Laserfiche WebLink
-- Bwk: 45158 Page: 496 <br /> September 30, 2015 <br /> Mr. Billy Tyus <br /> Focused Phase II ESA- 151 West Main Street/152 West Wood Street <br /> Page 3 <br /> Property where contaminants of concern would most likely be encountered, if present.A Site <br /> Plan depicting the locations of the soil borings and temporary groundwater monitoring well, is <br /> included as Attachment 2. <br /> All field and sampling activities were performed in accordance with the City of Decatur's <br /> USEPA-approved Quality Assurance Project Plan(QAPP)and the submitted Sampling and <br /> Analysis Plan (SAP). <br /> Environmental Setting <br /> Regional Physiographic Conditions <br /> Regional topography was determined by review of the United States Geological Survey(USGS) <br /> Decatur Quadrangle Map,dated 2015. According to the topographical map reviewed, the <br /> Property is approximately 660 feet above mean sea level(MSL). <br /> Regional Geology <br /> Based on the Illinois State Geologic Survey(ISGS)Berg Circular,Potential for Contamination <br /> of Shallow Aquifers from Land Burial of Municipal Waste, the Property is located in an area <br /> rated as D2. In general, a D2 rating area contains uniform, relatively impermeable sandy till at <br /> least 50-feet thick with no evidence of interbedded sand and gravel. <br /> Based on the borings conducted, the geologic profile of the Property consists of intervals of <br /> sandy-silts and silty-sand matrices until a depth of approximately 1-10 feet below ground <br /> surface (bgs), which were immediately underlain by a dense glacial till to the maximum boring <br /> depth of 25 feet bgs.As such, the geology of the Property is consistent with the documented <br /> geological sources. <br /> Soil Investigation <br /> Either a wheel-mounted Geoprobee 420M hand cart or a track-mounted hydraulically <br /> powered Geoprobee Model 7822 DT was used to advance a 2-inch diameter steel drive point <br /> to the top of the desired sampling interval.Soil cores were extracted from soil borings using a <br /> 3 or 5 foot tong Macrocore®or Dual Tube Samplere equipped with disposable polyethylene <br /> sample liners. Samplers were attached to the leading end of extension probe rods and driven <br /> downward until desired target depths were reached.After the desired depth interval was <br /> obtained, the sampler was extracted and the polyethylene liner opened,field logged and <br /> screened, and subsequently sampled in accordance with Fehr Graham Standard Operating <br /> Procedures (SOPs),as presented in the City's USEPA-approved QAPP. <br /> Soil borings associated with soil and groundwater sampling activities were advanced between <br /> 15.25 feet bgs depending on field conditions observed by Fehr Graham staff or the limitations <br /> of the drilling equipment used.The extracted soil cores were immediately field screened at 1- <br /> foot intervals by Fehr Graham staff with a MiniRae 3000 photoionization detector(PID) <br /> equipped with a 10.6 eV lamp. The PID was calibrated to 100 parts per million (ppm) <br /> isobutytene and 0 ppm fresh air calibration prior to use.The PID is designed to detect the <br /> presence of volatile organic compounds(VOCs)emanating from soil pores.The soil cores, as <br /> extracted, were visually examined, and the physical observations were logged by Fehr Graham <br /> staff in a field notebook.The soil sample intervals at each boring were selected for laboratory <br /> analysis based on registered PID readings, any physical evidence of contamination such as <br /> odors or staining, and/or from typical contaminant migration characteristics. <br />