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Technologies and Costs for Removal of Arsenic From Drinking Water

Technologies and Costs for Removal of Arsenic From Drinking Water

Technologies and Costs for Removal of Arsenic From Drinking Water

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4.l.2 Methods <strong>for</strong> Estimating Residuals H<strong>and</strong>ling <strong>and</strong> Disposal <strong>Costs</strong>Residuals h<strong>and</strong>ling <strong>and</strong> disposal costs can be difficult to estimate. There are a number <strong>of</strong>factors which affect capital <strong>and</strong> O&M costs, <strong>and</strong> disposal costs can be largely regional. EPA haspublished two manuals <strong>for</strong> estimating residuals h<strong>and</strong>ling <strong>and</strong> disposal costs; Small <strong>Water</strong> SystemByproducts Treatment <strong>and</strong> Disposal Cost Document (DPRA, 1993a), <strong>and</strong> <strong>Water</strong> System ByproductsTreatment <strong>and</strong> Disposal Cost Document (DPRA, 1993b). Both present a variety <strong>of</strong> h<strong>and</strong>ling <strong>and</strong>disposal options, applications <strong>and</strong> limitations <strong>of</strong> those technologies, <strong>and</strong> capital <strong>and</strong> O&M costequations.4.2 RESIDUALS HANDLING OPTIONS4.2.1 Gravity ThickeningGravity thickening increases the solids content <strong>of</strong> filter backwash, sedimentation basins, <strong>and</strong>treatment process sludges. It is generally used as a first step in residuals processing, precedingmechanical dewatering processes, evaporation ponds, <strong>and</strong>/or storage lagoons.Filter backwash streams are high volume, low solids slurries generated during the cleaning<strong>of</strong> granular filter media. Backwash volume depends on the number <strong>of</strong> filters used by a system <strong>and</strong> thefrequency with which they are cleaned. Typical backwash volumes range from 0.5 to 5 percent <strong>of</strong> theprocessed water flow with larger plants creating less backwash per million gallons produced thansmall systems due to increased plant efficiency (DPRA, 1993a). Backwash waters have an averagesolids concentration <strong>of</strong> 0.8 percent, compared to coagulation sludges which are typically characterizedby an average solids concentration <strong>of</strong> 0.5 to 2.0 percent (DPRA, 1993a).When possible, backwash waters are recycled within the treatment process. In gravitythickening, backwash waters are fed to a tank where settling occurs naturally. The sludges resultingfrom gravity thickening are discharged <strong>and</strong> further treated <strong>for</strong> ultimate disposal, <strong>and</strong> the decant iseither recycled or discharged to a surface water or to a publicly-owned treatment works (POTW).Gravity thickening reduces the quantity <strong>of</strong> water sent to waste due to backwashing, as well as the totalquantity <strong>of</strong> sludge generated (DPRA, 1993a). When recycling is not feasible, backwash waters maybe discharged to a surface water or a POTW, or may be treated by other mechanical or non-4-2

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