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2900 - Site Mitigation Program
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PR0536689
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Last modified
3/4/2019 1:15:01 PM
Creation date
3/4/2019 11:20:14 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
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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t Chevron Products Company 2 <br />Chevron Service Station #9-2033, 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 gg/L in the sample collected from SB -5 at 42 feet bgs. <br />I:\Chevron\92033\REPORTS\9-2033 SA CPT WPFA.doc <br />
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