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ARCHIVED REPORTS XR0003988
Environmental Health - Public
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3500 - Local Oversight Program
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PR0544084
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ARCHIVED REPORTS XR0003988
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Last modified
2/1/2019 3:07:44 AM
Creation date
1/31/2019 4:33:27 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0003988
RECORD_ID
PR0544084
PE
3500
FACILITY_ID
FA0005447
FACILITY_NAME
LODI READY MIX & BLDG MATERIAL
STREET_NUMBER
851
Direction
E
STREET_NAME
LODI
STREET_TYPE
AVE
City
LODI
Zip
95240
CURRENT_STATUS
02
SITE_LOCATION
851 E LODI AVE
P_LOCATION
02
P_DISTRICT
004
QC Status
Approved
Scanner
TMorelli
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EHD - Public
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' Lodi Ready Mix Page 4 <br /> Site Closure Report <br /> Project No.93.1 <br /> May 12, 1995 <br /> i <br />' In summary, Y Y laboratory analyses of soil samples tested from SB-1 (27, 32', 37', <br /> & 42') indicate that diesel and gasoline range petroleum hydrocarbons are not <br /> present in concentrations above detection limits. The following sections <br /> describe the procedures of the subsurface investigation. <br />' 2.1 Soil Boring Installation <br /> On July 6, 1993, Geological Technics Inc. and well drillers Osterberg and <br />' Stewart Inc. mobilized hollow stem auger and wire line coring equipment to <br /> the site. A single soil boring, SB-1, was advanced to a depth of 42 feet below <br />' ground surface directly south of the former UST excavation (Figure 2). Mr. <br /> Mike Collins of the PHS/EHD was on site to observe the drilling activity. <br /> During drilling, soil samples were collected for geological and analytical <br />' evaluation at 5 foot intervals starting at ten feet below ground surface to the <br /> total depth of 42 feet. Soil samples for laboratory analyses were collected in <br />' brass liners using a 2.5 inch modified California split spoon sampler. All soil <br /> samples were sealed with aluminum foil, capped, labeled and placed in a <br /> cooler at 4° Celsius for transport to the laboratory following Chain of Custody <br /> protocol. <br /> 2.2 Field Screening Methods <br /> Because every soil sample collected was not submitted for laboratory analysis, <br /> a screening process was used to gather additional information through field <br /> ' observation noting sediment type, especially grain size and clay content, <br /> moisture content, visible evidence of contamination, i.e., color change due to <br /> reduction of iron or discoloration from hydrocarbons and other pollutants, <br /> ' and the readings above background on a organic vapor meter (OVM). The <br /> OVM is a field portable photo ionization detector that uses a 10.2 eV lamp to <br /> detect compounds with ionization potential below 10.2 eV (hydrocarbon <br /> ' range). No reading above background (background = 1-2 ppm) was observed <br /> for the screened samples. <br /> ' 2.3 Soil Sample Analyses <br /> Soil samples collected from the 27, 32; 37, and 42 foot intervals were <br /> ' submitted to GeoAnalytical Laboratories of Modesto for analyses. These <br /> samples were tested for benzene, toluene, total xylenes and ethylbenzene <br /> ' (BTEX) by EPA method 8020, Total Petroleum Hydrocarbons as Gasoline <br /> (TPH-G) and Total Extractable Petroleum Hydrocarbons (TEPH) by EPA <br /> method 8015 modified. <br /> 1 <br />
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