Laserfiche WebLink
I <br />' 130 gallons per day per foot (gpd/ft) The hydraulic conductivity (K) was calculated by <br /> dividing the Ts by the aquifer thickness of 17 feet in the extraction well EX-1, where the <br /> aquifer thickness equals the thickness of the water column present in the well The <br />' calculated K ranged from 0 0057 to 0 00036 centimeters per second These hydraulic <br /> conductivities are representative of clayey sands, till, silty sands, fine sands and well sorted <br /> sands and are fairly consistent with the lithology described in the saturated zone on the <br /> boring logs (Attachment C) A summary of hydraulic properties determined during the <br />' pumping test is presented on Table 6 AQTESOLV output files are provided in Appendix H <br /> A theoretical capture zone was calculated for the extraction well EX-1 using the <br />' transmissivity calculated during the step-drawdown and constant-discharge pumping tests <br /> The capture zone is defined by the groundwater streamlines dividing the region producing <br /> inflow from the region that does not produce inflow to the extraction well The capture zone <br /> 1 is defined by three distances 1)"a" which is parallel to groundwater flow and downgradient <br /> of the pumping well (a = Q/2TrTi) where Q equals the pumping rate, T equals the <br /> transmissivity and i equals the groundwater gradient, 2) "b" which is perpendicular to <br /> groundwater flow from the pumping well to the streamline boundary (b = Q/4Ti), and 3) "c" <br /> 1 which is the half-width (radius) of the capture zone upgradient of the pumping well where <br /> streamlines are parallel to the groundwater flow direction (Javandel and Tsang 1986) Using <br /> the mean of transmissivity of 130 gallons per day per foot (gpolft), the hydraulic gradient of <br /> 1 0 005 and discharge rate of 0 8 gpm, the capture zone dimensions are 280 feet-in the "a" <br /> direction and 440 feet in the "b" direction <br /> The average capture zone for the aquifer was also approximated using the FLOWPATH <br /> model to simulate groundwater flow conditions at the site The model incorporated known <br /> hydraulic parameters and groundwater elevation data for the aquifer Groundwater <br /> 1 extraction at 0 8 gpm from the aquifer was modeled at well EX-1 and the resulting capture <br /> zone for that well is defined The results indicate a similar capture zone to that calculated by <br /> the Javandel and Tsang (1986) method <br /> 1 Groundwater Sample Collection <br /> Grab groundwater samples were collected from well EX-1 before and after the steady-state <br /> pumping test on August 12 and August 13, 2004 The groundwater samples were submitted <br /> 1 to Kiff Analytical for analysis of TPHg, BTEX, MtBE, TBA, DIPE, EtBE, and TAME by EPA <br /> Method 82608 <br /> 1 Laboratory Analytical Results <br /> Laboratory analyses of water samples collected before and after the steady-state pumping <br /> test are presented in Table 3 TPHg, BTEX, DIPE, ETBE, and TBA were not detected in <br /> 1 either water sample at concentrations above laboratory limits MTBE concentration <br /> decreased from 7,400 pg/L before the test to 5,400 pg/L after the test TAME also <br /> decreased from 22 pg/L before the test to 10 pg/L after the test Certified laboratory <br /> 1 analytical data and chain-of-custody documentation are included in Appendix F <br /> 1 <br /> i <br /> 1 <br /> 32262 Assessment&Feasibility Report&SCM doc 12 September 30 2004 <br />' 77EL 32262 04 0502 <br />