CN114259981B - Clay mineral loaded molybdenum disulfide composite material and preparation method and application thereof - Google Patents

Clay mineral loaded molybdenum disulfide composite material and preparation method and application thereof Download PDF

Info

Publication number
CN114259981B
CN114259981B CN202111594611.XA CN202111594611A CN114259981B CN 114259981 B CN114259981 B CN 114259981B CN 202111594611 A CN202111594611 A CN 202111594611A CN 114259981 B CN114259981 B CN 114259981B
Authority
CN
China
Prior art keywords
molybdenum disulfide
clay mineral
composite material
molybdenum
flower
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.)
Active
Application number
CN202111594611.XA
Other languages
Chinese (zh)
Other versions
CN114259981A (en
Inventor
侯浩波
李文龙
阚小清
曾天宇
周旻
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.)
Institute Of Resources And Environmental Technology Wuhan University Zhaoqing
Original Assignee
Institute Of Resources And Environmental Technology Wuhan University Zhaoqing
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 Institute Of Resources And Environmental Technology Wuhan University Zhaoqing filed Critical Institute Of Resources And Environmental Technology Wuhan University Zhaoqing
Priority to CN202111594611.XA priority Critical patent/CN114259981B/en
Publication of CN114259981A publication Critical patent/CN114259981A/en
Application granted granted Critical
Publication of CN114259981B publication Critical patent/CN114259981B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Landscapes

  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

The invention discloses a clay mineral loaded molybdenum disulfide composite material, and a preparation method and application thereof. The clay mineral loaded molybdenum disulfide composite material is formed by loading flower-shaped molybdenum disulfide microspheres on a clay mineral carrier, the composite material takes clay minerals with developed pores and high specific surface area as the carrier, and the heavy metal adsorption active ingredient molybdenum disulfide active nano-sheets are assembled into flower-shaped microspheres, so that the composite material has stable structural morphology, is highly dispersed on the carrier, has high exposure of active sites, shows good adsorption performance on heavy metals, and is suitable for being applied as a heavy metal pollution water body restoration material.

Description

Clay mineral loaded molybdenum disulfide composite material and preparation method and application thereof
Technical Field
The invention relates to an adsorption material, in particular to a clay mineral loaded molybdenum disulfide composite material, a preparation method thereof and application thereof in the aspect of heavy metal polluted water body restoration, belonging to the field of environmental functional materials,
Background
Molybdenum disulfide is a typical lamellar transition metal disulfide, each layer consists of two sulfur sheets and a built-in molybdenum sheet, and is similar to a sandwich structure, the layers are connected by Van der Waals force, and the molybdenum disulfide is easy to separate and has three crystal forms of 1T, 2H and 3R due to different stacking modes, so that the molybdenum sulfide has the most stable property. Common preparation methods are mechanical stripping, liquid stripping, chemical stripping, electrochemical stripping, chemical vapor deposition and hydrothermal synthesis. The former four methods are to prepare the molybdenum disulfide nanosheets by stripping the massive molybdenum disulfide by decomposing weak Van der Waals force between layers, and the latter method is to synthesize the molybdenum disulfide nanosheets by utilizing a molybdenum source and a sulfur source. Molybdenum disulfide is a typical n-type semiconductor, has a unique electronic energy band structure, and has excellent photocatalytic performance. As a two-dimensional material, molybdenum disulfide has a large interlayer spacing and excellent electrochemical performance, and is widely used for storing energy sources of lithium ion batteries. In addition, the method has wide application in the fields of field effect transistors, sensors, photodetectors, adsorption and the like.
Because of the unique two-dimensional structure, the two-dimensional molybdenum disulfide has a huge specific surface area, has become one of the most popular adsorbents since 2010, and sulfur atoms are exposed, so that the two-dimensional molybdenum disulfide has better adsorption capacity on metals. Liu and the like adopt ultrasonic liquid phase assisted stripping and hydrothermal synthesis to prepare two types of molybdenum disulfide nanosheets, the adsorption effect of different morphologies on Pb 2+ is explored, the result shows that under the condition of low concentration (60 mg/L), the removal rate of Pb 2+ is 98.4% and 20.6%, the adsorption capacity of the molybdenum disulfide prepared by the hydrothermal synthesis can reach 174.2mg/g("Role of structural characteristics of MoS2nanosheets on Pb2+removal in aqueous solution",LIU,Y,et al.,Environmental Technology&Innovation,2021,22(14–15):101385).Chen and other structural bond molybdenum disulfide/lignin composite materials for removing Cr (VI) in water environment, the composite materials have remarkable Cr (VI) removal effect at pH=2 and T=298.15 k and 20mg/L, the adsorption capacity is 198.70mg/g, Cr(Ⅵ)("Constructing MoS2/Lignin-derived Carbon Nanocomposites for Highly Efficient Removal of Cr(VI)from Aqueous Environment",CHEN,H,et al.,Journal of Hazardous Materials,2020,408(49):124847).Paul and the like of 99.35 can be removed in 30min, cd 2+ in water is removed by using cysteine, and the result shows that molybdenum disulfide prepared by the hydrothermal method can be loaded on carbon aerogel by Guo Qinming of Cd2+("Few-layer molybdenum disulfide nanosheets functionalized with L-cysteine for selective capture of Cd2+ions",BAZYLEWSKI,P,et al.,Flatchem,2018,11:15-23). university of 76+/-15 mg/g, and used for removing Cr (VI) in water, the removal capacity is up to 460.2mg/g, and the molybdenum disulfide has excellent reusability ("S 2/S and the preparation performance of Mo02-212, and the like). Zhong Weihong and the like are used for preparing molybdenum disulfide by a molten salt method, then the molybdenum disulfide is compounded with silver phosphate, and the prepared material can absorb 628.93mg/g of iodine ions (the adsorption performance test research of silver phosphate/molybdenum disulfide on iodine ions, bells and the like, hydrometallurgy, 2019,38 (06): 476-484). Although molybdenum disulfide is more applied to the removal of metal ions, the shape of the molybdenum disulfide which is generally prepared is not easy to regulate and control, the dispersibility is poor, and the molybdenum disulfide is limited by cost and has no wide application compared with the traditional adsorbents such as activated carbon.
Disclosure of Invention
Aiming at the defects existing in the prior art, the first aim of the invention is to provide a composite material formed by loading flower-shaped molybdenum disulfide microspheres on a clay mineral carrier, wherein the composite material takes clay minerals with developed pores and high specific surface area as the carrier, and heavy metal adsorption active ingredient molybdenum disulfide nano-sheets are assembled into flower-shaped microspheres, the structure is stable in appearance, the molybdenum disulfide nano-sheets are highly dispersed on the carrier, active sites are highly exposed, and good adsorption performance on heavy metals is shown.
The second aim of the invention is to provide a method for preparing the clay mineral loaded molybdenum disulfide composite material, which has simple steps, low raw material cost and mild conditions, and is beneficial to mass production.
The third purpose of the invention is to provide an application of the clay mineral loaded molybdenum disulfide composite material, which is used as a heavy metal adsorption material for repairing heavy metal polluted water, and has high adsorption efficiency and large capacity on heavy metal in heavy metal polluted water solution.
In order to achieve the technical aim, the invention provides a clay mineral loaded molybdenum disulfide composite material, which is formed by loading flower-shaped molybdenum disulfide microspheres on a clay mineral carrier.
The clay mineral loaded molybdenum disulfide composite material provided by the invention is formed by compounding active ingredient molybdenum disulfide and a clay mineral carrier, and has good adsorption performance on heavy metals based on the synergy between the ingredients and a special structure. The heavy metal adsorption active ingredient molybdenum disulfide two-dimensional nano-sheet is assembled into a micron-sized structure, the structural stability is good, the exposure of active sites is high, the adsorption effect of the heavy metal adsorption active ingredient molybdenum disulfide two-dimensional nano-sheet on the heavy metal is greatly improved, the clay mineral has rich pore structures and large specific surface area, the heavy metal adsorption active ingredient molybdenum disulfide two-dimensional nano-sheet has high physical adsorption performance, the pore structures and the high specific surface area of the clay mineral are utilized to provide attachment sites for the molybdenum disulfide active ingredient, the high dispersion of the molybdenum disulfide active ingredient is realized, and the reduction of the adsorption performance of the heavy metal caused by the agglomeration of the molybdenum disulfide active ingredient is prevented.
As a preferable scheme, the flower-shaped molybdenum disulfide microspheres are assembled by molybdenum disulfide nanosheets, and the particle size of the flower-shaped molybdenum disulfide microspheres is 2.5-3.5 mu m. The molybdenum disulfide nanosheets are of a nano structure and have high reactivity, and the nanosheets are assembled into a flower-shaped structure, so that an interlayer or pore structure is constructed, active sites are greatly exposed, and the reactivity is improved.
As a preferred embodiment, the clay mineral carrier is at least one of bentonite, diatomaceous earth, kaolin, sepiolite. The preferred clay minerals are lamellar or fluffy structures that provide attachment points for the molybdenum disulfide active ingredient loading.
As a preferable scheme, the mass ratio of the flower-shaped molybdenum disulfide microspheres to the clay mineral is 1:5-4:5. When the proportion of the flower-shaped molybdenum disulfide microspheres is too small, the chemical adsorption active sites of the composite material for heavy metals are too small, and when the proportion of the flower-shaped molybdenum disulfide microspheres is too high, the dispersibility of the molybdenum disulfide active ingredients is easy to be poor, so that the utilization rate of the molybdenum disulfide active ingredients is low.
The invention also provides a preparation method of the clay mineral loaded molybdenum disulfide composite material, which comprises the following steps of:
Scheme a: carrying out hydrothermal reaction on a molybdenum source, a sulfur source and clay minerals in an aqueous medium to obtain the catalyst;
Scheme B: and (3) carrying out hydrothermal reaction on a molybdenum source and a sulfur source in an aqueous medium, dispersing the obtained hydrothermal reaction product in water, and then adding clay mineral for heating and stirring reaction to obtain the catalyst.
The clay mineral loaded molybdenum disulfide composite material is mainly obtained through hydrothermal reaction, and in the scheme A, through one-step hydrothermal reaction, not only is the synthesis of flower-shaped molybdenum disulfide microspheres realized, but also the chemical bonding of the flower-shaped molybdenum disulfide microspheres and clay minerals is realized, and the in-situ loading is realized. In the scheme B, the synthesis of flower-shaped molybdenum disulfide microspheres is realized through two steps of reactions of hydrothermal reaction and conventional heating reaction, the first step of hydrothermal reaction mainly comprises the step of carrying the flower-shaped molybdenum disulfide microspheres on the surface of clay minerals in situ through chemical bonding, the two schemes can realize the synthesis of the clay mineral loaded molybdenum disulfide composite material, and the synthesized clay mineral loaded molybdenum disulfide composite material has good crystal structure morphology of molybdenum disulfide active components, high reactivity, good loading stability on the clay minerals and high dispersity, so that the composite material shows higher activity of adsorbing heavy metals.
The reaction principle in the scheme A of the invention is as follows: the sulfur source can be used as a reducing agent under a hydrothermal condition, hexavalent molybdenum is reduced to tetravalent molybdenum and molybdenum disulfide is generated, the molybdenum disulfide grows into a two-dimensional nano sheet structure under high temperature and high pressure, the two-dimensional nano sheet structure is assembled into a special flower-shaped microsphere structure, and in-situ load is realized by chemical bonding of sulfide anions of the molybdenum disulfide and metal ions in clay minerals; the key of the technology is that: the molybdenum source and the sulfur source solution are mixed with clay mineral, the molybdenum source and the sulfur source are dispersedly bonded on the surface of the clay mineral, and then the molybdenum disulfide generated by hydrothermal reduction reaction can directly realize load on the surface and pore structure of the clay mineral.
The reaction principle in the scheme B of the invention is as follows: the sulfur source can be used as a reducing agent under hydrothermal conditions, hexavalent molybdenum is reduced to tetravalent molybdenum and molybdenum disulfide is generated, the molybdenum disulfide grows into a two-dimensional nano sheet structure under high temperature and high pressure, the two-dimensional nano sheet structure is assembled into a special flower-shaped microsphere structure, and then the molybdenum disulfide material and clay mineral are heated and stirred to realize chemical bonding of the two materials.
As a preferred embodiment, in embodiment a or embodiment B: the molybdenum source is sodium molybdate dihydrate and/or ammonium molybdate tetrahydrate; the sulfur source is thiourea and/or thioacetamide. Both of these molybdenum and sulfur sources are common synthetic raw materials for molybdenum disulfide in the prior art.
In a preferred embodiment, in the embodiment a, the clay mineral is at least one of bentonite, diatomaceous earth, and kaolin. The preferred clay mineral has a mesoporous structure, and a large number of experiments show that the mesoporous structure is favorable for inducing uniform nucleation of molybdenum disulfide on the surface of the clay mineral and improving the purity of crystalline phases, so that flower-shaped molybdenum disulfide microspheres with better structural morphology are obtained, and the load stability is improved.
In a preferred embodiment, in the embodiment B, the clay mineral is at least one of bentonite and sepiolite.
As a preferred embodiment, in embodiment a or embodiment B: the molar ratio of the molybdenum source to the sulfur source is 1:3-1:6.
As a preferred embodiment, in the embodiment a, the clay mineral is 0.5 to 5 times the mass of the molybdenum source.
As a preferred embodiment, in the embodiment B, the clay mineral is 10 to 500% by mass of the hydrothermal reaction product. The clay mineral mass is more preferably 300-400% of the mass of the hydrothermal reaction product.
As a preferable scheme, in the scheme A, the temperature of the hydrothermal reaction is 160-260 ℃, the pH value is 3-5, and the reaction time is 12-36 h. In the hydrothermal reaction process, the special flower-shaped microsphere structure morphology molybdenum disulfide assembled by the molybdenum disulfide nanosheets is formed, chemical bonding between the molybdenum disulfide and clay minerals is realized, in-situ loading is realized, and loading stability is greatly improved. Further preferred hydrothermal reaction conditions: the temperature is 180-220 ℃ and the time is 20-28 h.
As a preferable scheme, in the scheme B, the temperature of the hydrothermal reaction is 160-260 ℃, the pH value is 3-5, and the reaction time is 12-36 h. In a preferred embodiment, in the embodiment B, the temperature of the heating and stirring is 25 to 65 ℃ and the time is 1 to 24 hours. In the hydrothermal reaction process, the special flower-shaped microsphere structural morphology molybdenum disulfide assembled by the molybdenum disulfide nanosheets is mainly formed, and the chemical bonding between the molybdenum disulfide and clay minerals is further realized through the heating reaction, so that in-situ loading is realized, and the loading stability is greatly improved. In a preferable pH environment, the specific surface area of clay mineral can be increased, so that the composite material with developed pores and higher specific surface area can be obtained. Further preferably, the temperature of the heating and stirring reaction is 25-35 ℃ and the time is 8-12 h.
The invention also provides application of the clay mineral loaded molybdenum disulfide composite material as a heavy metal adsorption material for repairing heavy metal polluted water.
As a preferable scheme, the clay mineral loaded molybdenum disulfide composite material is used for adsorbing Cd 2+ in heavy metal polluted water.
Compared with the prior art, the technical scheme of the invention has the beneficial technical effects that:
the clay mineral loaded molybdenum disulfide composite material provided by the invention is formed by compounding active ingredient molybdenum disulfide and a clay mineral carrier, and has good adsorption performance on heavy metals based on the synergy between the ingredients and a special structure. The heavy metal adsorption molybdenum disulfide active ingredient is assembled into a micron-sized structure by the two-dimensional nano sheet, the structural stability is good, the exposure of active sites is much, the adsorption effect of the heavy metal adsorption molybdenum disulfide active ingredient on the heavy metal is greatly improved, the clay mineral has rich pore structures and large specific surface area, the heavy metal adsorption molybdenum disulfide active ingredient has high physical adsorption performance, and the high dispersion of the heavy metal adsorption molybdenum disulfide active ingredient is realized by utilizing the pore structures and the high specific surface area of the clay mineral and providing the adhesion sites for the molybdenum disulfide active ingredient, so that the reduction of the adsorption performance of the heavy metal caused by the agglomeration of the molybdenum disulfide active ingredient is prevented.
The clay mineral loaded molybdenum disulfide composite material provided by the invention has good structural stability, a more developed pore structure, more heavy metal adsorption active sites and a better adsorption effect on heavy metals in heavy metal polluted water, and provides a foundation and reference for realizing heavy metal polluted water.
The clay mineral loaded molybdenum disulfide composite material provided by the invention has the advantages of simple preparation method, low raw material cost and mild conditions, and is beneficial to large-scale production.
Drawings
Fig. 1 is an X-ray diffraction pattern of the bentonite-based composite of example 2.
Fig. 2 is a scanning electron microscope image of the bentonite-based composite in example 2.
Fig. 3 is a transmission electron microscope image of the bentonite-based composite in example 2.
FIG. 4 is a drawing of Cd 2+ in the bentonite-based composite of example 8.
Detailed Description
In order to better explain the technical scheme and advantages of the present invention, the present invention will be further described in detail with reference to the following examples. It is noted that the following examples are given solely for the purpose of illustration and are not to be construed as limitations of the present invention, as will be apparent to those skilled in the art upon examination of the foregoing disclosure.
Example 1
In a 50ml beaker, 0.605g of sodium molybdate dihydrate, 0.57g of thiourea, 0.3025g of sepiolite and 40ml of deionized water were added, after stirring uniformly, a dilute hydrochloric acid solution of 0.1mol/L was added dropwise to adjust ph=3, poured into a hydrothermal reaction vessel, and heated to 160 ℃ at a rate of 1 ℃/min, and kept for 16 hours. After the reaction is finished, the liquid is colorless and transparent, the product is black solid, the black solid is taken out, the mixture is washed for 3 times by absolute ethyl alcohol and deionized water respectively, then the mixture is dried for 24 hours in vacuum, and the mixture is collected after grinding, thus obtaining the sepiolite-based composite material. The prepared composite material is applied to removing Cd 2+ in an aqueous solution, the solid-to-liquid ratio is 1.5g/L, the concentration of the Cd 2+ solution is 200mg/L, the temperature is 25 ℃, the pH=6, and the maximum adsorption capacity at the time of balancing is 62.35mg/L.
Example 2
In a 50ml beaker, 0.605g of sodium molybdate dihydrate, 1.14g of thiourea, 3.025g of bentonite and 40ml of deionized water are added, after stirring uniformly, a dilute hydrochloric acid solution of 0.1mol/L is added dropwise to adjust pH to be=5, the mixture is poured into a hydrothermal reaction kettle, the temperature is raised to 260 ℃ at a rate of 10 ℃/min, and the temperature is kept for 36 hours. After the reaction is finished, the liquid is colorless and transparent, the product is black solid, the black solid is taken out, the black solid is respectively washed for 3 times by absolute ethyl alcohol and deionized water, then the vacuum drying is carried out for 24 hours, the bentonite-based composite material is obtained after grinding and collection, and an X-ray diffraction pattern and a scanning electron microscope pattern of the prepared material are shown in figures 1 and 2. In the XRD pattern of FIG. 1, peaks of molybdenum disulfide, silica and montmorillonite are simultaneously present, and montmorillonite is a main phase of bentonite, and silica is a main constituent substance of bentonite. In the scanning electron microscope picture of fig. 2, bentonite is mainly stacked in a block shape, part of spherical molybdenum disulfide is embedded in the bentonite, the molybdenum disulfide in the enlarged view is in a sheet-shaped structure, and in the transmission electron microscope picture of fig. 3, molybdenum disulfide grains and main component silicon dioxide of carrier bentonite form a typical heterostructure, which can be shown to be chemically bonded. The prepared composite material is applied to removing Cd 2+ in an aqueous solution, the solid-to-liquid ratio is 1.5g/L, the concentration of the Cd 2+ solution is 200mg/L, the temperature is 25 ℃, the pH=6, and the maximum adsorption capacity at the time of balancing is 52.88mg/L.
Example 3
In a 50ml beaker, 0.605g of sodium molybdate dihydrate, 0.76g of thiourea, 1.50g of bentonite and 40ml of deionized water are added, after stirring uniformly, a dilute hydrochloric acid solution of 0.1mol/L is added dropwise to adjust pH to be=5, and the mixture is poured into a hydrothermal reaction kettle, heated to 200 ℃ at a speed of 5 ℃/min, and kept for 24 hours. After the reaction is finished, the liquid is colorless and transparent, the product is black solid, the black solid is taken out, and is respectively washed for 3 times by absolute ethyl alcohol and deionized water, then vacuum drying is carried out for 24 hours, and the bentonite-based composite material is obtained after grinding and collecting. The prepared composite material is applied to removing Cd 2+ in an aqueous solution, the solid-to-liquid ratio is 1.5g/L, the concentration of the Cd 2+ solution is 200mg/L, the temperature is 25 ℃, the pH=6, and the maximum adsorption capacity at the time of balancing is 75.33mg/L.
Example 4 (comparative example)
In a 50ml beaker, 0.605g of sodium molybdate dihydrate, 0.76g of thiourea, 1.50g of bentonite and 40ml of deionized water were added, after stirring uniformly, the pH=7 was adjusted, poured into a hydrothermal reaction kettle, heated to 200℃at a rate of 5℃per minute, and kept for 24 hours. After the reaction, the liquid is light yellow, and the product is black solid. Since the liquid environment is neutral, molybdenum disulfide is difficult to form, and thus bentonite-based composite materials cannot be obtained.
Example 5
In a 50ml beaker, 0.605g of sodium molybdate dihydrate, 0.57g of thiourea and 40ml of deionized water are added, after uniform stirring, 0.1mol/L of dilute hydrochloric acid solution is added dropwise to adjust pH to be 3, and the mixture is poured into a hydrothermal reaction kettle, heated to 160 ℃ at a speed of 1 ℃/min, and kept for 16 hours. After the reaction, the liquid is colorless and transparent, the product is black solid, the black solid is taken out, washed 3 times by absolute ethyl alcohol and deionized water respectively, dried in vacuum for 24 hours, and ground and collected. Then the prepared material is dispersed in water solution by ultrasonic, added with 0.04g of sepiolite, heated to 25 ℃ and stirred for 1h, thus obtaining the sepiolite-based composite material. The prepared composite material is applied to removing Cd 2+ in an aqueous solution, the solid-to-liquid ratio is 1.5g/L, the concentration of the Cd 2+ solution is 200mg/L, the temperature is 25 ℃, the pH=6, and the maximum adsorption capacity at the time of balancing is 50.76mg/L.
Example 6
In a 50ml beaker, 0.605g of sodium molybdate dihydrate, 1.14g of thiourea and 40ml of deionized water are added, after uniform stirring, 0.1mol/L of dilute hydrochloric acid solution is added dropwise to adjust pH to be=5, and the mixture is poured into a hydrothermal reaction kettle, heated to 260 ℃ at a speed of 10 ℃/min, and kept for 36 hours. After the reaction, the liquid is colorless and transparent, the product is black solid, the black solid is taken out, washed 3 times by absolute ethyl alcohol and deionized water respectively, dried in vacuum for 24 hours, and ground and collected. And then dispersing the prepared material in water solution by ultrasonic, adding 2g of bentonite, heating to 65 ℃, and stirring for 24 hours to obtain the bentonite-based composite material. The prepared composite material is applied to removing Cd 2+ in an aqueous solution, the solid-to-liquid ratio is 1.5g/L, the concentration of the Cd 2+ solution is 200mg/L, the temperature is 25 ℃, the pH=6, and the maximum adsorption capacity at the time of balancing is 45.38mg/L.
Example 7
In a 50ml beaker, 0.605g of sodium molybdate dihydrate, 0.76g of thiourea and 40ml of deionized water are added, after uniform stirring, 0.1mol/L of dilute hydrochloric acid solution is added dropwise to adjust pH to be 4, and the mixture is poured into a hydrothermal reaction kettle, heated to 200 ℃ at a speed of 5 ℃/min, and kept for 24 hours. After the reaction, the liquid is colorless and transparent, the product is black solid, the black solid is taken out, washed 3 times by absolute ethyl alcohol and deionized water respectively, dried in vacuum for 24 hours, and ground and collected. Then the prepared material is dispersed in water solution by ultrasonic, 1.5g of bentonite is added, then the mixture is heated to 35 ℃ and stirred for 12 hours, and the bentonite-based composite material is obtained. The prepared composite material is applied to removing Cd 2+ in an aqueous solution, the solid-to-liquid ratio is 1.5g/L, the concentration of the Cd 2+ solution is 200mg/L, the temperature is 25 ℃, the pH=6, and the maximum adsorption capacity at the time of balancing is 57.26mg/L.
Example 8
The composite material prepared in the example 3 is applied to the adsorption of Cd 2+ in an aqueous solution, the solid-to-liquid ratio is 1.5g/L, the concentration of Cd 2+ solution is 200mg/L, the temperature is 25 ℃, the pH=6, the adsorption result of the material is shown in figure 3, the adsorption capacity is obviously improved along with the change of time when the adsorption capacity is 0-75 min, the adsorption capacity tends to be stable after 75min, and the maximum adsorption capacity is 75.33mg/L.

Claims (3)

1. The application of the clay mineral loaded molybdenum disulfide composite material is characterized in that: the clay mineral loaded molybdenum disulfide composite material is used for adsorbing Cd 2+ in a heavy metal polluted water body;
The clay mineral loaded molybdenum disulfide composite material is formed by loading flower-shaped molybdenum disulfide microspheres on a clay mineral carrier; the flower-shaped molybdenum disulfide microspheres are assembled by molybdenum disulfide nanosheets, and the particle size of the flower-shaped molybdenum disulfide microspheres is 2.5-3.5 mu m; the clay mineral carrier is at least one of bentonite, diatomite and kaolin;
The clay mineral loaded molybdenum disulfide composite material is prepared by the following method: carrying out hydrothermal reaction on a molybdenum source, a sulfur source and clay minerals in an aqueous medium to obtain the catalyst; the temperature of the hydrothermal reaction is 160-260 ℃, the pH value is 3-5, and the reaction time is 12-36 h; the mol ratio of the molybdenum source to the sulfur source is 1:3-1:6;
the mass of the clay mineral is 0.5-5 times of the mass of the molybdenum source.
2. The use of a clay mineral supported molybdenum disulfide composite according to claim 1, characterized in that: the mass ratio of the flower-shaped molybdenum disulfide microspheres to clay mineral is 1:5-4:5.
3. The use of a clay mineral supported molybdenum disulfide composite according to claim 1, characterized in that:
the molybdenum source is sodium molybdate dihydrate and/or ammonium molybdate tetrahydrate;
the sulfur source is thiourea and/or thioacetamide.
CN202111594611.XA 2021-12-23 2021-12-23 Clay mineral loaded molybdenum disulfide composite material and preparation method and application thereof Active CN114259981B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202111594611.XA CN114259981B (en) 2021-12-23 2021-12-23 Clay mineral loaded molybdenum disulfide composite material and preparation method and application thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202111594611.XA CN114259981B (en) 2021-12-23 2021-12-23 Clay mineral loaded molybdenum disulfide composite material and preparation method and application thereof

Publications (2)

Publication Number Publication Date
CN114259981A CN114259981A (en) 2022-04-01
CN114259981B true CN114259981B (en) 2024-05-24

Family

ID=80829438

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202111594611.XA Active CN114259981B (en) 2021-12-23 2021-12-23 Clay mineral loaded molybdenum disulfide composite material and preparation method and application thereof

Country Status (1)

Country Link
CN (1) CN114259981B (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114887631B (en) * 2022-05-05 2023-08-18 中国石油大学(华东) Solvothermal method for preparing mixed morphology 1T-2H MoS 2 Preparation method and application of (C)
CN114804716B (en) * 2022-05-20 2023-07-25 西北民族大学 Modified clay, preparation method and application thereof, and glue-free fiber board
CN115418259B (en) * 2022-09-20 2023-06-27 西南交通大学 Grease thickening agent and preparation method thereof, and grease and preparation method thereof
CN116328717A (en) * 2023-02-16 2023-06-27 中南大学 Modified attapulgite-based material, and preparation method and application thereof

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107321299A (en) * 2017-08-30 2017-11-07 河北工业大学 The preparation method of molybdenum disulfide and scpiolitc nanofiber composite adsorbing material
CN108394936A (en) * 2018-04-20 2018-08-14 河北工业大学 The preparation method of molybdenum disulfide-Palygorskite Nanometer rod composite material
CN108525680A (en) * 2018-04-20 2018-09-14 河北工业大学 The preparation method of molybdenum disulfide-sepiolite nano-fiber composite material
CN111921489A (en) * 2020-08-04 2020-11-13 江西理工大学 Composite material for removing lead ions in solution and preparation method and application thereof

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107321299A (en) * 2017-08-30 2017-11-07 河北工业大学 The preparation method of molybdenum disulfide and scpiolitc nanofiber composite adsorbing material
CN108394936A (en) * 2018-04-20 2018-08-14 河北工业大学 The preparation method of molybdenum disulfide-Palygorskite Nanometer rod composite material
CN108525680A (en) * 2018-04-20 2018-09-14 河北工业大学 The preparation method of molybdenum disulfide-sepiolite nano-fiber composite material
CN111921489A (en) * 2020-08-04 2020-11-13 江西理工大学 Composite material for removing lead ions in solution and preparation method and application thereof

Non-Patent Citations (4)

* Cited by examiner, † Cited by third party
Title
Adsorption toward Cu(II) and inhibitory effect on bacterial growth occurring on molybdenum disulfide-montmorillonite hydrogel surface;Wei Wang et al.;《Chemosphere》;第248卷;摘要、第2.2节、正文第4页和图2 *
Qiwei Sun et al..Symbiotic composite composed of MoS2 and pelagic clay with enhanced disinfection efficiency.《RSC Advances》.2021,第11卷摘要、催化剂制备部分和第9623页右栏第2段. *
Symbiotic composite composed of MoS2 and pelagic clay with enhanced disinfection efficiency;Qiwei Sun et al.;《RSC Advances》;第11卷;摘要、催化剂制备部分和第9623页右栏第2段 *
凹凸棒负载TiO2对偶氮染料和纺织废水光催化脱污;胡春,王怡中;环境科学学报;21(第01期);摘要和第1.1节 *

Also Published As

Publication number Publication date
CN114259981A (en) 2022-04-01

Similar Documents

Publication Publication Date Title
CN114259981B (en) Clay mineral loaded molybdenum disulfide composite material and preparation method and application thereof
Gao et al. Efficient removal of fluoride from aqueous solutions using 3D flower-like hierarchical zinc-magnesium-aluminum ternary oxide microspheres
Ma et al. Multifunctional flexible composite aerogels constructed through in-situ growth of metal-organic framework nanoparticles on bacterial cellulose
US11439990B2 (en) Titanium carbide nanosheet/layered indium sulfide heterojunction and application thereof in degrading and removing water pollutants
Ryu et al. Recovery of lithium in seawater using a titanium intercalated lithium manganese oxide composite
CN104815637B (en) Method for hydrothermal method preparation of graphene-loaded flower-type titanium dioxide composite material
CN103585896B (en) A kind of preparation method of stratiform molybdenum sulfide nanometer sheet molecular separation membrane
CN107902697B (en) A kind of nanometer sheet self assembled three-dimensional VS of (001) orientation2Micron bar and preparation method thereof
CN102745675A (en) Preparation method of spinel-type magnetic MFe2O4/graphene composite material
Zhang et al. Studies on the removal of phosphate in water through adsorption using a novel Zn-MOF and its derived materials
CN109569670B (en) Preparation method of BiOBr/black phosphorus alkene heterojunction nano composite material
WO2019237452A1 (en) Method for preparing two-dimensional sheet-shaped cu-mof material
Yang et al. Facile fabrication of nanoscale hierarchical porous zeolitic imidazolate frameworks for enhanced toluene adsorption capacity
CN107840368A (en) A kind of nanometer sheet self assembly sub-micrometer flower-shape M-phase vanadium dioxide powder and preparation method thereof
Jiang et al. Cauliflower-like CuI nanostructures: green synthesis and applications as catalyst and adsorbent
CN104857927A (en) Vermiculite surface in-situ growth hydrotalcite material and preparation method thereof
Chen et al. Highly efficient and selective cesium recovery from natural brine resources using mesoporous Prussian blue analogs synthesized by ionic liquid-assisted strategy
CN113134339A (en) Preparation of zirconium-doped hydrotalcite-like adsorbent and application of zirconium-doped hydrotalcite-like adsorbent in treatment of phosphorus-containing wastewater
CN115703077B (en) PB@MoS2Application of catalyst in heterogeneous Fenton-like reaction
CN106602083B (en) A kind of method of hydro-thermal method synthesis Cu-N-C catalyst
CN103833080B (en) A kind of preparation method of molybdic acid cadmium porous ball
KR20080045627A (en) Method for synthesis of lithium manganese oxide by hydroysis and solvent-exchange process and preparation of ion-exchange type lithium adsorbent using the lithium manganese oxide
CN106582539A (en) Amino-modified mesoporous carbon CMK-3 material and preparation method as well as application thereof
CN108031481B (en) Ultrathin bismuth oxyhalide nanosheet photocatalyst stripped by silver intercalation and preparation method thereof
CN106745271B (en) A kind of sodium taurocholate improvement hydro-thermal method preparing tungsten disulfide nano slices

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