CN109174199B - Method for preparing Fenton-like catalyst and synchronously regenerating active carbon by microwave and application - Google Patents

Method for preparing Fenton-like catalyst and synchronously regenerating active carbon by microwave and application Download PDF

Info

Publication number
CN109174199B
CN109174199B CN201811345382.6A CN201811345382A CN109174199B CN 109174199 B CN109174199 B CN 109174199B CN 201811345382 A CN201811345382 A CN 201811345382A CN 109174199 B CN109174199 B CN 109174199B
Authority
CN
China
Prior art keywords
catalyst
fenton
chitosan
activated carbon
microwave
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
CN201811345382.6A
Other languages
Chinese (zh)
Other versions
CN109174199A (en
Inventor
刘福强
程松
朱常青
沈晨
江昊
张清清
仇欢
李爱民
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.)
Nanjing University
Original Assignee
Nanjing University
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 Nanjing University filed Critical Nanjing University
Priority to CN201811345382.6A priority Critical patent/CN109174199B/en
Publication of CN109174199A publication Critical patent/CN109174199A/en
Application granted granted Critical
Publication of CN109174199B publication Critical patent/CN109174199B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J31/00Catalysts comprising hydrides, coordination complexes or organic compounds
    • B01J31/26Catalysts comprising hydrides, coordination complexes or organic compounds containing in addition, inorganic metal compounds not provided for in groups B01J31/02 - B01J31/24
    • B01J31/28Catalysts comprising hydrides, coordination complexes or organic compounds containing in addition, inorganic metal compounds not provided for in groups B01J31/02 - B01J31/24 of the platinum group metals, iron group metals or copper
    • 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
    • B01J35/33Electric or magnetic properties
    • 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
    • B01J35/399Distribution of the active metal ingredient homogeneously throughout the support particle
    • 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
    • B01J37/34Irradiation by, or application of, electric, magnetic or wave energy, e.g. ultrasonic waves ; Ionic sputtering; Flame or plasma spraying; Particle radiation
    • B01J37/341Irradiation by, or application of, electric, magnetic or wave energy, e.g. ultrasonic waves ; Ionic sputtering; Flame or plasma spraying; Particle radiation making use of electric or magnetic fields, wave energy or particle radiation
    • B01J37/344Irradiation by, or application of, electric, magnetic or wave energy, e.g. ultrasonic waves ; Ionic sputtering; Flame or plasma spraying; Particle radiation making use of electric or magnetic fields, wave energy or particle radiation of electromagnetic wave energy
    • B01J37/346Irradiation by, or application of, electric, magnetic or wave energy, e.g. ultrasonic waves ; Ionic sputtering; Flame or plasma spraying; Particle radiation making use of electric or magnetic fields, wave energy or particle radiation of electromagnetic wave energy of microwave energy
    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01BNON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
    • C01B32/00Carbon; Compounds thereof
    • C01B32/30Active carbon
    • C01B32/354After-treatment
    • C01B32/36Reactivation or regeneration
    • C01B32/366Reactivation or regeneration by physical processes, e.g. by irradiation, by using electric current passing through carbonaceous feedstock or by using recyclable inert heating bodies
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/722Oxidation by peroxides
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/72Treatment of water, waste water, or sewage by oxidation
    • C02F1/725Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/306Pesticides
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/34Organic compounds containing oxygen
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/34Organic compounds containing oxygen
    • C02F2101/345Phenols
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/36Organic compounds containing halogen
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/38Organic compounds containing nitrogen
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/40Organic compounds containing sulfur
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/02Specific form of oxidant
    • C02F2305/026Fenton's reagent
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/50Improvements relating to the production of bulk chemicals
    • Y02P20/584Recycling of catalysts

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Engineering & Computer Science (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Materials Engineering (AREA)
  • Physics & Mathematics (AREA)
  • Hydrology & Water Resources (AREA)
  • Health & Medical Sciences (AREA)
  • Toxicology (AREA)
  • Inorganic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Optics & Photonics (AREA)
  • Electromagnetism (AREA)
  • General Health & Medical Sciences (AREA)
  • Plasma & Fusion (AREA)
  • Catalysts (AREA)

Abstract

The invention belongs to the technical field of functional materials and environmental protection, and particularly relates to a method for preparing a Fenton-like catalyst by microwave and synchronously regenerating activated carbon and application thereof, wherein the method uses cheap iron salt, chitosan and the like as raw materials, and quickly carbonizes a chitosan precursor by using heat generated by microwave regeneration of the activated carbon, so that the energy consumption and time for preparing the catalyst are greatly saved; the Fenton-like catalyst obtained by the invention mainly comprises nano ferroferric oxide particles and amorphous carbon, and has stronger magnetism, mechanical strength, chemical stability and better catalytic activity; the method has the advantages of simple process, low energy consumption and high efficiency, and the efficient, stable and cheap Fenton-like catalyst is prepared in an auxiliary manner while the activated carbon is regenerated, so that the method has a wide application prospect in the field of environmental protection.

Description

Method for preparing Fenton-like catalyst and synchronously regenerating active carbon by microwave and application
Technical Field
The invention belongs to the technical field of functional materials and environmental protection, and particularly relates to a method for preparing a Fenton-like catalyst by microwave and synchronously regenerating activated carbon and application thereof.
Background
The advanced oxidation technologies such as an electrocatalytic oxidation method, a photocatalytic method, an ozone oxidation method, a wet oxidation method, a Fenton-like method and the like can decompose and mineralize most of organic matters, and have a good effect of removing refractory organic matters. The heterogeneous Fenton-like method loads the catalyst on a stable matrix, and has the advantages of wide pH application range, small dosage of the medicament, mild application conditions, high degradation efficiency and the like. However, currently, fenton-like catalysts are mainly composed of powdery nanoparticles, and in order to improve catalytic activity, heavy metal elements such as Cu, Ni, and Co are generally doped. Although the catalyst has a large specific surface area and high catalytic activity, the catalyst is difficult to recover in the actual use process, and nano pollution and heavy metal pollution are easily caused after loss. Meanwhile, the traditional catalyst preparation and regeneration methods usually face the problems of long heat treatment time, atmosphere protection, high process energy consumption and the like.
Disclosure of Invention
The invention solves the technical problems in the prior art and provides a method for preparing a Fenton-like catalyst by microwave and synchronously regenerating activated carbon and application thereof.
In order to solve the problems, the technical scheme of the invention is as follows:
a method for preparing a Fenton-like catalyst by microwave and synchronously regenerating activated carbon comprises the following steps:
the Fenton-like catalyst precursor and the active carbon which adsorbs the organic matters are mixed and put into a microwave reactor for reaction.
Preferably, the Fenton-like catalyst precursor is chitosan/Fe (OH)3Xerogel microspheres.
Preferably, the microwave reaction power is 600-800W; the time is 2-5 min.
Preferably, after the microwave reaction, the fenton-like catalyst is separated from the activated carbon by a magnet.
Preferably, the preparation method of the fenton-like catalyst precursor comprises the following steps:
step 1, mixing chitosan, ferric salt and an organic acid aqueous solution to prepare sol A;
step 2, dropwise adding the sol A into an alkaline aqueous solution to obtain chitosan/Fe (OH)3Gel microspheres;
step 3, the obtained product isThe chitosan/Fe (OH)3Washing and drying the gel microspheres to obtain chitosan/Fe (OH)3Xerogel microspheres.
Preferably, in the step 1, the mass ratio of the iron element to the chitosan in the sol A is 1 (5-7).
Preferably, in the step 1, the mass fraction of chitosan in the sol A is 0.5-5%.
Preferably, in the step 1, the iron salt is FeCl3、FeNO3、Fe2(SO4)3Any one or more of them.
Preferably, in the step 1, the organic acid may be any one or more of formic acid, acetic acid, citric acid and oxalic acid.
The Fenton-like catalyst can be used for degrading organic matters in wastewater. For example, the method is used for treating wastewater containing dye, sulfamethoxazole, tetracycline hydrochloride, bisphenol A and the like.
Compared with the prior art, the invention has the advantages that,
the invention fully utilizes the heat generated during the microwave regeneration of the active carbon, uses cheap chitosan and iron sources, and synchronously prepares the magnetic biochar-based Fenton catalyst, and the preparation method is simple and environment-friendly, has low process cost, short period and low energy consumption. The prepared Fenton-like catalyst has a developed pore structure, high chemical stability, high mechanical property and high magnetism, and can be quickly separated and recovered from a solution under the action of a magnetic field. The ferroferric oxide nano particles and a small amount of simple substance iron are used as main catalytic sites of the catalyst, are uniformly distributed on the surface of the carbon matrix and are embedded in the carbon matrix, the reusability is good, the leaching amount of iron ions in the using process is small, and the catalyst can be rapidly regenerated after being unstable, so that the stability of the material is recovered.
The catalyst of the invention is characterized in that in the process of contacting with wastewater, solid-phase iron oxide and H2O2Heterogeneous Fenton-like reaction occurs to generate hydroxyl free radical and superoxide free radical with strong oxidizing property. The iron monomer in the catalyst can generate iron-carbon micro-electrolysis effect with the carbon matrix. Both of the above processes can release iron ions into the solutionActing as a homogeneous fenton-like catalyst. And abundant surface oxygen-containing functional groups on the carbon matrix can be complexed with iron ions in the solution, and the formed complex can accelerate Fe2+/Fe3+Thereby further promoting the decomposition of the organic matter.
Drawings
FIG. 1 is a flow chart of the present invention;
FIG. 2 is a scanning electron microscope image of the magnetic biochar microspheres obtained in examples 1, 2 and 3 of the present invention;
FIG. 3 is a transmission electron micrograph of magnetic biochar microspheres obtained in example 1 of the present invention;
FIG. 4 is an XRD spectrum of the magnetic biochar microspheres obtained in examples 1 to 6 of the present invention.
Detailed Description
Example 1:
first), 6g of chitosan is weighed, 2% acetic acid solution is added to 200g, and stirring is carried out until the chitosan is dissolved. Weighing 6.18g of nonahydrate and ferric nitrate (the mass ratio of the iron element to the chitosan is 1:7), slowly adding into the chitosan solution, and continuously stirring until the mixture is uniformly mixed; one end of a peristaltic pump hose is inserted into the mixed solution, the other end of the hose is suspended above a short beaker filled with 300ml of 1mol/LNaOH, the rotating speed of a magnetic rotor in the beaker is set to be 200rmp/min, the rotating speed of the peristaltic pump is set to be 30rmp/min, and the mixed solution is continuously dropped into an alkaline solution in a form of liquid drops to be crosslinked to form gel microspheres. Repeatedly washing the gel microspheres with distilled water until the pH value is not changed any more, and drying the gel microspheres in an oven at 80 ℃ for 2h (drying to constant weight) to prepare xerogel microspheres;
secondly), adding 10g of coal-made active carbon into 200mL of 500mg/L acid orange solution, oscillating for 6h at 120rmp/min on a shaking table at the temperature of 25 ℃, taking out and drying, and calculating the adsorption quantity of the coal-made active carbon;
and thirdly), filtering and drying the granular active carbon saturated with the adsorbed acid orange, weighing 10g of active carbon and 2g of dried gel, uniformly mixing, and putting into a microwave reactor for reaction, wherein the microwave power is set to be 600W, and the microwave reaction time is 2 min. And after the reaction is finished and the biological carbon microspheres are naturally cooled, separating the magnetic biological carbon microspheres by using a magnet, removing surface impurities by using dilute hydrochloric acid, ethanol and deionized water, and finally drying to obtain the magnetic biological carbon Fenton catalyst.
Fourthly), adding the regenerated active carbon into 200mL of acid orange solution with the concentration of 500mg/L, oscillating for 6h on a shaking table with the temperature of 25 ℃ at 120rmp/min, and taking out the active carbon, and calculating the adsorption quantity of the regenerated coal active carbon.
The electron micrograph of the magnetic biochar microspheres obtained in this example is shown in FIG. 2(a), and the cross-sectional view is shown in FIG. 2 (b).
The transmission electron micrograph of the magnetic biochar microspheres obtained in this example is shown in FIG. 3.
In example 1, FeCl for iron nitrate3Or Fe2(SO4)3Instead, the prepared Fenton-like catalyst has the same shape and property.
Example 2:
this embodiment is different from example 1 in that the amount of the nonahydrate and the ferric nitrate added in the first step) was 7.21g (the mass ratio of the iron element to the chitosan was 1:6), and the other steps were the same as example 1.
The electron micrograph of the magnetic biochar microspheres obtained in this example is shown in FIG. 2(c), and the cross-sectional view is shown in FIG. 2 (d).
Example 3:
this embodiment is different from example 1 in that the amount of the nine water and the ferric nitrate added in the step one) is 8.65g (the mass ratio of the iron element to the chitosan is 1:5), and the other steps are the same as example 1.
The electron micrograph of the magnetic biochar microspheres obtained in this example is shown in FIG. 2(e), and the cross-sectional view is shown in FIG. 2 (f).
Example 4:
this embodiment is different from example 2 in that the microwave reaction time in the third step) is 3min, and the rest is the same as example 2.
Example 5:
this embodiment is different from example 2 in that the microwave reaction time in the third step) is 4min, and the rest is the same as example 2.
Example 6:
this embodiment is different from example 2 in that the microwave reaction power in the third step) is 800W, and the other steps are the same as example 2.
Example 7:
the degradation rate of acid orange is taken as an index for investigating the activity of the catalyst, the dissolving-out concentration of iron is taken as an index for investigating the stability of the catalyst, and the influences of different iron elements and the quality of chitosan, the microwave reaction time and the microwave power on the activity and the stability of the catalyst are investigated. 0.1g of the catalyst described in examples 1 to 6 was put into a 100mL conical flask, and 50mL of 25mg/L acid orange solution and 0.1mL of hydrogen peroxide (30 wt%) solution were added in this order, and after reaction for 1 hour in a shaker at a rotation speed of 120rpm and a temperature of 50 ℃, the removal rate of acid orange in the solution and the iron content in the solution were measured without adjusting the pH of the solution.
The method of the invention changes the adsorption quantity of the activated carbon to the acid orange before and after regeneration into an investigation index of the regeneration effect of the activated carbon, and investigates the influence of different microwave reaction time and microwave power on the adsorption quantity of the regenerated granular activated carbon to the acid orange.
The above results are shown in the following table:
Figure BDA0001863606760000041
as can be seen from the results in the above table, the catalyst of the present invention shows good treatment effect when used for treating dye wastewater, and XRD spectrum results in FIG. 4 show that the material structure is not changed significantly after the reaction is finished, and can still be recovered rapidly by a magnet. Meanwhile, the activated carbon can be well regenerated.
Example 8:
0.1g of the catalyst obtained in example 2 was weighed into a 100mL Erlenmeyer flask, and 50mL of a 25mg/L bisphenol A solution and 0.1mL of a 30 wt% hydrogen peroxide solution were sequentially added to the Erlenmeyer flask, and the initial pH of the solution was an initial value, and after reacting for 1 hour in a shaker at a rotation speed of 120rpm and a temperature of 50 ℃, the removal rate of bisphenol A in the solution was determined to be 99.9%.
Example 9:
0.1g of the catalyst obtained in example 2 was weighed and put into a 100mL Erlenmeyer flask, and 50mL of a 25mg/L sulfamethoxazole solution and 0.1mL of a 30 wt% hydrogen peroxide solution were sequentially added to the Erlenmeyer flask, and the initial pH of the solution was an initial value, and after reaction for 1 hour in a shaker at a rotation speed of 120rpm and a temperature of 50 ℃, the removal rate of sulfamethoxazole in the solution was measured to be 99.2%.
Example 10:
0.1g of the catalyst obtained in example 2 was weighed and put into a 100mL Erlenmeyer flask, and 50mL of a tetracycline hydrochloride solution having a concentration of 25mg/L and 0.1mL of a hydrogen peroxide (30 wt%) solution were sequentially added, and the initial pH of the solution was an initial value, and after reacting for 1 hour in a shaker at a rotation speed of 120rpm and a temperature of 50 ℃, the removal rate of tetracycline hydrochloride in the solution was found to be 95.2%.
Examples 8-10 prove that the catalyst has a good broad spectrum for degrading organic matters.
Example 11:
one), weighing 0.1g of the catalyst obtained in example 2, adding 50mL of 25mg/L acid orange solution and 0.1mL of hydrogen peroxide (30 wt%) solution in sequence, wherein the initial pH of the solution is 6.77, reacting for 1h in a shaker at 120rpm and 50 ℃, and determining the removal rate of acid orange and the concentration of total iron in the solution. The catalyst obtained after the reaction was recovered by a magnet, and the above experiment was repeated after simple washing with pure water for a total of 5 cycles. After the 5 th reaction is finished, recovering the catalyst, cleaning and drying;
secondly), mixing the catalyst with 10g of active carbon, and then putting the mixture into a microwave reactor for reaction, wherein the microwave power is set to be 600W, and the microwave reaction time is 2 min. And after the microwave reaction is finished and the catalyst is naturally cooled, separating the catalyst by using a magnet, removing impurities on the surface of the catalyst by using dilute hydrochloric acid and distilled water, and finally drying to obtain the regenerated catalyst.
And thirdly), repeating the degradation experiment in the step one) by using the regenerated catalyst.
The final results of this example are shown in the following table:
Figure BDA0001863606760000051
as can be seen from the above results, the catalytic activity of the fenton-like reaction catalyst of the present invention is not reduced after multiple cycles. The leaching amount of iron is kept at a low level all the time, the leaching amount of iron is less than 0.5 percent of the total iron content of the catalyst, the catalyst particles are not broken after 5 times of circulation, and the stability (the leaching amount of iron) can be recovered after simple regeneration.
Comparative example 1:
the difference between this embodiment and example 1 is that no acid orange adsorbing saturated granular activated carbon is added:
first), 6g of chitosan is weighed, 2% acetic acid solution is added to 200g, and stirring is carried out until the chitosan is dissolved. Weighing 6.18g of nonahydrate and ferric nitrate (the mass ratio of the iron element to the chitosan is 1:7), slowly adding into the chitosan solution, and continuously stirring until the mixture is uniformly mixed; one end of a peristaltic pump hose is inserted into the mixed solution, the other end of the hose is suspended above a short beaker filled with 300ml of 1mol/LNaOH, the rotating speed of a magnetic rotor in the beaker is set to be 200rmp/min, the rotating speed of the peristaltic pump is set to be 30rmp/min, and the mixed solution is continuously dropped into an alkaline solution in a form of liquid drops to be crosslinked to form gel microspheres. Repeatedly washing the gel microspheres with distilled water until the pH value is not changed any more, and drying the gel microspheres in an oven at 80 ℃ for 2h (drying to constant weight) to prepare xerogel microspheres;
secondly), 2g of xerogel is put into a microwave reactor for reaction, the microwave power is set to be 600W, and the microwave reaction time is 2 min. And naturally cooling after the reaction is finished.
The experimental results show that: the catalyst with magnetism cannot be prepared.
Comparative example 2:
this embodiment is different from example 1 in that the amount of the nine water and the ferric nitrate added in the first step) is 10.82g (the mass ratio of the iron element to the chitosan is 1:4), and the other steps are the same as example 1.
Comparative example 3:
this embodiment is different from example 1 in that the amount of the nine water and the ferric nitrate added in the first step) is 4.33g (the mass ratio of the iron element to the chitosan is 1:10), and the other steps are the same as example 1.
Comparative example 4
This embodiment is different from example 2 in that the microwave reaction time in the third step) is 2min, and the rest is the same as example 2.
Comparative example 5
This embodiment is different from example 2 in that the microwave reaction time in the third step) is 5min, and the rest is the same as example 2.
Comparative example 6
0.1g of the catalyst described in comparative examples 2 to 5 was charged into a 100mL Erlenmeyer flask, and 50mL of 25mg/L acid orange solution and 0.1mL of hydrogen peroxide (30 wt%) solution were sequentially added to the Erlenmeyer flask, the initial pH of the solution was 6.77, and after reaction for 1 hour in a shaker rotating at 120rpm and at 50 ℃, the removal rate of acid orange in the solution and the content of iron in the solution were measured.
The method of the invention changes the adsorption quantity of the activated carbon to the acid orange before and after regeneration into an investigation index of the regeneration effect of the activated carbon, and investigates the influence of different microwave reaction time and microwave power on the adsorption quantity of the regenerated granular activated carbon to the acid orange.
The above results are shown in the following table:
Figure BDA0001863606760000061
it should be noted that the above-mentioned embodiments are only preferred embodiments of the present invention, and are not intended to limit the scope of the present invention, and all equivalent substitutions or substitutions made on the above-mentioned embodiments are included in the scope of the present invention.

Claims (7)

1. A method for preparing a Fenton-like catalyst by microwave and synchronously regenerating activated carbon is characterized by comprising the following steps of:
mixing a Fenton-like catalyst precursor and coal-made active carbon adsorbed with acid orange, and putting the mixture into a microwave reactor for reaction;
the Fenton-like catalyst precursor is chitosan/Fe (OH)3Xerogel microspheres;
the preparation method of the Fenton-like catalyst precursor comprises the following steps of:
step 1, mixing chitosan, ferric salt and an organic acid aqueous solution to prepare sol A;
step 2, dropwise adding the sol A into an alkaline aqueous solution to obtain chitosan/Fe (OH)3Gel microspheres;
step 3, mixing the chitosan/Fe (OH)3Washing and drying the gel microspheres to obtain chitosan/Fe (OH)3Xerogel microspheres.
2. The method for preparing a Fenton-like catalyst and synchronously regenerating activated carbon by microwaves according to claim 1, wherein the microwave reaction power is 600-800W; the time is 2-5 min.
3. The method for preparing a Fenton-like catalyst and synchronously regenerating activated carbon by microwaves according to claim 1, wherein in the step 1, the mass ratio of the iron element to the chitosan in the sol A is 1 (5-7).
4. The method for preparing a Fenton-like catalyst and synchronously regenerating activated carbon by microwaves according to claim 1, wherein in the step 1, the mass fraction of chitosan in the sol A is 0.5-5%.
5. The microwave Fenton-like catalyst preparation method using microwaves and synchronous activated carbon regeneration according to claim 1, wherein in the step 1, the iron salt is FeCl3、Fe(NO3)3、Fe2(SO4)3Any one or more of them.
6. The method for preparing a Fenton-like catalyst and synchronously regenerating activated carbon by microwaves according to claim 1, wherein in the step 1, the organic acid is any one or more of formic acid, acetic acid, citric acid and oxalic acid.
7. Use of a fenton-like catalyst prepared according to any one of claims 1 to 6 for the degradation of organic material in waste water.
CN201811345382.6A 2018-11-13 2018-11-13 Method for preparing Fenton-like catalyst and synchronously regenerating active carbon by microwave and application Active CN109174199B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201811345382.6A CN109174199B (en) 2018-11-13 2018-11-13 Method for preparing Fenton-like catalyst and synchronously regenerating active carbon by microwave and application

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201811345382.6A CN109174199B (en) 2018-11-13 2018-11-13 Method for preparing Fenton-like catalyst and synchronously regenerating active carbon by microwave and application

Publications (2)

Publication Number Publication Date
CN109174199A CN109174199A (en) 2019-01-11
CN109174199B true CN109174199B (en) 2020-10-27

Family

ID=64939478

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201811345382.6A Active CN109174199B (en) 2018-11-13 2018-11-13 Method for preparing Fenton-like catalyst and synchronously regenerating active carbon by microwave and application

Country Status (1)

Country Link
CN (1) CN109174199B (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109894097A (en) * 2019-04-09 2019-06-18 合肥工业大学 A kind of method of tetracycline antibiotics in removal water body
CN110743549B (en) * 2019-10-25 2022-09-09 北京工业大学 Preparation method of copper-based heterogeneous catalyst taking activated carbon spheres as carrier for wet oxidation

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2018045790A1 (en) * 2016-09-09 2018-03-15 南京大学 Mesoporous manganese ferrite fenton-like catalyst, preparation method therefor, and application thereof

Family Cites Families (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101780955B (en) * 2010-03-22 2012-03-14 哈尔滨工业大学 Chitosan activated carbon and preparation method thereof
CN104801280A (en) * 2015-04-01 2015-07-29 河海大学 Preparation method for biomass charcoal adsorbent loaded with chitosan magnetic nanoparticles
CN107282013A (en) * 2016-04-01 2017-10-24 成都理工大学 The porous magnetic chitosan gel rubber microballoon and preparation method of a kind of size tunable
CN107555529A (en) * 2017-09-14 2018-01-09 江苏科力特环保科技有限公司 A kind of activated carbon recovery process
CN108417849A (en) * 2018-03-23 2018-08-17 西北师范大学 A kind of preparation based on ferrite@chitosan schiff-base carbon material catalyst

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2018045790A1 (en) * 2016-09-09 2018-03-15 南京大学 Mesoporous manganese ferrite fenton-like catalyst, preparation method therefor, and application thereof

Also Published As

Publication number Publication date
CN109174199A (en) 2019-01-11

Similar Documents

Publication Publication Date Title
CN109647431B (en) Catalyst for catalytic oxidation treatment of refractory wastewater by ozone, preparation method and application thereof
Lv et al. Carbon zero-valent iron materials possessing high-content fine Fe0 nanoparticles with enhanced microelectrolysis-Fenton-like catalytic performance for water purification
CN111111661A (en) Metal organic framework derived iron-carbon catalyst applicable to heterogeneous electro-Fenton and preparation method thereof
CN112958090B (en) Efficient and stable iron-copper montmorillonite heterogeneous Fenton catalyst and preparation method and application thereof
CN109174199B (en) Method for preparing Fenton-like catalyst and synchronously regenerating active carbon by microwave and application
CN110694685B (en) Preparation method and application of ferromanganese cobalt Prussian blue and manganese oxide composite nano-box assembled by ultrathin nano-sheets
CN112206826B (en) Preparation method and application of cobalt-iron alloy magnetic chitosan carbonized microsphere
WO2012109846A1 (en) Methods for preparation and use of catalyst for hydrazine degradation
Liu et al. Nitrogen doped Cu/Fe@ PC derived from metal organic frameworks for activating peroxymonosulfate to degrade Rhodamine B
CN109908926B (en) Preparation method of ozone catalytic oxidation catalyst
CN112827511A (en) Cyclodextrin modified magnetic CuO-Fe3O4-biochar heterogeneous nano-catalyst and method for repairing organic pollution by using same
CN114797781B (en) Preparation method of lanthanum-loaded nitrogen-doped porous carbon-phosphorus adsorption material
Liu et al. Structural characterizations of zinc-copper silicate polymer (ZCSP) and its mechanisms of ozonation for removal of p-chloronitrobenzene in aqueous solution
Lu et al. Three-dimensional electro-Fenton degradation of ciprofloxacin catalyzed by CuO doped red mud particle electrodes: Electrodes preparation, kinetics and mechanism
CN113546626A (en) Nano zero-valent iron-copper carbon microsphere material and preparation method thereof
CN113332988B (en) Porous magnetic conductive copper-self-doped copper-zinc ferrite catalyst and preparation method and application thereof
CN114634220A (en) Method for photodegrading organic arsenide
CN111333154B (en) Preparation method and application of micro-electrolysis material
CN107684926B (en) Photocatalyst for treating dye in high-salinity wastewater and preparation method thereof
CN109908934B (en) Catalyst for catalytic oxidation reaction of ozone and preparation method thereof
CN103934014A (en) Method for preparing nitrogen-doped indium oxide nanorod/graphene oxide composite photocatalyst
CN108793312B (en) Method for removing antibiotics by using carbon nitride/nitrogen doped hollow mesoporous carbon/bismuth trioxide ternary Z-shaped photocatalyst
CN109908967B (en) Composite carrier material and preparation method thereof
CN108906108B (en) N-SrTiO3Microwave synthesis process of active carbon treatment material and application thereof
CN115212884B (en) Preparation method and application of catalyst based on metal ion reinforced free radical domination

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