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ARCHIVED REPORTS XR0012580
Environmental Health - Public
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3500 - Local Oversight Program
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PR0544482
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ARCHIVED REPORTS XR0012580
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Last modified
5/20/2019 5:51:49 PM
Creation date
5/20/2019 4:11:47 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0012580
RECORD_ID
PR0544482
PE
3528
FACILITY_ID
FA0000556
FACILITY_NAME
CHEROKEE LANE SERVICE STATION*
STREET_NUMBER
900
Direction
S
STREET_NAME
CHEROKEE
STREET_TYPE
LN
City
LODI
Zip
95240
APN
04742007
CURRENT_STATUS
02
SITE_LOCATION
900 S CHEROKEE LN
P_LOCATION
02
P_DISTRICT
004
QC Status
Approved
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Page 10 <br /> --� February 6, 1990 <br /> Job No.211-71-6 <br /> :he course of the test. The minor water level fluctuations observed in MW-25 are small and may or may not have <br /> been the result of drawdown due to the pump test, therefore, the data from well MW-25 are not reliable and <br /> were not analyzed. <br /> The drawdown and recovery data from well RW-1 were analyzed by the Jacob Approximation-Method (Cooper +. <br /> and Jacob, 1946)to detennine the aquifer properties of the uppermost unconfined aquifer in the vicinity of the <br /> subject site- Due to the large drawdown relative to the original aquifer thickness observed in recovery well <br /> RW-1, the drawdown and residual drawdowr data from the recovery well were corrected using the fo:lowing ',• <br /> method by Jacob(1944): <br /> - s' (s2/2b) i <br /> where , <br /> s' = Corrected drawdown (ft.) <br /> s = Observed drawdown (ft.) <br /> b = Original aquifer thickness (ft.) <br /> Appendix C contains the calculations used to determine the aquifer properties of the uppermost unconfined <br /> aquifer in the vicinity of the subject site. Based on our analysis of tine data from recovery well RW-1,the shallow, <br /> unconfined aquifer is predicted to exhibit the following average characteristics: <br /> Transmissivity- 170 gal./day/ft. ' <br /> Hydraulic Conductivity- 11 gal./day/ft' <br /> �'•1: <br /> Due to the relatively large distance of 94.6 feet between monitoring well MW-16 and recovery well RW-i,and ,. <br /> the low transmissivity predicted for the shallow aquifer at the site, the Jacob Approximation Method could not i. <br /> be used to analyze the tranxient portion of the drawdown curve for well MW-16. An attempt was made at . <br /> analyzing the drawdown data from well MW-16 using the type curve matching techniques described by Newman k <br /> (1975), however, the drawdown curve could not be matched to any of the type curves for unconfined aquifers. <br /> Du: to the relatively minor response of MW-16 to the ag7!ifer test and the effects of heterogeneities that <br /> probably exist in the natural aquifer system which are riot allowed for in general well hydraulic theory,it is our <br /> opinion that reliable aquifer parameters cannot be obtained through the analysis of the drawdown data from - ,,{ <br /> well MW-16. <br /> - Carmare Zone Analysis s <br /> Based on shallow ground-water levels measured at the subject site by Du Pora Environmental Services (1989a) <br /> on September 14, 1989,the ground-water gradient in the vicinity of well RW-1 is directed towards the southeast <br /> ------ ------- ----:at a-magnitude-of-approximately-0.024-foot-per-foot-(see Figure --7 ,, <br /> dimensions under the ground-water gradient that existed across the site on September 14, 1989 are calculated <br /> to give a downgradient radius'of 220 feet and a capture zone width of 690 feet(Appendix C). Table B lists the <br /> predicted capture zone dimensions for a variety of discharge rates based or a ground-water gradient magnitude , <br /> Du Pont Environmental Services <br />
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