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Ms Lori Duncan <br /> Page 2 of 3 <br /> The waste was stored on site in accordance with 49 CFR part 172 and 40 CFR part 262 Table 1 <br /> summarizes product thickness measurements and product removed Field notes associated with product <br /> bailing, including charts showing the measured product thickness in the well over time and the depth to fluid <br /> thickness in the wel I over time are included in Attachment 1 <br /> 22 Groundwater Monitoring <br /> Water level elevations were monitored in wells MW 1 through MW7 on March 3, 2005 The depth to water <br /> and depth to product in well MW3 were measured using an electronic water/hydrocarbon interface probe <br /> Depths to water in other site wells were measured using an electronic water level indicator <br /> Groundwater elevations were calculated by subtracting the measured depth to groundwater in each well <br /> from the respective wellhead elevation The depth to groundwater in the wells on March 3, 2005 ranged <br /> from 25 25 feet below the top of the well casing (btoc) in well MW3 (corrected for the presence of free <br /> product)to 26 29 feet btoc in well MW5 Groundwater flowed in a northeasterly direction with a calculated <br /> gradient of 0 0036 feet per foot (approximately 19 feet per mile) A potentiometric surface map for March <br /> 3, 2005 is shown on Figure 2 Groundwater monitoring data are summarized in Table 2 Monitoring data <br /> sheets are included in Attachment 2 <br /> 2 3 Well Purging <br /> An experienced Ground Zero technician purged wells MW1 through MW7 on March 3, 2005 using <br /> dedicated, disposable bailers The technician purged a minimum of three well casing volumes of water from <br /> . each well and measured physical parameters of temperature, pH and electrical conductivity during the <br /> purging process Purging was terminated at each well after the measured parameters stabilized <br /> All downhole equipment was decontaminated between wells by washing with a solution of laboratory-grade <br /> detergent, and then double rinsing with clean rinse water <br /> 2.4 Groundwater Sampling <br /> Groundwater samples were collected from each well after physical parameters had stabilized and the water <br /> in the well had recovered to pre-purged levels Samples were placed in an ice chest at a temperature of 4° <br /> Centigrade and submitted to Argon Laboratory under chain of custody protocol <br /> The samples were analyzed for the presence of TPHg, TPHd, BTEX, and VOCs pursuant to the existing <br /> groundwater monitoring and sampling program Field development/purge logs are included in Attachment <br /> 2 <br /> 3.0 GROUNDWATER ANALYTICAL RESULTS <br /> Tetrachloroethene (PCE) was detected in wells MW1, MW2, MW4, MW5, MW6, and MW7 at <br /> concentrations of 8 3 micrograms per liter (lig/L), 7 5 WL, 4 1 }tgll,, 2 8 gg/L, 43 gg/L, and 100 gg/L, <br /> respectively No PCE was detected in well MW3 (<20 gg/L) Cis-1,2-Dtchloroethene (cis-1,2-DCE) <br /> ranged from <0 5 gg/L in wells MW2 and MWS to 22 gg/L in well MW3 Chloroform ranged from 0 7 <br /> gg/L in well MW7 to 2 4 gg/L in well MW1, but was not detected in well MW3 (<2 0 gg/L) <br /> Trichloroethene(TCE) was detected only in wells MW6 (1 3 gg/L) and MW7 (2 9 gg/L) <br /> G 1GROUNDZ£1GABBARDIreports%QMR120051iQM2005 doc <br />