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i <br /> The previous soil sampling data in 1998-1999 showed that there was some minor leakage along <br /> the pipeline with the' most elevated levels at the pipeline sample at 60 feet from the original <br /> dispenser island (1998 Pipeline Sample at 60' from the dispenser). Very little contaminant was <br /> detected.in the other soil samples from the tank pit, pipeline and under the dispensers in 1998. <br /> Soil sample B-3 @ 3' collected from the former UST piping trench (near the vicinity of the <br /> original Pipeline Sample at 60' sample location) showed that only slight soil vapor and TPHD at <br /> 7.0 Mg/kg was detected at that location. <br /> Contaminated soil from the UST closure project was stockpiled at that time and had apparently <br /> been treated at the surface by aeration while waiting to be stockpiled, again while being placed <br /> into a common stockpile and then again when all soil was returned to the UST excavation, <br /> pipeline trench and dispenser island excavations. On the basis of the field observations and <br /> chemical soil results from 1998 and this 'study, there does not appear to be a contaminant <br /> presence along the former dispenser island area, pipeline trench or below the former tank pit. <br /> The laboratory noted that the very low TPHD results are noted as higher that those typical of <br /> TPHD and are interpreted as either matrix interference or degraded remnants of residual fuel. <br /> 7.0 Conclusions and Recommendations <br /> Wright collected 12 soil samples from along the former fuel pipeline and the underground <br /> storage tank pit. The purpose of the soil sampling and analyses was to ascertain the presence of <br /> residual fuel compounds. The former pipeline and former underground storage tank pit were <br /> located using ground penetrating radar and a review of historic aerial photographs. Six <br /> exploratory borings were advanced to collect soil samples in native soil below dispenser island <br /> area, pipeline trench and/or tank pit backfill. Native soils consisted of interbedded clayey sand, <br /> sandy silt and sand with gravel. Groundwater was not encountered in any shallow boring or at <br /> the maximum depth of the boring B-6 of 30 feet. <br /> Chemical analyses showed that TPHG, BTEX, fuel oxygenates, 1,2-Dichloroethane, Ethylene <br /> Dibromide, Ethanol and Methanol were not detected in any sample. Very low levels of TPHD <br /> were detected in the pipeline samples and one very low detection of TPHD in tank pit backfill. <br /> Soil samples collected below the tank pit in native soil showed that no contaminants were <br /> detected. The presence of the very low TPHD is interpreted as either residual fuel or matrix <br /> interferences. The laboratory noted that the TPHD detected hydrocarbons were higher boiling <br /> than typical Diesel fuel. <br /> In our opinion the chemical data do not show a significant contaminant problem. The excavation <br /> and handling of stockpiled contaminated soil in 1.998-1999 had addressed the problem. While a <br /> groundwater sample was desired by EHD, contaminants were not detected in soil samples from <br /> 15 to 30 feet below the backfilled tank pit. Given the estimated depth to groundwater (estimated <br /> over 70 feet) and lack of contaminant presence detected in soil samples, a groundwater threat is <br /> not present on the basis of these data. <br /> Page 5 of 7 <br />