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ARCHIVED REPORTS_XR0009417
Environmental Health - Public
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3500 - Local Oversight Program
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ARCHIVED REPORTS_XR0009417
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Last modified
12/11/2019 11:27:39 AM
Creation date
12/11/2019 9:46:26 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0009417
RECORD_ID
PR0545053
PE
3528
FACILITY_ID
FA0005720
FACILITY_NAME
SMITH CANAL PUMP STATION
STREET_NUMBER
2130
STREET_NAME
FONTANA
STREET_TYPE
DR
City
STOCKTON
Zip
95204
CURRENT_STATUS
02
SITE_LOCATION
2130 FONTANA DR
P_LOCATION
01
P_DISTRICT
003
QC Status
Approved
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EHD - Public
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.... ................ <br /> (VATC <br /> ASSOCIATES 1 Nc . <br /> f� <br /> In September 1999, ATC supervised the advancement of soil borings SB-11, S13-12 and - <br /> 13 at <br /> locations approximately 15 feet northwest, south, and northeast of well MW4, respectively. <br /> Analytical data indicated the groundwater sample from soil boring SB-12 was impacted with TPHd at <br /> a concentration of 24,000 ppb. The groundwater samples from SB-11 and SB-13 contained very low <br /> samples indicate that TPHd was present in only the samples collected beto nondetectable concentrations of TPHd. Results of laboratory analyses performed on select tween 14 and 16,5 feet bgs.ed soil <br /> Field observations indicated that the samples at these depths also exhibited the highest FID <br /> measurements. Soil samples SB11-15.5, SB12-16.5, and SBI3-14.0 contained detectable <br /> concentrations of TPHd at 390 ppm, 290 ppm, and 1,100 ppm, respectively. All the remaining soil <br /> samples were not detected. The September 1999 subsurface investigation activities are detailed in <br /> ATC's Summary Report, Subsurface Investigation, dated January 10, 2000. <br /> A groundwater pumping test was conducted during a 24-hour period starting on July 22, 1999 and <br /> ending July 23, 1999. The goal of the groundwater pump test was to provide aquifer data necessary to <br /> characterize the feasibility of operating a groundwater treatment system at the site. The radius of <br /> influence of groundwater extraction, groundwater drawdown, hydrogeologic properties of the aquifer, <br /> and the mass extraction rate of groundwater were to be determined by this pumping test. The results <br /> of the groundwater pumping test showed the radius of influence for groundwater extraction at the site <br /> is greater than 50 feet. Hydrogeologic properties of the aquifer, specifically, hydraulic conductivity <br /> (K), transmissivity (T), and the coefficient of storage (S) were measured. The average hydraulic <br /> conductivity (K) was calculated to be 0.001 meters/second, the average transmissivi <br /> calculated to be 6.79 square feet/minute, the Coefficient of Storage (S) was calculated using o per$ <br /> Jacob solution to be 0.0015. In addition, based on analytical results of samples taken during the <br /> groundwater pumping test, 6,000 gallons of groundwater were extracted from the subsurface, and <br /> 0.00005 lbs. of TPHd were removed from the subsurface during the twenty-four hour test. The <br /> groundwater pumping test activities are detailed in the Summary Report of Pumping Test, dated <br /> September 19, 2000. <br /> FIELD WORK <br /> From April 4 to June 30, 2003, static fluid levels were measured on generally a weekly or bi- <br /> weekly basis in monitoring wells MW1 through MW7. This occurred during groundwater <br /> extraction activities located on the northern adjacent property. On August 12, 2003, after <br /> groundwater extraction activities terminated, static fluid levels were again measured after the <br /> groundwater table had a chance to equilibrate. Table 1 summarizes the water level data collected <br /> during the reporting period and provides previous data for comparison. <br /> A groundwater gradient map was created for each monitoring event (Figures 2 through 10)using <br /> groundwater elevation data from all the wells monitored. Figures 2 through 9 depict a generally <br /> north groundwater flow direction at a magnitude of which ranged from 0.04 to 0.07 or 211 to <br /> 370 feet/mile. Figure 10 depicted a generally north groundwaterflow direction at a magnitude of <br /> 0.01 or 53 feet/mile. <br /> wM2574.0219uaTUYl3gnv2002.doc 3 <br />
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