CN113058542A - Preparation method and application of copper oxide @ hydrotalcite hybrid material - Google Patents

Preparation method and application of copper oxide @ hydrotalcite hybrid material Download PDF

Info

Publication number
CN113058542A
CN113058542A CN202110321165.9A CN202110321165A CN113058542A CN 113058542 A CN113058542 A CN 113058542A CN 202110321165 A CN202110321165 A CN 202110321165A CN 113058542 A CN113058542 A CN 113058542A
Authority
CN
China
Prior art keywords
copper oxide
hydrotalcite
hybrid material
copper
solution
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
Application number
CN202110321165.9A
Other languages
Chinese (zh)
Inventor
陈晓浪
陈少棚
邓桢澜
郭建兵
陆宗承
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.)
Sichuan Jiahe Co Ltd
Original Assignee
Sichuan Jiahe 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 Sichuan Jiahe Co Ltd filed Critical Sichuan Jiahe Co Ltd
Priority to CN202110321165.9A priority Critical patent/CN113058542A/en
Publication of CN113058542A publication Critical patent/CN113058542A/en
Pending legal-status Critical Current

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
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/06Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising oxides or hydroxides of metals not provided for in group B01J20/04
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J20/00Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
    • B01J20/02Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
    • B01J20/06Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising oxides or hydroxides of metals not provided for in group B01J20/04
    • B01J20/08Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising oxides or hydroxides of metals not provided for in group B01J20/04 comprising aluminium oxide or hydroxide; comprising bauxite
    • 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
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/288Treatment of water, waste water, or sewage by sorption using composite sorbents, e.g. coated, impregnated, multi-layered
    • 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
    • C02F2101/308Dyes; Colorants; Fluorescent agents
    • 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
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • C02F2101/40Organic compounds containing sulfur

Abstract

The invention discloses a preparation method and application of a copper oxide @ hydrotalcite hybrid material, wherein the preparation method comprises the following steps: firstly, preparing a copper oxide template with a microsphere appearance in advance, then ultrasonically dispersing the copper oxide template in water, co-precipitating a metal salt solution and an alkali liquor in a copper oxide dispersion system, and carrying out crystallization growth at a high temperature to obtain a hybridized copper oxide @ hydrotalcite material; the material is applied to adsorbing Congo red dye. According to the copper oxide @ hydrotalcite material prepared by the invention, on one hand, the modified hybrid material has a microsphere shape, and the specific surface area is obviously increased compared with that of the hybrid material before being unmodified; on the other hand, the modified hybrid material has more excellent Congo red adsorption performance, and the removal rate of the dye in the water body is improved.

Description

Preparation method and application of copper oxide @ hydrotalcite hybrid material
Technical Field
The invention belongs to the field of water adsorption treatment technology and environmental management, and particularly relates to a preparation method and application of a copper oxide @ hydrotalcite hybrid material.
Background
Hydrotalcite (LDH) based materials are two-dimensional inorganic materials with a unique layer structure, the chemical components of the layer are mainly metal ions with positive charges, and negative ion groups with negative charges are arranged between layers. Because the typical structural advantage of the hydrotalcite endows the hydrotalcite with electrostatic effect, ion exchange effect and the like on the pollutants of the dye, the hydrotalcite has more research and application in the aspect of adsorbing and removing the pollutants in the water body.
When the pure hydrotalcite is used as an adsorbent, the defects of low adsorption efficiency, limited adsorption capacity and the like exist, and the metal positive charge density, interlayer spacing and growth morphology on the surface of the hydrotalcite can influence the performance of the hydrotalcite to a certain extent, so that the existing adsorption material based on the hydrotalcite needs to be modified and designed, and the use value of the adsorption material as the adsorbent is improved.
In recent years, a research direction for regulating and controlling the functionality of hydrotalcite by introducing a modification method of a template to control the growth morphology of the hydrotalcite appears, for example, the hydrotalcite is grown outside the nanofiber by adopting a hydrothermal method by adopting a nanowire as the template, so that a nanofiber-hydrotalcite composite material is obtained, and the hydrotalcite-based composite material has better efficiency when being used for adsorbing heavy metal ions in a water body; in addition, the research is that the specific surface area and pore volume of the prepared material are larger by introducing one-step hybridization of graphene oxide and hydrotalcite, and the adsorption application is more facilitated. However, the current research on the adsorbent material has several defects: (1) the preparation process of the material is complicated, and the reaction conditions required by the experiment are not suitable for large-scale production; (2) the preparation process uses more organic solvents, and is easy to cause pollution and the like. Therefore, designing an adsorbent material with simple manufacturing process, low production cost and no self-pollution is a direction of important consideration in subsequent research.
Disclosure of Invention
In view of the above, the invention aims to provide a preparation method and an adsorption application of a copper oxide @ hydrotalcite hybrid material, and when the hydrotalcite-based modified material prepared by the method is used as an adsorbent, the hydrotalcite-based modified material has the advantages of high adsorption efficiency, good stability, low production cost and easiness in operation, and is relatively suitable for treatment of printing and dyeing wastewater in industry due to a simple preparation process; and the method can obtain the copper oxide @ hydrotalcite hybrid material with the best relative adsorption performance by changing the proportion of the copper oxide.
The preparation method of the copper oxide @ hydrotalcite hybrid material comprises the following steps:
step 1: and (3) preparing a copper oxide template with a microsphere shape in advance.
Weighing copper sulfate pentahydrate in a flask, adding deionized water, stirring for dissolving, dissolving ammonium oxalate in the deionized water to prepare a solution, quickly transferring the ammonium oxalate solution into the flask, heating to 70 ℃, magnetically stirring for 3 hours, and then performing suction filtration, washing and drying to obtain a copper oxalate precursor; and finally, putting the copper oxalate precursor obtained by the reaction into a muffle furnace, and calcining for 2 hours at 500 ℃ to obtain a copper oxide template sample.
Step 2: preparing the copper oxide @ hydrotalcite material.
Dispersing the prepared copper oxide sample in deionized water, adding the obtained product into a four-neck flask after ultrasonic dispersion, preparing a sodium nitrate solution, adding the obtained product into the flask, preparing a mixed metal salt solution of magnesium nitrate hexahydrate and aluminum nitrate nonahydrate, quickly adding the mixed metal salt solution of magnesium and aluminum into the flask, stirring, preparing a sodium hydroxide alkali liquor with a certain concentration, titrating the metal salt solution of magnesium and aluminum and the alkali liquor into the flask simultaneously under the protection of nitrogen atmosphere, quickly stirring in the titration process, controlling the titration rate of the alkali liquor so that the pH value of a reaction system in the titration process is 10, stirring for 1 hour after the titration is finished, heating to 75 ℃, standing and aging for 24 hours, performing suction filtration, washing and drying to obtain a hybrid sample precursor; and finally, placing the hybrid sample precursor prepared by the reaction in a muffle furnace at 500 ℃ to calcine for 4 hours to obtain the copper oxide @ hydrotalcite hybrid material.
Preferably, the mole ratio of the copper sulfate pentahydrate to the ammonium oxalate added in the step 1 is 1; the molar concentrations of copper ions and oxalate anions in deionized water are both 0.1 mol/L.
Preferably, the reaction in step 1 is carried out after the temperature is raised to 70 ℃ in advance; the stirring rate was kept constant during the reaction.
Preferably, the specific gravity of the copper oxide sample in the step 2 is 3-20 wt%; the ultrasonic dispersion time is 0.5-3 hours; the concentration of the sodium nitrate solution is 2 mol/L; the molar ratio of magnesium ions to aluminum ions in the solution is 3: 1; the concentration of the sodium hydroxide solution is 2 mol/L; and keeping the pH value of 9.8-10.2 in the reaction process.
Preferably, the deionized water used in the experimental reaction in step 2 needs to be boiled to remove CO2Processing; at the same time, the reaction system is strictly controlled at the strict N2The method is carried out under the protection of atmosphere.
The copper oxide @ hydrotalcite hybrid material prepared by the preparation method disclosed by the invention is applied to adsorption of Congo red dye.
The method for adsorbing Congo red dye by using the copper oxide @ hydrotalcite hybrid material disclosed by the invention uses the hybrid material; carrying out an adsorption test in a water bath constant temperature oscillator which is protected from light; the oscillation rate was 150 rpm; the shaking time is 360 minutes; the shaking temperature was room temperature.
The mechanism of the method is as follows: synthesizing and preparing CuO in a controllable microsphere shape through inorganic chemical reaction; then carrying out hybrid growth of hydrotalcite and copper oxide together by using CuO as a template through a coprecipitation method; and finally, calcining in a muffle furnace to obtain the modified copper oxide @ hydrotalcite hybrid material.
Compared with the prior art, the invention has the beneficial effects that:
compared with the existing research on the aspect that hydrotalcite hybridization modification is used for adsorbing Congo red dye, the method combines the characteristic that the spherical morphology has the maximum specific surface area, and takes copper oxide microspheres as a template to directionally regulate the hybridization growth of hydrotalcite to form the microsphere morphology, so that the obtained hybridization modified material has the relatively maximum specific surface area, and the maximized adsorption performance of the material is realized. By adjusting the relative content of the copper oxide template, the optimal hybridization proportion for high-efficiency adsorption is explored, and the preparation method and experimental parameters of the hybrid material with the optimal adsorption performance are obtained.
Drawings
FIG. 1 is an X-ray diffraction pattern of the prepared CuO template, calcined hydrotalcite derived oxide and hybrid modified copper oxide @ hydrotalcite.
FIG. 2 is an FTIR plot of prepared CuO template, hydrotalcite calcined derivative oxide and hybrid modified copper oxide @ hydrotalcite.
Fig. 3 is an SEM photograph of the prepared hybrid modified copper oxide @ hydrotalcite.
Fig. 4 is a TEM photograph of the prepared hybrid modified copper oxide @ hydrotalcite.
FIG. 5 shows Congo red adsorption performance of the prepared CuO template, calcined hydrotalcite derived oxide and hybrid modified copper oxide @ hydrotalcite.
Detailed Description
The present invention will be described in further detail with reference to the accompanying drawings and specific embodiments.
Example 1
A. 2.5g of copper sulfate pentahydrate (CuSO) are weighed out4·5H2O) reagent was dissolved in 100mL of water, and 1.42g of ammonium oxalate ((NH)4)2C2O4·H2O) is dissolved in 100mL of water, then the ammonium oxalate solution is rapidly added into the copper sulfate solution, stirred for 3 hours at 70 ℃, filtered, washed and dried to obtain CuC2O4·H2An O precursor; the obtained CuC2O4·H2And calcining the O precursor in a muffle furnace at 500 ℃ for 2 hours to obtain a CuO sample with a microsphere morphology.
B. Dispersing 0.06g of the CuO sample obtained in the step A in 20mL of deionized water, performing ultrasonic dispersion for 0.5 hour, adding the mixture into a four-neck flask, weighing 4.25g of sodium nitrate, dissolving the sodium nitrate in 30mL of deionized water, then respectively dissolving 9.62g of magnesium nitrate hexahydrate and 4.69g of aluminum nitrate nonahydrate in 50mL of deionized water, then rapidly adding the sodium nitrate solution into the flask, stirring, preparing 2mol/L of sodium hydroxide alkaline solution, titrating the magnesium and aluminum metal salt solution and the alkaline solution into the flask simultaneously under the protection of nitrogen atmosphere, rapidly stirring in the titration process, controlling the titration rate of the alkaline solution to ensure that the pH value of a reaction system in the titration process is 9.8-10.2, stirring for 1 hour after the titration is completed, then heating to 75 ℃, standing for 24 hours, performing suction filtration, water washing and drying to obtain a hybrid sample precursor; and finally, placing the hybrid sample precursor prepared by the reaction in a muffle furnace at 500 ℃ to calcine for 4 hours to obtain a copper oxide @ hydrotalcite sample.
And B, putting 50mg of the copper oxide @ hydrotalcite hybrid material prepared in the step B into a 250mL reagent bottle with a small opening, adding a Congo red solution with the initial concentration of 50mg/L into the bottle, oscillating at the constant temperature of 150rpm for 360 minutes at room temperature, sampling at regular intervals to determine the residual concentration of the Congo red, and calculating to obtain the maximum adsorption capacity of 327 mg/g.
Example 2
A. 2.5g of copper sulfate pentahydrate (CuSO) are weighed out4·5H2O) reagent was dissolved in 100mL of water, and 1.42g of ammonium oxalate ((NH)4)2C2O4·H2O) is dissolved in 100mL of water, then the ammonium oxalate solution is rapidly added into the copper sulfate solution, stirred for 3 hours at 70 ℃, filtered, washed and dried to obtain CuC2O4·H2An O precursor; the obtained CuC2O4·H2And calcining the O precursor in a muffle furnace at 500 ℃ for 2 hours to obtain a copper oxide sample with a microsphere morphology.
B. Dispersing 0.1g of the CuO sample obtained in the step A in 20mL of deionized water, adding the mixture into a four-neck flask after ultrasonic dispersion is carried out for 1 hour, weighing 4.25g of sodium nitrate to dissolve in 30mL of deionized water, then respectively dissolving 9.62g of magnesium nitrate hexahydrate and 4.69g of aluminum nitrate nonahydrate in 50mL of deionized water, then quickly adding the sodium nitrate solution into the flask for stirring, additionally preparing 2mol/L of sodium hydroxide alkaline solution, titrating the metal salt solution of magnesium and aluminum and the alkaline solution into the flask simultaneously under the protection of nitrogen atmosphere, quickly stirring in the titration process, controlling the titration rate of the alkaline solution to ensure that the pH value of a reaction system in the titration process is 9.8-10.2, stirring for 1 hour after the titration is finished, then heating to 75 ℃, standing and aging for 24 hours, carrying out suction filtration, water washing and drying to obtain a hybrid sample precursor; and finally, placing the hybrid sample precursor prepared by the reaction in a muffle furnace at 500 ℃ to calcine for 4 hours to obtain the copper oxide @ hydrotalcite hybrid material.
And B, putting 50mg of the copper oxide @ hydrotalcite hybrid material prepared in the step B into a 250mL reagent bottle with a small opening, adding a Congo red solution with the initial concentration of 50mg/L into the bottle, oscillating at the constant temperature of 150rpm for 360 minutes at room temperature, sampling at regular intervals to determine the residual concentration of the Congo red, and calculating to obtain the maximum adsorption capacity of 490 mg/g.
Example 3
A. 2.5g of copper sulfate pentahydrate (CuSO) are weighed out4·5H2O) reagent was dissolved in 100mL of water, and 1.42g of ammonium oxalate ((NH)4)2C2O4·H2O) is dissolved in 100mL of water, then the ammonium oxalate solution is rapidly added into the copper sulfate solution, stirred for 3 hours at 70 ℃, filtered, washed and dried to obtain CuC2O4·H2An O precursor; the obtained CuC2O4·H2And calcining the O precursor in a muffle furnace at 500 ℃ for 2 hours to obtain a CuO sample with a microsphere morphology.
B. Dispersing 0.2g of the CuO sample obtained in the step A in 20mL of deionized water, adding the mixture into a four-neck flask after ultrasonic dispersion is carried out for 2 hours, weighing 4.25g of sodium nitrate to dissolve in 30mL of deionized water, then respectively dissolving 9.62g of magnesium nitrate hexahydrate and 4.69g of aluminum nitrate nonahydrate in 50mL of deionized water, then quickly adding the sodium nitrate solution into the flask for stirring, additionally preparing 2mol/L of sodium hydroxide alkaline solution, titrating the metal salt solution of magnesium and aluminum and the alkaline solution into the flask simultaneously under the protection of nitrogen atmosphere, quickly stirring in the titration process, controlling the titration rate of the alkaline solution to enable the pH of the reaction system in the titration process to be 9.8-10, stirring for 1 hour after the titration is finished, then heating to 75 ℃, standing and aging for 24 hours, carrying out suction filtration, water washing and drying to obtain a hybrid sample precursor; and finally, placing the hybrid sample precursor prepared by the reaction in a muffle furnace at 500 ℃ to calcine for 4 hours to obtain the copper oxide @ hydrotalcite hybrid material.
And B, putting 50mg of the copper oxide @ hydrotalcite hybrid material prepared in the step B into a 250mL reagent bottle with a small opening, adding a Congo red solution with the initial concentration of 50mg/L into the bottle, oscillating at the constant temperature of 150rpm for 360 minutes at room temperature, sampling at regular intervals to determine the residual concentration of the Congo red, and calculating to obtain the maximum adsorption capacity of 540 mg/g.
Example 4
A. 2.5g of copper sulfate pentahydrate (CuSO) are weighed out4·5H2O) reagent was dissolved in 100mL of water, and 1.42g of ammonium oxalate ((NH)4)2C2O4·H2O) is dissolved in 100mL of water, then the ammonium oxalate solution is rapidly added into the copper sulfate solution, stirred for 3 hours at 70 ℃, filtered, washed and dried to obtain CuC2O4·H2An O precursor; the obtained CuC2O4·H2And calcining the O precursor in a muffle furnace at 500 ℃ for 2 hours to obtain a CuO sample with a microsphere morphology.
B. Dispersing 0.4g of the CuO sample obtained in the step A in 20mL of deionized water, adding the mixture into a four-neck flask after ultrasonic dispersion is carried out for 3 hours, weighing 4.25g of sodium nitrate to dissolve in 30mL of deionized water, then respectively dissolving 9.62g of magnesium nitrate hexahydrate and 4.69g of aluminum nitrate nonahydrate in 50mL of deionized water, then quickly adding the sodium nitrate solution into the flask for stirring, additionally preparing 2mol/L of sodium hydroxide alkaline solution, titrating the metal salt solution of magnesium and aluminum and the alkaline solution into the flask simultaneously under the protection of nitrogen atmosphere, quickly stirring in the titration process, controlling the titration rate of the alkaline solution to ensure that the pH value of a reaction system in the titration process is 9.8-10.1, stirring for 1 hour after the titration is finished, then heating to 75 ℃, standing and aging for 24 hours, carrying out suction filtration, water washing and drying to obtain a hybrid sample precursor; and finally, placing the hybrid sample precursor prepared by the reaction in a muffle furnace at 500 ℃ to calcine for 4 hours to obtain the copper oxide @ hydrotalcite hybrid material.
And B, putting 50mg of the copper oxide @ hydrotalcite hybrid material prepared in the step B into a 250mL reagent bottle with a small opening, adding a Congo red solution with the initial concentration of 50mg/L into the bottle, oscillating at the constant temperature of 150rpm for 360 minutes at room temperature, sampling at regular intervals to determine the residual concentration of the Congo red, and calculating to obtain the maximum adsorption capacity of 378 mg/g.
FIG. 1 is an X-ray diffraction pattern of the prepared CuO template, calcined hydrotalcite derived oxide and hybrid modified copper oxide @ hydrotalcite. As can be seen from the figure, the hybridized copper oxide @ hydrotalcite clearly shows the crystal face diffraction peaks of oxides derived from calcined hydrotalcite and CuO, which indicates that the obtained product is the required material after hybridization modification.
FIG. 2 is an FTIR plot of prepared CuO template, hydrotalcite calcined derivative oxide and hybrid modified copper oxide @ hydrotalcite. As can be seen, 657cm-1At points corresponding to the vibration peaks of the Mg-O metal oxide bond, 538 and 443cm-1Corresponding to the stretching vibration peaks of the Cu-O functional group along the (002) and (111) crystal planes.
Fig. 3 is an SEM photograph of the prepared hybrid modified copper oxide @ hydrotalcite. The appearance of the copper oxide @ hydrotalcite sample is mainly microspherical, the particle size of the microspheres is uniform, small gaps are dispersed on the surface of the microspheres, the size of the microspheres is approximately 1-3 micrometers, the specific surface area of the material is maximized due to the appearance of the microspheres, and the adsorption performance of the material is improved. As can be seen from the TEM photograph of fig. 4, CuO mainly acts as a template to control the morphology inside, and hydrotalcite sheets generated after calcination grow on the surface of the template to form a core-shell structure.
FIG. 5 shows Congo red adsorption performance of the prepared copper oxide @ hydrotalcite hybrid material; therefore, the modified hybrid material can quickly establish adsorption balance, the adsorption balance can be achieved within 20 minutes, the adsorption capacity after the adsorption balance is achieved is higher than that of the material before the modification, and the modified material is proved to have better adsorption performance.
The experiment also proves that: the adsorption performance of the copper oxide @ hydrotalcite hybrid material prepared by the method is better than that of pure hydrotalcite, and the adsorption stability of the copper oxide @ hydrotalcite hybrid material in different acid-base environments is better.
The above description is only for the purpose of illustrating the preferred embodiments of the present invention and is not to be construed as limiting the invention, and any modifications, equivalents, improvements and the like that fall within the spirit and principle of the present invention are intended to be included therein.

Claims (7)

1. The preparation method of the copper oxide @ hydrotalcite hybrid material is characterized by comprising the following steps of:
step 1: preparing a copper oxide template with a microsphere shape in advance:
weighing copper sulfate pentahydrate in a flask, adding deionized water, stirring for dissolving, dissolving ammonium oxalate in the deionized water to prepare a solution, quickly transferring the ammonium oxalate solution into the flask, heating to 70 ℃, magnetically stirring for 3 hours, and then performing suction filtration, washing and drying to obtain a copper oxalate precursor; finally, putting the copper oxalate precursor obtained by the reaction into a muffle furnace, and calcining for 2 hours at 500 ℃ to obtain a copper oxide template sample;
step 2: preparing a copper oxide @ hydrotalcite material;
dispersing the prepared copper oxide sample in deionized water, adding the obtained product into a four-neck flask after ultrasonic dispersion, preparing a sodium nitrate solution, adding the obtained product into the flask, preparing a mixed metal salt solution of magnesium nitrate hexahydrate and aluminum nitrate nonahydrate, quickly adding the mixed metal salt solution of magnesium and aluminum into the flask, stirring, preparing a sodium hydroxide alkali liquor with a certain concentration, titrating the metal salt solution of magnesium and aluminum and the alkali liquor into the flask simultaneously under the protection of nitrogen atmosphere, quickly stirring in the titration process, controlling the titration rate of the alkali liquor so that the pH value of a reaction system in the titration process is 10, stirring for 1 hour after the titration is finished, heating to 75 ℃, standing and aging for 24 hours, performing suction filtration, washing and drying to obtain a hybrid sample precursor; and finally, placing the hybrid sample precursor prepared by the reaction in a muffle furnace at 500 ℃ to calcine for 4 hours to obtain the copper oxide @ hydrotalcite hybrid material.
2. The preparation method of the copper oxide @ hydrotalcite hybrid material according to claim 1, wherein the molar ratio of the copper sulfate pentahydrate to the ammonium oxalate added in the step 1 is 1; the molar concentrations of copper ions and oxalate anions in deionized water are both 0.1 mol/L.
3. The preparation method of the copper oxide @ hydrotalcite hybrid material according to claim 1, wherein the reaction in the step 1 is performed after the temperature is raised to 70 ℃ in advance; the stirring rate was kept constant during the reaction.
4. The preparation method of the copper oxide @ hydrotalcite hybrid material according to claim 1, wherein the copper oxide sample in the step 2 is taken in an amount of 3 wt% to 20 wt%; the ultrasonic dispersion time is 0.5-3 hours; the concentration of the sodium nitrate solution is 2 mol/L; the molar ratio of magnesium ions to aluminum ions in the solution is 3: 1; the concentration of the sodium hydroxide solution is 2 mol/L; and keeping the pH value of 9.8-10.2 in the reaction process.
5. The method for preparing the copper oxide @ hydrotalcite hybrid material according to claim 1, wherein the deionized water used in the experimental reaction in the step 2 needs to be boiled to remove CO2Processing; at the same time, the reaction system is strictly controlled at the strict N2The method is carried out under the protection of atmosphere.
6. The application of the copper oxide @ hydrotalcite hybrid material prepared by the preparation method of any one of claims 1 to 5 in adsorbing Congo red dye.
7. A method for adsorbing Congo red dye by a copper oxide @ hydrotalcite hybrid material is characterized in that an adsorption test is carried out in a water bath constant temperature oscillator which is protected from light; the oscillation rate was 150 rpm; the shaking time is 360 minutes; the shaking temperature was room temperature.
CN202110321165.9A 2021-03-25 2021-03-25 Preparation method and application of copper oxide @ hydrotalcite hybrid material Pending CN113058542A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202110321165.9A CN113058542A (en) 2021-03-25 2021-03-25 Preparation method and application of copper oxide @ hydrotalcite hybrid material

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202110321165.9A CN113058542A (en) 2021-03-25 2021-03-25 Preparation method and application of copper oxide @ hydrotalcite hybrid material

Publications (1)

Publication Number Publication Date
CN113058542A true CN113058542A (en) 2021-07-02

Family

ID=76563619

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202110321165.9A Pending CN113058542A (en) 2021-03-25 2021-03-25 Preparation method and application of copper oxide @ hydrotalcite hybrid material

Country Status (1)

Country Link
CN (1) CN113058542A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN116082822A (en) * 2023-01-17 2023-05-09 盛鼎高新材料有限公司 Preparation method of high-temperature-resistant halogen-free flame-retardant polyurethane elastomer

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007289855A (en) * 2006-04-25 2007-11-08 Sakai Chem Ind Co Ltd Hydrogenation catalyst, its use and its manufacturing method
CN101274847A (en) * 2008-05-21 2008-10-01 北京化工大学 Spinel type ferrite magnetic hollow microsphere and preparation thereof
WO2012043960A1 (en) * 2010-09-30 2012-04-05 한국전력공사 Oxygen carrier particles and method for manufacturing same
CN105289576A (en) * 2015-11-12 2016-02-03 郑州轻工业学院 Preparation method of ZnAl-LDO-coated Nb2O5 photocatalysis material
CN110523415A (en) * 2019-09-03 2019-12-03 浙江天地环保科技有限公司 Copper and iron layered double hydroxide, copper and iron layered double hydroxide/C-base composte material and its preparation method and application
CN111001388A (en) * 2019-12-30 2020-04-14 中国科学院城市环境研究所 Preparation method and application of bamboo-based biochar phosphorus removal adsorbent

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007289855A (en) * 2006-04-25 2007-11-08 Sakai Chem Ind Co Ltd Hydrogenation catalyst, its use and its manufacturing method
CN101274847A (en) * 2008-05-21 2008-10-01 北京化工大学 Spinel type ferrite magnetic hollow microsphere and preparation thereof
WO2012043960A1 (en) * 2010-09-30 2012-04-05 한국전력공사 Oxygen carrier particles and method for manufacturing same
CN105289576A (en) * 2015-11-12 2016-02-03 郑州轻工业学院 Preparation method of ZnAl-LDO-coated Nb2O5 photocatalysis material
CN110523415A (en) * 2019-09-03 2019-12-03 浙江天地环保科技有限公司 Copper and iron layered double hydroxide, copper and iron layered double hydroxide/C-base composte material and its preparation method and application
CN111001388A (en) * 2019-12-30 2020-04-14 中国科学院城市环境研究所 Preparation method and application of bamboo-based biochar phosphorus removal adsorbent

Non-Patent Citations (4)

* Cited by examiner, † Cited by third party
Title
LU LU等: "Synthesis of novel hierarchically porous Fe3O4@MgAl–LDH magnetic microspheres and its superb adsorption properties of dye from water", 《JOURNAL OF INDUSTRIAL AND ENGINEERING CHEMISTRY》 *
容道清等: "镁铝水滑石纳米片可控制备及其吸附性能研究", 《功能材料》 *
王卫伟等: "草酸铜煅烧法制备多孔氧化铜及Cr(VI)吸附性能", 《硅酸盐通报》 *
贺怀儒等: "提高层状双金属氢氧化物水中吸附性能研究进展", 《水处理技术》 *

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN116082822A (en) * 2023-01-17 2023-05-09 盛鼎高新材料有限公司 Preparation method of high-temperature-resistant halogen-free flame-retardant polyurethane elastomer
CN116082822B (en) * 2023-01-17 2023-11-21 盛鼎高新材料有限公司 Preparation method of high-temperature-resistant halogen-free flame-retardant polyurethane elastomer

Similar Documents

Publication Publication Date Title
RU2311956C2 (en) Method of preparing mixed zirconium-cerium-based oxides
CN110975795A (en) Synthesis method of lithium extraction adsorbent
CN108380170B (en) Metal oxide doped aluminum oxide and preparation and application thereof
CN100347092C (en) Preparation method of ziroconium oxide composite nano crystal material
CN102030352A (en) Method for preparing nano material
CN103949193A (en) Universal method for preparation of inorganic hollow microspheres
CN104828869B (en) A kind of sodium manganese oxide micropowder and preparation method thereof
CN111924865B (en) Crystal face selective growth boehmite and preparation method thereof
Zhou et al. Synthesis and properties of octahedral Co 3 O 4 single-crystalline nanoparticles enclosed by (111) facets
CN112239223B (en) Preparation method of rare earth oxide powder with large specific surface area
CN112844444A (en) Method for preparing cerium dioxide catalytic material by utilizing carrier pore channel self-adsorption principle
CN113896244B (en) Porous disc-shaped lithium manganate electrode for extracting lithium from salt lake and preparation method thereof
CN105883910B (en) A kind of perovskite SrTiO3The preparation method and product of porous nano particle
CN113058542A (en) Preparation method and application of copper oxide @ hydrotalcite hybrid material
CN109529903B (en) Method for preparing nickel-nitrogen co-doped carbon material by using hydrotalcite as template
CN112850764A (en) Method for preparing shape-controllable aluminum oxide hollow microspheres without template agent
CN109046341B (en) Preparation method of visible light response silver silicate/attapulgite composite catalyst
WO2023216729A1 (en) Method for recovering phosphite ions in wastewater
CN109761261B (en) Green preparation method of cerium dioxide powder with controllable particle size and morphology and large specific surface area
CN105253904A (en) Alumina micro-nano powder preparation method
CN103449511A (en) Strontium titanate submicron crystal and preparation method thereof
CN104483351B (en) Palladium-doped hollow porous stannic oxide microcubes as well as preparation method and application thereof
CN113479897B (en) Method for preparing two-dimensional nano sheet silicate by using attapulgite and application thereof
CN103449490A (en) Porous aluminium oxide micro/nanospheres and preparation method thereof
CN114288983A (en) Titanium-based lithium ion exchanger and preparation method 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