CN112958139A - Preparation of CNK-OH/ferroferric oxide composite material and application of CNK-OH/ferroferric oxide composite material in photocatalytic degradation of tetracycline hydrochloride - Google Patents
Preparation of CNK-OH/ferroferric oxide composite material and application of CNK-OH/ferroferric oxide composite material in photocatalytic degradation of tetracycline hydrochloride Download PDFInfo
- Publication number
- CN112958139A CN112958139A CN202110252058.5A CN202110252058A CN112958139A CN 112958139 A CN112958139 A CN 112958139A CN 202110252058 A CN202110252058 A CN 202110252058A CN 112958139 A CN112958139 A CN 112958139A
- Authority
- CN
- China
- Prior art keywords
- cnk
- composite material
- ferroferric oxide
- oxide composite
- preparation
- 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
- SZVJSHCCFOBDDC-UHFFFAOYSA-N ferrosoferric oxide Chemical compound O=[Fe]O[Fe]O[Fe]=O SZVJSHCCFOBDDC-UHFFFAOYSA-N 0.000 title claims abstract description 85
- 239000002131 composite material Substances 0.000 title claims abstract description 46
- XMEVHPAGJVLHIG-FMZCEJRJSA-N chembl454950 Chemical compound [Cl-].C1=CC=C2[C@](O)(C)[C@H]3C[C@H]4[C@H]([NH+](C)C)C(O)=C(C(N)=O)C(=O)[C@@]4(O)C(O)=C3C(=O)C2=C1O XMEVHPAGJVLHIG-FMZCEJRJSA-N 0.000 title claims abstract description 35
- 229960004989 tetracycline hydrochloride Drugs 0.000 title claims abstract description 35
- 238000002360 preparation method Methods 0.000 title claims abstract description 19
- 238000013033 photocatalytic degradation reaction Methods 0.000 title claims abstract description 17
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims abstract description 24
- 239000011941 photocatalyst Substances 0.000 claims abstract description 11
- 238000000034 method Methods 0.000 claims abstract description 10
- QGBSISYHAICWAH-UHFFFAOYSA-N dicyandiamide Chemical compound NC(N)=NC#N QGBSISYHAICWAH-UHFFFAOYSA-N 0.000 claims abstract description 8
- 239000002243 precursor Substances 0.000 claims abstract description 7
- WCUXLLCKKVVCTQ-UHFFFAOYSA-M Potassium chloride Chemical compound [Cl-].[K+] WCUXLLCKKVVCTQ-UHFFFAOYSA-M 0.000 claims abstract description 5
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 claims description 12
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 11
- 229910021577 Iron(II) chloride Inorganic materials 0.000 claims description 10
- 229910021578 Iron(III) chloride Inorganic materials 0.000 claims description 10
- NMCUIPGRVMDVDB-UHFFFAOYSA-L iron dichloride Chemical compound Cl[Fe]Cl NMCUIPGRVMDVDB-UHFFFAOYSA-L 0.000 claims description 10
- RBTARNINKXHZNM-UHFFFAOYSA-K iron trichloride Chemical compound Cl[Fe](Cl)Cl RBTARNINKXHZNM-UHFFFAOYSA-K 0.000 claims description 10
- 239000012153 distilled water Substances 0.000 claims description 9
- 238000001291 vacuum drying Methods 0.000 claims description 9
- 238000005406 washing Methods 0.000 claims description 9
- 238000003756 stirring Methods 0.000 claims description 8
- 238000009210 therapy by ultrasound Methods 0.000 claims description 6
- 238000001035 drying Methods 0.000 claims description 5
- 229920000642 polymer Polymers 0.000 claims description 5
- 238000005119 centrifugation Methods 0.000 claims description 3
- 238000010438 heat treatment Methods 0.000 claims description 3
- 239000006185 dispersion Substances 0.000 claims description 2
- 238000002156 mixing Methods 0.000 claims description 2
- 238000002604 ultrasonography Methods 0.000 claims 2
- 238000000227 grinding Methods 0.000 claims 1
- 125000002887 hydroxy group Chemical group [H]O* 0.000 abstract description 13
- 230000004048 modification Effects 0.000 abstract description 9
- 238000012986 modification Methods 0.000 abstract description 9
- 230000001699 photocatalysis Effects 0.000 abstract description 7
- 238000012546 transfer Methods 0.000 abstract description 7
- 238000002513 implantation Methods 0.000 abstract description 5
- 239000000969 carrier Substances 0.000 abstract description 4
- 239000003054 catalyst Substances 0.000 abstract description 4
- 238000006243 chemical reaction Methods 0.000 abstract description 4
- 230000009286 beneficial effect Effects 0.000 abstract description 2
- 238000005470 impregnation Methods 0.000 abstract description 2
- 230000006872 improvement Effects 0.000 abstract description 2
- 238000006068 polycondensation reaction Methods 0.000 abstract description 2
- 239000002994 raw material Substances 0.000 abstract description 2
- 238000000926 separation method Methods 0.000 abstract description 2
- 238000006731 degradation reaction Methods 0.000 description 21
- 230000015556 catabolic process Effects 0.000 description 18
- 239000000203 mixture Substances 0.000 description 9
- 239000000047 product Substances 0.000 description 6
- 239000000725 suspension Substances 0.000 description 6
- 238000005033 Fourier transform infrared spectroscopy Methods 0.000 description 4
- 238000001816 cooling Methods 0.000 description 4
- 239000007943 implant Substances 0.000 description 4
- 238000010521 absorption reaction Methods 0.000 description 3
- 239000003242 anti bacterial agent Substances 0.000 description 3
- 230000000593 degrading effect Effects 0.000 description 3
- 238000005516 engineering process Methods 0.000 description 3
- 239000007789 gas Substances 0.000 description 3
- 238000011282 treatment Methods 0.000 description 3
- OWYWGLHRNBIFJP-UHFFFAOYSA-N Ipazine Chemical group CCN(CC)C1=NC(Cl)=NC(NC(C)C)=N1 OWYWGLHRNBIFJP-UHFFFAOYSA-N 0.000 description 2
- 229940088710 antibiotic agent Drugs 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- 230000003115 biocidal effect Effects 0.000 description 2
- 238000011161 development Methods 0.000 description 2
- 230000007613 environmental effect Effects 0.000 description 2
- 230000036541 health Effects 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 238000011160 research Methods 0.000 description 2
- 238000005070 sampling Methods 0.000 description 2
- 239000000243 solution Substances 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 241000282412 Homo Species 0.000 description 1
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 1
- 241001465754 Metazoa Species 0.000 description 1
- 238000004224 UV/Vis absorption spectrophotometry Methods 0.000 description 1
- 238000000862 absorption spectrum Methods 0.000 description 1
- 239000007864 aqueous solution Substances 0.000 description 1
- 238000005452 bending Methods 0.000 description 1
- 230000003197 catalytic effect Effects 0.000 description 1
- 238000006555 catalytic reaction Methods 0.000 description 1
- 238000012512 characterization method Methods 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 239000000356 contaminant Substances 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 201000010099 disease Diseases 0.000 description 1
- 208000037265 diseases, disorders, signs and symptoms Diseases 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 239000005447 environmental material Substances 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 210000003608 fece Anatomy 0.000 description 1
- 125000000623 heterocyclic group Chemical group 0.000 description 1
- 239000001257 hydrogen Substances 0.000 description 1
- 229910052739 hydrogen Inorganic materials 0.000 description 1
- 238000005286 illumination Methods 0.000 description 1
- 238000011065 in-situ storage Methods 0.000 description 1
- 238000002329 infrared spectrum Methods 0.000 description 1
- 230000031700 light absorption Effects 0.000 description 1
- 230000004298 light response Effects 0.000 description 1
- 239000000178 monomer Substances 0.000 description 1
- 231100000252 nontoxic Toxicity 0.000 description 1
- 230000003000 nontoxic effect Effects 0.000 description 1
- 230000003287 optical effect Effects 0.000 description 1
- 244000052769 pathogen Species 0.000 description 1
- 239000002957 persistent organic pollutant Substances 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 230000008569 process Effects 0.000 description 1
- 108090000623 proteins and genes Proteins 0.000 description 1
- 238000004445 quantitative analysis Methods 0.000 description 1
- 230000004044 response Effects 0.000 description 1
- 239000010865 sewage Substances 0.000 description 1
- 238000002336 sorption--desorption measurement Methods 0.000 description 1
- 230000003595 spectral effect Effects 0.000 description 1
- 238000001228 spectrum Methods 0.000 description 1
- 239000006228 supernatant Substances 0.000 description 1
- 230000002195 synergetic effect Effects 0.000 description 1
- 238000000870 ultraviolet spectroscopy Methods 0.000 description 1
- 210000002700 urine Anatomy 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
-
- B01J35/39—
-
- 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
- C02F1/30—Treatment of water, waste water, or sewage by irradiation
-
- 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
- C02F2101/38—Organic compounds containing nitrogen
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2305/00—Use of specific compounds during water treatment
- C02F2305/10—Photocatalysts
Abstract
The invention discloses a preparation method of a CNK-OH/ferroferric oxide composite material and application of the CNK-OH/ferroferric oxide composite material in photocatalytic degradation of tetracycline hydrochloride. The invention adopts dicyandiamide, KCl and NaOH as raw materials to synthesize a precursor CNK-OH by a solid-state thermal polycondensation method, and then Fe is subjected to impregnation3O4Loading on CNK-OH to obtain CNK-OH/Fe3O4A composite material. The composite material can be used as a photocatalyst for photocatalytic degradation of tetracycline hydrochloride, separation and transfer of photon-generated carriers are optimized through K implantation and hydroxyl modification, and improvement of dynamic behavior is realized. Despite Fe3O4Does not affect the transfer of photo-carriers in the volume, but it promotes the utilization of photoelectrons on the surface of the catalyst. Thus, implantation of K, hydroxyl modification andFe3O4the load constructs a rapid transfer and conversion channel for a photon-generated carrier, which is beneficial to more effectively conveying photoelectrons to the surface of the photocatalyst and generating active free radicals, so that CNK-OH/Fe3O4The photocatalytic activity is obviously improved.
Description
Technical Field
The invention belongs to the technical field of environmental materials, and particularly relates to a preparation method of a CNK-OH/ferroferric oxide composite material.
Background
Currently, with the rapid development of social economy, environmental problems have been raised as the focus of wide attention, and the threat to human health and social life is immeasurable, so that the progress of ecological civilization construction and sustainable development is seriously hindered, and the environmental problems can not be ignored before raining. Tetracycline hydrochloride (TCHC) is a broad spectrum antibacterial agent that has been widely used to treat diseases in humans and many animals. Since only 30% of TCHC is absorbed by the organism, the remainder enters the environment through urine and feces, and naturally accumulates in various bodies of water. In addition, the residues of TCHCs lead to the production of antibiotic-resistant pathogens and to the transfer of antibiotic-resistant genes, posing a serious threat to human health and ecological safety. Therefore, the removal of TC from the environment has become an urgent problem to be solved. Currently, there are several treatments for antibiotics in water, such as biological, physical and chemical methods. However, the method has fatal weaknesses in the degradation process, such as high energy consumption, low efficiency, secondary pollution and the like. The photocatalytic technology has high degradation rate, small secondary pollution and easy treatment, and nearly all antibiotics in sewage treatment can be degraded. The photocatalytic technology is a novel technology that converts light energy into chemical energy, and then generates holes, hydroxyl radicals, and superoxide radicals to degrade contaminants. It is considered one of the most effective methods for degrading pollutants due to its superior sustainable energy characteristics, avoidance of secondary pollution, economic cost and convenience of operation, and thus has attracted extensive attention.
How to efficiently utilize solar energy to improve photocatalytic degradation efficiency has become a topic of hot research. In the reported photocatalytic materials, g-C3N4(CN) based material as a novel Metalfree polymerThe photocatalyst has good photocatalytic performance under the irradiation of visible light, and the photocatalyst is low in cost, non-toxic and stable in heat. Thus, g-C3N4(CN) has been widely used for the degradation of organic pollutants and the direct production of clean hydrogen. However, g-C3N4The (CN) has a light absorption edge of about 450nm and a band gap of 2.7eV, and the use of the (CN) under the irradiation of visible light is limited. Therefore, there is a need to develop an effective visible light responsive photocatalyst to extend its spectral response to higher absorption wavelengths. In the research of the invention, the CNK-OH/Fe for efficiently degrading tetracycline hydrochloride under visible light is provided3O4A photocatalyst.
Disclosure of Invention
Aiming at the technical problems in the prior art, the invention aims to provide a preparation method of a CNK-OH/ferroferric oxide composite material with visible light response;
the invention also aims to provide a CNK-OH/ferroferric oxide composite material used as a photocatalyst for photocatalytic degradation of tetracycline hydrochloride.
Mono, CNK-OH/Fe3O4Preparation of composite materials
(1) Preparation of CNK-OH: the dicyandiamide, KCl and NaOH are ground and fully mixed, the mixture is heated to 300-600 ℃ (preferably 510-570 ℃) at the heating rate of 1-20 ℃/min (preferably 2.3 ℃/min) in a muffle furnace, the mixture is roasted at the constant temperature for 0.1-10 h (preferably 2-4), distilled water is added to dissolve the obtained polymer, and then the mixture is subjected to ultrasonic treatment, centrifugation, washing and vacuum drying at the temperature of 60-80 ℃ for 12-24 h to obtain a precursor, wherein the precursor is marked as CNK-OH. Wherein the molar ratio of dicyandiamide to KCl to NaOH is 7:4: 1; the ultrasonic treatment is intermittent ultrasonic treatment at 20000-25000 Hz for 0.5-1 h and 3-5 h, and the intermittent ultrasonic treatment is to regulate and control the appearance of the polymer in the dissolving process.
(2)CNK-OH/Fe3O4Preparing a composite material: dispersing CNK-OH in distilled water to obtain CNK-OH dispersion, adding FeCl3•6H2O and FeCl2•4H2Stirring O, mixing, adding NH3•H2Stirring and reacting O at 60-90 ℃ for 30-60 min, collecting the product by using a magnet, washing the product by using ethanol, and performing vacuum drying at 60-80 ℃ for 12-24 h to finally obtain K implantation, hydroxyl modification and Fe3O4Supported composite, labelled CNK-OH/Fe3O4. Wherein, CNK-OH and FeCl3•6H2The mass ratio of O is 1: 0.027-1: 0.162; CNK-OH and FeCl2•4H2The mass ratio of O is 0.01-0.06; FeCl3•6H2O and FeCl2•4H2The molar ratio of O is 2: 1; CNK-OH and NH3•H2The mass-to-volume ratio of O is 0.15-1 g/mL.
Di, CNK-OH/Fe3O4Characterization of the composite Material
1. UV-vis absorption Spectroscopy
FIG. 1 shows CNK-OH and 5% CNK-OH/Fe3O4(5% represents CNK-OH/Fe)3O4Middle Fe3O4Content of 5%) composite material, the absorption edge of pure CNK-OH is about 480nm, and CNK-OH/Fe is compared with pure CNK-OH3O4The composite material has an absorption edge with longer wavelength, the wavelength is obviously red-shifted to show that the band gap energy is reduced, and the composite material can absorb more visible light, which indicates that Fe3O4Has strong influence on the optical performance of the synthetic CNK-OH group catalyst and shows better photocatalytic performance.
2. Fourier transform infrared spectrogram (FT-IR)
FIG. 2 shows CNK-OH and different Fe3O4CNK-OH/Fe at content3O4For the determination of hydroxyl groups on the sample, fourier transform infrared spectroscopy (FT-IR) was used. In the spectrum of CNK-OH, 1147, 2142 and 2177cm-1The appearance of 3 peaks indicates that the hydroxyl groups are stably grafted on the CNK when KCl is introduced. CNK-OH loaded Fe3O4These latter peaks remained unchanged, indicating that CNK-OH is loaded with Fe3O4The post hydroxyl group can still exist stably. At 1200--1The series of peaks in the range, attributable to stretching vibrations of the CN heterocycle, was at 808cm-1The sharp peak at (A) is the bending vibration of the heptazine ring, indicating g-C3N4Is composed of heptazine monomers.
III, CNK-OH/Fe3O4Photocatalytic degradation of composite materials
The photocatalytic degradation performance of tetracycline hydrochloride was quantitatively analyzed using a UV-2500 UV-visible spectrophotometer. A300W Xe lamp (Aulight, CEL-HXF 300) was used as the illumination source. 20mg of CNK-OH/Fe3O4The photocatalyst is dissolved in 50ml of tetracycline hydrochloride (TCHC) aqueous solution, and the pH is adjusted to 3-4. Reacting the suspension for 1h under stirring in a dark environment to reach the adsorption-desorption balance of the catalyst, and sampling every 30min during the reaction; the suspension was irradiated with visible light (300W Xe lamp (Aulight, CEL-HXF 300)) and gassed (air, N, respectively)2(N2As reference), O2) Sampling at certain time intervals, collecting separated supernatant, and performing quantitative analysis by using an ultraviolet-visible spectrophotometer.
FIG. 3 shows CNK-OH and Fe3O4And CNK-OH/Fe3O4The photocatalytic degradation performance diagram for degrading tetracycline hydrochloride. FIG. 3a shows the degradation of tetracycline hydrochloride by CNK-OH under different gas conditions. From FIG. 3a, it can be easily seen that CNK-OH is in air, O under visible light irradiation2The degradation rate of tetracycline hydrochloride in 120min under the condition is 49 percent and 51 percent respectively. In FIG. 3b, it can be seen that the light is also visible and air, O, is introduced2In the case of (1), Fe3O4The degradation rate of tetracycline hydrochloride in 120min is 50% and 53% respectively. As can be seen in FIG. 3c, CNK-OH/Fe under visible light irradiation3O4In the air, O2The degradation of tetracycline hydrochloride in 120min in the system can reach 88.5 percent and 92.5 percent. CNK-OH/Fe3O4In a visible light and oxygen system, the degradation of the tetracycline hydrochloride is obviously improved because a synergistic effect exists between the light Fenton reaction and the in-situ catalytic degradation, namely, the oxygen-related free radicals participate in the light degradation reaction, and then the tetracycline hydrochloride is degraded through light catalysis. FIG. 3d shows the CNK-OH/Fe ratios in the visible light irradiation without gas introduction into the gas system3O4Degradation rate of tetracycline hydrochloride. Apparently, 5% CNK-OH/Fe3O4Has the best degradation effect on tetracycline hydrochloride.
In conclusion, the invention adopts dicyandiamide, KCl and NaOH as raw materials to synthesize the precursor CNK-OH by a solid-state thermal polycondensation method, and Fe is subjected to impregnation method3O4Loaded on CNK-OH to obtain K implanted and hydroxyl modified composite material CNK-OH/Fe3O4. The composite material can be used as a photocatalyst for photocatalytic degradation of tetracycline hydrochloride, separation and transfer of photon-generated carriers are optimized through K implantation and hydroxyl modification, and improvement of dynamic behavior is realized. Despite Fe3O4Does not affect the transfer of photo-carriers in the volume, but it promotes the utilization of photoelectrons on the surface of the catalyst. Thus, K implantation, hydroxyl modification and Fe3O4The load constructs a rapid transfer and conversion channel for a photon-generated carrier, which is beneficial to more effectively conveying photoelectrons to the surface of the photocatalyst and generating active free radicals, so that CNK-OH/Fe3O4The photocatalytic activity is obviously improved.
Drawings
FIG. 1 shows CNK-OH and CNK-OH/Fe3O4Ultraviolet and visible absorption spectrum of (1).
FIG. 2 shows CNK-OH and CNK-OH/Fe3O4An infrared spectrum of (1).
FIG. 3 shows CNK-OH and Fe3O4And CNK-OH/Fe3O4The photocatalytic degradation performance of (1).
Detailed Description
The following is a description of the present invention by way of specific embodiments3O4The preparation method and photocatalytic degradation performance of the composite material are further explained.
Example 1
(1) Preparation of CNK-OH: dicyandiamide (more than or equal to 99.0 percent), KCl (more than or equal to 99.5 percent) and NaOH (98.0 percent) are ground and fully mixed (the molar ratio of dicyandiamide to KCl to NaOH is 7:4: 1), the mixture is heated to 550 ℃ in a muffle furnace at the speed of 2.3 ℃/min, the mixture is calcined at constant temperature for 2-4 h, after the temperature is reduced, a polymer is taken out, distilled water is added to dissolve the polymer to prepare a solution of 1 g/L, and then the solution is subjected to ultrasonic treatment, centrifugation at 8000-10000 r/min for 3-5 min, washing and vacuum drying at 80 ℃ for 24h to obtain a precursor, wherein the precursor is marked as CNK-OH.
(2)CNK-OH/Fe3O4Preparing a composite material: dispersing 1g CNK-OH in 20mL distilled water to obtain CNK-OH suspension, adding FeCl3•6H2O (0.1mmol, 0.027g) and FeCl2•4H2O (0.05mmol, 0.010g), stirred at 80 ℃ for 30min, then 1ml NH3•H2Rapidly injecting O into the mixture, stirring at 80 deg.C for 30min, collecting the product with magnet, washing with ethanol for several times, drying in vacuum drying oven, cooling, and collecting the sample to obtain K implant, hydroxyl modification and Fe3O4Supported composite, labelled CNK-OH/Fe3O4。
(3)CNK-OH/Fe3O4The performance of the tetracycline hydrochloride photocatalytic degradation is as follows: under visible light irradiation, CNK-OH/Fe3O4The degradation rate of tetracycline hydrochloride in 120min reaches 75 percent; CNK-OH/Fe3O4At O2The degradation rate of tetracycline hydrochloride in the system within 120min reaches 92.5 percent, and the degradation efficiency is highest.
Example 2
(1) Preparation of CNK-OH: the same as in example 1.
(2)CNK-OH/Fe3O4Preparing a composite material: dispersing 1g CNK-OH in 20mL distilled water to obtain CNK-OH suspension, adding FeCl3•6H2O (0.2mmol, 0.054g) and FeCl2•4H2O (0.1mmol, 0.020g), stirred at 80 ℃ for 30min, then 2ml NH3•H2Rapidly injecting O into the mixture, stirring at 80 deg.C for 30min, collecting the product with magnet, washing with ethanol for several times, drying in vacuum drying oven, cooling, and collecting the sample to obtain K implant, hydroxyl modification and Fe3O4Supported composite, labelled CNK-OH/Fe3O4。
(3)CNK-OH/Fe3O4The performance of the tetracycline hydrochloride photocatalytic degradation is as follows: in the visibleUnder light irradiation, CNK-OH/Fe3O4The degradation rate of tetracycline hydrochloride in 120min reaches 70.5 percent; CNK-OH/Fe3O4At O2The degradation rate of tetracycline hydrochloride in the system within 120min reaches 85 percent.
Example 3
(1) Preparation of CNK-OH: the same as in example 1.
(2)CNK-OH/Fe3O4Preparing a composite material: dispersing 1g CNK-OH in 20mL distilled water to obtain CNK-OH suspension, adding FeCl3•6H2O (0.4mmol, 0.108g) and FeCl2•4H2O (0.2mmol, 0.040g), stirred at 80 ℃ for 30min, then 4ml NH3•H2Rapidly injecting O into the mixture, stirring at 80 deg.C for 30min, collecting the product with magnet, washing with ethanol for several times, drying in vacuum drying oven, cooling, and collecting the sample to obtain K implant, hydroxyl modification and Fe3O4Supported composite, labelled CNK-OH/Fe3O4。
(3)CNK-OH/Fe3O4The performance of the tetracycline hydrochloride photocatalytic degradation is as follows: under visible light irradiation, CNK-OH/Fe3O4The degradation rate of tetracycline hydrochloride in 120min reaches 70 percent; CNK-OH/Fe3O4At O2The degradation rate of tetracycline hydrochloride in the system within 120min reaches 78.5 percent.
Example 4
(1) Preparation of CNK-OH: the same as in example 1.
(2)CNK-OH/Fe3O4Preparing a composite material: dispersing 1g CNK-OH in 20mL distilled water to obtain CNK-OH suspension, adding FeCl3•6H2O (0.6mmol, 0.162g) and FeCl2•4H2O (0.3mmol, 0.060g), stirred at 80 ℃ for 30min, then 6ml NH3•H2Rapidly injecting O into the mixture, stirring at 80 deg.C for 30min, collecting the product with magnet, washing with ethanol for several times, drying in vacuum drying oven, cooling, and collecting the sample to obtain K implant, hydroxyl modification and Fe3O4Supported composite, markingIs CNK-OH/Fe3O4。
(3)CNK-OH/Fe3O4The performance of the tetracycline hydrochloride photocatalytic degradation is as follows: under visible light irradiation, CNK-OH/Fe3O4The degradation rate of tetracycline hydrochloride in an air system within 120min reaches 63.5 percent; CNK-OH/Fe3O4At O2The degradation rate of tetracycline hydrochloride in the system within 120min reaches 73%.
Claims (8)
1. A preparation method of a CNK-OH/ferroferric oxide composite material comprises the following steps:
(1) preparation of CNK-OH: grinding and fully mixing dicyandiamide, KCl and NaOH, heating to 300-600 ℃ in a muffle furnace at the heating rate of 1-20 ℃/min, roasting at constant temperature for 0.1-10 h, adding distilled water to dissolve the obtained polymer, and then performing ultrasonic treatment, centrifugation, washing and vacuum drying to obtain a precursor, wherein the label is CNK-OH;
(2)CNK-OH/Fe3O4preparing a composite material: dispersing CNK-OH in distilled water to obtain dispersion, adding FeCl3•6H2O and FeCl2•4H2O is fully stirred and mixed evenly, and NH is added3•H2Stirring and reacting O at 60-90 ℃ for 30-60 min, collecting the product with a magnet, washing with ethanol, and drying in vacuum to obtain CNK-OH/Fe3O4A composite material.
2. The preparation method of the CNK-OH/ferroferric oxide composite material as claimed in claim 1, wherein the CNK-OH/ferroferric oxide composite material comprises the following steps: in the step (1), the molar ratio of dicyandiamide to KCl to NaOH is 7:4: 1.
3. The preparation method of the CNK-OH/ferroferric oxide composite material as claimed in claim 1, wherein the CNK-OH/ferroferric oxide composite material comprises the following steps: in the step (1), the ultrasound is interrupted at 20000-25000 Hz for 0.5-1 h, and the ultrasound lasts for 3-5 h.
4. The method for preparing CNK-OH/ferroferric oxide composite material according to claim 1, wherein the CNK-OH/ferroferric oxide composite material is prepared by a method comprising the steps of: in step (2), CNK-OH and FeCl3•6H2The mass ratio of O is 1: 0.027-1: 0.162; CNK-OH and FeCl2•4H2The mass ratio of O is 0.01-0.06.
5. The preparation method of the CNK-OH/ferroferric oxide composite material as claimed in claim 1, wherein the CNK-OH/ferroferric oxide composite material comprises the following steps: in step (2), FeCl3•6H2O and FeCl2•4H2The molar ratio of O is 2: 1.
6. The preparation method of the CNK-OH/ferroferric oxide composite material as claimed in claim 1, wherein the CNK-OH/ferroferric oxide composite material comprises the following steps: in step (2), CNK-OH and NH3•H2The mass-to-volume ratio of O is 0.15-1 g/mL.
7. The preparation method of the CNK-OH/ferroferric oxide composite material as claimed in claim 1, wherein the CNK-OH/ferroferric oxide composite material comprises the following steps: in the steps (1) and (2), the vacuum drying is carried out for 12-24 hours at a constant temperature of 60-80 ℃.
8. The CNK-OH/ferroferric oxide composite material prepared by the method of claim 1 is used as a photocatalyst for photocatalytic degradation of tetracycline hydrochloride.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202110252058.5A CN112958139A (en) | 2021-03-08 | 2021-03-08 | Preparation of CNK-OH/ferroferric oxide composite material and application of CNK-OH/ferroferric oxide composite material in photocatalytic degradation of tetracycline hydrochloride |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202110252058.5A CN112958139A (en) | 2021-03-08 | 2021-03-08 | Preparation of CNK-OH/ferroferric oxide composite material and application of CNK-OH/ferroferric oxide composite material in photocatalytic degradation of tetracycline hydrochloride |
Publications (1)
Publication Number | Publication Date |
---|---|
CN112958139A true CN112958139A (en) | 2021-06-15 |
Family
ID=76277414
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN202110252058.5A Pending CN112958139A (en) | 2021-03-08 | 2021-03-08 | Preparation of CNK-OH/ferroferric oxide composite material and application of CNK-OH/ferroferric oxide composite material in photocatalytic degradation of tetracycline hydrochloride |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN112958139A (en) |
Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN105233850A (en) * | 2015-09-21 | 2016-01-13 | 河海大学 | Magnetic nanometer composite photocatalysis material, and preparation method thereof |
CN107321382A (en) * | 2017-07-04 | 2017-11-07 | 江苏理工学院 | A kind of modified g C3N4Photochemical catalyst and preparation method thereof |
CN110252379A (en) * | 2019-07-10 | 2019-09-20 | 西北师范大学 | A kind of preparation and application of palygorskite/graphite-phase carboritride composite material |
CN111266126A (en) * | 2020-02-25 | 2020-06-12 | 同济大学 | Preparation method and application of sulfur-doped graphite-phase carbon nitride nanosheet-loaded graphene and ferroferric oxide composite magnetic photocatalyst |
CN112090440A (en) * | 2020-09-22 | 2020-12-18 | 海南师范大学 | Oxygen-deficient titanium dioxide material of composite hydroxylated carbon nitride and preparation method thereof |
-
2021
- 2021-03-08 CN CN202110252058.5A patent/CN112958139A/en active Pending
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN105233850A (en) * | 2015-09-21 | 2016-01-13 | 河海大学 | Magnetic nanometer composite photocatalysis material, and preparation method thereof |
CN107321382A (en) * | 2017-07-04 | 2017-11-07 | 江苏理工学院 | A kind of modified g C3N4Photochemical catalyst and preparation method thereof |
CN110252379A (en) * | 2019-07-10 | 2019-09-20 | 西北师范大学 | A kind of preparation and application of palygorskite/graphite-phase carboritride composite material |
CN111266126A (en) * | 2020-02-25 | 2020-06-12 | 同济大学 | Preparation method and application of sulfur-doped graphite-phase carbon nitride nanosheet-loaded graphene and ferroferric oxide composite magnetic photocatalyst |
CN112090440A (en) * | 2020-09-22 | 2020-12-18 | 海南师范大学 | Oxygen-deficient titanium dioxide material of composite hydroxylated carbon nitride and preparation method thereof |
Non-Patent Citations (4)
Title |
---|
DINGLONG ZHU ET.AL: ""Flower-like-flake Fe3O4/g-C3N4 nanocomposite: Facile synthesis,characterization, and enhanced photocatalytic performance"", 《COLLOIDS AND SURFACES A》 * |
YUNXIANG LI ET.AL: ""Constructing Solid−Gas-Interfacial Fenton Reaction over Alkalinized‑C3N4 Photocatalyst To Achieve Apparent Quantum Yield of 49% at 420 nm"", 《J. AM. CHEM. SOC.》 * |
YUNXIANG LI ET.AL: ""In situ surface alkalinized g-C3N4 toward enhancement of photocatalytic H2 evolution under visible-light irradiation"", 《JOURNAL OF MATERIALS CHEMISTRY A》 * |
黄占斌等: "《环境材料学》", 30 November 2017, 冶金工业出版社 * |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN107899590B (en) | Preparation and application of metal Ag nano-particle deposited NiCo-LDH composite photocatalyst | |
CN107262131A (en) | A kind of visible light-responded Bi3O4Cl/g‑C3N4The preparation method and application of heterojunction material | |
CN107890877B (en) | Bi3O4Cl/CdS composite material, preparation method and application | |
CN108126718B (en) | In2S3/BiPO4Preparation method and application of heterojunction photocatalyst | |
CN112007632B (en) | Flower-shaped SnO 2 /g-C 3 N 4 Preparation method of heterojunction photocatalyst | |
CN110756215A (en) | CoP-HCCN composite photocatalyst and preparation method and application thereof | |
CN112316982A (en) | Method for preparing titanium-based metal organic framework homologous heterojunction photocatalyst | |
WO2020221240A1 (en) | Method for preparing tourmaline containing anthraquinone compound by means of thiol-ene click chemistry and application thereof | |
CN105688948B (en) | A kind of photochemical catalyst and its preparation method and application | |
CN112169798B (en) | Catalyst with collagen-based carbon material loaded with metal cobalt and preparation method and application thereof | |
CN111468100B (en) | Preparation method of in-situ grown polyacid niobium/graphene photocatalyst and application of in-situ grown polyacid niobium/graphene photocatalyst in tetracycline degradation | |
CN112934249A (en) | Preparation and application of phosphorus-doped graphite carbon nitride/ferroferric oxide composite material | |
CN112958139A (en) | Preparation of CNK-OH/ferroferric oxide composite material and application of CNK-OH/ferroferric oxide composite material in photocatalytic degradation of tetracycline hydrochloride | |
CN110575841B (en) | Novel photocatalyst material for methylene blue photodegradation and preparation method thereof | |
CN108554427B (en) | In2O3/BiOI semiconductor composite photocatalyst and preparation method and application thereof | |
CN111790409A (en) | Lanthanum oxide-bismuth-rich bismuth oxyiodide composite material and preparation method thereof | |
CN114768792B (en) | Purifying agent for sewage treatment and preparation method thereof | |
CN111346675A (en) | Preparation method and application of acid-sensitive control type PAA @ Ag/AgCl/CN composite photocatalyst | |
CN116393155A (en) | Carbocyclic doped g-C 3 N 4 Preparation method of heterojunction in basal plane and application of heterojunction in photo-reforming cellulose | |
CN110938230A (en) | Multifunctional foamed natural rubber with high catalytic performance and antibacterial performance and preparation method thereof | |
CN108479829A (en) | A kind of preparation of N doping Zinc vanadate photochemical catalyst | |
CN111790421B (en) | Graphite-phase carbon nitride modified fabric visible-light-driven photocatalyst and one-step preparation method and application thereof | |
CN108479826A (en) | A kind of silver carbonate is modified the preparation of two selenizing molybdenum composite photo-catalysts | |
CN113877619A (en) | Preparation method and application of carbon-nitrogen-doped titanium dioxide and biomass carbon composite material | |
CN115301267A (en) | Porous tubular carbon nitride catalyst suitable for visible light catalysis and preparation method and application thereof |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination |