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ARCHIVED REPORTS XR0001214
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2900 - Site Mitigation Program
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PR0536689
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ARCHIVED REPORTS XR0001214
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Entry Properties
Last modified
3/4/2019 2:06:41 PM
Creation date
3/4/2019 11:45:36 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0001214
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
Tags
EHD - Public
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Chevron Products Company 2 <br /> Chevron Service Station#9-2033 508 West Charter Way,Stockton CA March 5,2002 <br /> Street The City of Stockton maintenance yard, located to the south, is reported to have, <br /> or have had, one or more underground storage tanks (USTs) Current and the former <br /> station features are shown on Figure 2 <br /> A brief summary of previous investigations is included in Attachment A <br /> ASSESSMENT ACTIVITIES AND FINDINGS <br /> In May 2001, SECOR supervised cone penetration testing (CPT) at four onsite locations <br /> (SB-5 through SB-8) located at each corner of the site boundary to assess soil <br /> stratigraphy and collect discrete groundwater samples (Figure 2) CPT borings <br /> advanced at each location provided continuous soil behavior and pore pressure data to <br /> the total depth explored <br /> Each CPT borings was advanced to approximately 90- to 95- feet below ground surface <br /> (bgs) Adjacent to each CPT boring, a second direct-push borehole was advanced, while <br /> water samples were collected at intervals selected through pore pressure observation in <br /> the first boring Pore pressure and lithologic information were used to target two to <br /> three depth-discrete groundwater samples in each boring <br /> Groundwater samples were analyzed for the presence of total petroleum hydrocarbons <br /> quantified as gasoline (TPHg), benzene, toluene, ethylbenzene, xylenes (BTEX) and the <br /> fuel oxygenates by Environmental Protection Agency (EPA) method 8260B <br /> Upon completion, the borings were filled with grout from the bottom up and finished to <br /> surface grade with asphalt Field and laboratory procedures are presented in Attachment <br /> B The findings of this assessment are summarized below <br /> • Subsurface Conditions. Review of the boring logs and CPT profiles suggests <br /> silty mixtures with sand/ or clay mixtures with silt to clayey silt horizons to <br /> approximately 40 feet bgs, sandy to clayey silt horizons from approximately 40 <br /> feet bgs to 50 feet bgs, sandy silt to silty horizons from approximately 50 feet <br /> bgs to 80 feet bgs, sand to clayey silt horizons were encountered below 80 feet <br /> bgs Groundwater was generally encountered at approximately 21, 43 and 81 <br /> feet bgs at each boring location CPT logs are included in Attachment C <br /> • Groundwater Analytical Results. Groundwater samples were collected from <br /> each direct-push boring from the identified water bearing zones, or at a depth - <br /> interval showing distinct pore pressure and submitted for chemical analysis <br /> Summarized groundwater analytical results are presented in Table 1 A copy of <br /> laboratory analytical reports and chain-of-custody records are presented in <br /> Attachment D <br /> ■ TPHg was detected in seven groundwater samples at concentrations ranging <br /> from 180 micrograms per liter (µg/L) in the sample collected from SB-6 at <br /> 38 feet bgs to 100,000 pg/L in the sample collected from SB-5 at 42 feet bgs <br /> I\Chevron1920331REPORTSI9-2033 SA CPT WPFA doc <br />
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