CN109621910A - Nano zero valence iron-metal organic frame core-shell material preparation method and applications - Google Patents

Nano zero valence iron-metal organic frame core-shell material preparation method and applications Download PDF

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CN109621910A
CN109621910A CN201910001204.XA CN201910001204A CN109621910A CN 109621910 A CN109621910 A CN 109621910A CN 201910001204 A CN201910001204 A CN 201910001204A CN 109621910 A CN109621910 A CN 109621910A
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nzvi
dissolved
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zif
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CN109621910B (en
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文嘉
方颖
章海波
曾光明
张思宇
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Hunan 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
    • B01J20/22Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material
    • B01J20/223Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising organic material containing metals, e.g. organo-metallic compounds, coordination complexes
    • B01J20/226Coordination polymers, e.g. metal-organic frameworks [MOF], zeolitic imidazolate frameworks [ZIF]
    • 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
    • B01J20/28011Other properties, e.g. density, crush strength
    • 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
    • C02F1/285Treatment of water, waste water, or sewage by sorption using synthetic organic sorbents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/20Heavy metals or heavy metal compounds
    • C02F2101/22Chromium or chromium compounds, e.g. chromates
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/30Wastewater or sewage treatment systems using renewable energies
    • Y02W10/37Wastewater or sewage treatment systems using renewable energies using solar energy

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  • Organic Chemistry (AREA)
  • Analytical Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Inorganic Chemistry (AREA)
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  • Hydrology & Water Resources (AREA)
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Abstract

The invention discloses nano zero valence iron-metal organic frame core-shell material NZVI@ZD preparation methods, method includes the following steps: (1) weighs molysite and polyvinylpyrrolidone (PVP) is dissolved in the ethanol solution that volume fraction is 60%, continued mechanical stirs under a nitrogen atmosphere, obtains anaerobic mixed liquor;It weighs sodium borohydride to be dissolved in deionized water, and is added dropwise in above-mentioned anaerobic mixed liquor, whole process keeps nitrogen and mechanical agitation, obtain NZVI crude product, NZVI crude product is washed with dehydrated alcohol, magnet is dried in vacuo after separating and collecting, and obtains NZVI;(2) salt solubility is weighed in methanol, after being completely dissolved, is dispersed NZVI in cobalt salt solution, and NZVI/Co mixed liquor is obtained;It weighs organic ligand and is dissolved in methanol, be subsequently added in NZVI/Co mixed liquor, standing obtains NZVI@ZIF-67 crude product, is washed with methanol, magnet is dried in vacuo after separating and collecting, and obtains NZVI@ZIF-67;(3) by NZVI@ZIF-67 material in tube furnace, lead to nitrogen calcining, obtain NZVI@ZD.Method of the invention effectively can synchronize absorption and reduction to Cr (VI), can be applied to processing containing Cr (VI) waste water.

Description

Nano zero valence iron-metal organic frame core-shell material preparation method and applications
Technical field
The invention belongs to material preparation and water-treatment technology fields, are related to the preparation method of core-shell material NZVI@ZD and answer With being gone using NZVI reinforced metal organic frame (MOF) derived material NZVI@ZD to heavy metal Cr in water pollution (VI) It removes.
Background technique
(Cr (VI) is a kind of supertoxic agent to Cr VI, it is considered to be carcinogenic substance, mutagens and teratogens in biosystem. It is widely used in the fields such as chromium plating, leather process hides, cooling tower, wood preservation, weaving, pigment, and concentration is higher in the environment, work Concentration in industry waste water is 0.5~270mg L-1.The World Health Organization suggests for Cr (VI) concentration in surface water body being down to 0.05mg L-1.Therefore, before being discharged into Water Environment System, it is necessary to remove Cr (VI) from waste water.And it chooses and Cr (VI) is removed High-efficient material then becomes water pollution and repairs the important scientific problems that field needs to solve.
Metal-organic framework materials (MOFs) be by a suitable solvent, central metallic ions or metal cluster with have One kind of machine ligand self assembly has the porous material of crystal structure.Due to the combination of organic and inorganic materials, MOFs tool There are large specific surface area, Kong Rong great and the unique properties such as chemical structure can be cut.These intrinsic characteristics make MOFs in various applications In there is very high potentiality, such as gas absorption, separation, catalysis, drug release, optics and sensing.As adsorbent, MOFs High-specific surface area and porosity facilitate pollutant by the absorption and diffusion of skeleton, there is MOFs in heavy metal adsorption Wide application prospect.In recent years, nanoparticle (NPs) is controllably integrated into MOFs, by the uniqueness for collecting two components Property promotes the correlative study of material property, causes more and more concerns.Core-shell structure copolymer NPs@MOFs structure is as various A kind of common form of NPs/MOFs composite construction, it is considered to be realize inorganic NPs and multi-functional MOFs performance synergistic effect One of most convenient, most efficient method.There are two significant advantages for core-shell structure copolymer NPs MOFs structure tool: (1) due to MOFs shell Cladding, the migration of partial size is small, surface is high NPs core and aggregation are extremely limited, to maintain NPs core Stability and chemical activity;(2) the respective characteristic of NPs and MOFs can be effectively bonded together.The absorption property of MOFs Depend primarily on their aperture.However, the MOFs of most of reports is micropore (aperture < 2nm), this can hinder macromolecular Diffusion, and limit the interaction of they and activated centre in MOFs structure.
Nano zero valence iron (NZVI) have many advantages, such as large specific surface area, reducing power are strong, absorption property is strong, be easily isolated and It is applied to the removal of Cr (VI).However, NZVI technology the disadvantages of there is easy aggregation, easily oxidizable and poor fluidities, resistance The extensive use of NZVI technology is hindered.Therefore, it will usually select a suitable carrier material and NZVI compound, and in recent years MOFs is used as the carrier material compound with NZVI.Zhou et al. (J.Chromatogr.A, 1487 (2017) 22-29) in Merge MOFs and NZVI (Fe@MIL-101 (Cr)) for the first time within 2017.Li et al. people (J.Solid State Chem., 269 (2019) 16-23) use Zn-MOF-74 as the carrier material (nZVI@Zn-MOF-74) for supporting NZVI.However, Fe@MIL-101 (Cr) It is all made of coprecipitation preparation with nZVI Zn-MOF-74, NZVI is very likely only attached to MOF material surface, not It can be coated among composite material by MOF narrow gap by stabilization.
Therefore, it is shell material that how to select, which has the MOFs of high adsorption capacity to Cr (VI), which kind of technology to expand shell material using The duct of material, and how NZVI to be effectively encapsulated in inside shell material, so that the superior performance of composite material, it is right to improve its The absorption property of environmental contaminants especially heavy metal is the technical issues of being worth research.
Summary of the invention
The technical problem to be solved by the present invention is to overcome the deficiencies in the prior art, for currently with MOF or NZVI technology Deficiency present in treatment of heavy metal polluted water body provides one kind with nano zero valence iron (NZVI) as core, metal organic frame (MOF) derived material is the preparation method of the novel core-shell material NZVI ZD of shell and rapidly and efficiently removes (VI) containing Cr using it Waste water.The present invention increases the aperture of ZIF-67 shell using carbonization, and NZVI is encapsulated in porous shell, strengthens NZVI ZD and goes to remove water The effect of middle Cr (VI).
In order to solve the above technical problems, the invention adopts the following technical scheme:
The preparation method of core-shell material NZVI@ZD, comprising the following steps:
(1) it weighs molysite and polyvinylpyrrolidone (PVP) is dissolved in the ethanol solution that volume fraction is 60%, in nitrogen item Continued mechanical stirs under part, obtains anaerobic mixed liquor;It weighs sodium borohydride to be dissolved in deionized water, and drop by drop by it It is added in above-mentioned anaerobic mixed liquor, whole process keeps nitrogen and mechanical agitation, NZVI crude product is obtained, with anhydrous second Alcohol washs NZVI crude product, and magnet is dried in vacuo after separating and collecting, and obtains NZVI;
(2) salt solubility is weighed in methanol, after being completely dissolved, is dispersed NZVI in cobalt salt solution, and it is mixed to obtain NZVI/Co Close liquid;It weighs organic ligand and is dissolved in methanol, be subsequently added in NZVI/Co mixed liquor, it is thick that standing obtains NZVI@ZIF-67 Product is washed with methanol, and magnet is dried in vacuo after separating and collecting, and obtains NZVI@ZIF-67;
(3) by NZVI@ZIF-67 material in tube furnace, lead to nitrogen calcining, obtain NZVI@ZD.
In the preparation method of above-mentioned core-shell material NZVI@ZD, it is preferred that in the step (1), the molysite is hydration Iron chloride (FeCl3·6H2O), mechanical stirring carries out at room temperature, and the time of the stirring is 30min~35min, the vacuum Dry temperature be 59~61 DEG C, vacuum drying time be 7.5~8.5h, the time persistently stirred be 30min~ 35min, the ethanol washing number are 3~4 times.
In the preparation method of above-mentioned core-shell material NZVI@ZD, it is preferred that in the step (2), the cobalt salt is hydration Cobalt nitrate (Co (NO3)3·6H2O), the dwell temperature is room temperature, and time of repose is 23~25h, the vacuum drying temperature It is 59~61 DEG C, vacuum drying time is 7.5~8.5h, and the methanol washing times are 3~4 times.
In the preparation method of above-mentioned core-shell material NZVI@ZD, it is preferred that in the step (3), the calcination temperature is 795~805 DEG C, heating rate is 5~6 DEG C of min-1, calcination time is 120~130min.
As a general technical idea, the present invention also provides the preparation methods of above-mentioned core-shell material NZVI@ZD a kind of Application of the NZVI@ZD obtained in processing heavy metal containing sewage.
In above-mentioned application, it is preferred that in the application, the heavy metal containing sewage is containing Cr (VI) sewage.
Compared with the prior art, the advantages of the present invention are as follows:
(1) the present invention provides the preparation methods of core-shell material NZVI@ZD a kind of.By in ZIF-67 raw material self assembling process The modified NZVI of PVP is added, NZVI core is encapsulated in inside ZIF-67 shell, and is big by the duct that subsequent carbonisation expands shell Small, whole preparation process is simple.
(2) NZVI@ZD caused by the preparation method of core-shell material NZVI@ZD of the present invention is in the absorption property to Cr (VI) On be significantly improved.
Detailed description of the invention
The adsorbent that Fig. 1 is the embodiment of the present invention 1, comparative example 1, comparative example 2 synthesize imitates the absorption of Cr in solution (VI) Fruit figure.
Isothermal of the adsorbent that Fig. 2 is the embodiment of the present invention 1, comparative example 1, comparative example 2 synthesize to Cr (VI) absorption property Adsorb matched curve.
Isothermal of the adsorbent that Fig. 3 is the embodiment of the present invention 1, comparative example 1, comparative example 2 synthesize to Cr (VI) absorption property Adsorb fitting parameter.
Specific embodiment
Below in conjunction with Figure of description and specific preferred embodiment, the invention will be further described, but not therefore and It limits the scope of the invention.
Material employed in following embodiment and instrument are commercially available.
Embodiment 1:
A kind of preparation method of core-shell material NZVI@ZD of the invention, comprising the following steps:
(1) 1.45g FeCl is weighed3·6H2O and 50mg PVP is dissolved in 60mL 70% (v/v) ethanol solution, and logical nitrogen stirs It mixes.By NaBH4(0.7g+20mL water) is added dropwise in solution, is dripped and is continued logical nitrogen gas stirring 30min.Use ethanol wash Three times, it is centrifuged, 60 DEG C of vacuum drying 12h.Products therefrom is NZVI.
(2) 0.87g Co (NO is weighed3)3·6H2O and 0.0168g NZVI is dissolved in 30mL anhydrous methanol, ultrasound 5min obtains uniform mixed liquor;It weighs 0.98g methylimidazole MeIm to be dissolved in 10mL anhydrous methanol, be slowly added to It states in mixed liquor, acquired solution is stood for 24 hours at room temperature, obtain NZVI@ZIF-67 crude product, washed with methanol, magnet point From 60 DEG C of vacuum drying 8h after collection, NZVI@ZIF-67 is obtained.
(3) NZVI@ZIF-67 obtained by step (2) is transferred in tube furnace, maintaining nitrogen purge, with 5 DEG C/min rate liter Temperature calcines 120min to 800 DEG C at this temperature, is naturally cooling to room temperature to get NZVI@ZD.
Comparative example 1:
A method of preparing ZIF-67 monomer, comprising the following steps:
(1) 0.87g Co (NO is weighed3)3·6H2O and 0.0168g NZVI is dissolved in 30mL anhydrous methanol, obtains Co (NO3)3·6H2O solution.
(2) it weighs 0.98g methylimidazole MeIm to be dissolved in 10mL anhydrous methanol, obtains MeIm solution.
(3) MeIm solution is slowly added into Co (NO3)3·6H2O solution stands for 24 hours at room temperature, it is thick to obtain ZIF-67 Product is washed with methanol, and 60 DEG C of vacuum drying 8h after being collected by centrifugation obtain ZIF-67 monomer.
Comparative example 2:
A kind of to prepare using NZVI as core, ZIF-67 is the method for the core-shell material NZVI@ZIF-67 of shell, comprising the following steps:
(1) 1.45g FeCl is weighed3·6H2O and 50mg PVP is dissolved in 60mL 70% (v/v) ethanol solution, and logical nitrogen stirs It mixes.By NaBH4(0.7g+20mL water) is added dropwise in solution, is dripped and is continued logical nitrogen gas stirring 30min.Use ethanol wash Three times, it is centrifuged, 60 DEG C of vacuum drying 12h.Products therefrom is NZVI.
(2) 0.87g Co (NO is weighed3)3·6H2O and 0.0168g NZVI is dissolved in 30mL anhydrous methanol, ultrasound 5min obtains uniform mixed liquor;It weighs 0.98g methylimidazole MeIm to be dissolved in 10mL anhydrous methanol, be slowly added to It states in mixed liquor, acquired solution is stood for 24 hours at room temperature, obtain NZVI@ZIF-67 crude product, washed with methanol, magnet point From 60 DEG C of vacuum drying 8h after collection, NZVI@ZIF-67 is obtained.
The removal to heavy metal ion Cr (VI) in water of three kinds of embodiment products therefroms is tested:
Prepared serial adsorbent material in Example 1, comparative example 1 and 2 carries out absorption to the Cr (VI) in aqueous solution It removes, method particularly includes:
Compound concentration gradient is 5,10,25,50,100,200,400,600mg L-1Cr (VI) solution.20mL is taken respectively Cr (VI) solution adjusts pH=5.0 in 50mL conical flask.It is separately added into 0.01g embodiment 1, comparative example 1, institute in comparative example 2 The serial adsorbent material of generation.Then it is vibrated for 24 hours in constant temperature oscillator in 25 DEG C, revolving speed 170rpm.It, will after adsorption saturation Solution is collected after crossing 0.22 μm of filter membrane, in surveying Cr (VI) concentration on ultraviolet specrophotometer, is absorbed optical wavelength and is set as 540nm.
As shown in Figure 1, the NZVI@ZD prepared by embodiment 1 is right compared with adsorbent synthesized by other two kinds of comparison schemes Ratio 1 and 2 is in low concentration (50 and 100mg L-1) under experiment condition, adsorption saturation state is had reached, even and if embodiment 1 is dense Degree is increased to 600mg L-1Saturation is not reached, and adsorbance increases with the increase of concentration, shows embodiment 1 to solution yet Middle Cr VI has very superior absorption property compared with comparative example 1 and 2.
After series material carries out the fitting of adsorption isotherm model L-type by origin software to Cr (VI) Adsorption experimental results, As a result see Fig. 2 and Fig. 3, the adsorbance for obtaining three kinds of adsorbents is respectively 226.5mg g-1(embodiment 1), 29.35mg g-1It is (right Ratio 1), 36.53mg g-1(comparative example 2).
The above described is only a preferred embodiment of the present invention, being not intended to limit the present invention in any form.Though So the present invention is disclosed as above with preferred embodiment, and however, it is not intended to limit the invention.It is any to be familiar with those skilled in the art Member, in the case where not departing from Spirit Essence of the invention and technical solution, all using in the methods and techniques of the disclosure above Appearance makes many possible changes and modifications or equivalent example modified to equivalent change to technical solution of the present invention.Therefore, Anything that does not depart from the technical scheme of the invention are made to the above embodiment any simple according to the technical essence of the invention Modification, equivalent replacement, equivalence changes and modification, all of which are still within the scope of protection of the technical scheme of the invention.

Claims (6)

1. the preparation method of core-shell material NZVI@ZD, comprising the following steps:
(1) it weighs molysite and polyvinylpyrrolidone (PVP) is dissolved in the ethanol solution that volume fraction is 60%, in nitrogen item Continued mechanical stirs under part, obtains anaerobic mixed liquor;It weighs sodium borohydride to be dissolved in deionized water, and is dropwisely added Into above-mentioned anaerobic mixed liquor, whole process keeps nitrogen and mechanical agitation, NZVI crude product is obtained, with dehydrated alcohol pair NZVI crude product is washed, and magnet is dried in vacuo after separating and collecting, and obtains NZVI;
(2) salt solubility is weighed in methanol, after being completely dissolved, is dispersed NZVI in cobalt salt solution, and NZVI/Co mixing is obtained Liquid;It weighs organic ligand and is dissolved in methanol, be subsequently added in NZVI/Co mixed liquor, standing obtains NZVI@ZIF-67 and slightly produces Object is washed with methanol, and magnet is dried in vacuo after separating and collecting, and obtains NZVI@ZIF-67;
(3) by NZVI@ZIF-67 material in tube furnace, lead to nitrogen calcining, obtain NZVI@ZD.
2. the preparation method of core-shell material NZVI@ZD according to claim 1, which is characterized in that in the step (1), The molysite is Ferric Chloride Hydrated, and mechanical stirring carries out at room temperature, and the time of the stirring is 30min~35min, described true The dry temperature of sky is 59~61 DEG C, and vacuum drying time is 7.5~8.5h, the time persistently stirred be 30min~ 35min, the ethanol washing number are 3~4 times.
3. the preparation method of core-shell material NZVI@ZD described according to claim 1~any one of 2, which is characterized in that described In step (2), the cobalt salt is nitric hydrate cobalt, and the dwell temperature is room temperature, and time of repose is 23~25h, the vacuum Dry temperature is 59~61 DEG C, and vacuum drying time is 7.5~8.5h, and the methanol washing times are 3~4 times.
4. the preparation method of core-shell material NZVI@ZD described in any one of claim 1 to 3, which is characterized in that described In step (3), the calcination temperature is 795~805 DEG C, and heating rate is 5~6 DEG C of min-1, calcination time be 120~ 130min。
5. NZVI@ZD made from a kind of preparation method such as any one of Claims 1 to 4 core-shell material NZVI@ZD is being handled Application in heavy metal containing sewage.
6. application according to claim 5, which is characterized in that in the application, the heavy metal containing sewage is sewage containing Cr.
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Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111252879A (en) * 2020-03-03 2020-06-09 天津师范大学 Modified nano-iron and preparation method and application thereof
CN113275024A (en) * 2021-06-07 2021-08-20 上海大学 Preparation method and application of ZIF-67 derived wrapped S-Fe/Co @ C bimetallic catalyst
CN114212831A (en) * 2021-06-24 2022-03-22 浙江工业大学 Cobalt-modified zero-valent iron sulfide and preparation method and application thereof
CN115382519A (en) * 2022-04-26 2022-11-25 华侨大学 Core-shell magnetic zirconium-based adsorbent and preparation method and application thereof
CN115555050A (en) * 2022-10-09 2023-01-03 四川大学 Preparation method and application of carbon-coated metal-organic framework material loaded nano zero-valent iron material
CN115555050B (en) * 2022-10-09 2024-06-04 四川大学 Preparation method and application of carbon-coated metal-organic framework material loaded nano zero-valent iron material

Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103657596A (en) * 2013-12-13 2014-03-26 天津工业大学 Synthesis method of magnetic metal organic framework composite material
CN104096542A (en) * 2014-06-23 2014-10-15 广西师范大学 Novel magnetic Fe / C@ MOF composite absorbent and preparation method thereof
CN105170097A (en) * 2015-09-29 2015-12-23 安徽工程大学 TiO2/ZIF-8 nanocomposite with core-shell structure and preparation method of TiO2/ZIF-8 nanocomposite
CN106693935A (en) * 2016-12-28 2017-05-24 福建工程学院 Method for preparing magnetic carbon material from core-shell metal organic framework
CN106984273A (en) * 2017-04-21 2017-07-28 昆明理工大学 A kind of preparation method and applications of magnetic MOF composites
CN107029671A (en) * 2017-04-21 2017-08-11 昆明理工大学 A kind of MODIFIED Fe3O4The preparation method and applications of@MOF composites
CN107096515A (en) * 2017-04-19 2017-08-29 郑州轻工业学院 Fe3O4 PSS@Co MOF preparation method and applications
CN108187620A (en) * 2018-01-30 2018-06-22 南京大学 A kind of preparation method and application of MOFs char-forming materials

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103657596A (en) * 2013-12-13 2014-03-26 天津工业大学 Synthesis method of magnetic metal organic framework composite material
CN104096542A (en) * 2014-06-23 2014-10-15 广西师范大学 Novel magnetic Fe / C@ MOF composite absorbent and preparation method thereof
CN105170097A (en) * 2015-09-29 2015-12-23 安徽工程大学 TiO2/ZIF-8 nanocomposite with core-shell structure and preparation method of TiO2/ZIF-8 nanocomposite
CN106693935A (en) * 2016-12-28 2017-05-24 福建工程学院 Method for preparing magnetic carbon material from core-shell metal organic framework
CN107096515A (en) * 2017-04-19 2017-08-29 郑州轻工业学院 Fe3O4 PSS@Co MOF preparation method and applications
CN106984273A (en) * 2017-04-21 2017-07-28 昆明理工大学 A kind of preparation method and applications of magnetic MOF composites
CN107029671A (en) * 2017-04-21 2017-08-11 昆明理工大学 A kind of MODIFIED Fe3O4The preparation method and applications of@MOF composites
CN108187620A (en) * 2018-01-30 2018-06-22 南京大学 A kind of preparation method and application of MOFs char-forming materials

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
ZHE WANG: "In situ Carbothermal Synthesis of Nanoscale Zero-Valent Iron", 《EUR. J. INORG. CHEM.》 *

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111252879A (en) * 2020-03-03 2020-06-09 天津师范大学 Modified nano-iron and preparation method and application thereof
CN113275024A (en) * 2021-06-07 2021-08-20 上海大学 Preparation method and application of ZIF-67 derived wrapped S-Fe/Co @ C bimetallic catalyst
CN114212831A (en) * 2021-06-24 2022-03-22 浙江工业大学 Cobalt-modified zero-valent iron sulfide and preparation method and application thereof
CN114212831B (en) * 2021-06-24 2024-03-01 浙江工业大学 Cobalt-modified zero-valent iron sulfide and preparation method and application thereof
CN115382519A (en) * 2022-04-26 2022-11-25 华侨大学 Core-shell magnetic zirconium-based adsorbent and preparation method and application thereof
CN115555050A (en) * 2022-10-09 2023-01-03 四川大学 Preparation method and application of carbon-coated metal-organic framework material loaded nano zero-valent iron material
CN115555050B (en) * 2022-10-09 2024-06-04 四川大学 Preparation method and application of carbon-coated metal-organic framework material loaded nano zero-valent iron material

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