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2900 - Site Mitigation Program
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PR0542459
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Entry Properties
Last modified
6/11/2021 10:48:47 AM
Creation date
6/11/2021 10:12:42 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0542459
PE
2965
FACILITY_ID
FA0024400
FACILITY_NAME
CAARNG STOCKTON FMS #24
STREET_NUMBER
8010
Direction
S
STREET_NAME
AIRPORT
STREET_TYPE
WAY
City
STOCKTON
Zip
95206
APN
17726004
CURRENT_STATUS
01
SITE_LOCATION
8010 S AIRPORT WAY
P_LOCATION
01
QC Status
Approved
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SJGOV\dsedra
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EHD - Public
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Type II Work Plan - Addendum <br />UXO Construction Activities and Soil Removal Action <br />Preliminary Assessment/Site Investigation Update <br />California Army National Guard Facility <br />Stockton, California <br />Contract No GS-00E-007L/Task Order W91238-05-F-0084 <br />Version 2.0 <br />liquids. Based on the findings of potential soil contamination, and discussions with CA ARNG <br />representatives, soil samples were collected from the south excavation for laboratory analysis. <br />Figure 3 shows the former excavation and sample locations. <br />Laboratory analysis of the soil samples detected low concentrations of petroleum hydrocarbons <br />as gasoline (TPH-G, 1.26 mg/kg) and diesel (TPH-D, 115 mg/kg), and trace concentrations (less <br />than one mg/kg) of 11 volatile organic compounds (VOCs). The detected VOCs were non- <br />chlorinated and are typically found with fuel hydrocarbons. A total of 13 metals were also <br />identified above the method detection limit. Of these, arsenic and vanadium were detected at <br />concentrations exceeding the US EPA Preliminary Remediation Goal (PRG) for Industrial Soil <br />(US EPA, 2004). <br />Concentrations of arsenic and vanadium detected at the Site are believed to be representative of <br />background conditions. Studies performed in California (Kearney, 1996) and the western United <br />States (Shacklette and Boerngen, 1984) indicate that the detected concentrations fall well within <br />observed ranges and are near the mean expected value. Similar concentrations of these metals <br />were also detected at the copper sulfate contaminated soil removal site and at borings B11 and <br />B19 located east of the CSMS. <br />All visible, exposed construction debris and contaminated soil was removed from the excavation <br />and properly containerized for disposal. The excavation was backfilled with clean fill. <br />The northwest anomaly was excavated to a depth of four feet bgs, and the excavated material <br />checked thoroughly for debris. No buried objects were detected. <br />The northeast anomaly was excavated to a depth of seven feet bgs. A metal grounding/hold- <br />down strap was unearthed and was removed. <br />During May 2006 a geophysical investigation was performed at the south excavation. A report <br />of the findings of the geophysical investigation (Versar, Inc., 2006) identified the potential extent <br />of buried material associated with the former suspected CS (tear gas) excavation. A copy of the <br />geophysical report is included as Appendix B. <br />The findings of the report identified two anomalies in the unconsolidated fill west of the former <br />excavation. The estimated surface extent of the anomalies is shown on Figure 4. Please note <br />that the layout of the anomalies is based on two dimensional mapping. The length and depth are <br />indicated in the Geophysical Report, but the width of the anomalies is estimated. Based on these <br />data, Versar estimates between 300 and 400 cubic yards (bank yards) of potentially contaminated <br />soil and debris may be present. Figure 5 depicts the proposed excavation area. <br />104700 4965 300 Page 1-2 April 2007
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