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t1l KLEINFELDER <br /> topographical expression (fill areas above adjacent ground surface) the <br /> estimated extent of the fill is illustrated on Plate 2 and could extend an average <br /> of 940 feet by 140 feet wide. Please note however the areas beyond TP12 to <br /> the north and TP9 to the south have not been evaluated, therefore the extent of <br /> debris in these directions and other areas of the site remains unknown. The <br /> eastern extent of the fill against and/or below the western race track stands is <br /> also unknown east of TP1 . <br /> and the TP9 and TP12 and an assumed <br /> be <br /> 3) Assuming the fell does not extend y <br /> average fill depth of 15 feet the estimated removal volume would be <br /> approximately 61 ,000 cubic yards. Based on extrapolated dimensions in Plate <br /> 2, and an assumed fill depth of 15 feet the removal volume may be <br /> approximately 91 ,000 cubic yards. <br /> 4) The analytical findings in the AST, Dry Well and interior Race Track Area were <br /> overall unremarkable with the exception of arsenic detected at depth in two <br /> locations adjacent to two dry wells. The arsenic values (5.91 to 13.8 mg/kg) <br /> while exceeding residential PRGs and OEHHA health risk values based on <br /> Kleinfelder's experience with arsenic in the central valley are not atypical of <br /> background values. Please note however the evaluation in the Dry Well Area <br /> was conducted to evaluate potential leaching of contaminants at depth adjacent <br /> to the dry wells. Therefore, naturally occurring arsenic may be near the surface <br /> at values exceeding PRGS and OEHHA health risk numbers. <br /> 5) Based on the metal results in the debris area and the discussion in Section 6.1.3 <br /> the debris area is not suitable for the proposed residential development. <br /> Assuming future development of this area Kleinfelder recommends evaluating <br /> the extent of debris, further characterization for disposal purposes and removal <br /> to an approved disposal facility. Since evidence of building materials was found <br /> associated with the debris piles, the potential exists for said building materials to <br /> contain asbestos. If evidence of building materials is discovered to contain <br /> friable asbestos, this material would be classifed as a hazardous asbestos waste <br /> with disposal to a Class I landfill accepting asbestos waste materials. At least <br /> one soil sample with a total lead value of 1610 mg/kg indicates a hazardous <br /> waste classification for disposal purposes. Two of the composite samples also <br /> had lead values of 556 and 821 mg/kg, exceeding criteria of 350 mg/kg, which <br /> indicates disposal at a Class I disposal site (Hazardous Waste Disposal Facility) <br /> per Section 25157.8 of the California Health and Safety Code (CH&SC). While <br /> r there are some variances under Section 25157.8, they do not appear to apply to <br /> the site. Please also note that elevated total lead values as detected in the <br /> debris area will often fail the STLC criteria of 5 mg/l for classification as a <br /> hazardous waste for disposal purposes. <br /> 6) Significant cut and fill areas have been noted at the site. Although Kleinfelder <br /> has evaluated a large fill area west of the stands, other areas have not been <br /> evaluated for debris. Therefore additional debris could be encountered in future <br /> grading and development of the site. In the event debris, unusual odors or soil <br /> 58671.E02/ST05R1127/DH:ly Page 19 of 22 <br /> ©2005 Kleinfelder, Inc. September 15, 2005 <br />