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ARCHIVED REPORTS_XR0004587
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ARCHIVED REPORTS_XR0004587
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Last modified
3/5/2020 1:14:26 PM
Creation date
3/5/2020 11:52:22 AM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0004587
RECORD_ID
PR0507835
PE
2950
FACILITY_ID
FA0007793
FACILITY_NAME
SUPER STOP MARKET
STREET_NUMBER
290
Direction
N
STREET_NAME
MAIN
STREET_TYPE
ST
City
MANTECA
Zip
95336
APN
22309101
CURRENT_STATUS
02
SITE_LOCATION
290 N MAIN ST
P_LOCATION
04
P_DISTRICT
003
QC Status
Approved
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EHD - Public
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404hg&al re"la Inc Page 4 <br /> Groundwater Monitoring Report <br /> Project No 662 2 <br /> November 15, 2004 <br /> ' • MW-2, which is upgradient of the former USTs, has not contained contaminant <br /> concentrations above the laboratory detection limits for all quarterly events completed <br /> ' thus far in the investigation <br /> • MW-3 contained the gasoline oxygenate MTBE at 1500 µg/l <br /> • The detections of ETBE and TAME in wells MW-1 and MW-3 are intermittent and <br /> ' appear to be dependent on elevated MTBE concentrations and associated elevated <br /> reporting limits <br /> • Deep screened well MW-104 contained MTBE at 130 µg/1 This is the highest level <br /> ' recorded in the investigation <br /> • Figure 4 MTBE vs Groundwater Elevation in MW-3 illustrates a fairly direct <br /> relationship between the concentration of MTBE in groundwater and the elevation of <br /> groundwater in well MW-3 A reverse trend was present for the last several quarters A <br /> linear trend line has been added to the figure to show a general decline in both <br /> groundwater elevation and MTBE concentrations over time <br /> • TPH-G and BTEX were not present in any of the groundwater samples above the <br /> laboratory reporting limits <br /> 1 • In accordance with San Joaquin County directives, the groundwater samples were also <br /> analyzed for diesel, methanol, ethanol, 1,2-DCA, EDB and lead, which were all non- <br /> detect except for lead Wells MW-1, MW-3 and MW-104 contained 24, 28 and 37 1Ag/1 <br /> lead,respectively <br /> • Table 3 includes Dissolved Oxygen (DO) and Oxidation-Reduction Potential (ORP) <br /> measurements for the site's wells All four of the wells show low DO and low positive <br /> ORP values suggesting that the plume may be stable <br /> GTI makes the following conclusions <br /> • The latest monitoring event reflects the historical trends in groundwater direction and <br /> contaminant distribution L <br /> GTI makes the following reco endation <br /> • Discontinue-analysis for diesel, methanol, ethanol, ETBE, DIPE, TAME;TBA , 1,2-DCA, <br /> /EDB and lead\ These analyses do not contribute clarity to the site conceptual model nor <br /> augment site remedial alternatives <br /> ' Project Status Review <br /> • GTI's February 20, 2004 "Additional Site Characterization, Soil and Groundwater <br /> Investigation" report documents the advancement of several Cone Penetrometer Testing <br /> ' (CPT)borings in December 2003 Groundwater and soil data from these borings clarified <br /> the site conceptual model suggesting that residual contamination is localized beneath the <br /> former UST excavation, with the possibility that a submerged MTBE groundwater plume <br /> ' may be migrating off site <br /> I e In our April 19, 2004 work plan GTI proposed additional groundwater plume definition <br /> and an aquifer pumping test The SJC/EHD approved the work plan in their May 21, <br />
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