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ARCHIVED REPORTS_XR0008852
Environmental Health - Public
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EHD Program Facility Records by Street Name
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VAN BUREN
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3500 - Local Oversight Program
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PR0545786
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ARCHIVED REPORTS_XR0008852
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Last modified
6/1/2020 2:34:23 PM
Creation date
6/1/2020 2:02:07 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0008852
RECORD_ID
PR0545786
PE
3526
FACILITY_ID
FA0004969
FACILITY_NAME
CHASE CHEVROLET
STREET_NUMBER
424
Direction
N
STREET_NAME
VAN BUREN
STREET_TYPE
ST
City
STOCKTON
Zip
95205
CURRENT_STATUS
02
SITE_LOCATION
424 N VAN BUREN ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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27 December 1996 <br /> AGE-NC Project No 95-0143 <br /> Page 13 of 19 <br />' 6 1 3 MONITORING ACTIVITIES <br /> One of the potential problems associated with air sparging is lateral spreading of the contaminant <br />' plume Tlus can be caused by either mounding of ground water above injection points or lateral air <br /> flow away from sparging wells To detect this problem, ground water elevations in monitoring wells <br /> and extraction wells (if appropriate) should be monitored on a monthly basis, at the minimum, to <br />' detect mounding and the presence of organic vapor <br /> 614 FEASIBILITY <br /> Remediation of sizeable dissolved ground water plumes requires the installation of a considerable <br /> number of injection and extraction wells An intensive piping network for injection and extraction <br /> must also be installed Aar injection and extraction rates must be balanced to prevent the forced <br /> migration of contaminants However, air sparging has proven itself as a very effective method for <br /> remediation of soil in the smear zone <br /> An in-situ air sparging pilot test was performed for the same client at 423 North Madison Street from <br /> 02 to 07 February 1996 This site is located approximately 600 feet east of the subject property <br /> Installation of monitoring wells has revealed very similar lithology between the two sites Two <br /> sparging wells were supplied with approximately 15 psi of air during the test Induced pressure, <br /> organic vapor concentrations, ground water depth and dissolved oxygen concentrations were <br /> measured at surrounding monitoring wells Ground water samples were collected from monitoring <br /> wells before and after the sparging test Detailed procedures and results of the test were included in <br /> a February11-9 <br /> 96 Corrective Action Plan re aced for the Madison site <br /> i rt Z3 Ma <br /> IIncreased concentrations of organic vapor were observed at surrounding monitoring wells Induced <br /> pressure showed an initial increase during the pilot test, but diminished over the time of the test <br /> Initially, dissolved oxygen increased at the site,but also decreased over the duration of the sparging <br /> test These two anomalies may have been caused by channeling of the air flow from the sparging <br /> points A lower injection pressure, approximately 10 psi, combined with surging the injected air <br /> should be used to minimize the effects of air channeling and promote maximum interaction of the <br /> injected air with ground water A closer injection well spacing would be required with a lower <br /> injection rate Only slight ground water mounding was observed during the sparging test Data from <br /> the air sparging pilot test from the Madison site are included on Table 4 Due to the close proximity <br /> of the test site to the subject property and similar lithology, it is assumed that the two sites would <br /> yield similar "sparging" conditions <br /> Another concern with airsparging is precipitation of iron, which can cause clogging of sparging <br /> points Laboratory analysis of water samples indicated low concentrations of iron in water at the <br /> i <br /> i '� <br />
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