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ARCHIVED REPORTS_XR0011292
Environmental Health - Public
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3500 - Local Oversight Program
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PR0545145
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ARCHIVED REPORTS_XR0011292
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Last modified
1/9/2020 11:27:19 AM
Creation date
1/9/2020 11:03:14 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0011292
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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t <br /> Geological Technics Inc. Page 3 <br /> Groundwater Monitoring Report <br /> Project No.989.2 <br /> April 30,2003 <br /> 1.2 Laboratory Analyses <br /> ' The groundwater samples collected on November 19, 2002, were delivered to Sherwood <br /> Labs (Department of Health Services Certification No. 1400), of Hilmar, California, for the <br /> following analyses: <br /> ' • Benzene, toluene, ethylbenzene and xylene (BTEX by EPA method 8020/8015(m)) <br /> Gasoline range petroleum hydrocarbons (TPH-G by EPA method 8020/8015(m)) <br /> • Volatile Organic Compounds by GC/MS Fuel (MTBE, DIPE, ETBE, TAME, TBA, 1,2- <br /> DCA and EDB by EPA method 8260) <br /> ' The volatile organic compound samples were submitted by Sherwood Labs to Entech <br /> Analytical Labs of Santa Clara, California(DHS # 2346). <br /> ' The detection limits for these compounds are listed in the laboratory data sheets included in <br /> Appendix C and summarized in Table 2 of Appendix A. A Chain of Custody was <br /> completed for all samples collected and tracked to ensure sample integrity. <br /> On March 3, 2003, the laboratory data were submitted electronically to GeoTracker as <br /> required under AB2886. The confirmation number for the electronic submittal is <br /> 5936293482. <br /> 2.0 FINDINGS AND DISCUSSION <br /> ' 2.1 Hydrology of Site <br /> On February 14, 2003, the depth to groundwater was measured in all of the wells prior to <br /> purging. Depths to groundwater, in the water table wells, ranged from a high of 7,09 feet <br /> below the top of casing to a low of 8.48 feet below the top of casing. The average depth to <br /> water was 8.08 feet below the top of casing and the average groundwater elevation at the <br /> site is 1.02 feet below mean sea level. The wells are screened at 5 feet bgs and groundwater <br /> surface continues to be below the tops of the screens in the nine shallow monitoring wells. <br /> ' Site-specific groundwater gradient was calculated using MW-3, MW-7 and MW-9, and <br /> found to be N30°W at 0.0046 ft/ft. The calculated groundwater gradient is displayed on the <br /> groundwater gradient map, Figure 3. Previous groundwater gradient calculations show a <br /> ' consistent bearing of north-northwest. Bearings have been measured between N05°W and <br /> N45°W at the site and the slope historically averages 0.0050 ft/ft. Historical groundwater <br /> bearing and slope are summarized in Table 1 of Appendix A and are plotted on a Rose <br /> Diagram, Figure 4. <br /> i <br />
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