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ARCHIVED REPORTS_XR0008138
EnvironmentalHealth
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2900 - Site Mitigation Program
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PR0504943
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ARCHIVED REPORTS_XR0008138
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Last modified
6/18/2020 1:04:49 PM
Creation date
6/18/2020 12:10:53 PM
Metadata
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EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0008138
RECORD_ID
PR0504943
PE
2951
FACILITY_ID
FA0004032
FACILITY_NAME
AMERICAN MOULDING & MILLWORK (FRMR)
STREET_NUMBER
2801
STREET_NAME
WEST
STREET_TYPE
LN
City
STOCKTON
Zip
95204
APN
11709001
CURRENT_STATUS
02
SITE_LOCATION
2801 WEST LN
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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removed A 1500-gallon concrete septic tank was then excavated and broken up, and portions of the <br /> asphalt pavement were removed to provide access to the planned excavation areas All demolition debris <br /> was removed and disposed of at a Class III landfill <br /> 4 2 2 Soil Excavation and Sampling <br /> Estimates of the lateral and vertical extent of soil impacted from the underground tanks were <br /> estimated in previous investigations (JHKA, 1987 and Dames & Moore, 1988) It was apparent that soils <br /> had been impacted by TPH/D from 10 to 30 feet bgs on the east end of the former maintenance shop in <br />' the vicinity of the former 500 gallon waste oil tank Soils to the west of the shop, in the vicinity of the <br /> 10,000 gallon diesel UST had been impacted from 10 to 20 feet bgs (Dames & Moore, 1988) All <br />' previous investigations suggested that impacted soil extended directly below the former maintenance shop <br /> The approximate extent of the excavations along with geologic cross sections are presented in Figure 4 2 <br /> and 43 A VA1n,5�f�� �� � <br /> All excavation activities were conducted under the th and Safety Plan presented in the Soil <br /> t Remediation and Groundwater Monitoring Workplan es& Moore, 1990) which was consistent with <br /> the state and federal Occupational Safety and Heal thee <br /> Dames & Moore Site Safety Officers <br /> conducted "tailgate" Health and Safety meetings wi l subcontractors prior to the start of each day's <br /> activities Both excavations and stockpiled soils in the biotreatment cell were monitored for organic <br /> vapors using an organic vapor meter (OVM) as directed by the Health and Safety Plan OVM readings <br /> greater than 50 ppm would cause all workers in the vicinity to use personal protective breathing <br /> apparatus <br /> Excavated soils were screened for TPHID in the field by using a thin layer chromatography <br /> (TLC) method to rapidly assess TPHID concentrations Soils which were stained or gave detectable <br />' OVM readings were transported directly to the biotreatment cell Soils with TLC values for TPHID <br /> greater than 10,000 mg/kg were also transported directly to the biotreatment cell Soils with lower TLC <br /> values, were segregated into two stockpiles Soils with TLC-TPH/D concentrations less than 100 mg/kg <br /> were placed in a stockpile to the south of the site designated OBC (Figure 4 4) Soils with TLC-TPHID <br /> from 100 to 10,000 mg/kg were stockpile adjacent to the eastern excavation, labeled OB2 (Figure 4 4) <br /> All stockpiled soil was resampled and analyzed by a California Department of Health Services (DHS) <br /> certified laboratory <br />' Excavation of impacted soil and bioremediation treatment cell construction were performed by <br /> CKC, Inc of Paso Robles, California between June 11 and June 20, 1990 Excavation at the west end <br /> of the former maintenance building was performed with a track-mounted hydraulic excavator When all <br /> stained soils appeared to be removed, and each of the four walls then the walls and the floor of the <br /> SAC36 046 16 <br />
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