Laserfiche WebLink
Mr. Werner _ 2 _ � 16 September 1999 <br />Sicvol <br />Remedial Alternatives Evaluation Report <br />ies which <br />1. I have recently attended presentations on innovative ermal desorptiont in cleaning up VOCsin soil and <br />effectiveness of in-situ chemical oxidation and <br />ate these alternatives and compare them with technologies <br />groundwater. BP may wish to evalu <br />evaluated in the report. <br />2. The report states that the contaminant concentrations which are protective of <br />thaee beneficial Cleanup will be <br />groundwater have not been determined. Our 13 October 1998 letterp <br />achieved when it is demonstrated that background groundwater quality <br />zero)S' Background or zero been reached (since he <br />CDCs are not naturally occurring, their background concentration <br />concentrations typically mean less than the detection limit for that constituent. Due to economic or <br />technologic reasons, sometimes a background concentration cannot be achieved. e W ch an <br />nn1icaO that is _ <br />technically and economically feasible. For example, 1,1-DCE's detection limit and maximum <br />contaminant level for drinking are 0.5 and 6 µg/l, respectively. Therefore, the goal is to clean up <br />1,1-DCE to less than 0.5 µg/l, but if that is not possible, it must be cleaned up to at least 6 µg/l. In <br />an instance where the beneficial use protective level is less than the detection limit, the former <br />becomes the cleanup goal and any trace detection means exceedance of that goal. Table 1 shows the <br />beneficial use protective levels (i.e., WQOs) for 1,1-DCE and the other VOCs being detected at the <br />site. <br />Table 1— Water Quality Objectives <br />for Constituents of Concern <br />Reference <br />Constituents Detection Limit WQOI Maximum Contaminant Level <br />1,1-dichloroethene 0.5 a 6 µ <br />1,1-dichloroethene 0.5 µ 1 5 Agll Maximum Contaminant Level <br />1,1,1 -trichloroethane 0.5 µa 1 200 a 1 Maximum Contaminant Level <br />CAL EPA Cancer Potency Factor <br />1,1,2 -trichloroethane 0.5 µg/1 0.49 µg/1 as a Drinking Water Level <br />Chloroform 0.5 <br />U.S. EPA Integrated Risk <br />µg/1 6 µ Information System <br />CAL EPA Cancer Potency Factor <br />Tetrachloroethylene 0.5 µg/1 0.69 µ g/1 as a Drinking Water Level <br />California Public Health Goal for <br />Trichloroethylene 0.5 µg/1 0.8 µg/1 DrinkingWater <br />3. The report states that Alternative A, which consists of continued operation of the existing system, is <br />the most cost-effective option, allows migration of groundwater containing up to 50 µg/1 of VOCs, <br />and would eventually achieve maximum contaminant levels for drinking; Alternative B, which <br />consists of adding to Alternative A three extraction wells in the downgradient direction, would <br />shorten cleanup time and abate offsite migration of contaminants; and Alternative C, air sparging <br />with soil vapor extraction, is approximately 70% more expensive than Alternative B. The report <br />recommends Alternative A as the chosen alternative, but also states that if additional remedial <br />actions are warranted in the downgradient sections of the plume, addition of extraction wells is <br />