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3.2 Groundwater Monitoring <br /> The depth to groundwater and the calculated elevation of the static water level since 1995 are <br /> shown in Table 1. Groundwater monitoring took place on twice during the quarter. On July 13, KF- <br /> I through KF-5 and Chevron's well MW-8 were surveyed, monitored, and sampled, and a <br /> groundwater gradient map was prepared (Figure 3). Wells KF-6 and KF-7 had not been drilled at <br /> that time. These wells were monitored and sampled on October 17. In order to prepare a valid <br /> gradient map, the depth to the static water level was re-measured in the other wells (except the <br /> Chevron well) at the same time (Figure 4). <br /> Except for the 1-inch diameter wells, a two-stage submersible pump was used to purge the wells. <br /> Water temperature and conductivity were measured during purging. The purged water is stored in <br /> 55-gallon drums on the east side of the property. Depth measurements and purging data are shown <br /> in Appendix C. <br /> After purging, water samples were collected with a disposable plastic bailer and poured into 40-m1 <br /> vials. The vials were labeled, logged, placed in a cooled ice chest, and transported to Sequoia <br /> Analytical for analysis. The laboratory report and chain of custody form are in Appendix D. <br /> 4.0 RESULTS <br /> 4.1 Depth to Groundwater and Groundwater Gradient <br /> The static water level has risen steadily since monitoring began at this site in earl 1995 <br /> g y and the <br /> depth to groundwater now averages about 7 feet. As a result of this rise, the soil-water interface is <br /> now within the upper clay bed (aquitard). <br /> The data in Table 1 were used to contour the piezometric surface and interpret the groundwater <br /> flow direction, which are illustrated in Figures 3 and 4. In July, the gradient arced from north-south <br /> to east-west beneath the site and sloped at 0.0008 ft/ft to the northeast. This is an exceptionally flat <br /> gradient, and combined with the high static water level the net effect would be very slow <br /> groundwater flow. The are in the gradient is even more dramatic in the October data, because the <br /> static water level in KF-6 and KF-7 is higher than expected. This forms a trough in the gradient. <br /> The trough trends northwestward in the southeastern quarter of the site, but then swings to the north <br /> beneath the building. Its origin is unknown. <br /> 4.2 Soil Samples <br /> The six soil samples from KF-4 and KF-5 were analyzed for Total Petroleum Hydrocarbons as <br /> gasoline, benzene, toluene, ethylbenzene, and xylene, and five gasoline oxygenates. The results are <br /> summarized in Table 2,which also includes the results of previous samples for comparison. <br /> 5 <br />