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ARCHIVED REPORTS XR0008707
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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EL DORADO
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1502
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2900 - Site Mitigation Program
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PR0540300
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ARCHIVED REPORTS XR0008707
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Entry Properties
Last modified
9/14/2020 12:51:17 AM
Creation date
7/18/2019 4:52:10 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0008707
RECORD_ID
PR0540300
PE
2960
FACILITY_ID
FA0023037
FACILITY_NAME
FORMER UNOCAL NO 4409
STREET_NUMBER
1502
Direction
N
STREET_NAME
EL DORADO
STREET_TYPE
ST
City
STOCKTON
Zip
95204
APN
12708018
CURRENT_STATUS
01
SITE_LOCATION
1502 N EL DORADO ST
P_LOCATION
01
QC Status
Approved
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EHD - Public
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Mr Ed Ralston <br /> April 16, 2001 <br /> . Page 3 <br /> was updated with appropriate field personal and subcontractor information The field staff and <br /> contractors reviewed the SSP before beginning field operations at the site <br /> The specific scope of work is discussed below <br /> • Monitoring Well Installation. Three on-site deep groundwater monitoring wells <br /> (MW-5 through MW-7) were installed at the general locations shown on Figure 3 The <br /> wells are 2-inch diameter and were installed to a total depth of approximately 80 feet <br /> bgs The wells were constructed with 10-foot screen intervals placed from 70 to 80 feet <br /> bgs Off-site well MW-8, proposed for installation in the Harding Way, median was not <br /> installed because of subsurface utility corridors located beneath the median <br /> • Soil Selection and Analysis. Soil samples were collected every five vertical feet in the <br /> borings using a modified California split-spoon sampler Soil samples for laboratory <br /> analysis were selected from the saturated zone for vertical delineation of soil impacts <br /> based upon field screening results and depth intervals previously assessed A total of <br /> 12 soil samples were submitted to a California State-certified laboratory and analyzed <br /> for the presence of total petroleum hydrocarbons quantified as gasoline (TPH-g), <br /> benzene, toluene, ethylbenzene, and total xylenes (BTEX), and methyl tertiary-butyl <br /> ether(MtBE) by EPA Methods 8015 Modified and 8020 Samples with MtBE <br /> detection by EPA Method 8020 were confirmed by EPA Method 8260 No additional <br /> oxygenate analysis of soil samples was conducted based upon non-detection of Di- <br /> isopropyl ether(DIPE), Ethyl tert-butyl ether(ETBE), tert-Amyl methyl ether(TAME) <br /> and tert-Butyl alcohol (TBA) in over-excavation soil samples at depths of 11 and 13 <br /> feet bgs Sampling and analytical methods are presented in Attachment A <br /> • Groundwater Analysis. Gettler Ryan Inc developed and sampled the three deep <br /> monitoring wells in conjunction with the First Quarter 2001 groundwater monitoring <br /> event Groundwater samples were submitted to a California State-certified laboratory <br /> for analysis Groundwater samples were analyzed for the presence of TPH-g, BTEX, <br /> and for five oxygenates (MtBE, DIPE, ETBE, TAME and TBA), 1,2-Dicholorethane <br /> (1,2-DCA), and Ethylene dibromide (EDB) using EPA Methods 8015 Modified, 8020 <br /> and 8260, respectively <br /> • Well Surveying.Upon completion of well construction, the wells were surveyed by a <br /> licensed surveyor for location and elevation relative to mean sea level <br /> FINDINGS <br /> Subsurface Conditions <br /> Soils encountered during drilling (maximum explored depth of approximately 80 feet bgs) <br /> consisted of interbedded sands, silty sands, sandy silts, silty clays and clayey silts (Figure 2) Silts <br /> and clays with interbedded lenses of silty sand and sand are present to depths of approximately <br /> 45 feet bgs Silt and clay underlie the overexcavation area beneath the former dispensers At <br /> NlrancfpITrojectsTrolects1911\011UA101021911011rpt2 doe <br />
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