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hn KLEINFELDER <br /> known to have been running at least 5 days prior to sample collection. Field parameters and <br /> samples were obtained from the pump cutoff switch flow line. <br /> The two groundwater samples were submitted to Superior Precision Analytical for analysis. Total <br /> petroleum hydrocarbons as referenced to diesel (TPH-D) were detected in the sample from EW=1 <br /> (sample no. 14967) at 11,000 ug/I. Toluene and total xylenes were detected in the same sample at <br /> 0.6 ug/l and 5.8 ug/l respectively. Total petroleum hydrocarbons as referenced to gasoline (TPH- <br /> G) were not detected at the reporting limit of 500 ug/l in the sample from EW-1. The reporting <br /> limit was raised due to interference from other constituents in the sample. Benzene and <br /> ethylbenzene were not detected in the EW-1 sample at a 0.5 ug/l reporting limit for each. <br /> Benzene, toluene, ethylbenzene, total xylenes, TPH-G and TPH-D were not detected in the <br /> sample from MW-2 (sample no. 14966) at the following respective detection limits: 50 ug/I, 50 <br /> ug/I, 0.5 ug/l, 0.5 ug/i, 0.5 ug/l, and 0.5 ug/I. <br /> The following conclusions were made in our April 13, 1994 of the additional groundwater <br /> assessment: <br /> 1. Soil contamination above 100 mg/kg was reported to exist in the immediate vicinity of the <br /> excavated fuel pipelines at a depth of 9 feet to below the water table. Field screening <br /> results with a portable flame ionization detector (FID) during the installation of the <br /> monitoring wells indicates that the soil from a depth of 9 to 9-1/2 feet and deeper contains <br /> hydrocarbons in the areas near MW-3 and MW-4. It is apparent that the hydrocarbons in <br /> the soil is likely caused by capillary upward migration of diesel product from contaminated <br /> groundwater. <br /> 2. Free product was encountered in MW-1, MW-3, and MW-4 at 2.18, 0.3 5, and 0.53 feet in <br /> thickness respectively on February 28, 1994. Diesel was also detected in the sample from <br /> EW-1 at 11,000 ug/l. Note that when product thickness measurements were made shortly <br /> after well installation, little, if any product was found in the wells. After five days, product <br /> thickness increased significantly. In reviewing the water level and product thickness <br /> measurements, it is apparent that because the diesel floats on water, a well penetrating this <br /> diesel/water interface creates an unconfined depression open to the atmosphere. These <br /> conditions cause the diesel fuel to migrate to the well from the surrounding aquifer. The <br /> actual free product layer thickness is likely less than that depicted. Diesel and other <br /> 24-220176-FOl/CR43-8 (1994) Page 5 of 13 June 3, 1994 <br /> Copyright 1994 Kleinfelder, Inc. <br />