The Kansas Department of Health and Environment (KDHE) conducted a combined Phase I and Phase II Brownfields Targeted Assessment (BTA) on a 10.4 acre property with environmental uncertainties located at 2601 N 5th Street in the Coffeyville Industrial Park. The BTA was conducted for the City, who intends to purchase the property for redevelopment into an electric generation plant. Based on the Phase I findings, �Recognized Environmental Conditions� (RECs) were identified as potential releases of hazardous substances and/ or petroleum products based on the known groundwater contamination of PCE and TCE to the upgradient-east of the property, and the geophysical anomaly in the southwest corner of the BTA property that was identified through a survey in 1995 and 2007. Two Historical RECs (HRECs) were identified as previous chemical storage and uncharacterized disposals at the property. Due to the potential for impacts to soil and/or groundwater, a Phase II assessment was conducted. The Phase II BTA was performed in three days from March 3 to March 5, 2015, and consisted of advancing 21 collocated soil and groundwater borings using direct-push technology. Each soil boring was advanced to saturated conditions generally encountered from 16 to 19 feet (ft) below ground surface (bgs). Each soil core was visually screened and logged and soil samples were collected from two-foot intervals for in-field headspace screening using a photoionization detector (PID). PID readings did not exceed 3.1 ppm, but eleven soil samples were selected from each boring to be analyzed at an off-site laboratory for Volatile Organic Compounds (VOCs). In addition, surface soil samples (0 to 2 ft) were collected from each boring and analyzed for Resource Conservation and Recovery Act (RCRA) eight metals: mercury, arsenic, barium, cadmium, chromium, lead, selenium and silver. Following soil sample collection, each boring was completed with temporary casing and left in place for at least 24 hours for collection of groundwater samples. Each temporary casing was gauged, sampled, and subsequently plugged. All 22 groundwater samples were submitted to the laboratory and analyzed for VOCs and RCRA eight metals. Arsenic, barium, chromium, and lead were detected in various soil samples, and mercury was also detected in SB-6 (0 to 2 ft), but all metals detections were below their respective KDHE Risk-Based Standards for Kansas (RSK) levels. No VOCs were detected in any of the surface soil samples above laboratory reporting limits. Arsenic was detected in all groundwater samples and barium was detected in SB-17, but all concentrations were below their respective KDHE RSK levels, and no other metals were detected in the collected groundwater samples. Tetrachloroethylene (PCE) was detected in the groundwater at 28 micrograms per liter (�g/L) in SB-16 and 51 �g/L in SB-17. These concentrations exceed the KDHE RSK level of 5 �g/L for PCE. Aside from SB-21, which detected PCE at 1.4 �g/L, no other groundwater samples detected PCE above the laboratory detection limit. Trichloroethylene (TCE) was detected at 240 �g/L in SB-16 and 300 �g/L in SB-17, which exceed the KDHE RSK of 5 �g/L. TCE was also detected in SB-2 at 2.4 �g/L and SB-3 at 2.6 �g/L. No other locations detected TCE above the laboratory reporting limits. 1,1-Dichloroethene (1,1-DCE) was detected in SB-16 at 29 �g/L and in SB-17 at 33 �g/L, which exceed the KDHE RSK level of 7 �g/L. 1,1-DCE was not detected above the laboratory reporting limits in any of the additional samples. Other VOCs including cis-1,2-idichloroethene (cis-1,2-DCE), and 1,1,1-trichloroethane (1,1,1-TCA) were also detected in SB-16 and SB-17 below the KDHE RSK, but detections may be indicative of degradation of PCE and TCE. Various other VOCs including 1,1-dichloroethane (1,1-DCA), acetone, sec-butylbenzene, and 2-butanone were detected in various samples, but all detections were below their respective KDHE RSK levels. T