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2900 - Site Mitigation Program
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PR0515573
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
4/7/2020 3:32:38 PM
Creation date
4/7/2020 3:02:51 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0515573
PE
2950
FACILITY_ID
FA0012224
FACILITY_NAME
RIDGEWAY PROPERTY
STREET_NUMBER
1881
STREET_NAME
RUSTAN
STREET_TYPE
RD
City
TRACY
Zip
95376
CURRENT_STATUS
02
SITE_LOCATION
1881 RUSTAN RD
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
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GEOMATRIX <br /> Mr. Philip Isorena <br /> California Regional Water Quality Control Board <br /> September 14, 2000 <br /> Page 4 <br /> In addition to the four criteria for low risk groundwater, Chevron also should provide the <br /> information specified in Table 1 of Appendix B. <br /> The information specified in Table 1 of Appendix B is presented in Appendix E of the draft <br /> closure request. CEMC will include this information in the text of the final closure request. <br /> Conformance of a site to the low risk groundwater criteria relies on existence of NA at each <br /> site. For NA to be acceptable to Board staff, its remediation time must be comparable to <br /> those ofactive remedial alternatives. <br /> Comment addressed in Item B. <br /> Site-Specific Evaluation <br /> Chevron evaluated the site against the four criteria for low risk groundwater under Appendix <br /> B and provides justification as to why the site meets each criterion. Those four criteria and <br /> my comments on Chevron's assertions are described below. <br /> E. Contaminants remaining in the vadose zone must not reverse or threaten to reverse the <br /> mass reduction rate of groundwater pollutants discussed in 44 below. <br /> Chevron has not estimated the contaminant mass in the vadose zone or groundwater. <br /> Therefore, staff cannot determine whether or not mass reduction or its reversal has <br /> occurred. Chevron should estimate the mass and show that reduction has occurred or is <br /> occurring. The statement that residual hydrocarbons in soil are not adding amounts of <br /> soluble constituents to groundwater is incorrect because TPH characterized in the diesel <br /> range is being detected in monitoring wells (MWs) 1 and 4. <br /> It is possible to estimate the current mass of residual non-dissolved petroleum in soil (both <br /> above and below the water table), the current mass of dissolved petroleum in groundwater, <br /> and the current mass of degradation byproducts in groundwater. However, it is not <br /> possible to estimate what these masses were at the time the release occurred and, <br /> accordingly, it is not possible to estimate the historic "mass reduction rate of groundwater <br /> pollutants." <br /> To address RWQCB's comment in the final closure request, Geomatrix will attempt to <br /> obtain information about the composition of fresh San Joaquin Valley crude and compare <br /> it to the composition of weathered petroleum in the site subsurface. Qualitative <br /> observations will be noted. For example, fresh San Joaquin Valley crude contains <br /> measurable concentrations of BTEX, which may have affected groundwater at the time of <br /> the release. Since the release occurred, the mass of BTEX in groundwater generally has <br /> been <br /> reduced to non-detectable concentrations. Because little or no measurable BTEX <br /> remains in weathered petroleum at the site;this remaining petroleum will not reverse or <br /> threaten to reverse the mass reduction rate of BTEX in groundwater. Additionally, <br />
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