CN107649162A - A kind of composite photo-catalyst and preparation method and application - Google Patents

A kind of composite photo-catalyst and preparation method and application Download PDF

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CN107649162A
CN107649162A CN201710948003.1A CN201710948003A CN107649162A CN 107649162 A CN107649162 A CN 107649162A CN 201710948003 A CN201710948003 A CN 201710948003A CN 107649162 A CN107649162 A CN 107649162A
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solution
catalyst
composite photo
composite
photochemical catalyst
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董红军
吴海君
李春梅
刘春波
车慧楠
张晓旭
艾俊哲
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Jiangsu University
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J27/00Catalysts comprising the elements or compounds of halogens, sulfur, selenium, tellurium, phosphorus or nitrogen; Catalysts comprising carbon compounds
    • B01J27/24Nitrogen compounds
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J31/00Catalysts comprising hydrides, coordination complexes or organic compounds
    • B01J31/26Catalysts comprising hydrides, coordination complexes or organic compounds containing in addition, inorganic metal compounds not provided for in groups B01J31/02 - B01J31/24
    • B01J31/28Catalysts comprising hydrides, coordination complexes or organic compounds containing in addition, inorganic metal compounds not provided for in groups B01J31/02 - B01J31/24 of the platinum group metals, iron group metals or copper
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J35/00Catalysts, in general, characterised by their form or physical properties
    • B01J35/30Catalysts, in general, characterised by their form or physical properties characterised by their physical properties
    • B01J35/39Photocatalytic 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
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/08Heat treatment
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J37/00Processes, in general, for preparing catalysts; Processes, in general, for activation of catalysts
    • B01J37/08Heat treatment
    • B01J37/082Decomposition and pyrolysis
    • B01J37/088Decomposition of a metal salt
    • 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
    • C02F1/30Treatment of water, waste water, or sewage by irradiation
    • 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
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/10Photocatalysts

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Abstract

The invention belongs to catalysis material synthesis technical field.A kind of composite photo-catalyst and preparation method and application are refered in particular to, available for quadracycline pollutant of degrading under visible light.Precise Iron(III) chloride hexahydrate is dissolved in stirring in ethylene glycol and obtains solution A.Sodium acetate is added in solution A and forms solution B.G C are added in solution B3N4, stir and form solution C.Solution C is transferred in reactor, reacts 6h in 200 DEG C of baking oven.After room temperature, centrifuge, wash, be dried to obtain sample.

Description

A kind of composite photo-catalyst and preparation method and application
Technical field
The invention belongs to catalysis material synthesis technical field, using simple and quick solvent-thermal method one-step synthesis by Fe3O4 Nanosphere modifies g-C3N4Fe3O4/g-C3N4Composite mesoporous photochemical catalyst, it is dirty available for quadracycline of degrading under visible light Contaminate thing.
Background technology
China is antibiotic usage and big producer, produces the outlet of antibiotic raw material sub-fraction per year, and remaining is largely personal (including medical treatment and agricultural use), annual consumption 138g or so per capita, and U.S. annual consumption only 13g per capita according to statistics.According to 2006~2007 annual Ministry of Public Health whole nation Bacterial resistance surveillance results show that national hospital's antibacterials year utilization rate is up to 74%, and in developed countries such as the U.S. and Britains, the antibiotic utilization rate of hospital is only 22%~25%.In the inpatient of China, resist The utilization rate of raw element is then up to 70%, wherein surgical patients almost everybody use antibiotic, ratio is up to 97%.These digital tables Bright China has become one of country of abuse of antibiotics problem most serious in the world.Antibiotic is originally to be used to treat various non-diseases The medicine of poison infection, but shown many side effects in Clinical practice, research shows that part antibiotic has to fetus Teratogenesis.Tetracycline medication is clinically to use most, most widely used a kind of antibiotic, due to its have it is water-soluble compared with The features such as largely discharging with original shape after good, metabolism in vivo and be not susceptible to biodegradation in the environment, so as to easily in water Storage and accumulation form Environmental Residues thing in environment, cause a series of ecological pollution and influence human health problems.Meanwhile by Wider in such medicine antibacterial spectrum, its caused eco-toxicology effects is very huge, therefore, effectively removes hydrochloric acid in environment Tetracycline residue thing is very urgent.Research find the treatment technology conventional with some such as adsorb, be electrolysed, microbial degradation phase Than, Photocatalyst has using renewable solar energy, environment-friendly, pollutant removal is thorough, cost is cheap etc. significantly Advantage.
The core of Photocatalyst is the efficient conductor photocatalysis material of exploitation.Recent study is more partly to be led Body photochemical catalyst TiO2, because it is wide band gap semiconducter, ultraviolet can only be absorbed, causes sun light utilization efficiency very low.Although also Develop substantial amounts of TiO2Based composites, but the quick compound potential application for still limiting them of electron-hole pair.Graphite Phase carbon nitride (g-C3N4) it is a kind of novel semi-conductor catalysis material favored very much, not only there is narrower energy gap (2.7eV) can responding to visible light, but also there is acid and alkali resistance, photoetch and environmental protection.However, g-C3N4Still have In place of some shortcomings, such as specific surface area is relatively low, photo-generate electron-hole is higher to recombination rate, so as to cause its photocatalysis performance It is relatively low.
During people explore novel photocatalyst, Fe is found3O4It is a kind of potential catalysis material.Fe3O4It is By Fe2+、Fe3+And O2-The inverse spinel crystal structure of composition, allow its electronics in Fe2+And Fe3+Between transmitted, so as to With special electromagnetic property.Fe3O4Possess high saturation magnetization, Curie temperature and electric conductivity, while also have well Weatherability, light resistance, ultraviolet radiation absorption and shielding character, in microwave absorbing material, catalyst carrier, magnetic recording material, electronics Material and bio-medical material etc. have a wide range of applications, so to Fe3O4Controlledly synthesis and its physical and chemical performance Study significant.The iron oxide of nanoscale due to the quantum size effect of nano material, surface and interface effect etc., And with the physical and chemical properties different from body material.By Fe3O4For the composite photocatalyst material of composite construction cell formation, Such as metal/Fe3O4, graphene/Fe3O4、WO3/Fe3O4、TiO2/Fe3O4Etc. showing unique, efficient photocatalysis performance, but this It can not but be realized in one-component catalyst.It is different from other most metals oxide semiconductors, nanometer Fe3O4Have (electrical conductivity is up to 1.9 × 10 to good electric conductivity6S m-1) and band structure matching, it can be good at and g-C3N4Carry out coupling Close, and photocatalysis performance is improved by strengthening separation and the transfer of electron-hole pair, compensate for single g-C3N4Photoproduction electricity The shortcomings that son-hole is higher to recombination rate.Therefore, by nanometer Fe3O4To g-C3N4Nanometer sheet carries out surface modification, can prepare Efficient visible light composite photocatalyst.
In this work, by simple and quick solvent-thermal method one-step synthesis by Fe3O4Nanosphere surface modification g-C3N4's Fe3O4/g-C3N4Composite mesoporous photochemical catalyst, for photocatalytic degradation quadracycline.With g-C3N4Compare, optimal Fe3O4/g- C3N4Composite photo-catalyst is in 120min to the degradation rate of quadracycline up to 70.9%, about g-C3N4(23.3%) 3.04 again.Fe3O4Nanosphere is to g-C3N4Surface modification effect significantly improve its capacity gauge and current-carrying to solar spectrum The separative efficiency of son, while specific surface area and surface-active site are added, finally substantially increase and quadracycline is polluted The degradation capability of thing.Up to the present, not yet find using a simple and quick step solvent-thermal method in g-C3N4Surface modification Fe3O4Nanosphere builds Fe3O4/g-C3N4Composite mesoporous photochemical catalyst.
The content of the invention
The invention belongs to nano material synthesis technical field, using simple and quick solvent-thermal method one-step synthesis by Fe3O4Receive Rice ball modification g-C3N4Fe3O4/g-C3N4Composite mesoporous photochemical catalyst, available for Visible Light Induced Photocatalytic quadracycline pollutant.
The preparation method characteristic of the present invention comprises the following steps:
One, prepares g-C3N4Photochemical catalyst
1. melamine is taken to be put into open pot, with 2 DEG C of min-1Heating rate, be heated to 550 DEG C from room temperature, keep 4h。
2. taking out yellow solid after being cooled to room temperature, powder is ground to agate mortar, obtains g-C3N4Photochemical catalyst.
Two, prepare Fe3O4/g-C3N4Composite mesoporous photochemical catalyst
1. precise Iron(III) chloride hexahydrate is dissolved in stirring in ethylene glycol and obtains solution A.
2. sodium acetate is added in solution A forms solution B.
3. g-C is added in solution B3N4, stir and form solution C.
4. solution C is transferred in reactor, 6h is reacted in 200 DEG C of baking oven.
5. after room temperature, centrifuge, wash, be dried to obtain sample.
The mass volume ratio of sodium acetate and ethylene glycol is 3.6g:35mL.
Sodium acetate and g-C3N4Mass volume ratio be 36:5.
Wherein the amount of Iron(III) chloride hexahydrate is according to Fe3O4And g-C3N4Mass ratio be 0.05:0.5 to 0.15:0.5, most Fe is prepared into eventually3O4To g-C3N4Mass percent be respectively 10wt% to 30wt% Fe3O4/g-C3N4Composite mesoporous light is urged Agent;It is preferred that 20%.
In step (3), the time of magnetic agitation is 12h.
Drying temperature is 60 DEG C in step (5), drying time 12h.
In this work, X-ray diffraction (XRD), field emission scanning electron microscope (FESEM), transmission electron microscope are utilized (TEM)、N2The means such as adsorption-desorption isothermal and BJH pore-size distributions are to Fe3O4/g-C3N4Composite mesoporous photochemical catalyst carries out table Sign.Fig. 1 is g-C3N and Fe3O4/g-C3N4The XRD of composite mesoporous photochemical catalyst.Through Fe3O4After nanosphere modification, g- is found C3N4Stronger diffraction maximum positioned at 2 θ=27.6 ° decreases, and this is probably due to Fe3O4Nanosphere is modified in g-C3N4Surface institute Cause.Meanwhile positioned at 2 θ be 35.4 ° and 62.6 ° at occur coming from Fe3O4Diffraction maximum, this shows Fe3O4Success is modified in g- C3N4Surface.Fig. 2 (a) and (e) are g-C respectively3N4FESEM and TEM photos, it is observed that g-C3N4Structure in the form of sheets.Fig. 2 (b) and (c) in Fe3O4FESEM photos show obtain Fe3O4For uniform nanometer spherical.Fig. 2 (d) and (f) are Fe respectively3O4/ g-C3N4FESEM the and TEM photos of composite mesoporous photochemical catalyst, it is evident that Fe3O4Nanosphere is dispersed in g-C3N4Lamella knot Structure surface, Fe in Fig. 2 (g)3O4/g-C3N4First vegetarian noodles of composite mesoporous photochemical catalyst sweeps photo and shows that each element is uniformly distributed.Separately Outside, the N in Fig. 3 (a, b)2Adsorption-desorption curve and pore-size distribution show that two kinds of samples are meso-hole structure, its 25nm or so Pore-size distribution is g-C3N4Meso-hole structure, and Fe3O4/g-C3N4Pore-size distribution of the composite mesoporous photochemical catalyst in 5nm or so can Fe can be come from3O4Microballoon.Kinetic curve in Fig. 4 (a, b) shows the Fe obtained3O4/g-C3N4Composite mesoporous photocatalysis Agent significantly enhances the photocatalysis performance of degraded quadracycline pollutant, while has higher stability and reusable Property.
In the present invention, by the amount controllable preparation Fe for being accurately controlled reaction condition and reactant3O4/g-C3N4It is mesoporous Composite photo-catalyst.g-C3N4By Fe3O4Significantly improved after nanosphere surface modification to the absorbability of light and carrier Separative efficiency, specific surface area and surface-active site are added, be advantageous to improve photocatalytic activity.The present invention is different from existing skill The distinguishing feature of art is by Fe using this simple and quick solvent-thermal method one-step synthesis3O4Nanosphere surface modification g- C3N4Fe3O4/g-C3N4Composite mesoporous photochemical catalyst, solve some photochemical catalysts under visible light and quadracycline is polluted The problem of thing degradation efficiency is low.
The main object of the present invention:First, it is that accuracy controlling reaction condition and reactant are passed through using simple solvent-thermal method Amount synthesize by Fe3O4Nanosphere surface modification g-C3N4Fe3O4/g-C3N4Composite mesoporous photochemical catalyst provides one typically Example;2nd, Fe3O4/g-C3N4Composite mesoporous photochemical catalyst can be used for photocatalytic degradation quadracycline pollutant under visible ray.
Beneficial effect
Using simple and quick solvent-thermal method one-step synthesis by Fe3O4Nanosphere surface modification g-C3N4Fe3O4/g-C3N4 Composite mesoporous photochemical catalyst, its quadracycline of degrading under visible light illumination show excellent photocatalytic activity;The present invention Technique is very simple, the reaction time is shorter, so as to reduce energy consumption and reaction cost, is easy to produce in batches, nontoxic, meets Environment-friendly requirement.
Brief description of the drawings
Fig. 1 g-C3N4And Fe3O4/g-C3N4The XRD spectrums of composite mesoporous photochemical catalyst.
Fig. 2 g-C3N4FESEM (a) and TEM (e) photos, Fe3O4(b, c) and Fe3O4/g-C3N4Composite mesoporous photocatalysis The FESEM photos of agent (d), Fe3O4/g-C3N4The first vegetarian noodles of TEM (f) of composite mesoporous photochemical catalyst sweeps (g) photo.
Fig. 3 g-C3N4And Fe3O4/g-C3N4The N of composite mesoporous photochemical catalyst2Adsorption-desorption isothermal (a) and aperture point Cloth (b) figure.
Sample to the degradation kinetics curve (a) of quadracycline and circulates the degradation rate (b) of five times under Fig. 4 visible rays Figure.
Embodiment
Embodiment 1:10wt%Fe3O4/g-C3N4The preparation of composite mesoporous photochemical catalyst
One, prepares g-C3N4Photochemical catalyst
1. melamine is taken to be put into open pot, with 2 DEG C of min-1Heating rate, be heated to 550 DEG C from room temperature, keep 4h。
2. taking out yellow solid after being cooled to room temperature, powder is ground to agate mortar, obtains mesoporous g-C3N4Photocatalysis Agent.
Two, prepare 10wt%Fe3O4/g-C3N4Composite mesoporous photochemical catalyst
Solution A is obtained 1. weighing 0.1750g Iron(III) chloride hexahydrates and being dissolved in stirring in 35mL ethylene glycol.
2. 3.6g sodium acetates are added in solution A forms solution B.
3. 0.5g g-C is added in solution B3N4, magnetic agitation 12h formation solution Cs.
4. solution C is transferred in reactor, 6h is reacted in 200 DEG C of baking oven.
5. after room temperature, centrifugation, washing, dry 12h obtains sample in 60 DEG C of baking oven.
Embodiment 2:15wt%Fe3O4/g-C3N4The preparation of composite mesoporous photochemical catalyst
One, prepares g-C3N4Photochemical catalyst
1. melamine is taken to be put into open pot, with 2 DEG C of min-1Heating rate, be heated to 550 DEG C from room temperature, keep 4h。
2. taking out yellow solid after being cooled to room temperature, powder is ground to agate mortar, obtains mesoporous g-C3N4Photocatalysis Agent.
Two, prepare 15wt%Fe3O4/g-C3N4Composite mesoporous photochemical catalyst
Solution A is obtained 1. weighing 0.2625g Iron(III) chloride hexahydrates and being dissolved in stirring in 35mL ethylene glycol.
2. 3.6g sodium acetates are added in solution A forms solution B.
3. 0.5g g-C is added in solution B3N4, magnetic agitation 12h formation solution Cs.
4. solution C is transferred in reactor, 6h is reacted in 200 DEG C of baking oven.
5. after room temperature, centrifugation, washing, dry 12h obtains sample in 60 DEG C of baking oven.
Embodiment 3:20wt%Fe3O4/g-C3N4Composite mesoporous photochemical catalyst
One, prepares g-C3N4Photochemical catalyst
1. melamine is taken to be put into open pot, with 2 DEG C of min-1Heating rate, be heated to 550 DEG C from room temperature, keep 4h。
2. taking out yellow solid after being cooled to room temperature, powder is ground to agate mortar, obtains mesoporous g-C3N4Photocatalysis Agent.
Two, prepare 20wt%Fe3O4/g-C3N4Composite mesoporous photochemical catalyst
Solution A is obtained 1. weighing 0.3501g Iron(III) chloride hexahydrates and being dissolved in stirring in 35mL ethylene glycol.
2. 3.6g sodium acetates are added in solution A forms solution B.
3. 0.5g g-C is added in solution B3N4, magnetic agitation 12h formation solution Cs.
4. solution C is transferred in reactor, 6h is reacted in 200 DEG C of baking oven.
5. after room temperature, centrifugation, washing, dry 12h obtains sample in 60 DEG C of baking oven.
Embodiment 4:25wt%Fe3O4/g-C3N4Composite mesoporous photochemical catalyst
One, prepares g-C3N4Photochemical catalyst
1. melamine is taken to be put into open pot, with 2 DEG C of min-1Heating rate, be heated to 550 DEG C from room temperature, keep 4h。
2. taking out yellow solid after being cooled to room temperature, powder is ground to agate mortar, obtains mesoporous g-C3N4Photocatalysis Agent.
Two, prepare 25wt%Fe3O4/g-C3N4Composite mesoporous photochemical catalyst
Solution A is obtained 1. weighing 0.4376g Iron(III) chloride hexahydrates and being dissolved in stirring in 35mL ethylene glycol.
2. 3.6g sodium acetates are added in solution A forms solution B.
3. 0.5g g-C is added in solution B3N4, magnetic agitation 12h formation solution Cs.
4. solution C is transferred in reactor, 6h is reacted in 200 DEG C of baking oven.
5. after room temperature, centrifugation, washing, dry 12h obtains sample in 60 DEG C of baking oven.
Embodiment 5:30wt%Fe3O4/g-C3N4The preparation of composite mesoporous photochemical catalyst
One, prepares g-C3N4Photochemical catalyst
1. melamine is taken to be put into open pot, with 2 DEG C of min-1Heating rate, be heated to 550 DEG C from room temperature, keep 4h。
2. taking out yellow solid after being cooled to room temperature, powder is ground to agate mortar, obtains mesoporous g-C3N4Photocatalysis Agent.
Two, prepare 30wt%Fe3O4/g-C3N4Composite mesoporous photochemical catalyst
Solution A is obtained 1. weighing 0.5251g Iron(III) chloride hexahydrates and being dissolved in stirring in 35mL ethylene glycol.
2. 3.6g sodium acetates are added in solution A forms solution B.
3. 0.5g g-C is added in solution B3N4, magnetic agitation 12h formation solution Cs.
4. solution C is transferred in reactor, 6h is reacted in 200 DEG C of baking oven.
5. after room temperature, centrifugation, washing, dry 12h obtains sample in 60 DEG C of baking oven.
By strictly regulating and controlling the amount of Iron(III) chloride hexahydrate, ethylene glycol, sodium acetate, with simple and quick solvent-thermal method one Step synthesis is by Fe3O4Nanosphere modifies g-C3N4Fe3O4/g-C3N4Composite mesoporous photochemical catalyst, 50mg each sample has been investigated respectively Under visible light to quadracycline solution (10mg/L) degradation effect, this Fe is as a result shown3O4/g-C3N4It is composite mesoporous Photochemical catalyst significantly enhances photocatalytic activity.In addition, 20wt% Fe3O4/g-C3N4Composite mesoporous photochemical catalyst has most Good catalytic performance, reacted by 120min visible light catalytic, the degradation rate of quadracycline reaches 70.9%, shows to be obtained This Fe obtained3O4/g-C3N4Composite mesoporous photochemical catalyst can be applied to the improvement of quadracycline pollutant.

Claims (7)

1. a kind of composite photo-catalyst, the composite photo-catalyst is Fe3O4Nanosphere modifies g-C3N4Fe3O4/g-C3N4It is mesoporous Composite photo-catalyst, it is characterised in that prepare with the following method:
(1) precise Iron(III) chloride hexahydrate is dissolved in stirring in ethylene glycol and obtains solution A;
(2) sodium acetate is added in solution A and forms solution B;
(3) g-C is added in solution B3N4, stir and form solution C;
(4) solution C is transferred in reactor, reacts 6h in 200 DEG C of baking oven;
(5) after after naturally cool to room temperature, centrifuge, wash, be dried to obtain sample.
A kind of 2. composite photo-catalyst as claimed in claim 1, it is characterised in that the mass volume ratio of sodium acetate and ethylene glycol For 3.6g:35mL;Sodium acetate and g-C3N4Mass volume ratio be 36:5.
3. a kind of composite photo-catalyst as claimed in claim 1, it is characterised in that the amount of Iron(III) chloride hexahydrate is according to Fe3O4 And g-C3N4Mass ratio be 0.05:0.5 to 0.15:0.5, finally it is prepared into Fe3O4To g-C3N4Mass percent be 10wt% to 30wt% Fe3O4/g-C3N4Composite mesoporous photochemical catalyst.
A kind of 4. composite photo-catalyst as claimed in claim 3, it is characterised in that Fe3O4To g-C3N4Mass percent be 20wt%.
5. a kind of composite photo-catalyst as claimed in claim 1, it is characterised in that in step (3), the time of magnetic agitation is 12h。
6. a kind of composite photo-catalyst as claimed in claim 1, it is characterised in that drying temperature is 60 DEG C in step (5), is done The dry time is 12h.
7. the purposes of the composite photo-catalyst as described in claim 1-6 is any, for quadracycline of degrading under visible light Pollutant.
CN201710948003.1A 2017-10-12 2017-10-12 A kind of composite photo-catalyst and preparation method and application Pending CN107649162A (en)

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CN109647486A (en) * 2019-01-28 2019-04-19 华东交通大学 Ferroso-ferric oxide-graphite-like carbonitride composite magnetic photochemical catalyst preparation method and application
CN109847783A (en) * 2019-01-30 2019-06-07 太原理工大学 A kind of Fe3+/CdIn2S4/g-C3N4The preparation method and applications of ternary light fenton catalyst
CN109847783B (en) * 2019-01-30 2022-03-04 太原理工大学 Fe3+/CdIn2S4/g-C3N4Preparation method and application of ternary photo-Fenton catalyst
CN112044460A (en) * 2020-08-05 2020-12-08 太原理工大学 Method for enhancing mineralization of tetracycline antibiotics by graphite-phase carbon nitride
CN112044460B (en) * 2020-08-05 2022-11-08 太原理工大学 Method for enhancing graphite-phase carbon nitride mineralization tetracycline antibiotics
CN112934249A (en) * 2021-03-08 2021-06-11 西北师范大学 Preparation and application of phosphorus-doped graphite carbon nitride/ferroferric oxide composite material
CN112934249B (en) * 2021-03-08 2023-01-10 西北师范大学 Preparation and application of phosphorus-doped graphite carbon nitride/ferroferric oxide composite material
CN113856729A (en) * 2021-11-04 2021-12-31 齐鲁工业大学 Photodegradation catalyst, preparation method thereof and application thereof in degrading antibiotics
CN114029080A (en) * 2021-12-17 2022-02-11 江苏科技大学 Ternary heterojunction visible-light-driven photocatalyst and preparation method thereof
CN114029080B (en) * 2021-12-17 2024-02-27 江苏科技大学 Ternary heterojunction visible light catalyst and preparation method thereof

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