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P <br /> Only Tests. The pH increased by approximately 1 pH unit in both of the H2O2 Only tests. <br /> ORP and sulfate were not significantly affected. <br /> Treatments employing acid with or without iron (Tests 4 and 5 and Tests 8 and 9) <br /> increased the concentrations of Cr(VI) and sulfate and affected the concentrations of <br /> several metals. The concentrations of vanadium, magnesium, calcium, chromium, iron, <br /> manganese, cobalt, and nickel increased, often by an order of magnitude . The <br /> concentration of barium decreased, presumably due to precipitation of barium sulfate (the <br /> acid used in these tests was sulfuric acid). The concentration of sulfate increased to <br /> 4,0004,400 mg/L due to the acid. Addition of acid did not result in a permanent <br /> decrease in pH in the H202 /Acid tests (Tests 4 and 5), which were sampled after 48 <br /> hours, due to the high buffering capacit� of the soil (see Section 3 .5). A small decrease <br /> in pH was observed in the 5 % H2O2/Fe +/Acid test, which was sampled after 24 hrs. The <br /> 2% H202/Fe2+/Acid tests showed a significant drop in pH, but was due to poor mixing in <br /> this reactor (the stir bar became embedded in the soil while the reaction was running <br /> overnight.) <br /> In tests using chelated iron (Tests 6 and 7) the concentrations of chromium, iron, cobalt, <br /> nickel and copper increased. In most cases, the increase was at least an order of <br /> magnitude. The increase was presumably due to chelation of metals form the soil phase. <br /> The pH increased by about 0.5 pH units, which was less than when H202 Only was used. <br /> The concentration of sulfate increased to 27-30 mg/L . <br /> The concentration of arsenic was not affected by treatment with either H202 Only or <br /> H2O2/Acid. However, arsenic was completely removed to below the reporting limit of < <br /> 0 .005 mg/L when either chelated iron or acidified iron was used. <br /> 3.4 Off-Gas Formation/Longevity of H2O2 <br /> The rate at which off-gases were generated for each of the oxidant systems are shown in <br /> Figure 1 . H2O2 decomposition was rapid in these tests—in most cases, 75-99% of the <br /> off-gases were generated within 60 minutes. <br /> 3.5 Buffering Curves <br /> The change in soil pH after addition of acid is shown in Figure 2 . Addition of up to 100 <br /> mmol H+/kg soil (50 mL of pH 1 acid to 50 g soil) initially decreased the pH to 5 . 1 , but <br /> the pH attenuated to 7.3 within 7 days. Thus, the soil can easily buffer any added acid. <br /> However, the amount of acid needed to maintain low pH for an extended length of time <br /> would be significant. <br /> PRIMA Environmental, Inc. 15 Eval of Peroxide <br /> February 8, 2007 Cambria—G Street, Davis <br />