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ARCHIVED REPORTS XR0011361
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ARCHIVED REPORTS XR0011361
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Last modified
7/3/2019 6:34:22 PM
Creation date
7/3/2019 4:00:42 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0011361
RECORD_ID
PR0544624
PE
3526
FACILITY_ID
FA0005206
FACILITY_NAME
GEORGES SERVICE
STREET_NUMBER
1600
Direction
W
STREET_NAME
DURHAM FERRY
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
25510004
CURRENT_STATUS
02
SITE_LOCATION
1600 W DURHAM FERRY RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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Geological Technics Inc Page <br /> Groundwater Monitoring Report <br /> Project No 425 2 <br /> May 12,2003 <br /> t <br /> ' • BTEX & TPH-G concentrations in MW-2 show a decreasing trend since the June 20, <br /> 2001 monitoring event, however, this quarter there was a slight increase from the <br /> December 2002 monitoring event See Figure 7 for graph of Benzene and TPH-G versus <br /> time (MW-2) and Figure 8 for the distribution of IPH-G <br /> • Contaminant concentrations in wells MW-4 and MW-5 fluctuate seasonally but exhibit <br /> 1 an overall increasing trend MW-4 appears to maintain a relatively consistent <br /> concentiation of TPH-G <br /> • For the tenth consecutive event, wells MW-102 did not contain contaminant <br /> concentrations above the laboratory reporting limits <br /> • All three of the domestic wells were non-detect for this monitoring event <br /> o Dissolved Oxygen measurements were between 0 34 and 3 23 ppm, which is conducive <br /> ' to biodegradation activity <br /> • Oxidation-Reduction Potential (ORP) was measured (Table 5) The results for the <br /> ' March 2003 groundwater monitoring are inconclusive ORP values were negative in all <br /> tested monitoring wells DO measurements are low in most wells, corroborating with <br /> the negative ORP values <br /> 3 0 CONCLUSIONS AND RECOMMENDATIONS <br /> rhe following conclusions have been drawn regarding the status of the groundwater at this <br /> site and recommendations for future work <br /> Conclusions <br /> 1 The water table groundwater gradient historically flowed in a northerly direction at about <br /> 0 0020 ft/ft prior to May 1998 However, since that time, the gradient has fluctuated <br /> from north to northeast, the gradient is currently N85'E at 0 0021 ft/ft <br /> 2 The intermediate depth groundwater has flowed easterly, with three shifts to southeast <br /> during September 2000, September 2001 and December 2002 The northerly flow <br /> direction during the December 3, 2001 event was anomalous The gradient is currently <br /> N3 80E at 0 0014 ft/ft <br /> 3 Vertical groundwater gradients have been found to be flowing upward, during winter and <br /> early spring, and downward during late spring and summer However, it continued in an <br /> upward direction during this past summer and fall Upward vertical gradients dominate <br /> over downward gradients by a 4 1 ratio <br /> 4 The dominance of upward vertical flow of groundwater may be the primary reason the <br /> contaminants has not impacted the drinking water aquifer <br /> 5 The shallow water table groundwater plume is laterally defined except to the west <br /> Increases in TPH-G concentration in the western monitoring wells indicate that the plume <br /> may be spreading laterally toward the west <br />
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