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ARCHIVED REPORTS XR0007839
EnvironmentalHealth
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EL DORADO
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2900 - Site Mitigation Program
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PR0529779
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ARCHIVED REPORTS XR0007839
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Last modified
7/17/2019 10:32:47 AM
Creation date
7/17/2019 9:30:29 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0007839
RECORD_ID
PR0529779
PE
2960
FACILITY_ID
FA0019644
FACILITY_NAME
FORMER GENE GABBARD INC
STREET_NUMBER
640
Direction
N
STREET_NAME
EL DORADO
STREET_TYPE
ST
City
STOCKTON
Zip
95202
APN
13906004
CURRENT_STATUS
01
SITE_LOCATION
640 N EL DORADO ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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Ms Lori Duncan <br /> Page 3 of 4 <br /> 3 0 GROUNDWATER ANALYTICAL RESULTS <br /> All groundwater samples were analyzed for TPHg and TPHd using EPA method 801513, BTEX <br /> using EPA 802113, and VOCs and oxygenated gasoline additives using EPA 8260B <br /> Tetrachloroethene (PCE) was detected in wells MW1, MW2, MW4, MW5, MW6, and MW7 at <br /> concentrations of 12 parts per billion (ppb), 11 ppb, 6 6 ppb, 5 1 ppb, 44 ppb, and 95 ppb, <br /> respectively No PCE was detected m well MW3 (<2 0 ppb) cis-1,2-Dzchloroethene (cis-1,2-DCE) <br /> ranged from <0 5 ppb in well MW5 to 19 ppb in well MW3 Chloroform ranged from 0 7 ppb in <br /> well MW7 to 3 9 ppb in well MW1, but was not detected in well MW3 (<2 0 ppb) Trichloroethene <br /> (TCE) ranged from <0 5 ppb in wells MW4 and MWS to 5 2 ppb in well MW3 <br /> No petroleum hydrocarbons or gasoline additives were detected above method detection limits in <br /> groundwater samples collected from any site well, except well MW3 Well MW3 contained TPHg <br /> at 3,600 ppb, benzene at 20 ppb, toluene at 52 ppb, ethylbenzene at 26 ppb, and xylenes at 140 ppb <br /> Well MW3 also contained several additional VOCs associated with petroleum hydrocarbons <br /> Groundwater analytical results are summarized on Table 3 Attachment 3 contains laboratory <br /> reports and chain of custody documentation <br /> The distribution of dissolved PCE, TCE, and cis-1,2-DCE beneath the site are presented on Figures <br /> 3, 4, and 5, respectively The figures were created by plotting the average concentration of the <br /> target analyte over the last four sampling events, the results of which are noted on each figure <br /> Although the contours are based on the composite value, the contours for a given sampling round <br /> would be very similar if plotted separately <br /> 4.0 DISCUSSION <br /> Although groundwater beneath the site has consistently flowed northeast (Figure 2), the highest <br /> concentrations of PCE in groundwater were detected in well MW7, which is located northwest <br /> (cross-gradient) of the former UST Further, no PCE has been detected in well MW3, which was <br /> completed through the former UST's location The distribution of dissolved PCE in site wells <br /> (Figure 4) strongly suggests that the primary source of PCE in groundwater is off-site to the <br /> northwest The apparent distribution of dissolved TCE (Figure 5) and cis-1,2-DCE (Figure 6) <br /> beneath the site suggest that the former UST is a source of contamination for these constituents, but <br /> also suggest that a secondary source exist off-site to the northwest, based upon higher <br /> concentrations in wells MW6 and MW7 as compared to wells MW1 and MW2 TCE and cis-1,2- <br /> DCE are known breakdown products of PCE, and their distribution beneath the site is consistent <br /> with an off-site source of PCE <br /> 5.0 CONCLUSIONS <br /> Although measurable free product remains in well MW3 in the form of oily hydrocarbons, no <br /> dissolved petroleum hydrocarbon constituents have been detected in any other site well Further, the <br /> concentration of dissolved PCE in all site wells is decreasing over time, as illustrated on Figure 6 <br /> 6 1GROUNDZEIGABBARDIreports\QMR1200411QM2004 doc <br />
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