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ARCHIVED REPORTS_XR0002483
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0540859
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ARCHIVED REPORTS_XR0002483
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Last modified
1/15/2020 3:47:30 PM
Creation date
1/15/2020 3:07:38 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002483
RECORD_ID
PR0540859
PE
2960
FACILITY_ID
FA0023361
FACILITY_NAME
PLAY N PARK (FORMER BARNES TRUCKING)
STREET_NUMBER
1817
Direction
S
STREET_NAME
FRESNO
STREET_TYPE
AVE
City
STOCKTON
Zip
95206
CURRENT_STATUS
01
SITE_LOCATION
1817 S FRESNO AVE
P_LOCATION
01
QC Status
Approved
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EHD - Public
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ri r1 pp pp <br /> 0 4D�Q� • <br /> CLEARWATER <br /> G R O U P <br /> Environmental Services <br /> remained undelineated downgradient from the former UST system However, high contaminant <br /> concentrations in cross-gradient position of wells suggested that off-site sources may be contributing to <br /> contamination detected beneath the site Initial inquiries suggested and was later confirmed that there <br /> is existing fuel transport line in the area if the site, and that it is currently filled with nitrogen gas <br /> Based on this information, Clearwater recommended additional investigation along South Fresno <br /> Avenue to better understand the distribution of contamination and possible contribution from potential <br /> off-site sources The results of this phase of investigation were presented in Clearwater's Well <br /> Installation and Groundwater Monitoring Report - First Quarter 1999 <br /> In March 2000, Clearwater supervised the completion of one hydropunch, six soil borings, and the <br /> destruction of MW-5 Three of the borings were converted into monitoring wells (MW-5B, MW-7, and <br /> MW-8) All three wells were placed can the downgradient portion of the plume to help determine the <br /> downgradient extent of contaminants The hydropunch was performed in the former UST location to <br /> assess the vertical extent of groundwater contamination at 36 feet bgs Three soil borings were <br /> performed to define the lateral extent of soil and groundwater contamination an the northeastern <br /> portion of the site and assess possible off-site sources A total of three soil samples and one groundwater <br /> sample were analyzed from each boring Soil concentrations of TPHg and BTEX were only detected in <br /> boring MW-5B The highest soil concentration of TPHg (1,000 mg/kg) was detected at 25 feet bgs in <br /> MW-5B This sample was also analyzed for TPH as let fuel and contained 55 mg/kg Detectable <br /> concentrations of BTEX were present in soil samples collected from boring MW-5B at 25 feet and 35 feet <br /> bgs MTBE was not detected by EPA method 8260 in any of the soil samples analyzed Groundwater <br /> concentrations of TPHg and BTEX were detected in borings SB-9, MW-5B, MW-7 and MW-8 The <br /> highest groundwater concentration of TPHg (9,700 gg/L) was detected in MW-5B MTBE was not <br /> detected by EPA method 8260 in any of the groundwater samples analyzed <br /> Geologyand hvdrogeology <br /> Subsurface lithologies encountered during drilling consisted predominantly of silty clay, with <br /> subsidiary clayey sand with occasional sandy lenses Groundwater has been observed beneath the site <br /> from 4 71 feet bgs(MW-2 on March 9,2000)to 1196 feet bgs(MW-3 on September 29 1996) Groundwater <br /> elevation measurements within the last 12 months have indicated groundwater to flow generally to the <br /> south-east at a gradient ranging from 0 0005 ft/ft on May 30,2001 and 0 018 ft/ft on February 13, 2001 <br /> 7B178C Workplan for remedial feasibility testing 3 August 2001 <br />
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