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ARCHIVED REPORTS_XR0011159
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0506171
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ARCHIVED REPORTS_XR0011159
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Last modified
1/9/2020 5:10:36 PM
Creation date
1/9/2020 4:27:54 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0011159
RECORD_ID
PR0506171
PE
2950
FACILITY_ID
FA0003863
FACILITY_NAME
SOHAL #3
STREET_NUMBER
2494
Direction
E
STREET_NAME
FREMONT
STREET_TYPE
ST
City
STOCKTON
Zip
95205
APN
15328008
CURRENT_STATUS
02
SITE_LOCATION
2494 E FREMONT ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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CA IA <br /> 1 The distances from the pumping well to the observation wells were large, requiring a <br /> significantly longer pumping duration <br /> 2 The diameter (2-inch) of the pumping well limited pumping equipment The pump <br /> capacity was less than the yield of the aquifer <br /> 3 Sand and silt within the pumping well inhibited pump operation The pump had to be <br /> raised to operate effectively Therefore, the aquifer's entire thickness could not be <br /> utilized to determine maximum yield and drawdown <br /> Since significant pumping influence was not discernible in the observation wells, water level <br /> analysis is limited to well S-1-85 recovery data analysis Cambria analyzed the recovery data <br /> using AquiferTest for Windows® version 3 01 software from Waterloo Hydrogeologic, Inc <br /> Appendix I presents the analysis reports The aquifer appears to be confined based on boring <br /> logs and pump test data Step discharge test recovery data from well S-1-85 were analyzed by <br /> the Theis Recovery method to estimate the transmissivity and hydraulic conductivity of this <br /> water-beanng zone The Theis Recovery method assumes the following <br /> 1 The aquifer is confined and has an apparent infinite extent (a correction can be made <br /> for an unconfined aquifer within the analysis program) <br /> 2 The aquifer is homogenous, isotropic, and of uniform thickness over the area <br /> influenced by pumping <br /> 3 The piezometric surface was horizontal prior to pumping <br /> 4 The well is fully penetrating and pumped at a constant rate <br /> 5 Water removed from storage is discharged instantaneously with decline in head <br /> 6 The well diameter is small, so well storage is negligible <br /> Since the aquifer may not be of uniform thickness, the wells may not fully penetrate the water- <br /> bearing zone, and the aquifer wasn't adequately stressed, the assumptions are not completely <br /> satisfied, and the results should be considered approximate The hydraulic conductivity and <br /> transmissivity yielded from the Theis Recovery analysis of well S-1-85 step test data are 25 7 <br /> meters per day (m/day) and 165 meters squared per day (m2/day) This hydraulic conductivity is <br /> between medium-and coarse-grained sand (Todd, 1980) <br /> The limiting factors encountered during testing of well S-1-85 discussed above were also <br /> encountered during testing of well S-1 The results were similar, therefore, analysts is similarly <br /> limited as discussed above During the S-1 step test and constant rate test, water level data in <br /> well S-3 and S4 fluctuated approximately 0 1 feet This fluctuation is believed to be within the <br /> natural background fluctuation of the water table The effect on water levels in wells S-3 and S-4 <br /> due to pumping from well S-1 is not readily discernible <br /> 0797 9 <br />
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