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ARCHIVED REPORTS XR0001839
Environmental Health - Public
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3500 - Local Oversight Program
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PR0544430
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ARCHIVED REPORTS XR0001839
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Last modified
5/7/2019 2:28:44 PM
Creation date
5/7/2019 2:20:33 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0001839
RECORD_ID
PR0544430
PE
3526
FACILITY_ID
FA0005370
FACILITY_NAME
PARMAR TEXACO
STREET_NUMBER
521
Direction
N
STREET_NAME
CHEROKEE
STREET_TYPE
LN
City
LODI
Zip
95240
CURRENT_STATUS
02
SITE_LOCATION
521 N CHEROKEE LN
P_LOCATION
02
P_DISTRICT
004
QC Status
Approved
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1 <br /> 1 BACKGROUND <br /> The following background summary is based on a review of the Preliminary Report Evaluation <br /> of Soil and Ground-Water Contamination(Applied GeoSystems [AGS], September 21, 1988)and <br /> the Preliminary Investigation and Evaluation Report (Geological Audit Services, Inc [GAS], 10 <br /> 1 August 1991). The site is located at 521 North Cherokee Lane in Lodi, California (Plate 1) <br /> GAS reported that Ramcon removed five underground gasoline storage tanks (USTs) from the <br /> site by on 5 February 1988. Soil samples collected from beneath the largest tank (10,000 <br />' gallons) contained total petroleum hydrocarbons as gasoline (TPHg). Based on these results, <br /> Ramcon retained AGS to further delineate the extent of soil contamination and the potential that <br /> groundwater had been impacted. <br /> tIn August 1988, Applied GeoSystems drilled four borings (B-1 to B-4, Plate 2) After drilling, <br /> Applied GeoSystems converted B-4 into a 2-inch diameter shallow-groundwater monitor well <br /> (NM-1) Soil samples were collected at five foot intervals from each of the borings and <br /> qualitatively field screened for volatile organics using a photoionization detector (PID). <br /> Relatively low but positive PID readings were recorded by AGS on the Log of Boring for B-3 <br />' throughout most of the drilled hole. The highest PID reading from B-3 was recorded at a depth <br /> of 20 feet below ground surface (bgs). Although the upper hole (0 to approximately 25 feet bgs) <br /> of B-4 recorded background type PID readings, the highest recorded PID reading was recorded <br /> in boring B-4 at approximately the groundwater surface(40 feet bgs). None of the soil samples <br /> were submitted for quantitative analysis. Bonng B-4 was advanced to approximately 60 feet bgs <br /> and completed as MW-1. Prior to development, AGS observed a sheen on water removed from <br /> MW-1. The sheen was again observed prior to presampling purging Upon attempting to <br /> sample MW-1, AGS measured an immiscible product layer of 0.5 inches. The sample was not <br /> analyzed. <br /> In April 1991, Mr. Ganzer (Gamer and Williams) retained Falcon Energy and GAS to further <br /> define the extent of groundwater impact by TPHg at the site In May 1991, GAS supervised <br /> the installation of two additional 4-inch diameter monitor wells (MW-2 and MW-3, Plate 2). <br /> Soil samples were collected at five foot intervals from each of the monitor well borings from <br /> 10 to 45 feet bgs. Field observations during the drilling of MW-2 indicated the potential <br /> presence of petroleum hydrocarbons from approximately 45 feet bgs to the total depth of 60 feet <br /> bgs. Field observations while drilling MW-3 indicated the potential presence of petroleum <br /> hydrocarbons from approximately 20 feet to the total depth of 60 feet bgs. The 30, 35, 40, and <br /> 45 foot soil samples from each of the wells was submitted for quantitative analysis of TPHg and <br /> benzene, toluene, ethylbenzene, and xylenes (BTEX) by EPA Methods 8015M and 8020 <br /> respectively. Each of the samples contained the requested analytes The 40 foot bgs soil sample <br /> from MW-2 was the most impacted with laboratory reported concentrations of TPHg (880 <br /> mg/kg), and BTEX- 9.2, 45, 14, and 77 mg/kg respectively) <br /> In June 1991, GAS surveyed the wells relative to a temporary benchmark and measured the <br /> 1 <br />
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