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ARCHIVED REPORTS XR0001371
Environmental Health - Public
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1201
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3500 - Local Oversight Program
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PR0544188
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ARCHIVED REPORTS XR0001371
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Last modified
2/27/2019 1:26:33 PM
Creation date
2/27/2019 11:45:58 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0001371
RECORD_ID
PR0544188
PE
3526
FACILITY_ID
FA0006698
FACILITY_NAME
FERNANDOS PLACE
STREET_NUMBER
1201
Direction
S
STREET_NAME
CENTER
STREET_TYPE
ST
City
STOCKTON
Zip
95209
APN
14716003
CURRENT_STATUS
02
SITE_LOCATION
1201 S CENTER ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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WNg
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EHD - Public
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r <br /> k <br /> I , <br /> '^ 30 January 2004 - <br /> AGE-NC Project No 00-0769 .: <br /> Page 6 of 7 , <br /> I „r <br /> BTEX compounds were detected in samples MW-4E and MW-5E at concentrations of 20 gg/L and , <br />' 32 gg/L of benzene,20 gg/L and 38 lig/L oftoluene,5 7 µg/L and 8 2 µg/L ofethylbenzene and 18 2 <br /> µg/L and-47 gg/L of total xylenes, respectively <br /> The fuel oxygenate MTBE was detected in the HU-5 sample from MW-4E at a concentration of 12 <br /> pg/L <br />' No other constituents of concern were detected above laboratory reporting limits in the water <br /> u ' samples collected during the second quarter sampling event Analytical results of ground water <br /> monitoring well samples are summarized in Tables 2 through 5 The laboratory reports,(CTEL <br /> Project No CT214-0305161) and chain-of-custody forms are presented in Appendix C <br /> Y I I I <br /> 4.0. SUMMARY AND CONCLUSIONS <br /> I <br /> The following conclusions were drawn from the results of the site investigation <br /> • Depth to ground water at the site vaned between 25 02 and 29 00 feet bsg, relative ground <br />' water elevations at the site ranged between 14 32 and 18 25 feet below MSL during the May <br /> 2003 monitoring event HU-1 generally flowed southeast with a limb flowing 0 005 ft/ft to ' <br /> the southeast and 0 005 ft/ft to the east-southeast HU-2 generally flowed to the southwest <br /> with a limb flowing east-southeast at 0 002 ft/ft and north-northwest at 0 002 ft/ft HU-3 <br /> general ly,flowed north-northeast with a limb flowing east of north at 0 008 ft/ft and north- <br /> northeast at 0 011 ft/ft HU-4 generally flowed east-southeast with a limb flowing northeast j <br />' ','at 0 006 ft/ft and southeast at 0 004 ft/ft (Figures 3 through 6) <br /> � r, , rr <br /> • ; ,The most highly impacted ground water appears to be located near the first and second <br />' „former UST, Ilocations, figures 7 through 11 illustrate the lateral extent of <br /> Hydrocarbon-impacted ground water, as depicted within each modeled hydrogeologic unit , <br /> 'Vertically, hydrocarbon-impacted ground water was detected inleach each of the screened <br /> intervals of'multi-level wells MW-4 through MW-7 The concentrations of dissolved <br /> hydrocarbons increased at the total depth of well MW-7, representing the'lowest, down- ' " <br /> 'gradient point,in the`monitoring well network Up-gradient multi-level well MW-9 and F <br />' z cross-gradient multi-level well'MW-8 had low to nori-detectable concentrations ofpetroleu n <br /> ' hydrocarbon compounds <br /> ' — I ' , H <br /> • <br /> ' Concentrations of benzeneiwere detected in ground water samples collected from monitoring <br /> wells MW-4 and MW-5, screened in each of the five identified hydrogeologic units, above <br /> the DHS's Maximum Contaminant Levens (Mds) of 0 5 gg/L, 1,2-DCA was detected in, <br />' every unit except HU-5 E <br /> r ' I <br /> i <br /> 1 r a i <br /> Advanced Geol:nvironmental,Inc F <br /> I <br /> s, <br /> y I <br />
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