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i30 April 2005 <br /> AGE-NC Project No 95-0141 <br /> Page 7 of 10 <br />' 4.0. SITE CONCEPTUAL MODEL <br /> The site is located on essentially flat land that is occupied by a heating and air conditioning company <br /> Site structures include, a wain building utilized for office space and storage, a sheet metal shop <br /> utilized to manufacture parts and a covered storage area housing air conditioning units,the majority <br /> of the ground surface is covered by asphalt or concrete (Figure 2) Based on data collected to date <br /> from onsite and offsite soil borings and monitoring well installations, AGE has developed a site <br /> conceptual model for the release,migration and distribution of the contaminants in the subsurface <br />' Based on cone penetrometer test(CPT)log and soil borings,the soil stratigraphy generally consists <br /> of sand to silty sand interbedded with fine grained material From surface grade to 50 ft bsg the <br /> lithology is predominately fine grained with a discontinuous sandy layer from approximately 15 ft <br />' to 30 ft bsg From 50 ft to 105 ft bsg the lithology consists of alternating layers of sandy silt to sand <br /> and fine grained material The layers are laterally continuous and generally 15 to 20 ft thick, acting <br /> as aquifers and aquatards <br />' Based on the soil stratigraphy, supplemented with pore-pressure data from the CPT log, AGE <br /> g pp <br /> developed a hydrogeologic model consisting of six informal zones (Figure 11), a vadose <br /> (unsaturated) zone and five hydrogeologic units (HUs), in general, low pore pressures associated <br /> with the sandy HUs would suggest more rapid pore-pressure dissipation (e g , higher hydraulic <br /> Iconductivities) <br /> Site assessment activities to date identified the area where subsurface soil appears to be impacted <br /> by petroleum hydrocarbons, soil is impacted at the former UST location and appears to have <br /> migrated northeast towards MW-4 (Figures 12, 13 and 14) At the UST location, the highest <br /> concentrations of THP-9 were detected at shallow depths(less than 45 ft bsg) surrounding the UST <br />' location, but extend, in lower concentrations, to a depth of 65 feet bsg in the area of boring MW-6 <br /> Moderate to low concentrations of BTEX compounds were detected in soil samples collected from <br /> borings MW-1 through MW-4 and MW-6 at depths between 15 and 65 feet bsg <br />' The plume of impacted soil at the former UST release area has an estimated long dimension of 110 ft <br /> and short of dimension of 40 feet and a vertical depth of 70 ft bsg at MW-6 and 50 ft bsg at MW-4 <br />' (Figures 12, 13 and 14) Analytical results of soil samples are included in Tables 4 and 5 <br /> Between November 2000 and December 2004, sixteen ground water monitoring events were <br />' performed at the site to monitor dissolved petroleum hydrocarbon concentrations in ground water <br /> and to characterize ground water flow direction and gradient on the site Since initiation of the <br /> ground water monitoring program, ground water elevations have ranged from approximately 11 to <br />' 15 feet below mean sea level, and the ground water flow has been consistently towards the east to <br /> southeast at a low hydraulic gradients TPH-g and/or BTEX compounds have been detected in water <br />' Advanced GeoEnvironmentel,Inc <br />