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ARCHIVED REPORTS_PHASE II ENVIRONMENTAL SITE ASSESSMENT
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ARCHIVED REPORTS_PHASE II ENVIRONMENTAL SITE ASSESSMENT
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Last modified
4/3/2020 2:20:39 PM
Creation date
4/3/2020 2:08:51 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
PHASE II ENVIRONMENTAL SITE ASSESSMENT
RECORD_ID
PR0527620
PE
2959
FACILITY_ID
FA0018715
FACILITY_NAME
LEARNER COMPANY, THE
STREET_NUMBER
2711
STREET_NAME
NAVY
STREET_TYPE
DR
City
STOCKTON
Zip
95203
APN
14503009
CURRENT_STATUS
01
SITE_LOCATION
2711 NAVY DR
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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W GR <br /> • Southwest, IIrnc. <br /> 11.0 DISCUSSION AND EVALUATION OF FINDINGS <br /> 11.1 Soil Conditions <br /> Many of the highest concentrations of contaminants were found in areas heavily used for <br /> stockpiling and processing recyclable metals, i.e., B-3, B-4, B-6 and B-13 (see Table 1). <br /> Metal concentrations above TTLC limits, PCB concentrations exceeding PRGs, as well as <br /> elevated levels of O&G, TPH-mo and, to a lesser extent, TPH-d were found in the one-foot <br /> samples from these borings. As previously documented, potential contaminants such as <br /> residual oils on engine blocks and electric capacitors containing PCBs have been mixed with <br /> the metals brought in for recycling. The levels of lead, zinc, copper, chromium and antimony <br /> detected in B-13 and the levels of lead and/or zinc found in B-3, B-4, B-6, B-8, B-9 and B-16 <br /> classify these soils as hazardous wastes. Mishandling of lead-acid batteries has been <br /> documented on site in the past, and is considered a potential source of the lead contamination. <br /> B-13, located adjacent to the railroad spur in an area historically used for stockpiling, <br /> processing and possibly loading materials onto railcars, contained the highest soil <br /> concentrations of PCBs and all but 3 of the CAM 17 metals. <br /> • CAM17 metals occur naturally in soils, and detectable concentrations do not necessarily <br /> indicate impact from human activities. Naturally occurring levels vary depending on soil type <br /> and environment, but can be estimated by examining nearby sites with no known history of <br /> metal contamination. Table 3 provides a comparison of the range of metal concentrations <br /> detected in soil samples from the Learner site with those of soil samples recovered by WGR <br /> approximately a year ago on a nearby Port of Stockton site. Data from this site was selected <br /> for comparison due to its proximity to the Learner site and because the samples were collected <br /> from locations where metal contamination would not be expected. Table 3 is not intended to <br /> provide conclusive data regarding metal background levels in the soil at the Port of Stockton, <br /> but to offer a basis for comparison and evaluation of the Learner data. <br /> As shown in Table 3, the upper ranges of all 17 metals are higher in the Learner samples than <br /> in the reference samples. With the exception of arsenic, beryllium, cobalt and vanadium, the <br /> upper metal ranges of the Learner samples are at least an order of magnitude greater. <br /> Comparison of Table 1 with Table 3 reveals that concentrations of these metals in most of <br /> the five-foot Learner samples fall within the ranges of those in the reference samples. <br /> However, in approximately 50% of the one-foot samples from the Learner site, the antimony, <br /> cadmium, copper, lead, mercury, nickel and zinc concentrations exceed the upper limits of the <br /> • <br /> 704. PRI.05 24 July 21, 2008 <br />
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