step C, the metal salt is AgNO3、Mn(NO3)2And Fe (NO)3)3AgNO1-3 parts, Mn (NO)3)21-3 parts of Fe (NO)3)31-3 parts.
In the synthesis process of the catalyst-activated carbon composite material for decomposing dioxin, in the step C, the stirring time is 0.5-1.5h, the stirring temperature is 70-90 ℃, and the stirring speed is 400-450 rpm.
In the synthesis process of the catalyst-activated carbon composite material for decomposing dioxin, in the step D, the complexing agent is citric acid and ethylene glycol, 3.95-9.8 parts of citric acid and 0.05-0.2 part of ethylene glycol.
In the synthesis process of the catalyst activated carbon composite material for decomposing dioxin, in the step D, the ultrasonic penetration time is 5-15min, the ultrasonic frequency is 10-50KHZ, and the ultrasonic power density is 0.3-1KW/m3
In the synthesis process of the catalyst activated carbon composite material for decomposing dioxin, the step D is to add a complexing agent into the product C, perform ultrasonic penetration for 5 to 15min at a constant temperature of between 70 and 90 ℃, wherein the ultrasonic frequency is between 10 and 50KHZ, and the ultrasonic power density is between 0.3 and 1KW/m3Stirring for 1.5-2.5h at 380-420rpm, adding ammonia water dropwise to adjust pH to 6.5-7, and stirring to obtain D product.
In the synthesis process of the catalyst-activated carbon composite material for decomposing dioxin, the step E is to dry the product D in a forced air drying oven at 70-90 ℃ for 5-7 hours to obtain the product E.
In the synthesis process of the catalyst activated carbon composite material for decomposing dioxin, the step F is to sinter the product E at the temperature of 400-800 ℃ for 3-4h and at the temperature of 700-800 ℃ for 1-2h under the protection of hydrogen to obtain the product F, wherein the heating rate is 2-5 ℃/min.
In the synthesis process of the catalyst-activated carbon composite for decomposing dioxin, in the step G, the separation is gravity separation.
Compared with the prior art, the method comprises the steps of crushing the activated carbon, sieving the crushed activated carbon by a 200-mesh and 300-mesh sieve, soaking the crushed activated carbon in concentrated sulfuric acid under the condition of introducing nitrogen, and introducing the nitrogen to ensure that the activated carbon is fully contacted with the concentrated sulfuric acid, so that the specific surface area of the modified activated carbon is greatly increased, the surface area for adsorbing dioxin is large enough, and enough pores can be used for immobilizing the metal ion catalyst; the proportion of the product B, the metal salt and the complexing agent is proper, metal ions can be fully immobilized in the modified activated carbon under the conditions of reaction temperature and pH value, the sol performance is stable, the prepared catalyst has a remarkable catalytic effect, the catalyst is used for removing dioxin in waste incineration tail gas, the removal rate is more than 99.6 percent, and the proportion of deionized water and alcohol is proper, so that the vapor pressure is not too high when the sol is dried, and the sol is not cracked when the sol is dried; in the step D of the invention, the metal ions are distributed more uniformly by ultrasonic penetration, so that the metal ions are fully and fixedly loaded in the activated carbon, the generation of aggregates is avoided, the cracking probability of the sol during drying and sintering is reduced, the finished product has uniform texture, and the removal rate of the finished product to dioxin is higher and more stable; in the step F of the invention, the heating speed is proper, and small air holes in the product E can be eliminated slowly, so that the finished product is more compact and does not crack or form fine holes. According to the invention, the specific surface area of the modified activated carbon is increased, the catalyst is uniformly distributed in the activated carbon, the finished product is not easy to form pores and crack, the catalyst and the activated carbon have compact structures, the removal rate of the finished product on dioxin is higher and stable, and the service life of the finished product is prolonged.
Detailed Description
The present invention is further illustrated by the following examples, which are not to be construed as limiting the invention.
Example 1.
The synthesis process of the catalyst-activated carbon composite material for decomposing dioxin comprises the following steps,
A. crushing activated carbon (the activated carbon is washed and dried by deionized water), and sieving with a 200-mesh sieve to obtain a product A;
B. putting the product A into a container filled with concentrated sulfuric acid, introducing nitrogen into the bottom of the container, soaking for 3h at the flow rate of 30mL/min, washing until the pH value is 6.5, and drying to obtain a product B;
C. taking 6 parts of B product and 1 part of AgNO31 part of Mn (NO)3)2And 2 parts of Fe (NO)3)3Adding a mixed solution of 10 parts of alcohol and 30 parts of deionized water, and stirring for 0.5h at the stirring temperature of 70 ℃ and the stirring speed of 400rpm to obtain a product C;
D. adding complexing agent into product C, wherein the complexing agent is citric acid and ethylene glycol, the citric acid is 3.95 parts, the ethylene glycol is 0.05 part, and performing ultrasonic penetration for 5min at a constant temperature of 70 ℃, the ultrasonic frequency is 10KHZ, and the ultrasonic power density is 0.3KW/m3Stirring for 1.5h at the stirring speed of 380rpm, dropwise adding ammonia water to adjust the pH value to 6.6,stirring to obtain D product;
E. drying the product D in a forced air drying oven at 70 deg.C for 6.5h to obtain product E;
F. under the protection of hydrogen, placing the product E in a tube furnace, sintering at 400 ℃ for 3h, and sintering at 700 ℃ for 1h, wherein the heating rate is 2 ℃/min, and obtaining a product F;
G. and (4) performing gravity separation and impurity removal on the product F, washing the product F with deionized water until the pH value is 7, and drying the product F to obtain a finished product of the catalyst activated carbon composite material for decomposing dioxin.
The catalyst-activated carbon composite material for decomposing dioxin is used for decomposing dioxin in waste incineration tail gas: the prepared catalyst active carbon composite material for decomposing dioxin is filled in a tail gas discharge pipeline of a waste incineration device, and the removal rate of the dioxin in the tail gas reaches 99.78%.
Example 2.
The synthesis process of the catalyst-activated carbon composite material for decomposing dioxin comprises the following steps,
A. crushing activated carbon (the activated carbon is washed and dried by deionized water), and sieving with a 300-mesh sieve to obtain a product A;
B. putting the product A into a container filled with concentrated sulfuric acid, introducing nitrogen into the bottom of the container, soaking for 3h at the flow rate of the nitrogen of 60mL/min, washing until the pH value is 7, and drying to obtain a product B;
C. taking 3 parts of B product and 1 part of AgNO31 part of Mn (NO)3)2And 1 part of Fe (NO)3)3Adding a mixed solution of 15 parts of alcohol and 30 parts of deionized water, and stirring for 1.5 hours at the stirring temperature of 90 ℃ and the stirring speed of 450rpm to obtain a product C;
D. adding complexing agent into product C, wherein the complexing agent is citric acid and ethylene glycol, the citric acid is 3.95 parts, the ethylene glycol is 0.05 part, performing ultrasonic penetration for 15min at 90 ℃ constant temperature, the ultrasonic frequency is 50KHZ, and the ultrasonic power density is 1KW/m3Stirring for 2.5h at the stirring speed of 420rpm, dropwise adding ammonia water to adjust the pH value to 7, and stirring until the solution is in a sol state to obtain a product D;
E. and drying the product D in a forced air drying oven at 90 ℃ for 7h to obtain a product E.
F. Under the protection of hydrogen, placing the product E in a tube furnace, sintering at 600 ℃ for 3.5h, and sintering at 800 ℃ for 2h, wherein the heating rate is 5 ℃/min, and obtaining a product F;
G. and (4) performing gravity separation and impurity removal on the product F, washing the product F with deionized water until the pH value is 7, and drying the product F to obtain a finished product of the catalyst activated carbon composite material for decomposing dioxin.
The catalyst-activated carbon composite material for decomposing dioxin is used for decomposing dioxin in waste incineration tail gas: the prepared catalyst active carbon composite material for decomposing dioxin is filled in a tail gas discharge pipeline of a waste incineration device, and the removal rate of the dioxin in the tail gas reaches 99.69%.
Example 3.
The synthesis process of the catalyst-activated carbon composite material for decomposing dioxin comprises the following steps,
A. crushing activated carbon (the activated carbon is washed and dried by deionized water), and sieving with a 250-mesh sieve to obtain a product A;
B. putting the product A into a container filled with concentrated sulfuric acid, introducing nitrogen into the bottom of the container, soaking for 3h at the flow rate of 80mL/min, washing until the pH value is 7, and drying to obtain a product B;
C. taking 7 parts of B product and 2 parts of AgNO32 parts of Mn (NO)3)2And 2 parts of Fe (NO)3)3Adding a mixed solution of 20 parts of alcohol and 45 parts of deionized water, and stirring for 1 hour at the stirring temperature of 90 ℃ and the stirring speed of 450rpm to obtain a product C;
D. adding complexing agent into product C, wherein the complexing agent is citric acid and ethylene glycol, the citric acid is 7 parts, the ethylene glycol is 0.12 part, performing ultrasonic penetration for 15min at 90 ℃ constant temperature, the ultrasonic frequency is 30KHZ, and the ultrasonic power density is 0.7KW/m3Stirring for 2h at the stirring speed of 400rpm, dropwise adding ammonia water to adjust the pH value to 7, and stirring until the solution is in a sol state to obtain a product D;
E. and drying the product D in a forced air drying oven at 90 ℃ for 7h to obtain a product E.
F. Under the protection of hydrogen, placing the product E in a tube furnace, sintering at 500 ℃ for 3.5h, sintering at 800 ℃ for 2h, and heating at a speed of 3 ℃/min to obtain a product F;
G. and (4) performing gravity separation and impurity removal on the product F, washing the product F with deionized water until the pH value is 7, and drying the product F to obtain a finished product of the catalyst activated carbon composite material for decomposing dioxin.
The catalyst-activated carbon composite material for decomposing dioxin is used for decomposing dioxin in waste incineration tail gas: the prepared catalyst active carbon composite material for decomposing dioxin is filled in a tail gas discharge pipeline of a waste incineration device, and the removal rate of the dioxin in the tail gas reaches 99.85 percent.
Example 4.
The synthesis process of the catalyst-activated carbon composite material for decomposing dioxin comprises the following steps,
A. crushing activated carbon (the activated carbon is washed and dried by deionized water), and sieving with a 220-mesh sieve to obtain a product A;
B. putting the product A into a container filled with concentrated sulfuric acid, introducing nitrogen into the bottom of the container, soaking for 3h at the flow rate of the nitrogen of 60mL/min, washing until the pH value is 7, and drying to obtain a product B;
C. taking 9 parts of B product and 3 parts of AgNO33 parts of Mn (NO)3)2And 3 parts of Fe (NO)3)3Adding a mixed solution of 30 parts of alcohol and 60 parts of deionized water, and stirring for 1 hour at the stirring temperature of 90 ℃ and the stirring speed of 430rpm to obtain a product C;
D. adding complexing agent into product C, wherein the complexing agent is citric acid and ethylene glycol, the citric acid is 10 parts, the ethylene glycol is 0.2 part, performing ultrasonic penetration for 15min at 90 ℃ constant temperature, the ultrasonic frequency is 30KHZ, and the ultrasonic power density is 0.8KW/m3Stirring for 2h at the stirring speed of 400rpm, dropwise adding ammonia water to adjust the pH value to 7, and stirring until the solution is in a sol state to obtain a product D;
E. and drying the product D in a forced air drying oven at 90 ℃ for 6h to obtain a product E.
F. Under the protection of hydrogen, placing the product E in a tube furnace, sintering at 600 ℃ for 4h, sintering at 800 ℃ for 2h, and heating at the speed of 4 ℃/min to obtain a product F;
G. and (4) performing gravity separation and impurity removal on the product F, washing the product F with deionized water until the pH value is 7, and drying the product F to obtain a finished product of the catalyst activated carbon composite material for decomposing dioxin.
The catalyst-activated carbon composite material for decomposing dioxin is used for decomposing dioxin in waste incineration tail gas: the prepared catalyst active carbon composite material for decomposing dioxin is filled in a tail gas discharge pipeline of a waste incineration device, and the removal rate of the dioxin in the tail gas reaches 99.77 percent.
Example 5.
The synthesis process of the catalyst-activated carbon composite material for decomposing dioxin comprises the following steps,
A. crushing activated carbon (the activated carbon is washed and dried by deionized water), and sieving by a 260-mesh sieve to obtain a product A;
B. putting the product A into a container filled with concentrated sulfuric acid, introducing nitrogen into the bottom of the container, soaking for 2.5h at the flow rate of 55mL/min, washing until the pH value is 7, and drying to obtain a product B;
C. taking 5 parts of B product and 1 part of AgNO31 part of Mn (NO)3)2And 1 part of Fe (NO)3)3Adding a mixed solution of 20 parts of alcohol and 40 parts of deionized water, and stirring for 1 hour at the stirring temperature of 80 ℃ and the stirring speed of 430rpm to obtain a product C;
D. adding complexing agent into product C, wherein the complexing agent is citric acid and ethylene glycol, the citric acid is 6 parts, the ethylene glycol is 0.1 part, performing ultrasonic penetration for 10min at 80 ℃ for constant temperature, the ultrasonic frequency is 30KHZ, and the ultrasonic power density is 0.6KW/m3Stirring for 2h at the stirring speed of 400rpm, dropwise adding ammonia water to adjust the pH value to 7, and stirring until the solution is in a sol state to obtain a product D;
E. and drying the product D in a forced air drying oven at 80 ℃ for 6h to obtain a product E.
F. Under the protection of hydrogen, placing the product E in a tube furnace, sintering at 500 ℃ for 3.5h, and sintering at 750 ℃ for 1.5h, wherein the heating rate is 3 ℃/min, and obtaining a product F;
G. and (4) performing gravity separation and impurity removal on the product F, washing the product F with deionized water until the pH value is 7, and drying the product F to obtain a finished product of the catalyst activated carbon composite material.
The catalyst-activated carbon composite material for decomposing dioxin is used for decomposing dioxin in waste incineration tail gas: the prepared catalyst active carbon composite material for decomposing dioxin is filled in a tail gas discharge pipeline of a waste incineration device, and the removal rate of the dioxin in the tail gas reaches 99.89%.
In examples 1 to 5, stirring was carried out using a magnetic stirrer.
Comparative example. The waste incineration device without the catalyst activated carbon composite material for decomposing dioxin in the tail gas pipeline was used for testing the content of dioxin (ng TEQ/m) in 9 batches of waste incineration tail gas3) The measured dioxin content is shown in table 1:
Figure BDA0002046655410000101
the garbage samples in the embodiment and the comparative example of the invention are mixed garbage consisting of domestic garbage and medical waste garbage, the domestic garbage and the medical waste garbage in the garbage samples are fully mixed, and the samples are uniform. The waste incineration amount and incineration conditions in the comparative example and the examples were the same as the dioxin sampling conditions.
The present invention may be embodied in other specific forms without departing from the spirit or essential attributes thereof, and it should be understood that various changes and modifications can be effected therein by one skilled in the art without departing from the spirit and scope of the invention as defined in the appended claims.

Claims (6)

1. The synthesis process of the catalyst active carbon composite material for decomposing dioxin is characterized by comprising the following steps of: comprises the following steps of (a) carrying out,
A. crushing the activated carbon, and sieving the crushed activated carbon with a 200-mesh and 300-mesh sieve to obtain a product A;
B. putting the product A into a container filled with concentrated sulfuric acid, introducing nitrogen into the bottom of the container, soaking for 2-3h at the flow rate of 30-80mL/min, washing until the pH value is 6-7, and drying to obtain a product B;
C. taking 3-9 parts of B product and 3-9 parts of metal salt, wherein the metal salt is AgNO3、Mn(NO3)2And Fe (NO)3)3,AgNO31-3 parts of Mn (NO)3)21-3 parts of Fe (NO)3)31-3 parts of alcohol and 30-60 parts of deionized water, and stirring to obtain a product C;
D. adding 4-10 parts of complexing agent into the product C, wherein the complexing agent is citric acid and glycol, the citric acid is 3.95-9.8 parts, the glycol is 0.05-0.2 part, and ultrasonic penetration is carried out at a constant temperature of 70-90 ℃ for 5-15min at an ultrasonic frequency of 10-50KHZ and an ultrasonic power density of 0.3-1KW/m3Stirring, adding dropwise ammonia water to adjust pH to 6.5-7, and stirring to obtain D product;
E. drying product D to obtain gel to obtain product E;
F. under the protection of hydrogen, sintering the E product at the temperature of 400-800 ℃ for 4-6h at the temperature rising speed of 2-5 ℃/min to obtain an F product;
G. and separating and removing impurities from the F product, washing and drying to obtain a finished product of the catalyst active carbon composite material.
2. The synthesis process of the catalyst-activated carbon composite for decomposition of dioxin according to claim 1, characterized by comprising: in the step C, the stirring time is 0.5-1.5h, the stirring temperature is 70-90 ℃, and the stirring speed is 400-450 rpm.
3. The synthesis process of the catalyst-activated carbon composite for decomposition of dioxin according to claim 1, characterized by comprising: d, adding a complexing agent into the product C, and performing ultrasonic penetration for 5-15min at a constant temperature of 70-90 ℃, wherein the ultrasonic frequency is 10-50KHZ, and the ultrasonic power density is 0.3-1KW/m3Stirring for 1.5-2.5h at 380-420rpm, adding ammonia water dropwise to adjust pH to 6.5-7, and stirring to obtain D product.
4. The synthesis process of the catalyst-activated carbon composite for decomposition of dioxin according to claim 1, characterized by comprising: and E, drying the product D in a forced air drying oven at 70-90 ℃ for 5-7h to obtain a product E.
5. The synthesis process of the catalyst-activated carbon composite for decomposition of dioxin according to claim 1, characterized by comprising: and the step F is to sinter the E product at the temperature of 400-800 ℃ for 3-4h and at the temperature of 700-800 ℃ for 1-2h under the protection of hydrogen to obtain the F product, wherein the heating speed is 2-5 ℃/min.
6. The synthesis process of the catalyst-activated carbon composite for decomposition of dioxin according to claim 1, characterized by comprising: in step G, the separation is gravity separation.
CN201910360394.4A 2019-04-30 2019-04-30 Synthesis process of catalyst activated carbon composite material for decomposing dioxin Active CN110302800B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201910360394.4A CN110302800B (en) 2019-04-30 2019-04-30 Synthesis process of catalyst activated carbon composite material for decomposing dioxin

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201910360394.4A CN110302800B (en) 2019-04-30 2019-04-30 Synthesis process of catalyst activated carbon composite material for decomposing dioxin

Publications (2)

Publication Number Publication Date
CN110302800A CN110302800A (en) 2019-10-08
CN110302800B true CN110302800B (en) 2022-03-11

Family

ID=68074534

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201910360394.4A Active CN110302800B (en) 2019-04-30 2019-04-30 Synthesis process of catalyst activated carbon composite material for decomposing dioxin

Country Status (1)

Country Link
CN (1) CN110302800B (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113731420A (en) * 2021-09-28 2021-12-03 浙江大学 Catalyst for removing fly ash dioxin and preparation method and application thereof
CN114570402A (en) * 2022-01-22 2022-06-03 杭州星宇炭素环保科技有限公司 Preparation method of carbon-defect-containing and oxygen-doped carbon nitride photocatalytic material and application of carbon-defect-containing and oxygen-doped carbon nitride photocatalytic material in removal of tetracycline in water body

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP3803851B2 (en) * 1999-07-19 2006-08-02 日立造船株式会社 Dioxin oxidation catalyst
CN101637722A (en) * 2009-07-21 2010-02-03 浙江大学 Catalyst for removing organic pollutants in incineration gas and preparation method thereof
CN103418341A (en) * 2013-08-03 2013-12-04 彭晓领 Method for preparing activated carbon used for liquid phase adsorption
CN105771891A (en) * 2016-03-24 2016-07-20 宁波德纳希环保科技有限公司 Preparation method for modified activated carbon for adsorbing dioxins
CN105771576A (en) * 2016-03-24 2016-07-20 宁波德纳希环保科技有限公司 Process of utilizing modified activated carbon to remove dioxin
CN108404863A (en) * 2018-04-04 2018-08-17 成都达奇环境科技有限公司 A kind of activated carbon and preparation method thereof for Xi Fu bioxin

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP3803851B2 (en) * 1999-07-19 2006-08-02 日立造船株式会社 Dioxin oxidation catalyst
CN101637722A (en) * 2009-07-21 2010-02-03 浙江大学 Catalyst for removing organic pollutants in incineration gas and preparation method thereof
CN103418341A (en) * 2013-08-03 2013-12-04 彭晓领 Method for preparing activated carbon used for liquid phase adsorption
CN105771891A (en) * 2016-03-24 2016-07-20 宁波德纳希环保科技有限公司 Preparation method for modified activated carbon for adsorbing dioxins
CN105771576A (en) * 2016-03-24 2016-07-20 宁波德纳希环保科技有限公司 Process of utilizing modified activated carbon to remove dioxin
CN108404863A (en) * 2018-04-04 2018-08-17 成都达奇环境科技有限公司 A kind of activated carbon and preparation method thereof for Xi Fu bioxin

Also Published As

Publication number Publication date
CN110302800A (en) 2019-10-08

Similar Documents

Publication Publication Date Title
WO2021082761A1 (en) Lanthanum carbonate modified co-pyrolysis sludge biochar and preparation method and application thereof
CN109928391B (en) Modified distiller&#39;s grain-based activated carbon and preparation method thereof
CN113477217A (en) Preparation and application of poplar sawdust biochar loaded nano zero-valent iron composite material
CN105540819B (en) A kind of method of support modification preparation ozone catalyst processing organic wastewater with difficult degradation thereby
CN110302800B (en) Synthesis process of catalyst activated carbon composite material for decomposing dioxin
CN106076272A (en) A kind of preparation method of adsorbent for heavy metal
CN109046229B (en) Lanthanum hydroxide modified hydroxyapatite material and preparation method and application thereof
CN110201636B (en) Preparation method of modified biochar
CN108927109A (en) A kind of phosphogypsum modification charcoal method and its application
CN112938969A (en) Method for preparing nitrogen-sulfur co-doped activated carbon by pore-forming/doping integrated activating agent and application of method
CN109550484A (en) A kind of preparation method of instruction plant stem foot chromium ion adsorbent
CN106064962A (en) Utilize mud and coal ash for manufacturing for the method for catalyst particle electrode and application
CN112670526B (en) Preparation method and application of amorphous manganese dioxide modified shrimp shell carbon base frame
CN111804323B (en) Photocatalyst and application thereof in photocatalytic environment-friendly treatment of power battery
CN111545163B (en) Adsorbent for heavy metal wastewater treatment and preparation method thereof
CN103199267A (en) Preparation technology of nano-Fe3O4-V2O5-Au-doped poly-naphthylamine film modified netted glassy carbon electrode
CN111439823A (en) Modified coconut coir-loaded nano zero-valent iron composite material, and preparation method and application thereof
CN109046338B (en) Carbon material immobilized palladium catalyst, preparation and application thereof
CN114146684A (en) Modified red mud biochar material and preparation and application methods thereof
CN115025796A (en) Biomass-loaded MOFs-derived composite catalyst and preparation method and application thereof
CN109647410B (en) Preparation method of supported expanded graphite catalyst for treating EDTA-Cu wastewater
CN114054027A (en) Graphite material modified red mud Fenton catalyst with magnetic separation performance and preparation method and application thereof
CN107188167B (en) A method of active sludge carbon is prepared using activated by urine municipal sludge
CN113145059A (en) Preparation and application of sludge-based carbon iron material
CN114588872B (en) Iron-silver co-doped biochar with high adsorption capacity and preparation method 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
GR01 Patent grant
GR01 Patent grant