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ARCHIVED REPORTS_XR0009427
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0545053
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ARCHIVED REPORTS_XR0009427
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Last modified
12/11/2019 11:23:36 AM
Creation date
12/11/2019 9:49:11 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0009427
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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is <br /> V � <br /> TC <br /> �r <br /> f. _ A <br /> A S S O C I A T E S I N C <br /> groundwater extraction at the site is greater than 50 feet (Figure 4). Observation well MW-1 is <br /> located approximately.46 feet from pumping well MW-4 and the groundwater elevation dropped <br /> about 1.7 feet in this well. Observation wells MW-2, MW-3, and MW-5 are each located <br /> approximately 55 feet from pumping well MW-4 and the groundwater elevation dropped about <br /> 0.7`feet in each of these wells. In general, a small radius of influence is expected for pumping in <br /> an unconfined aquifer. <br /> 2_5 Groundwater Sampling and Analysis <br /> Grab groundwater samples were collected from well MW-4 approximately 7.5 hours after the <br /> start of the pump test and just prior to the completion of the pump test. Groundwater samples <br /> }_ were transferred to appropriate sample containers, using clean, disposable bailers with bottom <br /> r emptying devices to reduce volatilization. Sample containers were then labeled with sample <br /> t identification, placed on ice, and shipped under chain-of-custody to State-certified Sequoia <br /> Analytical for chemical analysis of TPHd utilizing EPA method 8015 modified. Groundwater <br /> analytical results are summarized in Table 2 and laboratory data sheets are presented in Appendix <br /> A. <br /> 3.0 SUBSURFACE CONDITIONS <br /> 3_1 Geology <br /> Soil beneath the site generally consists of gravel fill material from the surface to depths between 2 <br /> to 5 feet bgs. Soil from depths between 2 to 5 feet bgs.and 16 to 25 feet bgs primarily consisted <br /> of clay and silt. Soil from depths between 16 to 25-feet bgs-and approximately 30 to 36 feet bgs, <br /> L< the maximum depth explored, consisted of sand and silt. <br /> 3_2 Hydrosmologv <br /> Water level measurements were collected from wells MW-1 through MW-6 on September 22, <br /> 1999. Water levels ranged from 9.78 to 13.28 feet below the tops of the well casing elevations. <br /> The water level data were used to develop the groundwater elevation contour map (Figure 3). <br /> Assuming that horizontal isotropic conditions prevail, groundwater in the uppermost aquifer <br /> beneath the site flowed towards-th"orthwest. The average hydraulic gradient on September 22, <br /> f 1999 was calculated to Pe 0.007 ft/ft f'r approximately 37 ft/mile. <br /> A summary of groundwater monitoring data is presented in Table 4. <br /> 4.0 ANALYTICAL RESULTS i <br /> '-J The groundwater sample collected from well MW-4 on September 22, 1999 contained a <br /> J <br /> detectable concentration of TPHd at 1,340 ppb. The groundwater sample collected from well <br /> MW-4 on September 23, 1999 contained a detectable concentration of TPHd at 1,170 ppb. <br /> W:62574.02Veports\M-per tecaoc 5 <br />
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