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ARCHIVED REPORTS_XR0008558
Environmental Health - Public
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3500 - Local Oversight Program
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PR0545857
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ARCHIVED REPORTS_XR0008558
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Last modified
10/10/2020 10:29:28 PM
Creation date
7/15/2020 2:57:50 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0008558
RECORD_ID
PR0545857
PE
3528
FACILITY_ID
FA0005147
FACILITY_NAME
E-Z FOOD
STREET_NUMBER
2537
STREET_NAME
WATERLOO
STREET_TYPE
RD
City
STOCKTON
Zip
95205
APN
11914035
CURRENT_STATUS
02
SITE_LOCATION
2537 WATERLOO RD
P_LOCATION
99
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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/ <br /> SOIL VAPOR EXTRACTION PILOT TEST <br /> The purpose of the soil vapor extraction (SVE) pilot test is to collect data necessary to <br /> evaluate the performance and determine the effectiveness of, and design parameters for, an SVE <br /> system. The procedures for conducting the pilot test, as well as the data to be collected dung <br /> the test, are described below. <br /> The SVE <br /> pilot test is a 4 to $ hour test conducted on-site at one specific location. The <br /> procedure tests one well while monitoring surrounding wells for a change in pressure. The data <br /> collected during the test will allow Brown and Caldwell design engineers to determine the <br /> applicability of SVE at the site as well as provide the specific data required for design of a SVE <br /> remediation system. <br /> Primary equipment used during the pilot test will consist of a portable vacuum pump <br /> powered by a 5-horsepower electnc motor and a 40 kilowatt 240-volt portable generator to run <br /> the vacuum pump. In addition, flow rate data will be collected during the test using a pitot tube <br /> magnehelic type flow meter and vacuum measurements will be collected using a red guage oil <br /> manometer or calibrated magnehelic capable of reading vacuum. <br /> Emissions from the test will be controlled with granular activated carbon (GAC) consisting of <br /> two 55-gallon GAC drums placed in series. A portable photo-ionization detector (PID) will be <br /> used to momtor the GAC units for breakthrough. If breakthrough occurs, either a fresh GAC <br /> unit will be installed or the test will be terminated <br /> A temporary seal will be prepared for the top of the test well The soil/casing interface <br /> will be sealed with a bentorutelwater slurry to eliminate air leakage around the casing while <br /> flexible hose will be used to connect the well head to the vacuum pump. <br /> Vacuum extraction will be started at a low rate and vacuum will be measured with a <br /> temporary gage on existing monitoring wells, or other SVe wells, surrounding the test well. <br /> After one hour, the rate will be increased and vacuum will be measured again in the monitonng <br /> wells. This process will continue until the maximum rate of the equipment is reached. <br /> Extraction will continue at the maximum or optimum rate for a maximum of S hours, unless <br /> otherwise specified. The total length of the test will depend upon the concentrations of volatile <br /> organic constituents (VOCs) being removed, the extraction rate, and whether or not a sparge test <br /> is conducted. <br /> During the SVE test, total VOC readings will be collected every 15 minutes with a PID <br /> to identify the relative concentrations of total VOCs being removed Total VOC concentrations <br /> based on PID readings will be plotted versus time. Once the concentration stabilizes, a sparge <br /> test could be started. Continued monitoring of VOC concentration would indicate the <br /> effectiveness of the sparging. In addition, a maximum of 3 vapor samples will be collected, in <br /> 1-liter tedlar bags, from a sample tap located at the outlet of the vacuum pump, at selected times <br />
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