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ARCHIVED REPORTS XR0001671
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2900 - Site Mitigation Program
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PR0522479
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ARCHIVED REPORTS XR0001671
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Last modified
5/17/2019 2:48:32 PM
Creation date
5/17/2019 2:20:45 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0001671
RECORD_ID
PR0522479
PE
2957
FACILITY_ID
FA0015299
FACILITY_NAME
GEWEKE LAND DEVELOPMENT & MARKETING
STREET_NUMBER
16
Direction
S
STREET_NAME
CHEROKEE
STREET_TYPE
LN
City
LODI
Zip
95240
APN
04323013
CURRENT_STATUS
01
SITE_LOCATION
16 S CHEROKEE LN
P_DISTRICT
004
QC Status
Approved
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EHD - Public
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Workplan for Completion of an Aquifer Test <br /> 16 South Cherokee Labe, Lodi, California <br />' 2.1 Preliminary Pump Test <br />' A preliminary pump test will be performed prior to conducting the full-scale constant-rate <br /> aquifer test This preliminary test will be used to determine acceptable pumping rates (well <br /> yield), maximum anticipated drawdown in the extraction well, and to ensure that location <br />' of observation wells are appropiate to observe sufficient drawdown and produce useable <br /> data <br /> 2.2 Constant-Rate Aquifer Test <br /> The constant-rate aquifer test will be conducted a minimum of 24 to 48 hours after the <br />' completion of the preliminary pump test to allow for the water table to return to its static <br /> water level <br /> tBased on previous groundwater sampling results and well construction data, GeoAudit <br /> proposes to utilize Well EW-1 as the extraction well for the constant-rate aquifer test <br /> (Figure 2) Historically, six of the fifteen existing wells at the site (MW-1 through MW-6) <br /> were dry or contained little water column and exhibit slow recharge rates Due to these <br /> factors, we do not recommend using these wells as primary observation wells for the <br /> constant-rate aquifer test We propose to utilize Wells MW-7, MW-8, MW-9 and MW-14 <br /> . as primary observation wells The well screening intervals, total completion depths, and <br /> radial distances from the extraction well are presented in Table 1 <br /> During the pump test, drawdown in the extraction and observation wells will be measured <br /> using a datalogger equipped with pressure transducers The pressure transducers are placed <br /> near the bottom of each well where they measure the pressure exerted by the overlying <br /> water column (head) The pressure transducer and datal6gger measure the head to <br /> hundredths of a foot Once the aquifer test has been completed, the data stored in the <br /> datalogger is downloaded to a personal computer for analysis <br /> We propose to analyze the raw test data using the modified non-equilibnum method <br /> (Cooper and Jacob, 1946) In accordance with this method, data plots of drawdown versus <br /> time will be prepared on semi-loganthmic graphs and best-fit lines will be used to estimate <br /> aquifer transmissivity <br /> Because water will be extracted at a constant rate from Well EW-1 and drawdown <br /> measurements will be collected from the observation wells during the test, a distance- <br /> drawdown graph can also be prepared The distance-drawdown graph will be used to <br /> estimate the aquifer transmissivity independently of the those determined by time-drawdown <br /> Plots The radius of influence (i a capture zone) will also be estimated using the distance- <br /> drawdown graphs <br /> QwI081-1 Audit Semces Inc. <br /> CMS/Geweke wpl 2 <br />
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