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v <br /> A s s O C I A T E S I N C <br /> presented in Table 3-3 Refer to PRIMA'S Evaluation of Reductanis for the In Sitar Stabilization <br /> of Hexavalent Chromium included in Appendix B for detailed information <br /> Table 3-3 <br /> Summary of Baseline Groundwater Sample Analytical Results <br />' Analyte Units Sample ID <br /> MWA MW-2 MW-3 MW4 MW-5 MW-6 I MW-7 MW-8 MW-9 <br /> Chromium, Total ug/L 83 36 6,300 43 110 150 190 86 23 <br />' Manganese, Total ug/L 750 21 < 10 270 800 880 1,400 490 61 <br /> Manganese, Dissolved ug/L 780 < 5 < 5 76 < 5 < 5 < 5 < 5 < 5 <br /> Copper ug/L < 10 < 10 < 10 19 59 70 120 52 < 10 <br /> Zinc ug/L < 100 < 100 < 100 < 100 110 120 200 < 100 < 100 <br /> Arsenic ug/L < 5 < 5 < 5 7 15 16 19 13 98 <br /> Iron, Total ug/L 950 1,500 2,600 14,000 47,000 54,000 97,000 42,000 2,300 <br />' Iron, Dissolved ug/L 790 810 2,400 360 700 760 520 600 410 <br /> Alkalinity mg/L 680 630 250 390 280 270 440 360 270 <br />' CaCO3 <br /> Ammonia mg/L N 017 < 0 10 < 0 10 < 010 0 12 < 010 < 010 < 010 < 010 <br /> Nitrate mg/L N 55 97 35 2 2 18 16 42 99 77 <br /> Sulfate mg/L 29 31 38 91 90 74 13 42 26 <br /> TOC mg/L 42 1 1 8 1 3 14 1 1 4 1 1 2 1 14 1 1 3 1 1 <br />' 4.0 SUMMARY OF BENCH SCALE TESTING RESULTS <br /> Detailed methodology and results of the bench scale treatability study for reducing hexavalent <br />' chromium (CrVI) 3n the subsurface are presented in PRIMA's report presented in Appendix B <br /> In summary, bench scale laboratory testing was performed on soil and water collected from the <br />' site to evaluate the effectiveness of two potential reducing agents — ferrous iron solution and <br /> calcium polysulfide (Cascade°) — to chemically 2educe CrVI to divalent chromium (CrIII) <br /> Tests were conducted in the presence and absence of soil to assess the potential for in situ <br />' remediation via infection of solution into the subsurface Both the ferrous iron solution and <br /> Cascade were effective in decreasing the concentration of CrVI in groundwater in the presence <br /> and absence of soil Soil decreased the efficiency of each treatment, but complete removal of <br />' CrVI was achieved with ferrous iron solution and appears to be achievable with Cascade° if a <br /> greater concentration of Cascade" than used in the bench scale study were employed Both the <br /> ferrous iron solution and Cascade° affected secondary water quality parameters Manganese was <br /> affected significantly by both reducing agents resulting in high concentrations of this constituent <br /> The resultant high concentrations of manganese are likely attributable to the reducing agents <br /> reacting with naturally occurring manganese dioxide in the soil <br /> S lenvaronmuit d\625831rLP0Ftslbu1ch test rpt doc 7 <br />