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ARCHIVED REPORTS_XR0009427
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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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. --------.. <br /> A S S O C I ATE 5 INC . <br /> ATC discharged the extracted groundwater directl�to e City of Stocktonsewer system under <br /> an existing permit. The pumped groundwater was discharged into the sanitary sewer using an <br /> s access point approximately 30 feet north of well MW-3. Pumping test field notes are contained in <br /> Appendix B. <br /> 2_2 Analysis of Aquifer Test Data <br /> The constant discharge aquifer test is the most useful method to determine the aquifer parameters of <br /> hydraulic conductivity (K), transmissivity (T), and storage coefficient (S) in the water-bearing layer. <br /> The groundwater pumping rate during the pilot test, as measured-by-the-flow-meter, averaged <br /> approximately 3 gallons per minute (gpm) for the first half of thertest and 5.5 gpm for the second half <br /> s of the test. The collected data were analyzed using AQTESOLVTm-groundwater modeling:software <br /> and a recovery test analysis. <br /> r 2_3 Analysis of Aquifer Test Data using A TESOLVT' <br /> `. The aquifer parameters transmissivity and storage coefficient were calculated using AQTESOLVTm <br /> software. Drawdown data were used in solving for the aquifer parameters. Data from three <br /> observation wells were used for analysis because only wells MW1, MW3, and MW4 showed <br /> 4r r=;r significant drawdown during the aquifer test. Groundwater elevations measured in well MW5 showed <br /> no significant drawdown. Groundwater elevations measured during the test were recorded by <br /> transducers and are contained in Appendix D with the AQTESOLVTm input data. The aquifer <br /> E thickness was assumed to be an avof T7fe-ef based on approximate length of the water column <br /> in the wells. 7 <br /> { The Cooper-Jacob type-curve solutiotrfor--atr unconfined aquifer was used to estimate aquifer <br /> parameters. The results are presented in Table 5. Time versus drawdown plots using the Cooper- <br /> Jacob unconfined aquifer solution for each well are presented in Appendix E. <br /> The obtained results for the storage coefficient using the Cooper-Jacob solution were a little lower than <br /> expected for an unconfined aquifer. The storage coefficients for unconfined aquifers are typically <br /> between 0.01 and 0.3, while those for confined aquifers are typically between 0.00005 and 0.005 <br /> .1- <br /> (Driscoll page 210, 1986). The average storage coefficient calculated using the Cooper-Jacob solution <br /> f was 0.0015. Although the storage coefficients were lower than expected, this method was considered <br /> f, appropriate for the site conditions. <br /> The average hydraulic conductivity values(0.001 meters per second [m/s]) calculated and presented in <br /> u Table 5, fall within the average range for fine to coarse sand(1 to 10"5 m/s)(Driscoll page 74, 1986). <br /> 2_4 Radius of Influence of A uifer Test <br /> The observed maximum drawdown in each of the four observation wells was plotted against the <br /> distance of each well from well MW-4. Based on the observed data, the radius of influence for <br /> w:%62574.02Veports\RPT-pump test.dw 4 <br /> F-- <br />
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