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City of South Bend—Westem/Wayne Re-development <br /> March 1, 2011 <br /> Page 5 of 8 <br /> costs and the specific scope of services for performing any Phase II recommendations will be <br /> submitted under separate cover. Included within the report will be the qualifications of the <br /> environmental professional responsible for the assessment. <br /> TASK 2—PHASE II SITE ASSESSMENT <br /> As the proposed re-development of the subject site is residential; historical property uses become <br /> of significance given the potential for long-term exposure to residents/children, should <br /> contamination be present. We note that the northernmost portions of the subject site were <br /> residential until such time as the northeast quadrant was transitioned to a paved parking lot for <br /> autos associated with both the historical Gurly-Leep Buick and Gates Chevrolet Body Shop <br /> operations. The northwest quadrant continued as residential until such time as demolition of the <br /> units began in the mid to late 1980s. With respect to these former residential dwellings, historical <br /> heating oil UST systems are likely to be present, as well as significant volume of rubble <br /> associated with the former foundations. <br /> The southern half of the subject site was historically developed as residential (heating oil USTs, <br /> rubble), with subsequent conversion of the lots along Western Avenue to commercial operations <br /> that included a former gas station, a former dry cleaners, former department store, former auto <br /> battery sales/service facility, and more recently as a transmission repair facility. With the recent <br /> demolition of the former transmission repair facility, clean-up of the heating oil UST systems <br /> encountered was based on field screening and visual assessment. As such there were no <br /> confirmation samples collected as part of the removal actions. <br /> In light of the aforementioned, Wightman Petrie proposes some level of confirmation that the area <br /> of the general site is consistent with the criteria established under the RISC Residential <br /> guidelines. Such confirmation can be accomplished through the collection of various surface and <br /> subsurface soil samples, as well as groundwater samples collected from temporary wells. We <br /> note that any such borings or temporary wells should consider any additional Recognized <br /> Environmental Conditions identified during the completion of the Phase I Environmental Site <br /> Assessment(i.e., review of Sanborn Maps, historical aerials, site reconnaissance, etc.). <br /> SOIL SAMPLING VIA GEOPROBE METHODOLOGY <br /> Using Geoprobe methodologies (small track mounted hydraulically driven sampling probe) soil <br /> samples will be collected from a total of eight (8) locations across the subject site (GP1 — GP8). <br /> For each of the Geoprobe boring locations, discrete soil samples will be collected from a depth of <br /> approximately 1-foot below land surface (surface soils), as well as the interval immediately above <br /> the soil/groundwater interface (up to 30 feet below land surface), assuming that there are no <br /> other indications of the presence of contamination (visual/olfactory). Surface soils will also be <br /> collected from an additional four (4) locations across the subject site. Each 5-ft. soil sample <br /> interval (until groundwater is encountered or 30 feet below land surface) will be screened for the <br /> presence of volatile organics by placing a portion of the soil sample into a plastic bag, allowing <br /> time for equilibration, and insertion of a photo ionization detector (PID) probe to observe a <br /> reading of"total VOCs" in parts per million (ppm). All data associated with the field screening of <br /> VOCs will be recorded for future reference (Soil Boring Logs). Should field screening with the PID <br /> indicate the presence of significant VOCs, a sample of the soil in question will be collected and <br /> submitted for analysis. <br /> Surface soil samples will be analyzed for the presence of RCRA metals; whereas subsurface soil <br /> samples selected for laboratory analysis will be analyzed for the presence of Volatile Organic <br /> Compounds (VOCs) and Carcinogenic Polynuclear Aromatic Hydrocarbons (CPAHs). Wightman <br /> Petrie will utilize IDEM guidance Terra-Core Methods to collect soil samples from each discrete <br /> sampling interval for the analysis of VOCs. All soil samples will be labeled, packed on ice and <br /> forwarded to the laboratory under chain-of-custody procedures. <br />