CN109233838B - Eu (Eu)3+Se codoped with Fe3O4/g-C3N4Material and application thereof in environmental remediation - Google Patents

Eu (Eu)3+Se codoped with Fe3O4/g-C3N4Material and application thereof in environmental remediation Download PDF

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CN109233838B
CN109233838B CN201811305027.6A CN201811305027A CN109233838B CN 109233838 B CN109233838 B CN 109233838B CN 201811305027 A CN201811305027 A CN 201811305027A CN 109233838 B CN109233838 B CN 109233838B
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CN109233838A (en
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李艳
马振雄
丁邦东
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Yangzhou Polytechnic Institute
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    • 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
    • AHUMAN NECESSITIES
    • A62LIFE-SAVING; FIRE-FIGHTING
    • A62DCHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
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    • B01J35/39Photocatalytic properties
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    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
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    • A62D2101/00Harmful chemical substances made harmless, or less harmful, by effecting chemical change
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    • C02F2101/00Nature of the contaminant
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    • C02F2101/22Chromium or chromium compounds, e.g. chromates
    • 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
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Abstract

The invention relates to Eu3+Se codoped with Fe3O4/g‑C3N4Materials and their use in environmental remediation by Eu3+Se co-doping to make Fe3O4/g‑C3N4The material can reduce the content of effective heavy metals in water and soil.

Description

Eu (Eu)3+Se codoped with Fe3O4/g-C3N4Material and application thereof in environmental remediation
Technical Field
The invention belongs to the field of material and environment restoration, and particularly relates to Eu3+Se codoped with Fe3O4/g-C3N4Materials and their use in environmental remediation.
Background
Graphite phase carbon nitride (g-C)3N4) The photocatalyst has responsiveness to visible light, well makes up for the defects of the traditional titanium dioxide catalyst, and is widely used for preparing composite materials in the field of photocatalysis. The invention provides a Eu3+Se codoped with Fe3O4/g-C3N4Material and method for producing the sameApplication in environmental remediation.
Disclosure of Invention
The invention provides a Eu3+Se codoped with Fe3O4/g-C3N4Material, characterized in that said Eu3+Se codoped with Fe3O4/g-C3N4The preparation method of the material comprises the following steps:
(1) dissolving ferrous sulfate, ferric chloride and europium nitrate in water, adding hydrazine hydrate containing selenium, stirring for 30min, heating to 90 ℃, reacting for 12h, naturally cooling to room temperature, filtering, washing precipitate with deionized water, and drying for later use;
(2) grinding the precipitate obtained in the step (1) and melamine uniformly by using a mortar, putting the ground precipitate and melamine into a muffle furnace, heating to 500 ℃ at a heating rate of 10 ℃/min, preserving heat for 2 hours, and naturally cooling to room temperature to obtain the Eu3+Se codoped with Fe3O4/g-C3N4A material.
The molar ratio of the ferrous sulfate, the ferric chloride and the europium nitrate in the step (1) is 5:10:1, 3mL of selenium-containing hydrazine hydrate is used for each millimole of ferrous sulfate, and the selenium-containing hydrazine hydrate contains 6mg of selenium in each milliliter of hydrazine hydrate; the dosage of the melamine in the step (2) is 3.0 times of the molar weight of the ferrous sulfate. The ferrous sulfate is preferably anhydrous ferrous sulfate or ferrous sulfate heptahydrate, and the europium nitrate is preferably europium nitrate hexahydrate.
When the ferrous sulfate, the ferric chloride and the europium nitrate are dissolved in the step (1), the amount of water is preferably enough to fully dissolve the ferrous sulfate, the ferric chloride and the europium nitrate, and preferably 15mL of water is used per millimole of the ferrous sulfate.
Another embodiment of the present invention provides the above Eu3+Se codoped with Fe3O4/g-C3N4The preparation method of the material is characterized by comprising the following steps:
(1) dissolving ferrous sulfate, ferric chloride and europium nitrate in water, adding hydrazine hydrate containing selenium, stirring for 30min, heating to 90 ℃, reacting for 12h, naturally cooling to room temperature, filtering, washing precipitate with deionized water, and drying for later use;
(2) grinding the precipitate obtained in the step (1) and melamine uniformly by using a mortar, putting the ground precipitate and melamine into a muffle furnace, heating to 500 ℃ at a heating rate of 10 ℃/min, preserving heat for 2 hours, and naturally cooling to room temperature to obtain the Eu3+Se codoped with Fe3O4/g-C3N4A material.
The molar ratio of the ferrous sulfate, the ferric chloride and the europium nitrate in the step (1) is 5:10:1, 3mL of selenium-containing hydrazine hydrate is used for each millimole of ferrous sulfate, and the selenium-containing hydrazine hydrate contains 6mg of selenium in each milliliter of hydrazine hydrate; the dosage of the melamine in the step (2) is 3.0 times of the molar weight of the ferrous sulfate. The ferrous sulfate is preferably anhydrous ferrous sulfate or ferrous sulfate heptahydrate, and the europium nitrate is preferably europium nitrate hexahydrate.
When the ferrous sulfate, the ferric chloride and the europium nitrate are dissolved in the step (1), the amount of water is preferably enough to fully dissolve the ferrous sulfate, the ferric chloride and the europium nitrate, and preferably 15mL of water is used per millimole of the ferrous sulfate.
Another embodiment of the present invention provides the above Eu3+Se codoped with Fe3O4/g-C3N4The material is applied as an environmental remediation agent.
Another embodiment of the present invention provides the above Eu3+Se codoped with Fe3O4/g-C3N4The material is applied to removing heavy metals in soil and water. The heavy metal is preferably chromium, lead or cadmium.
Another embodiment of the present invention provides the above Eu3+Se codoped with Fe3O4/g-C3N4The pesticide is preferably carbamate pesticide, and further preferably metolcarb and carbaryl.
Drawings
SEM image of product A in FIG. 1;
FIG. 2 SEM image of product C;
FIG. 3 is a diagram showing the effect of products A-E on removing hexavalent chromium from water.
Detailed Description
In order to facilitate a further understanding of the invention, the following examples are provided to illustrate it in more detail. However, these examples are only for better understanding of the present invention and are not intended to limit the scope or the principle of the present invention, and the embodiments of the present invention are not limited to the following.
Example 1
(1) Dissolving ferrous sulfate heptahydrate (5mmol), ferric chloride (10mmol) and europium nitrate hexahydrate (1mmol) in water (75mL), adding selenium-containing hydrazine hydrate (15mL and 90mg of selenium), stirring for 30min, heating to 90 ℃, reacting for 12h, naturally cooling to room temperature, filtering, washing precipitate with deionized water, and drying for later use;
(2) grinding the precipitate obtained in the step (1) and melamine (15mmol) uniformly by using a mortar, putting the ground precipitate and melamine into a muffle furnace, heating to 500 ℃ at a heating rate of 10 ℃/min, preserving heat for 2 hours, and naturally cooling to room temperature to obtain the Eu3+Se codoped with Fe3O4/g-C3N4Material (hereinafter referred to as product a).
Example 2
(1) Dissolving ferrous sulfate heptahydrate (5mmol), ferric chloride (10mmol) and europium nitrate hexahydrate (1mmol) in water (75mL), adding hydrazine hydrate (15mL), stirring for 30min, heating to 90 ℃, reacting for 12h, naturally cooling to room temperature, filtering, washing precipitate with deionized water, and drying for later use;
(2) grinding the precipitate obtained in the step (1) and melamine (15mmol) uniformly by using a mortar, putting the ground precipitate and melamine into a muffle furnace, heating to 500 ℃ at a heating rate of 10 ℃/min, preserving heat for 2 hours, and naturally cooling to room temperature to obtain Eu3+Doping with Fe3O4/g-C3N4Material (hereinafter referred to as product B).
Example 3
(1) Dissolving ferrous sulfate heptahydrate (5mmol) and ferric chloride (10mmol) in water (75mL), adding hydrazine hydrate containing selenium (15mL and 90mg containing selenium), stirring for 30min, heating to 90 ℃, reacting for 12h, naturally cooling to room temperature, filtering, washing precipitate with deionized water, and drying for later use;
(2) the precipitate obtained in step (1) was mixed with melamine (15mmol) in a mortarGrinding uniformly, placing into a muffle furnace, heating to 500 ℃ at a heating rate of 10 ℃/min, preserving heat for 2 hours, and naturally cooling to room temperature to obtain Se-doped Fe3O4/g-C3N4Material (hereinafter referred to as product C).
Example 4
(1) Dissolving ferrous sulfate heptahydrate (5mmol) and ferric chloride (10mmol) in water (75mL), adding hydrazine hydrate (15mL), stirring for 30min, heating to 90 ℃, reacting for 12h, naturally cooling to room temperature, filtering, washing precipitate with deionized water, and drying for later use;
(2) grinding the precipitate obtained in the step (1) and melamine (15mmol) uniformly by using a mortar, putting the ground precipitate and melamine into a muffle furnace, heating to 500 ℃ at a heating rate of 10 ℃/min, preserving heat for 2 hours, and naturally cooling to room temperature to obtain Fe3O4/g-C3N4Material (hereinafter referred to as product D).
Example 5
(1) Dissolving ferrous sulfate heptahydrate (5mmol), ferric chloride (10mmol) and europium nitrate hexahydrate (1mmol) in water (75mL), adding selenium-containing hydrazine hydrate (15mL and 10mg selenium-containing), stirring for 30min, heating to 90 ℃, reacting for 12h, naturally cooling to room temperature, filtering, washing precipitate with deionized water, and drying for later use;
(2) grinding the precipitate obtained in the step (1) and melamine (15mmol) uniformly by using a mortar, putting the ground precipitate and melamine into a muffle furnace, heating to 500 ℃ at a heating rate of 10 ℃/min, preserving heat for 2 hours, and naturally cooling to room temperature to obtain Eu3+Se codoped with Fe3O4/g-C3N4Material (hereinafter referred to as product E).
Example 6 experiment for removing effective heavy metals from soil
Soil sample: pb 5.25 mg/kg; cd 1.10 mg/kg.
The experimental method comprises the following steps: taking 6 parts of 1.0kg soil sample, respectively adding products A-E (20 g each) into 5 parts of the sample, uniformly mixing to ensure that the mass water content is 40-60%, taking 1 part of the sample as a blank control, placing the sample in a sunlight room, regularly turning soil once every day, and detecting the content of effective heavy metals in the soil part after one week, wherein the results are shown in the following table.
Figure BDA0001851771010000041
Example 7 soil pesticide residue degradation experiment
Selecting a soil sample: sample 1: metolcarb 200 mg/kg; sample 2: the content of the carbaryl is 200 mg/kg.
The experimental method comprises the following steps: respectively taking 6 parts of 10kg samples 1 and 2, respectively adding the products A-E (50 g each) into 5 parts of the samples, uniformly mixing to ensure that the water content is 40-50%, taking the other 1 part of the samples as a blank control, and detecting the content of the pesticide in the soil after 1 month, wherein the results are shown in the following table.
Test product Content of metolcarb (mg/kg) Content of carbaryl (mg/kg)
Product A 15 13
Product B 128 125
Product C 107 112
Product D 139 131
Product E 76 62
Blank space 154 165
Example 8 test for removing hexavalent chromium from Water
Respectively taking 100mL of hexavalent chromium standard solution (10mg/L), respectively adding 20mg of product A, B, C, D, E, stirring and reacting for 120min, wherein the absorption and removal effects of hexavalent chromium are shown in figure 3.

Claims (8)

1. Eu (Eu)3+Se codoped with Fe3O4/g-C3N4Material, characterized in that said Eu3+Se codoped with Fe3O4/g-C3N4The preparation method of the material comprises the following steps:
(1) dissolving ferrous sulfate, ferric chloride and europium nitrate in water, adding hydrazine hydrate containing selenium, stirring for 30min, heating to 90 ℃, reacting for 12h, naturally cooling to room temperature, filtering, washing precipitate with deionized water, and drying for later use;
(2) grinding the precipitate obtained in the step (1) and melamine uniformly by using a mortar, putting the ground precipitate and melamine into a muffle furnace, heating to 500 ℃ at a heating rate of 10 ℃/min, preserving heat for 2 hours, and naturally cooling to room temperature to obtain the Eu3+Se codoped with Fe3O4/g-C3N4A material.
2. Eu according to claim 13+Se codoped with Fe3O4/g-C3N4The material is characterized in that the molar ratio of the ferrous sulfate, the ferric chloride and the europium nitrate in the step (1) is 5:10:1, 3mL of selenium-containing hydrazine hydrate is used for each millimole of the ferrous sulfate, and the selenium-containing hydrazine hydrate isSelenium content 6mg per ml hydrazine hydrate.
3. Eu according to any one of claims 1 to 23+Se codoped with Fe3O4/g-C3N4The material is characterized in that the dosage of the melamine in the step (2) is 3.0 times of the molar quantity of the ferrous sulfate.
4. Eu according to claim 13+Se codoped with Fe3O4/g-C3N4The material is characterized in that the ferrous sulfate is selected from anhydrous ferrous sulfate or ferrous sulfate heptahydrate, and the europium nitrate is selected from europium nitrate hexahydrate.
5. Eu according to claim 13+Se codoped with Fe3O4/g-C3N4The material is characterized in that when ferrous sulfate, ferric chloride and europium nitrate are dissolved in the step (1), the using amount of water is 15mL of water per millimole of ferrous sulfate.
6. Eu according to any one of claims 1 to 53+Se codoped with Fe3O4/g-C3N4The material is applied as an environmental remediation agent.
7. Eu according to any one of claims 1 to 53+Se codoped with Fe3O4/g-C3N4The material is applied to removing heavy metals in soil and water.
8. Use according to claim 7, characterized in that said heavy metal is selected from chromium, lead, cadmium.
CN201811305027.6A 2018-11-02 2018-11-02 Eu (Eu)3+Se codoped with Fe3O4/g-C3N4Material and application thereof in environmental remediation Expired - Fee Related CN109233838B (en)

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