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ARCHIVED REPORTS_XR0003169
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0545307
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ARCHIVED REPORTS_XR0003169
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Last modified
2/11/2020 10:11:39 AM
Creation date
2/11/2020 9:04:16 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0003169
RECORD_ID
PR0545307
PE
3528
FACILITY_ID
FA0000932
FACILITY_NAME
DOMINO'S #8588
STREET_NUMBER
305
Direction
S
STREET_NAME
HUTCHINS
STREET_TYPE
ST
City
LODI
Zip
95240
APN
03319020
CURRENT_STATUS
02
SITE_LOCATION
305 S HUTCHINS ST
P_LOCATION
02
P_DISTRICT
004
QC Status
Approved
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SJGOV\sballwahn
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EHD - Public
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Thes <br /> ba is SVE system is composed of a blower or vacuum pump <br /> which draws contaminant vapors to one or more extraction wells <br /> and then through surface manifold piping, valves, and a vapor- <br /> water separator for subsequent delivery to a vapor treatment <br /> unit. Vapors may be captured or destroyed using thermal <br /> incineration, catalytic oxidation, internal combustion, carbon <br /> adsorption, and/or biofiltration. <br /> Bioventing employs the SVE system concept to promote the in- <br /> situ aerobic biodegradation of hydrocarbon contaminants within <br /> vadose soils. This is accomplished by using the SVE mediated <br /> movement of air through the area of soil contamination to deliver <br /> the large volume of oxygen required to develop and maintain <br /> the biomass necessary to accomplish the mineralization (thorough <br /> aerobic biodegradation) of fuel hydrocarbons. It has been <br /> suggested that using air as a mechanism to deliver oxygen to <br /> unsaturated soil could be 1 , 000 times more efficient than <br /> transferring it to water (Wilson and Ward, 1986) . A number <br /> of sources have reported that analysis of SVE systems indicate <br /> that 20-38% of hydrocarbon removal is by biodegradation, with <br /> the remainder occurring by volatilization. Nutrients (primarily <br /> nitrogen and phosphorus) and moisture may also be added to <br /> increase biodegradation rates. The biological destruction <br /> component is particularly appropriate to the remediation process <br /> when the hydrocarbon contaminant is formed, in part, of compounds <br /> that are essentially not volatile. <br /> In order to confirm the applicability of SVE to the subject <br /> site, it is proposed that an additional well be installed in <br /> the immediate area of soil boring EB-11 ( see Figure 2 of text ) . <br /> The well will be constructed in the same manner as the previously <br /> installed groundwater monitoring wells and will be screened <br /> through the area of highest known hydrocarbon contamination <br /> ( 15-25 feet below ground surface) so as to permit acquisition <br /> of data as to the potential rate of treatment of the 1600-11 , 000 <br /> parts per million (ppm) levels of Total Petroleum Hydrocarbons <br /> as Gasoline (TPH-G) and 600-2400 ppm Total Petroleum Hydrocarbons <br /> as Diesel (TPH-D) detected in soil samples acquired from 15, <br /> 20 , and 25 feet bgs during the installation of soil boring EB- <br /> 11 . The extraction well will be fitted with the piping, <br /> instrumentation, and vacuum pump or blower to induce an air <br /> flow of approximately 55-100 cubic feet/minute (CFM) . <br /> System piping will be 4" to 6" diameter Schedule 40 PVC. Flow <br /> control valves and instrumentation to measure flow, pressure, <br /> temperature, and levels of target contaminants will be installed. <br /> Pulse venting is expected to enhance vapor removal efficiencies <br /> 1 and will be employed by operating wells only periodically in <br /> order to allow vapor to diffuse into large areas . <br /> Moisture within the extracted air-vapor stream will be removed <br /> 9 . <br />
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