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ARCHIVED REPORTS_XR0003066
Environmental Health - Public
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3500 - Local Oversight Program
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PR0545342
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ARCHIVED REPORTS_XR0003066
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Last modified
2/12/2020 3:48:42 PM
Creation date
2/12/2020 8:56:34 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0003066
RECORD_ID
PR0545342
PE
3528
FACILITY_ID
FA0000392
FACILITY_NAME
FLAMES LIQUOR
STREET_NUMBER
1301
Direction
W
STREET_NAME
KETTLEMAN
STREET_TYPE
LN
City
LODI
Zip
95242
APN
03104030
CURRENT_STATUS
02
SITE_LOCATION
1301 W KETTLEMAN LN
P_LOCATION
02
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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�a <br /> 28 February 2005 <br /> . AGE-NC Project No 99-0624 <br /> Page 3 of 12 <br /> 6� <br /> 2 2 BATCH GROUND WATER REMOVAL <br /> Due to the amount of time required for state-required bench testing and pilot testing of the ozone <br /> sparging system prior to full utilization,AGE proposes to extract petroleum-impacted ground water <br /> from the most-impacted well, MW-.r2 The-ground water will be directly pumped into an on-site <br /> holding tank(batch removal) on a bi-monthly basis f r one quarter at which time the effectiveness <br /> of this method of remediation will be ve aluated,the holding tank will be trucked offsite for disposal , <br /> of the impacted ground water The objectives of batch removal of ground water are to reduce the <br /> concentration of MTBE in the area of well MW-2 and to exert hydraulic control to prevent additional <br /> offsite migration of impacted ground water This method cannot be utilized as a long-term remedial <br /> alternative because cost of tank rental,trucking,and offsite ground water disposal is high,especially <br /> if additional site investigation delineates a wider MTBE-impact zone than presently realized The <br /> cost of each batch removal is estimated at approximately $10,000 to $15,000 <br /> 3.0. SITE CONCEPTUAL MODEL <br /> The site is located on essentially flat land that is developed into a car wash, convenience store and <br /> . fueling facility,the majority of the ground surface is covered by asphalt or concrete(Figure 2) Based <br /> on data collected to date from onsite and offsite soil borings and monitoring well installations,AGE <br /> has developed a site conceptual model for the release,migration and distribution of the contaminants <br /> in the subsurface <br /> Based on cone penetrometer test (CPT) logs and soil borings, the soil stratigraphy consists of an <br /> overall coarsening upwards sequence Below 85 feet below surface grade (bsg) to total depth <br /> (100 feet bsg), the sediments are dominantly stiff fine-grained sediments, with several thin, <br /> discontinuous clay and silt layers In the zone from 20 feet to approximately 85 feet bsg,the cross- <br /> sections generally depict thin,laterally continuous,mostly cemented sand layers,ranging in thickness <br /> from approximately 1 foot to approximately 5 feet, intercalated with fine-grained sediments, the <br /> frequency of occurrence of the sand layers appears to increase upwards as well as towards the south <br /> and east The upper 20 feet of soil generally consists of alternating silty to gravelly sand layers which <br /> fine upward to silts in the upper 7 feet <br /> Based on the soil stratigraphy, supplemented with pore-pressure data from the CPT logs, AGE <br /> developed a hydrogeologic model consisting of eight informal zones (Figure 3), a vadose <br /> (unsaturated)zone and seven hydrogeologic units(HUs), in general, low pore pressures associated <br /> with the sandy HUs would suggest more rapid pore-pressure dissipation (e g , higher hydraulic <br /> conductivities) <br /> Site assessment activities to date identified three areas where subsurface soil appears to be impacted <br /> Advanced GeoEnvironmentsl,Inc <br />
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