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E11C�ytg <br /> Mr James L Barton <br /> October 29, 2004 <br /> Page 5 <br /> Soil Boring and Sam hn <br /> On August 16, 2004, a geologist from ENSR observed Cascade Drilling, Incorporated (Cascade) <br /> Of Rancho Cordova, California advance soil boring MW-9R to an approximate depth of <br />' 70 feet bgs The boring was advanced using a truck mounted drill rig using 81/ -inch diameter <br /> hollow stem augers The soil boring was completed as groundwater monitoring well MW-9R <br /> The location of the monitoring well is shown on Figure 2 <br /> Soil samples were collected from MW-9R at a minimum of 5-foot intervals and at changes in <br /> lithology to the total depth of the boring The sod samples from the boring were logged using <br /> Unified Soil Classification System (USCS) visual and manual methods Soil samples collected <br />' were field screened for the presence of volatile organic compounds using a photoionization <br /> detector (PID) A soil boring log containing PID readings, USCS descriptions, and other <br /> pertinent drilling information is included in Attachment I <br />' <br /> Soil Sample Anal ical Results <br />' A soil sample collected from an approximate depth of 40 feet bgs was submitted to CLS in <br /> Rancho Cordova, California under chain-of-custody protocol The soil sample was analyzed for <br /> benzene, toluene, ethyl benzene and xylenes (BTEX), 1,2-dichloroethane (1,2-DCA), <br /> 1,2-dibromoethane (EDB), and MtBE using EPA Method 82606, and TPHg by EPA <br /> Method 8015 Modified Soil samples were collected using procedures described in <br /> Attachment A Soil sample analytical results are summarized in Table 12 and copies of the <br />' laboratory analytical reports are included in Attachment D <br /> Monitoring Welllnstallation <br />' Groundwater monitoring well MW-9R was constructed using 2-inch diameter, flush threaded, <br /> Schedule 40 PVC casing installed to a total depth of approximately 70 feet bgs The well was <br /> screened from approximately 50 to 70 feet bgs with a 0 02-inch machine slotted casing No 3 <br />' Monterey sand filter pack was placed from the base of the boring to approximately 5 to 8 feet <br /> above the top of the well screen A 2-feet thick bentonite seal was emplaced above each filter <br /> pack, and the remaining annular space was filled with cement grout containing approximately <br />' five percent bentonite to approximately 1-foot bgs The top of the well was completed with a <br /> flush grade traffic rated vault box set in concrete A well completion diagram for well MW-9R is <br /> presented in Attachment I <br /> Well Develo mens and warn lin <br /> Groundwater monitoring well MW-9R was developed and sampled on August 31, 2004, <br /> Iaccording to field methods and procedures outlined in Attachment A <br /> RQcsacramentoVroiects\Proiects1069401509$-293TinaRRepoftlQuartedy Monrtonng ReportO098 3rd Qtr 04 QMR doc <br /> i <br /> 6eieorar,no 35 Yepr,, o'Excohenre Envrronrnenra'SQrti icef <br /> t <br />