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I' quarterly data is needed to verify the temporal extent of this gradient directional change. <br /> Further analysis of the groundwater contours reveals that groundwater may be slightly <br /> mounded near the AS/SVE system. <br /> Vertical Groundwater Movement <br /> Comparison of the groundwater elevation measurements in well pairs MW-DIS-7S/7D and <br /> MW-DIS-8S/8D reveal a 0.012 ft/ft vertical gradient. Previous measurements at the site have <br /> shown a vertical gradient of between 0.006 and 0.02 ft/ft. Vertical migration is expected to be <br /> at least an order of magnitude less than the horizontal migration, despite the proportion of <br /> vertical to horizontal gradients. The slowness of vertical migration can be attributed-to the <br /> typical settling properties of irregular colloidal materials. Pore spacing and flow pathways <br /> preferentially align in the horizontal plane. <br /> Analytical Results <br /> Analyses of groundwater samples from monitoring wells are presented in Table 3-3. Gasoline <br /> I constituent concentrations show a favorable declining trend over the period of record (1991 - <br /> 1995). The following points describe how the declining trends noted.at the site exhibit <br /> i <br /> evidence of natural microbial degradation. <br /> • Gasoline constituents are preferentially degraded in a natural in-situ <br /> groundwater setting. The most readily degradable constituent under anoxic <br /> conditions is toluene, followed by the xylene species. Benzene and ethyl <br /> benzene are 'typically consumed more slowly. However, BTEX <br /> concentrations approaching solubility limits can be toxic to in-situ microbes. <br /> } <br /> • MW-DIS-2 groundwater has lower BTEX constituent concentrations than in <br /> MW-DIS-1, where a floating NAPL layer has occasionally been observed. <br /> Toluene concentrations have decreased in MW-DIS-2 by two orders of <br /> magnitude, xylenes have decreased by one order of magnitude, and the <br /> l ; <br /> concentration of benzene is unchanged over time. <br /> • Historically, there is little evidence of constituent concentration reduction in <br /> MW-DIS-1 until the AS/SVE system started up in February 1995. MW-DIS-1 <br /> is in the heart of the plume, where concentrations are greatest. Concentrations <br /> in MW-DIS-I are at the solubility limit. <br /> • Areas of a plume with the highest concentrations are typically in a state of <br /> negative oxidation-reduction potential, meaning they are electron-acceptor <br /> limited. <br /> • The initial contamination in MW-DIS-3,likely to have come from cross <br /> I contamination during well construction,declined'to non-detect levels over a ., `' <br /> l <br /> SFO10030982.DOC 3-21 <br /> i <br />