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3500 - Local Oversight Program
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PR0544495
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Last modified
5/28/2019 10:56:54 AM
Creation date
5/28/2019 10:43:31 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
WORK PLANS
RECORD_ID
PR0544495
PE
3528
FACILITY_ID
FA0003688
FACILITY_NAME
INDUSTRIAL RAILWAYS COMPANY - STOCKTON YARD
STREET_NUMBER
1645
STREET_NAME
CHEROKEE
STREET_TYPE
RD
City
STOCKTON
Zip
95205
APN
11910013
CURRENT_STATUS
02
SITE_LOCATION
1645 CHEROKEE RD
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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- REMEDIAL lON WORK PLAN, 1645 CHEROKEE R090, STOCKTON, CA <br /> 1.4 Regional Geologic Setting <br /> The subject property is situated at an elevation of 21 feet Mean Sea Level (MSL)and lies within the <br /> Great Valley Province, which is dominated by the alluvial basin of the Sacramento Valley. An area <br /> topographical map is provided as Figure 2. This region is composed primarily of Quaternary aged <br /> alluvium, mainly in the form of unconsolidated flood plain deposits. The main soil types that exist in <br /> this type of deposit are sand, silt, gravel and clay that are irregularly interstratified. The primary <br /> mechanism for sedimentation in this area has been fluvial. <br /> 1.5 Site Geologic Subsurface Conditions <br /> The subject property is underlain by layers of silt, sandy silt, and silty very fine grained sand (URS <br /> Greiner-Woodward Clyde Report dated September 1999). Groundwater has been encountered locally <br /> at approximate depths between 45-feet and 50-feet bgs and flows in a northeasterly trend. <br /> 2.0 PROPOSED REMEDIAL ACTION <br /> 2.1 Summary of Fieldwork and Rationale for Remedial Action <br /> Previous subsurface investigation efforts completed by URS Greiner-Woodward Clyde and Hydro <br /> Environmental Technologies between August 1999 and June 2004 have concluded that significantly <br /> detectable concentrations of residual petroleum hydrocarbon compounds remain in the native soils <br /> and/or shallow groundwater beneath the site. The residual contamination imbedded within the native <br /> soils located adjacent to the former tank excavation(s) have been determined to be a "secondary" <br /> source of ongoing contaminant migration and potential leaching of hydrocarbon constituents into the <br /> groundwater. <br /> Furthermore, evaluation of the geological conditions of the site and hydrocarbon concentrations -vs- <br /> time, indicates that additional mitigation of the contaminants of concern by in-situ means nor the <br /> �- ability of the affected soil and groundwater to naturally attenuate without interference is not effectual. <br /> Therefore, it is to this conclusion"that a remedial corrective action consisting of the removal of the <br /> accessible hydrocarbon affected soil considered as the secondary source, is hereby proposed. <br /> No definitive cleanup goals have been established for this site by any of the regulatory communities <br /> governing this site. Rather, it has been suggested by the Central Valley Regional Water Quality <br /> Control Board (CVRWQCB) and the SJCDEH that Risk Based Corrective Action (RBCA), risk <br /> �. screening guidance combined with residual mass contaminant levels be used to establish remedial <br /> goals. The American Society of Testing and Materials (ASTM) standard for RBCA, ASTM E-1739- <br /> 95 establishes provisions for determining "risk levels" which may increase the concentrations of <br /> specific constituents that may be safely left in place without producing a continual exposure concern <br /> to human health and/or the environment. Utilizing determining factors such as the presence of <br /> ecological receptors and site specific exposure pathways, and considering the residual contaminate <br /> mass and the threat potential of the contaminant to significantly impact groundwater, a realistic and <br /> reasonable remedial Site Specific Target Level(SSTL)can be established. <br /> The Preliminary Remedial Goal guideline established by the United Sates Environmental Protection <br /> Agency, Region IX for diesel in soil is 360 mg/kg. However, in consideration of the aforementioned <br /> factors and in consideration of the residual mass to produce a continual environmental liability and <br /> exposure concern, a SSTL of 750 mg/kg for the residual diesel in soil has been explicated and is <br /> hereby proposed for the remedial action to be completed at the subject site. <br /> 2 Sohm Environmental Solutions <br />
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