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Work Plan for UGT Investigations -3- 7 November 1991 <br />DDRW, Sharpe Site <br />these samples, these concentrations may indicate that ground water could <br />potentially have been impacted. Furthermore, these concentrations are not <br />significantly different than the concentrations of diesel, gasoline and <br />BTX in samples from D-19, D-39 and D-43. These latter three tank samples <br />were listed on Table 2-5, indicating that additional investigative work <br />would be required at these sites. Therefore, based on the Tables, it is <br />unclear what criteria were used to determine whether a tank site needed <br />further investigation. Sharpe needs to define the criteria by which a <br />site was determined to need additional investigation. <br />Page 2-7. The Plan lists the maximum allowable soil total petroleum hydrocarbon <br />(TPH) levels or cleanup levels for soils contaminated with diesel, <br />gasoline BTX's as 100 mg/kg, 10 mg/kg and 0.005 mg/kg, respectively. I do <br />not concur with the proposed cleanup levels for diesel and gasoline <br />because the rationale for selecting these concentrations was not presented <br />and because the depth at which these contaminant concentrations were found <br />is unknown. Ground water at Sharpe may be as little as about five to ten <br />feet below the depth of the tanks. Therefore, it may not be acceptable to <br />leave, for example, 100 mg/kg of diesel in the soils as this concentration <br />may continue to degrade ground water if left in-place. Sharpe needs to <br />provide the rationale for uniformly selecting these concentrations cleanup <br />levels for every tank site. Further information is needed, such as the <br />depth of the existing soils sample data, depth to ground water and types <br />of soils to determine the appropriate cleanup level for each UGT. <br />However, the proposed cleanup level for BTX of 0.005 mg/kg in the Plan is <br />acceptable. In the Tri -Regional Board Staff Recommendations, the <br />Practical Quantitation Limit (PQL) is 0.005 mg/kg. If Sharpe cleans up <br />the soils at the tank sites to the PQL, then this would be acceptable <br />because it would be considered a "clean closure" for soils at the tank <br />site and would be acceptable. <br />Page 2-7. Table 2-3 lists the tanks which meet the LUFT Manual Guidelines and thus, <br />would not need further investigation. The Plan also establishes 0.005 <br />mg/kg as the cleanup level for BTX's. However, several of the tanks (D-8, <br />D-10, D-17, D-21, D-29, D-32, D-33, D-41 and D-45) listed in this Table <br />have concentrations above the 0.005 mg/kg cleanup level established for <br />BTX's in the Plan. Therefore, these tanks would not be considered as <br />having had an adequate investigation and cleanup, per the criteria <br />established in the Plan. <br />Page 2-10. Table 2-5 summarizes those tanks which need additional investigation. It <br />is apparent that the tanks targeted for additional soils boring were based <br />on the investigative approach to complete an investigation for a <br />particular tank site rather than to perform additional investigations to <br />fill data gaps. This proposed investigative approach is acceptable. <br />However, the remaining tank sites will require investigation at a later <br />date to determine whether there were leaks from the removed tank, whether <br />ground water has been impacted and whether the tank site needs <br />remediation. <br />Page 2-10. Table 2-5 indicates that a soil boring was to be installed at tank site <br />D-6 due to the elevated concentrations of pesticides in the soils sample. <br />