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August 5, 1997 <br /> 38737 001 Harding Lawson Associates <br /> Ms Mary Meays <br />' San Joaquin County Public Health Services <br /> Page 6 <br />' HLA recommends additional work necessary to provide the data required to demonstrate compliance with <br /> the above criteria and pursue classification of the Site with a "low risk'groundwater designation (RWQCB, <br /> 1996) The additional work also address issues raised by PHS/EHD during a September 5, 1995 meeting <br /> with TVG(see discussion above) The following additional data are required <br /> • The groundwater data collected by SECOR do not provide the information necessary to delineate the <br /> vertical extent of impacted groundwater and therefore allow estimates of the hydrocarbon mass in the <br /> groundwater <br /> • Additional soil data in the area between boring SB-1 and SB-7 and beneath the forklift building near <br /> boring HAl are needed to define the lateral and vertical extent of impacted soil <br /> 1 . Intraplume groundwater monitoring well data from near the impacted soils are necessary to <br /> demonstrate that free product is not present, and also for compliance monitoring of whatever <br /> remedial measure is chosen <br /> Site-specific physical and chemical subsurface data to assess the efficacy remedial measures <br /> HLA proposes to perform the following scope of work at the Site in accordance with the existing TVG <br /> workplan approved by PHS/EHD and as modified below <br /> ♦ Advance two soil borings in the approximate locations of SECOR boring SB-9, and SB-10 <br /> ♦ Install an intraplume monitoring well in the boring located near SB-10 <br /> ' ♦ Advance one boring in the area HA1 to assess the vertical distribution of impacted soil in this area <br /> • All borings will be continuously logged <br /> • Collect soil samples at 5-foot minimum intervals in each boring <br /> 1 • Collect Hydropunch groundwater samples at three depths in each boring <br /> e Submit selected soils samples for analyses for TPHg (EPA Method 8015M) and BTEX (EPA Method <br /> 8020) <br /> ♦ Test selected samples for physical, chemical, and biological indicator parameters for bioremedial <br /> effectiveness <br /> The existing monitoring wells have not been sampled recently and are proposed to be sampled within the <br /> third quarter of 1997 The sampling will include the measurements of depth to groundwater and <br /> determination of the groundwater gradient and flow direction Prior to sampling, wells will be purged of <br /> at least three well casing volumes and monitored during the purging process for temperature, <br /> conductivity, and pH Purge water will be containerized in DOT-approved 55-gallon drums which will be <br /> labeled with the well number and accumulation date and retained on Site pending receipt of the <br /> analytical data Purging will be considered complete when the minimum volume has been purged and <br /> when the indicator parameters have stabilized to within 10 percent on successive readings The samples <br /> will be transported in accordance with chain-of-custody protocol to a state certified analytical laboratory <br /> Samples will be analyzed for TPHg with EPA Method 8015M and BTEX with EPA Method 8020 The <br /> resulting monitoring data when completed will be forwarded along with analytical data in the form of a <br /> brief letter report that will be submitted to the PHS/EHD and the RWQCB <br /> REMEDIAL APPROACH <br /> After the collection of data outlined above alternatives to achieve site closure will be considered and a <br /> Remedial Action Plan(RAP) will be developed Three remedial alternatives will be proposed and <br /> evaluated based on technical applicability and on cost efficiency With the proposed intraplume well, the <br /> existing monitoring network appears adequate in number and position to perform compliance monitoring <br /> ti <br />