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3500 - Local Oversight Program
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PR0545152
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Last modified
1/9/2020 3:04:31 PM
Creation date
1/9/2020 2:59:52 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
WORK PLANS
RECORD_ID
PR0545152
PE
3526
FACILITY_ID
FA0004021
FACILITY_NAME
STOCKTON CITY TAXI CAB COMPANY
STREET_NUMBER
2085
Direction
E
STREET_NAME
FREMONT
STREET_TYPE
ST
City
STOCKTON
Zip
95205
APN
14111223
CURRENT_STATUS
02
SITE_LOCATION
2085 E FREMONT ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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N <br /> ATC Associates Inc. <br /> 1 117 Lone Palm Avenue, Suite 201 <br /> \\V•// Modesto, California 95351 <br /> 209-579-2221 <br /> A 660CIATES INC . <br /> Fax: 209-579-2225 <br /> respect to petroleum hydrocarbon vapors. The vapor extraction wells are screened from 10 to 40 <br /> feet bgs. <br /> The actual radius of influence associated with each vapor extraction well varies depending on <br /> subsurface geologic conditions, the extent and distribution of hydrocarbon-impacted soil , and site- <br /> specific operating conditions of the vapor extraction system. The estimated radii of influence <br /> associated with VEl through VE4, based on the 2005 pilot test, are presented in Figure 7. <br /> 9.2 System Design Specifications <br /> 9.2.1 Vapor Extraction System <br /> The proposed soil vapor extraction system will utilize existing vapor extraction wells VE1 through <br /> VE4 (Figure 3). The extraction system will be operated tinder similar conditions as the previously <br /> conducted pilot tests to achieve similar results. Each vapor extraction well will be incorporated into <br /> the vapor extraction Avell network, howevcr their respective use (duration, episodic cycling, etc.) <br /> will be evaluated based upon vacuum response and vapor concentrations. <br /> The estimated removal rate of TPH observed during the long term pilot test using VE2 as the <br /> extraction well was approximately 8.3 pounds per hour. Thermal oxidation will be employed as the <br /> method of off-gas destruction. Removal rates will be the greatest during the first several months of <br /> system operation and will exceed the allowable emission limit without off-gas treatment. <br /> Subsurface piping will direct extracted vapor from the extraction wells to a nearby remediation <br /> compound (Figure 8). Components of the vapor extraction system located in the remediation <br /> compound wilt ' include the following: a thermal catalytic oxidizing tout containing a vapor <br /> extraction blower, a flow indicator that measures extracted airflow, a condensate separator to <br /> remove entrained droplets of moisture, associated piping, control valves, pressure gauges, flow <br /> inters, instrumentation and controls. The remediation compound wW and equipment will be <br /> surrounded by fencing to preclude public access. Based on ATC ' s experience at similar sites and <br /> the results of the pilot tests, a 250 elfin thermal catalytic oxidizer would be sufficient to operate the <br /> vapor extraction component of the system and remediate the off-gas. The vacuum blower on the <br /> unit would create a maximum vacuum of 14 inches of mercury and an airflow rate of 250 standard <br /> cubic feet per minute. The thermal oxidizer on the Ludt would operate at a minimum temperature of <br /> approximately 1 ,400 degrees Fahrenheit and have a destruction efficiency of 95% to 99%, The <br /> equipment will be staged on a trailer designed for temporary use. <br /> 9.2.2 Remediation System Layout <br /> Components of the vapor extraction system will be located in an enclosed compound in the <br /> northwestern portion of the site depicted on Figure 8. A network of subsurface piping will be used <br /> to convey recovered soil vapor from the four extraction wells to the remediation compound as <br /> shown on Figure 9. Piping will be installed at an estimated depth of two feet bgs. Well vaults will <br /> SVE System Design Plan ATC Associates Inc. <br /> Stockton City Tani <br /> Page 9 <br />
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