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ARCHIVED REPORTS_XR0005200
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ARCHIVED REPORTS_XR0005200
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Last modified
3/11/2020 5:52:29 PM
Creation date
3/11/2020 2:40:42 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0005200
RECORD_ID
PR0541650
PE
2960
FACILITY_ID
FA0023868
FACILITY_NAME
FORMER USA GASOLINE SERVICE STATION 110
STREET_NUMBER
2132
Direction
E
STREET_NAME
MARIPOSA
STREET_TYPE
RD
City
STOCKTON
Zip
95205
APN
1730635
CURRENT_STATUS
01
SITE_LOCATION
2132 E MARIPOSA RD
P_LOCATION
01
QC Status
Approved
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EHD - Public
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1 <br /> SECOND QUARTER,1997 <br /> GROUNDWATER MONITORING REPORT <br /> USA STATION#110- STOCKTON <br /> JULY,1997 <br />' The groundwater elevations ranged from 39 33 to 39 85-feet below mean sea level Groundwater <br /> elevations have increased an average of 1 65-feet since the last sampling event <br /> ' Groundwater elevation contours constructed from the Apnl 21, 1997 gauging activities indicate <br /> groundwater is flowing to the northeast at a hydraulic gradient of approximately 0 0014-feet/feet <br /> A review of the historical field data suggests that the groundwater generally flows to the northeast <br /> with minor fluctuations to the north and south, as shown on Figures 4 and 5 <br /> 3.2 Results of Groundwater Laboratory Analyses <br /> TPH G concentrations ranged from non-detect at the reporting limit of 50 nucrograms per liter <br /> (jig/1) in MW-1-P, MW-4-P, MW-5-P, and MW-6-P to 3,300 pgll m MW-2-P Benzene <br /> concentrations ranged from non-detect (ND) at the method detection limit of 0 5 µg/l in MW-I-P, <br /> MW-4-P, MW-5-P, MW-6-P, and MW-2 to 460 gg/l in MW-2-P MTBE and total lead have <br /> been ND at the method detection limits in all the wells sampled since the March, 1995 sampling <br /> ' event Analyses for these constituents will not be continued, as described in the"First Quarter, <br /> 1997, Groundwater Monitoring" Analytical results are summarized in Table 2, and shown on <br /> Figure 6 Copies of laboratory reports and COC documentation are provided in Appendix B <br /> 3.3 Conclusions <br /> ' The groundwater has risen since the October, 1996 measurements, but the site continues to be <br /> affected by groundwater pumpage in the area The presence of higher levels of TPH and BTEX <br /> compounds in MW-1, when compared to nearby MW-3-P, may be explained by the well <br /> construction MW-1 is perforated between 40 and 70-feet, and MW-3-P between 55 and 90- <br /> feet With the groundwater at 66-feet bgs, the analysis from MW-1 appears to reflect the <br /> concentration at the top of the water table and MW-3-P is more representative of the water <br /> bearing zone Both wells contained low levels of benzene this quarter <br /> r-,, _ <br /> ' Levels of TPH G and BTEX compounds in M}�V. 2-P Have increased to,historically high levels <br /> This may be due to groundwater solubilizmg prQleum compounds in the vadose zone or <br /> capillary fringe ' <br /> It is our opinion that the impacted groundwater plume continues to be minimal m size and appears <br /> to be stable Downgradient wells have been co'iWtently ND at the method detection limit, which <br /> ' define a "zero-line" closure These findings suggest tlt closure as a low risk site may be <br /> warranted <br /> i <br /> 3 <br />
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