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KLEINFELDER <br /> SCOPE OF WORK <br /> The following scope of work was developed to assess the vertical limits of crude oil impacted <br /> soil and potential impact to groundwater beneath the rupture area. As part of assessing the <br /> vertical limits of the petroleum impacted soil, the sampling and analyses will be performed to <br /> pre-characterize the soil prior to future disposal. The following sampling and analyses plan for <br /> pre-characterization for disposal purposes assumes an estimated volume of approximately 20,000 <br /> cubic yards of affected soil. Kleinfelder understands that assuming 20,000 cubic yards of <br /> affected material, local landfills will require one 4-point composite sample for every 2,000 cubic <br /> yards of soil. Pre-characterization of the material is based on in-situ sampling and disposal to a <br /> Class 11 Landfill. Please note however, that should pre-characterization indicate disposal of <br /> material to a Class I Landfill, then the soil should not be directly loaded for disposal during <br /> future excavation activities. Under these conditions Kleinfelder recommends stockpiling and <br /> additional soil sampling and analyses to reduce potential disposal costs. <br /> SOIL SAMPLING <br /> A total of 104 discrete soil samples will be collected from twenty nine (29) push probes <br /> advanced within and near the estimated footprint area of petroleum impacted soil (Plate 1). Four <br /> of these pushprobes will be advanced to assess groundwater conditions (GI through G4). Gl <br /> will be located within the footprint area and G2, G3 and G4 will be located near the perimeter of <br /> the surveyed footprint area. Twenty five locations (P1 to P25) will be placed within the footprint <br /> area. Nineteen of the 25 probes advanced in the footprint area will be located within a grid-like <br /> pattern generally based on a 75-foot spaced grid pattern. Six of the remaining 25 probes will be <br /> advanced in the assumed greatest petroleum impacted areas located east and northeast of the <br /> rupture site (Based on aerial photograph depicting surface oil accumulation and field <br /> observations by Kleinfelder). <br /> The twenty five pushprobes (P1 to P25) will be advanced to depths ranging from the surface to <br /> approximately 20 feet below ground surface (bgs) [maximum estimated depth of petroleum <br /> impacted soil] within the surveyed footprint of the spill area. Kleinfelder anticipates that up to <br /> half of the pushprobe borings located in less impacted areas, will not have to be advanced to <br /> depths greater than ten feet bgs. The four pushprobe borings Gl through G4 will be advanced to <br /> approximate total depths of 40 feet bgs. The actual total depths of the pushprobes will be based <br /> on field observations and field screening using a photo-ionization detector (PID). The PID <br /> measures ionizable compounds in air in parts per million by volume (ppmv). Therefore, based <br /> on field screening and observations, greater sampling depths may be necessary. <br /> Kleinfelder proposes to collect approximately 88 discrete soil samples from the proposed 26 <br /> pushprobe locations advanced in the footprint area (P1 through P25 and Gl). These discrete <br /> samples will be collected in petroleum impacted soil based on field observations and PID <br /> readings for profile purposes. <br /> Kleinfelder estimates that two discrete soil samples will be collected for laboratory analyses <br /> from eight probe locations (P5, P12, P13, P14, P22, P23, P24 and P25) in the southwest portion <br /> of the footprint area and four discrete soil samples collected from the remaining pushprobe <br /> 02001PROP.ENV/ST04P118/DH:ss Page 1 of <br /> Copyright 2004,Kleinfelder,Inc. March 22,2004 <br />