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ARCHIVED REPORTS XR0002741
Environmental Health - Public
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3500 - Local Oversight Program
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ARCHIVED REPORTS XR0002741
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Last modified
11/7/2018 9:20:41 AM
Creation date
11/6/2018 3:31:51 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002741
RECORD_ID
PR0508502
PE
3526
FACILITY_ID
FA0008117
FACILITY_NAME
ARCO STATION #4932
STREET_NUMBER
16
Direction
E
STREET_NAME
HARDING
STREET_TYPE
WAY
City
STOCKTON
Zip
95204
APN
13902001
CURRENT_STATUS
01
SITE_LOCATION
16 E HARDING WAY
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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Atlanc Richfield Company 9 <br /> ARCO 4932, 16 E Huding Way,Stockton CA lune 7 2002 <br /> Soil stratigraphy at the proposed depths specified within SECOR's January 15, <br /> 2002 work plan and the SJCEHD February 14, 2002 letter within the boreholes <br /> for extraction well EW-1 and deep well DMW-1 consisted of silty sand In <br /> order to prevent the possible migration of petroleum hydrocarbon-impacted <br /> ' groundwater Into deeper zones, the borehole for well EW-1 was filled with <br /> bentonite through the sandy silt layer encountered between approximately 45 <br /> feet and 50 feet bgs, and completed within the sandy silt/clayey silt layer at <br /> approximately 44 feet bgs For the same reason, well DMW-1 was advanced <br /> through encountered layers of silty sand and sand between approximately 73 <br /> feet and 80 feet bgs, and completed within a clayey silt layer at approximately <br /> 81 feet bgs <br /> Within the past work plan submittals, SECOR proposed that the extraction wells <br /> 1 would be installed with a 4-Inch diameter casing Well EW-1 was constructed <br /> with a 6-Inch casing to increase the volume for the future removal and treatment <br /> of petroleum hydrocarbon-impacted groundwater beneath the site <br /> ' • Logging of Soil. Instead of logging soil at 5-foot intervals as proposed within <br /> the past work plan submittals, soils were continuously logged between 50 feet <br /> and 81 feet bgs in the boring for deep well DMW-1, and between 20 feet and 50 <br /> feet bgs in the boring for extraction well EW-1 to evaluate soil stratigraphy <br /> beneath the site <br /> RESULTS OF AQUIFER TESTING <br /> The purpose of this test was to evaluate hydrogeologic conditions beneath the site and to <br /> determine whether GWE is a feasible alternative for remediating dissolved petroleum <br /> hydrocarbons and MtBE in groundwater beneath the site <br /> Methodology <br /> Prior to beginning the step drawdown and constant rate pumping tests, pressure <br /> transducers with built-in data-loggers were installed in pumping well GWE-1 and <br /> ' observation wells MW-1, MW-2, MW-4, and 1\4W-6 on April 1, 2002 to monitor water <br /> levels before, during, and after aquifer testing (Figures 2 and 3) The data-loggers were <br /> programmed to record water level depths at one-minute intervals <br /> A step-drawdown test was conducted on April 2, 2002 using a submersible pump in <br /> well EW-1 Prior to the start of the test, water levels in pumping well EW-1 and the <br /> four observation wells (MW-1, MW-4, MW-6, and MW-7) were monitored Well EW- <br /> 1 was subsequently pumped for a specified period at different pumping rates (steps) <br /> while monitoring changes in the water level in the pumping well The water levels and <br /> corresponding times were recorded during each step to allow for analysis of the <br /> ' drawdown attributed to each step, and to provide information needed for the selection of <br /> an optimum pumping rate for the constant-rate pumping test The optimum pumping <br /> ' IIARCO149321Reports\Asmt&AgfrTstRpt doc <br />
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