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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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8. Section 1 .2, Post ROD Action Plan; and Table 1-3 , Primary Document <br /> Schedule <br /> Table 1-3 implies that the following documents will not be submitted for <br /> regulatory agency review: the 308 Design Analysis Report (DAR) , the <br /> 1008 DAR, and the draft final versions of the Remedial Design Work Plan <br /> (RDWP) , the Remedial Action Work Plan (RAWP) , and the Remedial Action <br /> Report (RAR) . Only the 608 DAR and draft versions of the other reports <br /> are identified for agency review. EPA recommends that DDJC-Tracy <br /> provide the 308 DAR for agency review. If agencies have significant <br /> design concerns, it will be more cost effective to identify such <br /> concerns early on in the design process, rather than to wait until the <br /> 608 design. Also, depending on the nature of agency comments on the <br /> draft RDWP, RAWP, and RAR, draft final versions of these documents may <br /> need to be submitted to the regulatory agencies for review. EPA and <br /> DDJC-Tracy can discuss further if these other documents should be <br /> considered primary or secondary documents. Section 1.2 and Table 1-3 <br /> should be revised to address these concerns. <br /> 9 . Section 3 .2.2.3, SWMU 8 Groundwater Remediation, page 3-13 <br /> Please modify the text to indicate that if dieldrin is not reported <br /> above the aquifer cleanup standard during 1998 and concentrations are <br /> not increasing, then "immediate" groundwater remediation is not <br /> necessary. However, please indicate that continued monitoring is <br /> required, and that groundwater remediation is not completely precluded <br /> at the end of 1998. The RI/FS modeling evaluation, as reported in <br /> Section 6.3 .7.4.6.5 of the RI/FS, indicated a peak dieldrin <br /> concentration of 7.0 ug/L after 30 years. This implies that <br /> concentrations observed in 1998 may be exceeded at a later date, and <br /> thus there exists a potential future need for groundwater remediation. <br /> 10. Section 3 .2.2.4, OU-1 Groundwater Design Data Gaps, page 3-13 <br /> Reference to Section 4.3 .2 should be corrected to 4.2.3 . <br /> 11. Section 3 .2.2.7, Northwest Corner of Depot Extraction Well; and Figure <br /> 3-2, Proposed CPT Wells <br /> Extraction well EW048A (Figure 3-2) seems prematurely located <br /> considering that additional CPT sampling and monitoring well sampling <br /> have yet to be performed. Please modify this section to indicate that <br /> the proposed well location and pump tests are based on available data <br /> only, and that these may be modified based on the results of further <br /> groundwater sampling. <br /> 12 . Figure 3-1, Proposed Extraction Wells <br /> Figure 3-1 should differentiate between proposed extraction wells which <br /> are expected to be installed and proposed extraction wells which may not <br /> be installed (i.e. , EW040AU, EW041AU, EW042AU, and EW045AU) , as <br /> explained in the text. <br /> 4 <br />
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