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Ivy Tower Phase II <br />February 27, 2012 <br />Page 4 of 7 <br />(ppm). All data associated with the field screening of VOCs will be recorded for future reference (Soil <br />Boring Logs). <br />In addition, a portion of each discrete sampling interval will also be collected for submittal to a laboratory. <br />Wightman Petrie proposes to submit two (2) soil samples from each of the seven (7) boring locations <br />based on the PID field screening results and /or other indications of the presence of potential <br />contamination (visual or olfactory). In the event that field screening with a PID, visual or olfactory <br />observations do not indicate the presence of contamination; the soil sample collected from the upper two <br />(2) feet within the boring, as well as the interval immediately above the soil /groundwater interface will be <br />submitted for laboratory analysis. Each of the soil samples selected for laboratory analysis will be <br />analyzed for the presence of Volatile Organic Compounds (VOCs) via EPA Method 8260, and <br />carcinogenic Polynuclear Aromatic Hydrocarbons (cPAHs). Wightman Petrie will utilize IDEM guidance <br />Terra -Core Methods to collect soil samples from each discrete sampling interval for the analysis of VOC <br />constituents. All soil samples will be labeled, packed on ice and forwarded to the laboratory under chain - <br />of- custody procedures. <br />Temporary Geoprobe Well Installation for Groundwater Sampling <br />Wightman Petrie proposes to convert each of the seven (7) Geoprobe soil borings to temporary wells with <br />insertion of a Geoprobe groundwater sampling device, which allows for the extension of a stainless steel <br />slotted screen for collection of a groundwater sample from the point at which the saturated or water - <br />bearing zone is encountered. For this proposal, Wightman Petrie has assumed that the water - bearing <br />zone will be encountered within 25 -feet of land surface. <br />We would also note that each of the three (3) borings /temporary wells installed within the vacant lot south <br />of Building 113, as well as the boring /temporary well proposed for the grassy area west of Building 112 <br />include the sampling of groundwater at various depths, based on the presence of a chlorinated solvent <br />plume being identified in at a depth approximately 10 to 15 ft. greater than the depth at which the <br />groundwater aquifer was originally encountered (i.e., 40 feet below ground surface). <br />Once installed, each temporary well would be purged until such time as the water discharge becomes <br />relatively free of solids or until at least three (3) gallons of water has been removed. Wightman Petrie <br />proposes that groundwater from each of the temporary wells be analyzed for Volatile Organic <br />Compounds via EPA Method 8260, and carcinogenic PAHs via EPA Method 8270 SIM. For those <br />temporary wells at which multiple groundwater samples will be collected (total of four); Wightman Petrie <br />proposes that groundwater sample from the deeper of the screened intervals be analyzed for the <br />presence of VOCs only. Each groundwater sample will be appropriately labeled, packed on ice, and <br />forwarded to the laboratory (priority overnight delivery) under chain -of- custody procedures. Analysis will <br />also include the analysis of a water sample for QA/QC purposes (Volatile Organic Compound only). <br />Wightman Petrie will plug the boreholes /wells with bentonite once soil and groundwater sampling <br />activities have been completed. <br />Reporting <br />Upon receipt of the laboratory analyses, data will be reviewed and tabularized. Comparison of the data <br />for each respective chemical constituent will be made to the Risk Integrated System of Closure (RISC) <br />Default Closure Values for Residential and Industrial /Commercial Properties. Upon completion of the <br />initial data review, a "Letter Report" will be prepared which presents the sample collection and analytical <br />methodologies used during the field phase of the assessment. Copies of the sample location maps, <br />tabulated data and comparison to RISC Default Closure Values will also be incorporated. <br />Recommendations for any additional assessment activities will be made for review and comment. <br />