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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
Fields
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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Pre-Design Technical Su• -2- • 19 December 1996 <br /> DDRW-Sharpe <br /> The seven remaining VOC sites required further characterization to determine if they are a <br /> source areas for VOC in the ground water and warrant in-situ volatilization (ISV). Two <br /> additional sites were added to this characterization effort after a data review indicated that they <br /> may be degrading ground water. Information collected from the additional field work was to be <br /> used to determine if these areas required ISV or if they were in compliance with the ISV cleanup <br /> standard. The ISV standard as stated in Section 9.2.2 of the OU2 ROD, states that VOC <br /> contaminated soils will be remediated to be; 1) (a) protective of human health and the <br /> environment, and (b) not cause or threaten to cause concentrations in the ground water to exceed <br /> aquifer cleanup levels. <br /> All Parties agreed in the Sharpe ROD that a WE soil gas concentration at or below 350 ppbv <br /> would be considered to satisfy the ISV standard. However for those sites in which the soil gas <br /> concentrations in the vadose zone exceed 350 ppbv TCE, an interpretation of soil gas data is <br /> needed to evaluate what concentrations of VOCs will potentially reach the ground water at each <br /> VOC site. <br /> The technical and economic analysis presented in the Pre-Design Technical Summary is <br /> relevant only for areas where ISV has been operated and the VOC concentrations are below the <br /> ISV cleanup standard and Sharpe wants to proceed with remedial action. Therefore, the <br /> technical and economic analysis presented in section 5.2.2 is not appropriate at this time. This <br /> section should be replaced with an analysis to evaluate if concentrations of VOCs in the vadose <br /> zone could impact water quality and to determine if the standard under Section 9.2.2 has been <br /> met. <br /> 2. Based on 1987 data, Sites P-ID and P-5A (see Table 1)were targeted for ISV treatment because <br /> they were believed to be source areas for groundwater contamination found in plume 1 and <br /> plume 5. Omission of the areas from taking actions as required in the OU2 ROD will require <br /> preparation of a primary document that will provide greater detail and explanation into why the <br /> field results from this effort do not reflect the data collected in 1987. <br /> 3. It appears that the Pre-Design investigation was not conducted in some of the areas which <br /> showed the highest concentrations of VOCs. Soil gas investigations of VOC contaminated soil <br /> identified in the Pre-Design Technical Summary do not consistently match up with the areas of <br /> high concentration VOCs identified in the 1987 data. Specifically, sites P-113, P-4C and P5A <br /> identified during the 1987 investigation do not appear to have been adequately investigated <br /> during the Pre-Design field effort. Please incorporate the 1987 data into the VOC-contaminated <br /> site maps presented in the Technical Summary. Discrepancies between any locations of 1987 <br /> "hot spots" and the areas investigated in the Pre-Design Technical Summary, need to be <br /> explained. <br /> 4. The assumption in the ROD, that elevated levels of lead and chromium existed within 2 feet of <br /> the ground surface at locations where levels of chromium and lead exceeded the cleanup <br /> standard at depth, was not proven correct. Seven areas were reported to exceed the action levels <br /> in the South Balloon Area in the OU2- ROD on pages 28, 33 and 44. Soil samples collected as <br /> part of the RDFS detected the following concentrations. <br />
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