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ARCHIVED REPORTS_XR0005026
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2900 - Site Mitigation Program
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PR0507952
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ARCHIVED REPORTS_XR0005026
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Last modified
9/16/2020 12:50:34 AM
Creation date
3/17/2020 2:04:46 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0005026
RECORD_ID
PR0507952
PE
2950
FACILITY_ID
FA0007846
FACILITY_NAME
OLYMPIAN CFN
STREET_NUMBER
983
STREET_NAME
MOFFAT
STREET_TYPE
BLVD
City
MANTECA
Zip
95336
APN
22115006
CURRENT_STATUS
01
SITE_LOCATION
983 MOFFAT BLVD
P_LOCATION
04
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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' 27 October 2004 <br /> • AGE-NC Project No 96-0254 <br /> Page 5 of 10 <br /> t5.0. GROUND WATER MONITORING PROGRAM <br /> Quarterly ground water monitoring has been ongoing at the site since January 2000 TPH-g and <br /> ' TPH-d have been detected only in two (MW-1 and MW-2)of the eight monitoring wells, and with <br /> the exception of 8 2 ug/1 xylenes detected in well MW-1 in August 2000, BTEX compounds have <br /> not been detected in ground water samples collected from the site since sampling began-MTBE has <br /> 1 been detected in all wells except MW-6 and MW-8, MTBE has been detected eac�quarter lin the <br /> samples collected from wells MW-1 and MW-2 at concentrations ranging from Z µg/1 to , <br /> µg/1, and rote ittently in wells MW-3 through MW-5 and MW-7 at concentrations ranging from <br /> 0 51 µg/1 to 210 µg/1 <br /> Based on the investigation to date ground water at the site is only impacted with MTBE at <br /> concentrations requiring active site remediation_'The vertical extent of MTBE-impacted ground4'? <br /> water has been defined at levels below:30 microg�r maYna s_per_liter~. The lateral extent of MTBE- <br /> impacted groundwater has generally been defined,to levels required for site assessment and closure <br /> tFurther assessment may be required to fully define the MTBE-impacted ground water vertically4Ac& <br /> beyond 50 feet bsg <br /> ' • MTBE concentrations in the most impacted wells MW-1 and MW-2 have declined noticeably since <br /> monitoring began in 1999 (Tables 4 and 5) A trend analysis for MTBE in well MW-1 showed <br /> exponentially declining concentrations over time at a correlation coefficient(accuracy)of 93(93%) <br /> ' (Appendix B) Utilizing a logarithmic presentation of the data(Appendix B), AGE estimated that <br /> since 2001,MTBE had attenuated at an approximate rate of 2,500µg/1/yr At the current decay rate, <br /> ' MTBE concentrations in well MW-1 will achieve the state secondary maximum contaminant level <br /> for drinking water of 5 µg11 by year 2008 (Appendix B) and the maximum contaminant level of <br /> 13 µg/1 sooner <br /> ' Analytical results of ground water samples are summarized in Tables 4 and 5 Cross sections <br /> depicting the general lithology in the soil beneath the site are illustrated on Figure 4 The lateral <br /> ' extent of dissolved MTBE is depicted on Figure 5 The trend analysis of dissolved MTBE in well <br /> samples is shown in Appendix B <br /> MASS OF DISSOLVED MTBE <br /> Based un giound watei analytical results for July 2004,AGE estimated the areal extent and mass of - <br /> dissolved MTBE in ground water (Figure 5) AGE assumes the following conditions <br /> ' The distribution of dissolved hydrocarbon concentrations on-site can be approximated by an <br /> ellipse area with a column depth to the deepest ground water sample collected, containing <br /> the higher MTBE concentrations, <br /> ' Advanced Geo Environmental,Inc <br />
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