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ARCHIVED REPORTS_XR0006239
EnvironmentalHealth
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2900 - Site Mitigation Program
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PR0540885
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ARCHIVED REPORTS_XR0006239
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Last modified
4/10/2020 5:06:30 PM
Creation date
4/10/2020 3:03:25 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0006239
RECORD_ID
PR0540885
PE
2960
FACILITY_ID
FA0023381
FACILITY_NAME
FORMER EXXON SERVICE STATION NO 73942
STREET_NUMBER
4444
Direction
N
STREET_NAME
PERSHING
STREET_TYPE
AVE
City
STOCKTON
Zip
95207
APN
11022017
CURRENT_STATUS
01
SITE_LOCATION
4444 N PERSHING AVE
P_LOCATION
01
QC Status
Approved
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SJGOV\sballwahn
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EHD - Public
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On 18 September 1990 a preliminary pump test was conducted in well RW 1 to establish a sus- <br /> tainable pumping rate for this well. The test lasted about 12 hours and determined that a pump- <br /> ing rate of 3 6 gpm should be used for the actual pump test. Wells RW2 and RW3 were moni- <br /> tored during the preliminary test, but no significant drawdown (more than 0 01 feet) was ob- <br /> served The total drawdown observed in well RW 1 during this initial test was 6.26 feet. <br /> On 19 September, a long-term pumping test was conducted in well RW 1: water was pumped <br /> from the well to a temporary storage tank with a submersible pump. The test was started at 0804 <br /> hours, after all monitoring wells were gauged, and lasted 11 hours During the first nine hours of <br /> the test a pumping rate of 3 7 gpm was maintained; after that, because drawdown was significant <br /> and did not stabilize, the pumping rate was reduced to 2 7 gpm The test was completed at 1905 <br /> ihours Water table recovery measurements were continually recorded for two hours after the <br /> pumping was stopped. During this pumping/recovery test, depths to water in three wells (RWI, <br />' RW2, and RW3) were monitored using two HERMIT SE 1000B electronic data loggers and <br /> three pressure transducers These wells, along with wells MWI and MWS, were periodically <br /> double-checked using a Solinst water level indicator or oil/water interface probe The flow rate <br /> was monitored with an Omega turbine totalizer calibrated to 0 1 gallons Water was discharged <br /> into a 10,000-gallon Baker tank, and after testing it was disposed of in the sanitary sewer <br /> On 20 September a two-hour pumping test was conducted on well RW2 This well was pumped <br /> at the rate of 2 4 gpm, and induced drawdown was monitored in wells RW 1 and RW3. <br /> Pump Test Analysis <br />' To determine the hydraulic properties of the aquifer, recovery data from well RW 1 and draw- <br /> down data from well RW3 (while RW1 was pumped) were used Data from well RW2 were not <br /> used, because the water level fluctuated, and the total observed drawdown of 0.03 feet may not <br /> reflect a real aquifer response to the pumping of RW 1 Recovery data from RW3 were also not <br /> used because a 1-foot thickness of LPH the water table apparently affected its return to initial <br /> level. the water table there did not move up during the first two hours after pumping was <br /> stopped, and it was still about 0 1 feet below the initial static level 20 hours after the test was <br /> concluded <br /> Because the aquifer thickness is unknown, for interpretation purposes it was assumed to be 20 <br /> feet thick, based on well logs RW 1, RW2, and RW3 The aquifer was assumed to be homogene- <br /> ous and unconfined, without horizontal boundaries The results of the tests are summarized in <br /> Table 3 The values differ from well to well, reflecting either the heterogeneous nature of the <br /> alluvial sediments underlying the site or the "well skin" effect that developed during well drilling <br /> and development. <br /> Theis's equation was used to estimate the radius of influence• <br /> R = 1 5(Tt/S)°5 (De Marsily, 1986) <br /> ca�.gn3vau�si� 6 <br />
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