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2900 - Site Mitigation Program
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PR0508450
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
5/29/2019 11:58:23 AM
Creation date
5/29/2019 11:10:41 AM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0508450
PE
2960
FACILITY_ID
FA0008087
FACILITY_NAME
DDJC-TRACY
STREET_NUMBER
25700
STREET_NAME
CHRISMAN
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
25207002
CURRENT_STATUS
01
SITE_LOCATION
25700 CHRISMAN RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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• Following statistical evaluation of Phase I data, determine if additional Phase II <br /> sampling is required to determine the extent of metals and pesticides. <br /> 23. Pages 5-193 and 197, PCE in Areas 2 and 3 soil <br /> In the Phase II recommendation for both Areas 2 and 3, VOCs are not proposed for <br /> further investigation. EPA believes the number of soil borings drilled in the Phase I <br /> RI may be inadequate to delineate the lateral extent of VOCs. PCE was detected in <br /> the soil of Areas 2 and 3. In Area 2, the highest concentration was detected in a <br /> shallow soil sample at a depth of about 2 feet (SB-114). Of the samples collected <br /> from soil boring SB-117 in Area 3, the highest PCE concentration was detected in a <br /> shallow soil sample at a depth of 2 feet. Since deeper samples detected PCE at lower <br /> concentrations, it is less likely that the PCE originates from volatilization of the <br /> contaminated saturated zone and more likely it is from a shallow source in the vadose <br /> zone or a surface spill. <br /> • During the Phase II RI, the use of soil gas surveys should be performed to <br /> delineate the lateral extent of contamination around the spots where the highest <br /> PCE concentrations were detected. Also, vertical profile surveys of soil VOC <br /> vapor concentrations may locate potential vadose zone sources. <br /> 24. Section 6, 'Preliminary Risk Evaluation" <br /> Section 6 generally describes the approach to be used for the baseline risk assessment. <br /> However there are a number of areas/issues which require further clarification or <br /> elaboration. Further, it is not clear how 'conclusions" presented in this preliminary <br /> Risk Evaluation will relate to the draft BRA Work Plan (due to the regulatory agencies <br /> on February 12, 1994). <br /> a. Current and future land use conditions have not been clearly distinguished. In <br /> a baseline risk assessment, it is necessary to provide estimates for both current <br /> and expected future land uses. If existing and future land use conditions are <br /> anticipated to be the same, this needs to be discussed. This is important <br /> because the potential exposure pathways shown in the site conceptual model <br /> (Figure 6-1) may differ for current and future land use scenarios. <br /> • Please distinguish between current and future land uses. <br /> b. Potential receptors, not included in the site conceptual model (Figure 6-1) are <br /> trespassers, visitors, and attendees at the on-site day-care center. <br /> • These receptors should be considered. <br /> C If groundwater at the site is considered potable or potentially potable, other <br /> EPA 14FEB94 a/10 <br />
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