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ARCHIVED REPORTS XR0003073
EnvironmentalHealth
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2900 - Site Mitigation Program
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PR0508132
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ARCHIVED REPORTS XR0003073
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Entry Properties
Last modified
10/10/2018 10:22:55 AM
Creation date
10/10/2018 9:02:40 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS XR0003073
FileName_PostFix
XR0003073
RECORD_ID
PR0508132
PE
2957
FACILITY_ID
FA0007953
FACILITY_NAME
CHEVRON #9-5775
STREET_NUMBER
301
STREET_NAME
KETTLEMAN
STREET_TYPE
LN
City
LODI
Zip
95240
APN
04514002
CURRENT_STATUS
01
SITE_LOCATION
301 KETTLEMAN LN
P_DISTRICT
004
QC Status
Approved
Scanner
TMorelli
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EHD - Public
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Chevron Products Company 8 <br />Former Chevron Service Station 95775 301 West Kettleman Lane Lodi, California March 30, 2000 <br />Water level changes caused by barometric pressure were minimal in wells MW -5B <br />and MW -8B, which are screened in the deeper water -bearing zone (>80 feet bgs) <br />during the performance of the constant -rate pumping test No barometric pressure <br />correction was applied for the constant -rate pumping test data of these deep wells <br />Water level changes caused by barometric pressure were evaluated for water level <br />measurements collected in wells MW -1, and MW-14/EX-2, which are screened in the <br />shallow water -bearing zone, and MW -5A, which is screened from 70 to 75 feet bgs <br />Barometric corrections were applied during the evaluation of the constant -rate <br />pumping test data, by estimating the barometric efficiency, calculating a barometric <br />correction factor, and subtracting the barometric correction factor from observation <br />well water levels Barometric efficiency (Be) and the barometric correction factor <br />(Bc) were calculated from late time recovery data for each well using the following <br />relationships <br />Be = AH(t) / AB(t) <br />Bc =Be x AB(t) <br />where, AB(t) is the change in barometric pressure at time t, and AH(t) is the change in <br />head at time t Corrected drawdown data was then plotted with barometnc pressure <br />. curves and uncorrected drawdown data to evaluate the effects of the barometric <br />pressure correction <br />0 <br />Estimated barometric efficiencies for the unconfined observation were determined to <br />be approximately 72 percent for MW -1 and 80 percent for MW-14/EX-2 No clear <br />relationship could be established between barometric pressure fluctuations and water <br />level fluctuations in wells MW -1 or MW -5 Based on this, correction of data for <br />barometric efficiency was not performed for data collected from MW -1 or MW -5 <br />Barometric efficiency plots are presented on Figures 10 through 12 The barometric <br />pressure changes shown in the figures are in feet H2O Plots of uncorrected and <br />corrected drawdown versus time for observation wells MW -1 and MW-14/EX-2 <br />during the constant -rate pumping test is presented as Figures 13 and 14 <br />To evaluate the effect of regional fluctuations in groundwater levels during the <br />pumping test, water levels were monitored electronically in observation wells during <br />the background phase Background phase pumping data indicate that site water levels <br />fluctuate in the observation wells Based on G -R's continuous momtonng conducted <br />in 1999 and SECOR's observations during background momtonng, these water level <br />fluctuations were most likely attnbuted to the effect of periodic pumping Well 12 <br />Because of the influence of pumping from the mumcipal well, sufficient data over a <br />significant time period (i e, 7 days) could not be collected As such, regional water <br />level (antecedent) trends during the background phase could not be determined <br />[ IChevron1957751Agwfer test\Revised195775Aqutfertestrevised doc <br />
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