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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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5.3.1 Case Study 1: Fairbanks, Alaska <strong>and</strong> Eugene, OregonThe EPA <strong>Drinking</strong> <strong>Water</strong> Research Division (DWRD) conducted field POU studies inFairbanks, Alaska <strong>and</strong> Eugene, Oregon (Fox <strong>and</strong> Sorg, 1987; Fox, 1989). Pilot systems were installedin two homes in each community, <strong>and</strong> each system consisted <strong>of</strong> an activated alumina bed, ion exchangebed <strong>and</strong> reverse osmosis system. Influent arsenic concentrations ranged from 0.05 to 1.16 mg/L <strong>and</strong>was believed to be naturally occurring.The RO systems at each <strong>of</strong> the four locations per<strong>for</strong>med well on start-up, achieving 60 to 80percent removal <strong>of</strong> arsenic. Over time, however, the arsenic removal efficiency decreased to 50percent or less. At the initial removal efficiencies, effluent arsenic levels met the current MCL <strong>of</strong> 50ppb, but over time failed to sufficiently reduce the levels to below the MCL.Low-pressure RO units (40 - 60 psig) consistently achieved greater than 50 percent removal,but with high influent arsenic concentrations, much higher removal efficiency is necessary to achievethe MCL. The high-pressure unit (196 psig) operated <strong>for</strong> 350 days <strong>and</strong> produced 684 gallons <strong>of</strong>treated water which met the MCL.The IX beds evaluated were 1 cubic foot in size <strong>and</strong> were filled with a strong base anionexchange resin (Dowex-SBR). The IX beds effectively reduced arsenic levels to below the MCL,but required pre-treatment to ensure effective removal. This involved regeneration <strong>and</strong> chemicaltreatment <strong>of</strong> the resin to the chlorine <strong>for</strong>m.The AA beds were identical to the IX beds with the exception that they were filled withgranular activated alumina (Alcoa-F1) rather than resin. Over the course <strong>of</strong> this study, the AA bedseffectively reduced arsenic levels; however, the media required pre-treatment to reduce the pH <strong>of</strong> theAA to 5.5 - 6.0 (the pH at which AA most effectively removes arsenic). Pre-treatment <strong>of</strong> the AA bedinvolved passing a sodium hydroxide solution through the tank, rinsing with clean water, <strong>and</strong> thentreating with dilute sulfuric acid. Improperly treated alumina per<strong>for</strong>med poorly initially (30 to 40percent removal), <strong>and</strong> per<strong>for</strong>mance significantly deteriorated over time (5 to 20 percent removal).Proper pre-treatment, however, allowed <strong>for</strong> efficient operation periods <strong>of</strong> longer than one year.5.3.2 Case Study 2: San Ysidro, New MexicoA field study was also conducted in San Ysidro, NM to evaluate the effectiveness <strong>of</strong> POU ROunits. This work is documented in several sources (Thomson <strong>and</strong> O’Grady, 1998; Fox, 1989; Fox <strong>and</strong>Sorg, 1987; <strong>and</strong> Clif<strong>for</strong>d <strong>and</strong> Lin, 1985). San Ysidro source water is from an infiltration gallery underthe local river banks <strong>and</strong> contains 5.2 mg/L fluoride <strong>and</strong> 0.23 mg/L arsenic. The water is also highin other inorganic contaminants, including iron (2.5 mg/L), manganese (0.6 mg/L) <strong>and</strong> total dissolved5-5

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