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kTJ KLEINFELDER <br /> 6 CONCLUSIONS AND RECOMMENDATIONS <br /> Kleinfelder conducted a limited soil and groundwater assessment to assess the lateral and vertical <br /> limits of potential petroleum impacted soil at the petroleum pipeline spill area (subject site). <br /> Kleinfelder collected much of the data in 4-point composite soil samples for the anticipated profile- <br /> process for disposal purposes (Class II Landfill). Please note however acceptance criteria may <br /> include additional sampling and analyses depending upon the specific landfill and gate acceptance <br /> criteria, therefore, additional analysis may be needed. Kleinfelder has preliminarily noted that the <br /> highest concentration of constituents detected in composite samples may exceed gate acceptance <br /> criteria at a Class H Landfill/s. If concentrations limits are not acceptable to local Class H <br /> Landfill/s, excavation activities may need to involve onsite stockpiling and additional sampling and <br /> analyses for additional detailed profiling of the petroleum impacted soil. Potential disposal at a <br /> Class I Landfill will markedly increase transportation and disposal costs. Additional details <br /> regarding these items will be addressed under separate cover in a workplan to be submitted to <br /> SJC/EHD. The following conclusions and recommendations were developed based on the data and <br /> information obtained from Kleinfelder's Limited Soil and Groundwater Assessment <br /> 1) Based on field indications (PID reading, discolored soil and odors etc.) and analytical results <br /> significant petroleum impacted soil was noted primarily north and east of the Chevron crude <br /> oil pipeline at depths ranging from 5 to 12 feet bgs (See Plate 3). A portion of significant <br /> petroleum impacted soil was also noted west and immediately south of the rupture area <br /> (south of the Chevron pipeline) at depths estimated at 5 to 8 feet bgs. The southern-most <br /> portion of the footprint area, with an estimated area of 27,000 square feet did not appear to be <br /> impacted by petroleum constituents. These estimates do not include a significant underlying <br /> leaching(transition zone)noted prior to encountering"clean" soil. <br /> 2) Kleinfelder estimates an in-place volume of 17,710 cubic yards of obvious petroleum <br /> impacted soil and an estimated excavated volume of 23,440 cubic yards. Including the <br /> transition zone Kleinfelder anticipates remedial excavation depths will range from 12 to 20 <br /> feet bgs and volumes to approximately double. For anticipated clean up excavation activities <br /> (including the transitions zone) Kleinfelder estimates an in-place volume of 35,844 cubic <br /> yards and an estimated final excavation volume of 47,000 cubic yards. Please note onsite <br /> stockpiles of petroleum impacted soil from Chevrons clean-up activities are not included in <br /> this estimate. <br /> 3) Nine discrete soil samples were collected and analyzed primarily to assess the vertical limits <br /> of petroleum impacted soil. These nine discrete soil samples were collected from the <br /> approximately total depths of pushprobes PP2, PP6, PP10, PPI 1, PP17, PPI 8, PP19, PP21 <br /> and PP25, located mostly in obviously petroleum impacted areas. Sampling depths ranged <br /> from 7 to 24 feet. Eight of these nine soil samples were non-detected for the requested <br /> petroleum constituents. One of the nine soil samples collected from PP19 at a depth of 19 <br /> feet had a reported TPH-D concentration of 9.5 mg/kg. Based on the discrete soil sampling <br /> results of these nine samples it appears the vertical migration of petroleum constituents is <br /> 44843.T03/ST04RIO25 Page 13 of 16 <br /> Copyright 2004 Kleinfelder,Inc. August 6,2004 <br />