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' Report-Soil and Groundwater Investigation <br /> Herman&Helen's Marina <br /> September 30, 1996 <br /> ' Page-S- <br /> TABLE 3 <br /> Geotechnical Testing (Soil - August 1996) <br /> ' Specific Organic Permeability Moisture% Porosity % Dry Density pcf <br /> Gravity Carbon cm/sec (initial) (initial) (initial) <br /> ' Content % <br /> ASTM Method D-854 D-2974 D-5084 D-5084 D-5084 D-5084 <br /> Sample I.D. <br /> ' 1432-GPI-8 2.59 2.5 4x10" 44.3 59.32 65.7 <br /> 1432-GP3-10 2.64 12.4 2x10 53.6 60.72 64.7 <br /> ' 4.0 CONCLUSIONS <br /> Based on the data presented above, the limits of gasoline and diesel contamination in the soil <br /> ' and groundwater appear to be sufficiently established to the north and south of the former location of <br /> the USTs. TPH-G, BTEX, and MTBE were detected at elevated concentrations at GP-4, indicating <br /> ' that the northeastern and eastern limit of the plume have not been established. The eastern edge of <br /> the property is bordered by an irrigation ditch and agricultural crop land. The previous investigation <br /> t conducted in August, 1995, indicates that the western edge of the plume is at or near the shoreline of <br /> the adjacent river. The TEPH (motor oil range) concentrations detected in the soil at GP-2, GP-3, <br /> ' and GP-4 are likely to be associated with the natural organic content of the soil (i.e., peat). This <br /> interpretation is made due to the lack of a motor oil pattern on the TEPH chromatogram and the <br /> negative TEPH results for the groundwater analyses. According to Gregory Merciadis of <br /> ' GeoAnalytical Laboratories, false positives are considered to be common regarding the TEPH <br /> analysis of organic rich soils due to interference from plant or animal fats. An estimate of the extent <br /> ' of soil and groundwater contamination is shown in Figure 3, Appendix A. <br /> ' The geotechnical testing indicated that the soils have a relatively low average permeability <br /> (3x10) which is characteristic of silty clay. For comparison, class II landfill liners are required by <br /> ' State law to have a permeability not more than 1x1 O-6 cm/sec, which is of the same order of <br /> magnitude. The organic carbon content ranged from 2.5% to 12.4%. The average dry density <br /> ' (65.2 pcf) is appropriately low considering the high peat content of the soil. The average porosity <br /> (60.02%) is indicative of organic rich, silty clays. <br /> 1 <br /> n <br /> ' L• CONDOR <br />