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Water treatment residuals

Drinking water treatment residuals (iron rich) Laboratory solutions 23 2 6.0 0.3 As(lll)... [Pg.366]

As was shown previously in some examples [15-18] in a large ozonation plant for water treatment, residual ozone in the gas exiting the ozonation stages could be sent back to the head of the water plant where it is injected in another compartment to aid flocculation, remove iron and manganese, or reduce the trihalomethane formation potential (see Fig. 8). In these cases, it is not surprising that these plants could also have a final disinfection ozonation step. [Pg.44]

Process for Recovery of Coagulants from Water Treatment Residuals... [Pg.945]

Application of Donnan Membrane Process for Recovery of Coagulants from Water Treatment Residuals which describes the coupled interdiffusion of A and B in terms of one diffusion coefficient ... [Pg.953]

A practical application of this process could be in setting up a counter-current flow of acidified water treatment residual feed against an acid sweep solution through a stack of cation-exchange membranes. The process schematic is shown in Figure 34.4 [35]. [Pg.954]

SenGupta, A.K., Li, P., and Cumbal, L. Selective alum recovery from water treatment residuals. AWWA Research Foundation, Denver, CO, ISBN 0-89867-899-4, 140 pp, 1997. [Pg.978]

The empirical constitutive parameters for five materials with different compactibilities are shown in Table 2. The 9-pm spheres with n = d = 0, and K = Kq = constant correspond to an incompressible material. The Kaolin flat is moderately com-pactible and the Mierlo biosolidsj water treatment residue,activated sludge with n and S... [Pg.2774]

The lEPs obtained in [2969] probably represent metal oxide-dextrin precipitates rather than pure metal oxides. Activated carbons studied in [2970] had very high ash content. Water treatment residual was studied in [2971]. The material studied in [2972] was impure. Other examples of surface charging studies carried out in complex, ill-defined materials can be found in [2722,2834,2973-2978]. [Pg.864]

Butkus, M.A. and Grasso, D., Impact of phosphate sorption on water-treatment residual surface characteristics Prelude to reuse, Environ. Eng. Sci., 16, 117, 1999. [Pg.1045]

Keeley, J., Jarvis, P, Judd, S.J., 2014. Coagulant recovery from water treatment residuals a review of applicable technologies. Crit. Rev. Environ. Sci. Technol. 44 (2014), 2675-2719. [Pg.47]

Lower explosive limit—The lowest concentration of a substance that will produce a fire or fiash when an ignition source is present, expressed as a percent of vapor or gas in the air by volume. Low-level waste—Radioactively contaminated industrial or research waste such as paper, rags, plastic bags, medical waste, and water-treatment residues. [Pg.493]

ComweU, David A., Water Treatment Residuals Engineering, AWWA Research Foundation and American Water Works Association, Denver, CO, 2006. [Pg.152]

Low-level waste Radioactively contaminated industrial or research waste such as paper, rags, plastic bags, medical waste, and water-treatment residues. [Pg.259]


See other pages where Water treatment residuals is mentioned: [Pg.369]    [Pg.377]    [Pg.946]    [Pg.2773]    [Pg.399]    [Pg.538]   


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