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Reniedlai>on Plan <br /> Cleanup and Abatement Order No -00-707 EAI Project No 1232 <br /> event (MW-l0A at 1 2 µg/L and MW-18 at 4 2 µg/L) The highest deep zone benzene <br />' concentration was in monitoring well MW-25D at 2,500 4g/L (see Figure 12) <br /> 35 Fuel Oxygenates <br />' Fuel oxygenates, e g , MTBE, TBA, DIPE, ETBE, TAME, EDB, ethanol or methanol (based <br /> on EPA Method 8260B) are not chemicals of concern <br />' 3.6 Findings <br /> Based on the results of the latest soil and ground water quality assessments, the following are <br /> inferred <br /> • Historical operation of the RIW drew fuel hydrocarbons present beneath the Unocal and <br /> Wards sites to the RIW, impacting ground water beneath Pacific Avenue and <br /> Robinhood Drive <br /> 0 Ground water flow direction for the area (when the RIW is not in operation) is easterly <br /> • The highest concentrations of dissolved hydrocarbons are present in Unocal well MW- <br /> 25D, which is screened from 61 to 66 feet bgs No dissolved hydrocarbons above the <br /> laboratory reporting hi-nit were detected in well MW-25S, which is screened from 25 to <br /> 45 feet bgs and located immediately next to well MW-25D <br /> • Unocal well MW-23S/D is the most downgradient well (when the RIW was formerly in <br /> operation) and the deepest well located on the Unocal site Well MW-23 S/D is slotted <br /> between 86 and 91 feet bgs, and from 97 5 to 102 5 feet bgs TPH-G at 1,510 tig/L and <br />' 242 dig/L was detected in MW-23S in March and May 2001 and at 1,420 µg/L and 138 <br /> 4g/L in MW-23D, respectively Benzene at 59 4 and 11 8 ltg/L was detected in MW- <br /> 23S in March 2001 and May 2001 and at 60 9 and 12 3 pg/L in MW-23D, respectively <br />' These data indicate the vertical extent of contamination has not been defined in this area <br /> of the project Further, since well MW-23S/D is located in the downgradient access of <br /> the plume (when the RIW was formerly in operation) from well MW-25D, it is probable <br /> that the vertical extent of ground water contamination in the area between these two <br /> wells extends to depths of 100 feet bgs <br /> i Well MW-22S/D is located in the vicinity of the RIW and screened from 30 to 50 feet <br /> bgs, and from 61 to 66 feet bgs No dissolved hydrocarbons above the laboratory <br /> reporting limit were detected in well MW-22S in March and May monitoring events <br /> TAH-G (1,800 µg/L and 890 µg/L) and benzene (140 µg/L and 93 9 pg/L) were <br /> detected in well MW-22D <br /> • Well M W-24S/D is the well located ciosest to the RIW ana screenea from 85 to 90 feet <br /> bgs, and from 98 to 103 feet bgs This is the deepest screened well associated with this <br />' project TPH-G (2,660 µg/L and 6,710 µg/L) and benzene (538 ltg/L and 1,220 µg/L) <br /> were detected in well MW-24S in March and May 2001 monitoring events, <br /> respectively In March 2001, no dissolved hydrocarbons above the laboratory reporting <br /> limits were detected in well MW-24D In May 2001, TPH-G (111 �tg/L) and benzene <br /> (41 9 �tg/L) were detected in this well <br /> 65 1232P RAP ADD -5- <br />' ENVIRONMENTAL AUDIT,INC® <br />