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Ozonization water treatment method by taking fluorine-doped manganese dioxide nano composite material as catalyst

A nano-composite material, manganese dioxide technology, applied in the field of environmental catalysis and water treatment, can solve the problems of narrow degradation range, low mineralization rate, slow reaction rate, etc., and achieve the effect of simple and environmentally friendly synthesis process without secondary pollution

Inactive Publication Date: 2013-03-20
JIANGNAN UNIV
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

However, due to the problems of slow reaction rate, narrow degradation range, and low mineralization rate of ozone oxidation alone, the catalytic ozonation reaction with catalyst added in the ozone oxidation process has its unique application prospects.

Method used

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  • Ozonization water treatment method by taking fluorine-doped manganese dioxide nano composite material as catalyst
  • Ozonization water treatment method by taking fluorine-doped manganese dioxide nano composite material as catalyst
  • Ozonization water treatment method by taking fluorine-doped manganese dioxide nano composite material as catalyst

Examples

Experimental program
Comparison scheme
Effect test

Embodiment 1

[0017] Weigh 9mmol KMnO 4 , Dissolve it in 80mL of water, and stir it evenly with a magnetic stirrer. Weigh 6mmol MnCl 2 4H 2 O was dissolved in 20 mL of water, and then added dropwise at a rate of 2.4 mL / min to the previously dissolved and stirred KMnO 4 in solution. After the dropwise addition is completed, continue to stir for 1 hour, and then add 15 mL of 0.2 mol·L -1 NH 4 The F solution was added dropwise to the aforementioned solution that had been reacted for 1 h. Waiting for NH 4 After all the solution F was added dropwise, after continuing to stir at the same rate for 1 h, the reaction liquid was transferred to a 120 mL hydrothermal reaction kettle, and reacted at 160° C. for 6 h. After the completion of the hydrothermal reaction, the reactor was naturally cooled to room temperature, and the obtained product was washed to neutrality, and dried at 80° C. for 18 hours to obtain the final nanomaterial.

Embodiment 2

[0019] Weigh 9mmol KMnO 4 , Dissolve it in 80mL of water, and stir it evenly with a magnetic stirrer. Weigh 6mmol MnCl 2 4H 2 O was dissolved in 20 mL of water, and then added dropwise at a rate of 2.4 mL / min to the previously dissolved and stirred KMnO 4 in solution. After the dropwise addition is completed, continue to stir for 1 hour, and then add 15 mL of 0.4 mol·L -1 NH 4 The F solution was added dropwise to the aforementioned solution that had been reacted for 1 h. Waiting for NH 4 After all the solution F was added dropwise, after continuing to stir at the same rate for 1 h, the reaction liquid was transferred to a 120 mL hydrothermal reaction kettle, and reacted at 160° C. for 6 h. After the completion of the hydrothermal reaction, the reactor was naturally cooled to room temperature, and the obtained product was washed to neutrality, and dried at 80° C. for 18 hours to obtain the final nanomaterial.

Embodiment 3

[0021] Weigh 9mmol KMnO 4 , Dissolve it in 80mL of water, and stir it evenly with a magnetic stirrer. Weigh 6mmol MnCl 2 4H 2 O was dissolved in 20 mL of water, and then added dropwise at a rate of 2.4 mL / min to the previously dissolved and stirred KMnO 4 in solution. After the dropwise addition is completed, continue to stir for 1 hour, and then add 15 mL of 0.6 mol·L -1 NH 4 The F solution was added dropwise to the aforementioned solution that had been reacted for 1 h. Waiting for NH 4 After all the solution F was added dropwise, after continuing to stir at the same rate for 1 h, the reaction liquid was transferred to a 120 mL hydrothermal reaction kettle, and reacted at 160° C. for 6 h. After the completion of the hydrothermal reaction, the reactor was naturally cooled to room temperature, and the obtained product was washed to neutrality, and dried at 80°C for 18 hours to obtain the final nanomaterial.

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Abstract

The invention provides an ozonization water treatment method by taking a fluorine-doped manganese dioxide nano composite material as a catalyst. The fluorine-doped manganese dioxide nano composite material is added into waste water containing phenol organics and is used as the catalyst for promoting degrading of ozone on phenol organic pollutants. On the basis, the invention also provides a novel ozonization water treatment method. The method belongs to the technical field of water treatment and environment catalysis. A non-metal element fluorine is introduced into the fluorine-doped manganese dioxide nano composite material; the fluorine-doped manganese dioxide nano composite material has the characteristics that the synthesis steps are easy to operate, and the scale is small; the fluorine-doped manganese dioxide nano composite material is high in dispersion property in an aqueous solution system and is easy to recycle; and during ozonization water treatment, the method has a wide prospect.

Description

technical field [0001] The invention proposes an ozonated water treatment method using a fluorine-doped manganese dioxide nanocomposite material as a catalyst to reduce water pollution, and belongs to the field of environmental catalysis and water treatment. Background technique [0002] At present, the industry continues to progress, but inevitably produces a lot of pollution. As an important industrial raw material widely used in the fields of drugs, dyes, fibers, phenolic resin synthesis, and medical disinfectants, the usage of phenol at home and abroad has been on the rise. Phenol is considered a highly toxic substance due to its inhibitory ability to the central nervous system and damage to kidney function. Due to the structural problems of phenol, the phenolic substances in the wastewater discharged from various factories are extremely difficult to degrade naturally. Ozone itself has a certain oxidation ability and is easy to decompose. It is an ideal oxidant for deg...

Claims

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Application Information

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Patent Type & Authority Applications(China)
IPC IPC(8): C02F1/78B01J23/34
Inventor 董玉明李坤蒋平平王光丽赵辉
Owner JIANGNAN UNIV