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ARCHIVED REPORTS_XR0012120
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0541653
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ARCHIVED REPORTS_XR0012120
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Last modified
10/10/2020 11:26:53 PM
Creation date
7/9/2020 8:55:01 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012120
RECORD_ID
PR0541653
PE
2965
FACILITY_ID
FA0023871
FACILITY_NAME
TOP FILLING STATION
STREET_NUMBER
101
Direction
S
STREET_NAME
WILSON
STREET_TYPE
WAY
City
STOCKTON
Zip
95205
APN
15125307
CURRENT_STATUS
01
SITE_LOCATION
101 S WILSON WAY
P_LOCATION
01
QC Status
Approved
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EHD - Public
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02 June 2005 <br /> AGE-NC Project No 95-0130 <br /> Page 10 of 13 <br /> Utilizing a Blue-White Industries F-2000 flow meter,total flow(totalizer)was recorded between 29 <br /> December 2004 and 08 March 2005 (Table 9) During this time,the extraction and treatment interim <br /> ground water remediation system was in operation for approximately 69 days Based on the total of <br /> approximately 81,280 gallons of water recorded during this time, AGE estimated that an average <br /> 1,178 gallons of water was discharged per day during this time <br /> 4 6 MASS-VOLUME REMOVAL CALCULATIONS <br />' Between 29 December 2004 and 08 March 2005, an estimated 43 94 pounds of total petroleum <br /> hydrocarbons were extracted from ground water (Table 9), since the system was initiated on 17 <br /> November 2004, a total mass of 58 pounds of petroleum hydrocarbons have been removed The <br /> December 2004 to March 2005 mass-volume calculations of gasoline-impacted ground water <br /> extracted from the ground water extraction and treatment system are presented in Appendix K Plots <br /> of cumulative ground water pump and treat mass removal trends and influent ground water TPH-g <br />' concentrations versus time are included in Appendix L <br /> 5.0. SUMMARY AND CONCLUSIONS <br />' The implications from the March 2005 ground water monitoring event are as follows <br /> • Ground water flow direction within Hydrologic Units 1 and 2 (First Water Zone) was <br /> inferred to be towards the southeast at a gradient of 0 003 ft/ft(Figure 3), ground water flow <br /> direction within Hydrologic Units 2 and 3 (Second Water Zone)was inferred to be towards <br /> the northeast at a gradient of 0 003 ft/ft <br />' • Between January 1995 and August 2001, ground water elevations at the site generally <br /> increased from 44 feet to 23 feet below MSL, since August 2001 and present day, ground <br />' water elevations have generally fluctuated between 24 feet and 29 feet below MSL(Table 2) <br /> • Ground water at the site was generally observed between 44 and 46 feet bsg and was above <br /> the screened intervals of wells MW-1 through MW-5,MW-6 (B-E),MW-7 (B-E), VW-1 C, <br />' VW-2A and VW-3A (i e screened below ground water table), and may not yield samples <br /> fully representative of shallowest ground water conditions <br />' • The greatest concentrations of Top Filling Station dissolved TPH-g and BTEX were detected <br /> in samples collected from wells MW-7B(50-55 ft),VW-1 C(48-63 ft)and VW-2A(43-63 ft) <br /> which is consistent with previous monitoring results (Table 3) TPH-g concentrations were <br /> I detected as high as 230,000 µg/l from well VW-2A and benzene as high as 87,000 gg/l from <br /> well MW-7B (Table 4) Additionally, the deepest detection of dissolved TPH-g and BTEX <br /> were detected in samples collected from well MW-6E(137-142 feet),the approximate extent <br /> Advanced GeoEnvironmental,Inc <br />
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