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Mr James Barton <br />' July 30, 2004 <br /> Page 4 <br />' Soil Borings and Sampling <br /> On July 6 and July 7, 2004, a geologist from ENSR observed Cascade Drilling, Inc of Rancho <br />' Cordova, California advance soil borings MW-28 through MW-30 to approximate depths of 70 <br /> feet bgs The borings were advanced using a truck mounted drill rig using 8 114-inch diameter <br /> hollow stem augers The soil borings were completed as groundwater monitoring wells MW-28 <br /> through MW-30 The locations of the monitoring wells are shown on Figure 2 <br /> Soil samples were collected from MW-28 using a continuous core sampler to the total depth of <br /> the boring Soil samples were collected from MW-29 and MW-30 at a minimum of 5-foot <br />' intervals and at changes in lithology to the total depth of each boring <br /> The soil samples from each boring were logged using Unified Soil Classification System (USCS) <br />' visual and manual methods Soil samples collected were field screened for the presence of <br /> volatile organic compounds using a photolonization detector (PID) Soil boring logs containing <br /> PID readings, USCS descriptions, and other pertinent drilling information are included in <br /> Attachment C <br /> Soil Sample Analytical Results <br /> Selected soil samples collected from each boring at depths between 40 and 41 feet bgs were <br /> submitted to California Laboratory Services (CLS) in Rancho Cordova, California under chain- <br /> of-custody protocol Sall samples were analyzed for benzene, toluene, ethylbenzene, and total <br /> xylenes (BTEX) using EPA Method 8021, total petroleum hydrocarbons as gasoline (TPHg) by <br /> EPA Method 8015 Modified and methyl tertiary butyl ether (MtBE) using EPA Method 8260B <br /> Soil samples were collected using procedures described in Attachment D Concentrations of <br /> BTEX, TPHg and MtBE were not reported at or above the laboratory reporting limits in soil <br /> samples collected during this investigation <br />' Soil sample analytical results are summarized in Table 1 and copies of the laboratory analytical <br /> reports are included in Attachment E <br />' Monitoring Well Installation <br /> Groundwater monitoring wells MW-28 through MW-30 were constructed using 2 inch diameter, <br /> flush threaded, Schedule 40 polyvinyl chloride (PVC) casing installed to a total depth of <br /> approximately 70 feet bgs The wells are screened from approximately 50 to 70 feet bgs with a <br /> 0 02 inch machine slotted casing No 3 Monterey sand filter pack was placed from the base of <br />' the borings to approximately 4 to 8 feet above the top of the well screen A 2-feet thick <br /> bentonite seal was emplaced above each filter pack, and the remaining annular space was filled <br /> with cement grout containing approximately five percent bentonite to approximately 1-foot bgs <br /> The top of each well was completed with a flush grade traffic rated vault box set In concrete <br /> Well completion diagrams for wells MW-28 through MW-30 are presented In Attachment C <br /> J 1Proiects106940W98-2931FinaAReports15098 Well Results Report doc <br /> M <br />' 01 p 3( Vea- Cn"nr1Pl C`'f11 EMIHN7117enlal Seine <br />