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PR0537902
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Last modified
5/27/2021 3:44:48 PM
Creation date
5/27/2021 3:30:40 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
COMPLIANCE INFO
RECORD_ID
PR0537902
PE
2953
FACILITY_ID
FA0021870
FACILITY_NAME
WILSON WAY PROPERTY
STREET_NUMBER
4001
Direction
N
STREET_NAME
WILSON
STREET_TYPE
WAY
City
STOCKTON
Zip
95205
APN
13202008
CURRENT_STATUS
01
SITE_LOCATION
4001 N WILSON WAY
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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Project No. 014-13157 <br />Page No. 2 <br />composite sample S26, S27, S28, S29. Although the concentrations of arsenic and cobalt exceeded the <br />ESLs and USEPA RSLs, the concentrations are within background levels' for naturally occurring arsenic <br />and cobalt (28 mg/kg and 22 mg/kg, respectively) in soil in California. <br />Formaldehyde does not appear to be present at the site over a large area as evidenced by the fact that only <br />two (2) samples (B1 at 10 feet bgs and composite sample S26, S27, S28, and S29) contained <br />concentrations of formaldehyde above the MDL of 0.60 mg/kg. Formaldehyde is not usually present in <br />soil because it volatilizes upon contact with soil. According to the Formaldehyde Counci12, <br />Formaldehyde does not accumulate in the environment either, because it is broken down within a few <br />hours by sunlight or by bacteria present in soil or water. Based on the low concentrations detected in soil <br />and the fact that the concentrations do not exceed the established regulatory screening level (USEPA <br />RSL), it does not appear that formaldehyde poses a significant risk to the environment in the areas <br />sampled. <br />Elevated concentrations of TPH-d and TPH-mo appeared to be localized in the soil/debris mounds and <br />former wood and metal debris area along the west central portion of the subject site. The only composite <br />sample (S26, S27, S28, and S29) concentrations that exceeded the ESLs for TPH-d and TPH-mo were <br />located near the western property line (see Figure 2). Although TPH-d and TPH-mo were detected in <br />discrete soil sample S-29A, the concentrations were well below those of the soil sample that composed <br />the composite sample S26, S27, S28. Thus, it appears that the elevated concentrations of TPH-d and <br />TPH-mo were localized in the area of composite sample S26, S27, S28. Krazan recommended that <br />additional soil samples be completed in this area to determine the vertical extent of TPH-d and TPH-mo <br />impacted soil. However, the client stated that they did not want to conduct additional soil sampling, but <br />instead indicated their desire to move forward with a limited excavation remedial approach in the area of <br />composite sample S26, S27, S28. <br />Client-Directed Scope <br />On January 17, 2014, the client requested that Krazan prepare a workplan to address the hydrocarbon- <br />impacted soil. <br />PROPOSED LIMITED EXCAVATION ACTIVITIES <br />The objective of this project is to conduct limited excavation activities that result in removal of the <br />hydrocarbon-impacted soil in the area of previous composite sample S26, S27, S28. <br />' Diamond, David, et. Al. 2009, Analysis of Background Distribution of Metals in Soil at Lawrence Berkeley National <br />Laboratory, June 2002, Revised April 2009. <br />2 Formaldehyde Council, Formaldehyde: Facts and Background Information, November 2007, <br />http:/ / formaldehydefacts.ore_base/pdf/ fact_sheets/11_01_07-FormadehydeFactsandBackgroundInformation.pdf <br />KRAZAN & ASSOCIATES, INC. <br />With Offices Serving the Western United States <br />014-13157 2014-3-28 WP for Excavation_Wilson Way Stockton FINAL
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