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Modified halloysite composite material and application thereof

A composite material and halloysite nanotube technology, applied in the field of modified halloysite composite materials, can solve problems such as poor heavy metal adsorption effect, and achieve the effects of preventing condensation and increasing contact area.

Pending Publication Date: 2022-03-18
GUANGZHOU UNIVERSITY
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

[0004] In order to overcome the problem in the prior art that the loaded zero-valent iron composite material has a poor adsorption effect on heavy metals, one of the purposes of the present invention is to provide a modified halloysite composite material, and the second purpose of the present invention is to provide this modified Application of Halloysite Composite Materials

Method used

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  • Modified halloysite composite material and application thereof
  • Modified halloysite composite material and application thereof
  • Modified halloysite composite material and application thereof

Examples

Experimental program
Comparison scheme
Effect test

Embodiment 1

[0046] with attachedfigure 1 The shown process flow prepares the modified halloysite composite material, which specifically includes the following steps:

[0047] (1) Add 2.0 g of halloysite nanotubes (HNTs) into the reaction vessel, add 200 mL of deionized aqueous solution, and obtain a suspension by stirring and ultrasonication;

[0048] (2) Add 0.4 g of dopamine hydrochloride to the suspension obtained in step (1), adjust the pH value to 8.5 with Tris-HCl buffer, perform magnetic stirring at room temperature, and the stirring reaction time is 24h, and centrifugation after the reaction is completed ;

[0049] (3) Wash the solid sample obtained in step (2), dry it at 60° C. for 12 h, and grind it to prepare dopamine-modified halloysite nanotubes, which are denoted as P-HNTs;

[0050] (4) add 1.0g of P-HNTs in the container, add the mixed solution of 200mL deionized water and absolute ethanol, the volume ratio of water and absolute ethanol is 4:1, obtain suspension by stirrin...

Embodiment 2

[0058] The configuration of uranium standard solution and the determination method of uranium concentration are as follows:

[0059] Configuration of uranium standard solution: Accurately weigh 2.1095g of uranyl nitrate hexahydrate, dissolve it in a beaker with deionized water, fully dissolve it and transfer it to a 1L volumetric flask, and use 1% nitric acid to dilute to volume. Uranium solutions of different concentrations were obtained by diluting the stock solution.

[0060] The determination method of uranium concentration is as follows: trace amount of uranium is determined by spectrophotometry. The color is developed in a 10mL colorimetric tube; the maximum absorption wavelength is 651nm, the addition amount of the solution to be tested is 2mL, the addition amount of 0.1mol / L HCl is 500μL, the addition amount of 500mg / L arsine azo III is 2mL, the masking agent The amount of EDTA added was 1 mL.

[0061] Drawing of the standard curve: Take a part of the prepared mother...

Embodiment 3

[0072] The modified halloysite composite (P-HNTs@nZVI) prepared in Example 1 was used for uranium adsorption. The specific steps and results are as follows:

[0073] Take five groups of uranium-containing wastewater, adjust the pH of the uranium-containing wastewater to 6.0, the concentration of uranium in the wastewater to be 20 mg / L, and the volume of the uranium wastewater to be 50 mL, and add 0.005, 0.010, 0.015, 0.020, 0.025 g of P-HNTs@ nZVI, the mass concentration of the material is 0.1, 0.2, 0.3, 0.4, 0.5g / L, put it into a constant temperature oscillator, the speed is 180rpm, and the reaction is 5h. After shaking, it is quickly filtered. The filtrate is taken, and the concentration of uranium ions in the solution after adsorption is measured and calculated. , the results are shown in the appendix Image 6 .

[0074] like Image 6 As shown, with the increase of the dosage of P-HNTs@nZVI, the adsorption capacity gradually decreased. When the dosage was 0.1 g / L, the ad...

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Abstract

The invention discloses a modified halloysite composite material and application thereof. The invention relates to a modified halloysite composite material. The modified halloysite composite material comprises a dopamine modified halloysite nanotube, the dopamine modified halloysite nanotube is loaded with nano zero-valent iron. According to the modified halloysite composite material, the carrier effect of the halloysite nanotubes is fully exerted, and nano zero-valent iron is introduced to the surface of the halloysite by utilizing the specific chelation effect of dopamine, so that the agglomeration of the zero-valent iron is effectively prevented, and the contact area with pollutants is increased. When the modified halloysite composite material is used for adsorbing heavy metals in wastewater, the reduction effect of zero-valent iron is fully exerted, and the adsorption effect on the heavy metals is improved.

Description

technical field [0001] The invention belongs to the technical field of nanomaterials, and in particular relates to a modified halloysite composite material and its application. Background technique [0002] Clay minerals have the advantages of large specific surface area and strong ion exchange capacity. They are a kind of high-quality environmentally friendly adsorption materials with unique structures. They are often used as filling materials and adsorption media for radioactive waste liquids. Halloysite nanotubes are widely available and inexpensive, and have potential applications in environmental remediation due to their high porosity, inertness, and abundance. Its special tubular structure can be used as a carrier for metals, metal oxides and polymers, which has become a research hotspot. A single halloysite has poor adsorption performance for pollutants, and it is of great significance to use its tubular structure to load materials with high adsorption performance. ...

Claims

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Application Information

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IPC IPC(8): B01J20/22C02F1/28C02F101/20
CPCB01J20/22B01J20/12B01J20/02C02F1/281C02F1/705G21F9/12C02F2101/20C02F2101/006
Inventor 苏敏华欧涛韩卫星刘贺瑶李家宜沈琮杰黄颖
Owner GUANGZHOU UNIVERSITY