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2900 - Site Mitigation Program
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PR0535111
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Last modified
9/10/2020 11:04:44 AM
Creation date
9/10/2020 10:47:49 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
COMPLIANCE INFO
RECORD_ID
PR0535111
PE
2959
FACILITY_ID
FA0020295
FACILITY_NAME
GORDON
STREET_NUMBER
1085
Direction
S
STREET_NAME
UNION
STREET_TYPE
RD
City
MANTECA
Zip
95337
APN
22224012
CURRENT_STATUS
01
SITE_LOCATION
1085 S UNION RD
P_LOCATION
04
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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ARCADIS Mr. McKinley Lewis, Jr. <br /> April 20, 2011 <br /> Three shallow soil boring locations (B-8, B-29, and B-43)were identified as "hot <br /> spots" during the PEA investigation based on shallow sample results (0 to 0.5 foot <br /> below ground surface [bgs]). <br /> Lead was detected in soil samples B-29(1,600 milligrams per kilogram [mg/kg])and <br /> B-43 (1,300 mg/kg)at concentrations above California's Total Threshold Limit <br /> Concentration (TTLC)of 1,000 mg/kg. These samples were subsequently analyzed <br /> for the Soluble Threshold Limit Concentrations (STLC)for lead. The STLC criterion <br /> for lead is 5 micrograms per liter(mg/1). Lead was not detected above the TTLC in <br /> B-8 (680 mg/kg); however, the STLC lead result for B-8 indicated a concentration of <br /> 49 mg/I. Soluble lead was also detected at 67 mg/I in sample B-29. Soluble lead was <br /> not detected above the STLC in B-43 (2.4 mg/1). <br /> The dioxin 95 percent(%) Upper Confidence Limit (UCL)calculated for the Site <br /> based upon five soil samples was 5.75 picograms per gram (pg/g or parts per trillion <br /> [ppt]), slightly above the California Human Health Screen Level (CHHSL)of 4.6 ppt. <br /> The ash sample collected from within the silo(S-3) indicated a dioxin total toxic <br /> equivalency of 26.9. This result was not included in the calculation because the <br /> sample was obtained from a different media and the ash is contained within the silo. <br /> Dioxin 95 %UCL for the site soil was slightly above the CHHSL; however, it does not <br /> appear to be a significant concern except for the ash material within the silo. <br /> A screening number of 12 mg/kg was selected for evaluating arsenic in soil for this <br /> Site based on the background plot from the data and assumed past agricultural use <br /> of the Site. In the Interim Guidance for Sampling Agricultural Properties(Third <br /> Revision) by the DTSC California Environmental Protection Agency, dated August 7, <br /> 2008 (DTSC 2008b), the DTSC cites results of soil sampling at multiple former <br /> agricultural sites for proposed school locations. The document references a <br /> screening level of 12 mg/kg for school locations. <br /> Eleven shallow soil samples (B-7-0.5, B-8-0.5, B-9-0.5, B-11-0.5, B-18-0.5, B-21-0.5, <br /> B-22-0.5, B-26-0.5, B-29-0.5, B-31-0.5, and B-48-0.5)collected and analyzed at the <br /> Site indicated arsenic concentrations above background ranging from 16 to 59 <br /> mg/kg. Elevated arsenic concentrations appear to be relatively shallow based on <br /> deeper soil samples analyzed from soil borings B-7-2.0 (9.8 mg/kg) and B-11-2.0 <br /> (8.5 mg/kg)with concentrations below the background. Areas of elevated arsenic <br /> concerns are depicted on Figure 1. Based on the analytical sampling and results, <br /> arsenic detected at the Site above background concentrations is shallow and defined <br /> in discrete areas. <br /> Page: <br /> Final PEA Work Plan Addendum-Apr71-RV009808.doc 4/11 <br />
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