CN105771877A - Method for preparing composite adsorption material MnO2-Fe3O4 with core-shell structure - Google Patents

Method for preparing composite adsorption material MnO2-Fe3O4 with core-shell structure Download PDF

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Publication number
CN105771877A
CN105771877A CN201610254142.XA CN201610254142A CN105771877A CN 105771877 A CN105771877 A CN 105771877A CN 201610254142 A CN201610254142 A CN 201610254142A CN 105771877 A CN105771877 A CN 105771877A
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Prior art keywords
adsorption material
mno2
fe3o4
composite adsorption
core
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李秋菊
张景
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University of Shanghai for Science and Technology
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University of Shanghai for Science and Technology
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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
    • 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
    • B01J20/28014Solid 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 form
    • 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
    • C02F1/281Treatment of water, waste water, or sewage by sorption using inorganic sorbents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/288Treatment of water, waste water, or sewage by sorption using composite sorbents, e.g. coated, impregnated, multi-layered

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  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Inorganic Chemistry (AREA)
  • Analytical Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

The invention discloses a method for preparing a core-shell composite adsorption material MnO2-Fe3O4, relates to a method for preparing a composite adsorption material MnO2-Fe3O4 with a core-shell structure, and aims to solve the technical problems that the adsorption material MnO2 is small in particle size, low in apparent density, difficult to separate and recycle, and high in probability of causing secondary pollution. The method for preparing the core-shell composite adsorption material comprises the following steps: at normal temperature, adding 0.51 g of KMnO4 to 40 mL of deionized water; dropwise adding 0.8 mL of HCl (37wt%), stirring for 15 minutes, and then adding 0.35 g of Fe3O4 (nanoscale) to obtain a mixture; transferring the mixture to a 50 mL high pressure reaction kettle to react for 6 hours at 110 DEG C; centrifugally separating the solution, and repeatedly washing precipitate with deionized water and alcohol for four times, and drying in a vacuum drying oven at 60 DEG C for 12 hours, to obtain the composite adsorption material MnO2-Fe3O4; subsequently, a method for applying a magnetic field can be used for separating the composite adsorption material adsorbing heavy metals from the water body, and has high operability.

Description

Nucleocapsid structure composite adsorbing material MnO2-Fe3O4Preparation method
Technical field
The present invention relates to the composite adsorbing material MnO of a kind of nucleocapsid structure2-Fe3O4Preparation method.
Background technology
Absorption method, because its floor space is little, technique is simple and convenient to operate, heavy metal treatment effeciency high, receives much concern in water processes.But adsorbing material particle diameter is little, apparent density is low, difficult separation and recycling, easily causes secondary pollution, and when processing low concentration heavy metal water, treatment effect is the best, sensible less than GB discharge.Therefore, research be not only able to process the effective and easily separated adsorbing material recycled of low-concentration heavy metal imperative.Compound adsorbing material is a kind of new thinking of development, it is possible to the shortcoming making up two or more single adsorbing materials itself, while ensureing adsorbance, makes NEW TYPE OF COMPOSITE regneration of adsorbent material program simple, and easy recycling reaches the purpose of economical and efficient.In various types of adsorbents, research worker finds that the metal-oxide with hydrolysising property has good chemical affinity with heavy metal, this quasi-metal oxides includes Mn, Fe, Al, Zn etc., and compare with other metal-oxides, to have specific surface area big because of it for Mn oxide, the features such as isoelectric point, IP is low, and surface hydroxyl is abundant, have the strongest absorbability to the heavy metal in water.And Fe3O4Not only there is absorption property, the most certain magnetic, it is possible to use its magnetic reclaims, therefore select MnO2And Fe3O4Mainly comprise composition as composite adsorbing material, make compound after material be not only able to the low-concentration heavy metal treatment effect that had, while can also carry out magnetic recovery.
Summary of the invention
One nucleocapsid structure composite adsorbing material MnO of the present invention2-Fe3O4Preparation method carry out according to the following steps:
(a). under room temperature, by 0.51gKMnO4Join in the deionized water of 40mL, be added dropwise over the HCl(37wt% of 0.8mL), stir 15min, be subsequently adding 0.35g Fe3O4(nanoscale);
(b). more above-mentioned mixed liquor is transferred to 110 DEG C of reaction 6h in the autoclave of 50mL;
(c). centrifugation, by precipitate deionized water and ethanol cyclic washing 4 times, it is dried 12h at 60 DEG C of vacuum drying ovens;Finally give composite adsorbing material MnO2-Fe3O4
Accompanying drawing explanation
Fig. 1 is the apparent figure that composite adsorbing material is mixed in water and Magneto separate.
Fig. 2 is for pure compound MnO2、Fe3O4With composite MnO2-Fe3O4FTIR(fourier conversion infrared spectrum analysis, resolution: standard 0.5cm-1;) comparison collection of illustrative plates.
Fig. 3 is composite MnO2-Fe3O4And Fe3O4XRD(X x ray diffraction analysis x) comparison chart.
Fig. 4 is composite MnO2-Fe3O4Scanning electron microscope (SEM) photograph.
Fig. 5 is composite MnO2-Fe3O4Transmission electron microscope picture.
Detailed description of the invention
Now the specific embodiment of the present invention is reported in rear.Embodiment 1, in the present embodiment, core-shell composite material MnO2-Fe3O4Preparation method carry out according to the following steps: (1). under room temperature, by 0.51gKMnO4Join in the deionized water of 40mL, be added dropwise over the HCl(37wt% of 0.8mL), stir 15min, be subsequently adding 0.35g Fe3O4(nanoscale).(2). more above-mentioned mixed liquor is transferred to 110 DEG C of reaction 6h in the autoclave of 50mL.(3). centrifugation, by precipitate deionized water and ethanol cyclic washing 4 times, it is dried 12h at 60 DEG C of vacuum drying ovens, finally gives composite adsorbing material MnO2-Fe3O4(such as Fig. 2 and Fig. 3).
Adsorbing material prepared by present embodiment method is a kind of by MnO2And Fe3O4The material (Fig. 2) being composited, even particle size distribution, at about 70nm (such as Fig. 4);MnO2With armorphous existence, (in Fig. 3, XRD figure spectrum does not has MnO2The existence of peak spectrum);This composite has nucleocapsid structure (Fig. 5);This composite has good dispersibility (Fig. 1 is left) and superior Magneto separate (Fig. 1 is right) in water.
Can be by this composite of the experimental verification removal effect to low-concentration heavy metal: in an experiment, Cu in water body2+Initial concentration be 10mg/L, the present embodiment composite adsorbing material MnO2-Fe3O4Dosage be 1g/L, final Cu2+Clearance be 99.81%.

Claims (1)

1. a nucleocapsid structure composite adsorbing material MnO2-Fe3O4Preparation method, it is characterised in that there is following process and step:
(a). at normal temperatures, by 0.51g KMnO4Join in the deionized water of 40mL, be added dropwise over the HCl(37wt% of 0.8mL), stir 15min, be subsequently adding 0.35g Fe3O4(nanoscale);
(b). more above-mentioned mixed liquor is transferred to 110 DEG C of reaction 6h in the autoclave of 50mL;
(c). centrifugation, by precipitate deionized water and ethanol cyclic washing 4 times, it is dried 12h at 60 DEG C of vacuum drying ovens;Finally give composite adsorbing material MnO2-Fe3O4
CN201610254142.XA 2016-04-23 2016-04-23 Method for preparing composite adsorption material MnO2-Fe3O4 with core-shell structure Pending CN105771877A (en)

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Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107281999A (en) * 2017-05-26 2017-10-24 北京工业大学 A kind of ferriferous oxide/manganese dioxide nano-composite material and preparation method and application
CN108014745A (en) * 2017-12-23 2018-05-11 福州大学 The preparation method and applications of nano-magnetic iron-based-Mn oxide
CN108404930A (en) * 2018-04-17 2018-08-17 上海电力学院 A kind of low-temperature denitration catalyst and preparation method thereof with nucleocapsid
CN114797889A (en) * 2022-04-12 2022-07-29 上海工程技术大学 Fe 3 O 4 @MnO 2 -CeO 2 Nano material and preparation method and application thereof
CN116408101A (en) * 2023-02-07 2023-07-11 上海电力大学 Preparation method and application of ferroferric oxide-manganese dioxide micro motor with core-shell structure

Citations (4)

* Cited by examiner, † Cited by third party
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CN102068995A (en) * 2011-01-11 2011-05-25 河北师范大学 Preparation method of nano magnetic core-shell catalyst for degrading dye wastewater
CN102188949A (en) * 2011-04-12 2011-09-21 哈尔滨工业大学 Method for preparing MnO2/Fe3O4 composite adsorbent and method for removing arsenic (III) in water by utilizing composite adsorbent
CN103007882A (en) * 2012-12-13 2013-04-03 同济大学 Preparation method of Fe3O4@MnO2/active carbon magnetic compound adsorption material
CN104016522A (en) * 2014-06-23 2014-09-03 瀚蓝环境股份有限公司 Method for handling emergent chlorophenol pollution of water body by using Fe3O4-MnO2 core-shell material

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CN102068995A (en) * 2011-01-11 2011-05-25 河北师范大学 Preparation method of nano magnetic core-shell catalyst for degrading dye wastewater
CN102188949A (en) * 2011-04-12 2011-09-21 哈尔滨工业大学 Method for preparing MnO2/Fe3O4 composite adsorbent and method for removing arsenic (III) in water by utilizing composite adsorbent
CN103007882A (en) * 2012-12-13 2013-04-03 同济大学 Preparation method of Fe3O4@MnO2/active carbon magnetic compound adsorption material
CN104016522A (en) * 2014-06-23 2014-09-03 瀚蓝环境股份有限公司 Method for handling emergent chlorophenol pollution of water body by using Fe3O4-MnO2 core-shell material

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Title
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Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107281999A (en) * 2017-05-26 2017-10-24 北京工业大学 A kind of ferriferous oxide/manganese dioxide nano-composite material and preparation method and application
CN107281999B (en) * 2017-05-26 2020-07-03 北京工业大学 Iron oxide/manganese dioxide nano composite material and preparation method and application thereof
CN108014745A (en) * 2017-12-23 2018-05-11 福州大学 The preparation method and applications of nano-magnetic iron-based-Mn oxide
CN108014745B (en) * 2017-12-23 2020-05-08 福州大学 Preparation method and application of nano magnetic iron-manganese oxide
CN108404930A (en) * 2018-04-17 2018-08-17 上海电力学院 A kind of low-temperature denitration catalyst and preparation method thereof with nucleocapsid
CN114797889A (en) * 2022-04-12 2022-07-29 上海工程技术大学 Fe 3 O 4 @MnO 2 -CeO 2 Nano material and preparation method and application thereof
CN114797889B (en) * 2022-04-12 2023-10-17 上海工程技术大学 Fe (Fe) 3 O 4 @MnO 2 -CeO 2 Nanometer material and preparation method and application thereof
CN116408101A (en) * 2023-02-07 2023-07-11 上海电力大学 Preparation method and application of ferroferric oxide-manganese dioxide micro motor with core-shell structure

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