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SITE INFORMATION AND CORRESPONDENCE_FILE 1
Environmental Health - Public
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2900 - Site Mitigation Program
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SITE INFORMATION AND CORRESPONDENCE_FILE 1
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Last modified
1/24/2020 3:08:30 PM
Creation date
1/24/2020 2:34:59 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
FileName_PostFix
FILE 1
RECORD_ID
PR0505432
PE
2960
FACILITY_ID
FA0006779
FACILITY_NAME
DIVIDEND PROPERTY
STREET_NUMBER
13170
Direction
W
STREET_NAME
GRANT LINE
STREET_TYPE
RD
City
TRACY
Zip
95376
CURRENT_STATUS
02
SITE_LOCATION
13170 W GRANT LINE RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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GEOMATRIX <br /> Mr. Don O. Culbertson <br /> Chevron Pipe Line Company <br /> S March 1995 <br /> Page 3 <br /> t <br /> The WSF of fresh petroleum products and crude oil has been investigated at <br /> laboratory conditions using gas chromatography (GC) in a qualitative manner (Bruya <br /> and Friedman, 1992). The chromatograms produced during this study are provided <br /> as pairs; (a) of each pair is the GC trace of a fresh petroleum product and (b) of <br /> each pair is the GC trace of the WSF of the product in (a). The WSF of each pair <br /> was collected by obtaining a water sample in equilibrium with and immediately <br /> underneath the floating product. Note that the scale of the Y-axis is not consistent <br /> among all chromatograms (Figures la through 3b); this is not critical as this <br /> research was primarily qualitative. The first pair of GC traces shows a fresh crude <br /> oil and the WSF of the crude oil (Figures la and lb). The crude oil trace shows <br /> constituents that elute from about C, to C,0 (the limit for this GC column); the <br /> dominant peaks are the n-alkanes. The WSF of this crude oil is limited primarily to <br /> the low molecular weight alkanes (C, through Ch) and BTEX (C6 through C8), with <br /> very low concentrations of C9 through C„ constituents, most likely C9 and CIO <br /> monoaromatics and the smaller PNAs. The gasoline trace (Figure 2a) shows peaks <br /> that elute from approximately C, to C12. The WSF of this gasoline (Figure 2b) <br /> shows that the alkanes C, through C6, BTEX, alkylated benzenes (C9, CIO and C„), <br /> naphthalene (CIO), and methyl naphthalenes (CII) were detected. The diesel trace <br /> (Figure 3a) shows constituents that elute between approximately C6 and C24. The <br /> WSF of this diesel (Figure 3b) shows that the alkanes C4 through C6i BTEX, <br /> alkylated benzenes, naphthalenes, and phenanthrenes (C14) and anthracenes (C14) <br /> were detected. <br /> The WSF of fresh fuels in equilibrium with groundwater at laboratory conditions <br /> has been investigated in a quantitative manner by GC and GC/MS analyses (Thomas <br /> and Delfino, 1991). This research supports the qualitative findings of Bruya and <br /> Friedman (1992) and indicates that the WSF of the fuels tested includes the <br /> monoaromatics and the PNAs having 14 carbons or fewer (Table 1); the low-boiling <br /> alkanes were not included as target analytes in this study. <br /> These studies provide clear evidence that, at controlled laboratory conditions and <br /> when analyzed by standard commercial analytical methods, the detectable WSF of <br /> fresh crude oil and fresh fuels is limited to the low molecular weight alkanes ( <br /> C6), the monoaromatics, and the PNAs having 14 carbons or fewer. Under field <br /> conditions, however, the presence of phenanthrenes (C14) and anthracenes (C14) may <br /> not be detected at practical detection limits during routine analyses of environmental <br /> samples because of their very low concentrations and the probable lack of true <br /> equilibrium conditions. <br />
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