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ARCHIVED REPORTS_XR0004073
EnvironmentalHealth
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2900 - Site Mitigation Program
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PR0508110
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ARCHIVED REPORTS_XR0004073
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Last modified
9/16/2020 2:07:32 AM
Creation date
2/13/2020 10:06:54 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0004073
RECORD_ID
PR0508110
PE
2950
FACILITY_ID
FA0006134
FACILITY_NAME
POMBO RANCH
STREET_NUMBER
24100
Direction
S
STREET_NAME
LAMMERS
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
24002002
CURRENT_STATUS
01
SITE_LOCATION
24100 S LAMMERS RD
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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Pombo Property <br /> Subsurface Investigation Report <br /> Page: 7 <br /> point, and at the end of the sampling day. De-ionized or organic-free water (also <br /> • provided by the laboratory) was then introduced into the bailer as a final stage of <br />' cleaning. This water was then poured into sample vials to be used as a bailer <br /> blank. <br /> Immediately prior to sampling, water levels and well depth measurements were <br />' taken in all wells at the site. Each well was evacuated using a stainless steel <br /> bladder pump, which does not introduce air into the water column. The pH, <br /> temperature, and electrical conductivity of the water were monitored as the well <br /> was evacuated. A field log of well monitoring information was maintained (see <br /> Appendix C - Well Monitoring Data Sheets). Instruments calibrated to known <br /> 1 standards were used to monitor these parameters. At least 5 well volumes were <br /> evacuated from each well, and more, if necessary, until the above parameters <br /> stabilized. The wells or other sampling points were sampled in order of the least <br /> ' to the most contaminated, as best known or estimated. The samples were <br /> carefully poured from a Teflon bailer into clean glass vials with Teflon-lined <br /> screw caps. Care was taken to ensure that no air space existed in the vials by <br />?' inverting to check for bubbles and re-sampling if necessary. <br /> The groundwater samples were analyzed or extracted within 14 days according to <br /> their EPA methods. The samples were analyzed for Total Petroleum <br /> Hydrocarbons (gasoline & diesel), BTX&E (Benzene, Toluene, Xylene, and Ethyl <br /> Benzene) and MTBE by EPA Method 8020. Analysis was conducted by <br /> ' GeoAnalytical Laboratories; a state certified analytical laboratory. <br /> ' 3.0 SITE CONDITIONS <br /> s <br /> 3.1 Site Geology & Groundwater Occurrence <br /> The Pombo Ranch is located on the southwestern edge of the San Joaquin Delta. <br /> The shallow unconsolidated sediments present at Pombo Ranch are composed <br /> fine-grained overbank and coarse grained channel deposits sourced from <br /> ' Cretaceous and Tertiary rocks exposed in the Coast Range Mountains to the west. <br /> Soil boring logs are presented in Appendix B. <br /> r' The sediments encountered in the area of the underground fuel storage tank in this <br /> investigation (Geoprobew borings 9, 10, 11, 12 and monitoring wells 1, 2, and 3, <br /> ' July 1999) are composed of tan silty plastic clays which grade into a tan very fine <br /> grained, well sorted, silty sand at 15 to 20 below grade. A thin shallow sandy unit <br /> (upper sand) is present within the upper silty clay in boring B 133/9, B10, B11, <br /> MW 1, and MW3. This sandy unit appears to be confin to semi-confined <br /> beneath the overlying silty clay in borings B3/9, B 10, and B 11. The shallow <br /> sandy unit is not present in borings to the east and south of the former <br /> underground storage tank. A coarse sand to pebble gravel was encountered at 5 <br /> feet in boring B 12. The well sorted sand present at the base of the borings (lowe .Z <br /> . sand) dives to the west with an apparent dip of approximately 25 degrees. <br />
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