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2900 - Site Mitigation Program
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PR0545445
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Last modified
3/3/2020 4:40:31 PM
Creation date
3/3/2020 4:20:39 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
COMPLIANCE INFO
RECORD_ID
PR0545445
PE
2961
FACILITY_ID
FA0025798
FACILITY_NAME
CALIFORNIA ARMY NATIONAL GUARD
STREET_NUMBER
333
Direction
N
STREET_NAME
WASHINGTON
STREET_TYPE
ST
City
LODI
Zip
95240
APN
04123045
CURRENT_STATUS
02
SITE_LOCATION
333 N WASHINGTON ST
QC Status
Approved
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Diesel Impacted Soil Removal Report May 2010 <br /> California Army National Guard Armory <br /> Lodi, CA <br /> 3.0 DESCRIPTION OF REMOVAL ACTIVITIES <br /> The following discussion summarizes activities related to subsurface clearance,pre-characterization <br /> sampling, diesel fuel impacted soil excavation and disposal, confirmation sampling, and site restoration. <br /> All activities were performed in substantial accordance with procedures outlined in the December 2009 <br /> Workplan. <br /> 3.1 SITE CLEARANCE <br /> On January 28,2010, OTIE coordinated clearance from underground utilities in the immediate vicinity of <br /> the diesel spill using Precision Locating(Precision), a California-licensed underground utilities-locating <br /> contractor. The purpose of this procedure was to ensure clearance from underground utility lines (e.g., <br /> water, sewer,telecommunications, cable television, electric, gas, etc.)that might be impacted by either <br /> pre-characterization sampling activities or by excavation activities to be performed subsequent to pre- <br /> characterizing soils in the area. <br /> In accordance with California law,the proposed excavation area was properly marked prior to notifying <br /> Underground Service Alert(USA) about proposed subsurface excavation activities. Following USA <br /> notification,Precision performed a geophysical survey of the pre-characterization and proposed <br /> excavation area footprint.No subsurface utilities were identified in the immediate area of the proposed <br /> excavation area footprint by either USA or Precision. <br /> Photographs documenting site clearance activities are presented with the photographic log in Appendix B. <br /> 3.2 PRE-CHARACTERIZATION SAMPLING <br /> On January 28,2010, following underground utilities clearance as described above, OTIE collected nine <br /> pre-characterization soil samples at depths ranging from 12 to 40 inches below ground surface (bgs). The <br /> approximate locations of these samples (LODI-SO-01 through LODI-SO-09) are shown in Figure 3 <br /> (Appendix A). The locations for these samples were based on visual inspection and field judgment of <br /> impacted soils. The objective of the sampling effort was to determine an accurate estimate of vertical and <br /> lateral extent of impacts so that the volume of soils requiring excavation could be quantified. <br /> OTIE collected soil samples from within the visibly stained area and up to 2 feet beyond the visible edges <br /> of that area using a hand auger which was decontaminated prior to collection of each sample. Soil <br /> samples were placed into sterile glass containers,preserved in accordance with analytical methodology <br /> protocols, and submitted under chain-of-custody documentation to Curtis &Tompkins, Ltd. (C&T), an <br /> analytical laboratory having California Environmental Laboratory Accreditation Program(ELAP) and <br /> USACE ELAP certifications. C&T analyzed the samples for extractable petroleum hydrocarbons, or Total <br /> Petroleum Hydrocarbons as Diesel Fuel(TPH-D)by gas chromatography(GC)using United States <br /> Environmental Protection Agency(EPA)Method 8015B. <br /> Consistent with the strategy in the Workplan, a threshold of 100 milligrams per kilogram(mg/kg)was <br /> used as a cleanup goal for TPH-D. Although not strictly applicable to this site,this threshold has <br /> historically been used in relation to the California Leaking Underground Fuel Tank(LUFT)protocol for <br /> managing and remediating LUFT sites and represented a reasonable point of reference concentration for <br /> comparison of results. In accordance with this strategy, soil shown via pre-characterization sampling to <br /> exceed the 100 mg/kg threshold would be excavated and disposed. <br /> Photographs and field notes documenting pre-characterization sampling activities are presented in <br /> Appendices B and C,respectively. Pre-characterization sampling results are presented in tabular form in <br /> Section 4.1. <br />
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