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Phase II Environmental Site Assessment <br />2534 Kenzie Terrace <br />WSB Project No. R-020198-000 Page 5 <br />2. Investigation <br />A total of 8 environmental borings (B-1 through B-4 and V-1 through V-4) were advanced at the Site on <br />April 22, 2022, to investigate potential impacts to soil, groundwater, and soil vapor. The environmental <br />borings were completed by Bergerson-Caswell, Inc. of Maple Plain, Minnesota using a truck-mounted <br />push probe drill rig. The boring locations are depicted on Figure 2. <br />2.1 Soil Sampling <br />Continuous soil sampling was conducted at each boring using a four-foot long rod with a new <br />acetate liner for each sample. The soil borings were advanced to depths that ranged from 24 to <br />28 feet below grade. Soil profiles were assessed at two-foot intervals and labeled accordingly. <br />Each sample was visually examined for evidence of contamination, field classified, and screened <br />for organic vapors using a PID equipped with a 10.6 eV lamp. Soil boring logs are included as <br />Appendix B. <br />Two soil samples were collected from each of the four soil borings during the investigation and <br />submitted to Eurofins TestAmerica Laboratory of Cedar Falls, Iowa (Eurofins) for analytical <br />testing. In general, soil samples were submitted for laboratory analysis in compliance with the <br />MPCA guidance document 4-01 Soil and Groundwater Assessments Performed During Site <br />Investigations and/or field observations. Following completion of sampling and screening <br />activities, the borings were sealed with bentonite grout in accordance with MDH requirements. <br />2.2 Groundwater Sampling <br />A total of two groundwater samples were collected and submitted to Eurofins for analytical <br />testing. Groundwater samples were collected by installing a size 10 slotted polyvinyl chloride <br />(PVC) screen (temporary well screen) into the boring, then inserting a section of new <br />polyethylene tubing into the screened well interval. A check valve was used to draw the sample. <br />Groundwater samples collected for RCRA Metals analysis were field filtered prior to laboratory <br />analysis. Unique identification numbers were assigned to groundwater samples using the boring <br />number and the designation of “GW” for groundwater. Water level measurements and screen <br />depths are included in the soil boring logs in Appendix B. <br />2.3 Soil Vapor Sampling <br />A total of four soil vapor samples were collected from a depth of 4 feet below grade and <br />submitted to Eurofins for analytical testing. Each sample was collected using a one-liter summa <br />canister equipped with a regulator calibrated to collect the sample with an approximate five- <br />minute draw (i.e., a flow rate of 200 milliliters (mL) per minute).