No description available.

Contaminants in aqueous environments exist in phases that are sorbed to suspended or colloidal material and that are dissolved in solution. Polymer flocculants can be used to remove suspended or colloidal material along with sorbed contaminants, but they remove little of the dissolved contaminants. In the study presented here, development of polymers to sorb contaminants from aqueous solution during the flocculation process was investigated. Atrazine and phosphate (H₂PO₄ ̄) were chosen as test contaminants. For a given test contaminant, multiple copies of a functional group that interacted with that contaminant were inserted into the polymer backbone of a polyacrylamide flocculant. The functional groups inserted into the polymer structure acted as a trap for the dissolved contaminant. The traps were a cyclic secondary amine that interacted with atrazine, and a thiourea that interacted with phosphate. Modified flocculants with different configurations and densities of trapping groups were made and evaluated for removal of the test contaminants from aqueous suspensions. The suspensions consisted of bentonite or kaolinite in water with a known concentration of a test contaminant. The atrazine source was labeled with ¹⁴C and concentrations were measured using a scintillation counter. The source of phosphate used was NaH₂PO₄ and ion chromatography was used to measure the aqueous concentrations of phosphate. In general, the modified polymer flocculants containing trapping groups removed significantly more atrazine and phosphate from suspension compared to the control polymer flocculants ([alpha] =0.05). While the amount of modified polymers needed to achieve significant removal of the test contaminant were higher than the Environmental Protection Agency limit for concentration of polyacrylamide flocculants in water, it was possible to enhance the polymers sorbtion and removal of contaminants from solution during the flocculation process.

No description available.

Polymer flocculants, traditionally used with primary coagulant to enhance flocculation and sedimentation, are used in the coagulation-/microfiltration process as well assuming they can improve membrane performance similarly. However, there are several uncertainties concerning the use of polymer flocculants in the coagulation-microfiltration process. First, polymer flocculants may not have measurable effect on turbidity removal, because microfiltration membranes can remove significantly smaller particles than those removed by the conventional treatment process. Second, the effect of using polymer flocculants on NOM removal has been controversial. Although a number of studies reported improved NOM removal when polymers were used, others reported no or negative impact of polymers on NOM removal. Third, polymer flocculants are high molecular weight organic compounds. When carried over to membrane residual polymers can potentially foul the membranes. Finally, the use of polymer flocculants will change floc properties (i.e. size, fractal dimension, and stickiness) and subsequently bring uncertain effect on cake layer resistance. Therefore, the role of polymer flocculants in coagulation-microfiltration system needs to be carefully assessed for system optimization. In the reported research, three types of polymer flocculants with different charge and molecular weights were tested for comprehensively evaluating the impact of polymer flocculants on the performance of coagulation-microfiltration of surface water. Operation conditions such as inline filtration, direct filtration, and filtration with sedimentation were included. Two membrane reactors were designed to study the mechanism through which polymer flocculants affect the performance of coagulation-microfiltration systems. The result demonstrated that the use of polymer flocculants provides little to no benefit to turbidity and NOM removal in most cases, but pDADMACs can enhance NOM removal if applied properly; All polymer flocculants significantly increased membrane fouling except for pDADMACs when sedimentation proceeds MF; Polymer flocculants increase deposition/attachment of floc particles on the membrane surface through both adsorption of residual polymer on the membrane surface and polymer molecules on the floc particle surface; Even though polymers form larger and more fractal floc particles, they did not have notable impact on cake layer structure.