CN110665455A - Mercury removing adsorbent with core-shell structure and preparation method thereof - Google Patents

Mercury removing adsorbent with core-shell structure and preparation method thereof Download PDF

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CN110665455A
CN110665455A CN201911012730.2A CN201911012730A CN110665455A CN 110665455 A CN110665455 A CN 110665455A CN 201911012730 A CN201911012730 A CN 201911012730A CN 110665455 A CN110665455 A CN 110665455A
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core
shell structure
mercury removal
solution
removal adsorbent
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何平
张熠
赵昕熠
秦煌
魏杰
徐天红
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Shanghai University of Electric Power
Shanghai Electric Power University
University of Shanghai for Science and Technology
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Shanghai Electric Power University
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • 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
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/02Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by adsorption, e.g. preparative gas chromatography
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/86Catalytic processes
    • B01D53/8665Removing heavy metals or compounds thereof, e.g. mercury
    • 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
    • B01J20/28Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties
    • B01J20/28002Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof characterised by their form or physical properties characterised by their physical properties
    • B01J20/28009Magnetic 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
    • B01J27/00Catalysts comprising the elements or compounds of halogens, sulfur, selenium, tellurium, phosphorus or nitrogen; Catalysts comprising carbon compounds
    • B01J27/02Sulfur, selenium or tellurium; Compounds thereof
    • B01J27/04Sulfides
    • B01J27/047Sulfides with chromium, molybdenum, tungsten or polonium
    • B01J27/051Molybdenum
    • B01J27/0515Molybdenum with iron group metals or platinum group metals
    • B01J35/33
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D2258/00Sources of waste gases
    • B01D2258/02Other waste gases
    • B01D2258/0283Flue gases

Abstract

The invention discloses a mercury removal adsorbent with a core-shell structure, which is characterized in that the mercury removal adsorbent is made of Fe3O4The nanoparticles are used as carriers through reaction of Fe3O4Surface in-situ growth MoS2Nanosheet, forming Fe3O4@MoS2Core-shell structure to obtain a core-shell structured polymerA mercury sorbent. In the invention, Fe3O4Dispersing the nano particles serving as a raw material into deionized water, adding ammonium molybdate tetrahydrate and thiourea, and preparing a mercury removal adsorbent, namely MoS, by using a hydrothermal method2@Fe3O4The nano composite material has good crystallinity, controllable appearance and size and good adsorption performance.

Description

Mercury removing adsorbent with core-shell structure and preparation method thereof
Technical Field
The invention belongs to the field of mercury removal materials, and particularly relates to a mercury removal adsorbent with a core-shell structure and a preparation method thereof.
Background
Molybdenum disulfide, metallic luster, black powder, a hexagonal system and a layered structure. The molybdenum disulfide and the graphene have similar structures and performances, only weak van der waals force exists between layers, the bonding energy is very low, the layers are easy to separate, and the friction factor is very low. Molybdenum disulfide has good heat resistance and stable chemical properties, is insoluble in dilute acid and water, but is soluble in aqua regia and hot concentrated sulfuric acid. Due to these characteristics, molybdenum disulfide (MoS2) has an energy band gap with an adjustable size, and thus has attracted much attention as a high-tech material in recent years, and is widely used in the fields of photoelectric devices, mechanical lubrication, catalysis, semiconductor materials, and the like. Compared with common molybdenum disulfide, the nano molybdenum disulfide has more excellent performance and plays an important role in the fields of aerospace, military and the like. The nano-grade molybdenum disulfide has larger specific surface area, is easier to adsorb gas particles, has higher sensitivity to light and gas, and is also applied to the aspect of detection. Molybdenum disulfide, however, has poor conductivity, which also limits its applications.
The magnetic nano-particles are novel nano-functions, have good biocompatibility and special magnetic functions, are mainly used for adsorbing heavy metal ions and organic pollutants in the environment, the composite material obtained by attaching peroxidase to the surface of the magnetic nano-particles has the advantages of the magnetic nano-particles and the catalytic activity of the enzyme, can be used for biocatalysis and bioseparation, and various composite structures of various substances can endow the composite material with various characteristics, so that the magnetic nano-particles have wide application fields. Along with the wide application of nano magnetic materials in various fieldsUsed as an important magnetic material-nano Fe3O4The particles have small particle size, high specific surface area, magnetism and permanent agglomeration. And the preparation process is nontoxic and non-dangerous.
Ferroferric oxide, chemical formula Fe3O4. The black iron oxide is also called magnetic iron oxide because it is a black crystal having magnetism, and can be approximately regarded as a compound composed of ferrous oxide and iron oxide (FeO. Fe)2O3). The substance is soluble in acid solution, and insoluble in water, alkali solution, and organic solvent such as ethanol and diethyl ether. The natural ferroferric oxide is insoluble in acid solution and is easily oxidized in air in a wet state. Fe3O4The nano-particles are magnetic black crystals, are small in size and large in specific surface area, have poor surface smoothness and can increase the contact surface of chemical reaction.
In recent years, a great deal of research shows that the nano material has no remarkable high efficiency for removing typical toxic pollution. Nano Fe3O4As functional materials, many special functions are exhibited in terms of magnetic recording materials, special catalytic materials, basic materials for magnetic fluids, and the like, but since Fe3O4The mutual attraction between the magnetic nano particle dipoles leads the nano particles to be easy to agglomerate, the surface of the nano particles is modified, the dispersibility of the nano particles and the stability of colloid of the nano particles can be improved, and a new function is introduced. The magnetic composite adsorbent is prepared by introducing the magnetic oxide into the adsorbent, and the rapid separation can be realized by using an external magnetic field.
Disclosure of Invention
The invention aims to provide a novel, efficient and recyclable mercury removal adsorbent with a core-shell structure and a preparation method thereof.
In order to achieve the purpose, the invention provides a mercury removal adsorbent with a core-shell structure, which is characterized in that the mercury removal adsorbent with the core-shell structure is made of Fe3O4The nanoparticles are used as carriers through reaction of Fe3O4Surface in-situ growth MoS2Nanosheet, forming Fe3O4@MoS2And (4) obtaining the mercury removal adsorbent with the core-shell structure by the core-shell structure.
The invention also provides a preparation method of the mercury removal adsorbent with the core-shell structure, which is characterized by comprising the following steps:
step 1: mixing ammonium molybdate tetrahydrate [ (NH)4)6Mo7O24·4H2O]Adding thiourea into deionized water, and stirring for dissolving to obtain a solution A;
step 2: mixing Fe3O4Dispersing the nano particles into the solution A, and uniformly stirring to obtain a solution B;
and step 3: pouring the solution B into a stainless steel reaction kettle with a polytetrafluoroethylene lining, and reacting for 10 hours at 160-200 ℃ to enable Fe3O4MoS deposition on surface of nanoparticles2Nanosheet, naturally cooling, washing and drying to obtain the mercury removal adsorbent with the core-shell structure, namely MoS2@Fe3O4A nanocomposite material.
Preferably, in the step 1, the concentration of ammonium molybdate tetrahydrate in the solution A is 0.024-0.028 mol/L, the concentration of thiourea is 0.833-1 mol/L, and the molar ratio of ammonium molybdate tetrahydrate to thiourea is not more than 0.0283: 1.
Preferably, in the step 2, the concentration of ammonium molybdate tetrahydrate in the solution B is 0.024-0.028 mol/L, the concentration of thiourea is 0.833-1 mol/L, and Fe3O4The concentration of the nano particles is 0.0072-0.0086 mol/L.
Preferably, Fe in said step 23O4The preparation of the nano-particles comprises: FeCl is added3·6H2O dissolved in pure ethylene glycol solution (concentration)>99%), stirring and dissolving by using a magnetic stirrer, sequentially adding anhydrous sodium acetate and polyethylene glycol, magnetically stirring for 60-90 min, transferring to a reaction kettle, reacting for 8h at 200 ℃, cooling to room temperature, repeatedly washing for 3-5 times by using deionized water and anhydrous ethanol respectively, placing in a drying oven, and drying at 60 ℃ to obtain Fe3O4And (3) nanoparticles.
Preferably, the washing in step 3 specifically comprises: washing with deionized water and anhydrous ethanol respectively in 7000r/min high speed centrifuge for 3-6 times, each for 3 min.
According to the invention, Fe3O4 is used as a raw material, a MoS2/Fe3O4 nano composite material is synthesized by a hydrothermal method, in-situ coating of MoS2 on Fe3O4 is realized, Fe3O4 is used as a carrier, and a catalyst adsorbent is coated on the surface of particles, so that the mercury removal adsorbent with a core-shell structure is prepared.
The mercury removal adsorbent with the core-shell structure has MoS2@Fe3O4Core-shell structure of Fe3O4@MoS2The core-shell structure has very positive chemical effect, Fe3O4Has certain magnetism, so that MoS generated on the surface2Condensed in Fe3O4Surface of nanoparticles, MoS2Is itself of graphene-like structure, Fe3O4The mercury adsorbent also has a larger specific surface area, and is beneficial to the adsorption of elemental mercury. Iron oxide has a large specific surface area and intrinsic magnetism, and is easy to cause a spontaneous aggregation phenomenon. The prepared MoS2/Fe3O4 nano-particle has good crystallinity, controllable morphology and size and good catalytic and adsorption properties.
Compared with the prior art, the invention has the beneficial effects that:
(1) the adsorbent for demercuration and the recovery method thereof provided by the invention have the advantages of simple and controllable process and mild operation conditions, and the demercuration efficiency of the obtained demercuration adsorbing material in a nitrogen atmosphere is very high.
(2) The demercuration adsorbent can be used for demercuration of flue gas of a power plant and can also be used for adsorbing mercury exposed to the atmospheric environment at ordinary times, and the mercury can be sprayed by adopting a method of spraying activated carbon by the power plant, and Fe3O4The adsorbent is a matrix, and the adsorbent saturated in adsorption can be partially recovered by a magnet, and can be reused after being desorbed after recovery.
(3) The demercuration adsorbent prepared by the invention has MoS2@Fe3O4The core-shell structure is easy to prepare due to the special structure and magnetism, and can be partially recycled by utilizing a magnetThe mercury removing adsorbent is environment-friendly and economical, has high efficiency, is an ideal mercury removing adsorbent and has good application prospect.
Drawings
Fig. 1 is an SEM image of demercuration adsorbent 1 prepared in example 1 of the present invention;
fig. 2 is an SEM image of the demercuration adsorbent 2 prepared in example 2 of the present invention;
fig. 3 is an SEM image of the demercuration adsorbent 3 prepared in example 3 of the present invention;
FIGS. 4 to 6 are mercury concentration change curves of the demercuration adsorbents 1, 2 and 3 prepared in the embodiments 1 to 3 of the present invention in a demercuration adsorption experiment;
FIG. 7 shows a reaction platform for mercury adsorption experiments in flue gas using a fixed bed according to the present invention.
Detailed Description
The invention will be further illustrated with reference to the following specific examples. It should be understood that these examples are for illustrative purposes only and are not intended to limit the scope of the present invention. Further, it should be understood that various changes or modifications of the present invention may be made by those skilled in the art after reading the teaching of the present invention, and such equivalents may fall within the scope of the present invention as defined in the appended claims.
The invention adopts a fixed bed as a reaction platform of a flue gas mercury adsorption experiment, and the capability of the composite material for removing mercury is researched by referring to fig. 7. N at a constant flow rate2The mercury generator mixes the mercury vapor with a certain concentration and the protective gas nitrogen in the gas mixing valve. In order to keep the system stable, the mixed gas firstly passes through a bypass and then passes through a mercury analyzer, and finally the gas is recovered after being treated by a tail gas treatment device. When the mercury source signal is stable and the temperature controller maintains the reaction temperature at 120 ℃, the gas path is cut to the main path, the mixed gas starts to react with the adsorbent fixed by quartz cotton and quartz beads through the quartz tube, and the content of mercury in the mixed gas is measured and recorded for 2 hours.
Example 1
The embodiment provides a preparation method of a mercury removal adsorbent with a core-shell structure, which comprises the following specific steps:
step 1: 1.35g of FeCl3·6H2O dissolved in 40mL of pure ethylene glycol solution (concentration)>99 percent), stirring for 30min by using a magnetic stirrer, sequentially adding 3.6g of anhydrous sodium acetate and 1.0g of polyethylene glycol, and magnetically stirring for 60-90 min at the rotating speed of 5 r/min; transferring the obtained solution to a 100ml water reaction kettle, reacting for 8 hours at 200 ℃, cooling to room temperature after the reaction is finished, repeatedly washing for 3-5 times by using absolute ethyl alcohol and deionized water, and washing the washed Fe3O4The nano particles are put into an oven and dried at the temperature of 60 ℃ to obtain clean Fe3O4A nanoparticle;
step 2: 1.75g of ammonium molybdate tetrahydrate [ (NH4)6Mo7O24·4H2O]Adding 3.8g of thiourea into 50mL of deionized water, and stirring for 30min by using a magnetic stirrer at the rotating speed of 5r/min to obtain a solution A;
and step 3: 0.1g of Fe obtained in step 13O4Dispersing the nano particles into the solution A prepared in the step 2, and stirring for 30min by using a magnetic stirrer at the rotating speed of 5r/min to obtain a solution B;
and 4, step 4: pouring the solution B obtained in the step 3 into a stainless steel reaction kettle with a polytetrafluoroethylene lining, and reacting for 10 hours at 160 ℃ to enable Fe3O4MoS deposited on surface of nano-particles2Naturally cooling the nano-sheets, centrifugally washing the nano-sheets for 3-6 times in a 7000r/min high-speed centrifuge by using deionized water and absolute ethyl alcohol for 3min each time, and finally drying the cleaned samples in a 60 ℃ drying oven for 10h to obtain a mercury removal adsorbent 1, namely MoS2@Fe3O4A nanocomposite material.
Example 2
The difference between the example and the example 1 is that the hydrothermal reaction temperature in the step 4 is 180 ℃, the rest steps are the same as the example 1, and finally the mercury-removing adsorbent 2 is obtained.
Example 3
The difference between this example and example 1 is that the hydrothermal reaction temperature in step 4 is 200 ℃, the rest steps are the same as example 1, and finally mercury-removing adsorbent 3 is obtained.
As shown in FIGS. 1, 2 and 3, the temperature of synthesis is variedElevation of (3), Fe3O4The surface of the nano particle is coated with more MoS2Nanosheets, MoS2The crystallinity and order of the nanoplatelets also increase.
As shown in figures 4, 5 and 6, the smoke of a simulated power plant (120 ℃) is treated by N2As a carrier gas, the demercuration rates of the mercury removal adsorbent 1 and the mercury removal adsorbent 2 can almost reach 100% within 50min, the demercuration rate of the mercury removal adsorbent 3 is 98-100%, the demercuration rates are stable, the demercuration rate of molybdenum disulfide produced by the process can only reach about 80%, and the demercuration effect of the invention is far better than that of industrial molybdenum disulfide.

Claims (6)

1. The mercury removal adsorbent with the core-shell structure is characterized in that the mercury removal adsorbent is made of Fe3O4The nanoparticles are used as carriers through reaction of Fe3O4Surface in-situ growth MoS2Nanosheet, forming Fe3O4And the @ MoS2 core-shell structure is adopted to obtain the mercury removal adsorbent with the core-shell structure.
2. The preparation method of the mercury removal adsorbent with the core-shell structure, which is described in claim 1, is characterized by comprising the following steps:
step 1: adding ammonium molybdate tetrahydrate and thiourea into deionized water, and stirring for dissolving to obtain a solution A;
step 2: mixing Fe3O4Dispersing the nano particles into the solution A, and uniformly stirring to obtain a solution B;
and step 3: pouring the solution B into a stainless steel reaction kettle with a polytetrafluoroethylene lining, and reacting for 10 hours at 160-200 ℃ to enable Fe3O4MoS deposition on surface of nanoparticles2Nanosheet, naturally cooling, washing and drying to obtain the mercury removal adsorbent with the core-shell structure, namely MoS2@Fe3O4A nanocomposite material.
3. The method for preparing the mercury removal adsorbent with the core-shell structure according to claim 2, wherein in the step 1, the concentration of ammonium molybdate tetrahydrate in the solution A is 0.024-0.028 mol/L, the concentration of thiourea is 0.833-1 mol/L, and the molar ratio of ammonium molybdate tetrahydrate to thiourea is not more than 0.0283: 1.
4. the method for preparing the mercury removal adsorbent with the core-shell structure according to claim 2, wherein in the step 2, the concentration of ammonium molybdate tetrahydrate in the solution B is 0.024-0.028 mol/L, the concentration of thiourea is 0.833-1 mol/L, and Fe3O4The concentration of the nano particles is 0.0072-0.0086 mol/L.
5. The method for preparing mercury removal sorbent with core-shell structure according to claim 2, wherein in the step 2, Fe3O4The preparation of the nano-particles comprises: FeCl is added3·6H2Dissolving O in a pure ethylene glycol solution, stirring and dissolving by using a magnetic stirrer, sequentially adding anhydrous sodium acetate and polyethylene glycol, magnetically stirring for 60-90 min, transferring to a reaction kettle, reacting for 8h at 200 ℃, cooling to room temperature, repeatedly washing with deionized water and anhydrous ethanol for 3-5 times respectively, placing in an oven, and drying at 60 ℃ to obtain Fe3O4And (3) nanoparticles.
6. The method for preparing the mercury removal adsorbent with the core-shell structure according to claim 2, wherein the washing in the step 3 specifically comprises: and respectively carrying out centrifugal washing for 3-6 times and 3min each time by using deionized water and absolute ethyl alcohol in a 7000r/min high-speed centrifuge.
CN201911012730.2A 2019-10-23 2019-10-23 Mercury removing adsorbent with core-shell structure and preparation method thereof Pending CN110665455A (en)

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CN111250035A (en) * 2020-02-20 2020-06-09 上海电力大学 Flower-ball-shaped molybdenum-based composite ferroferric oxide adsorbent material for demercuration and preparation method thereof
CN112090431A (en) * 2020-09-11 2020-12-18 浙江理工大学 Gamma-Fe2O3@MoS2Magnetic composite material and preparation method thereof
CN112090430A (en) * 2020-09-11 2020-12-18 浙江理工大学 Fe3O4@MoS2Magnetic composite structure and preparation method thereof
CN112808228A (en) * 2020-12-30 2021-05-18 华北电力大学(保定) WSe2/halloysite nanotube demercuration adsorbent and preparation method and application thereof
CN113926497A (en) * 2021-10-08 2022-01-14 浙江工商大学 Aptamer modification based MoS2Microfluidic array mass spectrum chip made of composite material and preparation method and application thereof
CN115382499A (en) * 2022-08-10 2022-11-25 中国科学院生态环境研究中心 Molybdenum disulfide/ferroferric oxide magnetic nano material with core-shell structure and preparation method and application thereof
CN115634661A (en) * 2022-10-25 2023-01-24 唐山师范学院 Efficient adsorbent and preparation method and application thereof

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Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111250035A (en) * 2020-02-20 2020-06-09 上海电力大学 Flower-ball-shaped molybdenum-based composite ferroferric oxide adsorbent material for demercuration and preparation method thereof
CN112090431A (en) * 2020-09-11 2020-12-18 浙江理工大学 Gamma-Fe2O3@MoS2Magnetic composite material and preparation method thereof
CN112090430A (en) * 2020-09-11 2020-12-18 浙江理工大学 Fe3O4@MoS2Magnetic composite structure and preparation method thereof
CN112808228A (en) * 2020-12-30 2021-05-18 华北电力大学(保定) WSe2/halloysite nanotube demercuration adsorbent and preparation method and application thereof
CN113926497A (en) * 2021-10-08 2022-01-14 浙江工商大学 Aptamer modification based MoS2Microfluidic array mass spectrum chip made of composite material and preparation method and application thereof
CN113926497B (en) * 2021-10-08 2022-12-30 浙江工商大学 Aptamer modification based MoS 2 Microfluidic array mass spectrum chip made of composite material and preparation method and application thereof
CN115382499A (en) * 2022-08-10 2022-11-25 中国科学院生态环境研究中心 Molybdenum disulfide/ferroferric oxide magnetic nano material with core-shell structure and preparation method and application thereof
CN115634661A (en) * 2022-10-25 2023-01-24 唐山师范学院 Efficient adsorbent and preparation method and application thereof
CN115634661B (en) * 2022-10-25 2023-11-21 唐山师范学院 Efficient adsorbent and preparation method and application thereof

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Application publication date: 20200110