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ARCHIVED REPORTS XR0001253
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0536689
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ARCHIVED REPORTS XR0001253
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Last modified
3/4/2019 6:22:12 PM
Creation date
3/4/2019 1:16:38 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0001253
RECORD_ID
PR0536689
PE
2957
FACILITY_ID
FA0021073
FACILITY_NAME
STKN CHARTER WAY COMMINGLED PLUME
STREET_NUMBER
508
Direction
W
STREET_NAME
CHARTER
STREET_TYPE
WAY
City
STOCKTON
Zip
95206
APN
16504016
CURRENT_STATUS
01
SITE_LOCATION
508 W CHARTER WAY
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
Scanner
WNg
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EHD - Public
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01 <br />lib <br />Environmental Assessment Report 3 <br />. Chevron U 5 A Products Company,508 Charter Way,Stockton CA —May Ill 1995 <br />Completed wells were surveyed by Morrow Surveying for horizontal position and elevation relative to <br />Mean sea level datum using a City of Stockton benchmark as a reference (Appendrx C) Elevations <br />Were obtained for top -of -well -casings and the well box rims <br />On March 23, 1995, wells MW -1, MW -2 and MW -3 were developed by Groundwater Technology using <br />a PVC bailer Prior to development activities, depth to water was measured in each well relative to <br />top -of -well -casing to determine the static water level (Table 3) Wells were manually developed using <br />a surge block and bailer in order to remove fine-grained sediment Approximately 20 gallons of water <br />(equivalent to 7 well volumes) was extracted from each of the wells All water generated during <br />development was pumped into a DOT -approved purge water trailer and transported to the Chevron <br />refinery in Richmond, California for recycling <br />30 RESULTS OF SOIL SAMPLE ANALYSES <br />Tables 1 and 2 summarize the laboratory analytical results for soil samples collected on March 15 <br />and 16, 1995 Table 1 presents data on BTEX and petroleum hydrocarbons The highest <br />concentrations of BTEX and TPH-G were detected in the sample collected at 35 feet BGS from boring <br />MW -3 at concentrations of 10, 4 6, 1 1, 8 3, and 250 milligrams per kilogram (mg/kg, equivalent to <br />parts per million, or ppm), respectively BTEX and TPH-G were below laboratory detection limits in <br />samples selected for these analyses from boring MW -2 TPH-D and total oil & grease were also below <br />laboratory detection limits in samples analyzed for these compounds from boring MW -1 <br />Concentrations of purgeable halocarbons (EPA method 8010), extractable organics (EPA method <br />8270), and cadmium to samples collected from the 10- and 35 -foot depths from boring MWA were <br />below laboratory detection limits (Table 2) Levels of lead, nickel and zinc detected in these samples <br />were all below comparable Soluble Threshold Limit Concentration (STLC) limits Total chromium was <br />detected to sample MWA-10 at a concentration of 31 mg/kg, which is less than the STLC limit of 50 <br />ppm for chromium Vl <br />Copies of laboratory analyses reports and chain -of -custody manifests for the sod samples collected <br />March 15 and 16, 1995 are included to Appendix D <br />40 GROUNDWATER GRADIENT <br />Potentfometnc surface elevations in the three monitoring wells, calculated from gauging data collected <br />March 23, 1995, indicate groundwater flow to the east-northeast at a gradient of 0 004 (Figure 2, <br />Table 3) <br />• <br />0071 EAFi ,ptlChv 1081 <br />�19 GROUNDWATM <br />❑❑ TECHNOLOGY . <br />
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