CN116605973A - Catalyst for treating tetracycline wastewater and preparation method and application thereof - Google Patents

Catalyst for treating tetracycline wastewater and preparation method and application thereof Download PDF

Info

Publication number
CN116605973A
CN116605973A CN202310563658.2A CN202310563658A CN116605973A CN 116605973 A CN116605973 A CN 116605973A CN 202310563658 A CN202310563658 A CN 202310563658A CN 116605973 A CN116605973 A CN 116605973A
Authority
CN
China
Prior art keywords
chitosan
cobalt ferrite
solution
coated cobalt
microsphere
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.)
Granted
Application number
CN202310563658.2A
Other languages
Chinese (zh)
Other versions
CN116605973B (en
Inventor
余薇薇
陈士凌
李卓林
疏明慧
毛羽丰
艾婷
赵雅倩
刘洋
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.)
Chongqing Jiaotong University
Original Assignee
Chongqing Jiaotong 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 Chongqing Jiaotong University filed Critical Chongqing Jiaotong University
Priority to CN202310563658.2A priority Critical patent/CN116605973B/en
Publication of CN116605973A publication Critical patent/CN116605973A/en
Application granted granted Critical
Publication of CN116605973B publication Critical patent/CN116605973B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • 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
    • 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
    • B01J23/002Mixed oxides other than spinels, e.g. perovskite
    • 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
    • B01J23/75Cobalt
    • 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
    • B01J31/02Catalysts comprising hydrides, coordination complexes or organic compounds containing organic compounds or metal hydrides
    • B01J31/06Catalysts comprising hydrides, coordination complexes or organic compounds containing organic compounds or metal hydrides containing polymers
    • 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
    • B01J35/50Catalysts, in general, characterised by their form or physical properties characterised by their shape or configuration
    • B01J35/51Spheres
    • 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
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/34Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32
    • C02F2103/343Nature of the water, waste water, sewage or sludge to be treated from industrial activities not provided for in groups C02F2103/12 - C02F2103/32 from the pharmaceutical industry, e.g. containing antibiotics
    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/30Wastewater or sewage treatment systems using renewable energies
    • Y02W10/37Wastewater or sewage treatment systems using renewable energies using solar energy

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Materials Engineering (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Catalysts (AREA)
  • Removal Of Specific Substances (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

The invention provides a catalyst for treating tetracycline waste water, a preparation method and application thereof, wherein a certain proportion of chitosan coated cobalt ferrite microspheres and peroxymonosulfate are added into the tetracycline waste water for degradation treatment under dark conditions; the preparation method of the chitosan coated cobalt ferrite microsphere comprises the following steps: step one, dissolving chitosan in acetic acid to obtain chitosan solution, and adding CoCl 2 ·6H 2 O and FeCl 3 ·6H 2 O is dissolved inObtaining a metal salt solution in deionized water; uniformly mixing the metal salt solution and the chitosan solution, eliminating bubbles, then dropwise adding the mixture into the sodium hydroxide-sodium acetate mixed solution at a certain temperature, continuously reacting for a period of time, and standing and cooling after the reaction is finished; washing the obtained product with deionized water until the pH value of the supernatant is neutral, and then freeze-drying the product to obtain a finished product of the chitosan coated cobalt ferrite microsphere; the microsphere prepared by the invention has stronger magnetism and better magnetic recovery capability.

Description

Catalyst for treating tetracycline wastewater and preparation method and application thereof
Technical Field
The invention relates to the field of wastewater treatment, in particular to a catalyst for treating tetracycline wastewater, and a preparation method and application thereof.
Background
In recent years, with the progress of technology and the rapid growth of population, water pollution is continuously increased, and the global water resource condition is continuously deteriorated.
Antibiotics refer to a class of secondary metabolites produced by microorganisms, including bacteria, fungi, actinomycetes, or higher animals and plants, during life, that have antipathogenic or other activities and interfere with the developmental functions of other living cells. At present, antibiotics are widely applied to the fields of medicine, animal disease prevention and treatment, aquaculture, livestock, agriculture and the like, but the absorption capacity of people and livestock to the antibiotics is extremely limited, and meanwhile, due to abuse of the antibiotics, a large amount of antibiotics enter a water body. The application of the tetracycline in various industries of human medicine brings great convenience to human society, but the application and abuse of the tetracycline lead 70% of the tetracycline not to be fully absorbed by animals or human bodies but to be released into the environment, so that the tetracycline is polluted and destroyed. Tetracyclines can disrupt cell ribosome formation and inhibit protein synthesis, thereby producing an inhibitory effect on cell formation. After the tetracycline enters the human body, the tetracycline can form huge poison to cells of some viscera in the human body, and reduce metabolism of the human body. The administration of tetracyclines not only can lead to gastrointestinal lesions, but also can lead to repeated infection of a large number of drug-resistant bacteria, so that human beings can be treated without drugs, and even more and more drug-resistant bacteria can be generated.
Tetracyclines have a stable chemical structure and low biodegradability, and decay periods in the environment are relatively long, which are difficult to effectively remove by conventional water treatment methods. Therefore, it is important to explore an efficient and environmentally friendly method to rapidly remove tetracyclines in an aqueous environment.
Disclosure of Invention
The oxidative degradation capability of the peroxymonosulfate is limited, the chitosan coated cobalt ferrite microsphere can not react with tetracycline, and the self adsorption capability is not strong. Cobalt ferrite can activate the persulfate to produce free radical to degrade tetracycline, but the cobalt ferrite is easy to agglomerate in the process of catalytic reaction, and the defect can be well overcome in a persulfate/chitosan coated cobalt ferrite microsphere system.
In view of the above, the invention provides a tetracycline wastewater treatment method, which utilizes chitosan coated cobalt ferrite microsphere to activate peroxymonosulfate to degrade tetracycline wastewater, specifically, under dark condition, adding a certain proportion of chitosan coated cobalt ferrite microsphere and peroxymonosulfate into the tetracycline wastewater to degrade;
preferably, the mass concentration (g/L) of the catalyst is 1:5 of the mass concentration (mmol/L) of the peroxomonosulfate; most preferably, 0.1g/L chitosan coated cobalt ferrite microsphere and 0.5mmol/L persulfate are added;
the preferred operation is that the degradation treatment is carried out in the constant-temperature oscillation of the gas bath, the preferred temperature is 25 ℃, the preferred rotating speed is 200r/min, and the preferred reaction time is 2h;
the preparation method of the chitosan coated cobalt ferrite microsphere comprises the following steps:
step one, dissolving chitosan in acetic acid to obtain chitosan solution, and adding CoCl 2 ·6H 2 O and FeCl 3 ·6H 2 O is dissolved in deionized water to obtain a metal salt solution;
preferably, chitosan is mixed with acetic acid at a volume concentration of 2% at m: v (g/ml) =1:40, coCl is added 2 ·6H 2 O、FeCl 3 ·6H 2 O is dissolved in deionized water according to the mol ratio of 1:2;
uniformly mixing the metal salt solution and the chitosan solution, eliminating bubbles, then dropwise adding the mixture into the sodium hydroxide-sodium acetate mixed solution at a certain temperature, continuously reacting for a period of time, and standing and cooling to room temperature after the reaction is finished;
preferably, eliminating bubbles by ultrasonic treatment for 20 min;
preferably, the mixture is added into a sodium hydroxide-sodium acetate mixed solution dropwise at the temperature of 85-95 ℃ for 2h of reaction;
preferably, mixing sodium hydroxide, sodium acetate and deionized water according to a mass ratio of 3:1:60;
washing the obtained product with deionized water until the pH value of the supernatant is neutral, and then freeze-drying the product to obtain a catalyst finished product;
preferably, the mixture is freeze-dried at a temperature of-60 ℃ and a vacuum degree of 20Pa for 12 hours.
The material prepared by the process is spherical, has an internal porous structure, can expose more active sites to activate the peroxymonosulfate to generate free radicals, improves the activity of the catalyst, and has better activation capability than the common peroxymonosulfate/chitosan system.
The main active sites on the peroxymonosulfate/chitosan coated cobalt ferrite microsphere material are provided by Fe and Co metal ions, and the catalyst has higher electron transfer capability. H in the reaction process 2 O molecules are physically adsorbed on the microsphere surface and are combined with metal cations Fe 3+ And Co 2+ Combine to form Fe 3+ -OH and Co 2+ -OH, dissolution of the peroxomonosulphate into the system, SO 4 - The sum OH will be instantaneously formed and the tetracycline oxide will be decomposed into CO 2 And H 2 O. At the same time, high valence metal Co 3+ Can form SO with less contribution to tetracycline degradation 5 - ·;Fe 2+ Can also be combined with surface activitySubstance binding, inducing the formation of reactive oxygen species, then through the Fe formed 3+ The reaction between the substance and the peroxymonosulfate produces more Fe 2+ And reactive free radicals, fe 2+ /Fe 3+ And Co 2+ /Co 3+ The cyclic reaction between them is represented by Fenton-like reaction, and the reversible oxidation and reduction maintains the structure and high-performance activation of cobalt ferrite. Can efficiently catalyze the degradation and removal of the tetracycline in the water body by the persulfates.
The reaction of the chitosan coated cobalt ferrite microsphere in the water body comprises the following steps:
Co 2+ -OH+HSO 5 - →Co 3+ -OH+SO 4 - ·+H 2 O
Fe 3+ -OH+HSO 5 - →Fe 2+ -OH+SO 5 - ·+H +
SO 4 - ·+H 2 O→SO 4 2- +H + +·OH
SO 4 - + & OH+TC- & gtintermediate- & gtCO 2 +H 2 O+SO 4 2-
Co 3+ -OH+HSO 5 - →Co 2+ -OH+SO 5 - ·+H +
Fe 2+ -OH+HSO 5 - →Fe 3+ -OH+SO 4 - ·+H 2 O
The invention has the following effects:
(1) The invention has the advantages that the surface metal ions participate in the reaction in the catalytic reaction process, reversible oxidation-reduction reaction exists in the reaction process, and the reaction is catalyzed by the form of intermediate products, although Fe is generated 2+ And Co 3+ But then consume Fe 2+ And Co 3+ So the reaction process maintains CoFe 2 O 4 Structurally stable and high performance peroxymonosulfate activation.
(2) The three-dimensional network structure of the chitosan coated cobalt ferrite microsphere can better effectively solve the problem of easy agglomeration of cobalt ferrite compared with a layered structure and the like, and provides more active sites, so that the chitosan coated cobalt ferrite microsphere has good catalytic performance.
(3) Meanwhile, the hollow microspheres have stronger magnetism and better magnetic recovery capability; after 5 times of cyclic use, the catalyst still has good catalytic performance, the metal ion precipitation rate is low, and secondary pollution to the water body is avoided; is a material extremely suitable for catalyzing the degradation of the tetracycline by the persulfates, and has better prospect in the field of tetracycline degradation.
Drawings
In order to more clearly illustrate the embodiments of the present invention or the technical solutions in the prior art, the drawings that are required to be used in the embodiments or the description of the prior art will be briefly described below, and it is obvious that the drawings in the following description are only embodiments of the present invention, and that other drawings can be obtained according to the provided drawings without inventive effort for a person skilled in the art.
FIG. 1 is a scanning electron microscope image of a microsphere;
FIG. 2 is an X-ray spectroscopy chart of the microspheres;
FIG. 3 is an X-ray diffraction pattern of microspheres;
FIG. 4 is a graph of magnetic strength of microspheres;
FIG. 5 is a graph of pore size distribution of microspheres;
FIG. 6 is a diagram of a Persulfate (PMS), chitosan-coated cobalt ferrite alone (CS/CoFe) 2 O 4 ) Microsphere, PMS/CS/CoFe 2 O 4 System, PMS/CoFe 2 O 4 And the system and the PMS/CS system degrade the tetracycline effect graph.
Detailed Description
The following description of the embodiments of the present invention will be made clearly and fully with reference to the accompanying drawings, in which it is evident that the embodiments described are only some, but not all embodiments of the invention. All other embodiments, which can be made by those skilled in the art based on the embodiments of the invention without making any inventive effort, are intended to be within the scope of the invention.
The preparation method of the chitosan coated cobalt ferrite microsphere of the following example and comparative example is as follows:
step one, 1g of chitosan was dissolved in 40mL of 2% acetic acid to obtain a chitosan solution, and 0.01M CoCl was added 2 ·6H 2 O and 0.02M FeCl 3 ·6H 2 O is dissolved in 10mL of deionized water to obtain a metal salt solution;
slowly adding the metal salt solution into the chitosan solution, stirring for 30min by using a magnetic stirrer, and eliminating bubbles by ultrasonic treatment for 20 min; then dripping the obtained solution into a sodium hydroxide/sodium acetate mixed solution at the temperature of 90 ℃, standing and cooling to room temperature after the reaction is finished;
the preparation method of the sodium hydroxide/sodium acetate mixed solution comprises the following steps of dissolving 7.5g of sodium hydroxide and 2.45g of sodium acetate in 150ml of deionized water;
and thirdly, washing the product of the step two by deionized water until the pH value of the decanted supernatant is neutral, and then freeze-drying at the temperature of-60 ℃ and the vacuum degree of 20Pa for 12 hours to obtain a finished product.
Example 1
The whole reaction process is kept dark, 200mL of waste water containing tetracycline is poured into a conical flask, and then 0.1g/L chitosan coated cobalt ferrite microsphere and 0.5mmol/L potassium peroxomonosulphonate (PMS/CS/CoFe) are added into the waste water 2 O 4 The system is characterized in that a conical flask is placed in a gas bath constant temperature oscillating box, the set temperature is 25 ℃, the rotating speed is 200r/min, the reaction time is 2h, the final concentration of TC is measured after the reaction is finished, and the initial concentration of TC is 20mg/L.
Comparative example 1
Unlike example 1, this comparative example only added 0.5mmol/L of potassium peroxymonosulphonate to the wastewater, i.e. "PMS alone" system.
Comparative example 2
Unlike example 1, this comparative example only added 0.2g/L of chitosan-coated cobalt ferrite microspheres, i.e. "CS/CoFe alone", to the wastewater 2 O 4 "System".
Comparative example 3
Unlike example 1The comparative example, however, was carried out by adding 0.2g/L cobalt ferrite and 0.5mmol/L potassium peroxomonosulphonate to the wastewater, i.e. "PMS/CoFe 2 O 4 "System".
Comparative example 4
Unlike example 1, this comparative example added 0.2g/L chitosan and 0.5mmol/L potassium peroxymonosulphonate to the wastewater, i.e. "PMS/CS" system.
According to the graph 2, the carbon (C), oxygen (O), iron (Fe) and cobalt (Co) elements in the material prepared by the invention are uniformly distributed, and the material has high purity without doping other elements; as can be seen from FIG. 3, the diffraction peak of the chitosan coated cobalt ferrite microsphere is compared with that of standard CoFe 2 O 4 Correspondingly, the main crystal phase in the microsphere is CoFe 2 O 4 A phase; according to the graph shown in fig. 4, the characterization shows that the microsphere has better magnetic property, and can be recycled through an external magnetic field; as can be seen from fig. 5, the prepared microsphere has compact structure, rich pore channels, larger specific surface area and pore volume, and is beneficial to providing more active sites in the reaction, thereby improving the catalytic performance;
as can be seen from FIG. 6, the "PMS alone" system had a tetracycline degradation rate of 41.5% and "CS/CoFe alone", with reference to TC removal rate 2 O 4 "the tetracycline degradation rate of the system is 1.2%," PMS/CS/CoFe 2 O 4 "the tetracycline degradation rate of the system is 86.4%," PMS/CoFe 2 O 4 The tetracycline degradation rate of the system is 71.7 percent, and the tetracycline degradation rate of the PMS/CS system is 52.6 percent;
in five groups of systems, "PMS/CS/CoFe 2 O 4 The system has the strongest tetracycline degradation capability, namely the chitosan coated cobalt ferrite microsphere and the peroxymonosulfate system.
The previous description of the disclosed embodiments is provided to enable any person skilled in the art to make or use the present invention. Various modifications to these embodiments will be readily apparent to those skilled in the art, and the generic principles defined herein may be applied to other embodiments without departing from the spirit or scope of the invention. Thus, the present invention is not intended to be limited to the embodiments shown herein but is to be accorded the widest scope consistent with the principles and novel features disclosed herein.

Claims (8)

1. A method for treating tetracycline waste water is characterized in that a catalyst and persulphate with a certain proportion are added into the tetracycline waste water for degradation treatment under a dark condition, and the catalyst is chitosan coated cobalt ferrite microspheres.
2. The method for treating tetracycline wastewater as defined in claim 1, wherein 0.1g of catalyst and 0.5mmol of peroxymonosulfate are added per liter of wastewater.
3. A method for preparing the chitosan coated cobalt ferrite microsphere according to claim 1, comprising the following steps:
step one, dissolving chitosan in acetic acid to obtain chitosan solution, and adding CoCl 2 ·6H 2 O and FeCl 3 ·6H 2 O is dissolved in deionized water to obtain a metal salt solution;
uniformly mixing the metal salt solution and the chitosan solution, eliminating bubbles, then dropwise adding the mixture into the sodium hydroxide-sodium acetate mixed solution at a certain temperature, continuously reacting for a period of time, and standing and cooling to room temperature after the reaction is finished;
and thirdly, washing the obtained product by deionized water until the pH value of the supernatant is neutral, and then freeze-drying the product to obtain the finished product of the chitosan coated cobalt ferrite microsphere.
4. A method according to claim 3, wherein in step one, chitosan is mixed with acetic acid having a volume concentration of 2% in m:v (g/ml) =1:40, coCl 2 ·6H 2 O and FeCl 3 ·6H 2 The O molar ratio was 1:2.
5. A process according to claim 3, wherein in step two the reaction is carried out at a temperature of 85-95 ℃ for 2 hours.
6. A production method according to claim 3, wherein sodium hydroxide, sodium acetate and deionized water are mixed in a mass ratio of 3:1:60 to produce a sodium hydroxide-sodium acetate mixed solution.
7. A process according to claim 3, wherein in step three, the mixture is freeze-dried at a temperature of-60 ℃ and a vacuum of 20Pa for 12 hours.
8. A chitosan-coated cobalt ferrite microsphere prepared by the method of any one of claims 3-7.
CN202310563658.2A 2023-05-18 2023-05-18 Catalyst for treating tetracycline wastewater and preparation method and application thereof Active CN116605973B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202310563658.2A CN116605973B (en) 2023-05-18 2023-05-18 Catalyst for treating tetracycline wastewater and preparation method and application thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202310563658.2A CN116605973B (en) 2023-05-18 2023-05-18 Catalyst for treating tetracycline wastewater and preparation method and application thereof

Publications (2)

Publication Number Publication Date
CN116605973A true CN116605973A (en) 2023-08-18
CN116605973B CN116605973B (en) 2024-03-12

Family

ID=87683007

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202310563658.2A Active CN116605973B (en) 2023-05-18 2023-05-18 Catalyst for treating tetracycline wastewater and preparation method and application thereof

Country Status (1)

Country Link
CN (1) CN116605973B (en)

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2020109304A1 (en) * 2018-11-28 2020-06-04 Consejo Superior De Investigaciones Científicas (Csic) Preparation method for preparing a catalyst based on iron nanoparticles, cobalt nanoparticles or alloys thereof, the catalyst thus prepared and use of the catalyst for the selective hydrogenation of carbon dioxide to isobutane
CN112264096A (en) * 2020-11-23 2021-01-26 陕西科技大学 Magnetic Fenton-like catalyst based on chitosan and preparation method and application thereof
CN113145177A (en) * 2021-01-20 2021-07-23 陕西科技大学 Hydrotalcite/chitosan composite spherical catalyst, preparation method and application
CN113209968A (en) * 2021-04-27 2021-08-06 北京工业大学 Preparation method and application of magnetic copper-iron bimetallic biomass carbon microspheres
CN113559909A (en) * 2021-07-27 2021-10-29 陕西科技大学 Magnetic LDO/CN composite catalyst and preparation method and application thereof

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2020109304A1 (en) * 2018-11-28 2020-06-04 Consejo Superior De Investigaciones Científicas (Csic) Preparation method for preparing a catalyst based on iron nanoparticles, cobalt nanoparticles or alloys thereof, the catalyst thus prepared and use of the catalyst for the selective hydrogenation of carbon dioxide to isobutane
CN112264096A (en) * 2020-11-23 2021-01-26 陕西科技大学 Magnetic Fenton-like catalyst based on chitosan and preparation method and application thereof
CN113145177A (en) * 2021-01-20 2021-07-23 陕西科技大学 Hydrotalcite/chitosan composite spherical catalyst, preparation method and application
CN113209968A (en) * 2021-04-27 2021-08-06 北京工业大学 Preparation method and application of magnetic copper-iron bimetallic biomass carbon microspheres
CN113559909A (en) * 2021-07-27 2021-10-29 陕西科技大学 Magnetic LDO/CN composite catalyst and preparation method and application thereof

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
国秋菊等: ""纳米CoFe2O4 颗粒制备及性能研究"", 粉体纳米技术, no. 1, pages 16 - 19 *

Also Published As

Publication number Publication date
CN116605973B (en) 2024-03-12

Similar Documents

Publication Publication Date Title
CN111790422B (en) Graphitized nitrogen-complexed Fe (III) -Fe0Catalyst, and synthesis method and application thereof
CN110302841B (en) Preparation method of foamed nickel supported bimetal MOF-based ozone catalyst, product and application thereof
CN113908878B (en) Preparation method and application of bimetallic Prussian blue analogue catalyst
CN102000573A (en) Modified activated carbon and application thereof
CN112521617B (en) Polyacid-based metal organic framework material for adsorbing antibiotics and preparation method and application thereof
CN113083369B (en) electro-Fenton catalyst derived based on iron-based metal organic framework and preparation method and application thereof
CN108083347B (en) Preparation of cobalt ion induced flower-like cobalt manganese oxide and product and application thereof
CN113426454A (en) Three-dimensional porous graphene loaded nano zero-valent iron/manganese oxide composite material and preparation method and application thereof
CN114272944A (en) Silver phosphate/cobalt tungstate composite acoustic catalytic material and preparation method and application thereof
CN114100638A (en) Preparation method and application of iron-carbon intercalation molybdenum disulfide catalyst
CN106423275A (en) Magnetic composite material used for degrading antibiotics in water through visible light
CN115318300A (en) Preparation method of magnetic biochar with catalytic and specific phosphorus adsorption performances
CN116605973B (en) Catalyst for treating tetracycline wastewater and preparation method and application thereof
CN115445645B (en) Cu 2+1 O@MXene Fenton catalyst and preparation method and application thereof
CN116726934A (en) LDH composite catalytic material and preparation method and application thereof
CN113943041B (en) Method for promoting nano zero-valent iron-manganese bimetallic material to remove organic pollutants in water body
CN114177911B (en) Carbon-supported multi-metal oxide catalyst and preparation method and application thereof
CN112973738B (en) Magnetic self-assembly MoS 2 @Fe 3 O 4 @Cu 2 Preparation method and application of O photocatalyst
CN112657555B (en) Monodisperse Fe-O cluster doped Ni-based metal organic framework composite photocatalyst and preparation method and application thereof
CN111229279B (en) Carbon nitride quantum dot-loaded hierarchical-pore inverse opal structure CuO-SiO 2 Preparation and use thereof
CN108452770B (en) MIL-101 confined ZrO2Phosphorus removal nano-particle adsorbent and preparation method and application thereof
CN111569890A (en) Graphene oxide-terbium oxide-iron oxide composite material, synthetic method and application thereof in catalytic degradation
CN114835171B (en) Preparation method and application of porous nano cobaltosic oxide
CN117680181A (en) Ultra-high-load single-atom copper catalyst and preparation method and application thereof
CN115254084B (en) Preparation method and application of composite catalyst with black material loaded with metal nano particles

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