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SU0012952 SSCRPT
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SU0012952 SSCRPT
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Last modified
1/27/2020 10:03:22 AM
Creation date
9/4/2019 11:45:19 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSCRPT
RECORD_ID
SU0012952
PE
2626
FACILITY_NAME
UP-7-95
STREET_NUMBER
2705
Direction
W
STREET_NAME
COUNTRY CLUB
STREET_TYPE
BLVD
City
STOCKTON
Zip
95204-
APN
12308029
ENTERED_DATE
1/16/2020 12:00:00 AM
SITE_LOCATION
2705 W COUNTRY CLUB BLVD
P_LOCATION
99
P_DISTRICT
001
QC Status
Approved
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SJGOV\sballwahn
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FilePath
\MIGRATIONS\C\COUNTRY CLUB\2103\SSC RPT.PDF
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EHD - Public
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TERRA VAC <br /> 5. Representative Contaminant Concentrations <br /> The representative contaminant concentrations are calculated by the GSI/RBCA model <br /> from actual soil and groundwater sample analytical results collected over a period of time. <br /> These concentrations represent mean contaminant concentrations beneath the site. <br /> Hydrocarbon concentration data from soil samples collected from exploratory boxings at <br /> the site were used to establish a representative hydrocarbon concentrations for the risk <br /> assessment modeling. For the purposes of arriving at conservative representative <br /> hydrocarbon concentrations, analytical results less than reporting limits were omitted. The <br />{ remaining soil sampling data were entered into the model to calculate representative <br />+' hydrocarbon concentrations in soil beneath the site. <br /> If soil or groundwater representative contaminant concentrations are below RBSL or SSIL <br /> concentrations calculated by the GSI/RSCA model, no significant health risk is present. <br /> 5.1 Exposure Pathway Characterization and Evaluation <br /> To pose a risk to human health or the environment three components must be present at <br /> the site: an affected source medium, mechanism of contaminant transport, and a current <br /> or potential receptor. To develop risk-based cleanup goals, reasonable mechanisms for <br /> contaminant transport from the source zone to a point .of contact with a human <br /> population or ecological resource must first be identified. Tier One and Tier Two RSCA <br /> evaluations consider several standard exposure pathways for contaminant migration from <br /> the source to the receptor via air, soil, groundwater, or surface water transport <br /> mechanisms. These exposure pathways can be grouped according to the medium of <br /> exposure. Figures 10 and 11 illustrate a Baseline Exposure Flowchart and Typical <br /> Exposure Pathways For Tier 1 and Tier 2 Evaluations. <br />' Potential exposure pathways at the site are 1) Ingestion of impacted soil, 2) Dermal contact <br /> with impacted soil, 3) ingestion of impacted groundwater, and 4) inhalation of <br /> hydrocarbons volatilized from vadose zone soils and/or groundwater to outdoor and indoor <br /> air from sources beneath the site. Surface soils (<3 feet bgs) do not contain detectable <br /> concentrations of benzene, and so ingestion of impacted soil and dermal contact with <br /> impacted soil are unlikely exposure pathways. As there were no water production wells <br /> identifiedand all residents within the survey area were found to be on the municipal <br /> water supply, ingestion of groundwater is eliminated as a potential exposure pathway. <br /> Available data indicate that vadose zone soils may be a source for the volatilization of <br /> hydrocarbons to outdoor or indoor air. Available data also indicate that groundwater is a <br /> potential source of volatilization to outdoor or indoor air. Inhalation. of volatilized <br /> hydrocarbons from soil and groundwater, therefore, is a potential exposure pathway. <br /> 6. GSIIRBCA TIER ONE MODEL EVALUATION <br /> Terra Vac applied the GSIIRBCA Tier One evaluation using default parameters to develop <br /> site specific RBSLs that apply to future onsite commercial usage and current adjacent site <br /> residential scenarios. <br /> Project 30-0212 8 coaltonl30-02121capVev51cap-rev5Am <br /> July 15, 1998 _�,. <br />
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