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ARCHIVED REPORTS_XR0008363
Environmental Health - Public
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3500 - Local Oversight Program
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PR0545864
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ARCHIVED REPORTS_XR0008363
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Last modified
7/21/2020 9:57:46 AM
Creation date
7/21/2020 9:40:00 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0008363
RECORD_ID
PR0545864
PE
3528
FACILITY_ID
FA0004530
FACILITY_NAME
MARLOWE PROPERTY
STREET_NUMBER
4648
STREET_NAME
WATERLOO
STREET_TYPE
RD
City
STOCKTON
Zip
95215
CURRENT_STATUS
02
SITE_LOCATION
4648 WATERLOO RD
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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28 April 1995 <br /> AGE-NC-95-0103 <br /> Page 7 of I 1 <br /> I5 1 4 MONITORING ACTIVITIES <br /> I Monitoring of vapor extraction systems involves weekly measurement of Vapor concentrations at <br /> the inlet to the destruction unit and periodic service and repair Systems can be equipped with <br /> automatic telecommunication system to alert the operator of system malfunction or failure Vapor <br /> samples should be collected monthly to monitor the efficiency of the remediation program When <br /> the concentration of extracted vapors decreases and stabilizes after se,,eral months of operation, <br /> borings are drilled to collect soil samples for quantitatv,e analysis in the laboratory <br /> 51 5 FEASIBILITY <br /> Generally, a vacuum of l-inch of Dater is required to successful]) Nolatillze subsurface <br /> hydrocarbons The nlaxnnum vacuum measured at NMI-I and NIW-3 (at 1800 rpm) Naas plotted <br />' versus the distance of each Nell from the extraction x\ell Figure 4 is a graph of distance \s <br /> vaCUL1111. for 11ff-1 and MW-3 Drawing a best-fit line throuoh these data points will deteiimne <br /> the effective radius of influence at this site r <br /> I <br /> Frons Figui e 4, the effective radius of influence at the site appears to be approximately 29 feet <br /> Figure 4 predicts a vacuuni of less than our detection le\el in NIW-2, corresponding to field data <br /> A vacuum of 33 inches is predicted at M-1, corresponding to t,,pical \acuum generated by a <br /> VES The screened inter\al of the monitoring wells, \Oic11 ,\ere used as observation ��ells for this <br /> test, is at and belox� the screened interval of VW-1 therefore, observations form these hells <br /> should be indicati\e of conditions at the site <br /> Peti oleum hydrocarbons N\ere detected in soil samples ti oin V\\-I at depths of 25, 35 and 45 <br /> feet Most of the petroleum h)di ocai bon impacted soil is �N ithin 15 feet of the bottom of the <br /> former UST cavity HoN�e\er, small concentrations of toluene and xylenes are present at a depth <br /> of 45 feet Plugging or filling the bottom 25 feet (72 to 47 feet depth) of VW-1 will facilitate a <br /> more effective iemediation rate, targeting the impacted zone <br /> Petroleum hydiocarbons were not detected in soil samples from X IW-3 or 11911'-4 However, Iow <br /> concentrations of petroleum hydiocaibons weie detected in Nff-1 at a depth of 45 feet <br /> Therefore, the impacted soil appears to be limited to the area immediately around the former UST <br /> Iexcavation, apparently within a 20-foot radius <br /> I A drawback of vapor extraction is that the i ernediation rates will vary depending on the <br /> characteristics of soil layers For instance, sandy soil Nvill cleanup more quickly than more <br /> fine-grained soil, such as silt or clay This method is not usually effective rn soils Nvith 111911 clay <br /> content <br /> I <br />
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