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1 <br /> Corrective Action Plan <br /> Prior to the monitoring well installation, in November 1989, a soil boring designated as B-9 had <br /> been drilled adjacent to the UST. Analyses of soil samples collected during the drilling of soil <br /> tboring B-9 and the adjacent monitoring well MW-1 (now BEI-MW3) indicated the soil was <br /> impacted from near the surface to a depth of more than 20 feet bgs. The highest concentrations <br /> of TPHg were found at a depth of 15 feet bgs. Also, in both borings near the former UST, the <br /> ' elevated TPHg concentrations were evident in samples taken as high as 5 feet bgs. This <br /> occurrence indicates the petroleum release may have resulted from a leaking dispenser or piping <br /> ' most likely located in the immediate vicinity of the UST. <br /> The wells installed by Greg Drilling for Blymer were completed at a depth of approximately 30 <br /> ' feet bgs. The water table at the time of well installation was approximately 20 feet bgs. The <br /> wells were screened from 15 feet bgs to the bottom. Casing size for the Blymer monitoring wells <br /> has been reported at different times as either 2-inch-diameter or 4-inch-diarneter. Field <br /> ' observation has shown, however, that they are, in fact, 4-inch-diameter wells. The well <br /> construction data for all monitoring wells associated with the site investigations are summarized <br /> in Table 2. <br /> ' With respect to groundwater gradient and flow direction, monitoring well BEI-MW3 is <br /> considered to be located at the source, At various times during the groundwater monitoring <br /> tperiod, well BEI-MW2 has been downgradient and crossgradient. BEI-MW1 has been both <br /> upgradient and crossgradient of the source. <br /> », In November 1991, SRK installed three monitoring wells and two test borings. The monitoring <br /> wells are designated on the site plan(Figure 2) as SRK-MW1, SRK-MW2, and SRK-MW3, the <br /> t test borings as SRK-BH1 and SRK-BH2. During drilling of the wells and test borings, soil <br /> samples collected from depths of 15 feet and 30 feet bgs from each boring were analyzed. No <br /> hydrocarbon concentrations were detected in any of the samples (see Table 1). During the time <br /> t of drilling, the depth to the water table at the site was approximately 24-25 feet bgs. The wells <br /> were completed at depths of 38-39 feet bgs and were screened from 23-24 feet bgs to the bottom. <br /> The sand pack in these wells extended approximately 5 feet above the screen. The wells were 4- <br /> inch-diameter casing installed in a 10-inch-diameter boring. Well construction details are <br /> summarized in Table 2. <br /> With respect to groundwater gradient and flow direction, monitoring wells SRK-MWI and SRK- <br /> MW2 have, at various times during the monitoring period (1991 to the present), ranged between <br /> upgradient and crossgradient of the source. SRK-MW3 has generally ranged between <br /> ' crossgradient and upgradient of the source. <br /> ' In April 1996, Park installed two monitoring wells on the Union Pacific Railroad property <br /> immediately adjacent and south of the site. The wells are designated as MW-7-P and MW-8-P. <br /> Their respective locations are illustrated on the site pian(Figure 2). Soil samples collected during <br /> ' the installation of these wells were analyzed at the depths of 10, 15, and 20 feet bgs. Elevated <br /> hydrocarbon concentrations (101 mg/kg TPHg) were detected in the soil sample collected from <br /> OST <br /> 701-1-2.cap Page 5 <br />