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ARCHIVED REPORTS_XR0003102
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ARCHIVED REPORTS_XR0003102
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Last modified
2/6/2020 2:58:24 PM
Creation date
2/6/2020 9:03:43 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0003102
RECORD_ID
PR0527643
PE
2960
FACILITY_ID
FA0005232
FACILITY_NAME
TONY GONZALES TRUCKING INC
STREET_NUMBER
1855
STREET_NAME
JACKSON
STREET_TYPE
AVE
City
ESCALON
Zip
95320
APN
22715406
CURRENT_STATUS
02
SITE_LOCATION
1855 JACKSON AVE
P_LOCATION
06
P_DISTRICT
004
QC Status
Approved
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SJGOV\sballwahn
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EHD - Public
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f <br /> A <br /> Mr. Marty Hartzell <br /> Page 5 of 10 <br /> water were recorded in the observation wells during the test. The influent vapor sample contained <br /> 1,900 ug/1 TPHg. <br /> The IC Engine was also operated on VW2 for 8'.hours on December 13, 2001 and 8 hours on <br /> December 18, 2001. Flow rates fluctuated over a wide range during these to days, from 10-50 cfm on <br /> December 13 and from 15-80 cfin on December 18. The flow rate-on December 18 was never steady <br /> at 80 cfm, rather it bounced rapidly between 20-80 cfm during the first two hours of the test before <br /> stabilizing at between 15 and 35 cfm. Applied vacuums ranged from 20-45 inches of water on <br /> December 13 and 22-52 inches of water on December 18. Applied vacuums ranging from 0.3 to 0.8 <br /> inches of water were measured in observation well VW l a and applied vacuums of 0.5 to 1.1 inches of <br /> water were measured in well VWIb. Hydrocarbon vapor concentrations with the PID ranged from <br /> 385 to 651 ppm. The TPHg concentration in influent vapor samples collected on December 13 and <br /> December 18 was 2,100 ugll for both samples. <br /> Table 2 lists the physical data measured during the VET. Analytical data are summarized in Table 3. <br /> Laboratory data sheets and chain of custody documentation are included in Attachment D. <br /> EVALUATION OF TEST RESULTS <br /> Estimated Radius of Influence <br /> The effective radius of influence (ROI) for soil vapor extraction has been defined as the radial <br /> distance from a vapor extraction well at which recorded vacuum levels suggest that subsurface air <br /> flow occurs and is presumed to be sufficient for remediation. Most R01 concepts assume that <br /> subsurface air flows through homogeneous and isotropic soils and that short circuiting effects are <br /> negligible. Conventionally, the ROI is calculated for horizontal flow. However, flow should occur <br /> in three dimensions despite the attenuating effects of anisotropic sedimentary bedding. <br /> Methods for estimating an effective ROI vary due to the complexity of modeling the vapor <br /> extraction process. It is widely thought that an induced vacuum of 0.50 inches of water should be <br /> sufficient to induce subsurface airflow within the zone of influence for sandy soil types. Therefore, <br /> to determine the ROI one can plot the observed induced vacuum response as a function of the <br /> distance from the extraction well on a semi-log graph. A straight line is fit to the plotted data. The <br /> radial distance corresponding to the value of the cut-off vacuum (0.5 inches of water) is interpolated <br /> to be the effective ROI for a given extraction well at a certain applied vacuum. <br /> Air-flow modeling studies conducted by others suggest that the distance from the extraction well at <br /> which 1 percent of the applied wellhead vacuum persists should be sufficient to induce subsurface <br /> airflow and can be interpreted as an effective ROI (Chevron Research and Technology Company, <br /> Environmental Group, October 10, 1991). This method is based upon theoretical model <br /> predictions, which project that roughly 90 percent of the total air extracted from the well flows <br /> through soils within the radius of influence when a I% cut-off is used. The effective ROI is then <br /> G:XDmaIGRO[1NUZEgo ittlReporu5VETRPT doe <br />
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