CN103172251B - Novel chitosan-based sludge dewatering flocculant and preparation method thereof - Google Patents

Novel chitosan-based sludge dewatering flocculant and preparation method thereof Download PDF

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CN103172251B
CN103172251B CN201310140816.XA CN201310140816A CN103172251B CN 103172251 B CN103172251 B CN 103172251B CN 201310140816 A CN201310140816 A CN 201310140816A CN 103172251 B CN103172251 B CN 103172251B
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chitosan
sludge dewatering
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flocculant
water
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CN103172251A (en
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叶林
黄朋
赵晓文
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Sichuan University
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Abstract

The invention discloses a novel chitosan-based sludge dewatering flocculant and a preparation method thereof. The novel chitosan-based sludge dewatering flocculant is characterized by being prepared through the following steps of: dispersing 5-300 parts of modified montmorillonite into 10-500 parts of water to carry out ultrasonic dispersion for 10minutes, ultrasonic power:300W; dissolving 100 parts of hydrophobic cationic chitosan into water to prepare a solution with the concentration of 20-50%, raising the temperature to 40-80 DEG C, introducing N2, adding 0.01-1.5 parts of initiating agent and uniformly stirring; then, dropwise adding 10-50 parts of montmorillonite dispersing solution and reacting for 3-6hours; and cooling the product to the room temperature, cleaning by using an acetone precipitation, and carrying out vacuum drying at 40 DEG C for 6hours to obtain the novel chitosan-based sludge dewatering flocculant.

Description

A kind of novel chitosan base Sludge Dewatering Flocculant and preparation method thereof
Technical field
The preparation method who the present invention relates to a kind of chitosan-based Sludge Dewatering Flocculant, belongs to macromolecule material preparation area.
Background technology
Chitosan is chitin deacetylase product, natural, nontoxic, by D-1, and the 4-glycosidic link straight chain superpolymer that is formed by connecting, relative molecular mass is 5 * 10 5~3 * 10 6between, in molecular chain, adjacent six-ring plane has certain angle, and side has methylol, hydroxyl and amido, has determined its good absorption, chelating, crosslinked, bridge formation function, not only to heavy metal ion, there is huge legendary turtle to close adsorption, also electronegative molecule in planar water effectively.Liu Xiaona, Guizhou Normal University's journal (natural science edition), 2011,29(2), Yi Mou city sewage treatment plant residual mud is object, studied the impact of chitosan flocculant on dewatering performance of sludge, the minimum water ratio that can reach mud while adding concentration and be the chitosan solution 6mL of 6g/L in 100mL excess sludge is 70.42%.Zhang Yintang etc.; Shanghai environmental science; 2002; 21(1) studied the application of chitosan flocculant in active sludge conditioning; and compare with polyacrylamide (PAM) flocculation agent and polymerize aluminum chloride (PAC), when chitosan throwing amount (dewatered sludge mass percent) is at 0.8-1.2%, pH value has good conditioning effect when 5-8; substantially suitable with PAM effect, be better than PAC.Chitose-acrylic amide graft copolymerization flocculant is prepared in Chinese invention patent 200810069906.3 researchs of Zheng Huaili, is 94.9%, and is suitable for sludge dewatering to the turbidity removal rate of simulated wastewater.For improving chitosan electric density, impelling the cohesion of mud elimination of colloid stability; Dong Yihua etc.; environmental protection science; 2006; 32(5) by acrylamide, dimethyl diallyl ammonium chloride and chitosan generation graft copolymerization; synthesized the cationic modified polymeric flocculant of chitosan, sludge treatment test shows that its treatment effect is better than PAM, can significantly improve sedimentation and the dewatering of mud.As can be seen here, chitosan and derivative thereof have good application prospect for active sludge conditioning.But it is little in actual applications, because chitosan molecule amount is lower, to build bridge, roll up the effect of sweeping, and consumption is large, thereby has a strong impact on its flocculating effect.
Summary of the invention
The object of this invention is to provide a kind of novel chitosan base Sludge Dewatering Flocculant and preparation method thereof, be characterized in introducing the flexible long branched chain structure of positively charged ion in chitosan molecule, by it, form physics entanglement network structure and make up the defect that chitosan molecule amount is lower, better bring into play surface charge neutralization and bridging and netting effect; Simultaneously that clay absorbent and the cationic chitosan with strong adsorptive power and ion-exchange capacity is compound, employing has the surfactant modified polynite of the cationoid reaction type surface of chain alkyl, strengthen the interface interaction of itself and chitosan molecule and the absorption of dirt in mud, volume are swept to effect, realizing the dehydration of mud efficient flocculating.
Object of the present invention is realized by following technical measures, and wherein said raw material mark, except specified otherwise, is parts by weight.Chitosan-based Sludge Dewatering Flocculant prepare formula constituent be by weight:
Figure GDA0000429388570000021
Wherein, initiator is any in ceric ammonium nitrate, ammonium persulphate, Potassium Persulphate, sodium bisulfite;
2,3-epoxypropyl dimethyl chain alkyl ammonium chloride molecular formula is:
Figure GDA0000429388570000022
n=7~15;
Acrylyl oxy-ethyl dimethyl chain alkyl brometo de amonio molecular formula is:
Figure GDA0000429388570000023
m=7~15。
The preparation of dewatering cationic chitosan:
In there-necked flask, add 2-10 part chitosan, 20-100 part Virahol, 10-80 part distilled water, be warming up to 35 ℃, swelling 30 minutes; Then be warming up to 60-80 ℃, slowly adding concentration is 2 of 20-50%, 3-epoxypropyl dimethyl chain alkyl aqueous ammonium chloride solution 4-40 part, reaction 6h; Product washing with acetone, in 50 ℃ of vacuum-dryings, obtains light yellow solid product;
The preparation of modified montmorillonoid:
1-5 part sodium-based montmorillonite (Na-MMT) is dispersed in the ethanol/water mixed solution that 100-500 part, volume ratio are 1/1, in 60 ℃, stir 1 hour, then add 0.1-16 part acrylyl oxy-ethyl dimethyl chain alkyl brometo de amonio, continue to stir 3 hours, product is in 60 ℃ of vacuum-dryings;
The preparation of novel chitosan base Sludge Dewatering Flocculant:
5~300 parts of modified montmorillonoids are scattered in 10-500 part water and carry out ultrasonic dispersion 10min, and ultrasonic power is 300W; By 100 parts of water-soluble solution that are mixed with 20-50% concentration of dewatering cationic chitosan, be warming up to 40~80 ℃, logical N 2, add 0.01~1.5 part of initiator, stir; Drip subsequently polynite dispersion soln 10-500 part, react 3~6h; Product is cooled to room temperature, with acetone precipitation washing, in 40 ℃ of vacuum-drying 6h, obtains novel chitosan base Sludge Dewatering Flocculant.
Novel chitosan base Sludge Dewatering Flocculant performance:
Novel chitosan base Sludge Dewatering Flocculant prepared by employing the present invention is for sludge dewatering, and when its consumption is 0.1g/L, resistivity is 5.15 * 10 10cm/g, filter cake moisture content is 83.32%, and supernatant fluid turbidity is 5.3NTU, and the dewatering performance of sludge of more unmodified chitosan is significantly improved.
Tool of the present invention has the following advantages
The present invention calls at a kind of novel chitosan base Sludge Dewatering Flocculant of preparation, has following features:
(1) in chitosan molecule, introduce the flexible long branched chain structure of positively charged ion, by it, form physics entanglement network structure and make up the defect that chitosan molecule amount is lower, to negative charge mud can better bring into play surface charge neutralization and bridging and netting effect;
(2) montmorillonite adsorbent and the cationic chitosan with strong adsorptive power and ion-exchange capacity is compound, employing has the surfactant modified surface of clay of cationoid reaction type of chain alkyl, surfactant molecule is grafted in chitosan molecule, strengthen the interface interaction of clay and chitosan molecule; Its positively charged ion backbone of while also can strengthen it absorption of dirt, volume are swept to effect, thereby realizes the dehydration of mud efficient flocculating.
Embodiment
Below by embodiment, the present invention is specifically described; be necessary to be pointed out that at this present embodiment is only used to further illustrate the present invention; can not be interpreted as limiting the scope of the invention, the person skilled in the art in this field can make some nonessential improvement and adjustment to the present invention according to the content of the invention described above.
Embodiment 1
In there-necked flask, add 110g chitosan, 1250mL Virahol, 1250mL distilled water, be warming up to 35 ℃, swelling 30 minutes; Then be warming up to 60 ℃, slowly add concentration be 30% 2,3-epoxypropyl dimethyl-octa alkyl ammonium chloride aqueous solution 800mL, reaction 6h; Product washing with acetone, in 50 ℃ of vacuum-dryings, obtains light yellow solid product;
20g sodium-based montmorillonite (Na-MMT) is dispersed in the ethanol/water mixed solution that 1000mL, volume ratio are 1/1, in 60 ℃, stir 1 hour, then add 3g acrylyl oxy-ethyl dimethyl dodecyl bromination ammonium, continue to stir 3 hours, product is in 60 ℃ of vacuum-dryings;
10g modified montmorillonoid is scattered in 180mL water and carries out ultrasonic dispersion 10min, and ultrasonic power is 300W; By the water-soluble solution that is mixed with 25% concentration of 100g dewatering cationic chitosan, be warming up to 50 ℃, logical N 2, add initiator 0.06g, stir; Drip subsequently polynite dispersion soln 160mL, reaction 6h; Product is cooled to room temperature, with acetone precipitation washing, in 40 ℃ of vacuum-drying 6h, obtains novel chitosan base Sludge Dewatering Flocculant.
Embodiment 2
In there-necked flask, add 400g chitosan, 4000mL Virahol, 3000mL distilled water, be warming up to 35 ℃, swelling 30 minutes; Then be warming up to 70 ℃, slowly add concentration be 40% 2,3-epoxypropyl dimethyl lauryl ammonium chloride aqueous solution 3500mL, reaction 6h; Product washing with acetone, in 50 ℃ of vacuum-dryings, obtains light yellow solid product;
45g sodium-based montmorillonite (Na-MMT) is dispersed in the ethanol/water mixed solution that 3500mL, volume ratio are 1/1, stirs 1 hour in 60 ℃, then add 8g acrylyl oxy-ethyl dimethyl-octa alkyl brometo de amonio, continue to stir 3 hours, product is in 60 ℃ of vacuum-dryings;
20g modified montmorillonoid is scattered in 400mL water and carries out ultrasonic dispersion 10min, and ultrasonic power is 300W; By the water-soluble solution that is mixed with 40% concentration of 100g dewatering cationic chitosan, be warming up to 70 ℃, logical N 2, add initiator 0.09g, stir; Drip subsequently polynite dispersion soln 300mL, reaction 5h; Product is cooled to room temperature, with acetone precipitation washing, in 40 ℃ of vacuum-drying 6h, obtains novel chitosan base Sludge Dewatering Flocculant.
Embodiment 3
In there-necked flask, add 500g chitosan, 5000mL Virahol, 6000mL distilled water, be warming up to 35 ℃, swelling 30 minutes; Then be warming up to 80 ℃, slowly add concentration be 50% 2,3-epoxypropyl dimethyl cetyl chloride aqueous ammonium 4000mL, reaction 6h; Product washing with acetone, in 50 ℃ of vacuum-dryings, obtains light yellow solid product;
65g sodium-based montmorillonite (Na-MMT) is dispersed in the ethanol/water mixed solution that 5000mL, volume ratio are 1/1, in 60 ℃, stir 1 hour, then add 16g acrylyl oxy-ethyl dimethyl hexadecyl brometo de amonio, continue to stir 3 hours, product is in 60 ℃ of vacuum-dryings;
40g modified montmorillonoid is scattered in 500mL water and carries out ultrasonic dispersion 10min, and ultrasonic power is 300W; By the water-soluble solution that is mixed with 50% concentration of 100g dewatering cationic chitosan, be warming up to 80 ℃, logical N 2, add initiator 1.2g, stir; Drip subsequently polynite dispersion soln 450mL, reaction 4h; Product is cooled to room temperature, with acetone precipitation washing, in 40 ℃ of vacuum-drying 6h, obtains novel chitosan base Sludge Dewatering Flocculant.

Claims (2)

1. a novel chitosan base Sludge Dewatering Flocculant, is characterized in that the raw material of this chitosan-based Sludge Dewatering Flocculant is composed of the following components, is by weight:
Formula constituent prepared by flocculation agent is by weight:
Figure FDA0000429388560000011
Wherein, initiator is any in ceric ammonium nitrate, ammonium persulphate, Potassium Persulphate, sodium bisulfite;
2,3-epoxypropyl dimethyl chain alkyl ammonium chloride molecular formula is:
Figure FDA0000429388560000012
n=7~15;
Acrylyl oxy-ethyl dimethyl chain alkyl brometo de amonio molecular formula is:
Figure FDA0000429388560000013
m=7~15。
2. the preparation method of novel chitosan base Sludge Dewatering Flocculant as claimed in claim 1, is characterized in that the method comprises the following steps:
The preparation of dewatering cationic chitosan:
In there-necked flask, add 2-10 part chitosan, 20-100 part Virahol, 10-80 part distilled water, be warming up to 35 ℃, swelling 30 minutes; Then be warming up to 60-80 ℃, slowly adding concentration is 2 of 20-50%, 3-epoxypropyl dimethyl chain alkyl aqueous ammonium chloride solution 4-40 part, and reaction 6h, product washing with acetone, in 50 ℃ of vacuum-dryings, obtains light yellow solid product;
The preparation of modified montmorillonoid:
1-5 part sodium-based montmorillonite (Na-MMT) is dispersed in the ethanol/water mixed solution that 100-500 part, volume ratio are 1/1, in 60 ℃, stir 1 hour, then add 0.1-16 part acrylyl oxy-ethyl dimethyl chain alkyl brometo de amonio, continue to stir 3 hours, product is in 60 ℃ of vacuum-dryings;
The preparation of novel chitosan base Sludge Dewatering Flocculant:
5~300 parts of modified montmorillonoids are scattered in 10-500 part water and carry out ultrasonic dispersion 10min, and ultrasonic power is 300W; By 100 parts of water-soluble solution that are mixed with 20-50% concentration of dewatering cationic chitosan, be warming up to 40~80 ℃, logical N 2, add 0.01~1.5 part of initiator, stir; Drip subsequently polynite dispersion soln 10-500 part, react 3~6h; Product is cooled to room temperature, with acetone precipitation washing, in 40 ℃ of vacuum-drying 6h, obtains novel chitosan base Sludge Dewatering Flocculant.
CN201310140816.XA 2013-04-23 2013-04-23 Novel chitosan-based sludge dewatering flocculant and preparation method thereof Expired - Fee Related CN103172251B (en)

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CN104310556B (en) * 2014-11-16 2015-09-16 张亦彬 A kind of preparation method and application of multi-effect flocculant
CN104310570B (en) * 2014-11-16 2015-09-30 宏飞集团有限公司 A kind of preparation method of oxidizing, flocculating composite water disposal agent and application thereof
CN104803569A (en) * 2015-04-01 2015-07-29 遵义师范学院 Method for treating sludge through coupling of electrochemistry and flocculant
CN109111080A (en) * 2018-08-01 2019-01-01 华南理工大学 A kind of cation montmorillonite type sludge dehydrating agent and its preparation method and application
CN108996885A (en) * 2018-08-27 2018-12-14 华南理工大学 A kind of montmorillonite type oxidized sludge dehydrating agent and its preparation method and application
CN114516681A (en) * 2022-01-21 2022-05-20 丁金萍 Composite flocculant for industrial wastewater treatment and preparation method thereof
CN114849657B (en) * 2022-04-27 2023-09-29 南昌市国昌环保科技有限公司 Preparation of a high-efficiency amphiphilic chitosan-loaded bentonite adsorbent and its application in coking wastewater
CN114805688A (en) * 2022-05-25 2022-07-29 重庆交通大学 A kind of modified flocculant and its preparation method and application

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