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UPDATE 28 8-02-94 <br /> conservative using the highest permeability calculated from soil <br /> samples and an organic carbon of 0 1% The models were run on <br /> three areas of approximately 100 square feet each. Area 1 <br /> (polygon 1) is the area around soil boring SB13 , Area 2 (polygon <br /> 2) is the area around soil boring SB14 and Area 3 (polygon 3) is <br /> the area around soil boring SB15 . Under the above conditions <br /> VLEACH ran on the February 2, 1994 data, predicted that over a <br /> 140 year timeframe 430 pounds of gasoline range hydrocarbons <br /> would be delivered to ground water and BIOPLUME calculated that <br /> the majority of the hydrocarbons would be oxidized, with only one <br /> area of impact (SB14) , where dissolved oxygen would be reduced to <br /> zero in an area of approximately 300 square feet Maximum impact <br /> would occur during year 55 with 17 5 grams/square foot The <br /> impact would then decline as dissolved oxygen levels start to <br /> increase back to background of 8 mg/L These models showed that <br /> the contamination in soil as of February 2, 1994 , using a worst <br /> case senario, would only impact the ground water near SB14 , be of <br /> limited lateral extent, never leave the site and would eventually <br /> degrade with time <br /> The VES was restarted on February 16 , 1994, see Table 3 Since <br /> the above mentioned fate modeling was performed (February 2 , <br /> 1994) another 124 pounds of gasoline range hydrocarbons have been <br /> removed from the site The above models were updated (thru July <br /> 12 , 1994) with this new removal amount and can be found as <br /> Appendix A of this report Basically the Models VLEACH and <br /> BIOPLUME were adjusted by the subtracting the removed 124 pounds <br /> from the amount that remained on February 2 , 1994 of 531 pounds <br /> and then determining the percentage of contaminant that remained <br /> for each sample point used in the original modeling <br /> Approximately 76 6% of the February 2 , 1994 calculated <br /> contaminant remains in the soil as of July 12 , 1994 Also <br /> BIOPLUME was adjusted to respond to ug/L of ground water <br /> concentrations instead of the mg/L as was previously modeled, <br /> February 2 , 1994 Results of this current modeling (July 12 , <br /> 1994) indicate that during the 100 years biodegradation is faster <br /> than contaminant delivery, therefore the TPHg would never reach 1 <br /> ug/L During the decade ending in year 60 maximium impact would <br /> occur with a dissolved oxygen of 1 38 mg/L near SB14 As long as <br /> there is oxygen available the petroleum hydrocarbons will be <br /> degraded as they come in contact with ground water The <br /> following table shows the modeled predictions for dissolved <br /> oxygen in ground water, the amount of gasoline range hydrocarbons <br /> that will come in contact with the ground water, and the net <br /> results of TPHg in the ground water, where oxidation will occur, <br /> beneath SB14 <br /> pages <br />