The KDHE conducted a Phase I Brownfields Targeted Assessment (BTA) for the City of Chanute on the property known as Katy Park. The City has plans to rehabilitate existing facilities and expand the pedestrian/bike path resulting in beneficial recreational uses for the local community. Based on the Phase I report, �Recognized Environmental Conditions� (RECs) were identified as potential releases of hazardous substances and/or petroleum products associated with the historical use of the northeast portion of the site as a bulk petroleum facility from circa 1916 through the 1940�s and potential contaminant migration from adjoining and nearby properties which include a former oil patch storage facility, automotive repair and salvage facilities, filling station, former dry cleaning facility, and an unregulated dump site. Due to the potential for soil and groundwater impacts, a Phase II assessment was recommended. The Phase II BTA took place in July, 2014 and consisted of nine collocated soil/groundwater borings and two groundwater borings. A total of 16 soil samples were collected, including one duplicate, and consisted of two samples collected from each boring (surface and subsurface) with the exception of SB-2, SB-4, and SB-9, where only one surface sample was collected. Groundwater samples were collected from each of the soil borings as well as from two additional groundwater borings, making for a total of 12 groundwater samples including one duplicate. All soil and groundwater samples were analyzed for Resource Conservation and Recovery Act (RCRA) metals: mercury, arsenic, barium, cadmium, chromium, lead, selenium and silver, Volatile Organic Compounds (VOCs), Total Petroleum Hydrocarbons (TPH) Gasoline Range Organics (GRO), and TPH Diesel Range Organics (DRO). TPH DRO was detected in the soil sample SB-3 (4-6 feet) at 3,480 milligrams per kilogram (mg/kg), which exceeds the Tier 2 KDHE Risk-Based Standards for Kansas (RSK) residential level of 2,000 mg/kg for soil pathway, but is below the nonresidential level of 7,830 mg/kg for soil to groundwater pathway. Soil samples SB-3 (2-4 feet), SB-4 (2-4 feet), and SB-5 (2-4 feet) also detected TPH DRO, but concentrations were below the KDHE RSK residential levels. TPH GRO was detected in SB-3 (4-6 feet), but detections were below KDHE RSK values. Various VOCs were detected in SB-3 (2-4 feet) and SB-3 (4-6 feet), but all detections were below their respective KDHE RSK residential values. Arsenic, barium, chromium, and lead were detected in all 16 soil samples. In addition, mercury and cadmium were detected in SB-3 (2-4 feet), SB-4 (2-4 feet), and SB-5 (2-4 feet), and cadmium was detected in SB-5 (4-6 feet); however all metals concentrations were below the corresponding KDHE RSK residential level. TPH DRO was detected in groundwater at a concentration of 8.1 milligrams per liter (mg/L) in SB-3, which exceeds the KDHE RSK residential and non-residential levels of 0.5 mg/L and 0.72 mg/L, respectively. The sample from GW-2 also detected TPH DRO in groundwater, but concentrations were below their respective KDHE RSK values. TPH GRO was only detected in the duplicate groundwater sample at SB-3, with a concentration of 0.56 mg/L, which slightly exceeds the KDHE RSK level of 0.5 mg/L. Groundwater samples SB-1 through SB-9 detected arsenic and barium, but concentrations were below the KDHE RSK residential levels and no other metals were detected in the groundwater samples. Various VOCs were detected at SB-2, SB-3, GW-1, and GW-2, but all concentrations were below their respective KDHE RSK residential levels. The TPH DRO exceedance in the groundwater and subsurface soil at SB-3 (4-6 feet) is located within the portion of the site historically used for bulk petroleum storage and handling operations, and appears to be localized. Additionally, all groundwater samples collected down gradient from SB-3 were either below KDHE residential standards or were non-detect for TPH DRO, further indicatin