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accessible areas in close proximity include alleyways to the immediate west and south of <br />the subject site (side gradient and up gradient). <br />Using Geoprobe methodologies (small track mounted hydraulically driven sampling <br />probe) soil samples from a total of five locations. One soil boring (GP -5) is proposed for <br />the common alleyway to the west of the subject site. Two additional soil borings are <br />proposed for the residential lot to the southwest of the site. One of the borings (GP -6) <br />would be located within the front yard, along Indiana Avenue; the second (GP -7) being <br />located in the rear yard, along the eastern property boundary of the lot. The fourth boring <br />(GP -8) will be established within the east /west alleyway, near the intersection of Kendall <br />Avenue. The final boring (GP -9) is proposed to be located within the public park area to <br />the east of the subject site, across Kendall Avenue. <br />For each of the Geoprobe boring locations, discrete soil samples will be collected at 4- <br />foot intervals throughout the soil profile to a depth of 20 feet below ground surface, or <br />until saturated soil conditions are encountered. Each soil sample interval will be <br />screened for the presence of volatile organics by placing a portion of the soil sample into <br />a plastic bag, allowing time for equilibration, and insertion of a photo ionization detector <br />(PID) probe to observe a reading of "total VOCs" in parts per million (ppm). All data <br />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 <br />submittal to the laboratory. PES proposes to submit two soil samples from each of the <br />five boring locations based on the PID field screening results and /or other indications of <br />the presence of potential contamination (visual or olfactory). In the event that field <br />screening with a PID, visual or olfactory observations do not indicate the presence of <br />contamination; the two depth intervals immediately above the soil /groundwater interface <br />will be submitted for laboratory analysis. Each of the soil samples selected for <br />laboratory analysis will be analyzed for the presence of Volatile Organic Compounds <br />(VOCs). PES will utilize IDEM guidance Terra -Core Methods to collect soil samples from <br />each discrete sampling interval for the analysis of VOCs. All soil samples will be <br />labeled, packed on ice and forwarded to the laboratory under chain -of- custody <br />procedures. <br />Temporary Geoprobe Well Installation for Groundwater Sampling <br />PES proposes to convert each of the five Geoprobe soil borings to temporary wells with <br />insertion of a Geoprobe groundwater sampling device, which allows for the extension of <br />a stainless steel slotted screen for collection of a groundwater sample from the point at <br />which the saturated or water - bearing zone is encountered. For this proposal, PES has <br />assumed that the water - bearing zone will be encountered within 20 -feet of land surface. <br />Once installed, each temporary well would be purged until such time as the water <br />discharge becomes relatively free of solids or until at least three gallons of water have <br />been removed. PES proposes that groundwater from each of the temporary wells be <br />analyzed for VOCs. Each groundwater sample will be appropriately labeled, packed on <br />ice, and forwarded to the laboratory (priority overnight delivery) under chain -of- custody <br />procedures. PES will plug the boreholes /wells with bentonite once soil and groundwater <br />sampling activities have been completed. <br />Reporting <br />Upon receipt of the laboratory analyses, data will be reviewed and tabularized. <br />Comparison of the data for each respective chemical constituent will be made to the <br />