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ARCHIVED REPORTS_XR0002669
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0545259
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ARCHIVED REPORTS_XR0002669
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Last modified
1/31/2020 5:11:03 PM
Creation date
1/31/2020 3:30:59 PM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0002669
RECORD_ID
PR0545259
PE
3528
FACILITY_ID
FA0004966
FACILITY_NAME
CHEVRON USA (INACT)
STREET_NUMBER
45
Direction
E
STREET_NAME
HARDING
STREET_TYPE
WAY
City
STOCKTON
Zip
95204
APN
12707037
CURRENT_STATUS
02
SITE_LOCATION
45 E HARDING WAY
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
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SJGOV\sballwahn
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EHD - Public
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fringe and in the vadose zone Additionally, oxygen will continue to be supplied to the <br /> subsurface environment When volatilization is no longer a significant contributor to mass <br /> reduction, operation will shift into a low flow configuration This will allow operation that is <br /> tailored toward biodegradation and maintain efficient resou,ce use <br /> According to the EPA, this technique is able to treat large volumes of soil effectively and with <br /> minimal disruption to property use Advantages of this alternative are that it degrades semi- <br /> and non-volatile organic compounds, and it degrades impact in place Also, in biovent mode <br /> potential air emissions are significantly reduced On the down side, the EPA recognizes that <br /> SVE/biovent ng targets only volatile and biodegradable constituents, and effectiveness is <br /> limited in heterogeneous soils The EPA estimates that on average, the lifespan of this tech- <br /> nique (reaching approximately 90 percent mass reduction) is between 1 and 4 years It has <br /> been PACIFIC's experience that, given a properly designed and operated system, the <br /> effectiveness of SVE/bioventing is exhausted within a 3 year period Conditions for <br /> terminating SVE are provided below <br /> An important aspect of implementing SVE as a remedial action is understanding when the <br /> application may be discontinued This should not be confused with terminating remedial <br /> action Operation and maintenance of the proposed WQLZ would continue until specific <br /> criteria are met General criteria for terminating remedial action (including closing the <br /> . proposed WQLZ) is outlined in association with site water quality protection standards and <br /> goals Following is a method by which use of SVE may be terminated <br /> As SVE proceeds, hydrocarbon concentrations in soul vapor decay At a constant extraction <br /> flow rate, concentration decay may be attributed to the decrease in hydrocarbon mixture <br /> volatility and mass, and the limitations imposed by mass transfer mechanisms Typically, <br /> concentration decay continues until an asymptote concentration is reached It is reasonable to <br /> presume the effectiveness of SVE implementation is exhausted when (1)the asymptote <br /> concentration is reached, (2)the asymptote concentration is relatively low (biodegradation is <br /> controlled by hydrocarbon concentrations and availability), and (3) it is shown that hydro- <br /> carbon impact areas were affected SVE influence can be readily documented by collecting <br /> subsurface pressure data and there are methods for identifying a zero trend slope (or asymp- <br /> tote) An asymptote concentration that does not significantly differ from initial concentrations <br /> is also easily identified PACIFIC proposes to terminate implementation of SVE when the <br /> effectiveness is exhausted according to the above criteria <br /> Showing that a true asymptote has been reached will be accomplished in two stages First, <br /> pulsed operation of SVE will be instituted to show that negligible hydrocarbon mass is avail- <br /> able, and that the hydrocarbon mixture left in place is relatively immobile Next, a statistical <br /> test will be completed to show the slope of the hydrocarbon concentration versus time curve <br /> is nearly zero <br /> 320133'IB/1918REV 23 August 31, 1995 <br />
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