Fe3O4@poly(m-phenylenediamine)@MnO2 magnetic core-shell structure nanocomposite material and preparation and application methods thereof

A nanocomposite material, poly-m-phenylenediamine technology, applied in chemical instruments and methods, alkali metal compounds, other chemical processes, etc., can solve the problems of few functional groups on the surface of magnetic iron nanoparticles and difficulty in achieving uniform loading of manganese oxide, etc. Achieve excellent adsorption performance, fast magnetic separation and recovery, and realize the effect of magnetic separation and recovery

Inactive Publication Date: 2016-06-08
CENT SOUTH UNIV
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

However, there are few functional groups on the surface of magnetic iron nanoparticles, and it is difficult to achieve uniform loading of manganese oxide.

Method used

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  • Fe3O4@poly(m-phenylenediamine)@MnO2 magnetic core-shell structure nanocomposite material and preparation and application methods thereof
  • Fe3O4@poly(m-phenylenediamine)@MnO2 magnetic core-shell structure nanocomposite material and preparation and application methods thereof
  • Fe3O4@poly(m-phenylenediamine)@MnO2 magnetic core-shell structure nanocomposite material and preparation and application methods thereof

Examples

Experimental program
Comparison scheme
Effect test

Embodiment 1

[0037] In the presence of non-magnetic iron particles, sodium persulfate is used as the oxidizing agent to polymerize m-phenylenediamine monomer, the ratio of monomer to oxidizing agent is 1:1, and the polymerization reaction is 3 hours. The synthesized pure PmPD (poly-m-phenylene diamine) was combined with 20mM KMnO under different pH conditions. 4 For the reaction, the pH was controlled to 3, 2, and 1, respectively.

[0038] The TEM images of materials synthesized under different pH conditions are shown in figure 1 .

[0039] by figure 1 It can be seen that when pH=3, rough small fluffy substances appear on the surface of the particles in CD. As the pH decreases, the surface of the particles gradually becomes rougher, and the scale of the outer surface becomes deeper, indicating that new substances may be formed; pH= The structure of yolk-shell appears at 2, which may be KMnO 4 It reacts with the outer surface of PmPD first, and the reaction product is loaded on the outer surface...

Embodiment 2

[0041] Weigh the equivalent amount of m-phenylenediamine monomer and Na 2 S 2 O 8 Add Fe sequentially 3 O 4 In dispersion, Fe 3 O 4 The concentration of the dispersion is 0.5-2g / L, Fe 3 O 4 The mass ratio with m-phenylenediamine monomer is 2:1-1:4. The reaction is shaken under ice-water bath conditions; after the reaction, it is washed with water and ethanol and dried to obtain Fe 3 O 4 Poly-m-phenylenediamine nanoparticles; measure 100mL of deionized water, add a certain amount of 1M HCl to adjust the pH to 2, and weigh 0.1g Fe 3 O 4 The poly-m-phenylenediamine was ultrasonically dispersed in a solution with pH=2. Then respectively weigh 0.05g, 0.1g, 0.2g, 0.4g, 0.8g potassium permanganate and add to the above Fe 3 O 4 In the poly-m-phenylene diamine dispersion liquid, the shaking reaction for 5 hours, magnetic separation, washing 3 times with water, washing 2 times with anhydrous ethanol, and drying the washed sample at 60 ℃, to obtain Fe 3 O 4 Poly-m-phenylenediamine MnO 2 Mag...

Embodiment 3

[0047] At room temperature, prepare As(III) solutions of different concentrations and adjust the pH to 5.0±0.2 with HCl. Weigh 0.01g of the Fe prepared in Example 2 3 O 4 Poly-m-phenylenediamine MnO 2 The magnetic core-shell structure nanocomposite material was added to 20mLAs(III) solution, placed in a constant temperature water bath shaking box for adsorption experiment, the reaction time was 8h; solid-liquid separation was carried out under the action of an external magnetic field, filtered and collected, the As(III) in the filtrate The concentration of) is determined by ICP-OES. Different proportions of Fe 3 O 4 Poly-m-phenylenediamine MnO 2 The adsorption isotherm of the magnetic core-shell nanocomposite for As(III) is as Figure 4 Shown. It can be seen from this figure that as the initial concentration of the As(III) solution increases, the adsorption capacity increases. Compare different proportions of Fe 3 O 4 Poly-m-phenylenediamine MnO 2 Magnetic core-shell structure ...

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Abstract

The invention discloses a Fe3O4@poly(m-phenylenediamine)@MnO2 magnetic core-shell structure nanocomposite material and preparation and application methods thereof, and belongs to the fields of magnetic composite material synthesis and water treatment research. The preparation method comprises the following steps that 1, Fe3O4 is dispersed into an aqueous solution, a certain quantity of m-phenylenediamine monomers (mPD) and a sodium persulfate solution are sequentially added, and after a reaction is finished, Fe3O4@poly(m-phenylenediamine) nano particles are obtained; 2, the Fe3O4@poly(m-phenylenediamine) nano particles obtained through the reaction are dispersed into an acidic aqueous solution, a potassium permanganate solution is added, and the Fe3O4@poly(m-phenylenediamine)@MnO2 magnetic core-shell structure nanocomposite material is obtained after a reaction. According to the preparation method, the technology is simple, operation is convenient, uniform loading of manganese dioxide on the surfaces of the magnetic particles can be achieved, high efficiency and low cost are achieved, and magnetic separation is easy; the obtained product has the good removing effect on arsenic in a water body, is safe, stable, reusable and capable of reducing secondary pollution and has the good application prospect.

Description

Technical field [0001] The invention belongs to the field of the synthesis of metal oxide and organic matter-coated magnetic core nanoparticles and their water treatment, and specifically relates to a controlled synthesis of Fe 3 O 4 Poly-m-phenylenediamine MnO 2 The magnetic core-shell structure nanocomposite material and its preparation method, and its application in the adsorption of trivalent arsenic in water. Background technique [0002] Arsenic is the most common and one of the most serious pollutants harmful to public health and the environment. Arsenic pollution of groundwater has become a global environmental problem, directly affecting the safety of drinking water. [0003] Inorganic arsenic in water mainly exists as As(V) and As(III), and the toxicity of trivalent arsenic is much higher than that of pentavalent arsenic. The methods that have been reported so far have good removal efficiency for low-toxic pentavalent arsenic, but low removal rate for high-toxic trivalen...

Claims

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Application Information

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Patent Type & AuthorityApplications(China)
IPC IPC(8): B01J20/26B01J20/28B01J20/30C02F1/28C02F1/58
CPCB01J20/26B01J20/0222B01J20/0229B01J20/28009B01J20/28019C02F1/288
Inventor王海鹰宋婷婷彭兵柴立元王婷杨卫春杨志辉唐崇俭
OwnerCENT SOUTH UNIV