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SITE INFORMATION AND CORRESPONDENCE
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2900 - Site Mitigation Program
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PR0523686
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
5/22/2019 9:51:21 AM
Creation date
5/22/2019 9:46:56 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0523686
PE
2950
FACILITY_ID
FA0015978
FACILITY_NAME
FORMER TIGER LINES YARD
STREET_NUMBER
1430
Direction
S
STREET_NAME
CHEROKEE
STREET_TYPE
LN
City
LODI
Zip
95241
APN
06206039
CURRENT_STATUS
01
SITE_LOCATION
1430 S CHEROKEE LN
P_LOCATION
02
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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r <br /> Former LTS Rentals - 2 - 24 July 2012 <br /> 1430 and 1600 South Cherokee Lane, Lodi <br /> SITE INVESTIGATION <br /> Recommendations in a 2003 Phase I Site Assessment (PSA) included the proposed <br /> removal of a set of six ASTs and fuel dispensers, an underground vapor recovery tank <br /> associated with the AST system, and a truck wash rack with an underground clarifier. The <br /> PSA also recommended a site investigation to assess whether soil had been impacted (see <br /> Figure 2 for site features). <br /> In June and September 2003, Advanced GeoEnvironmental (AGE) collected soil samples <br /> from exploratory trenches to locate impacted soil surrounding the AST locations (see Figure <br /> 3 for trench sample locations and Table 1 for soil analytical results). AGE detected total <br /> petroleum hydrocarbons as diesel (TPHd) at a maximum concentration of 6,400 milligrams <br /> per kilogram (mg/kg), and traces of ethylbenzene, xylenes, polycyclic aromatic <br /> hydrocarbons (PAHs), and lead. In 2005, five soil borings (SB-1 through SB-5) were drilled <br /> and sampled in the former AST containment area (see Figure 3 for boring locations and <br /> Table 1 for soil analytical results). <br /> Soil encountered during drilling at the site consisted of silt from the ground surface to 10-15 <br /> feet below the ground surface (bgs). Beneath this surficial unit, interbedded sands, silts and <br /> clays were present to total depth. Poorly-graded sands and silty sands are the predominant <br /> soils. <br /> Groundwater samples were collected from SB-1 through SB-4 at 55 feet bgs (see Table 2 <br /> for results). Analytical results for all groundwater samples were non-detect for total <br /> petroleum hydrocarbons as diesel (TPHd), total petroleum hydrocarbons as gasoline <br /> (TPHg), BTEX and fuel oxygenates including MtBE. Regional groundwater flow is toward <br /> the south-southeast. However at a nearby fuel leak investigation site, groundwater flow is <br /> toward the northwest. <br /> REMEDIATION <br /> In their 22 October 2009 work plan, Ground Zero proposed the removal of hydrocarbon <br /> impacted soil that was identified in the vicinity of the former ASTs and the investigation and <br /> removal of any hydrocarbon impacted soil that may be associated.with the former fuel <br /> dispenser area. There was no hydrocarbon impacts associated with the clarifier or <br /> underground vapor recovery tank. <br /> Remediation activities performed by Ground Zero at the site included the excavation of <br /> overburden and petroleum impacted soil; segregating and stockpiling soil; and sampling of <br /> both the overburden and petroleum impacted soil stockpiles. <br /> The first phase of excavation activities occurred in November and December of 2009. An <br /> area of approximately 5,500 square feet was excavated beneath the former AST <br /> containment area and beneath the former pump island. Petroleum impacted soil was <br /> encountered in the northeast corner of the former AST containment area (see Figure 4 for <br /> excavation limits) vertically between 15 and 38 feet bgs. Approximately 3,800 cubic yards <br /> of impacted soil was stockpiled on asphalt pavement northeast of the excavation. Following <br />
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