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ARCHIVED REPORTS_XR0005144
EnvironmentalHealth
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2900 - Site Mitigation Program
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PR0535112
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ARCHIVED REPORTS_XR0005144
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Last modified
9/24/2020 12:23:22 AM
Creation date
3/17/2020 2:57:41 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0005144
RECORD_ID
PR0535112
PE
2957
FACILITY_ID
FA0020296
FACILITY_NAME
CHAPIN BROTHERS INC
STREET_NUMBER
1766
STREET_NAME
MONTE DIABLO
STREET_TYPE
AVE
City
STOCKTON
Zip
95203
APN
13505050
CURRENT_STATUS
01
SITE_LOCATION
1766 MONTE DIABLO AVE
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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each approximate 50 cubic yards of stockpiled soil These three samples were coin osited b the <br /> • PP Y P P P Y <br /> laboratory for analysis Results of these analyses indicated that only very low concentrations of TPHg <br /> and BTEX(no benzene) remained in the soil Based on the laboratory test results, the San Joaquin <br /> County Air Pollution Control District allowed uncontrolled soil aeration to mitigate the remaining <br /> petroleum hydrocarbons in the soil The soil was spread over the surface of an access road on the <br /> property and allowed to aerate <br /> On November 26, 1993, soil sample composites were collected from the aerated stockpile in the same <br /> manner as before A composite sample consisting of three individual samples was also collected from <br /> the substrate beneath the formerly contaminated soil to verify that contaminants had not migrated <br /> to soil below the aerated stockpiled soil Laboratory analyses of these samples indicated that TPHg <br /> and BTEX concentrations had been reduced to less than the nummum detection limits of the <br /> laboratory methods (Table 2) <br /> 5.0 FIELD INVESTIGATION <br /> The results of our field investigation indicated that subsurface soil and groundwater is significantly <br /> contaminated with TPHg and BTEX beneath the site and to a somewhat lesser degree offsite mainly <br /> toward the southwest The vertical and lateral extents of soil and groundwater contamination were <br /> defined during the plume delineation work, and the remediation feasibility studies at the site indicated <br /> that the hydraulic conductivity of the shallow groundwater-bearing zone is low, although vadose zone <br /> soil permeability appears relatively high <br /> 5.1 Soil Boring <br /> SEACOR drilled four initial soil borings at the site Two of the borings were located on the subject <br /> property and two of the borings were located offsite (Figure 3) Three of the borings (B2 through <br /> B4)were drilled to total depths of approximately 35 feet below grade (approximately 14 feet below <br /> the groundwater surface) for the purpose of installing 2-mch diameter groundwater monitor wells <br /> The remaining boring(B5) was drilled to approximately 25 feet below ground surface to install a 4- <br /> inch diameter vapor extraction well The proposed locations of these soil borings/monitor wells were <br /> selected to represent groundwater in the assumed upgradient, downgradient, cross-gradient directions <br /> (Figure 3) <br /> Drilling was performed by Geo-Environmental Drilling (Lic C57 9676923) of Yuba City, California <br /> using a CME55 drilling ng equipped with 8-inch hollow-stem augers on December 27 and 28, 1993 <br /> The augers were steam cleaned prior to drilling each boring to prevent downhole or cross-boring <br /> contamination Flowing sands were encountered in boring B2/MW2 at approximately 20 feet below <br /> ground surface where the shallow groundwater-bearing zone existed Directly beneath this 1- to 2- <br /> foot thick groundwater-bearing zone, a medium gray silty clay was encountered, which apparently <br /> has provided an effective aquiclude against the downward migration of contaminants <br /> SEACOR 014-01-1 par <br /> 5 <br />
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