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ARCHIVED REPORTS_XR0011294
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0545145
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ARCHIVED REPORTS_XR0011294
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Last modified
1/9/2020 11:36:42 AM
Creation date
1/9/2020 11:05:22 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0011294
RECORD_ID
PR0545145
PE
3528
FACILITY_ID
FA0003820
FACILITY_NAME
VALLEY WHOLESALE DRUG
STREET_NUMBER
1401
Direction
W
STREET_NAME
FREMONT
STREET_TYPE
ST
City
STOCKTON
Zip
95203
APN
13525031
CURRENT_STATUS
02
SITE_LOCATION
1401 W FREMONT ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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Geological T¢cluucs Inc. Page 4 <br /> Groundwater Monitoring Report <br /> .Project No. 9W2 <br /> January 15,2003 <br /> • Low concentrations of MTBE were present in MW-1, MW-4, MW-5, MW-6, MW-8 and <br /> MW-9. The levels are consistent with previous monitoring events. <br /> ' • Concentrations of MTBE in MW-4, MW-5 and MW-6 decreased since the <br /> September 2002 monitoring event. <br /> ' • MW-1 shows a MTBE concentration of 1.7 µg/L due to the lower laboratory <br /> detection limits, reduced to 1.0 µg/L from 5.0 tig/L. <br /> • A plot of TPH-gasoline versus groundwater elevation for MW-1 shows that generally <br /> the concentrations of TPH-gasoline fluctuate with groundwater elevation and that the <br /> concentration is decreasing. <br /> Historically, the fuel oxygenates DIPS, ETBE, TAME and TBA as well as 1 ,2 DCA and <br /> 1 EDB have not been detected in any of the site's monitoring wells. This holds true for <br /> the new monitoring wells. <br /> Laboratory Data Sheets are included in Appendix C. The data are summarized in Table 2 of <br /> Appendix A. Chart 1 is a plot of TPH-gasoline versus groundwater elevation for MW-1. <br /> During purging of the monitoring wells, field measurements of the oxidation-reduction <br /> potential (ORP) of the water were taken using an YSI 3560 Flowcell meter. During this <br /> groundwater monitoring event, dissolved oxygen was measured in all the wells using an <br /> YSI dissolved oxygen meter. These measurements are summarized in Table 3 of Appendix <br /> A and in the field logs of Appendix B. The results suggest that the plume reaction with the <br /> groundwater follows a seasonal pattern. Further discussion will follow the installation and <br /> monitoring of additional wells. <br /> ' 3.0 CONCLUSIONS AND RECOMMENDATIONS <br /> The following conclusions have been drawn from the data generated from this site <br /> investigation work: <br /> Conclusions <br /> • Concentrations of TPH-G and BTEX have steadily decreased since 1996, suggesting <br /> ' that the plume either is migrating or is attenuating from natural causes. <br /> • Dissolved oxygen readings at the site range from 0.91 ppm at the plume boundary to <br /> 0.38 ppm within the plume. MW-101 has a dissolved oxygen measurement of 1.67 <br /> PPM. <br /> • Groundwater analyses of MW-101 suggest there are no gasoline range petroleum <br /> hydrocarbons impacting deep groundwater at this site. The thick clay found during the <br /> ' installation of the deep monitoring well should form a barrier to contaminant migration. <br /> • MTBE plume has moved downgradient from the source, the former USTs. However, <br /> MTBE concentrations are low and potential risks are negligible <br /> i <br />
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