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Mr Kyle Christie Project 20805-144 004 <br /> July 26, 1996 <br /> Page 2 <br /> In November 1991, RESNA observed the removal of five USTs and associated piping and <br /> collected compliance soil samples from the UST cavity and piping trenches The former <br /> UST cavity was not overexcavated and soil and fill material removed concurrent with the <br /> UST removal was used to backfill the cavity Soil containing residual petroleum <br /> hydrocarbons was also left in-place in the piping trenches New USTs and piping were <br /> installed in November and December 1991 <br /> RESNA directed additional site investigation activities in October 1992 Eleven soil <br /> borings were drilled to depths of 36 to 63 feet bgs Four borings were converted to vapor <br /> extraction wells and four borings were converted to groundwater monitoring wells <br /> Groundwater was encountered in the four borings converted to monitoring wells at a depth <br /> of approximately 54 feet bgs Boring and well locations are shown on Figure 2 <br /> Quarterly groundwater monitoring events began in October 1992 Over the duration of the <br /> monitoring program, groundwater samples collected from all monitoring wells (MW-1 <br /> through MW-4) were below laboratory detection lirruts for total petroleum hydrocarbons <br /> as gasoline (TPHG), benzene, toluene, ethylbenzene, or total xylenes (BTEX) with the <br /> exception of one sampling event conducted in October 1993, in which ethylbenzene was <br /> detected at a concentration of 0 7 micrograms per liter (MW-3) Historical groundwater <br /> analytical results are presented in Appendix A <br /> The depth to groundwater recorded over the duration of the quarterly monitoring program <br /> ranged from approximately 50 to approximately 54 feet bgs (see Appendix A) Perched <br /> groundwater conditions may explain the difference between the depth to groundwater <br /> encountered during the October 1990 investigation and the depth groundwater was <br /> encountered during all future investigations and monitoring Only three of the five soil <br /> borings encountered groundwater during the October 1990 investigation, and in those <br /> three bonngs groundwater was encountered on top of a silt unit <br /> TPH MASS CALCULATIONS <br /> The TPH mass calculations are based on estimated lateral and vertical extent of soil <br /> impacted by TPHG The lateral and vertical extent of impacts were evaluated using the <br /> soil sample analytical results obtained from the former UST cavity, former piping <br /> trenches, and exploratory borings TPHG isoconcentration maps were prepared for four <br /> depth intervals based on the distribution of petroleum hydrocarbon impacts and soil types <br /> • Two to 6 feet bgs for evaluation of near surface impacts, generally related to the <br /> piping trenches Soil type generally consists of sand to silty sand <br /> is <br /> 5AOX\08051440 DOC-961dms 1 <br />