Laserfiche WebLink
UPDATE 28 8-02-94 <br /> Vacuum Influence <br /> As was stated earlier, vapor recovery has removed the lighter <br /> fractions of gasoline range (through ethylbenzene) petroleum <br /> hydrocarbons from the soil and has greatly reduced the petroleum <br /> hydrocarbons dissolved in the ground water beneath this site <br /> Figure 3A represents the vacuum influence generated from the <br /> vapor recovery system, as measured on July 21, 1994 <br /> System Operation. <br /> Prior to turning the system off on December 30, 1993 a flow rate <br /> of 51 cubic feet per minute was maintained by the two blowers <br /> that are placed in series, that exhaust through 2 (in series) 110 <br /> gallon and one 85 gallon activated carbon vapor scrub units The <br /> vapor scrub units are serviced by Exceltran and Cameron Yakima <br /> for change-out and rejuvenation Prior to turning the system off <br /> on December 30, 1993 the system had operated 12847 hours and <br /> recovered an estimated 18 , 191 pounds of gasoline range <br /> hydrocarbons Since turning the system back on on February 16, <br /> 1994 until the last sampling of the system on July 21, 1994 an <br /> additional 131 pounds of gasoline range hydrocarbons has been <br /> recovered Pounds per day recoveries have been reduced to <br /> approximately 0 8 pounds per day, which is approximately 43% of <br /> the production rate prior to the turning the system off on <br /> December 30 , 1993 (1 85 pounds per day) <br /> METHODS AND QA/QC <br /> WELL SAMPLING AND ANALYTICAL TECHNIQUES <br /> Depth to ground water and ground water samples were obtained from <br /> all of the ground water monitoring wells on September 15 , 1993 <br /> Vacuum and depth to water measurements were obtained from all of <br /> the wells on October 27 , 1993 Depth to top of fluid and ground <br /> water measurements were obtained using a clean product water <br /> interface probe The probe, lowered into the well , by an <br /> attached tape calibrated in 0 02 foot intervals, signals at the <br /> contact of floating product and at the top of ground water The <br /> measurement is obtained from the calibrated tape reading adjacent <br /> to a reference point on the casing The probe is cleaned with <br /> trssodium phosphate water followed by a distilled water rinse <br /> before measuring the next well Measurements are started at the <br /> historically cleanest wells and progress to the dirtiest well <br /> All depth to ground water measurements were obtained before <br /> purging the wells for sampling The depth to water is then <br /> subtracted from the elevation of the casing' s reference point for <br /> a corrected ground water elevation A computer generated <br /> gradient program was not utilized The more interpretive <br /> gradient map was developed by calculating the gradient from each <br /> well to all surrounding wells (difference in ground water <br /> elevations/distance between wells) , "l e It MW1 to MW2 , MW1 to <br /> MW3 , MW1 to MW4 , and MW1 to MW6 Depth to ground water data from <br /> MW5 is not used, this well was installed in a slant boring and <br /> page? <br />