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ARCHIVED REPORTS XR0006603
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ARCHIVED REPORTS XR0006603
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Last modified
6/21/2019 6:32:39 PM
Creation date
6/21/2019 9:08:47 AM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0006603
RECORD_ID
PR0505513
PE
2950
FACILITY_ID
FA0006438
FACILITY_NAME
United # 5446
STREET_NUMBER
1403
Direction
W
STREET_NAME
COUNTRY CLUB
STREET_TYPE
BLVD
City
STOCKTON
Zip
95204
APN
12323246
CURRENT_STATUS
02
SITE_LOCATION
1403 W COUNTRY CLUB BLVD
P_LOCATION
99
P_DISTRICT
001
QC Status
Approved
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Groundwater Monitoring Well,CPT,and Ozone Microsparge System Installation Report <br /> Tosco(76) Service Station No 11192, Stockton,California <br /> May 9 2003 <br /> Prior to well development and groundwater sample collection on January 3, 2003, GR personnel <br /> measured the depth to groundwater in wells MW-1 and MW-3 through MW-13 at depths ranging <br /> between 13 79 and 18 81 feet below top of casing (TOC) SPHs were not observed in any of the <br /> wells These data were used to construct a Potentiometric Map (Figure 4) Based on these data, <br /> shallow groundwater beneath the subject site generally flows northeast at a calculated hydraulic <br /> gradient of 0 001 to 0 0003 feet/feet, which is generally consistent with historical data <br /> 5-7,Laboratory Analysis <br /> The soil samples collected from the two well borings and the groundwater samples from the two <br /> CPT borings were analyzed by Sequoia Analytical in Sacramento, California (FLAP No 1624) <br /> The groundwater samples collected from the monitoring wells were analyzed by STL in <br /> Pleasanton, California (ELAP No 2496) The soil and CPT groundwater samples were analyzed <br /> for TPHg by EPA Method 8015 modified, BTEX and MtBE by EPA Method 8021, the fuel <br /> oxygenates TBA, ETBE, TAME, DIPS, MtBE, ethanol, and lead scavengers 1,2-DCA and 1,2- <br /> dibromoethane (EDB) by EPA Method 8260B, and methanol by 8015B modified The <br /> groundwater samples from the monitoring wells were analyzed for TPHg, BTEX, and fuel <br /> oxygenates by EPA Method 8260B Copies of the laboratory analytical reports and chain-of- <br /> custody records are included in Appendix F <br /> 5.3 Groundwater Ana ayheal Results <br /> TPHg and BTEX constituents were not detected above laboratory detection limits in the <br /> groundwater samples analyzed from the two new wells MW-12 and MW-13 MtBE and TBA were <br /> the only fuel oxygenates detected in the groundwater samples from wells MW-12 and MW-13 at <br /> concentrations of 220 and 1,700 ppb, and 13,000 and 20,000 ppb, respectively Groundwater <br /> chemical data are summarized in Table 1 <br /> TPHg and BTEX constituents were not detected above laboratory detection limits in the <br /> groundwater samples analyzed from select depths in the CPT borings CPT-2 and CPT-3 Of the <br /> fuel oxygenates, MtBE and methanol were detected in the groundwater sample CPT-2 75 at <br /> concentrations of 2 0 and 2,700 ppb, respectively MtBE was detected in CPT-3 100 at a <br /> concentration of 6 8 ppb MtBE and TBA were detected in CPT-3 125 at concentrations of 290 and <br /> 88, respectively Grab groundwater chemical data are summarized in Table 2 and presented on <br /> Figure 5 <br /> 5-4 So*1 Anal3lical Result <br /> MtBE was detected in soil boring MW-12 (6 5') at a concentration of 0 0067 ppm TPHg, MtBE, <br /> TBA, and TAME were detected in soil boring MW-12 (11 5') at a concentration of 0 68, 1 1, 0 25, <br /> • 140245 8 9 <br />
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