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ASPECT CONSULTING <br />20 FINAL PROJECT NO. AS190583A-08  MAY 21, 2025 <br /> I = tidally averaged horizontal gradient (feet/foot); and <br /> ne = effective porosity (dimensionless). <br />A groundwater seepage velocity is calculated for fill unit within each Unit, and for the Log <br />Pond fill and sawdust layer, using the average K value and hydraulic gradient for the Unit, <br />as presented in Table 2-4. A Darcy velocity (also known as specific discharge), for use in <br />volumetric flux calculations, is also calculated for each Unit by not including effective <br />porosity in the equation. The average K values by Unit were derived as described above <br />and are presented in Tables 2-2 and 2-3. An average hydraulic gradient along the shoreline <br />of each Unit was calculated based on the tidally averaged (net) groundwater elevation <br />contours presented on Figure 2-9. To calculate an average gradient for each Unit, the <br />horizontal distance between the tidally averaged groundwater elevation contour located <br />closest to the shoreline and the next groundwater elevation contour inland was calculated <br />at 25-foot increments along the higher groundwater elevation contour. The gradient for <br />each point was then calculated as the 1-foot elevation difference divided by the horizontal <br />distance, and the average of the 25-foot point measurements within each Unit is applied as <br />the average gradient for the Unit. The nearshore gradient within the Log Pond fill was <br />calculated as the average of the tidally averaged groundwater elevations for wells <br />REC6-MW-2 and MW-6 as depicted on Figure 2-9. The nearshore gradient for the Log <br />Pond sawdust layer was calculated the difference between shoreline well LP-MW-7 <br />groundwater elevation and the average tide elevation for a 2-day period in which the <br />groundwater measurement was collected, averaged for the July and September 2017 <br />groundwater measurements. Table 2-4 presents the tidally averaged hydraulic gradient for <br />the fill unit in each Unit and for the Log Pond hydrostratigraphic units. <br />Applying the Unit-specific average K and gradient estimates, and an assumed site-wide <br />effective porosity of 0.2 based on literature values, the Upland Area groundwater seepage <br />velocities in the fill unit outside of the Log Pond are estimated to range from 3 feet/year in <br />Unit E to 100 feet/year in Unit B, with the variation due primarily to the K difference. The <br />corresponding Darcy velocity estimates range from 1 cubic feet/square foot per year <br />(ft3/ft2-year) in Unit E to 20 ft3/ft2-year in Unit B. Within the former Log Pond, the <br />estimated groundwater seepage velocities in the lower-permeability Log Pond fill and <br />sawdust unit are 0.8 and 5 feet/year (Darcy velocities of 0.2 and 0.9 ft3/ft2-year, <br />respectively) (Table 2-4). <br />2.4.4.2.5 Estimates of Groundwater Flux to East Waterway <br />The volumetric flux of groundwater (cubic feet per year [ft3/year]) from the fill aquifer to <br />the East Waterway is also estimated for each Unit. To do so, the Unit-specific cross <br />sectional area for flow perpendicular to the groundwater flow direction is estimated as the <br />shoreline length multiplied by the aquifer thickness along the shoreline (thickness <br />estimated as described above). The volumetric groundwater flux from each Unit is then <br />calculated by multiplying the respective Darcy velocity by the shoreline cross sectional <br />area. <br />The estimated groundwater fluxes from the fill unit (excluding the Log Pond) to the East <br />Waterway range from 10,000 ft3/year in Unit E to 420,000 ft3/year in Unit B. Within the <br />Log Pond, the estimated groundwater fluxes from the Log Pond fill and sawdust unit are