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Preparation method and application of a tetraaminoiron ligand-bonded cyclodextrin catalyst

A technology of tetraamino and cyclodextrin, applied in the direction of organic compound/hydride/coordination complex catalysts, chemical instruments and methods, physical/chemical process catalysts, etc. impact and other issues, to achieve good economic and environmental benefits, improve stability, and low input costs

Active Publication Date: 2021-09-24
DALIAN UNIV OF TECH
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

This method does not mention the effect of cyclodextrin complexation on the catalytic performance of tetraaminoiron ligand catalysts in aqueous solution
There is no report on the construction of catalytic system by combining cyclodextrin and tetraaminoiron ligand in the form of covalent bond

Method used

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  • Preparation method and application of a tetraaminoiron ligand-bonded cyclodextrin catalyst
  • Preparation method and application of a tetraaminoiron ligand-bonded cyclodextrin catalyst
  • Preparation method and application of a tetraaminoiron ligand-bonded cyclodextrin catalyst

Examples

Experimental program
Comparison scheme
Effect test

Embodiment 1

[0025] Weigh 3.0 g of tetraaminomacrocyclic ligand and add it into a 250 mL three-neck flask, add 40 mL of chlorosulfonic acid and 2.0 mL of thionyl chloride, react at 60°C-70°C for 8 hours, add ice water and stir for 1 hour, filter, and use Wash with ice water and dry to obtain the sulfonyl chloride-substituted tetraaminomacrocyclic ligand.

[0026] Weigh 2.7g of the sulfonyl chloride-substituted tetraaminomacrocyclic ligand, add it to a 500mL three-neck flask filled with 100mL of dry tetrahydrofuran solution, add 10mL of n-butyl lithium in n-hexane solution (2.5mol / L), and react at 60°C 20min. After completion of the reaction, add 1.08g of anhydrous FeCl in the above reaction solution 3 , heated at 60°C for 4 h, the solid was collected by filtration, washed with 10 mL of tetrahydrofuran and diethyl ether, and dried to obtain the sulfonyl chloride-substituted tetraaminoiron ligand.

[0027] Add 75mL of distilled water to a 500mL three-necked flask and add 6.0g of β-cyclodex...

Embodiment 2

[0031] Prepare an aqueous solution of organic pollutants with a concentration of 100 μg / L, adjust pH=8.0, take 20 mL and add it to a 50 mL Erlenmeyer flask, add tetraaminoiron ligand-bonded cyclodextrin catalyst and hydrogen peroxide, so that the catalyst, oxidant and The molar concentration ratio of pollutants is 1:100:100. The reaction was oscillated in a constant temperature shaking box at 25°C (rotating speed 200r / min), and samples were taken at 0, 2, 4, 8, 15, and 30 min, and the samples were analyzed by HPLC-MS / MS. Tetraamino iron ligand catalyst / H 2 o 2 The degradation rate of the system to carbamide, acetochlor, metolachlor, isoprocarb and malathion can reach more than 99% within 2 minutes. Tetraamino iron ligand bonded cyclodextrin catalyst / H 2 o 2 The first-order degradation reaction rate of the system to acetamiprid, sulfamethoxazole, sulfathiazole, sulfamethazine, norfloxacin, and thiabendazole is 0.035-0.049min -1 , is 1.3-2.2 times of the degradation rate of...

Embodiment 3

[0033] Prepare a sodium dihydrogen phosphate solution with a concentration of 0.2mol / L, take 5mL and add it to a 15mL centrifuge tube, add a quantitative tetraaminoiron ligand-bonded cyclodextrin catalyst to make the concentration 0.25mmol / L (112.5mg / L) , quickly mixed and transferred to a quartz cuvette, and measured the absorbance at a wavelength of 365nm with a UV spectrophotometer every 120s. The hydrolytic stability of the tetraaminoiron ligand-bonded cyclodextrin catalyst prepared in Example 1 was investigated according to the change of absorbance. The first-order hydrolysis reaction rate of tetraaminoiron ligand-bonded cyclodextrin catalyst is 4.4×10 -5 the s -1 , while the hydrolysis reaction rate of the tetraaminoiron ligand catalyst alone and the hydrolysis reaction rate of the tetraaminoiron ligand / cyclodextrin mixed system were 3.6×10 - 3 the s -1 and 8.0×10 -4 the s -1 , are respectively 82 times and 20 times of the hydrolysis reaction rate of tetraaminoiron...

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Abstract

The invention provides a preparation method and application of a tetraaminoiron ligand-bonded cyclodextrin catalyst. The preparation method comprises the following steps: adding the tetraaminomacrocyclic ligand into chlorosulfonic acid and thionyl chloride to carry out sulfonyl chloride reaction to obtain the tetraaminomacrocyclic ligand substituted by sulfonyl chloride. Disperse the prepared sulfonyl chloride-substituted tetraaminomacrocyclic ligand in tetrahydrofuran solution, add n-butyl lithium in n-hexane solution for hydrogen extraction, add ferric chloride for metal chelation reaction, and obtain sulfonyl chloride-substituted tetraamino Iron ligand. Dissolve β-cyclodextrin in sodium hydroxide solution, dissolve the prepared tetraaminoiron ligand substituted with sulfonyl chloride in acetonitrile and add it dropwise to the cyclodextrin solution for cyclodextrin modification reaction to obtain tetraaminoiron ligand Iron ligand-bonded cyclodextrin catalyst. The catalyst has good stability, significant effect, mild reaction conditions, small dosage, and low input cost. It is a green and efficient catalytic system, which provides a new solution to the problem of water organic pollution and has a good application prospect.

Description

technical field [0001] The invention belongs to the technical field of water pollution control, and relates to a preparation method of a novel tetraaminoiron ligand-bonded cyclodextrin catalyst, in particular to a tetraaminoiron ligand that improves the catalytic activity and stability of the tetraaminoiron ligand Preparation method and application of bonded cyclodextrin catalyst. Background technique [0002] The problem of organic pollution of water bodies has attracted much attention, and both surface water and groundwater are subject to different degrees of organic pollution. The amount of organic pollutants in water bodies is increasing, and most organic pollutants are toxic, endocrine disrupting, and bioaccumulative, and pose potential risks to aquatic organisms and human health. Some organic pollutants in water bodies have a relatively stable structure, and some pollutants will be transformed into transformation products with stable structures, making it difficult fo...

Claims

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Application Information

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Patent Type & Authority Patents(China)
IPC IPC(8): B01J31/22C08B37/16C02F1/72
CPCB01J31/1805C02F1/722C02F1/725C08B37/0012
Inventor 蔡喜运刘清泉蔡本哲
Owner DALIAN UNIV OF TECH