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    Home > Chemicals Industry > Chemical Technology > Amphoteric polymer flocculant CGAAC

    Amphoteric polymer flocculant CGAAC

    • Last Update: 2021-11-03
    • Source: Internet
    • Author: User
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    Amphoteric polymer flocculant CGAAC

    [Preparation]

    ① Carboxymethylation reaction Weigh a quantitative amount of F691 powder, add a certain volume of solvent to disperse it evenly, then add quantitative lye to alkalize for 30 minutes, then add quantitative chloroacetic acid , and etherify at 50°C to obtain carboxymethylation Product
    .

    ② Grafting copolymerization: Add carboxymethylated product and deionized water into a four-necked flask, pass nitrogen and heat to a predetermined temperature, add initiator and acrylamide monomer under stirring, and cool after reacting for a certain period of time to obtain the product CGAA
    .

    ③Mannich reaction dissolves a certain concentration of graft copolymer in deionized water, then adds calculated amount of formaldehyde and dimethylamine , reacts at 30~70℃, and after cooling, the product is neutralized to pH=6~7 to obtain amphoteric Macromolecular flocculant CGAAC
    .

    [Application] (1) Application in natural source water treatment

    Take the natural source water of a river in the south, which contains 1.
    75mg/L of humic acid and 0.
    2% of kaolin
    .


    Take the upper suspension, the raw water turbidity measured is 230NTU, pH=6.


    Table 3-88 CGAC and CG-A combined with PAC to remove natural source water turbidity experimental results

    It can be seen from the test data in Table 3-88 that because the source water contains a small amount of humic acid, a small amount of CGAC with a suitable amount of PAC can achieve a turbidity removal rate of 99.


    6%, and the turbidity removal effect is better than pure turbidity water without humic acid.


    (2) Study on the flocculation and dewatering performance of sludge

    Wang Jie et al.
    used CGAAC, a modified product of amphoteric F691 powder, to treat activated sludge, and compared the flocculation performance with cationic polyacrylamide (PAM-C).
    The results are shown in Figure 3-33
    .


    It can be seen from Figure 3-33 that the ability of CGAAC to convert the attached water on the sludge surface into free water is significantly greater than that of PAM-C, so the sedimentation speed of the sludge is faster, especially after the sedimentation for 30 minutes, the effect is more obvious



     

     

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