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ARCHIVED REPORTS_XR0004665
Environmental Health - Public
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3500 - Local Oversight Program
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PR0545482
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ARCHIVED REPORTS_XR0004665
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Last modified
3/10/2020 11:56:10 AM
Creation date
3/10/2020 9:06:20 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0004665
RECORD_ID
PR0545482
PE
3528
FACILITY_ID
FA0005075
FACILITY_NAME
DONS MOBILE GLASS
STREET_NUMBER
151
Direction
S
STREET_NAME
MAIN
STREET_TYPE
ST
City
MANTECA
Zip
953365719
APN
21941015
CURRENT_STATUS
02
SITE_LOCATION
151 S MAIN ST
P_LOCATION
04
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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1 <br /> Corrective Action Plan <br /> 22 Hydrogealogic Characteristics <br /> The groundw ater elevation at the site has fluctuated from more than 25 feet below ground surface <br /> (bas) in 1991 (at the height of the drought period) to less than 15 feet bgs during the most recent <br /> monitoring events in early 1997 The direction of groundwater flow over this period has covered <br /> an approximate 140 degree range from approximately north 60 degrees west to north 80 degrees <br /> 1 east The water table beneath the site has been relatively flat with a gradient ranging from 0 0005 <br /> to 0 012 (a median gradient of less than 0 003) <br /> ' The soil at the site has been logged by different geologists (Greg Drilling for Blymer Engineers <br /> Inc [Blymer], Steffen Robertson and Kirsten [SRK], and Park Environmental Corporation <br /> [Part.]) during each phase of the site )Investigation involving monitoring well installations OST <br /> ' believes that the considerable variations in the type and size of the soil described in the logs <br /> represent interpretive differences rather than lateral variation in the soil According to the logs <br /> provided by Blymer and by Park,the soil consists of relatively thick(>I 0 feet) layers of fine sand <br /> (which SRK calls sandy clay) interbedded with thinner (<5 feet) layers of clay or silt The <br /> drilling logs for all monitoring wells are presented in Appendix A Because of the variations in <br /> well logging and the limited area of concern, the construction of geologic cross-sections was not <br /> considered particularly useful or practical Although the site was not subjected to aquifer pump <br /> testing or soil vapor extraction treatability testing, both groundwater extraction and soil vapor <br /> extraction (SVE) are considered viable The rationale for these assumptions are presented in a <br /> later section of this CAP <br /> ' 3.0 BACKGROUND SUMMARY <br /> Both soil and groundwater at this facility have been impacted by excessive concentrations of <br /> petroleum hydrocarbons, specifically gasoline The background summary has been derived from <br /> several phases of site investigation and groundwater monitoring conducted between 1988 to the <br /> present by three environmental consulting firms, Blymer, SRK, and Park A comprehensive <br /> review of the following technical reports along with DST's more than twelve years experience <br /> in soil and groundwater remediation provide the basis for the CAP <br /> • Environmental Site Assessment and Structural Inspection, 1989, by Blymer <br /> ' Update Information, 1990, by Blymer <br /> • Phase II Environmental Audit, December 1991, by SRK, <br /> • Quarterly Ground Water Monitoring, July 1992, by SRK <br /> • Quarterly Ground Water Monitoring, October 1992, by SRK <br /> • Quarterly Ground Water Monitoring, April 1993, by SRK <br /> • Quarterly Ground Water Monitoring, January 1994 by SRK <br /> • Soil and Water Investigation Work Plan Noy ember 1994, Part. <br /> • Quarterly Ground Water Monitoring November 1994, by Park <br /> • Quarterly Ground Water Monitoring, .Pune 1995, by Park <br /> OST <br /> ' 701-1-2 cap Nee 3 <br />
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