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2900 - Site Mitigation Program
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PR0009005
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
5/11/2020 12:04:28 PM
Creation date
5/11/2020 11:15:01 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0009005
PE
2953
FACILITY_ID
FA0004053
FACILITY_NAME
LUSTRE-CAL NAME PLATE CO
STREET_NUMBER
110
Direction
E
STREET_NAME
TURNER
STREET_TYPE
RD
City
LODI
Zip
95240
APN
04124048
CURRENT_STATUS
01
SITE_LOCATION
110 E TURNER RD
P_LOCATION
02
P_DISTRICT
004
QC Status
Approved
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If significant rebound occurs according to the above criteria, pulsing operations will be <br /> reinstated. <br /> 4.6 Soil Gas Cleanup Goals <br /> In addition to the SVE system performance goal of VOC asymptotic stabilization, which is <br /> based on operating the system to its technically and economically practicable limits, it may <br /> also be appropriate at some sites to evaluate SVE system performance by measuring its <br /> effect on reducing VOC concentrations in soil. Where appropriate, it is proposed that SVE <br /> systems operating in Lodi also have as a performance goal achieving cleanup levels in <br /> vadose zone soils set in accordance with the 'Interim Guidance for Remediation of VOC <br /> Impacted Sites" published by the California Regional Water Quality Control Board for the <br /> Los Angeles Region in January 1995 ("RWQCB Guidance"). The RWQCB Guidance <br /> presents VOC cleanup standards for vadose zone, unsaturated soils based on attenuation <br /> factors derived from equations using site-specific soil vapor, chemical, and other physical <br /> parameters. This guidance document specifically indicates that the procedure assumes <br /> that VOCs are in liquid phase and that only the liquid phase is moving downward to impact <br /> groundwater quality. The document further assumes that VOCs in residual and gaseous <br /> phases are considered as lost mass in the subsurface. Therefore, the attenuation factor <br /> method is likely not applicable for sites where the majority of the contaminant mass in the <br /> vadose zone is in a gaseous phase. <br /> It is not currently known whether soil cleanup standards established by applying the <br /> RWQCB Guidance are achievable even if SVE systems are operated to the fullest <br /> technically and economically practicable extent. On the other hand, it may be possible to <br /> achieve these soil cleanup levels before the SVE systems reach asymptotic mass removal. <br /> As a result, the overall performance goal proposed for SVE systems in Lodi would allow <br /> their operation to be terminated upon achieving either asymptotic stabilization, as <br /> described in Section 4 above, or RWQCB Guidance soil gas cleanup standards. <br /> DTSC has calculated preliminary soil cleanup levels and soil gas cleanup levels based on <br /> the RWQCB Guidance. The preliminary DTSC-established soil gas cleanup goals will be <br /> refined when site specific data are collected. Site specific data, including soil moisture <br /> content, porosity, bulk density, and organic fraction, will be used to determine site-specific <br /> soil gas cleanup goals rather than the mean values used by DTSC for the preliminary <br /> estimates. Soil gas cleanup goals will be to assess SVE performance at all sites. <br /> 8 <br />
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