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ARCHIVED REPORTS XR0008192
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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EL DORADO
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1448
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3500 - Local Oversight Program
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PR0544673
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ARCHIVED REPORTS XR0008192
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Entry Properties
Last modified
8/19/2020 3:39:47 AM
Creation date
7/18/2019 3:44:48 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0008192
RECORD_ID
PR0544673
PE
3528
FACILITY_ID
FA0006182
FACILITY_NAME
REGAL STATION #604
STREET_NUMBER
1448
Direction
N
STREET_NAME
EL DORADO
STREET_TYPE
ST
City
STOCKTON
Zip
95202
CURRENT_STATUS
02
SITE_LOCATION
1448 N EL DORADO ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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vacuum Influence. R604 •UPDATE 20 7-16-1993 <br /> As was stated earlier, vapor recovery has removed the lighter <br /> fractions of gasoline range petroleum hydrocarbons from the soil <br /> (through ethylbenzene) and has greatly reduced the petroleum <br /> hydrocarbons dissolved in the ground water beneath this site . <br /> Figure 5 represents the vacuum influence generated from the <br /> vapor recovery system as measured before obtaining depth to <br /> ground water measurements on June 18, 1993 <br /> System Operatson. <br /> Currently a flow rate that fluctuates between 85 cubic feet per <br /> minute and 90 cubic feet per minute is being maintained through <br /> the two blowers that are placed in series, prior to exhausting <br /> through 2 (in series) 110 gallon and one 85 gallon activated <br /> carbon vapor scrub units These are serviced by Exceltran and <br /> Cameron Yakima for change-out and rejuvenation From May 14 , to <br /> June 18, 1993 the system has operated 703 hours and recovered 288 <br /> pounds of gasoline range hydrocarbons (9 8 pounds per day) <br /> METHODS AND QA/QC <br /> WELL SAMPLING AND ANALYTICAL TECHNIQUES <br /> Depth to ground water and vacuum measurements were obtained from <br /> all of the ground water monitoring wells on May 14 , 1993 Depth <br /> to top of fluid and ground water measurements were obtained using <br /> a clean product water interface probe The probe, lowered into <br /> the well attached to a tape calibrated in 0 . 02 foot intervals, <br /> signals at the contact of floating product and at the top of <br /> ground water The measurement is obtained from the calibrated <br /> tape reading adjacent to a reference point on the casing The <br /> probe is cleaned with trisodi.um phosphate soapy water followed by <br /> a distilled water rinse before measuring the next well <br /> Measurements are started at the historically cleanest wells and <br /> progress to the dirtiest wells . All depth to ground water <br /> measurements were obtained before purging the wells for sampling <br /> The depth to water is then subtracted from the elevation of the <br /> casing' s reference point for a corrected ground water elevation <br /> A computer generated gradient program was not utilized The more <br /> interpretive gradient map was developed by calculating the <br /> gradient from each well to all surrounding wells (difference -.n <br /> ground water elevations/distance between wells) , °3 e " MW1 to <br /> MW2 , MW to MW3 , MW1 to MW4 , and MW1 to MW6 Depth to ground <br /> water data from MW5 is not used, this well was installed in a <br /> slant boring and produced an anomalous high when used From <br /> these gradient lines, data points representing the contact for <br /> the proposed contours are plotted along each individual line <br /> Once the data points have been plotted between all the wells, the <br /> data points representing a given gradient elevation (-45 foot <br /> contour, for example) are connected with site specific factors, <br /> "1 e " incorporating conditions caused by local geology, <br /> hydrogeology, utility trenches, etc These are used to control <br /> the contour between data points This site is presently bung <br /> influenced by vapor extraction at MWS, VSB3 , VSB5, VSB9 and <br /> VS1311 . A vacuum at these wells and surrounding wells will <br /> page 6 <br />
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