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Explore metal concentration, speciation, soil conditions, and more factors affecting arsenic and lead mobility in soil near smelters and orchards.
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MTCA Science Advisory Board Presentation Establishing Moderate Soil Levels for Arsenic October 23, 2006
Arsenic and Lead Mobility • Metal concentration • Metal speciation • Soil redox and pH conditions • Precipitation • Soil composition and permeability • Other (i.e., application of phosphate fertilizers)
Soil Profiles Near the Tacoma Smelter Lead Arsenic
Groundwater Data • No Specific combined GW/Soil study • However on Vashon – lots of soil data and lots of GW Data • 22 Group A systems • 137 Group B systems • 50 to 75 % of Group A and B systems receive water from 25 ft or less • DOH and King County Databases
Equilibrium Partitioning Model Where: Cs = Soil Concentration (mg/kg) Cw = Groundwater concentration or cleanup level (μg/L) USF = Unit conversion factor (1 mg/1,000 μg) DF = Dilution factor (dimensionless: 20 for unsaturated zone soil) Kd = Distribution coefficient (L/kg) θw = Water-filled soil porosity (mL water/mL soil: 0.3 for unsaturated soil) Pb = Dry soil bulk density (1.5 kg/L)
Kd - Distribution Coefficient Container Soil (mg/kg) Kd = = L/kg Water (mg/L) Water (mg/L) Soil (mg/kg)
Kd - Arsenic Examples of Kd values reported in literature reviews
Kd - Lead Examples of Kd values reported in literature reviews
Equilibrium Partitioning Model Arsenic (CS =25 mg/kg) CW (Kd of 29, MTCA) = 43 μg/L CW(Kdof 2512, EPA median) = 0.50 μg/L CW(Kdof 1585, EPA mean) = 0.79 μg/L CW(Kd of 1825, Sauve median) = 0.68 μg/L CW(Kd of 13119, Sauve mean) = 0.10 μg/L
Equilibrium Partitioning Model Arsenic (CS = 251 mg/kg) CW (Kd of 2,510) = 5 μg/L