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WORK PLANS_FILE 2
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PR0541693
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WORK PLANS_FILE 2
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Entry Properties
Last modified
2/6/2020 11:23:50 AM
Creation date
2/6/2020 10:12:41 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
FileName_PostFix
FILE 2
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
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SJGOV\sballwahn
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EHD - Public
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r <br /> � vkT(Z <br /> ASS O C I ATE S INC . <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 /> 1 the direction of regional groundwater flow is generally to the east. The groundwater basin has been <br /> - I 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 /> r Water Channel empties into the San Joaquin River approximately 2 miles downstream from the <br /> -{ site. <br /> 2.3 Site Geolou and Hydroeeolo¢y <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 bgs. From 11 to 17 <br /> feet to approximately 35 feet bgs, the sediments consist predominantly of sand and silt, with some <br /> clay layers. Soil boring logs are contained in Appendix A and cross section locations and geologic <br /> cross sections depicting the interpreted subsurface conditions are shown on Figures 4, 5 , and 6, <br /> I. I respectively. <br /> During groundwater monitoring activities conducted on June 8, 2000, groundwater was <br /> encountered at approximately 21 feet bgs. From July 1997 to July 2000, static water levels have <br /> fluctuated from approximately 20 to 29 feet bgs; variations in depth to water between the wells <br /> during each monitoring event are apparently due to seasonal fluctuations and possible hydraulic <br /> influence caused by the Stockton Deep Water Channel which is located approximately 1 ,000 feet to <br /> lthe southwest. <br /> f Based on groundwater elevations measured on June 11 , 2001 , the direction of groundwater flow is <br /> -1 generally toward the northeast at an approximate gradient of 0.008 ft/ft. The groundwater gradient <br /> map for June 11 , 2001 is shown on Figure 3. The direction of groundwater flow has ranged from <br /> 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 by <br /> J overexcavating the former tank locations. The former tank locations were excavated to a depth <br /> of approximately 22 feet below ground surface (bgs). The excavation was limited to the north by <br /> the on-site building. The confirmation samples collected from the base of the overexcavation <br /> `) still contained elevated concentrations of volatile organics. The overexcavated soil was disposed <br /> of at Forward Landfill. <br />' rI <br /> `J On June 30 and July 1 , 1997, Smith Technology personnel supervised advancement of seven soil <br /> borings, SBI 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:\wordpro\62596\reports\irp.doc 2 <br /> I <br />
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