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ARCHIVED REPORTS_XR0003213
Environmental Health - Public
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EHD Program Facility Records by Street Name
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2900 - Site Mitigation Program
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PR0541693
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ARCHIVED REPORTS_XR0003213
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Last modified
2/6/2020 12:20:05 PM
Creation date
2/6/2020 11:05:56 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0003213
RECORD_ID
PR0541693
PE
2960
FACILITY_ID
FA0023897
FACILITY_NAME
TOYOTA TOWN INC
STREET_NUMBER
610
Direction
N
STREET_NAME
HUNTER
STREET_TYPE
ST
City
STOCKTON
Zip
95202
APN
13906033
CURRENT_STATUS
01
SITE_LOCATION
610 N HUNTER ST
P_LOCATION
01
QC Status
Approved
Scanner
SJGOV\sballwahn
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EHD - Public
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� v <br /> o <br /> A S S O C I A T E S I N C <br /> The site is in the Eastern San Joaquin County Groundwater Basin (California Department of Water <br /> ' Resources, 1980) According to the San Joaquin Flood Control and Water Conservation District, <br /> the direction of regional groundwater flow is generally to the east The groundwater basin has been <br /> developed for intensive irrigation, domestic, industrial, municipal, and stock use <br /> There is one surface stream near the site, the eastward extension of the Stockton Deep Water <br /> ' Channel (including MacLeod Lake) approximately 1,000 feet to the southwest The Stockton Deep <br /> Water Channel empties into the San Joaquin River approximately 2 miles downstream from the <br /> site <br /> 223 Site Geology and Hydrogeology <br /> Based on information obtained from previous borings at the site, sediments underlying the site <br /> consist primarily of clay from ground surface to approximately 11 to 17 feet below ground surface <br /> (bgs) From 11 to 17 feet to approximately 35 feet bgs, the sediments consist predominantly of <br /> sand and silt, with some clay layers Soil boring logs are contained in Appendix A and cross <br /> section locations and geologic cross sections depicting the interpreted subsurface conditions are <br /> shown on Figures 4, 5, and 6, respectively <br /> During groundwater monitoringactivities conducted on December 31 200 <br /> 1, groundwater was <br />' encountered at approximately 24 feet bgs From July 1997 to December 2001, static water levels <br /> have fluctuated from approximately 20 to 29 feet bgs, variations in depth to water between the <br /> wells during each monitoring event are apparently due to seasonal fluctuations and possible <br /> hydraulic influence caused by the Stockton Deep Water Channel which is located approximately <br /> 1,000 feet to the southwest <br /> Based on groundwater elevations measured on December 31, 2001, the direction of groundwater <br /> flow is generally toward the northeast at an approximate gradient of 0 007 ft/ft The groundwater <br /> gradient map for December 31, 2001 is shown on Figure 3 The direction of groundwater flow has <br /> ranged from east to northeast since groundwater monitoring was initiated in July 1997 <br /> 3.0 PREVIOUS ENVIRONMENTAL WORK <br />' On January 21, 1988, Falcon Energy, attempted to remove all VOC contaminated soil b <br /> p y <br /> overexcavating the former tank locations The former tank locations were excavated to a depth <br /> Iof approximately 22 feet bgs The excavation was limited to the north by the on-site building <br /> The confirmation samples collected from the base of the overexcavation still contained elevated <br />' concentrations of volatile organics The overexcavated soil was disposed of at Forward Landfill <br /> On June 30 and July 1, 1997, Smith Technology personnel supervised advancement of seven soil <br /> borings, SB 1 through SB7, at the site to depths ranging from approximately 40 to 45 feet bgs at <br /> the site to investigate the horizontal and vertical extent of petroleum hydrocarbon soil and <br />' w Iwordpro1625961reponsloff--site doc 2 <br />
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