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2900 - Site Mitigation Program
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PR0505092
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Last modified
2/5/2019 4:58:08 PM
Creation date
2/5/2019 4:46:43 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0505092
PE
2960
FACILITY_ID
FA0006532
FACILITY_NAME
LYOTH LOADING STATION/CHEVRON
STREET_NUMBER
26501
Direction
S
STREET_NAME
BANTA
STREET_TYPE
RD
City
TRACY
Zip
95376
CURRENT_STATUS
01
SITE_LOCATION
26501 S BANTA RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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0 <br /> GEDMATRIX <br /> Ms. Katie Hower <br /> Chevron Pipe Line Company <br /> 19 March 1997 <br /> Page 3 <br /> 5. The potential risk to human health posed by the affected soil and groundwater will be <br /> assessed under appropriate land use scenarios. <br /> 6. After four quarterly monitoring events, site data will be compared to RWQCB draft "Low <br /> Risk Criteria" (or applicable updates) for appropriate remedial strategy or site closure. <br /> The four quarterly monitoring events may incorporate historical data, if such data <br /> represent seasonal changes and water level fluctuations. <br /> ANALYTICAL SUITE <br /> As discussed earlier,the petroleum associated with the Old Valley Pipeline is a degraded crude oil <br /> and/or Bunker C fuel oil that is composed primarily of a broad range of medium-to high-boiling <br /> petroleum hydrocarbons. In some cases, it may be necessary to fingerprint the material present to <br /> further evaluate that it is Old Valley Pipeline product. The purpose of collecting samples for <br /> chemical analysis is to evaluate the potential threat to groundwater or risks to human health posed <br /> by the residual petroleum. Accordingly, the analytical suite will be focused on providing data <br /> appropriate for that purpose. The measurement of BTEX and PNAs is important for both <br /> protection of groundwater and human health. BTEX and the low molecular weight PNAs are the <br /> most water soluble petroleum components of concern and RWQCB has WQOs for these <br /> constituents. Benzene and the carcinogenic PNAs are the most toxic constituents potentially <br /> associated with the residual petroleum. Therefore, both soil and groundwater samples will be <br /> analyzed for BTEX and PNAs. <br /> The measurement of TPH as crude oil in soil by Method 8015M (GC-FID), or equivalent, at Old <br /> Valley Pipeline sites is useful as a site investigation tool,but it is not used in health risk <br /> assessments. The RWQCB WQOs include TPH measurements for gasoline and diesel products, <br /> but not crude oil/Bunker C, in groundwater. Although gasoline and diesel products are not present <br /> at these sites,the RWQCB has made it clear that these WQOs will be applied to "gasoline-range <br /> hydrocarbons"(C4 to C12) and"diesel-range hydrocarbons" (CIO to C14) found in site groundwater <br /> samples. Accordingly,TPH measurements incorporating these ranges will be performed on site <br /> groundwater samples. Because the WQOs are for gasoline and diesel products, the groundwater <br /> samples will be quantified against gasoline and diesel standards so that the comparison to WQOs <br /> is as direct as possible. Groundwater samples will not be analyzed for fractions greater than C„ or <br /> by Method 418.1. <br /> Using TPH as WQOs at Old Valley Pipeline sites is problematic because of positive interferences <br /> to the Method 8015M measurement. Based on recent research performed by Geomatrix (Zemo <br /> and Synowiec, 1995; Zemo, 1996; Foote et al., 1996), the TPH measurement of groundwater <br /> samples has been demonstrated to be positively interfered with by both soluble non-petroleum <br /> hydrocarbons resulting from intrinsic biodegradation and non-dissolved petroleum sorbed to <br /> particulates entrained within turbid samples. This research has shown that removal of these <br />
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