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ARCHIVED REPORTS_XR0011494
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2900 - Site Mitigation Program
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PR0535812
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ARCHIVED REPORTS_XR0011494
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Last modified
5/18/2020 9:32:44 AM
Creation date
5/18/2020 9:23:12 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0011494
RECORD_ID
PR0535812
PE
2959
FACILITY_ID
FA0020626
FACILITY_NAME
COLBERG BOAT WORKS
STREET_NUMBER
401
Direction
N
STREET_NAME
STOCKTON
STREET_TYPE
ST
City
STOCKTON
Zip
95203
APN
13546010
CURRENT_STATUS
01
SITE_LOCATION
401 N STOCKTON ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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r <br /> Second Quarter 1998 Groundwater Monitoring Report and Closure Request for Former Diesel Tank Site <br /> • CoIberg Boat Works,401 North Stockton Street,Stockton,California <br /> Page 3 <br /> Groundwater Samlin and Anal sis <br /> On April 0, 1998, Apex personnel collected groundwater samples from monitoring wells MW-I <br /> through MW-6 in accordance to the Apex SOP included as Appendix A The samples were <br /> subnutted, under chain-of-custody documentation, to California Laboratory Services of Rancho <br /> Cordova, California, a state-certified analytical laboratory The samples were analyzed for <br /> concentrations of total petroleum hydrocarbons, as gasoline (TPHg) and diesel (TPHd), by <br /> Modified EPA Method 8015, benzene, toluene, ethylbenzene, total xylenes (BTEX) and methyl t- <br /> butyl ether (MTBE) by EPA Method 8020 The analytical results are summarized in Table 2 <br /> The laboratory analytical reports and chain-of-custody form are included in Appendix B Figure 4 <br /> shows the distributions of TPHg, TPHd, benzene and MTBE in the shallow groundwater on April <br /> 30, 1998 at the subject site <br /> MASS BALANCE CALCULATION FOR FORMER DIESEL TANK SITE <br /> Estimated Area of Diesel Impact <br /> During the moiutonng well installations, soil samples were collected from MW-1 through MW-6 <br /> . at 15 feet and 20 feet below grade Diesel was not detected in the soil samples collected from any <br /> of the soil borings The results of the soil boring and well installation were documented by Apex <br /> in Results of Subsurface Investigation, dated August 21, 1997 <br /> Based on the past quarterly groundwater monitoring results, the groundwater at the subject site <br /> flows in an east and north-east direction Diesel has not been detected in the groundwater <br /> samples collected from the down-gradient well (MW-5) or the up-gradient well (MW-6) near the <br /> former diesel tank area Therefore, diesel impact to the groundwater at the former diesel tank <br /> area is confined to the immediate proximity of the former diesel tank basin and the monitoring <br /> well MW-4, which is adjacent to the former diesel tank basin The vertical extent of groundwater <br /> diesel impact is above 15 feet below grade since no soil samples collected from the mon itonng <br /> well borings contained diesel at 15 and 20 feet below grade Figure 5 shows the estimated extent <br /> of diesel impact to groundwater on April 30, 1998 at the former diesel tank location <br /> Residual Diesel Mass Balance Calculation <br /> Since diesel in the groundwater is defined and not migrating, a mass balance calculation was <br /> performed to estimate the residual diesel mass remained in the shallow groundwater and <br /> subsurface soil at the former diesel tank area The results of the mass balance estimation indicates <br /> that the residual diesel mass in the groundwater and soil is approximately S poun s The <br /> detailed mass calculations and assumptions are included in Appendix C <br /> •1 <br /> �1.2��.Qr rv�-ss �ti ck <br /> JY C 1_PROJECTICOL01 001-COLBERG BOAT WORKSIQMR04981QMR0498 DOC <br />
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