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ARCHIVED REPORTS XR0011650
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0521409
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ARCHIVED REPORTS XR0011650
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Last modified
6/20/2019 1:39:58 PM
Creation date
6/20/2019 11:44:54 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0011650
RECORD_ID
PR0521409
PE
2950
FACILITY_ID
FA0014531
FACILITY_NAME
PLYMOUTH ROAD STORM DRAIN PROJECT
STREET_NUMBER
0
STREET_NAME
COUNTRY CLUB
STREET_TYPE
BLVD
City
STOCKTON
Zip
95204
CURRENT_STATUS
01
SITE_LOCATION
0 COUNTRY CLUB BLVD
QC Status
Approved
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EHD - Public
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k'q KLEINFELDER <br /> Country Club Boulevard and Pershing Avenue (south of former Shell Station) Total lead <br /> concentrations ranged from 0 24 mg/l to 0 97 mg/l in groundwater samples collected in the <br /> ' Pershing site area <br /> 43 COMPARISON TO REGULATORY LIMITS (SOIL) <br /> The soil sampling analytical results were compared to the Total Threshold Limit Concentration <br /> ' (TTLC) and Soluble Threshold Limit Concentration (STLC) regulated levels as expressed in <br /> California Code of Regulations 22CCR§66261 24 and/or the Residential U S EPA Region IX <br /> Preliminary Remediation Goals (PRGs), dated October 1, 2002 <br /> ' were selected because the are typically more stringent PRGs are <br /> PRGs for residential sites y yp y $ <br /> contaminant concentrations in environmental media (i a soil, air, water), calculated by the U S <br /> ' EPA, that can be used as screening tools to evaluate a site for potential human health risks <br /> PRGs are calculated using standard assumptions and are specific for land use conditions (e g <br /> residential or industrial) The chemical concentrations calculated by the U S EPA typically <br /> correspond to a fixed Ievel of risk (usually 10"6, or 1 in 1,000,000 cancer risk, or a non-cancer <br /> hazard quotient of 1) for soil, air, and water The following exposure pathways were accounted <br /> ' for in the PRG calculation for soils assuming residential land use <br /> • Ingestion <br /> • Inhalation of particulates <br /> • Inhalation of volatiles <br /> • Dermal (skin) absorption <br /> For the inhalation pathways, volatilization factors and particulate emission factors are used to <br /> estimate exposure due to emissions from soil to air For the dermal absorption pathway, a 10% <br /> ' skin absorption factor was used to calculate the PRGs for the constituents of concern at the <br /> subject site This factor assumes the dermal dose is equal to an adult's ingestion dose <br /> If contaminant concentrations at the subject site exceed the estimated PRG values and the <br /> exposure pathways used to calculate those PRGs are inappropriate for the site, additional site <br /> evaluations, such as an evaluation of background levels, supplementary sampling and <br /> ' calculations using site-specific data may be necessary <br /> From the requested suite of analyses (See Section 3 3) only a single analyte, total lead was <br /> ' detected in soil samples in the Mission and Pershing areas Total lead was detected in each of <br /> the fifteen soil samples at concentrations ranging from 3 3 to 7 8 mg/kg at approximate depths of <br /> ' 9 % feet bgs <br /> The upper limit of the range of concentrations for total lead detected did not exceed the Total <br /> Threshold Limit Concentration (TTLC) Regulated Level (1,000 mg/kg) for classification of total <br /> tlead as a hazardous waste per California Code of Regulations 22CCR §66261 24 Additionally <br /> these concentrations were not greater than 10-times the Soluble Threshold Limit Concentration <br /> ' — (STLC) Regulated Level (50 mg/kg) for lead as expressed in 22CCR §6626124 The factor of <br /> 28699 E01 /STOIR191 Page 10 of 16 <br /> July 21,2003 <br /> Gopynght 2003,Kleinfelder,Inc <br /> 1 <br />
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