Laserfiche WebLink
Working To Restore Nature <br /> Addendum One to Remedial Action Plan March 1, 1993 <br /> Coca-Cola Former Distribution Facility, Stockton, California 54006.01 <br /> four other borings. Soil type was primarily clayey and sandy silt. Cumulative results of <br /> laboratory analyses of soil samples are summarized in Tables A-1 and A-2, and are listed <br /> ' under October/November 1990 data TPHg was nondetectable in all eleven borings, with <br /> the exception of B-15/VEW-2 and B-16/VEW-3. TPHg in these two borings ranged from <br /> nondetectable to 630 ppm (at 5 feet in B-16/VEW 3). TPHd was nondetectable in all <br /> ' borings except B-14/VEW-1 through B-17/VEW-4, and ranged from nondetectable to 50 <br /> ppm (in B-16/VEW-3 at 15 feet). BTEX was nondetectable in five of the borings, and in <br /> the other six borings ranged from nondetectable to 44 ppm total xylenes (in B-16/VEW 3). <br /> TPHg soil concentration contours at depths of 0 to 30 feet are shown graphically in Plate <br /> 4. PNAs were nondetectable in all of the 14 samples tested, with the exception of B- <br /> 16/VEW-3 which contained 3,500 ppm naphthalene at a depth of 5 feet, as reported in <br /> Table A-2. <br /> In November 1990, the groundwater sample from newly constructed well MW-6 indicated <br /> ' nondetectable concentrations of TPHg, and BTEX. TPHd was detected at a concentration <br /> of 64 ppb. <br /> Preliminary Vapor Extraction Test <br /> In November 1990, a preliminary vapor extraction test was conducted to determine the <br /> ' feasibility of using vapor extraction as a soil remediation alternative (USTEC, September <br /> 1991). The test was conducted on VEW-1 through VEW-4 and MW-1, MW-4, and MW-5. <br /> Applied wellhead vacuums ranged from about 50 to 66 inches of water. Induced vacuums <br /> ' in the observation wells were measured, and ranged from 0.1 to about 6 inches of water. <br /> Distances between wells ranged from 12.5 to 94.5 feet. Extracted soil vapor concentrations <br /> ' were not determined, nor was the effective radius of influence. One year later in November <br /> 1991,four additional vapor extraction wells (VEW-5 through VEW 8)were installed. These <br /> four new wells were not previously tested for a soil vapor extraction system. Boring logs for <br /> ' these four wells were included in the fourth quarter 1991 monitoring report(USTEC, 1992), <br /> but results of soil laboratory analyses for these vapor wells were not available to RESNA <br /> at this writing. <br /> uarterly Groundwater Monitoring <br /> ' Quarterly groundwater monitoring was initiated after the wells were installed. Table A-4 <br /> summarizes depth to water (DTW) measurements and groundwater elevations. DTW <br /> ranges from about 67 feet to about 71 feet, and groundwater elevation is about 52 feet <br /> below mean sea level (MSL). The groundwater flow direction is generally toward the <br /> northeast, at a shallow gradient of about 0.002 feet per foot. <br /> A-4 <br /> 1 <br />