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ARCHIVED REPORTS_MONITORING WELL INSTALLATION REPORT - SITE ASSESSMENT WORK PLAN
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ARCHIVED REPORTS_MONITORING WELL INSTALLATION REPORT - SITE ASSESSMENT WORK PLAN
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Last modified
12/19/2019 4:41:53 PM
Creation date
12/19/2019 4:28:54 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
MONITORING WELL INSTALLATION REPORT - SITE ASSESSMENT WORK PLAN
RECORD_ID
PR0507398
PE
2950
FACILITY_ID
FA0007748
FACILITY_NAME
CFN CARDLOCK FACILITY
STREET_NUMBER
2211
Direction
N
STREET_NAME
WILSON
STREET_TYPE
WAY
City
STOCKTON
Zip
95205
APN
11707050
CURRENT_STATUS
02
SITE_LOCATION
2211 N WILSON WAY
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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' Historical Background:gr d. River City Petroleum and Connell Motor Lift Truck <br /> ' Page 11 of 13 <br /> DISTRIBUTION OF STODDARD SOLVENT WITH BTEX <br /> ' 0 A release of stoddard solvents occurred from an unidentified source on the westernp ortion <br /> of the site. The most possible source is a set of dry well storm drains. Available data is <br /> ' suggestive of a spill or discharge at the western edge of the building in the area of borings <br /> P26,P27,CPT32 and various wells including the extraction well EW-1.The highest impact <br /> t to soil in the upper vadose zone is present at borings P26, P27, P14, P25 and EW-1. Once <br /> released to the subsurface, the contaminants migrated to a vertical depth of approximately <br /> 40 feet bsg, at which point the contaminants migrated locally down to a depth of 70 or 80 <br /> ' feet bsg.Minor concentrations of 1,2-DCA and tetrachloroethene were detected at the depths <br /> of 45 feet to 65 feet bsg, within the stoddard plume area west of the building. The highest <br /> impact to soil near the water table and below the water table to a depth of 70 feet bsg occurs <br /> ' in the area of boring EW-1,P27 to 55 feet and borings P26 and P32 to a depth of 70 feet bsg. <br /> • Total petroleum hydrocarbons quantified as stoddard solvent (TPH-ss) were detected in <br /> various ground water samples at maximum concentrations of 20,000 gg/l TPH-ss(MW-16), <br /> with moderate concentrations of BTEX at 34 µg/l benzene, 59 gg/l toluene, 120 gg/l <br /> ethylbenzene and 560 µg/1 xylene, respectively. <br /> ' The vertical and the lateral extent of TPH stoddard has been defined by sample collected. <br /> • The aerial extent of the soil contamination in the vadose zone is defined. <br /> DISTRIBUTION OF TPH-G AND BTEX-FORMER UST AREA <br /> ' 0 A release of petroleum hydrocarbons(TPH-g, TPH-d) and benzene,toluene, ethylbenzene <br /> ' and xylene (BTEX) compounds occurred from dispenser line releases. <br /> • Petroleum hydrocarbons were not detected in the soil samples collected from below the <br /> former UST area, nor excavation, however the most significant mass of hydrocarbons are <br /> ' found below the UST area proper. Available data is suggestive of a release that was most <br /> severe at the southern most dispenser islands, less at the north dispensers and even less <br /> between the dispenser islands.Once released TPH/BTEX to the subsurface,the contaminants <br /> ' migrated north under the former UST area then to a vertical depth of approximately 55 feet <br /> bsg near the current water table, where the variation concentration in soil samples suggest <br /> a smear zone between 50 feet and 60 feet bsg.At this point the TPH contaminants migrated <br /> ' locally down to a depth of 75 feet bsg,where non-detect soil samples were collected at the <br /> former UST area. Additionally, minor concentrations of 1,2-DCA were detected in soil <br />' samples collected at the depths of 65 feet to 85 feet bsg, collected below the former UST <br /> area. <br /> • The highest TPH-g and BTEX impact to soil in the upper vadose zone is present at <br /> Advanced GeoEnvironmental,Inc. <br />
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