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SITE INFORMATION AND CORRESPONDENCE FILE 1
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0544625
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SITE INFORMATION AND CORRESPONDENCE FILE 1
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Last modified
7/3/2019 8:12:28 PM
Creation date
7/3/2019 4:20:08 PM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
SITE INFORMATION AND CORRESPONDENCE
FileName_PostFix
FILE 1
RECORD_ID
PR0544625
PE
3528
FACILITY_ID
FA0003113
FACILITY_NAME
ZAPIEN MARKET
STREET_NUMBER
4491
Direction
W
STREET_NAME
DURHAM FERRY
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
25504003
CURRENT_STATUS
02
SITE_LOCATION
4491 W DURHAM FERRY RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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I <br /> 1.0 Introduction <br /> Enhanced vacuum recovery (EVR) is the practice of applying negative pressure to a pumping <br /> well to increase groundwater production. Research by Hackenberg et. al., (1994) specifies <br /> that it is theoretically possible to attain a two-fold increase in groundwater production when <br /> EVR is applied to a single pumping well in:a silty aquifer. This paper presents an empirical <br /> study in which a two-fold production increase was not only achieved; it was maintained for <br /> the duration of a 72 hour field test. <br /> The test site is located in the East Bay region of the San Francisco Bay Area in northern <br /> California. At the field test site, aquifer thickness is approximately 28 feet and depth to <br /> groundwater is approximately 23 feet below ground surface (bgs). Gasoline from a leaking <br /> underground storage tank (LUST) had impacted the soils and groundwater at the test site. As <br /> an interim measure, a soil vapor extraction (SVE) system consisting of a blower and activated <br /> carbon beds was placed into operation prior to the implementation of the EVR pilot test. The <br /> SVE remediation was very effective because the vadose soils are comprised of well graded <br /> gravels. Remediation of contaminated groundwater posed a significant challenge because the <br /> unconfined aquifer is predominantly comprised of highly plastic clay. The results of <br /> conventional pump tests conducted on groundwater wells at the site indicated that aquifer, <br /> production could not sustain pumping rates exceeding 0.5 gallons per minute (gpm). One well <br /> was pumped dry in 20 minutes at a discharge rate of 0.3 gpm. <br /> The results of the EVR pilot test reveal a sustained flow of 1 gpm. The EVR method has <br /> influenced the overall groundwater recovery and treatment system design at the test site. .The <br /> observed increase in sustainable flow has reduced the number of recovery wells needed to <br /> capture the contaminant plume, and shortened the estimated time period to complete aquifer... <br /> remediation. <br /> To date, little has been published about EVR. Rippberger (1989) briefly mentions that <br /> increased NAPL flow occurs in wells subjected to vacuum. Theoretical and practical work in <br /> this realm, like that by Hackenberg et. al., (1994), Mastroianni et. al., (1994), and Mastroianni <br /> and Hackenberg (1992) have not been widely applied. Groundwater recovery optimization <br /> methods, such as those discussed by Nolter and Kotziers (1991) and others; commonly <br /> employed LNAPL recovery methods, as presented by Kaluarachchi and Elliot (1995) and <br /> others; as well as SVE optimization modeling; as presented by Benson, et al. (1993), Sepehr <br /> and Samani (1993) and others do not include the use of EVR. <br /> In contrast, Parker (1995) and Schaal (1992) indicate that EVR can be used to remove <br /> LNAPL from wells without smearing well screens and the formation with LNAPL as do <br /> common dual pump water/product systems: Mastroianni et. al., (1994), Mastroianni and <br /> Hackenberg (1992), Millan (1993), and Parker (1995) indicate that LNAPL recovery can be <br /> increased through use of EVR. In these cases, EVR is used to overcome the interstitial pore <br /> pressures that retard LNAPL flow. <br /> 516 <br />
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