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ARCHIVED REPORTS_XR0004599
Environmental Health - Public
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PR0507835
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ARCHIVED REPORTS_XR0004599
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Last modified
3/5/2020 12:41:15 PM
Creation date
3/5/2020 12:01:29 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0004599
RECORD_ID
PR0507835
PE
2950
FACILITY_ID
FA0007793
FACILITY_NAME
SUPER STOP MARKET
STREET_NUMBER
290
Direction
N
STREET_NAME
MAIN
STREET_TYPE
ST
City
MANTECA
Zip
95336
APN
22309101
CURRENT_STATUS
02
SITE_LOCATION
290 N MAIN ST
P_LOCATION
04
P_DISTRICT
003
QC Status
Approved
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SJGOV\sballwahn
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EHD - Public
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GraloguaI Tecknus I= Page 10 <br /> Dual Phase Extraction Pilot Test Report <br /> Project No 662 2 <br /> February 22,2005 <br /> 1 December 6b at 09 40 and the initial extraction was approximately 299 inches of water <br /> vacuum (22 inches Hg x 13 6=299 2) <br /> ' The vacuum influence did extend to the locations of the monitoring points as indicated by the <br /> data in Table 6 The vacuum measured in MW-1 started at 163 inches and eventually rose to <br /> ' 6 12 inches after -22 hours Similarly, the vacuum influence measured in MW-2 started at <br /> 0 27 inches and rose to 0 82, but MW-3 started at 6 80 inches of vacuum and fell to 4 08 <br /> inches by the time 22 hours had elapsed <br /> ' The vapor extraction rate from EW-2 started at 108 cubic feet per minute (cfm) As the <br /> vacuum influence spread through preferential pathways in the subsurface the rate would be <br /> ' expected to increase but it decreased to 79 cfm after -22 hours had elapsed It is noted that <br /> significant rain fall was present on December 6 & 7 at the start of the test and this may <br /> account for less influence as the soils became saturated The decrease in flow coincided with <br /> ' an increase in inches of Mercury(Hg) vacuum <br /> 5.2 Groundwater Extraction <br /> The dual phase extraction equipment removed soil vapor and groundwater together through <br /> the same stinger hose In this fashion the water could not be metered to measure the <br /> extraction rate The extracted water was contained in a tank on the treatment trailer until the <br /> tank's upper limit switch was activated by the rising water level Upon activation, a pump <br /> ' would transfer the water through a meter and into the 5,200 gallon tank trailer supplied by <br /> American Valley GTI staff monitored the transfer meter and used the data to determine <br /> pumping rates by dividing the gallons pumped by the elapsed time Table 5 in Appendix A <br /> ' contains the groundwater pumping rate data In addition, GTI performed field estimates of <br /> pumping rates utilizing a calibrated tube on the trailer's holding tank The volume between <br /> two calibration marks was divided by the time required to fill the tube between the marks to <br /> ' produce the pumping rate These data are included to Table 5 in the "field gpm" column <br /> Note The amount of water extracted listed in Table 5 is 29,009 gallons based on the <br /> treatment system trailer's meter The meter is suspect because the amount transported off <br /> site by American Valley totaled 32,250 gallons based on the truck(s) gauges This latter <br /> amount was confirmed utilizing a meter on the railroad tank car into which the water was <br /> ' pumped by American Valley <br /> ' Solinst Leveloggers®Problems <br /> GTI intended to prepare time draw down graphs to document response to groundwater <br /> extraction But several problems were encountered in using the Solinst Leveloggers® <br /> (Leveloggers) to record depth to groundwater in the wells A Solinst Barologger® was <br /> suspended in well MW--2 to measure barometric pressure during the test period The data <br /> from this unit was to be used to compensate the Leveloggers to remove the effect of <br /> ' barometric pressure fluctuations due to weather changes The Barologger® failed to operate <br /> 1 <br />
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