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A kind of modified polyaniline adsorbent and its preparation method and application

A technology of polyaniline and adsorbent, which is applied in the field of antibiotic pollutant treatment, can solve the problems of high selectivity requirements of photocatalytic oxidation degradation method, long degradation time of biochemical method, easy hardening of electrolytic bed, etc., achieve environmental friendliness and increase adsorption capacity , The effect of simple preparation process

Active Publication Date: 2019-01-04
BEIJING NORMAL UNIVERSITY
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

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Problems solved by technology

Among them, the coagulation precipitation method, Fenton oxidation method, ozone oxidation method, and membrane separation method have the problem of high cost; the electrolytic bed of the electrolytic method is easy to harden; the photocatalytic oxidation degradation method has high requirements for selectivity; the biochemical method has a long degradation time and other issues; and the above method has high requirements on the chemical oxygen demand and the concentration of ciprofloxacin in the water body, and its treatment effect is directly related to the pollutant concentration and pH value. It is generally used for relatively stable water quality and pollutants. In the treatment of industrial wastewater with high concentration

Method used

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  • A kind of modified polyaniline adsorbent and its preparation method and application
  • A kind of modified polyaniline adsorbent and its preparation method and application
  • A kind of modified polyaniline adsorbent and its preparation method and application

Examples

Experimental program
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Effect test

Embodiment 1

[0022] (1) Weigh 3g of oxidant ammonium persulfate and dissolve it in 30mL 0.5mol / L protonic acid solution, and record it as solution A; take 1mL aniline monomer and dissolve it in 20mL 0.5mol / L protonic acid solution, and record it as solution B; The protic acid is a mixture of hydrochloric acid and dodecylbenzenesulfonic acid, and the molar ratio of the two is 0.6:1; the solution A and the solution B are ultrasonically dispersed and then cooled to -5~0°C;

[0023] (2) Slowly drop solution A into solution B to obtain a mixed solution;

[0024] (3) Static oxidation polymerization reaction occurs at -5~0℃, and the reaction time is 2~18h;

[0025] (4) After the reaction is completed, the reaction product is filtered and washed, dried in vacuum and then ground and dispersed to obtain the modified polyaniline adsorbent.

[0026] The modified polyaniline adsorbent prepared in this embodiment is as follows: figure 1 As shown, it is composed of polyaniline with a micro-nano seconda...

Embodiment 2

[0028] (1) Take by weighing 15.7g oxidant ammonium persulfate and dissolve in 33mL 2mol / L protonic acid solution, and record as solution A; get 8mL aniline monomer and dissolve in 20mL 2mol / L protonic acid solution, and record as solution B; The protic acid is a mixture of hydrochloric acid and dodecylbenzenesulfonic acid, and the molar ratio of the two is 0.6:1; the solution A and the solution B are ultrasonically dispersed and cooled to -5~0°C;

[0029] (2) Slowly drop solution A into solution B to obtain a mixed solution;

[0030] (3) Static oxidation polymerization reaction occurs at -5~0℃, and the reaction time is 2~18h;

[0031] (4) After the reaction is completed, the reaction product is filtered and washed, dried in vacuum and then ground and dispersed to obtain the modified polyaniline adsorbent.

Embodiment 3

[0033] (1) Take 2.4g of oxidant ammonium persulfate and dissolve it in 37mL 1mol / L protonic acid solution, and record it as solution A; get 4mL aniline monomer and dissolve it in 20mL 1mol / L protonic acid solution, and record it as solution B; The protic acid is a mixture of hydrochloric acid and dodecylbenzenesulfonic acid, and the molar ratio of the two is 0.6:1; the solution A and the solution B are ultrasonically dispersed and cooled to -5~0°C;

[0034] (2) Slowly drop solution A into solution B to obtain a mixed solution;

[0035] (3) Static oxidation polymerization reaction occurs at -5~0℃, and the reaction time is 2~18h;

[0036] (4) After the reaction is completed, the reaction product is filtered and washed, dried in vacuum and then ground and dispersed to obtain the modified polyaniline adsorbent.

[0037] The method of modified polyaniline adsorption ciprofloxacin of the present invention adopts static adsorption method, and concrete steps are as follows:

[0038]...

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Abstract

The invention belongs to the technical field of antibiotic pollutant treatment and particularly relates to modified polyaniline adsorbent and a preparation method and application thereof. The adsorbent is prepared from polyaniline with micro-nano two-stage structure, wherein micro polyaniline acts as a support framework in fibrous form, and nano polyaniline is distributed on the surface of the support frame and is in spherical particle form. The adsorbent is prepared by chemical in-situ oxidation; since the adsorbent has the advantages of unique micro-nano two-stage structure, large specific surface area and rich surface polyfunctional groups, adsorbing efficiency and capacity of polyaniline for ciprofloxacin are effectively increased.

Description

technical field [0001] The invention belongs to the technical field of antibiotic pollutant treatment, and in particular relates to a modified polyaniline adsorbent and its preparation method and application. Background technique [0002] In recent years, with the widespread use of antibiotics, a large number of antibiotics have entered the water environment, and the problem of water pollution caused by antibiotics has attracted widespread attention in the world. Among them, ciprofloxacin, as a typical antibiotic, is widely used in disease prevention and treatment. Studies have shown that only a small part of drugs can be metabolized and degraded in animals, and most of ciprofloxacin is excreted in feces in the form of original drugs and metabolites, and enters the ecological environment through sewage treatment discharge, animal manure application, etc. produce adverse effects. Therefore how to reduce the content of ciprofloxacin in the water environment is of great signi...

Claims

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Application Information

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Patent Type & Authority Patents(China)
IPC IPC(8): B01J20/26B01J20/28B01J20/30C02F1/28
CPCB01J20/265B01J20/28014B01J2220/4806C02F1/285
Inventor 俞盈姜晓满田朝晖张平呼丽娟赵金博马彦琪
Owner BEIJING NORMAL UNIVERSITY