CN110743591A - Preparation method and application of doped composite catalyst - Google Patents
Preparation method and application of doped composite catalyst Download PDFInfo
- Publication number
- CN110743591A CN110743591A CN201911001362.1A CN201911001362A CN110743591A CN 110743591 A CN110743591 A CN 110743591A CN 201911001362 A CN201911001362 A CN 201911001362A CN 110743591 A CN110743591 A CN 110743591A
- Authority
- CN
- China
- Prior art keywords
- cds
- preparation
- solid
- doped
- temperature
- 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.)
- Pending
Links
- 239000003054 catalyst Substances 0.000 title claims abstract description 46
- 238000002360 preparation method Methods 0.000 title claims abstract description 30
- 239000002131 composite material Substances 0.000 title claims abstract description 25
- KRKNYBCHXYNGOX-UHFFFAOYSA-N citric acid Chemical compound OC(=O)CC(O)(C(O)=O)CC(O)=O KRKNYBCHXYNGOX-UHFFFAOYSA-N 0.000 claims abstract description 57
- 238000000034 method Methods 0.000 claims abstract description 54
- XSQUKJJJFZCRTK-UHFFFAOYSA-N Urea Chemical compound NC(N)=O XSQUKJJJFZCRTK-UHFFFAOYSA-N 0.000 claims abstract description 19
- 239000004202 carbamide Substances 0.000 claims abstract description 19
- 229910000359 iron(II) sulfate Inorganic materials 0.000 claims abstract description 11
- 238000012719 thermal polymerization Methods 0.000 claims abstract description 11
- 238000011068 loading method Methods 0.000 claims abstract description 9
- 238000007654 immersion Methods 0.000 claims abstract description 3
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims description 54
- 239000007787 solid Substances 0.000 claims description 43
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 23
- 238000010438 heat treatment Methods 0.000 claims description 21
- 238000006243 chemical reaction Methods 0.000 claims description 19
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical group [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 17
- 239000008367 deionised water Substances 0.000 claims description 16
- 229910021641 deionized water Inorganic materials 0.000 claims description 16
- 239000000463 material Substances 0.000 claims description 12
- 239000000843 powder Substances 0.000 claims description 12
- 238000001035 drying Methods 0.000 claims description 11
- IXCSERBJSXMMFS-UHFFFAOYSA-N hydrogen chloride Substances Cl.Cl IXCSERBJSXMMFS-UHFFFAOYSA-N 0.000 claims description 11
- 229910000041 hydrogen chloride Inorganic materials 0.000 claims description 11
- 238000001816 cooling Methods 0.000 claims description 10
- 229910052755 nonmetal Inorganic materials 0.000 claims description 10
- 238000000227 grinding Methods 0.000 claims description 9
- JMANVNJQNLATNU-UHFFFAOYSA-N oxalonitrile Chemical compound N#CC#N JMANVNJQNLATNU-UHFFFAOYSA-N 0.000 claims description 9
- 229910052799 carbon Inorganic materials 0.000 claims description 8
- 229910002804 graphite Inorganic materials 0.000 claims description 8
- 239000010439 graphite Substances 0.000 claims description 8
- 239000012535 impurity Substances 0.000 claims description 8
- 238000003756 stirring Methods 0.000 claims description 8
- 238000005406 washing Methods 0.000 claims description 8
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims description 6
- 239000000203 mixture Substances 0.000 claims description 6
- 239000000725 suspension Substances 0.000 claims description 6
- 238000005470 impregnation Methods 0.000 claims description 5
- 239000002096 quantum dot Substances 0.000 claims description 5
- 229910052742 iron Inorganic materials 0.000 claims description 4
- 238000002156 mixing Methods 0.000 claims description 4
- 239000002243 precursor Substances 0.000 claims description 4
- 239000011206 ternary composite Substances 0.000 claims description 4
- 239000011218 binary composite Substances 0.000 claims description 3
- 238000004519 manufacturing process Methods 0.000 claims description 3
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 claims description 3
- 230000007935 neutral effect Effects 0.000 claims description 3
- 239000002904 solvent Substances 0.000 claims description 3
- 150000001875 compounds Chemical class 0.000 claims description 2
- 229920000547 conjugated polymer Polymers 0.000 claims description 2
- 238000001132 ultrasonic dispersion Methods 0.000 claims description 2
- 239000002351 wastewater Substances 0.000 abstract description 11
- 229910021645 metal ion Inorganic materials 0.000 abstract description 6
- 239000007769 metal material Substances 0.000 abstract description 6
- 238000003911 water pollution Methods 0.000 abstract description 5
- 238000007598 dipping method Methods 0.000 abstract description 2
- 230000000379 polymerizing effect Effects 0.000 abstract description 2
- XEEYBQQBJWHFJM-UHFFFAOYSA-N iron Substances [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 49
- 239000000243 solution Substances 0.000 description 17
- 230000003197 catalytic effect Effects 0.000 description 8
- 230000015556 catabolic process Effects 0.000 description 7
- 238000006731 degradation reaction Methods 0.000 description 7
- 230000003647 oxidation Effects 0.000 description 7
- 238000007254 oxidation reaction Methods 0.000 description 7
- 230000007547 defect Effects 0.000 description 5
- 230000001699 photocatalysis Effects 0.000 description 5
- RBTBFTRPCNLSDE-UHFFFAOYSA-N 3,7-bis(dimethylamino)phenothiazin-5-ium Chemical compound C1=CC(N(C)C)=CC2=[S+]C3=CC(N(C)C)=CC=C3N=C21 RBTBFTRPCNLSDE-UHFFFAOYSA-N 0.000 description 4
- 230000000694 effects Effects 0.000 description 4
- 229960000907 methylthioninium chloride Drugs 0.000 description 4
- 238000007146 photocatalysis Methods 0.000 description 4
- 239000010802 sludge Substances 0.000 description 4
- 238000001179 sorption measurement Methods 0.000 description 4
- CWYNVVGOOAEACU-UHFFFAOYSA-N Fe2+ Chemical compound [Fe+2] CWYNVVGOOAEACU-UHFFFAOYSA-N 0.000 description 3
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 3
- 238000009303 advanced oxidation process reaction Methods 0.000 description 3
- 230000015572 biosynthetic process Effects 0.000 description 3
- 238000005516 engineering process Methods 0.000 description 3
- 230000007613 environmental effect Effects 0.000 description 3
- 229910001448 ferrous ion Inorganic materials 0.000 description 3
- 229910052739 hydrogen Inorganic materials 0.000 description 3
- 239000001257 hydrogen Substances 0.000 description 3
- 238000005286 illumination Methods 0.000 description 3
- 238000011065 in-situ storage Methods 0.000 description 3
- 239000011148 porous material Substances 0.000 description 3
- 239000000047 product Substances 0.000 description 3
- 238000003786 synthesis reaction Methods 0.000 description 3
- 238000003917 TEM image Methods 0.000 description 2
- 239000007864 aqueous solution Substances 0.000 description 2
- 239000002585 base Substances 0.000 description 2
- 150000001721 carbon Chemical class 0.000 description 2
- 238000000354 decomposition reaction Methods 0.000 description 2
- 238000005265 energy consumption Methods 0.000 description 2
- 239000013505 freshwater Substances 0.000 description 2
- 230000036541 health Effects 0.000 description 2
- 231100000572 poisoning Toxicity 0.000 description 2
- 230000000607 poisoning effect Effects 0.000 description 2
- 238000011160 research Methods 0.000 description 2
- 238000004627 transmission electron microscopy Methods 0.000 description 2
- 238000005303 weighing Methods 0.000 description 2
- 239000002253 acid Substances 0.000 description 1
- 230000004913 activation Effects 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 230000033558 biomineral tissue development Effects 0.000 description 1
- 238000006555 catalytic reaction Methods 0.000 description 1
- 238000012512 characterization method Methods 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 239000000356 contaminant Substances 0.000 description 1
- 230000018109 developmental process Effects 0.000 description 1
- 239000003814 drug Substances 0.000 description 1
- 229940079593 drug Drugs 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- TUJKJAMUKRIRHC-UHFFFAOYSA-N hydroxyl Chemical compound [OH] TUJKJAMUKRIRHC-UHFFFAOYSA-N 0.000 description 1
- 239000013067 intermediate product Substances 0.000 description 1
- 230000007246 mechanism Effects 0.000 description 1
- 150000004706 metal oxides Chemical class 0.000 description 1
- 231100000956 nontoxicity Toxicity 0.000 description 1
- 230000005693 optoelectronics Effects 0.000 description 1
- 239000007800 oxidant agent Substances 0.000 description 1
- 230000001590 oxidative effect Effects 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 238000004321 preservation Methods 0.000 description 1
- 230000005855 radiation Effects 0.000 description 1
- 150000003254 radicals Chemical class 0.000 description 1
- 230000008929 regeneration Effects 0.000 description 1
- 238000011069 regeneration method Methods 0.000 description 1
- 238000000870 ultraviolet spectroscopy Methods 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
Images
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J27/00—Catalysts comprising the elements or compounds of halogens, sulfur, selenium, tellurium, phosphorus or nitrogen; Catalysts comprising carbon compounds
- B01J27/24—Nitrogen compounds
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B3/00—Hydrogen; Gaseous mixtures containing hydrogen; Separation of hydrogen from mixtures containing it; Purification of hydrogen
- C01B3/02—Production of hydrogen or of gaseous mixtures containing a substantial proportion of hydrogen
- C01B3/04—Production of hydrogen or of gaseous mixtures containing a substantial proportion of hydrogen by decomposition of inorganic compounds, e.g. ammonia
- C01B3/042—Decomposition of water
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/722—Oxidation by peroxides
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/725—Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B2203/00—Integrated processes for the production of hydrogen or synthesis gas
- C01B2203/02—Processes for making hydrogen or synthesis gas
- C01B2203/0266—Processes for making hydrogen or synthesis gas containing a decomposition step
- C01B2203/0277—Processes for making hydrogen or synthesis gas containing a decomposition step containing a catalytic decomposition step
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B2203/00—Integrated processes for the production of hydrogen or synthesis gas
- C01B2203/10—Catalysts for performing the hydrogen forming reactions
- C01B2203/1041—Composition of the catalyst
- C01B2203/1047—Group VIII metal catalysts
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/308—Dyes; Colorants; Fluorescent agents
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
- C02F2101/40—Organic compounds containing sulfur
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E60/00—Enabling technologies; Technologies with a potential or indirect contribution to GHG emissions mitigation
- Y02E60/30—Hydrogen technology
- Y02E60/36—Hydrogen production from non-carbon containing sources, e.g. by water electrolysis
Landscapes
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Engineering & Computer Science (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Health & Medical Sciences (AREA)
- Combustion & Propulsion (AREA)
- Inorganic Chemistry (AREA)
- General Health & Medical Sciences (AREA)
- Materials Engineering (AREA)
- Catalysts (AREA)
Abstract
The invention discloses a preparation method and application of a doped composite catalyst. The method is a preparation method of a non-metallic material CN/CDs and metal ion Fe (II) doped composite catalyst, and the CN/CDs are prepared firstly, then the Fe (II) is doped, and CN/CD is obtained by an immersion method3/Fe6A catalyst. Wherein CN/CDxThe loading amounts of CDs synthesized by the thermal polymerization method were 0.5 wt%, 1 wt%, 2 wt%, 3 wt%, 4 wt%, 5 wt%, 6 wt%, respectively. Fe (II) is loaded on CN/CD by dipping method3Above, it is recorded as CN/CD3/Fe6. Then a series of Fe (II) with different concentrations are dopedHetero in CN/CD3Preparation of CN/CD3/FeyComposite materials (y is 3, 4, 5, 6), y is FeSO4Initial concentration of solution fe (ii). The invention also discloses CN/CD3/Fe6The preparation method of the catalyst comprises the steps of preparing CN, preparing CDs, and thermally polymerizing urea and citric acid to obtain CN/CDxFinally, Fe (II) is doped in CN/CD3And (4) finishing. The method has simple process, can realize the high-efficiency removal of the dye wastewater, is easy to regenerate, and has good industrial application prospect in the aspect of water pollution treatment.
Description
Technical Field
The invention relates to the technical field of catalytic materials, in particular to a preparation method and application of a non-metallic material CN/CDs and metal ion Fe (II) doped composite catalyst.
Background
In recent years, the average annual average worldwide is about 4200 hundred million m3The polluted wastewater is discharged to rivers, lakes and seas. Pollute nearly 5.5 trillion m3The human body can drink fresh water, which is equivalent to about 14 percent of the total runoff of the whole world. Water pollution poses serious harm to the health of people. The Fenton reaction is one of Advanced Oxidation Processes (AOPs), which generally uses less energy than direct Oxidation and the reaction principle is to generate highly reactive free radical molecules, the most common of which is hydroxyl radical (HO.), a very reactive species with a rate constant of 10 for attacking most organic molecules6-109Lmol-1s-1In the range, the Fenton oxidation method has the advantages of wide application range, strong anti-interference capability, simple operation, degradation and mineralization and the like, thereby being the most popular AOPs at present.
The traditional Fenton oxidation method is limited by the pH value range and has the defects of large iron sludge amount, and the graphite phase carbon nitride (g-C)3N4) Is a non-metal visible light catalytic material, and is widely applied in the fields of environmental protection, wastewater treatment and the like. Due to its physics and chemistryThe material has the advantages of stable property, environmental friendliness and low cost, can exist in acid-base solution, and is considered to be a photocatalytic material with good development prospect. Can be used for illumination production H2、CO2Reduction and degradation of organic contaminants. CDs, which have been found to have been developed for over a decade in 2004, have been widely used in the fields of sensors, photocatalytic water splitting and light emitting diodes, etc. due to their excellent optoelectronic properties, non-toxicity and good biocompatibility.
CDs can be H so far2O2The composite material synthesized by CN/CDs can be used for H without illumination2O2Decompose to generate HO, and calculate H2O2Decomposition of H under the system of/CN/CDs2O2Has a reaction rate constant greater than that of a series of non-metal oxides, and has a low activation energy. The composite material pair H2O2Has high selectivity, forms an adsorption catalysis double site by catalyzing CDs on the adsorption site, and can solve the problem of g-C3N4H generated in situ in the photocatalytic direction2O2Poisoning problems, so that higher energy conversion efficiency can be obtained.
In many researches, metal ions and nonmetal catalytic materials are coupled to improve the catalytic performance of the materials, a reaction principle different from a photocatalysis mechanism is selected, a homogeneous Fenton method and a Fenton-like method are combined under the condition of not depending on external energy input of illumination radiation or ultrasonic waves, and a novel catalytic method which is low in energy consumption, low in cost and environment-friendly is formed under the condition of additionally adding an oxidant.
Disclosure of Invention
The technical problem to be solved by the invention is as follows: in order to overcome the defects of the technology, a preparation method and application of a non-metal material CN/CDs and metal ion Fe (II) doped composite catalyst which has low energy consumption, low cost and environmental protection are provided.
The invention adopts the following technical scheme for solving the technical problems:
the invention combines the traditional Fenton method with a non-metal catalyst, overcomes the defects of the Fenton method and the similar Fenton method, and adopts the method in H2O2The method is applied to the field of treating organic dye wastewater. The graphite phase carbon nitride can adsorb H in the solution2O2The carbon sites on the support and Fe (II) may be such that H2O2The composite material prepared by the principle solves the problem of H generated in situ by photocatalysis2O2The difficult problem of poisoning CN can be achieved, and simultaneously, higher conversion efficiency can be obtained. In addition, the insoluble composite material can generate HO under acid and alkali conditions, and can perform non-selective oxidation on the dye wastewater, thereby avoiding the problems of sludge generation and the like under pH value and alkaline conditions in the conventional oxidation technology. CN/CD prepared in addition3/Fe6Low material price, wide application range, strong catalytic degradation effect and the like.
The invention discloses a preparation method of a doped composite catalyst, which is a preparation method of a non-metallic material CN/CDs and a metal ion Fe (II) doped composite catalyst3/Fe6A catalyst.
The catalyst is prepared by taking a conjugated polymer non-metal framework material CN with a graphite structure as a carrier and CDs and Fe (II) as active components; wherein CDs are loaded on the carrier by a thermal polymerization method with citric acid as a carbon source, the loading amounts are respectively 0.5-6 wt%, and Fe (II) is doped in CN/CDs by an immersion method, the doping amounts are respectively 3-6 mM; the compound of Fe (II) is FeSO4The solvent used in the impregnation method is water.
The invention also discloses a preparation method of the non-metallic material CN/CDs and metal ion Fe (II) doped composite catalyst, which comprises the following steps:
(1)g-C3N4preparing;
(2) preparing CDs;
(3)g-C3N4preparation of/CDs;
(4)CN/CD3/Fe6and (4) preparing.
The method specifically comprises the following steps:
(1)g-C3N4the preparation of (1):
and putting the urea into a crucible, putting the urea into a muffle furnace together for heating, naturally cooling, and taking out to obtain a light yellow solid. And then, respectively cleaning the obtained solid once by using deionized water, HCl, NaOH and deionized water to remove impurities on the surface of the solid. Finally, the obtained sample is placed in a drying box to be heated to obtain a dried solid, and the dried solid is ground to obtain light yellow powder which is recorded as CN;
(2) preparing CDs;
4g of citric acid is poured into the crucible, and then the crucible is placed into a muffle furnace to be heated to a certain temperature and kept for a period of time. Cooling to room temperature gave an orange solid noted as CDs, which was dissolved with NaOH solution and then pH adjusted to neutral with NaOH to give CDs solution.
(3) Preparation of CN/CDs:
citric acid is taken as a precursor of the carbon dots, and a similar thermal polymerization method is adopted to prepare the carbon nanodot/graphite phase carbon nitride. The method comprises the following steps: taking x as an example, citric acid and urea are uniformly mixed and put into a crucible, the crucible and the mixture are put into a muffle furnace to be heated, and then the mixture is naturally cooled and taken out to obtain a black solid. And then washing the obtained black solid with deionized water, HCl and NaOH respectively, and then washing once with the deionized water to remove impurities on the surface of the solid. Heating the obtained sample in a drying oven to obtain dried solid, grinding to obtain black powder, and recording as CN/CD3. Preparation of a series of CN/CD with different contentsx(x ═ 1, 2, 3, 4, 5, 6), where x is the initial mass ratio of citric acid to urea;
(4)CN/CD3/Fe6the preparation of (1):
the preparation of the Fe (II) modified carbon nano-dot/graphite phase carbon nitride ternary composite material adopts a synthesis step of an impregnation method. The specific method is to prepare the CN/CD3Binary composite material in FeSO4The solution is stirred evenly. Ultrasonically dispersing the suspension, heating and stirring until the suspension is dried, and grinding the obtained sample into powderFinally, it is recorded as CN/CD3/Fe6. Followed by preparation of a series of Fe (II) -doped CN/CD with different concentrations3/FeyTernary composites (y ═ 3, 4, 5, 6) in which y is FeSO4Initial concentration of solution fe (ii).
Preferably, in the step (1), the precursor of CN is urea, and the synthesis is performed by a thermal polymerization method. The reaction conditions are as follows: raising the temperature to 600 ℃ at the speed of 1 ℃/min, and preserving the temperature for 3 h. Too low a temperature or too short a time may affect the product, and higher yields may be achieved under the preferred reaction conditions.
Further preferably, the concentrations of HCl and NaOH are 0.1 mol/L.
Preferably, in the step (1), after the thermal polymerization, the temperature in the muffle furnace is slowly cooled to room temperature at a cooling rate of 1 ℃/min.
In the step (2), the temperature in the muffle furnace cannot exceed 200 ℃, and the heat preservation time cannot be less than 30 min.
In the step (3), the mass ratio of the citric acid to the urea is 1:200, 1:100, 1:50, 3:100, 1:25 and 3:50 respectively.
The volume of the CN pore channel is limited, and in order to increase the specific surface area of the CN, the invention adopts a thermal polymerization method to load CDs on the surface of the CN, so that the specific surface area and the pore size of the CN can be increased, and the adsorption capacity is enhanced.
FeSO4The aqueous solution of (A) should not be heated too fast, CN/CD3And ferrous ion water solution is loaded into the pore canal, and the water solution and the ferrous ion water solution are well dispersed by an ultrasonic disperser. And then, ensuring that the stirring speed is not too fast or too slow, the ferrous ion aqueous solution cannot be well dispersed, the contact area is small, preferably, the stirring speed is 400r/min, the reaction temperature is 60 ℃, and the drying time is 6-7 hours.
The prepared catalyst preferably has the Fe (II) loading of 6mM, and the catalyst at the loading has the best effect on the degradation of the dye.
The invention discloses the application of the catalyst in organic dye; the using conditions of the catalyst are as follows: the temperature was 25 ℃. Preferably, the catalyst prepared by the invention is more suitable for treating organic wastewater. Especially under the condition of normal temperature, such as 25 ℃, the conversion rate of the catalyst prepared by the invention to methylene blue is as high as 100%.
After the catalyst is used, the catalyst is washed and centrifuged by using a volatile solvent, a product and an intermediate product attached to the catalyst are washed off, and then the catalyst is heated to 50-80 ℃ in a vacuum state and kept for 5-6 hours to realize regeneration.
Compared with the prior art, the invention has the following outstanding technical effects:
1. the traditional Fenton method has very high requirements on pH, can generate iron sludge and cannot be popularized in a large range. Therefore, the invention combines the traditional Fenton method with a non-metal catalyst, overcomes the defects of the traditional Fenton method, and adopts the method in H2O2The method is applied to the field of treating organic dye wastewater.
2. The graphite phase carbon nitride can adsorb H in the solution2O2The carbon sites on the support and Fe (II) may be such that H2O2The composite material prepared by the principle solves the problem of H generated in situ by photocatalysis2O2The difficult problem of poisoning CN can be achieved, and simultaneously, higher conversion efficiency can be obtained.
3. The insoluble composite material can generate HO & lt- & gt under acid-base conditions, and can perform non-selective oxidation on the dye wastewater, thereby avoiding the problems of sludge generation and the like under the conditions of pH value and alkalinity of the conventional oxidation technology. CN/CD prepared in addition3/Fe6Low material price, wide application range, strong catalytic degradation effect and the like.
CN/CD prepared by the invention3/Fe6The catalyst has strong catalytic action on organic dye wastewater, and can show 100% conversion rate at lower temperature. Compare CN/CD3The degradation rate of the dye is greatly improved.
Description of the drawings:
FIG. 1 shows CN, CN/CD prepared in examples 1, 2 and 43And CN/CD3/Fe6Infrared profiles of the three materials;
FIG. 2 shows CN, CN/CD prepared in examples 1 and 43/Fe6Transmission electron microscopy images of (a). In FIG. 2, A is a transmission electron micrograph of CN, B is a transmission electron micrograph of CN, and C is CN/CD3/Fe6D is CN/CD3/Fe6E is CN/CD3/Fe6F is CN/CD3/Fe6Transmission electron microscopy images of (a).
FIG. 3 shows CN, CN/CD prepared in examples 1, 2 and 43And CN/CD3/Fe6Adsorption isotherms of the three materials;
FIG. 4 shows CN, CDs and CN/CD prepared in examples 1, 2, 3 and 43/Fe6And CN/CD with different loading amountsxXRD characterization pattern of (a).
Detailed Description
The invention discloses a non-metal material CN/CDs and Fe (II) doped composite catalyst, which combines the traditional Fenton method and the non-metal catalyst to overcome the defects of the traditional Fenton method and synthesizes CN/CD by a thermal polymerization methodxThe loading amounts of CDs were 0.5 wt%, 1 wt%, 2 wt%, 3 wt%, 4 wt%, 5 wt%, 6 wt%, respectively. Fe (II) is loaded on CN/CD by dipping method3Above, it is recorded as CN/CD3/Fe6. Then a series of Fe (II) with different concentrations are doped in CN/CD3Preparation of CN/CD3/FeyComposite materials (y ═ 3, 4, 5, 6), where y is FeSO4Initial concentration of solution fe (ii).
The invention also discloses the CN/CD3/Fe6The preparation method of the catalyst comprises the following steps: firstly preparing CN, then preparing CDs, then thermal polymerizing urea and citric acid to obtain CN/CDxFinally, Fe (II) is doped in CN/CD3Obtaining the catalyst CN/CD3/Fey. The catalyst has simple preparation process and mild condition, can realize the high-efficiency removal of the dye wastewater, is easy to regenerate, and has good industrial application in the aspect of water pollution treatmentAnd (4) foreground.
The following examples further illustrate the invention, but the content of the invention is not limited thereto at all.
Example 1
(1)g-C3N4The preparation of (1):
g-C3N4the preparation method comprises the following steps of weighing 50g of urea, putting the urea into a crucible, putting the urea into a muffle furnace together, heating to 600 ℃ at the speed of 1 ℃/min, preserving heat for 3h, naturally cooling, and taking out to obtain a light yellow solid. And then sequentially washing the obtained solid with deionized water, 0.1mol/L HCl, 0.1mol/L NaOH and deionized water once respectively to remove impurities on the surface of the solid. And finally, putting the obtained sample in a drying oven to be heated for 2 hours at the heating temperature of 100 ℃ to obtain a dried solid, and manually grinding the dried solid to obtain light yellow powder which is recorded as CN.
(2) Preparing CDs;
pouring 4g of citric acid into a crucible, then putting the crucible into a muffle furnace to heat to 200 ℃, wherein the heating rate is 5 ℃/min, and keeping the temperature for 40 min. Cooling to room temperature gave an orange solid noted CDs, which was dissolved in 10g/L NaOH solution and then adjusted to neutral pH with NaOH to give a CDs solution.
(3) Preparation of CN/CDs:
citric acid is taken as a precursor of the carbon dots, and a similar thermal polymerization method is adopted to prepare the carbon nanodot/graphite phase carbon nitride. The specific method comprises the steps of uniformly mixing 1.5g of citric acid and 50g of urea, putting the mixture into a crucible, putting the crucible and the mixture into a muffle furnace, heating to 600 ℃ at the speed of 1 ℃/min, preserving the temperature for 3 hours, naturally cooling, and taking out to obtain a black solid. And then sequentially washing the obtained solid with deionized water, 0.1mol/L HCl, 0.1mol/L NaOH and deionized water once respectively to remove impurities on the surface of the solid. Finally, the obtained sample is placed in a drying oven to be heated for 2 hours at the heating temperature of 100 ℃ to obtain a dried solid, and the dried solid is manually ground to obtain black powder, namely CN/CD with the load of 3wt percent3。
(4)CN/CD3/Fe4The preparation of (1):
the preparation of the Fe (II) modified carbon nano-dot/graphite phase carbon nitride ternary composite material adopts a synthesis step of an impregnation method. The specific method is to prepare the CN/CD3Weighing 0.4g of binary composite material, and adding into 100mL of 4mM FeSO4The solution is stirred evenly. Ultrasonically dispersing the suspension for 25min, heating and stirring at 60 deg.C until drying, manually grinding the obtained sample into powder to obtain CN/CD with 4mM loading3/Fe4。
The degradation rate of the catalyst prepared by the embodiment to methylene blue can reach 100% under atmospheric pressure by using an ultraviolet-visible spectrophotometer method for testing.
Example 2
(1)CN/CD3The load of (2):
taking 50g of urea and 1.5g of citric acid, uniformly mixing, putting into a crucible, putting into a muffle furnace together, heating to 600 ℃ at the speed of 1 ℃/min, preserving heat for 3h, naturally cooling, and taking out to obtain a black solid. And then sequentially washing the obtained solid with deionized water, 0.1mol/L HCl, 0.1mol/L NaOH and deionized water once respectively to remove impurities on the surface of the solid. Finally, the obtained sample is placed in a drying oven to be heated at the temperature of 100 ℃ for 2 hours to obtain a dried solid, and the dried solid is manually ground to obtain black powder, namely CN/CD with the load of 3 wt%3。
(2)CN/CD3/Fe5The load of (2):
the obtained CN/CD30.4g of the suspension was weighed into a container and 100ml of 5mM FeSO was added4Ultrasonically dispersing the solution for 25min, heating and stirring at 60 deg.C until drying, manually grinding the obtained sample into powder to obtain CN/CD with a loading of 5mM3/Fe5。
The conversion of methylene blue by the catalyst prepared in this example was 100% at atmospheric pressure as measured by uv-vis spectrophotometer.
Example 3
(1)CN/CD3The load of (2):
taking 50g of urea and 1.5g of citric acid, uniformly mixing, putting into a crucible, putting into a muffle furnace together, heating to 600 ℃ at the speed of 1 ℃/min, preserving heat for 3h, naturally cooling, and taking out to obtain a black solid. And then sequentially washing the obtained solid with deionized water, 0.1mol/L HCl, 0.1mol/L NaOH and deionized water once respectively to remove impurities on the surface of the solid. Finally, the obtained sample is placed in a drying oven to be heated at the temperature of 100 ℃ for 2 hours to obtain a dried solid, and the dried solid is manually ground to obtain black powder, namely CN/CD with the load of 3 wt%3。
(2)CN/CD3/Fe6The load of (2):
the obtained CN/CD30.4g of the suspension was weighed into a container, and 100ml of 6mM FeSO was added4Performing ultrasonic dispersion on the solution for 25min, heating and stirring at 60 ℃ until the solution is dried, manually grinding the obtained sample, and grinding into powder to obtain CN/CD with the load of 6mM3/Fe6。
The conversion of methylene blue by the catalyst prepared in this example was 100% at atmospheric pressure as measured by uv-vis spectrophotometer.
Application example 1 Water pollution treatment
The average annual worldwide is about 4200 hundred million m3The polluted wastewater is discharged to rivers, lakes and seas. Pollute nearly 5.5 trillion m3The amount of the potable fresh water is about 14 percent of the total amount of the global runoff. Water pollution poses serious harm to the health of people.
CN/CD prepared by the invention3/Fe6The catalyst can be used for catalyzing and decomposing pollutants in water such as dye wastewater, medicines and personal care products, and the conversion rate can reach 100%.
Application example 2 photocatalytic hydrogen production
At present, the world energy is in short supply, and hydrogen is used as a novel clean energy, so that the emission can be reduced, the dependence on fossil energy is reduced, and great research significance is realized.
CN/CD prepared by the invention3/Fe6The catalyst can be inCatalytic decomposition of H in the field of photocatalysis2O produces hydrogen.
Claims (10)
1. A process for preparing the doped composite catalyst includes such steps as preparing CN/CDs, doping Fe (II), and immersing to obtain said CN/CD3/Fe6A catalyst.
2. The preparation method of the doped composite catalyst according to claim 1, wherein the catalyst is prepared by taking a conjugated polymer non-metal framework material CN with a graphite structure as a carrier and CDs and Fe (II) as active components; wherein CDs are loaded on the carrier by a thermal polymerization method with citric acid as a carbon source, the loading amounts are respectively 0.5-6 wt%, and Fe (II) is doped in CN/CDs by an immersion method, the doping amounts are respectively 3-6 mM; the compound of Fe (II) is FeSO4The solvent used in the impregnation method is water.
3. The preparation method of the doped composite catalyst according to claim 2, wherein the urea is put into a crucible, put into a muffle furnace together for heating, then naturally cooled, and taken out to obtain a light yellow solid; then, sequentially washing the obtained solid by using deionized water, HCl, NaOH and deionized water once respectively to remove impurities on the surface of the solid; finally, the obtained sample is placed in a drying oven to be heated to obtain a dried solid, and the dried solid is ground to obtain light yellow powder g-C3N4And is referred to as CN.
4. The method for preparing the doped composite catalyst according to claim 3, wherein the amount of the urea is 50g, the concentrations of HCl and NaOH are 0.1mol/L, and the heating reaction conditions are as follows: raising the temperature to 600 ℃ at the speed of 1 ℃/min, and preserving the temperature for 3 h.
5. The method of claim 2, wherein the CDs are prepared by the following method; pouring 4g of citric acid into a crucible, then placing the crucible into a muffle furnace, heating the crucible to a certain temperature, keeping the temperature for a period of time, then cooling the crucible to room temperature to obtain orange solids, recording the orange solids as CDs, dissolving the solid CDs by using a NaOH solution, and finally adjusting the pH value to be neutral by using NaOH to obtain a CDs solution.
6. The method for preparing the doped composite catalyst of claim 5, wherein the concentration of NaOH is 10g/L, and the heating reaction conditions are as follows: raising the temperature to 200 ℃ at the speed of 5 ℃/min, and preserving the temperature for 40 min.
7. The method of claim 2, wherein CN/CDs is prepared by the following method;
the preparation method of the carbon nanodot/graphite phase carbon nitride by using citric acid as a precursor of the carbon dots and adopting a thermal polymerization method comprises the following steps: taking x as an example, uniformly mixing citric acid and urea, putting the mixture into a crucible, putting the crucible and the mixture into a muffle furnace, heating, naturally cooling, and taking out to obtain a black solid; then, sequentially washing the obtained solid by using deionized water, HCl, NaOH and deionized water once respectively to remove impurities on the surface of the solid; heating the obtained sample in a drying oven to obtain dried solid, and grinding to obtain black powder which is binary composite material CN/CD3;
Finally, a series of CN/CD with different contents are prepared by a thermal polymerization methodxAnd x is 1, 2, 3, 4, 5 and 6, and x is the initial mass ratio of the citric acid to the urea.
8. The method for preparing the doped composite catalyst of claim 7, wherein the amount of urea is 50g, the amount of citric acid is 1.5g, the concentrations of HCl and NaOH are 0.1mol/L, and the heating reaction conditions are as follows: raising the temperature to 600 ℃ at the speed of 1 ℃/min, and preserving the temperature for 3 h.
9. The method for preparing the doped composite catalyst according to claim 2, wherein the CN/CD is synthesized by the following impregnation method3/Fe6: the CN/CD prepared by the method of claim 73In FeSO4Uniformly stirring the solution, and grinding a sample obtained after ultrasonic dispersion and heating and stirring for 6-7 hours till the sample is dried into powder which is CN/CD3/Fe6(ii) a Followed by preparation of a series of Fe (II) -doped CN/CD with different concentrations3/FeyTernary composite materials, y being 3, 4, 5, 6, where y is FeSO4Initial concentration of solution fe (ii).
10. The method of claim 9, wherein the CN/CD is a CD catalyst30.4g, FeSO4The solution is 100mL of 6mM, and the reaction conditions are as follows: the suspension is ultrasonically dispersed for 25min and heated and stirred at 60 ℃.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201911001362.1A CN110743591A (en) | 2019-10-21 | 2019-10-21 | Preparation method and application of doped composite catalyst |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201911001362.1A CN110743591A (en) | 2019-10-21 | 2019-10-21 | Preparation method and application of doped composite catalyst |
Publications (1)
Publication Number | Publication Date |
---|---|
CN110743591A true CN110743591A (en) | 2020-02-04 |
Family
ID=69279127
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201911001362.1A Pending CN110743591A (en) | 2019-10-21 | 2019-10-21 | Preparation method and application of doped composite catalyst |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN110743591A (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN113603182A (en) * | 2021-08-17 | 2021-11-05 | 武汉理工大学 | Method for degrading organic pollutants in water by catalyst and ionizing radiation |
CN116162454A (en) * | 2022-12-21 | 2023-05-26 | 江苏瀚彩新材料有限公司 | High ECL efficiency oxazine ring functionalized carbon dot and preparation method and application thereof |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108772090A (en) * | 2018-05-30 | 2018-11-09 | 上海交通大学 | The g-C of iron-based quantum dot modification3N4It can be seen that optical drive class fenton catalyst |
CN108993561A (en) * | 2018-05-24 | 2018-12-14 | 广东工业大学 | A kind of carbon dots modification oxygen doping carbon nitride photocatalyst and its preparation method and application |
-
2019
- 2019-10-21 CN CN201911001362.1A patent/CN110743591A/en active Pending
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108993561A (en) * | 2018-05-24 | 2018-12-14 | 广东工业大学 | A kind of carbon dots modification oxygen doping carbon nitride photocatalyst and its preparation method and application |
CN108772090A (en) * | 2018-05-30 | 2018-11-09 | 上海交通大学 | The g-C of iron-based quantum dot modification3N4It can be seen that optical drive class fenton catalyst |
Non-Patent Citations (1)
Title |
---|
LIJUAN FANG: "Degradation Mechanism of Methylene Blue by H2O2 and Synthesized Carbon Nanodots/Graphitic Carbon Nitride/Fe(II) Composite", 《THE JOURNAL OF PHYSICAL CHEMISTRY》 * |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN113603182A (en) * | 2021-08-17 | 2021-11-05 | 武汉理工大学 | Method for degrading organic pollutants in water by catalyst and ionizing radiation |
CN116162454A (en) * | 2022-12-21 | 2023-05-26 | 江苏瀚彩新材料有限公司 | High ECL efficiency oxazine ring functionalized carbon dot and preparation method and application thereof |
CN116162454B (en) * | 2022-12-21 | 2024-02-13 | 江苏瀚彩新材料有限公司 | High ECL efficiency oxazine ring functionalized carbon dot and preparation method and application thereof |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
Hasanpour et al. | Photocatalytic performance of aerogels for organic dyes removal from wastewaters: Review study | |
CN105110423B (en) | Carbon-aerogel-carried bimetal organic framework electro-Fenton cathode and preparation method thereof | |
Huang et al. | Novel Au@ C modified g-C3N4 (Au@ C/g-C3N4) as efficient visible-light photocatalyst for toxic organic pollutant degradation: Synthesis, performance and mechanism insight | |
Du et al. | π-π conjugation driving degradation of aromatic compounds with in-situ hydrogen peroxide generation over Zn2In2S5 grown on nitrogen-doped carbon spheres | |
CN102000573B (en) | Modified activated carbon and application thereof | |
Luo et al. | Facile synthesis of PVDF photocatalytic membrane based on NCQDs/BiOBr/TiO2 heterojunction for effective removal of tetracycline | |
CN112044367B (en) | Cobalt-manganese hydrotalcite aerogel and preparation method and application thereof | |
CN109675607A (en) | Fe3O4The preparation method of@ZnO@N-C composite photocatalyst material | |
Jiang et al. | New and highly efficient Ultra-thin g-C3N4/FeOCl nanocomposites as photo-Fenton catalysts for pollutants degradation and antibacterial effect under visible light | |
Zhou et al. | TiO2 nanotube arrays sensitized by copper (II) porphyrins with efficient interfacial charge transfer for the photocatalytic degradation of 4-nitrophenol | |
CN110756215A (en) | CoP-HCCN composite photocatalyst and preparation method and application thereof | |
CN110743591A (en) | Preparation method and application of doped composite catalyst | |
CN115845888B (en) | PbBiO2Br/Ti3C2Preparation method of composite catalyst and application of composite catalyst in photocatalytic degradation of methyl orange | |
CN106362742A (en) | Ag/ZnO nano-composite, preparation method thereof and application of composite | |
CN103272647B (en) | A kind of preparation method for dye decolored cellulose base ZnO-CdS composite photo-catalyst | |
CN111111734B (en) | Preparation and application of ferrous disulfide/carbon nitride composite photocatalyst | |
CN113231059A (en) | Composite catalyst for electron beam sewage treatment and preparation method and application thereof | |
CN113617366A (en) | Material for degrading organic pollutants in wastewater | |
Ali et al. | Effective removal of organic compounds using a novel cellulose acetate coated by PA/g-CN/Ag nanocomposite membranes | |
CN112169798A (en) | Catalyst with collagen-based carbon material loaded with metal cobalt and preparation method and application thereof | |
CN116603527A (en) | Preparation of biochar-supported cobalt-iron layered bimetallic oxide catalyst and application of catalyst in advanced oxidation | |
Wen et al. | Utilizing three-dimensional ordered macroporous NiFe2O4 Loaded With g-C3N4 as a heterogeneous photo-Fenton catalyst for tetracycline degradation | |
Zhang et al. | Integration between CuMOF and g-C3N4 for effective suppressing charge recombination in photocatalytic peroxymonosulfate activation | |
CN108940349B (en) | Method for removing dye pollutants by using silver chromate/sulfur-doped nitrogen carbon Z-type photocatalyst | |
Chen et al. | In situ growing Cu2 (OH) 2CO3 on oxidized carbon nitride with enhanced photocatalytic hydrogen evolution and pollutant degradation |
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 | ||
RJ01 | Rejection of invention patent application after publication | ||
RJ01 | Rejection of invention patent application after publication |
Application publication date: 20200204 |