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ARCHIVED REPORTS_XR0009593
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0542235
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ARCHIVED REPORTS_XR0009593
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Last modified
5/4/2020 3:12:57 PM
Creation date
5/4/2020 2:39:43 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0009593
RECORD_ID
PR0542235
PE
2960
FACILITY_ID
FA0024262
FACILITY_NAME
CANEPA CAR WASH
STREET_NUMBER
248
Direction
E
STREET_NAME
PARK
STREET_TYPE
ST
City
STOCKTON
Zip
95202
APN
13906035
CURRENT_STATUS
01
SITE_LOCATION
248 E PARK ST
P_LOCATION
01
QC Status
Approved
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SITE BACKGROUND CANEPA'S CAR WASH,PARK STREET <br /> The site is located in the downtown business district of Stockton, California One 12,000-gallon unleaded <br /> gasoline underground storage tank (UST), one 5,000-gallon leaded gasoline UST, and one 5,000-gallon <br /> diesel fuel UST were removed from the site in 1990 According to WHF Environmental Consultants, Inc <br /> (WHF), soil samples collected from the UST excavation from approximately 15 feet below the ground <br /> surface (bgs) contained elevated concentrations of gasoline and gasoline constituents Between September <br /> 1993 and March 1994, WHF installed six soil borings and seven monitor wells in and around the site <br /> Three of the monitor wells (MW-1, MW-2, and MW-3) were constructed with a screened interval from 45 <br /> to 65 feet bgs Monitor wells MW-4 through MW-7 were constructed with a screened interval from 40 to <br /> 60 feet bgs <br /> Beginning in April 1997, Condor implemented a quarterly groundwater monitoring program at the site <br /> Following the July 1998 quarterly groundwater monitoring event, Mr Rowe of the PHSIEHD requested <br /> the installation of additional monitor wells The tops of the screened intervals of monitor wells MW-I <br /> through MW-7 are submerged below the present groundwater table Condor prepared a work plan dated <br /> November 17, 1998, for the installation of four additional monitor wells (MW-8 through MW-1 1) In a <br /> letter dated September 7, 2001, however, Mr Jeffrey Wong of the PHSIEHD requested that an additional <br /> work plan be submitted by October 20, 2001 to define the lateral and vertical extent of groundwater <br /> contamination and the vertical extent of soil contamination at the site Mr Wong also requested submittal <br /> of a Sensitive Receptor Survey Report for a 2,000-toot radius around the site by November 10, 2001 In <br /> response to Mr Wong's request, Condor submitted the Work Plan for Additional Soil and Groundwater <br /> Investigation, dated October 17, 2001 The work plan describes several proposed direct push borings <br /> intended to investigate the lateral and vertical extent of contamination and assist in the siting of additional <br /> monitor wells in a subsequent phase of work, if necessary Mr Wong subsequently approved the work <br /> plan, with modifications, in a letter dated October 29, 2001 <br /> Site investigation activities pursuant to the above described work plan were performed from March 25 <br /> through March 28, 2002, details of the investigation are presented in Condor's Additional Soil and <br /> Groundwater Investigation Report, dated May 8, 2002 Investigation activities included the installation <br /> ot, two Cone Penetrometer test (CPT) borings, one soil boring, and, twenty-one direct push (hydropunch) <br /> borings to investigate the vertical extent of groundwater contamination at the site and to evaluate it <br /> lithologic composition was limiting the vertical extent of groundwater contamination, to evaluate the <br /> lateral extent of shallow groundwater contamination, and, to evaluate the vertical extent of the <br /> groundwater contamination down-gradient of the site <br /> Laboiatory analytical results of the soil samples indicated that relatively elevated concentrations of <br /> gasoline constituents are present down to the deepest sample collected (approximately 82 feet bgs) <br /> However, the lowest concentrations of gasoline constituents were detected in the sample collected at 82 <br /> feet bgs, indicating the potential for some attenuation of concentrations beginning at that depth MTBE <br /> was not detected at or above the laboratory reported detection limit in any of the soil samples In addition, <br /> laboratoiy analytical results from the groundwater sample collected proximal to the soil samples indicated <br /> that the gasoline is partitioning into the groundwater phase with some difficulty, probably as a result of <br /> the relatively fine-grained soil texture <br /> The laboratory analytical results of the hydropunch groundwater samples indicate that relatively elevated <br /> concentrations of gasoline constituents are present at depths below the water table both proximal (CPTI) <br /> I <br />
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