CN111135839A - Iron oxide modified attapulgite/bismuth molybdate composite photocatalyst and preparation method and application thereof - Google Patents

Iron oxide modified attapulgite/bismuth molybdate composite photocatalyst and preparation method and application thereof Download PDF

Info

Publication number
CN111135839A
CN111135839A CN201911386147.8A CN201911386147A CN111135839A CN 111135839 A CN111135839 A CN 111135839A CN 201911386147 A CN201911386147 A CN 201911386147A CN 111135839 A CN111135839 A CN 111135839A
Authority
CN
China
Prior art keywords
attapulgite
iron oxide
photocatalyst
oxide modified
tetracycline hydrochloride
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
CN201911386147.8A
Other languages
Chinese (zh)
Other versions
CN111135839B (en
Inventor
姚超
尹克诚
左士祥
李霞章
刘文杰
吴凤芹
严向玉
王灿
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Jiangsu Naou New Materials Co ltd
Original Assignee
Jiangsu Naou New Materials Co ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Jiangsu Naou New Materials Co ltd filed Critical Jiangsu Naou New Materials Co ltd
Priority to CN201911386147.8A priority Critical patent/CN111135839B/en
Publication of CN111135839A publication Critical patent/CN111135839A/en
Application granted granted Critical
Publication of CN111135839B publication Critical patent/CN111135839B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/70Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
    • B01J23/76Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/84Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36 with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
    • B01J23/85Chromium, molybdenum or tungsten
    • B01J23/88Molybdenum
    • B01J23/887Molybdenum containing in addition other metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/8876Arsenic, antimony or bismuth
    • 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
    • B01J37/02Impregnation, coating or precipitation
    • B01J37/0201Impregnation
    • 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
    • B01J37/10Heat treatment in the presence of water, e.g. steam
    • 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
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/34Organic compounds containing oxygen
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/38Organic compounds containing nitrogen
    • 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
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/30Wastewater or sewage treatment systems using renewable energies
    • Y02W10/37Wastewater or sewage treatment systems using renewable energies using solar energy

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Materials Engineering (AREA)
  • Thermal Sciences (AREA)
  • Physics & Mathematics (AREA)
  • Health & Medical Sciences (AREA)
  • Toxicology (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Catalysts (AREA)

Abstract

The invention belongs to the field of preparation of photocatalytic materials, and particularly relates to an iron oxide modified attapulgite/bismuth molybdate composite photocatalyst as well as a preparation method and application thereof. According to the invention, the attapulgite is firstly acidified, then the iron element is loaded in the attapulgite structure through impregnation, iron generates iron oxide quantum dots in the pores of the attapulgite during the heat treatment process to obtain the iron oxide modified attapulgite, so that the light responsiveness of the attapulgite is improved; then useThe modified attapulgite is used as a framework as a catalyst carrier sodium molybdate to ensure that Bi2MoO6The nanocrystalline grows along the attapulgite skeleton to obtain the composite photocatalytic material, and the invention promotes the generated Bi2MoO6The crystal grows in situ on the attapulgite, and the crystal forms a heterojunction with the attapulgite and the ferric oxide to obtain high-efficiency photocatalytic performance, and has outstanding application effect in degrading tetracycline hydrochloride.

Description

Iron oxide modified attapulgite/bismuth molybdate composite photocatalyst and preparation method and application thereof
Technical Field
The invention belongs to the field of preparation of composite materials, and particularly relates to application of an iron oxide modified attapulgite/bismuth molybdate composite photocatalyst and a preparation method thereof.
Background
Antibiotics are widely applied to human medical treatment and agricultural production, and with the increase of the dosage of the antibiotics, environmental pollution is becoming serious day by day and even poses serious threat to human health. Therefore, the removal of antibiotics from wastewater has attracted attention and is a hot topic in the field. Nowadays, a large number of methods are used for removing antibiotics, such as biological methods, physical methods, chemical methods, and the like, and in particular, photocatalytic degradation has the advantages of simple operation, high efficiency, low cost, and the like, and is considered to be an ideal technology for antibiotic treatment.
The attapulgite is a natural one-dimensional nano mineral material containing water and rich in magnesium and aluminum, but the attapulgite does not have photoresponse, so that the attapulgite is modified in the prior art to achieve the effect of visible light response, and the attapulgite is used as a photocatalyst to expand the application of the attapulgite in the field of photocatalysis.
The invention firstly uses hydrochloric acid to remove impurities and then soaks the solution containing Fe3+The solution is stirred and evaporated, and Fe (OH) is generated due to hydrolysis of iron3. High temperature calcination conditions → Fe2O3Loaded in the attapulgite structure, the photoresponse of the material is improved.
Also prepared and assembled herein as Bi2MoO6And mixing it with modified attapulgite, Fe2O3The heterojunction formed between the particles can separate oxidation and reduction reaction sites from space, and a network structure consisting of common-angle octahedrons is beneficial to carrier transmission, so that the utilization rate of photo-generated electrons and holes is effectively improved, and high-efficiency photocatalysis performance is obtained.
Disclosure of Invention
In order to fully utilize most visible light in sunlight energy and solve the problem of low utilization rate of sunlight, the invention provides an iron oxide modified attapulgite/bismuth molybdate composite photocatalytic material, iron element is loaded in an attapulgite structure by an immersion method, on one hand, iron oxide quantum dots generated in the heat treatment process of iron are in attapulgite pores, so that the light responsiveness of the attapulgite is improved; on the other hand, the attapulgite framework is used as a catalyst carrier, and Bi2MoO6The nano crystal grows on the surface of the reaction medium in situ, so that a good dispersion effect can be achieved, and the contact area between the nano crystal and the reaction medium is increased.
In addition, aiming at the defects in the prior art, the invention aims to disclose a preparation method of the iron oxide modified attapulgite/bismuth molybdate composite material, and the prepared catalyst is applied to catalytic degradation of antibiotics.
The purpose of the invention is realized by the following technical scheme that the iron oxide modified attapulgite/bismuth molybdate composite material is prepared by the following steps:
(1) firstly, preparing the iron oxide modified attapulgite: adding a certain amount of attapulgite into hydrochloric acid solution to prepare dispersed slurry, and stirring for 24h at 80 deg.C to obtain acidified attapulgite material; and then adding the acidified attapulgite into an iron chloride solution, soaking and stirring, evaporating to dryness at 80 ℃, and then carrying out heat treatment at 500 ℃ for 2h to obtain the iron oxide modified attapulgite. The concentration of the hydrochloric acid is preferably 1-8 mol/L, the solid content in the dispersed slurry is preferably 7-10%, and the concentration of the ferric chloride solution is preferably 2-6 mol/L.
Acidifying with hydrochloric acid to remove impurities and remove Ca in natural minerals2+、Mg2+、Al3+Plasma; for subsequent Fe3+The modification provides a new location. The optimal acidification concentration is 4M, and the acidification treatment time is 24 h.
(2) Adding a certain amount of bismuth nitrate pentahydrate (Bi (NO)3)3·5H2O) dispersing into 40mL of glycol solution, and magnetically stirring for 20-30min until a clear transparent solution is formed; the mass concentration of the bismuth nitrate pentahydrate solution is preferably 0.020-0.050 g/mL.
(3) Adding a certain amount of sodium molybdate (Na)2MoO4·2H2O) and the attapulgite modified by the ferric oxide are placed in deionized water for ultrasonic dispersion for 30min to obtain a uniform suspension; wherein the molar ratio of Bi to Mo is 2: 1; bi2MoO6Accounts for 15 to 100 percent of the weight of the iron oxide modified attapulgite; pre-impregnating, and adsorbing MoO by using the pore channels on the attapulgite4 2-Therefore, the bismuth molybdate crystals formed subsequently can grow along the attapulgite framework, a heterojunction can be formed favorably, the binding force is improved, and the bismuth molybdate crystals cannot grow along the attapulgite framework and are difficult to form the heterojunction if the bismuth molybdate crystals are not soaked in advance.
(4) And (3) adding the suspension prepared in the step (3) into the step (2), transferring the suspension to a hydrothermal kettle, carrying out hydrothermal treatment for 10-24h at the temperature of 160-180 ℃, carrying out suction filtration, washing and drying to obtain the iron oxide modified attapulgite/bismuth molybdate composite material.
The invention has the beneficial effects that: the invention adopts a hydrothermal method to prepare the iron oxide modified attapulgite/bismuth molybdate composite material, and has the advantages of simple method, easy operation, low cost and the like.
The attapulgite utilized by the invention is cheap and easy to obtain, has better adsorption performance and more active sites, and can be used as an excellent carrier of the catalyst after being subjected to acidizing and dipping treatment. Iron oxide quantum dots (the size of the iron oxide quantum dots is smaller than or close to the exciton Bohr radius, and the general diameter is not more than 10nm) are generated after the iron oxide enters an attapulgite structure for heat treatment, so that the concave is improvedLight responsiveness of attapulgite. Then loading Bi thereon2MoO6Nanocrystalline, Fe2O3And Bi2MoO6And a heterojunction is formed, and the carrier separation efficiency is synergistically improved.
Mixing sodium molybdate (Na)2MoO4·2H2O) and attapulgite modified by ferric oxide are ultrasonically dispersed together, and the aim is to pre-disperse MoO4 2-Ions are pre-combined with the ferric oxide quantum dots in the modified attapulgite pore structure, so that Bi is convenient2MoO6The crystal grows on the attapulgite in situ to form a heterojunction between the crystal and the attapulgite, so that the carrier separation efficiency is effectively improved.
Drawings
FIG. 1 is a TEM image of the iron oxide-modified attapulgite and the composite material of example 2;
FIGS. 1(a), (b) are iron oxide modified attapulgite materials from which it can be seen that iron oxide quantum dots are deposited on an attapulgite structure; FIG. 1(c) is an image of the composite material prepared in example 2, in which the compact bismuth molybdate crystals coated on the surface of attapulgite are seen, and in the high-order image of FIG. 1(d), the lattice lines of iron oxide and bismuth molybdate are clearly seen, and the two are tightly combined together.
FIG. 2 is a graph showing the degradation performance of tetracycline hydrochloride in examples 1 to 3 and comparative examples 1 to 2.
Detailed Description
Embodiments of the present invention will now be described in detail with reference to the following examples, which are intended to be illustrative of the present invention and should not be construed as limiting the scope of the invention. The examples were carried out under the conventional conditions, unless otherwise specified. The reagents or instruments used are not indicated by the manufacturer, and are all conventional products available commercially.
The degradation performance test used in the experiments was,
the experiment uses tetracycline hydrochloride as a degradation object and a 300W high-pressure mercury lamp as a light source. 0.10g of the catalyst was weighed into a photochemical reactor, and then a prepared tetracycline hydrochloride solution (20mg/L, 100mL) was added thereto, and the mixture was cooled to room temperature. Starting a magnetic stirring device, introducing air from the bottom of the bottle for bubbling, carrying out dark adsorption for 30min to ensure that the solution reaches adsorption and desorption balance, then starting a mercury lamp (carrying an optical filter, filtering out ultraviolet light, and measuring under the condition that the wavelength is more than 420 nm), periodically sampling for 10mL, taking supernatant after centrifugal separation, measuring the absorbance of the supernatant at the wavelength of 352nm on a UV-3600 type ultraviolet-visible spectrophotometer, and calculating the degradation rate by the following formula:
η=(1-At/A0)×100%
wherein η is the degradation rate (%), A0As absorbance of stock solution, AtAbsorbance of the solution after t time
The preparation process of the iron oxide modified attapulgite/bismuth molybdate composite material comprises the following steps:
example 1
(1) Firstly, preparing the iron oxide modified attapulgite: adding 5.0g attapulgite into 40mL hydrochloric acid solution (4M) to prepare dispersed slurry, and stirring at 80 deg.C for 12 hr to obtain acidified attapulgite material; and then adding the acidified attapulgite into 80mL of ferric chloride solution (4M), soaking and stirring, evaporating to dryness at 80 ℃, and then carrying out heat treatment at 500 ℃ for 2h to obtain the iron oxide modified attapulgite.
(2) Adding 1mmol of bismuth nitrate pentahydrate (Bi (NO)3)3·5H2O) is dispersed into 40mL of glycol solution, and is magnetically stirred for 30min until a clear transparent solution is formed;
(3) adding 0.5mmol of sodium molybdate (Na)2MoO4·2H2O) and 1496.2mg of iron oxide modified attapulgite are placed in deionized water for ultrasonic dispersion for 30min to obtain a uniform suspension;
(4) and (3) adding the suspension prepared in the step (3) into the step (2), transferring the suspension into a hydrothermal kettle, carrying out hydrothermal treatment at 160 ℃ for 12 hours, carrying out suction filtration, washing and drying to obtain the iron oxide modified attapulgite/bismuth molybdate composite material with the mass content of bismuth molybdate being 30%.
After 3 hours of photocatalytic degradation, the tetracycline hydrochloride degradation efficiency of the catalyst is measured as follows: 73.58 percent.
Example 2
(1) Firstly, preparing the iron oxide modified attapulgite: adding 5.0g attapulgite into 40mL hydrochloric acid solution (4M) to prepare dispersed slurry, and stirring at 80 deg.C for 24 hr to obtain acidified attapulgite material; and then adding the acidified attapulgite into 80mL of ferric chloride solution (4M), soaking and stirring, evaporating to dryness at 80 ℃, and then carrying out heat treatment at 500 ℃ for 2h to obtain the iron oxide modified attapulgite.
(2) Adding 2mmol of bismuth nitrate pentahydrate (Bi (NO)3)3·5H2O) is dispersed into 40mL of glycol solution, and is magnetically stirred for 30min until a clear transparent solution is formed;
(3) adding 1mmol of sodium molybdate (Na)2MoO4·2H2O) and 1795.5mg of iron oxide modified attapulgite are placed in deionized water for ultrasonic dispersion for 30min to obtain a uniform suspension;
(4) and (3) adding the suspension prepared in the step (3) into the step (2), transferring the suspension into a hydrothermal kettle, carrying out hydrothermal treatment at 160 ℃ for 12 hours, carrying out suction filtration, washing and drying to obtain the iron oxide modified attapulgite/bismuth molybdate composite material with the mass content of bismuth molybdate of 50%.
After 3 hours of photocatalytic degradation, the tetracycline hydrochloride degradation efficiency of the catalyst is measured as follows: 92.09 percent.
As can be seen from figure 1, the iron oxide quantum dots are deposited on the attapulgite structure, and the particle size of the iron oxide is obviously less than 10 nm; and the surface of the attapulgite is coated with compact bismuth molybdate crystals. If loaded, Bi is generated2MoO6The crystal is loaded with ferric oxide and bismuth molybdate with larger grain diameter, and Bi is prepared firstly2MoO6The crystals are easy to block the pores dissolved out by the prior acidification treatment, are not favorable for the subsequent tight combination of the iron oxide semiconductor material and the attapulgite main body structure, and have poor structural stability of the catalyst.
Example 3
(1) Firstly, preparing the iron oxide modified attapulgite: adding 1.0g attapulgite into 40mL hydrochloric acid solution (4M) to prepare dispersed slurry, and stirring at 80 deg.C for 12 hr to obtain acidified attapulgite material; and then adding the acidified attapulgite into 80mL of ferric chloride solution (2M), soaking and stirring, evaporating to dryness at 80 ℃, and then carrying out heat treatment at 500 ℃ for 3h to obtain the iron oxide modified attapulgite.
(2) 2mmol bismuth nitrate pentahydrate (Bi (NO)3)3·5H2O) is dispersed into 40mL of glycol solution, and is magnetically stirred for 30min until a clear transparent solution is formed;
(3) adding 1mmol of sodium molybdate (Na)2MoO4·2H2O) and 897.8mg of iron oxide modified attapulgite are placed in deionized water for ultrasonic dispersion for 30min to obtain a uniform suspension;
(4) and (3) adding the suspension prepared in the step (3) into the step (2), transferring the suspension into a hydrothermal kettle, carrying out hydrothermal treatment for 18h at 160 ℃, carrying out suction filtration, washing and drying to obtain the iron oxide modified attapulgite/bismuth molybdate composite material with the mass content of bismuth molybdate being 100%.
After 3 hours of photocatalytic degradation, the tetracycline hydrochloride degradation efficiency of the catalyst is measured as follows: 81.84 percent.
Comparative example 1
(1) Firstly, preparing acidified attapulgite: adding 5.0g attapulgite into 40mL hydrochloric acid solution (4M) to prepare dispersed slurry, and stirring at 80 deg.C for 24 hr to obtain acidified attapulgite material; heat treatment is carried out for 2h at 500 ℃ to obtain the acidified attapulgite material.
(2) Adding 1mmol of bismuth nitrate pentahydrate (Bi (NO)3)3·5H2O) is dispersed into 40mL of glycol solution, and is magnetically stirred for 30min until a clear transparent solution is formed;
(3) adding 0.5mmol of sodium molybdate (Na)2MoO4·2H2O) and 1496.2mg of acidified and modified attapulgite are placed in deionized water for ultrasonic dispersion for 30min to obtain a uniform suspension;
(4) and (3) adding the suspension prepared in the step (3) into the step (2), transferring the suspension into a hydrothermal kettle, carrying out hydrothermal treatment at 160 ℃ for 12 hours, carrying out suction filtration, washing and drying to obtain the modified attapulgite/bismuth molybdate composite material with the mass ratio of 30%.
After 3 hours of photocatalytic degradation, the tetracycline hydrochloride degradation efficiency of the catalyst is measured as follows: 56.04 percent.
Comparative example 2
(1) Firstly, preparing the iron oxide modified attapulgite: adding 10.0g attapulgite into 40mL hydrochloric acid solution (6M) to prepare dispersed slurry, and stirring at 80 deg.C for 12 hr to obtain acidified attapulgite material; and then adding the acidified attapulgite into 80mL of ferric chloride solution (2M), soaking and stirring, evaporating to dryness at 80 ℃, and then carrying out heat treatment at 500 ℃ for 5h to obtain the iron oxide modified attapulgite.
(2) Adding 1mmol of bismuth nitrate pentahydrate (Bi (NO)3)3·5H2O) is dispersed into 40mL of glycol solution, and is magnetically stirred for 30min until a clear transparent solution is formed;
(3) adding 0.5mmol of sodium molybdate (Na)2MoO4·2H2O) and 1496.2mg of iron oxide modified attapulgite are placed in deionized water for ultrasonic dispersion for 30min to obtain a uniform suspension;
(4) and (3) adding the suspension prepared in the step (3) into the step (2), transferring the suspension into a hydrothermal kettle, carrying out hydrothermal treatment at 160 ℃ for 12 hours, carrying out suction filtration, washing and drying to obtain the iron oxide modified attapulgite/bismuth molybdate composite material with the mass ratio of 30%.
After 3 hours of photocatalytic degradation, the tetracycline hydrochloride degradation efficiency of the catalyst is measured as follows: 63.02 percent.
The raw materials and equipment used in the invention are common raw materials and equipment in the field if not specified; the methods used in the present invention are conventional in the art unless otherwise specified. The above description is only a preferred embodiment of the present invention, and is not intended to limit the present invention, and all modifications of the above embodiments made according to the technical spirit of the present invention are included in the scope of the present invention.

Claims (8)

1. A photocatalyst for degrading tetracycline hydrochloride is characterized in that: the photocatalyst is an iron oxide modified attapulgite/bismuth molybdate composite material.
2. A method for preparing the photocatalyst for degrading tetracycline hydrochloride according to claim 1, wherein the preparation step comprises:
(1) adding attapulgite into a hydrochloric acid solution to prepare dispersion slurry, and carrying out hydrothermal stirring for a period of time to obtain an acidified attapulgite material; and then adding the acidified attapulgite into an iron chloride solution, soaking and stirring, evaporating to dryness, and performing heat treatment to obtain the iron oxide modified attapulgite.
(2) Adding bismuth nitrate pentahydrate (Bi (NO)3)3·5H2O) dispersing into the ethylene glycol solution, and stirring to obtain a clear transparent solution;
(3) mixing sodium molybdate (Na)2MoO4·2H2O) and the attapulgite modified by the ferric oxide are placed in deionized water for ultrasonic dispersion to obtain a uniform turbid liquid;
(4) and (3) adding the suspension prepared in the step (3) into the transparent solution prepared in the step (2), transferring the transparent solution to a hydrothermal kettle for hydrothermal reaction, and performing suction filtration, washing and drying after the reaction to prepare the iron oxide modified attapulgite/bismuth molybdate composite material.
3. The method for preparing the photocatalyst for degrading tetracycline hydrochloride according to claim 2, wherein: the step (1) is to stir the mixture for 24 hours in a hydrothermal way at the temperature of 80 ℃, and the heat treatment condition is to heat treat the mixture for 2 hours at the temperature of 500 ℃.
4. The method for preparing the photocatalyst for degrading tetracycline hydrochloride according to claim 2, wherein: in the bismuth nitrate pentahydrate and the sodium molybdate, the molar ratio of Bi/Mo is 2: 1.
5. The method for preparing the photocatalyst for degrading tetracycline hydrochloride according to claim 2, wherein: the Bi2MoO6The mass ratio of the attapulgite to the iron oxide modified attapulgite is 0.15-1: 1.
6. The method for preparing the photocatalyst for degrading tetracycline hydrochloride according to claim 2, wherein: the hydrothermal reaction conditions in the step (4) are as follows: carrying out hydrothermal reaction for 10-24h at 160-180 ℃.
7. The method for preparing the photocatalyst for degrading tetracycline hydrochloride according to claim 2, characterized in that: the iron oxide modified attapulgite is formed by generating iron oxide quantum dots in an attapulgite structure, wherein the size of the iron oxide is not more than 10 nm.
8. Use of a photocatalyst according to any one of claims 1 to 7 for the degradation of tetracycline hydrochloride.
CN201911386147.8A 2019-12-29 2019-12-29 Iron oxide modified attapulgite/bismuth molybdate composite photocatalyst and preparation method and application thereof Active CN111135839B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201911386147.8A CN111135839B (en) 2019-12-29 2019-12-29 Iron oxide modified attapulgite/bismuth molybdate composite photocatalyst and preparation method and application thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201911386147.8A CN111135839B (en) 2019-12-29 2019-12-29 Iron oxide modified attapulgite/bismuth molybdate composite photocatalyst and preparation method and application thereof

Publications (2)

Publication Number Publication Date
CN111135839A true CN111135839A (en) 2020-05-12
CN111135839B CN111135839B (en) 2022-12-30

Family

ID=70521448

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201911386147.8A Active CN111135839B (en) 2019-12-29 2019-12-29 Iron oxide modified attapulgite/bismuth molybdate composite photocatalyst and preparation method and application thereof

Country Status (1)

Country Link
CN (1) CN111135839B (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111974376A (en) * 2020-09-04 2020-11-24 河南师范大学 Bi2MoO6Preparation method and application of photocatalyst
CN112264098A (en) * 2020-12-15 2021-01-26 兰州理工大学 Iron oxide-loaded attapulgite-chitosan heterogeneous composite catalyst and preparation method thereof

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107649117A (en) * 2017-10-27 2018-02-02 盛世园林集团股份有限公司 A kind of bismuth molybdate/attapulgite clay compounded visible light catalytic material and preparation method thereof, application
CN108479777A (en) * 2018-03-28 2018-09-04 常州大学 A kind of preparation method and applications of attapulgite composite photo-catalyst
CN108906068A (en) * 2018-06-12 2018-11-30 延安大学 Iron (III)/molybdic acid bismuthino composite photocatalyst material and preparation method with oxygen defect
CN110465287A (en) * 2019-08-02 2019-11-19 南京理工大学 A kind of bismuth molybdate-concave convex rod composite material and preparation method

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107649117A (en) * 2017-10-27 2018-02-02 盛世园林集团股份有限公司 A kind of bismuth molybdate/attapulgite clay compounded visible light catalytic material and preparation method thereof, application
CN108479777A (en) * 2018-03-28 2018-09-04 常州大学 A kind of preparation method and applications of attapulgite composite photo-catalyst
CN108906068A (en) * 2018-06-12 2018-11-30 延安大学 Iron (III)/molybdic acid bismuthino composite photocatalyst material and preparation method with oxygen defect
CN110465287A (en) * 2019-08-02 2019-11-19 南京理工大学 A kind of bismuth molybdate-concave convex rod composite material and preparation method

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
YANQING YANG ET AL.: "A three-dimensional (3D) structured Bi2WO6-palygorskite composite and their enhanced visible light photocatalytic property", 《SEPARATION AND PURIFICATION TECHNOLOGY》 *
张倩萍等: "Fe2O3/凹凸棒土吸附-光催化法处理间氯甲苯工业废水研究", 《精细与专用化学品》 *

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111974376A (en) * 2020-09-04 2020-11-24 河南师范大学 Bi2MoO6Preparation method and application of photocatalyst
CN112264098A (en) * 2020-12-15 2021-01-26 兰州理工大学 Iron oxide-loaded attapulgite-chitosan heterogeneous composite catalyst and preparation method thereof

Also Published As

Publication number Publication date
CN111135839B (en) 2022-12-30

Similar Documents

Publication Publication Date Title
CN101574652B (en) Loaded photo-catalyst and preparation method and use thereof
CN102389837A (en) Magnetic polypyrrole/titanium dioxide/clay nano-composite photocatalyst and preparation method thereof
CN103100398A (en) Preparation method of natural zeolite loaded one-dimensional TiO2 nanowire with high catalytic activity
CN108654678A (en) One type Fenton oxidation catalyst and its application
CN111135839B (en) Iron oxide modified attapulgite/bismuth molybdate composite photocatalyst and preparation method and application thereof
CN111036265A (en) Composite nano photocatalyst CDs-N-BiOCl and preparation method and application thereof
CN104941584A (en) SiO2/C composite material for adsorbing heavy metal ions in water body and application thereof
CN108686658B (en) C-QDs-Fe2O3/TiO2Composite photocatalyst and preparation method thereof
CN105618050A (en) Visible-light responded compound catalyst for degrading organic pollutants in salt-containing wastewater and preparation method of visible-light responded compound catalyst
CN113398936A (en) Zinc oxide/ZnFe-LDH @ charcoal visible-light-driven photocatalyst and preparation method and application thereof
CN112958061A (en) Oxygen vacancy promoted direct Z mechanism mesoporous Cu2O/TiO2Photocatalyst and preparation method thereof
CN112246283A (en) Bismuth tungstate @ MIL-100(Fe) composite material and preparation method and application thereof
CN112774718A (en) Cuprous oxide/tubular graphite-like phase carbon nitride composite catalyst and preparation method and application thereof
CN111790414A (en) Mixed crystal TiO2BiOBr composite material and preparation method and application thereof
CN111744503A (en) Z-shaped heterojunction MoS2/Bi2WO6Composite photocatalyst and preparation method and application thereof
CN110743575A (en) AgIn with adsorption-photocatalysis synergistic effect5S8/SnS2Method for preparing solid solution catalyst
CN101716501B (en) Zinc titanate micro-nano photocatalysis material and preparation method thereof
CN113398914A (en) Preparation method of visible light catalyst synthesized by one-pot hydrothermal method
CN108187701B (en) Preparation method of AgCl/BiOCl photocatalyst with tubular AgCl structure
CN109331846A (en) Preparation method of the compound bismuth tungstate of nano silver/silver bromide and products thereof and application
CN109046341A (en) A kind of preparation method of visible light-responded silver silicate/concave convex rod composite catalyst
CN113856616A (en) Zirconium-containing silicon-based adsorbent, preparation method thereof and application of adsorbent in removing methylene blue in water
CN113893841A (en) Barium titanate nano material for piezoelectric catalytic degradation of trace organic pollutants in water and preparation and application thereof
CN112718001A (en) Nano cellulose based aerogel composite photocatalyst and application thereof
CN111573818A (en) Ozone catalytic membrane reactor assembly and application method thereof in water treatment engineering

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant