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HomeMy WebLinkAboutAS-3505_28649_CA_CAI_20170309_PerformanceALL 7606 Whitehall Executive Center Drive, Suite 800 Charlotte, NC 28273 Tel: 704-529-3200 Fax: 704-529-3272 www.atcgroupservices.com N.C. Engineering License No. C-1598 1 March 9, 2017 Mr. Dan Murphy North Carolina Department of Environmental Quality Asheville Regional Office Division of Waste Management - UST Section 2090 US Highway 70 Swannanoa, North Carolina 28778 Re: Corrective Action Performance Report Cajah’s Mountain Superette 1990 Connelly Springs Road Lenoir, Caldwell County, North Carolina 28645 Facility ID No. 0-004593 NCDEQ Incident No. 28649 Risk Classification: High (H190D) ATC Project No. CARCAJA Dear Mr. Murphy: ATC Associates of North Carolina, P.C. (ATC), on behalf of Cary Oil Company (Cary Oil), is submitting the enclosed summary of Air Sparge/Soil Vapor Extraction (AS/SVE) system operation and maintenance (O&M) activities conducted in January 2017. If you have any questions or comments, please contact us at (704) 529-3200. Sincerely, ATC Associates of North Carolina, P.C. Christine E. Schaefer Project Manager cc: Mr. Glenn Petti – Cary Oil Company 7606 Whitehall Executive Center Drive, Suite 800 Charlotte, NC 28273 Telephone: 704-529-3200 Fax: 704-529-3272 www.atcgroupservices.com N.C. Engineering License No. C-1598 1 March 9, 2017 Mr. Dan Murphy North Carolina Department of Environmental Quality Asheville Regional Office Division of Waste Management - UST Section 2090 US Highway 70 Swannanoa, North Carolina 28778 Re: Corrective Action Performance Report Cajah’s Mountain Superette 1990 Connelly Springs Road Lenoir, Caldwell County, North Carolina 28645 Facility ID No. 0-004593 NCDEQ Incident No. 28649 Risk Classification: High (H190D) ATC Project No. CARCAJA Dear Mr. Murphy: ATC Associates of North Carolina, P.C. (ATC), on behalf of Cary Oil Company (Cary Oil), is submitting a Corrective Action Performance Report which summarizes historical remedial efforts and Air Sparge/Soil Vapor Extraction (AS/SVE) system operation and maintenance (O&M) activities conducted in January 2017. As outlined in the October 31, 2012, Corrective Action Plan (CAP), high vacuum extraction through the implementation of Aggressive Fluid/Vapor Recovery (AFVR) technology appeared to be the most feasible and cost effective option for recovering remaining free product from on-site well MW-8. AFVR events were conducted between March 2012 and December 2013 and recovered approximate totals of 44 gallons of liquid phase product, 54.17 gallons of vaporized product, and 1,870 gallons of petroleum contact water from well MW-8. Historical free product recovery information is summarized in Table 1. Adsorbent socks were installed and changed as necessary in well MW-8 beginning in February 2015 to recover remaining free product. The sock was removed in early July 2015, and the well has not indicated free product during subsequent groundwater monitoring events. Natural attenuation was determined in the CAP to be the most feasible and cost effective remedial option for reducing groundwater contaminant concentrations in portions of the intermediate and deep zones of the unconfined aquifer. Historical natural attenuation sampling indicates an environment conducive to potential bioremediation in the intermediate and deep aquifer zones. Generally, measured dissolved oxygen concentrations are consistently above anoxic and hypoxic conditions, indicating a potential for aerobic activity. Dissolved oxygen concentrations in wells IMW-1 and DMW-1 remain particularly high. Petroleum compound concentrations had generally shown an increasing trend in downgradient, intermediate well IMW- 1, until January 2016 when concentrations began decreasing. Some contaminant concentration rebounding was observed in well IMW-1 during a recent monitoring event in December 2016, but the increases may be Cajah’s Mountain Superette – Corrective Action Performance Report March 9, 2017 NCDEQ Incident No. 28649 ATC Project No. CARCAJA 2 due to off-site system downtime. Impact in this well will continue to be monitored and remedial system adjustments should be made as deemed necessary. Impact in on-site, deep well DMW-1 is generally decreasing with time. Contaminants of concern in other intermediate and deep wells remain minimal. The CAP identified AS/SVE as the chosen corrective action technologies for shallow petroleum-impacted groundwater at this site. Air sparge and soil vapor extraction wells were installed at the site on December 30, 2013, through January 15, 2014. The on-site and off-site system installations were completed on January 13, 2014, through January 24, 2014. System startup activities were conducted on March 26, 2014. However, due to noise concerns, the off-site system was turned off until April 9, 2014, when the telemetry was programmed to operate the system from 8:00 am to 8:00 pm. Scheduled O&M site visits were conducted by ATC personnel on January 18 and January 31, 2017. On-site system run-time was 99% from January 18 to January 31, 2017. Vacuum readings for each well point at the on-site SVE manifold were set at approximately 40 inches of water. Following a reduction in measurable product at the site, sparge wells AS-1 through AS-3 were started in October 2015. Pressure readings for each well point at the on-site AS manifold were set at approximately eight psi. The off-site system was not operational from January 18 to January 31, 2017. Downtime was generally attributable to a power fault which resulted in burned SVE motor wires. A local motor repair shop assessed the blower motor and identified the following: one endbell needs to be bushed and the motor needs new bearings, lip seal, and filter media. ATC submitted a request for pre-approval of costs for these repairs to the NCDEQ on March 7, 2017. Additional off-site system assessment may be required following completion of repairs by the motor repair shop. As discussed in an Active Remediation Monitoring Report, dated February 13, 2017, effluent air samples were collected from the on-site and off-site SVE systems on December 14, 2016, to evaluate petroleum vapor removal and to assist with system optimization efforts. The air samples were submitted to Prism Laboratories, Inc. for analysis by EPA Method TO-18. Table 2 shows SVE cumulative recovery calculations based on system effluent sampling data. Assuming consistent recovery during each day of operation between sampling dates, approximately 899.1 and 41.5268 pounds of total BTEX have been recovered by the on-site and off- site SVE systems, respectively, from startup through December 14, 2016. A groundwater monitoring event was conducted at the site on December 28 and 29, 2016. Groundwater contamination above NCDEQ 2L standards is generally located in front of the on-site building in the vicinity of the former UST system and migrates downgradient to the east-southeast across Connelly Springs Road towards well IMW-1 and slightly to the southwest towards wells MW-9 and DMW-2. Contaminant concentrations in the source area generally indicate a decreasing trend with time, though some rebounding was observed in December 2016. Adjustments to the off-site SVE system were made in April 2016 to focus efforts on the western portion of the off-site property. In July 2016, significantly lower contaminant concentrations were observed in off-site well MW-11 which has historically contained the highest off-site shallow aquifer impact concentrations. Off-site contaminant concentrations generally increased in December 2016 during system downtime. ATC recommends continued AS/SVE system O&M visits and site groundwater monitoring at the Cajah’s Mountain Superette site. System O&M visits should continue to be conducted twice per month and continued efforts to troubleshoot the off-site system issues should be implemented. Quarterly SVE effluent air sampling is recommended during scheduled O&M visits. ATC recommends groundwater monitoring events be conducted on a semi-annual basis during winter and summer months. TABLES Table 1 Free Product Recovery Information Cajah's Mountain Superette 1990 Connelly Springs Road Lenoir, North Carolina Facility ID Number 0-004593 Incident Number 28649 Date Well ID Free Product Recovery Method Product Thickness Before Recovery (Feet) Product Thickness After Recovery (Feet) Amount of Vaporized Product (Gallons) Amount of Liquid (Water and Product) (Gallons) Amount of Liquid Product (Gallons) Total Amount of Product Recovered (Gallons) 3/28/2012 MW-8 AFVR 2.15 0.01 6.76 226 44 50.76 6/28/2012 MW-8 AFVR 0.48 0.00 6.07 231 0.00 6.07 9/28/2012 MW-8 AFVR 0.26 0.00 8.68 231 0.00 8.68 12/13/2012 MW-8 AFVR 0.69 0.00 12.79 226 0.00 12.79 3/14/2013 MW-8 AFVR 0.31 0.00 5.34 231 0.00 5.34 7/24/2013 MW-8 AFVR 0.94 0.00 2.97 189 0.00 2.97 9/16/2013 MW-8 AFVR 0.61 0.00 5.34 270 0.00 5.34 12/18/2013 MW-8 AFVR 1.12 0.00 6.22 310 0.00 6.22 AFVR = Aggressive Fluid/Vapor Recovery 12/18/2013 6.22 98.17 7/24/2013 2.97 86.61 9/16/2013 5.34 91.95 12/13/2012 12.79 78.30 3/14/2013 5.34 83.64 6/28/2012 6.07 56.83 9/28/2012 8.68 65.51 Date of Recovery Event Total Volume of Free Product Recovered from Site During Current Recovery Event (Gallons) Cumulative Total Volume Recovered to Date from All Recovery Events (Gallons) 3/28/2012 50.76 50.76 Date Cross-Sectional Area of Pipe Conversion Factor3 Days of Operation Cumulative Recovery (ft2) (lb-m3/mg-ft3)(lb/hr) (lb/day) (days) (lbs) 04/04/14* 0.08700 1,116 97.09 413 0.00000006243 0.1502 3.60 9.00 32.44 07/10/14 0.08700 1,116 97.09 6.04 0.00000006243 0.0022 0.05 97.00 37.56 10/27/14 0.08700 714 62.12 281.0 0.00000006243 0.0654 1.57 109.0 208.6 03/04/15 0.08700 719 62.55 313.0 0.00000006243 0.0733 1.760 128.0 433.9 06/18/15* 0.08700 763 66.38 26.30 0.00000006243 0.0065 0.1569 106.0 450.5 10/29/15 0.08700 603 52.46 275.0 0.00000006243 0.05404 1.2970 32.00 492.0 12/15/15 0.08700 647 56.29 476.0 0.00000006243 0.10036 2.4087 47.00 605.2 03/31/16 0.08700 588 51.16 178.8 0.00000006243 0.03426 0.8223 107.0 693.2 06/27/16 0.08700 1,269 110.4 162.7 0.00000006243 0.06728 1.615 44.00 764.3 09/29/16 0.08700 596 51.9 181.0 0.00000006243 0.03516 0.844 106.0 853.7 12/14/16 0.08700 383 33.3 199.2 0.00000006243 0.02486 0.597 76.0 899.1 04/04/14* 0.08700 626 54.46 0.64 0.00000006243 0.0001 0.003 9.00 0.02820 07/10/14 10/27/14 0.08700 575 50.03 0.45 0.00000006243 0.0001 0.002 87.00 0.2043 03/04/15 0.08700 523 45.50 0.00 0.00000006243 0.0000 0.000 128.0 0.2043 06/18/15* 0.08700 731 63.60 0.00 0.00000006243 0.0000 0.000 106.0 0.2043 10/29/15 0.08700 528 45.94 0.00 0.00000006243 0.0000 0.000 55.00 0.2043 12/15/15 0.08700 368 32.02 0.00 0.00000006243 0.0000 0.000 47.00 0.2043 03/31/16 0.08700 645 56.12 0.00 0.00000006243 0.0000 0.000 107.0 0.2043 06/27/16 0.08700 720 62.64 0.00 0.00000006243 0.0000 0.000 54.00 0.2043 10/31/16 0.08700 523 45.50 0.00 0.00000006243 0.0000 0.000 53.00 0.2043 12/14/16 0.08700 2,832 246.38 42.4 0.00000006243 0.0391 0.939 44.00 41.5268 Notes: * Effluent velocity inferred; reading not collected 3. Conversion factor to convert units of concentration from m /3 to lb/f 3 4. Mass removal rate = (air flow rate) x (total BTEX) x (conversion factor) x (60 min/hr or 1,440 min/day) Facility ID Number 0-004593 Incident Number 28649 Effluent Velocity (ft/min) Table 2 SVE System Cumulative Recovery Cajah's Mountain Superette 1990 Connelly Springs Road Lenoir, North Carolina Off-Site System No Sample Collected; System Down 2. Total BTEX concentrations in effluent air are based on EPA Method 18 laboratory data Air Flow Rate1 (ft3/min) Total BTEX2 (mg/m3) 1. Air flow rate = (cross-sectional area) x (effluent velocity) Mass Removal Rate4 On-Site System FIGURE SITE HAMBY/CAJAH'SMT PARK TRIPLETT HAMBY/CAJAH' MT PARK WILLIAMS/BRANDON APARTMENTS PRICE CHURCH SHELL CHURCH PR O J E C T N O . NO T E S : DA T E TI T L E SC A L E RE V . B Y PR E P . B Y CA D F I L E CORRECTIVE ACTION PERFORMANCE REPORT Cajah’s Mountain Superette 1990 Connelly Springs Road Lenoir, Caldwell County, North Carolina 28645 Facility ID No. 0-004593 NCDEQ Incident No. 28649 Risk Classification: High (H190D) ATC Project No. CARCAJA November 1, 2017 7606 Whitehall Executive Center Drive, Suite 800 Charlotte, NC 28273 Tel: 704-529-3200 Fax: 704-529-3272 www.atcgroupservices.com N.C. Engineering License No. C-1598 November 1, 2017 Mr. Dan Murphy North Carolina Department of Environmental Quality Asheville Regional Office Division of Waste Management - UST Section 2090 US Highway 70 Swannanoa, North Carolina 28778 RE: Corrective Action Performance Report Cajah’s Mountain Superette 1990 Connelly Springs Road Lenoir, Caldwell County, North Carolina 28645 Facility ID No. 0-004593 NCDEQ Incident No. 28649 Risk Classification: High (H190D) ATC Project No. CARCAJA Dear Mr. Murphy: ATC Associates of North Carolina, P.C., on behalf of Cary Oil Company, is submitting the enclosed Corrective Action Performance Report for the Cajah’s Mountain Superette site. This report includes information pertaining to the operation and maintenance of the air sparge and soil vapor extraction systems from February through April 2017. If you have any questions or require additional information, please contact us at (704) 529-3200. Sincerely, ATC Associates of North Carolina, P.C. Christine E. Schaefer Project Manager cc: Mr. Glenn Petti – Cary Oil Company Site Identification: Date of Report: 11/1/2017 Site Risk: High (H190D) Facility I.D.: 0-004593 UST Incident Number (if known): 28649 Site Name: Cajah’s Mountain Superette Street Address: 1990 Connelly Springs Road City/Town: Lenoir Zip Code: 28645 County: Caldwell Description of Geographical Data Point (e.g., diesel fill port): Former Tank Basin Location Method (GPS, topographical map, other): Google Earth Latitude (decimal degrees): 35. 83749120° N Longitude (decimal degrees): 81. 5387323° W Information about Contacts Associated with the Leaking UST System: UST Owner: Cary Oil Company Address: 110 Mackenan Drive, Suite 300, Cary, NC 27511 Phone: (919) 462-1100 Property Owner: Mary Lindsay Address: 127 Dell Circle, Hudson, NC 28638 Phone: (828) 728-2674 Consultant/Contractor: ATC Associates of North Carolina, P.C. Address: 7606 Whitehall Executive Center Dr., Charlotte, NC 28273 Phone: (704) 529-3200 Analytical Laboratory: Prism Laboratories, Inc. State Certification No.: 402 Address: 449 Springbrook Road, Charlotte, NC 28224 Phone: (704) 529-6364 Information about Release: Date Discovered: August 28, 2008 Estimated Quantity of Release: Unknown Cause of Release: Unknown Source of Release (Dispenser/Piping/UST): Unknown Sizes and contents of UST system(s) from which the release occurred: Two 8,000-gallon gasoline USTs and one 4,000-gallon gasoline UST and associated dispensers TABLE OF CONTENTS 1.0 EXECUTIVE SUMMARY ............................................................................................................ 1  2.0 SUPPORTING INFORMATION AND CAP IMPLEMENTATION ......................................... 2  3.0 GROUNDWATER REMEDIATION ............................................................................................ 4  4.0 CONCLUSIONS AND RECOMMENDATIONS ......................................................................... 6  5.0 REPORT LIMITATIONS .............................................................................................................. 7  TABLES Table 1 Site History Table 2 Public and Private Water Supply Well and Other Receptor Information Table 3 Historical Groundwater Sampling Results Table 4 Free Product Recovery Information Table 5 Monitored Natural Attenuation Parameters Table 6 SVE System Cumulative Recovery FIGURES Figure 1 Site Topographic Map Figure 2 Site Map Figure 3 Site Vicinity Map Figure 4 Remedial System Design APPENDICES Appendix A Laboratory Analytical Report Cajah’s Mountain Superette November 1, 2017 Corrective Action Performance Report Page 1 1.0 EXECUTIVE SUMMARY Cary Oil Company (Cary Oil) retained ATC Associates of North Carolina, P.C. (ATC) to prepare a Corrective Action Performance Report for the project site located at 1990 Connelly Springs Road in Lenoir, Caldwell County, North Carolina. Figure 1 shows the site and vicinity on part of a United States Geological Survey (USGS) site topographic map. A map showing site details is provided as Figure 2. This report documents three months of remedial system operation and maintenance. Groundwater impact at the site has historically been identified at concentrations exceeding Gross Contamination Levels (GCLs). Generally decreasing trends have been observed over time. However, according to groundwater analytical results obtained from a monitoring event performed on December 28 and 29, 2016, contaminant concentrations increased, and benzene was reported in well MW-8 at a concentration above the GCL. The remedial systems were not operational during the December 2016 groundwater monitoring event and that may be the reason for observed increased dissolved impact. Petroleum hydrocarbons were detected above the associated 15A NCAC 2L .0202 Standards (2L Standards) in eight of the 14 sampled site monitoring wells in December 2016. Historical groundwater sampling results are provided in Table 3. Free product has historically been identified in site well MW-8 at a maximum thickness of 2.97 feet. Free product was not identified in site monitoring wells in December 2016. As outlined in the October 31, 2012, Corrective Action Plan (CAP), high vacuum extraction through the implementation of Aggressive Fluid/Vapor Recovery (AFVR) technology appeared to be the most feasible and cost effective option for recovering remaining free product from on-site well MW-8. AFVR events were conducted between March 2012 and December 2013 and recovered approximately 44 gallons of liquid phase product, 54.17 gallons of vaporized product, and 1,870 gallons of petroleum-contact water from well MW-8. Historical free product recovery information is summarized in Table 4. Adsorbent socks were installed and changed as necessary in well MW-8 beginning in February 2015 to recover remaining free product. The sock was removed in early July 2015, and the well has not indicated free product during subsequent groundwater monitoring events. Natural attenuation was determined in the CAP to be the most feasible and cost effective remedial option for reducing groundwater contaminant concentrations in the intermediate and deep aquifer zones. Historical natural attenuation sampling indicates an environment conducive to potential bioremediation in the intermediate and deep aquifer zones. Generally, measured dissolved oxygen concentrations are consistently Cajah’s Mountain Superette November 1, 2017 Corrective Action Performance Report Page 2 above anoxic and hypoxic conditions, indicating a potential for aerobic activity. Dissolved oxygen concentrations in wells IMW-1 and DMW-1 tend to be particularly high. Natural attenuation parameters are presented in Table 5. Petroleum compound concentrations had generally shown an increasing trend in downgradient, intermediate well IMW-1, until January 2016 when concentrations began decreasing. Some contaminant concentration rebounding was observed in well IMW-1 during a recent monitoring event in December 2016, but the increases may be due to off-site system downtime. Impact in this well will continue to be monitored and remedial system adjustments should be made as deemed necessary. Impact in on-site, deep well DMW-1 is generally decreasing with time. Contaminants of concern in other intermediate and deep wells remain minimal. The CAP identified air sparge/soil vapor extraction (AS/SVE) as the chosen corrective action technologies for shallow petroleum-impacted groundwater at the site. Air sparge and soil vapor extraction wells were installed at the site on December 30, 2013, through January 15, 2014. The on-site and off-site system installations were completed on January 13, 2014, through January 24, 2014. System startup activities were conducted on March 26, 2014. However, due to noise concerns, the off-site system was turned off until April 9, 2014, when the telemetry was programmed to operate the system from 8:00 am to 8:00 pm. Based on impact to vicinity water supply wells and historical free product and groundwater impact in site monitoring wells, the risk classification for the site has been designated as “High” and ranked H190D by the North Carolina Department of Environmental Quality (NCDEQ). Therefore, groundwater contamination must be remediated to concentrations which are equal to or less than the associated 2L Standards. 2.0 SUPPORTING INFORMATION AND CAP IMPLEMENTATION An underground storage tank (UST) system consisting of three tanks was formerly located on-site and was operated by Cary Oil from April 2005 until August 2008 when the UST system was removed. During UST removals, soil impact was identified and led to assessment requests from the North Carolina Department of Environment and Natural Resources (NCDENR; currently the NCDEQ). The subject property is owned by Mary Lindsay and has one building that currently operates as a catering business known as Mooresridge Catering. The site formerly operated as a convenience store which included a UST system consisting of two 8,000-gallon gasoline USTs and one 4,000-gallon gasoline Cajah’s Mountain Superette November 1, 2017 Corrective Action Performance Report Page 3 UST. Site history including on-site UST system information is summarized in Table 1. A site plan that indicates monitoring well locations and other site features is provided as Figure 2. The perennial surface water body identified in the closest proximity to the site is Stafford Creek located approximately 2,000 feet to the southwest of the site. A branch of Little Gunpowder Creek lies approximately 2,500 feet to the east of the site. The Caldwell County Geographic Information System database identified surface water bodies towards the east and west at distances of 700 and 500 feet from the site, respectively; however, these surface water bodies were not identified during field activities. Surface cover at the site consists mostly of asphalt on the east side of the property and grass and gravel on the west side of the property. The site lies in the Inner Piedmont in an area characterized by inter-fingered biotite gneiss, biotite schist, and mica schist with some other minor rock types that are heavily metamorphosed and structurally complex. The shallow subsurface contains overburden of soil, saprolite, and partially weathered rock (PWR) that derive from in-place weathering. Findings from the Comprehensive Site Assessment (CSA) suggest that most of the unconsolidated subsurface materials exhibit high permeability for the Piedmont and probably can best be described as saprolite or PWR. During assessment activities, rock was encountered at decreasing depths with distance from the site towards the east, with depths ranging from 85 feet below ground surface (bgs) at on-site well DMW-3 to 20 feet bgs at downgradient well MW-21. Depth to groundwater in the site monitoring wells ranged from approximately 25 to 35 feet below top of casing (TOC) during the December 2016 groundwater sampling event. Based on the recent groundwater level measurements and calculation of groundwater elevations, groundwater flows towards the east-southeast across the site. Baton Water Corporation and the Town of Lenoir supply public water in the site vicinity. Twenty-one (21) private water supply wells have been identified within approximately 1,500 feet of the site. Water supply well information for the area is summarized in Table 2, and supply well locations relative to the source area are depicted on Figure 3. Between 2008 and 2012, site assessment, AFVR events for free product recovery, and a CAP with pilot testing were conducted related to the Cajah’s Mountain Superette release. Free product recovery efforts in the form of AFVR events, conducted between 2012 and 2013 recovered approximately 44 gallons of liquid phase product, 54.17 gallons of vaporized product, and 1,870 gallons of petroleum-contact water from well MW-8. Cajah’s Mountain Superette November 1, 2017 Corrective Action Performance Report Page 4 Historical free product recovery information is summarized in Table 4. Adsorbent socks were installed and changed as necessary in well MW-8 between February 2015 and July 2015, and the well has not indicated free product during subsequent groundwater monitoring events. Based on results of the CAP and pilot testing, ATC found that AS and SVE technologies appeared to be the most feasible and cost effective remedial options for reducing groundwater contaminant concentrations in the shallow aquifer, and monitored natural attenuation was chosen for groundwater in the intermediate and deep zones. The AS/SVE wells were installed from December 30, 2013, to January 15, 2014. Depths of the air sparge wells ranged from 50 feet to 95 feet bgs, depending on zones of groundwater impact and depth of bedrock. Wells SVE-2 through SVE-7 and SVE-10 through SVE-14 were installed to depths of 34 feet or 35 feet bgs, depending on vicinity groundwater levels. Wells SVE-8 and SVE-9 were installed to depths of 26 feet bgs due to the elevated water table encountered behind the on-site building. Vapor extraction well SVE-1 was installed to a depth of 35 feet bgs on August 22, 2012, for the pilot study. The systems were installed during the period of December 2013 through January 2014. The on-site and off- site air sparge systems consist of six and eight air sparge wells, respectively, rotary claw air compressors, and schedule 80 PVC piping for transferring compressed air from the remediation systems to the air sparge wells. The on-site and off-site vapor extraction systems consist of nine and five vapor extraction wells, respectively, regenerative vacuum blowers, condensate collection vessels, and schedule 40 PVC piping for transferring extracted vapors from the vapor extraction wells to the remediation systems. A system design drawing is included as Figure 4. 3.0 GROUNDWATER REMEDIATION System startup activities were conducted on March 26, 2014. However, due to noise concerns, the off-site system was turned off until April 9, 2014, when the telemetry could be programmed to operate the system from 8:00 am to 8:00 pm. Efforts have been made to reduce excessive noise that originates from the building but minimal reductions have been observed. Air sparge wells AS-1 through AS-3 were left off, by means of closed system manifold valves, until free product was sufficiently recovered from the area. Following a reduction in measurable product at the site, sparge wells AS-1 through AS-3 were started in October 2015. Off-site wells AS-10 and AS-11 were shut down on April 13, 2016, and wells AS-9 and AS-12 were shut down on April 28, 2016, to provide more Cajah’s Mountain Superette November 1, 2017 Corrective Action Performance Report Page 5 sparge pressure to the west side of the off-site property where higher dissolved contaminant concentrations exist. On-site system downtime has historically often been attributable to high temperature alarms which shut the system down during summer months, and power losses following storms. Off-site system downtime in 2014 occurred due to bad motor windings on the SVE blower which shut the system down. The off-site SVE blower was replaced under warranty by the system fabricator on October 15, 2014. Electrical issues (power outages, phase losses, and an indicated electrical fault) occurred at both the on-site and off-site systems in 2015. The systems were ultimately shut down manually by ATC as a safety precaution. The issue was identified to be melted high voltage fuses in each system which led the systems to run on one phase and then shut down. A small fire at the on-site catering business building occurred in August 2015, which Duke Energy attributed to insufficiently sized wires for the load. The wires were subsequently changed by Duke Energy. The combined issues are potentially related to a general electrical issue in the area, possibly caused by recent electrical storms. High voltage fuses on the on-site and off-site SVE blowers were replaced in October 2015 and the systems were re-started. Due to frequent shutdowns, the off-site SVE blower vacuum was reduced in 2016 as it was determined the operating capacity of the unit could not be fully achieved in the actual operating conditions. That is to say, the potential capacity of the blower is assumed under ideal conditions which are rarely achieved in an environmental, non-climate controlled setting. System operation and maintenance was conducted twice per month from February to April 2017 to check system components and perform routine maintenance. Efforts are made to combine site visits with visits conducted at another Cary Oil site in the vicinity, Tilley’s Superette. On-site system run-time was approximately 93% from February to April 2017. System downtime was due to a phase fault from storms in the area during the reporting period. Vacuum readings for each well point at the on-site SVE manifold were set at approximately 40 inches of water. Pressure readings for each well point at the on-site AS manifold were set at approximately nine pounds per square inch (psi). The off-site system was not operational from February to April 2017. The system downtime began in December 2016 and was generally attributable to a power fault which resulted in burned SVE motor wires. A local motor repair shop assessed the blower motor and identified the following: one endbell needs to be bushed and the motor needs new bearings, lip seal, and filter Cajah’s Mountain Superette November 1, 2017 Corrective Action Performance Report Page 6 media. Costs for these repairs were approved by the NCDEQ on March 8, 2017. The blower will be reinstalled following repairs. SVE influent air samples are collected on a quarterly basis during system operation to identify the efficiency of the SVE systems and assist with system optimization efforts. An SVE influent air sample was collected from the on-site system on March 14, 2017, and was submitted to Prism Laboratories, Inc. for analysis by EPA Method 18. The laboratory analytical report is provided in Appendix A. Table 6 shows SVE cumulative recovery calculations based on system influent sampling data. Based on laboratory analytical results from quarterly influent air sampling, approximately 1,311 and 41.53 pounds of total BTEX have been recovered by the on-site and off-site SVE systems, respectively, since startup. The on-site and off-site system influent total BTEX concentrations upon initial startup and sampling in April 2014 were 413 mg/m3 and 0.64 mg/m3, respectively. The influent total BTEX concentrations during the most recent sampling were 290 mg/m3 and 42.4 mg/m3 for the on-site and off-site systems. Free product has historically been identified in on-site well MW-8 at a maximum thickness of 2.97 feet. Following multiple AFVR events and adsorbent sock changeouts, the well has not indicated free product since 2015. Groundwater contamination above NCDEQ 2L Standards is generally located in front of the on-site building in the vicinity of the former UST system and migrates downgradient to the east-southeast across Connelly Springs Road towards well IMW-1 and slightly to the southwest towards wells MW-9 and DMW-2. Contaminant concentrations in the source area generally indicate a decreasing trend with time, though some rebounding was observed in December 2016. 4.0 CONCLUSIONS AND RECOMMENDATIONS The AS/SVE systems were started at the site in March and April 2014, and dissolved contaminant concentrations generally indicate a decreasing trend system system startup. However, a groundwater monitoring event, conducted in December 2016, indicated recent groundwater contaminant increases. System downtime during the monitoring event may be attributable to the contaminant increases. Free product was not observed in gauged wells in December 2016. Impact concentrations in intermediate and deep wells appear generally stable or are decreasing. ATC recommends continued AS/SVE system operation and maintenance (O&M) visits and site groundwater monitoring at the Cajah’s Mountain Superette site. System O&M visits should continue to be conducted Cajah’s Mountain Superette November 1, 2017 Corrective Action Performance Report Page 7 twice per month and continued efforts to optimize system efficacy should be implemented. Quarterly SVE effluent air sampling is recommended during scheduled O&M visits. ATC recommends groundwater monitoring events be conducted on a semi-annual basis during winter and summer months. 5.0 REPORT LIMITATIONS This investigation is intended to be a non-biased assessment of on-site environmental conditions proximate to the location of the former and/or current UST system. Subsurface investigative and remedial methodologies were performed in general accordance with applicable state and federal regulatory requirements. The information presented in this report is based upon site-specific observations, generally accepted geological and environmental consulting practices, and analytical results for environmental samples collected at the time of the field investigation was performed. The data presented in this report are believed to represent subsurface conditions at the facility; however, data may not be completely representative of subsurface conditions at every location. ATC assumes no liability arising from environmental impact to, or from, the site, regardless of the date of impact occurrence or findings. TABLES Table 1 Site History Cajah's Mountain Superette 1990 Connelly Springs Road Lenoir, North Carolina Facility ID Number 0-004593 Incident Number: 28649 Zip Telephone Number 27511 (919) 462-3194 Zip Telephone Number 27511 (919) 462-3194 1 Gasoline None 4,000 Fiberglass 24' x 64" Fiberglass Reinforced Plastic Early 1980s Removed 8/14/08 Yes 2 Gasoline None 8,000 Fiberglass 8' x 21.4" Fiberglass Reinforced Plastic Early 1980s Removed 8/14/08 Yes 3 Gasoline None 8,000 Fiberglass 8' x 21.4" Fiberglass Reinforced Plastic Early 1980s Removed 8/14/08 Yes State UST ID Number(s) Facility ID Number 1, 2, and 3 0-004593 Street Address 110 Mackenan Drive, Suite 300 Cary Oil Company City State Cary NC 4/2005 to 8/14/2008 1, 2, and 3 Material Released Construction Details 0-004593 Name of Owner Dates of Ownership (m/dd/yy) to (m/dd/yy) UST ID Number(s) Facility ID Number 4/2005 to 8/14/2008 Name of Operator Street Address Dates of Operation (m/dd/yy) to (m/dd/yy) Cary Oil Company Cary NC 110 Mackenan Drive, Suite 300 City UST ID Number Current/Last Contents Previous Contents Capacity (gallons) Release confirmed during 8/14/08 excavation Tank Dimensions Description of Associated Piping and Pumps Date Tank Installed Status of Tank Was Release Associated With UST System? Date of Release Description of Release 28649 Gasoline 8/14/08 Incident Number Table 2 Public and Private Water Supply Well and Other Receptor Information Cajah's Mountain Superette 1990 Connelly Springs Road Lenoir, North Carolina Facility ID Number 0-004593 Incident Number: 28649 PW-1 Jimmie & Louise Beane / 1511 Bradshaw Terrace, Lenoir, NC 28645 1511 Bradshaw Terrace Lenoir 828-728-9368 Not in use Unknown Unknown 400 Downgradient Well not operational and property provided municipal water by Baton Water Corporation PW-2 CitiMortgage, Inc. / 1000 Technology Drive, O'Fallon, MO 63368 1433 Brandon Road Lenoir NA In use for potable water by next- door Price & Shell Unknown Unknown 450 Downgradient Well services more than one residence (Price & Shell) PW-3 Henry & Linda Johnson / 1535 Bradshaw Terrace, Lenoir, NC 28645 1535 Bradshaw Terrace Lenoir 828-728-5256 Not in use Unknown Unknown 775 Downgradient Not accessible - According to Mr. Johnson, well has been filled over the years with sticks and rocks, and water is not accessible PW-4 Clifford & Jeanie Stewart / 319 Welcome Ave., Greenville, SC 29611 1554 Bradshaw Terrace Lenoir NA Not in use Unknown Unknown 1,100 Downgradient PW-5 Poarch Dixie Land Tate Azor / 1490 Land Street, Lenoir, NC 28645 1497 Land Street Lenoir NA Not in use Approx. 40-45' Unknown 1,000 Sidegradient PW-6 Ryan & Shirley Rozzelle / 186 Mountain Oak Lane, Hickory, NC 28601 1418 Brandon Road Lenoir 828-495-3456 Unknown Unknown Unknown 850 Sidegradient Current well use unknown; Property provided municipal water by Baton Water Corporation PW-7 Helen Sullivan / 904 Second St. NE, Apt. 234, Hickory, NC 28601 Justin Lane (No address number) Lenoir 828-728-2757 Not in use Unknown Unknown 1,200 Sidegradient Well operational but not in use and property provided municipal water by Baton Water Corporation PW-8 Brandon Apartments (Keith and Patricia Williams) / 1415 N. Catwaba Church Avenue, Lenoir, NC 28645 3715 Panda Lane Lenoir 828-728-9167 Not in use Unknown Unknown 1,000 Downgradient Well not operational and property provided municipal water by Baton Water Corporation PW-9 Randy & Joyce Kestner / 4593 Horseshoe Bend Road, Hudson, NC 28638 3725 Happy Horse Lane Lenoir NA In use for potable water Unknown Unknown 1,100 Downgradient PW-10 Berry Kaylor / 3965 Greenwood Drive, Lenoir, NC 28645 3965 Greenwood Drive Lenoir 828-728-6946 Not in use Unknown Unknown 1,475 Sidegradient PW-11 Sherri Barnwell / 1499 Union Grove Road, Lenoir, NC 28645 1499 Union Grove Road Lenoir 828-728-3412 Not in use Unknown Unknown 1,300 Sidegradient Well not operational and property provided municipal water by Baton Water Corporation PW-12 Roger & Penny Triplett / 1740 Taylorsville Road SE, Lenoir, NC 28645 1512 Union Grove Road Lenoir NA Not in use Unknown Unknown 1,100 Sidegradient Property provided municipal water by Baton Water Corporation PW-13 William Rudicil / 1520 Union Grove Road, Lenoir, NC 28645 1520 Union Grove Road Lenoir NA Not in use Unknown Unknown 1,190 Sidegradient Property provided municipal water by Baton Water Corporation PW-14 Karen Sanders / 1522 Union Grove Road, Lenoir, NC 28645 1522 Union Grove Road Lenoir 828-726-1420 Not in use Unknown Unknown 1,210 Sidegradient PW-15 Arnold & Wanda Correll / 1528 Bradshaw Terrace, Lenoir, NC 28645 1528 Bradshaw Terrace Lenoir 828-728-7497 In use for outdoor/irrigation water Approx. 90 Unknown 525 Downgradient Well depth estimated by Mr. Correll; Property provided municipal water by Baton Water Corporation; Well only supplies water to outside spigots; Well not operational during winter PW-16 Theohary & Linda Smargian / PO Box 967, Hudson, NC 28638 1518 Bradshaw Terrace Lenoir NA Not in use Approx. 176* Unknown 400 Downgradient Well not operational and property provided municipal water by Baton Water Corporation PW-17 Douglas & Katherine Hawkins / 1980 Connelly Springs Road, Lenoir, NC 28645 1980 Connelly Springs Road Lenoir NA Not in use Unknown Unknown 150 Sidegradient Well installed in 1961; Mary Lindsay (subject property owner) is POA; well is beneath house and not accessible PW-18 Jimmie & Louise Beane** / 1511 Bradshaw Terrace, Lenoir, NC 28645 1514 Bradshaw Terrace Lenoir NA Not in use Unknown Unknown 240 Downgradient Well not operational and property provided municipal water by Baton Water Corporation PW-20 Cajah's Mt Park LLC (Steve Hamby) / PO Box 1114, Hudson, NC 28638 0 Connellly Springs Road (Cajah's Mountain Mobile Home Park)Lenoir NA Not In use Unknown Unknown 325 Sidegradient No access to well, well reportedly not operational, and property provided municipal water by Baton Water Corporation PW-21 Paula Fetherbay c/o Paula St. Clair / 1975 Connelly Springs Road, Lenoir, NC 28645 1975 Connelly Springs Road Lenoir NA In use for potable water Unknown Unknown 375 Sidegradient PW-22 Daniel Ace / 3733 Happy Horse Lane, Lenoir, NC 28645 3733 Happy Horse Lane Lenoir NA Reportedly, in use for potable water Unknown Unknown 1,100 Downgradient N/A East N/A N/A Surface water 700 Downgradient Stream was not identified on USGS topographic map, but was depicted on Caldwell County Geographic Information website, and could not be located during field activities. N/A West N/A N/A Surface water 500 Downgradient Stream was not identified on USGS topographic map, but was depicted on Caldwell County Geographic Information website. * On 7/26/10, due to difficulty encountered gauging depth of the two foot diameter well with an o/w interface meter, it was estimated that depth of PW-16 was approximately 176 ft bgs, as the meter appeared to reach bottom at that depth. ** residential property is currently leased; The Beanes are the owner for the residential property NA = Not Available Unnamed intermittent stream Unnamed intermittent stream Description Phone Number Usage Well Screen Interval (ft) Well Use Comment Approx. distance from source area of release (ft) Up/Down/ or Crossgradient* Approx. distance from source area of release (ft) Up/Down/Crossgradient/Ot her CommentPotable Well ID Well Depth (ft bgs) Receptor ID Location Contact Property Owner Contact Information Property Address City Phone Number Historical Groundwater Sampling Results Cajah's Mountain Superette 1990 Connelly Springs Road Lenoir, North Carolina Facility ID Number 0-004593 Incident Number: 28649 C5-C8 Aliphatics Carbon Fraction Clas C9-C18 Aliphatics Carbon Fraction Clas C9-C22 Aromatics Carbon Fraction Clas C 5 - C 8 C9 - C 1 2 C 9 - C 1 0 1 , 2 , 4 - T r i m e t h y l b e n z e n e 1 , 3 , 5 - T r i m e t h y l b e n z e n e B r o m o d i c h l o r o m e t h a n e B r o m o f o r m C h l o r o f o r m C h l o r o m e t h a n e D i b r o m o c h l o r o m e t h a n e D i b r o m o m e t h a n e E t h y l e n e D i b r o m i d e ( E D B ) I s o p r o p y l E t h e r I s o p r o p y l b e n z e n e M e t h y l t e r t b u t y l e t h e r ( M T B E ) n - B u t y l b e n z e n e n - P r o p y l b e n z e n e 1 , 2 , - D i c h l o r o e t h a n e T r i c h l o r o e t h y l e n e ( T C E ) T e t r a c h l o r o e t h y l e n e ( P C E ) p - I s o p r o p y l t o l u e n e s e c - B u t y l b e n z e n e S t y r e n e N a p h t h a l e n e B e n z e n e T o l u e n e E t h y l b e n z e n e T o t a l X y l e n e s T o t a l B T E X E t h y l e n e D i b r o m i d e ( E D B ) L e a d 12/10/2008 180 1.6 42 3.1 1.6 0.65 <0.1 11 3.3 <0.1 <0.1 *<0.022 0.24 0.34 65 0.4 0.63 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 10 2.5 1.2 3.3 17.0 <0.022 110 11/17/2009 1,300 35 61 2.9 2.1 <0.1 <0.1 13 <0.1 <0.1 <0.1 *<0.022 <0.1 0.46 18 0.7 0.83 <0.2 <0.1 <0.2 0.53 <0.1 <0.1 <0.1 17 5.1 0.75 9.5 32.4 <0.022 149 2/3/2012 1,180 488 137 19.1 7.6 <0.50 <0.50 5.2 <1.0 <0.50 <0.50 *<0.020 <0.50 2.2 3.7 1.6 5.2 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 6.1 26.6 18.1 6.9 41.0 92.6 <0.020 36.6 8/22/2012 1,570 125 135 3.4 5.4 <0.12 <0.12 7.0 <0.20 <0.10 NA *0.020 0.22 J 3.5 6.1 1.4 6.4 <0.16 <0.18 <0.14 0.50 1.5 <0.10 <0.10 49.2 13.9 2.5 26.8 92.4 0.020 20.0 1/23/2014 549 <50.0 <50.0 1.5 1.7 <0.50 <0.50 8.1 <1.0 <0.50 <0.50 *<0.020 <0.50 1.1 0.75 0.53 0.96 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 11.4 0.54 <0.50 5.3 17.2 <0.020 10.0 7/18/2014 785 542 117 16.3 8.8 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 0.62 5.5 5.0 2.9 6.0 <0.50 <0.50 <0.50 NA 2.4 <0.50 <2.0 37.4 4.7 2.8 44.0 88.9 <0.020 47.0 1/14/2015 163 131 <50.0 <0.50 0.57 <0.50 <0.50 9.4 <1.0 <0.50 <0.50 *<0.020 <0.50 1.1 0.77 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 0.53 <0.50 <2.0 8.2 <0.50 <0.50 3.6 11.8 <0.020 37.4 7/22/2015 NA NA NA 0.98 1.40 <0.50 <0.50 8.5 <1.0 <0.50 <0.50 *<0.020 <0.50 0.93 0.81 <0.50 0.45 J <0.50 <0.50 <0.50 NA 0.49 J <0.50 <2.0 6.9 <0.50 <0.50 3.9 10.8 <0.020 6.8 1/20/2016 NA NA NA <0.50 <0.50 0.27 J <0.50 14.8 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 43.4 7/20/2016 NA NA NA 1.9 3.7 <0.50 <0.50 4.4 <1.0 <0.50 <0.50 <0.50 <0.50 0.78 5.8 <0.50 0.42 J <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 8.1 14.1 9.0 28.2 59.4 NA 20.5 12/29/2016 NA NA NA 19.1 4.0 <0.50 <0.50 3.5 <1.0 <0.50 <0.50 <0.50 <0.50 2.4 3.0 <0.50 1.6 <0.50 <0.50 <0.50 NA 0.25 J 0.44 J <2.0 12.9 11.8 33.9 204.8 263.4 NA 22.2 3/13/2009 605 540 <100 29.3 10.7 1.8 <0.1 16.2 <1.0 <0.1 <0.1 *<0.02 2.8 1.7 72.1 1.1 3.7 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 151 80.8 11.6 116.1 360 <0.02 22.7 11/17/2009 2,600 460 660 110 38 <0.1 <0.1 16 <0.1 <0.1 <0.1 *<0.023 <0.1 3.9 340 <0.1 6.3 0.74 <0.1 <0.2 3.2 <0.1 <0.1 3.8 630 170 16 320 1,136 <0.023 22.4 2/3/2012 1,980 1,450 213 79.1 28.3 0.74 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 6.1 5.7 135 <0.50 10.9 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 3.7 336 79.3 32.7 233 681 <0.020 31.5 8/22/2012 3,660 1,180 1,180 126 53.2 <2.3 <2.4 14.1 <3.9 <2.0 NA *0.042 15.3 4.4 J 389 <2.0 7.4 J <3.3 <3.6 <2.7 <2.0 <2.0 <2.0 7.2 J 939 89.7 18.3 447 1,494 0.042 29.4 1/24/2014 2,020 445 <250 52.0 18.9 <1.0 <1.0 <1.0 <2.0 <1.0 <1.0 *<0.020 8.1 1.6 222 <1.0 1.3 <1.0 <1.0 <1.0 NA <1.0 <1.0 5.9 272 20.7 2.5 135.3 430.5 <0.020 <5.0 7/17/2014 2,350 696 <250 19.7 23.1 <1.2 <1.2 <1.2 <2.5 <1.2 <1.2 *<0.020 17.3 2.8 444 <1.2 2.2 <1.2 <1.2 <1.2 NA <1.2 <1.2 14.2 499 19.7 5.1 187.4 711.2 <0.020 11.7 1/14/2015 613 345 94.2 <2.5 16.8 <2.5 <2.5 5.7 <5.0 <2.5 <2.5 *<0.020 10.0 <2.5 274 <2.5 <2.5 <2.5 <2.5 <2.5 <2.5 <2.5 <2.5 14.1 345 10.9 3.9 68.9 428.7 <0.020 15.8 7/22/2015 NA NA NA 3.3 2.1 <1.2 <1.2 3.4 <2.5 <1.2 <1.2 *<0.020 7.1 1.4 197 <1.2 0.74 J 0.73 J <1.2 <1.2 NA <1.2 <1.2 7.1 143 2.4 1.4 12.8 159.6 <0.020 8.9 1/20/2016 NA NA NA 0.88 0.35 J <0.50 <0.50 2.7 <1.0 <0.50 <0.50 <0.50 0.62 0.58 12.6 <0.50 <0.50 <0.50 <0.50 <0.50 NA 0.26 J <0.50 <2.0 16.1 <0.50 <0.50 2.6 18.7 NA 61.8 7/20/2016 NA NA NA 0.34 J <0.50 <0.50 <0.50 5.1 <1.0 <0.50 <0.50 <0.50 <0.50 0.46 J 4.4 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 6.9 <0.50 <0.50 1.35 J 8.25 J NA 37.1 12/28/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 2.1 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 3.2 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 15.6 3/13/2009 <100 <100 <100 <0.50 <0.50 <0.50 <0.1 0.68 <1.0 <0.1 <0.1 *<0.02 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 ND <0.02 19.5 11/17/2009 <30 <10 <35 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 *<0.022 <0.1 <0.1 <0.2 <0.1 <0.1 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.1 ND <0.022 165 2/3/2012 <50.0 <50.0 <50.0 <0.50 <0.50 2.5 <0.50 11.9 <1.0 0.71 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 161 8/23/2012 <35 <35 <35 <0.10 <0.10 2.3 0.12 17.1 <0.20 0.27 J NA *<0.0091 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0091 100 1/23/2014 <50.0 <50.0 <50.0 <0.50 <0.50 1.4 <0.50 18.2 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 148 7/18/2014 <50.0 <50.0 <50.0 <0.50 <0.50 2.1 <0.50 22.7 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 174 1/14/2015 <50.0 <50.0 <50.0 <0.50 <0.50 1.5 <0.50 22.6 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 108 7/22/2015 NA NA NA <0.50 <0.50 0.97 <0.50 17.5 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 51.9 3/13/2009 <100 <100 <100 <0.50 <0.50 <0.50 <0.1 <0.50 <1.0 <0.1 <0.1 *<0.02 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 0.60 <0.50 <0.50 0.6 <0.02 25.9 11/17/2009 <30 <10 <35 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 *<0.022 <0.1 <0.1 <0.2 <0.1 <0.1 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 <0.1 0.5 <0.2 0.41 1.0 <0.022 185 2/3/2012 <50.0 <50.0 <50.0 <0.50 <0.50 1.2 <0.50 6.0 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 61.9 8/22/2012 94.8 J <35 <35 <0.10 <0.10 1.7 <0.12 8.5 <0.20 0.36 J NA *<0.0097 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0097 47.9 1/23/2014 <50.0 <50.0 <50.0 <0.50 <0.50 0.58 <0.50 11.6 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 31.4 7/18/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 17.7 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 17.5 1/14/2015 <50.0 <50.0 <50.0 <0.50 <0.50 0.59 <0.50 14.8 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 13.2 7/22/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 7.7 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 26.7 11/17/2009 800 50 130 12 3.7 <0.1 <0.1 7.7 <0.1 <0.1 <0.1 *<0.022 <0.1 0.87 1.7 <0.1 1.4 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 1.1 35 88 9.9 61 193.9 <0.022 <10 2/3/2012 156 155 <50.0 4.7 1.0 <0.50 <0.50 1.4 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 4.2 <0.50 3.8 1.3 8.3 13.4 <0.020 35.0 8/22/2012 146 <35 <35 <0.10 <0.10 <0.12 <0.12 0.73 <0.20 <0.10 NA *<0.0095 <0.11 0.18 J <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 0.36 J <0.13 <0.15 0.63 J 0.99 <0.0095 <5.0 1/24/2014 131 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 32.9 7/18/2014 55.2 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 9.2 1/14/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 1.3 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 18.9 7/22/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 1.2 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 79.4 1/20/2016 NA NA NA <0.50 0.87 <0.50 <0.50 0.58 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 0.39 J 6.5 1.9 5.18 J 13.97 J NA 36.8 7/20/2016 NA NA NA 4.7 6.5 <0.50 <0.50 0.68 <1.0 <0.50 <0.50 <0.50 <0.50 1.7 <0.50 <0.50 0.41 J <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 1.2 3.3 4.1 103.0 111.6 NA 13.6 12/29/2016 NA NA NA 27.1 15.8 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 4.4 <0.50 <0.50 1.4 <0.50 <0.50 <0.50 NA 0.37 J <0.50 <2.0 6.1 1.2 <0.50 291.8 299.1 NA 3.0 J Table 3 EPA METHOD 6010 DATE SAMPLED EPA METHOD 504.1 EPA METHOD 6200B (Target analytes reported above method detection limits) MADEP VPH SAMPLE I.D. MW-3 MW-1 MW-2 MW-5 MW-4 Page 1 of 7 Historical Groundwater Sampling Results Cajah's Mountain Superette 1990 Connelly Springs Road Lenoir, North Carolina Facility ID Number 0-004593 Incident Number: 28649 C5-C8 Aliphatics Carbon Fraction Clas C9-C18 Aliphatics Carbon Fraction Clas C9-C22 Aromatics Carbon Fraction Clas C 5 - C 8 C9 - C 1 2 C 9 - C 1 0 1 , 2 , 4 - T r i m e t h y l b e n z e n e 1 , 3 , 5 - T r i m e t h y l b e n z e n e B r o m o d i c h l o r o m e t h a n e B r o m o f o r m C h l o r o f o r m C h l o r o m e t h a n e D i b r o m o c h l o r o m e t h a n e D i b r o m o m e t h a n e E t h y l e n e D i b r o m i d e ( E D B ) I s o p r o p y l E t h e r I s o p r o p y l b e n z e n e M e t h y l t e r t b u t y l e t h e r ( M T B E ) n - B u t y l b e n z e n e n - P r o p y l b e n z e n e 1 , 2 , - D i c h l o r o e t h a n e T r i c h l o r o e t h y l e n e ( T C E ) T e t r a c h l o r o e t h y l e n e ( P C E ) p - I s o p r o p y l t o l u e n e s e c - B u t y l b e n z e n e S t y r e n e N a p h t h a l e n e B e n z e n e T o l u e n e E t h y l b e n z e n e T o t a l X y l e n e s T o t a l B T E X E t h y l e n e D i b r o m i d e ( E D B ) L e a d Table 3 EPA METHOD 6010 DATE SAMPLED EPA METHOD 504.1 EPA METHOD 6200B (Target analytes reported above method detection limits) MADEP VPH SAMPLE I.D. 11/17/2009 1,200 990 410 23 4 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 *<0.023 3 3.7 130 0.79 7.2 0.34 <0.1 <0.2 1.9 0.9 <0.1 1.2 370 180 39 168 757 <0.023 45.2 2/2/2012 790 479 69.3 13.3 4.9 <0.50 <0.50 2.5 <1.0 <0.50 <0.50 *<0.020 <0.50 1.6 5.2 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 112 36.2 13.8 61.7 223.7 <0.020 92.3 8/22/2012 1,060 331 320 20.8 9.2 <0.59 <0.59 2.0 J <0.98 <0.51 NA *0.062 2.4 J 2.6 4.9 0.69 J 4.9 <0.82 <0.90 <0.69 0.63 J 1.2 J <0.50 2.0 J 226 77.1 24.9 122.1 450.1 0.062 18.1 1/23/2014 282 54.0 <50.0 3.6 1.5 <0.50 <0.50 2.4 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 1.0 <0.50 0.57 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 21.1 5.7 3.0 12.2 42.0 <0.020 41.2 7/17/2014 1/13/2015 7/22/2015 1/19/2016 7/19/2016 12/28/2016 11/17/2009 4,200 550 1,000 100 31 <0.1 <0.1 12 <0.1 <0.1 <0.1 *<0.023 12 7.4 290 3.2 9.3 1.4 <0.1 <0.2 2.6 <0.1 0.58 5.4 920 890 78 520 2,408 <0.023 <10 2/2/2012 1,840 1,840 428 88.7 31.0 <0.50 <0.50 15.0 <1.0 <0.50 <0.50 *<0.020 4.0 5.9 95.0 <0.50 8.0 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 4.1 252 131 15.4 291.6 690 <0.020 52.5 8/22/2012 2,250 784 753 110 32.1 <1.2 <1.2 11.7 <2.0 <1.0 NA *0.058 9.4 5.8 196 2.9 J 10.9 <1.6 <1.8 <1.4 1.3 J 2.0 J <1.0 4.3 J 463 275 43.5 418 1,199.5 0.058 <5.0 1/23/2014 3,790 1,880 <500 195 64.3 <5.0 <5.0 <5.0 <10.0 <5.0 <5.0 *0.052 11.4 12.6 170 <5.0 26.7 <5.0 <5.0 <5.0 NA <5.0 <5.0 <20.0 811 952 132 814 2,709 0.052 73.2 7/18/2014 3,140 1,800 <500 148 47.3 <5.0 <5.0 <5.0 <10.0 <5.0 <5.0 *0.085 6.1 9.4 68.1 <5.0 19.9 <5.0 <5.0 <5.0 NA <5.0 <5.0 <20.0 520 1,040 137 720 2,417 0.085 19.2 1/14/2015 2,930 2,610 <2,500 179 54.7 <5.0 <5.0 <5.0 <10.0 <5.0 <5.0 *<0.020 9.8 10.9 112 <5.0 23.2 <5.0 <5.0 <5.0 <5.0 <5.0 <5.0 <20.0 650 934 126 734 2,444 <0.020 216 7/22/2015 NA NA NA 101 39.9 <2.5 <2.5 4.6 <5.0 <2.5 <2.5 *0.085 9.8 7.8 134 <2.5 14.2 1.8 J <2.5 <2.5 NA 2.7 <2.5 7.4 J 434 401 59.4 387 1,281 0.085 23.5 1/20/2016 NA NA NA 34.2 14.7 <1.2 <1.2 4.0 <2.5 <1.2 <1.2 <1.2 5.9 3.8 125 <1.2 3.0 0.70 J <1.2 <1.2 NA 1.5 <1.2 7.5 276 17.2 4.3 89.2 386.7 NA 38.7 7/20/2016 NA NA NA 71.4 <1.0 <1.0 <1.0 <1.0 <2.0 <1.0 <1.0 <1.0 12.2 4.1 132 <1.0 6.5 1.2 <1.0 <1.0 NA <1.0 <1.0 13.5 235 152 38.6 266 691.6 NA 67.3 12/29/2016 NA NA NA 54.8 18.9 <1.0 <1.0 <1.0 <2.0 <1.0 <1.0 <1.0 12.1 1.8 244 <1.0 1.9 1.4 <1.0 <1.0 NA <1.0 <1.0 27.1 77.7 37.2 16.1 139.9 270.9 NA 21.5 11/17/2009 31,000 4,100 8,700 580 130 <5 <0.1 <5 <5 <0.1 <0.1 *2.8 <5 25 <10 <5 61 39 27 27 <5 <5 29 130 1,900 17,000 900 4,600 24,400 2.8 <10 2/2/2012 8/22/2012 1/20/2014 7/17/2014 1/13/2015 7/22/2015 NA NA NA 4,130 2,480 <12.5 <12.5 <12.5 <25.0 <12.5 <12.5 *20.0 <12.5 335 77.2 434 1,220 <12.5 <12.5 <12.5 NA <12.5 83.3 2,330 6,810 36,100 4,160 19,240 66,310 20.0 8.9 1/20/2016 NA NA NA 5,330 1,290 <125 <125 <125 <250 <125 <125 <125 <125 189 <125 <125 626 <125 <125 <125 NA <125 <125 1,320 1,800 21,500 3,040 19,530 45,870 NA 54.1 7/20/2016 NA NA NA 5,350 1,500 <62.5 <62.5 <62.5 <125 <62.5 <62.5 <62.5 <62.5 204 208 259 708 <62.5 <62.5 <62.5 NA <62.5 55.8 J 1,280 4,950 24,600 2,610 15,440 47,600 NA 48.7 12/29/2016 NA NA NA 3,590 852 <100 <100 <100 <200 <100 <100 <100 <100 137 208 <100 425 <100 <100 <100 NA <100 63.1 J 1,000 7,310 36,400 2,750 16,320 62,780 NA 6.7 7/28/2010 <30 <35 <5 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 *<0.021 <0.1 <0.2 <0.2 <0.1 <0.1 <0.1 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 ND <0.021 23.7 2/2/2012 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.019 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 1.6 <0.50 1.1 2.7 <0.019 6.4 8/22/2012 784 186 218 <0.10 <0.10 <0.10 <0.10 <0.10 <0.11 <0.10 NA *<0.0094 <0.10 <0.10 <0.10 <0.10 <0.10 <0.10 <0.10 <0.10 <0.10 <0.10 <0.10 <0.15 <0.10 0.26 J <0.10 <0.22 0.26 <0.0094 <5.0 1/22/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 31.5 7/17/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 50.0 1/14/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 56.7 7/22/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 15.4 7/28/2010 <30 <35 <5 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 *<0.021 <0.1 <0.2 <0.2 <0.1 <0.1 <0.1 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 0.12 1.4 <0.1 0.29 1.8 <0.021 <10 2/2/2012 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 0.83 <0.50 <1.5 0.83 <0.020 4.9 J 8/23/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0095 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0095 20.2 1/22/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 21.3 7/17/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 1/14/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 17.3 7/22/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 9.0 Not Sampled Due To Presence Of Free Product Not Sampled Due to Mud in Well Not Sampled Due to Presence of Free Product MW-10 Not Sampled Due to Mud/Sediment in Well Not Sampled Due to Presence of Free Product Not Sampled Due To Presence Of Free Product Not Sampled Due to Mud in Well Not Sampled Due To Presence Of Free Product MW-9 MW-7 MW-8 Not Sampled Due to Mud/Sediment in Well MW-6 Not Sampled Due to Mud/Sediment in Well Not Sampled Due to Mud/Sediment in Well Page 2 of 7 Historical Groundwater Sampling Results Cajah's Mountain Superette 1990 Connelly Springs Road Lenoir, North Carolina Facility ID Number 0-004593 Incident Number: 28649 C5-C8 Aliphatics Carbon Fraction Clas C9-C18 Aliphatics Carbon Fraction Clas C9-C22 Aromatics Carbon Fraction Clas C 5 - C 8 C9 - C 1 2 C 9 - C 1 0 1 , 2 , 4 - T r i m e t h y l b e n z e n e 1 , 3 , 5 - T r i m e t h y l b e n z e n e B r o m o d i c h l o r o m e t h a n e B r o m o f o r m C h l o r o f o r m C h l o r o m e t h a n e D i b r o m o c h l o r o m e t h a n e D i b r o m o m e t h a n e E t h y l e n e D i b r o m i d e ( E D B ) I s o p r o p y l E t h e r I s o p r o p y l b e n z e n e M e t h y l t e r t b u t y l e t h e r ( M T B E ) n - B u t y l b e n z e n e n - P r o p y l b e n z e n e 1 , 2 , - D i c h l o r o e t h a n e T r i c h l o r o e t h y l e n e ( T C E ) T e t r a c h l o r o e t h y l e n e ( P C E ) p - I s o p r o p y l t o l u e n e s e c - B u t y l b e n z e n e S t y r e n e N a p h t h a l e n e B e n z e n e T o l u e n e E t h y l b e n z e n e T o t a l X y l e n e s T o t a l B T E X E t h y l e n e D i b r o m i d e ( E D B ) L e a d Table 3 EPA METHOD 6010 DATE SAMPLED EPA METHOD 504.1 EPA METHOD 6200B (Target analytes reported above method detection limits) MADEP VPH SAMPLE I.D. 7/28/2010 75,000 5,700 24,000 1,800 520 <50 <0.1 <50 <50 <0.1 <0.1 *3.1 190 110 5,600 <50 270 <100 <50 <100 <50 <50 84 700 15,000 37,000 2,800 14,100 68,900 3.1 19.3 2/2/2012 56,300 68,400 <10,000 2,090 492 <0.50 <0.50 <0.50 <1.0 0.73 <0.50 *4.1 151 116 2,590 <0.50 273 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 565 9,890 27,100 2,980 15,290 55,260 4.1 18.1 8/23/2012 17,700 8,370 4,730 2,150 528 <120 <120 <160 <200 <100 NA *2.4 131 J <100 3,210 <100 309 J <160 <180 <140 <100 <100 <100 616 8,720 31,700 3,140 17,310 60,870 2.4 19.5 1/22/2014 71,500 47,800 5,070 2,130 489 <125 <125 <125 <250 <125 <125 *2.7 <125 <125 1,960 <125 265 <125 <125 <125 NA <125 <125 538 7,860 30,300 2,650 14,460 55,270 2.7 55.7 7/17/2014 54,100 33,200 <5,000 1,540 360 <5.0 <5.0 <5.0 <10.0 <5.0 <5.0 *0.93 57.6 69.4 1,210 <5.0 187 <5.0 <5.0 <5.0 NA <5.0 44.4 510 5,350 19,300 1,900 10,410 36,960 0.93 39.7 1/13/2015 54,700 59,600 <10,000 2,860 644 <100 <100 <100 <200 <100 <100 *2.5 <100 124 1,400 <100 361 <100 <100 <100 <100 <100 <100 739 6,650 28,100 3,200 17,760 55,710 2.5 48.5 7/21/2015 NA NA NA 2,270 568 <125 <125 <125 <250 <125 <125 *2.4 83.9 J 103 J 1,870 <125 307 <125 <125 <125 NA <125 67.8 J 728 5,630 26,000 2,960 15,150 49,740 2.4 14.9 1/20/2016 NA NA NA 2,530 594 <125 <125 <125 <250 <125 <125 <125 94.8 J 105 J 2,510 <125 322 <125 <125 <125 NA <125 <125 642 5,450 23,900 2,920 16,260 48,530 NA 54.8 7/19/2016 NA NA NA 851 201 <20.0 <20.0 <20.0 <40.0 <20.0 <20.0 <20.0 <20.0 34.1 138 <20.0 105 <20.0 <20.0 <20.0 NA <20.0 13.4 J 229 693 4,110 686 3,870 9,359 NA 23.2 12/28/2016 NA NA NA 2,360 539 <100 <100 <100 <200 <100 <100 <100 <100 93.5 J 864 <100 307 <100 <100 <100 NA <100 <100 605 3,400 20,400 2,540 13,750 40,090 NA 7.4 7/28/2010 <30 <35 <5 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 *<0.021 <0.1 <0.2 <0.2 <0.1 <0.1 <0.1 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 2.7 2.7 <0.021 15.2 2/2/2012 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <4.0 8/23/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0094 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0094 11.8 1/20/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 11.0 7/17/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 0.96 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 58.0 1/13/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *0.10 0.58 <0.50 46.0 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND 0.10 437 7/21/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *0.23 3.5 <0.50 207 <0.50 <0.50 1.1 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND 0.23 45.7 1/19/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 3.2 <0.50 188 <0.50 <0.50 0.68 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 29.3 7/19/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 6.4 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 50.5 12/28/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 10.2 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 9.7 2/2/2012 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 4.5 J 8/24/2012 163 50.8 J <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0096 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0096 <5.0 1/21/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 7/16/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 5.9 1/13/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 12.8 7/21/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 5.5 2/2/2012 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 4.3 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 11.4 8/23/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0092 <0.11 <0.10 1.7 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0092 14.5 1/20/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 21.1 7/17/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.021 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.021 12.4 1/13/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 117 7/21/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 2.9 <0.50 33.5 <0.50 <0.50 0.68 <0.50 <0.50 NA <0.50 <0.50 <2.0 1.1 <0.50 <0.50 <1.5 ND <0.020 7.7 1/19/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 4.1 <0.50 122 <0.50 <0.50 1.0 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 40.7 7/19/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 1.6 <0.50 14.2 <0.50 <0.50 0.29 J <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 92.6 12/28/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 1.1 <0.50 9.3 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 4.0 J 2/2/2012 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 8/23/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0095 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0095 <5.0 1/20/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 7/16/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 1/13/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 7/21/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 2/2/2012 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 10.6 8/24/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0096 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0096 41.7 1/21/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 152 7/16/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.021 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.021 98.0 1/13/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 233 7/21/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.021 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.021 30.7 MW-15 MW-16 MW-11 MW-12 MW-14 MW-13 Page 3 of 7 Historical Groundwater Sampling Results Cajah's Mountain Superette 1990 Connelly Springs Road Lenoir, North Carolina Facility ID Number 0-004593 Incident Number: 28649 C5-C8 Aliphatics Carbon Fraction Clas C9-C18 Aliphatics Carbon Fraction Clas C9-C22 Aromatics Carbon Fraction Clas C 5 - C 8 C9 - C 1 2 C 9 - C 1 0 1 , 2 , 4 - T r i m e t h y l b e n z e n e 1 , 3 , 5 - T r i m e t h y l b e n z e n e B r o m o d i c h l o r o m e t h a n e B r o m o f o r m C h l o r o f o r m C h l o r o m e t h a n e D i b r o m o c h l o r o m e t h a n e D i b r o m o m e t h a n e E t h y l e n e D i b r o m i d e ( E D B ) I s o p r o p y l E t h e r I s o p r o p y l b e n z e n e M e t h y l t e r t b u t y l e t h e r ( M T B E ) n - B u t y l b e n z e n e n - P r o p y l b e n z e n e 1 , 2 , - D i c h l o r o e t h a n e T r i c h l o r o e t h y l e n e ( T C E ) T e t r a c h l o r o e t h y l e n e ( P C E ) p - I s o p r o p y l t o l u e n e s e c - B u t y l b e n z e n e S t y r e n e N a p h t h a l e n e B e n z e n e T o l u e n e E t h y l b e n z e n e T o t a l X y l e n e s T o t a l B T E X E t h y l e n e D i b r o m i d e ( E D B ) L e a d Table 3 EPA METHOD 6010 DATE SAMPLED EPA METHOD 504.1 EPA METHOD 6200B (Target analytes reported above method detection limits) MADEP VPH SAMPLE I.D. 2/2/2012 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 8.0 8/24/2012 78.4 J <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0095 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0095 16.3 1/21/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 95.6 7/16/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.021 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.021 91.4 1/13/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 139 7/21/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 0.33 J <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 21.7 2/2/2012 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 0.60 <0.50 <1.5 0.60 <0.020 28.2 8/23/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0093 0.39 J <0.10 1.2 <0.10 <0.11 <0.16 <0.18 <0.14 0.72 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0093 42.6 1/20/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 2.1 <0.50 1.7 <0.50 <0.50 0.81 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 79.3 7/16/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 1.7 <0.50 <0.50 0.63 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 50.9 1/13/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *0.023 2.0 <0.50 1.0 <0.50 <0.50 1.2 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND 0.023 109 7/21/2015 1/19/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 0.33 J <1.0 <0.50 <0.50 <0.50 2.2 <0.50 2.8 <0.50 <0.50 1.3 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 14.4 7/19/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 0.62 <0.50 <0.50 0.60 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 54.9 12/28/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 1.1 <0.50 1.2 <0.50 <0.50 1.6 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 2.8 J 2/2/2012 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <20.0 8/23/2012 <35 <35 41.6 J <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0093 <0.11 <0.10 0.30 J <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0093 25.3 1/20/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.019 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.019 139 7/16/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.021 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.021 54.5 1/13/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.021 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.021 112 7/21/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <100 2/2/2012 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 15.6 8/23/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 0.21 J <0.20 <0.10 NA *<0.0097 0.14 J <0.10 0.38 J <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0097 8.2 1/21/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 41.7 7/16/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.021 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.021 26.8 1/13/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 64.3 7/21/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.021 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.021 24.4 2/2/2012 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 3.9 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <4.0 8/24/2012 60.8 J <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0095 <0.11 <0.10 2.5 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0095 <5.0 1/21/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 7/16/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 1/13/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 7/21/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 3.4 J 4/3/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *0.024 1.7 <0.10 47.4 <0.10 <0.11 0.64 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND 0.024 29.9 8/23/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0097 0.80 <0.10 24.0 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0097 7.5 1/22/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 8.9 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 7/17/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 *<0.020 <0.50 <0.50 1.6 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 66.0 1/13/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 2.3 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 109 7/21/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 0.49 J <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 7.2 1/19/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 0.32 J <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 21.4 J 7/19/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 0.41 J <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 56.3 12/28/2016 MW-20 Not Sampled - Aboveground Pool Obstructing Well MW-17 MW-18 MW-22 MW-21 MW-19 Not Sampled - Could Not Find Page 4 of 7 Historical Groundwater Sampling Results Cajah's Mountain Superette 1990 Connelly Springs Road Lenoir, North Carolina Facility ID Number 0-004593 Incident Number: 28649 C5-C8 Aliphatics Carbon Fraction Clas C9-C18 Aliphatics Carbon Fraction Clas C9-C22 Aromatics Carbon Fraction Clas C 5 - C 8 C9 - C 1 2 C 9 - C 1 0 1 , 2 , 4 - T r i m e t h y l b e n z e n e 1 , 3 , 5 - T r i m e t h y l b e n z e n e B r o m o d i c h l o r o m e t h a n e B r o m o f o r m C h l o r o f o r m C h l o r o m e t h a n e D i b r o m o c h l o r o m e t h a n e D i b r o m o m e t h a n e E t h y l e n e D i b r o m i d e ( E D B ) I s o p r o p y l E t h e r I s o p r o p y l b e n z e n e M e t h y l t e r t b u t y l e t h e r ( M T B E ) n - B u t y l b e n z e n e n - P r o p y l b e n z e n e 1 , 2 , - D i c h l o r o e t h a n e T r i c h l o r o e t h y l e n e ( T C E ) T e t r a c h l o r o e t h y l e n e ( P C E ) p - I s o p r o p y l t o l u e n e s e c - B u t y l b e n z e n e S t y r e n e N a p h t h a l e n e B e n z e n e T o l u e n e E t h y l b e n z e n e T o t a l X y l e n e s T o t a l B T E X E t h y l e n e D i b r o m i d e ( E D B ) L e a d Table 3 EPA METHOD 6010 DATE SAMPLED EPA METHOD 504.1 EPA METHOD 6200B (Target analytes reported above method detection limits) MADEP VPH SAMPLE I.D. 2/2/2012 309 406 <50.0 25.0 <0.50 0.67 <0.50 1.1 <1.0 0.74 <0.50 *0.42 16.5 2.6 84.6 <0.50 3.1 3.6 <0.50 <0.50 <0.50 <0.50 <0.50 10.8 260 71.1 21.8 215 567.9 0.42 <4.0 8/23/2012 2,300 865 477 76.3 <2.0 <2.3 <2.4 <3.2 <3.9 <2.0 NA *1.1 51.9 7.3 J 251 <2.0 11.6 12.3 <3.6 <2.7 <2.0 <2.0 <2.0 31.3 967 266 82.1 638 1,953.1 1.1 <5.0 1/22/2014 3,060 2,060 <1,000 110 <5.0 <5.0 <5.0 <5.0 <10.0 <5.0 <5.0 *1.5 61.0 8.9 247 <5.0 12.2 16.5 <5.0 <5.0 NA <5.0 <5.0 42.3 1,470 65.2 85.8 796 2,417.0 1.5 <5.0 7/17/2014 4,160 2,360 <1,250 112 9.8 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *1.5 74.9 11.5 292 1.8 15.1 21.3 <0.50 <0.50 NA <0.50 <0.50 53.1 1,360 78.5 118 785 2,341.5 1.5 <5.0 1/13/2015 5,250 5,210 <5,000 104 8.6 <5.0 <5.0 <5.0 <10.0 <5.0 <5.0 *1.4 57.8 9.4 282 <5.0 12.4 16.3 <5.0 <5.0 <5.0 <5.0 <5.0 47.4 1,360 23.4 88.5 783 2,254.9 1.4 <5.0 7/21/2015 NA NA NA 71.1 6.6 <5.0 <5.0 <5.0 14.1 <5.0 <5.0 *1.6 54.3 9.8 311 <5.0 12.0 17.8 <5.0 <5.0 NA <5.0 <5.0 47.2 1,550 17.6 78.0 691 2,336.6 1.6 2.5 J 1/19/2016 NA NA NA 1.4 1.0 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 11.8 0.86 61.6 <0.50 <0.50 3.2 <0.50 <0.50 NA <0.50 <0.50 4.8 144 0.44 J 0.80 17.0 162.24 J NA 9.1 7/19/2016 NA NA NA 1.7 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 0.25 J 23.6 0.63 150 <0.50 0.56 6.1 <0.50 <0.50 NA <0.50 <0.50 6.0 155 <0.50 4.2 12.1 171.3 NA 15.4 12/28/2016 NA NA NA 38.5 7.1 <2.0 <2.0 <2.0 <4.0 <2.0 <2.0 <2.0 60.4 2.1 429 <2.0 2.1 17.2 <2.0 <2.0 NA <2.0 <2.0 15.5 405 10.0 12.1 253.1 680.2 NA 5.4 4/3/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *0.0096 J 0.91 <0.10 1.2 <0.10 <0.11 <0.12 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND 0.0096 J <5.0 8/23/2012 61.0 J <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0095 0.42 J <0.10 0.60 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0095 <5.0 1/22/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 7/17/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 1/13/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 7/22/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 0.65 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 1/19/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 0.55 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA <5.0 7/19/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 0.51 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA <5.0 12/28/2016 11/17/2009 1,300 180 230 41 <0.1 <0.1 <0.1 7.9 <0.1 <0.1 <0.1 *<0.022 2.3 2.6 450 1.2 3.2 <0.2 <0.1 <0.2 2.1 <0.1 <0.1 3.4 140 0.41 3 21.8 165.6 <0.022 <10 2/3/2012 1,510 502 90 31.1 <0.50 <0.50 <0.50 15.7 <1.0 <0.50 <0.50 *0.023 2.7 2.8 490 1.6 2.1 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 3.7 134 0.61 1.0 54.2 189.8 0.023 11.7 8/22/2012 757 160 181 11.9 <1.0 <1.2 <1.2 7.9 <2.0 <1.0 NA *0.026 2.1 J 1.1 J 349 <1.0 <1.1 <1.6 <1.8 <1.4 <1.0 <1.0 <1.0 1.5 J 57.9 11.8 <1.5 28.3 98.0 0.026 <5.0 1/23/2014 251 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 4.1 <1.0 <0.50 <0.50 *<0.020 1.2 <0.50 325 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 8.8 7/17/2014 273 <50.0 <50.0 <0.50 <0.50 1.1 <0.50 16.4 <1.0 <0.50 <0.50 *<0.020 1.8 <0.50 448 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 1/14/2015 123 <50.0 <50.0 <1.0 <1.0 <1.0 <1.0 10.3 <2.0 <1.0 <1.0 *<0.020 1.4 <1.0 174 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <4.0 <1.0 <1.0 <1.0 <3.0 ND <0.020 9.7 7/22/2015 NA NA NA <0.50 <0.50 0.88 <0.50 12.9 <1.0 <0.50 <0.50 *<0.020 1.4 <0.50 118 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 8.0 1/20/2016 NA NA NA <0.50 <0.50 0.67 <0.50 10.9 <1.0 <0.50 <0.50 <0.50 1.3 <0.50 101 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 8.7 7/20/2016 NA NA NA <0.50 <0.50 0.83 <0.50 11.3 <1.0 <0.50 <0.50 <0.50 0.84 <0.50 44.5 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 0.60 <0.50 <0.50 <1.5 0.60 NA 12.9 12/29/2016 NA NA NA 0.34 J <0.50 0.88 <0.50 12.7 <1.0 <0.50 <0.50 <0.50 0.52 <0.50 51.0 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 1.3 <0.50 <0.50 0.28 J 1.58 NA 7.1 7/28/2010 <30 <35 <5 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 *<0.021 <0.1 <0.2 <0.2 <0.1 <0.1 <0.1 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 1.4 2 <0.1 3.1 6.5 <0.021 <10 2/2/2012 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 1.3 6.9 0.77 3.7 12.7 <0.020 <4.0 8/22/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 0.28 J <0.10 NA *<0.0096 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0096 <5.0 1/22/2014 399 <50.0 <50.0 0.62 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 5.5 <0.50 <0.50 3.84 3.84 <0.020 <5.0 7/17/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 10.0 1/14/2015 85.8 74.8 <50.0 3.5 0.69 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *0.028 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 39.1 9.7 1.9 25.6 76.3 0.028 5.8 7/22/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 1/20/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA <5.0 7/20/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 4.4 J 12/28/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA <5.0 2/3/2012 <50.0 69.9 <50.0 0.69 <0.50 <0.50 <0.50 0.66 <1.0 <0.50 <0.50 *<0.021 <0.50 <0.50 25.8 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 1.7 1.5 <0.50 2.4 5.6 <0.021 4.2 J 8/22/2012 58.4 J <35 <35 0.17 J <0.10 <0.12 <0.12 <0.16 1.4 <0.10 NA *<0.0095 0.22 J <0.10 33.2 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 0.52 0.46 J <0.15 0.26 J 1.24 <0.0095 <5.0 1/23/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 27.1 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.30 <0.50 <1.5 ND <0.020 <5.0 7/17/2014 <50.0 <50.0 <50.0 0.55 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 25.1 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 1.0 1.0 <0.020 <5.0 1/14/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 7/22/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 0.41 J <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 0.56 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 1/20/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA <5.0 7/20/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 4.6 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA <5.0 12/29/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 6.4 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA <5.0 IMW-1 IMW-2 Not Sampled - Could Not Find DMW-1 DMW-2 DMW-3 Page 5 of 7 Historical Groundwater Sampling Results Cajah's Mountain Superette 1990 Connelly Springs Road Lenoir, North Carolina Facility ID Number 0-004593 Incident Number: 28649 C5-C8 Aliphatics Carbon Fraction Clas C9-C18 Aliphatics Carbon Fraction Clas C9-C22 Aromatics Carbon Fraction Clas C 5 - C 8 C9 - C 1 2 C 9 - C 1 0 1 , 2 , 4 - T r i m e t h y l b e n z e n e 1 , 3 , 5 - T r i m e t h y l b e n z e n e B r o m o d i c h l o r o m e t h a n e B r o m o f o r m C h l o r o f o r m C h l o r o m e t h a n e D i b r o m o c h l o r o m e t h a n e D i b r o m o m e t h a n e E t h y l e n e D i b r o m i d e ( E D B ) I s o p r o p y l E t h e r I s o p r o p y l b e n z e n e M e t h y l t e r t b u t y l e t h e r ( M T B E ) n - B u t y l b e n z e n e n - P r o p y l b e n z e n e 1 , 2 , - D i c h l o r o e t h a n e T r i c h l o r o e t h y l e n e ( T C E ) T e t r a c h l o r o e t h y l e n e ( P C E ) p - I s o p r o p y l t o l u e n e s e c - B u t y l b e n z e n e S t y r e n e N a p h t h a l e n e B e n z e n e T o l u e n e E t h y l b e n z e n e T o t a l X y l e n e s T o t a l B T E X E t h y l e n e D i b r o m i d e ( E D B ) L e a d Table 3 EPA METHOD 6010 DATE SAMPLED EPA METHOD 504.1 EPA METHOD 6200B (Target analytes reported above method detection limits) MADEP VPH SAMPLE I.D. 2/2/2012 <50.0 116 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <4.0 8/23/2012 47.4 J <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 1.4 <0.10 NA *<0.0094 <0.11 <0.10 0.18 J <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 0.16 J 0.23 J 0.22 J <0.15 <0.30 0.45 <0.0094 <5.0 1/21/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 2.4 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 7/17/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 1/13/2015 <50.0 <50.0 <50.0 1.5 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 0.64 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 6.3 5.0 <0.50 7.2 18.50 <0.020 <5.0 7/21/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 0.39 J <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 1/19/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 0.78 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 0.57 <0.50 <0.50 0.28 J 0.85 J NA <5.0 7/19/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 0.40 J <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 12.4 12/28/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 0.32 J <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA <5.0 4/3/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0095 0.18 J <0.10 3.1 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 0.58 <0.13 <0.15 <0.30 0.58 <0.0095 <5.0 8/23/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 0.52 <0.10 NA *<0.0095 0.26 J <0.10 5.2 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 0.79 <0.13 <0.15 <0.30 0.79 <0.0095 <5.0 1/22/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 7/17/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 0.55 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 1/13/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 7/21/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 3.4 J 1/19/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 0.28 J <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA <5.0 7/19/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 0.30 J <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 13.7 12/28/2016 7/26/2010 NA NA NA <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.1 <0.1 *<0.023 <0.1 <0.2 <0.2 <0.1 <0.1 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 0.84 0.12 <0.1 <0.1 2.7 2.8 <0.023 NA 5/5/2011 <30 <40 <10 <0.1 <0.1 <0.1 <0.1 <0.1 0.97 <0.1 <0.1 *<0.021 <0.5 <0.2 <0.2 <0.1 <0.1 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 ND <0.021 NA 8/29/2012 39.6 J <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0093 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0093 NA 1/20/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA NA 7/26/2010 NA NA NA <0.1 <0.1 <0.1 <0.1 0.31 <0.2 <0.1 <0.1 *<0.021 <0.1 <0.2 6 <0.1 <0.1 0.12 <0.1 <0.2 <10 <0.1 <0.1 0.34 0.12 <0.1 <0.1 <0.1 0.12 <0.021 NA 5/5/2011 <30 <40 <10 <0.1 <0.1 <0.1 <0.1 0.22 1.5 <0.1 <0.1 *<0.02 <0.5 <0.2 2.5 <0.1 <0.1 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 ND <0.02 NA 8/24/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 1.6 <0.20 <0.10 NA *<0.0096 <0.11 <0.10 3.7 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0096 NA 1/24/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 3.4 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 7/16/2014 1/15/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 3.4 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 7/22/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 3.0 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 1/20/2016 8/29/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0093 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0093 NA 1/15/2015 7/22/2015 8/29/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0093 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0093 NA 1/15/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 7/22/2015 5/5/2011 <30 <40 <10 <0.1 <0.1 <0.1 <0.1 0.4 0.33 <0.1 <0.1 *<0.022 <0.5 <0.2 <0.2 <0.1 <0.1 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 ND <0.022 NA 8/24/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 0.44 J <0.20 <0.10 NA *<0.0096 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0096 NA 1/24/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 7/16/2014 1/15/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 7/22/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 0.34 J <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA Not Sampled - No One Home, No Access Not Sampled - No One Home, No Access Not Sampled - No One Home, No Access Not Sampled - Well House Partialy Collapsed and Multiple Hazards to Access Sample PortPW-2 Not Sampled - No One Home, No Access PW-4 PW-5 Not Sampled - No One Home, No Access PW-6 PW-1 Not Sampled - Could Not Find DMW-4 DMW-5 Page 6 of 7 Historical Groundwater Sampling Results Cajah's Mountain Superette 1990 Connelly Springs Road Lenoir, North Carolina Facility ID Number 0-004593 Incident Number: 28649 C5-C8 Aliphatics Carbon Fraction Clas C9-C18 Aliphatics Carbon Fraction Clas C9-C22 Aromatics Carbon Fraction Clas C 5 - C 8 C9 - C 1 2 C 9 - C 1 0 1 , 2 , 4 - T r i m e t h y l b e n z e n e 1 , 3 , 5 - T r i m e t h y l b e n z e n e B r o m o d i c h l o r o m e t h a n e B r o m o f o r m C h l o r o f o r m C h l o r o m e t h a n e D i b r o m o c h l o r o m e t h a n e D i b r o m o m e t h a n e E t h y l e n e D i b r o m i d e ( E D B ) I s o p r o p y l E t h e r I s o p r o p y l b e n z e n e M e t h y l t e r t b u t y l e t h e r ( M T B E ) n - B u t y l b e n z e n e n - P r o p y l b e n z e n e 1 , 2 , - D i c h l o r o e t h a n e T r i c h l o r o e t h y l e n e ( T C E ) T e t r a c h l o r o e t h y l e n e ( P C E ) p - I s o p r o p y l t o l u e n e s e c - B u t y l b e n z e n e S t y r e n e N a p h t h a l e n e B e n z e n e T o l u e n e E t h y l b e n z e n e T o t a l X y l e n e s T o t a l B T E X E t h y l e n e D i b r o m i d e ( E D B ) L e a d Table 3 EPA METHOD 6010 DATE SAMPLED EPA METHOD 504.1 EPA METHOD 6200B (Target analytes reported above method detection limits) MADEP VPH SAMPLE I.D. PW-7 5/5/2011 <30 <40 <10 <0.1 <0.1 4.2 3.5 3.2 0.19 7.2 0.1 *<0.021 <0.5 <0.2 <0.2 <0.1 <0.1 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 ND <0.021 NA 5/5/2011 <30 <40 <10 <0.1 <0.1 <0.1 <0.1 <0.1 0.93 <0.1 <0.1 *<0.022 <0.5 <0.2 0.64 <0.1 <0.1 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 ND <0.022 NA 8/24/2012 42.9 J <35 <35 <0.10 <0.10 <0.12 <0.12 0.20 J <0.20 <0.10 NA *<0.0096 0.30 J <0.10 0.40 J <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0096 NA 1/24/2014 7/18/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 1/15/2015 7/22/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 1/20/2016 PW-10 1/15/2015 PW-11 8/29/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0093 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0093 NA 8/29/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 0.54 <0.20 <0.10 NA *<0.0095 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0095 NA 1/15/2015 7/22/2015 1/15/2015 7/22/2015 PW-14 1/15/2015 11/17/2009 <30 <10 <35 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 *<0.022 <0.1 <0.1 <0.2 <0.1 <0.1 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.1 ND <0.022 NA 7/26/2010 NA NA NA <0.1 <0.1 <0.1 <0.1 1.3 <0.1 <0.1 <0.1 *<0.022 <0.1 <0.1 <0.2 <0.1 <0.1 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 1.2 <0.1 <0.1 <0.2 <0.1 ND <0.022 NA 5/5/2011 <30 <40 <10 <0.1 <0.1 <0.1 <0.1 1.2 0.78 <0.1 <0.1 *<0.022 <0.5 <0.2 0.25 <0.1 <0.1 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 ND <0.022 NA 7/18/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 1/15/2015 7/22/2015 11/17/2009 440 80 220 9.6 2.2 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 *NA <0.1 0.5 <0.1 <0.1 1.1 <0.1 <0.1 <0.2 <0.1 <0.1 0.46 2.7 12 170 16 81 ND NA NA 7/26/2010 NA NA NA <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 *<0.021 <0.1 <0.1 <0.2 <0.1 <0.1 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 1.4 4.3 <0.2 3.9 ND <0.021 NA 5/5/2011 <30 <40 <10 <0.1 <0.1 <0.1 <0.1 0.21 0.3 <0.1 <0.1 *<0.022 <0.5 <0.2 <0.2 <0.1 <0.1 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 ND <0.022 NA 8/29/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0094 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0094 NA 1/20/2016 7/26/2010 NA NA NA <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 *<0.022 <0.1 <0.1 <0.2 <0.1 <0.1 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.1 ND <0.022 NA 8/29/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0096 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0096 NA 1/20/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.50 ND NA NA 5/5/2011 <30 <40 <10 <0.1 <0.1 <0.1 <0.1 0.10 1.7 <0.1 <0.1 *<0.023 <0.5 <0.2 <0.2 <0.1 <0.1 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 ND <0.023 NA 8/24/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0097 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0097 NA 1/27/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 7/18/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 1/15/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 7/22/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 2/2/2012 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 0.90 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 8/24/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0095 <0.11 <0.10 0.85 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0095 NA 1/24/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 7/18/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 1/15/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 7/22/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 1/20/2016 400 700 200 400 400 0.6 4 70 3 0.4 NE 0.02 70 70 20 70 70 0.4 3 0.7 25 70 70 6 1 600 600 500 N/A 0.02 15 NE NE NE 28,500 25,000 NE 4000 70,000 3,000 400 NE 50 70,000 25,000 20,000 6,900 30,000 400 3,000 700 11,700 8,500 70,000 6,000 5,000 260,000 84,500 85,500 N/A 50 15,000 1. All measurements are in micrograms per liter (ug/L)9. Analytical table indicates target analyte concentrations reported above method detection limit 2. NC 2L GW Standard = Title 15A NCAC 2L .0202 Groundwater Standard. (Amended Effective April 16, 2012 10. NA = Not Analyzed for specified paramete 3. "<" or ND = Not detected above method detection limit or laboratory reporting limi 11. N/A = Not Applicabl 4. GCL = Gross Contaminant Level established by NCDEQ 12. J = Estimated value below the laboratory reporting limit but above the method detection limi 5. Target analyte concentrations detected above 2L Groundwater Standards are bolded 6. Target analyte concentrations detected above GCLs are bolded and italicize 7. NE = Not Established. 14. * = Value reported under EPA Method 504.1 PW-15 Not Sampled - Owner Refused Access Not Sampled - Owner Refused Access Not Sampled - No One Home, No Access Not Sampled - Well Not Operational During Winter Not Sampled - No One Home, No Access Not Sampled - No One Home, No Access PW-12 8. VPH = Volatile Petroleum Hydrocarbons: C5-C8 and C9-C18 aliphatic chains, and C9-C22 aromatic chain Not Sampled - No One Home and Outside Water Turned Off Not Sampled - No One Home, No Access Not Sampled - No One Home, No Access Not Sampled - No One Home, No Access Not Sampled; Outside Spigots Winterized and No One Home PW-21 13. Methylene chloride, a known laboratory contaminant, was reported at 0.2 ug/L for water collected from PW-16 on July 26, 2010; and at 0.51 ug/L for water collecte from PW-7 on May 5, 2011. PW-9 Not Sampled - No One Home, No Access PW-16 Not Sampled - No One Home, No Access PW-22 PW-13 GCLs NC 2L GW Standards PW-18 Page 7 of 7 Table 4 Free Product Recovery Information Cajah's Mountain Superette 1990 Connelly Springs Road Lenoir, North Carolina Facility ID Number 0-004593 Incident Number 28649 Date Well ID Free Product Recovery Method Product Thickness Before Recovery (Feet) Product Thickness After Recovery (Feet) Amount of Vaporized Product (Gallons) Amount of Liquid (Water and Product) (Gallons) Amount of Liquid Product (Gallons) Total Amount of Product Recovered (Gallons) 3/28/2012 MW-8 AFVR 2.15 0.01 6.76 226 44 50.76 6/28/2012 MW-8 AFVR 0.48 0.00 6.07 231 0.00 6.07 9/28/2012 MW-8 AFVR 0.26 0.00 8.68 231 0.00 8.68 12/13/2012 MW-8 AFVR 0.69 0.00 12.79 226 0.00 12.79 3/14/2013 MW-8 AFVR 0.31 0.00 5.34 231 0.00 5.34 7/24/2013 MW-8 AFVR 0.94 0.00 2.97 189 0.00 2.97 9/16/2013 MW-8 AFVR 0.61 0.00 5.34 270 0.00 5.34 12/18/2013 MW-8 AFVR 1.12 0.00 6.22 310 0.00 6.22 AFVR = Aggressive Fluid/Vapor Recovery 56.83 9/28/2012 8.68 65.51 Date of Recovery Event Total Volume of Free Product Recovered from Site During Current Recovery Event (Gallons) Cumulative Total Volume Recovered to Date from All Recovery Events (Gallons) 3/28/2012 50.76 50.76 6/28/2012 6.07 12.79 5.34 2.97 5.34 6.22 78.30 83.64 86.61 91.95 98.17 12/13/2012 3/14/2013 7/24/2013 9/16/2013 12/18/2013 Table 5 Monitored Natural Attenuation Parameters Cajah's Mountain Superette 1990 Connelly Springs Road Lenoir, North Carolina Facility ID Number 0-004593 Incident Number 28649 Sample I.D.Date Sampled Dissolved Oxygen Nitrate Manganese Ferrous Iron Sulfate Methane 8/23/2012 3.22 0.17 0.832 <0.10 <2.0 0.00501 1/22/2014 5.87 0.038 2.12 <0.50 <2.0 0.0091 7/17/2014 6.08 0.040 1.88 <0.50 <2.0 0.0088 1/13/2015 2.93 0.080 1.99 0.87 <2.0 0.0077 7/21/2015 2.05 0.066 2.89 1.2 1.6 J 0.0090 J 1/19/2016 1.49 0.34 0.964 <0.50 1.4 J 0.0027 J 7/19/2016 5.01 NA NA NA NA NA 12/28/2016 8.54 NA NA NA NA NA 8/23/2012 3.56 <0.10 0.0994 0.34 2.0 0.00427 1/22/2014 7.22 0.023 0.0086 <0.50 3.6 <0.0066 7/17/2014 4.05 <0.020 0.0091 <0.50 3.9 <0.0066 1/13/2015 3.05 0.069 <0.0050 <0.50 5.8 <0.0066 7/22/2015 5.48 0.017 J 0.0486 <0.50 3.8 0.0021 J 1/19/2016 3.39 0.053 0.0206 <0.50 7.4 0.0019 J 7/19/2016 6.10 NA NA NA NA NA 12/28/2016 8/22/2012 3.09 0.80 0.214 0.33 6.3 0.00517 1/23/2014 10.11 1.2 0.188 <0.50 5.9 <0.0066 7/17/2014 12.17 1.2 0.253 <0.50 <2.0 <0.0066 1/14/2015 5.49 1.3 0.405 1.0 <2.0 <0.0066 7/22/2015 5.70 1.1 0.444 <0.50 1.5 J <0.0100 1/20/2016 2.26 1.1 0.290 <0.50 1.5 J 0.0015 J 7/20/2016 5.40 NA NA NA NA NA 12/28/2016 4.33 NA NA NA NA NA 8/22/2012 1.31 <0.10 0.510 0.48 <2.0 0.0237 1/22/2014 1.09 0.061 0.399 <0.50 <2.0 0.512 7/17/2014 11.37 0.057 0.586 <0.50 14.4 0.288 1/14/2015 1.99 0.23 0.509 0.80 9.2 1.58 7/22/2015 1.31 0.58 0.371 <0.50 7.5 0.0020 J 1/20/2016 1.35 <0.020 0.363 <0.50 1.8 J 4.49 7/20/2016 4.52 NA NA NA NA NA 12/28/2016 2.17 NA NA NA NA NA 8/22/2012 2.30 <1.0 <0.015 <0.10 <20 0.00180 1/23/2014 4.98 <0.020 <0.0050 <0.50 5.1 <0.0066 7/17/2014 3.32 <0.020 <0.0050 <0.50 12.6 0.01470 1/14/2015 5.06 0.48 0.0203 <0.50 6.2 <0.0066 7/22/2015 2.02 <0.020 0.0199 <0.50 11.3 0.0020 J 1/20/2016 1.91 0.21 0.0165 <0.50 5.8 0.0019 J 7/20/2016 4.69 NA NA NA NA NA 12/29/2016 1.95 NA NA NA NA NA 8/23/2012 1.67 <2.5 0.0171 <0.10 <50 0.0047 1/21/2014 4.52 <0.020 0.0150 <0.50 10 0.0206 7/17/2014 7.24 <0.020 0.0071 <0.50 9.9 0.0652 1/13/2015 2.45 <0.020 <0.0050 <0.50 10.4 0.0330 7/21/2015 1.91 <0.020 0.0156 0.70 9.5 <0.0100 1/19/2016 1.41 <0.020 0.0205 <0.50 15.2 0.0352 7/19/2016 4.31 NA NA NA NA NA 12/28/2016 1.82 NA NA NA NA NA 8/23/2012 1.65 0.11 0.0532 0.52 7.6 0.00126 1/22/2014 4.77 <0.020 0.0206 0.83 8.0 <0.0066 7/17/2014 3.59 0.022 0.0161 <0.50 6.6 <0.0066 1/13/2015 3.16 0.095 0.0059 <0.50 5.9 <0.0066 7/21/2015 2.63 0.050 0.0478 <0.50 5.4 0.0015 J 1/19/2016 1.63 0.089 0.0176 <0.50 6.0 0.0017 J 7/19/2016 7.82 NA NA NA NA NA 12/28/2016 1. All concentrations are in milligrams per liter (mg/L). 2. "<" = Not detected above laboratory reporting limit. 3. Dissolved oxygen readings collected in the field with water quality equipment. 4. Values in bold indicate levels greater than the laboratory reporting limit. 5. NA = Not Analyzed. IMW-1 IMW-2 Not Sampled - Could Not Find DMW-5 Not Sampled - Could Not Find DMW-1 DMW-2 DMW-3 DMW-4 Date Cross-Sectional Area of Pipe Conversion Factor3 Days of Operation Cumulative Recovery (ft2) (lb-m3/mg-ft3)(lb/hr) (lb/day) (days) (lbs) 04/04/14* 0.08700 1,116 97.09 413 0.00000006243 0.1502 3.60 9.00 32.44 07/10/14 0.08700 1,116 97.09 6.04 0.00000006243 0.0022 0.05 97.00 37.56 10/27/14 0.08700 714 62.12 281.0 0.00000006243 0.0654 1.57 109.0 208.6 03/04/15 0.08700 719 62.55 313.0 0.00000006243 0.0733 1.760 128.0 433.9 06/18/15* 0.08700 763 66.38 26.30 0.00000006243 0.0065 0.1569 106.0 450.5 10/29/15 0.08700 603 52.46 275.0 0.00000006243 0.05404 1.2970 32.00 492.0 12/15/15 0.08700 647 56.29 476.0 0.00000006243 0.10036 2.4087 47.00 605.2 03/31/16 0.08700 588 51.16 178.8 0.00000006243 0.03426 0.8223 107.0 693.2 06/27/16 0.08700 1,269 110.4 162.7 0.00000006243 0.06728 1.615 44.00 764.3 09/29/16 0.08700 596 51.9 181.0 0.00000006243 0.03516 0.844 106.0 853.7 12/14/16 0.08700 383 33.3 199.2 0.00000006243 0.02486 0.597 76.0 899.1 03/14/17 0.08700 2,020 175.7 290.0 0.00000006243 0.19090 4.582 90.0 1,311.4 04/04/14* 0.08700 626 54.46 0.64 0.00000006243 0.0001 0.003 9.00 0.02820 07/10/14 10/27/14 0.08700 575 50.03 0.45 0.00000006243 0.0001 0.002 87.00 0.2043 03/04/15 0.08700 523 45.50 0.00 0.00000006243 0.0000 0.000 128.0 0.2043 06/18/15* 0.08700 731 63.60 0.00 0.00000006243 0.0000 0.000 106.0 0.2043 10/29/15 0.08700 528 45.94 0.00 0.00000006243 0.0000 0.000 55.00 0.2043 12/15/15 0.08700 368 32.02 0.00 0.00000006243 0.0000 0.000 47.00 0.2043 03/31/16 0.08700 645 56.12 0.00 0.00000006243 0.0000 0.000 107.0 0.2043 06/27/16 0.08700 720 62.64 0.00 0.00000006243 0.0000 0.000 54.00 0.2043 10/31/16 0.08700 523 45.50 0.00 0.00000006243 0.0000 0.000 53.00 0.2043 12/14/16 0.08700 2,832 246.38 42.4 0.00000006243 0.0391 0.939 44.00 41.5268 Notes: * Effluent velocity inferred; reading not collected 3. Conversion factor to convert units of concentration from m /m3 to lb/ft3 4. Mass removal rate = (air flow rate) x (total BTEX) x (conversion factor) x (60 min/hr or 1,440 min/day) Facility ID Number 0-004593 Incident Number 28649 Effluent Velocity (ft/min) Air Flow Rate1 (ft3/min) Total BTEX2 (mg/m3) Mass Removal Rate4 1. Air flow rate = (cross-sectional area) x (effluent velocity) 2. Total BTEX concentrations in effluent air are based on EPA Method 18 laboratory data On-Site System Off-Site System No Sample Collected; System Down Table 6 SVE System Cumulative Recovery Cajah's Mountain Superette 1990 Connelly Springs Road Lenoir, North Carolina FIGURES SITE PR O J E C T N O . NO T E S : DA T E TI T L E SC A L E RE V . B Y PR E P . B Y CA D F I L E DC S A I D SITE HAMBY/CAJAH'SMT PARK TRIPLETT HAMBY/CAJAH' MT PARK WILLIAMS/BRANDON APARTMENTS PRICE CHURCH SHELL CHURCH PR O J E C T N O . NO T E S : DA T E TI T L E SC A L E RE V . B Y PR E P . B Y CA D F I L E PW-21 PW-20 PW-22 PW-8 PR O J E C T N O . NO T E S : DA T E TI T L E SC A L E RE V . B Y PR E P . B Y CA D F I L E PR O J E C T N O . NO T E S : DA T E TI T L E SC A L E RE V . B Y PR E P . B Y CA D F I L E APPENDIX A LABORATORY ANALYTICAL REPORT CORRECTIVE ACTION PERFORMANCE REPORT Cajah’s Mountain Superette 1990 Connelly Springs Road Lenoir, Caldwell County, North Carolina 28645 Facility ID No. 0-004593 NCDEQ Incident No. 28649 Risk Classification: High (H190D) ATC Project No. CARCAJA December 18, 2017 7606 Whitehall Executive Center Drive, Suite 800 Charlotte, NC 28273 Tel: 704-529-3200 Fax: 704-529-3272 www.atcgroupservices.com N.C. Engineering License No. C-1598 December 18, 2017 Mr. Dan Murphy North Carolina Department of Environmental Quality Asheville Regional Office Division of Waste Management - UST Section 2090 US Highway 70 Swannanoa, North Carolina 28778 RE: Corrective Action Performance Report Cajah’s Mountain Superette 1990 Connelly Springs Road Lenoir, Caldwell County, North Carolina 28645 Facility ID No. 0-004593 NCDEQ Incident No. 28649 Risk Classification: High (H190D) ATC Project No. CARCAJA Dear Mr. Murphy: ATC Associates of North Carolina, P.C., on behalf of Cary Oil Company, is submitting the enclosed Corrective Action Performance Report for the Cajah’s Mountain Superette site. This report includes information pertaining to the operation and maintenance of the air sparge and soil vapor extraction systems from May through July 2017. If you have any questions or require additional information, please contact us at (704) 529-3200. Sincerely, ATC Associates of North Carolina, P.C. Christine E. Schaefer Project Manager cc: Mr. Glenn Petti – Cary Oil Company Site Identification: Date of Report: 12/18/2017 Site Risk: High (H190D) Facility I.D.: 0-004593 UST Incident Number (if known): 28649 Site Name: Cajah’s Mountain Superette Street Address: 1990 Connelly Springs Road City/Town: Lenoir Zip Code: 28645 County: Caldwell Description of Geographical Data Point (e.g., diesel fill port): Former Tank Basin Location Method (GPS, topographical map, other): Google Earth Latitude (decimal degrees): 35. 83749120° N Longitude (decimal degrees): 81. 5387323° W Information about Contacts Associated with the Leaking UST System: UST Owner: Cary Oil Company Address: 110 Mackenan Drive, Suite 300, Cary, NC 27511 Phone: (919) 462-1100 Property Owner: Mary Lindsay Address: 127 Dell Circle, Hudson, NC 28638 Phone: (828) 728-2674 Consultant/Contractor: ATC Associates of North Carolina, P.C. Address: 7606 Whitehall Executive Center Dr., Charlotte, NC 28273 Phone: (704) 529-3200 Analytical Laboratory: Prism Laboratories, Inc. State Certification No.: 402 Address: 449 Springbrook Road, Charlotte, NC 28224 Phone: (704) 529-6364 Information about Release: Date Discovered: August 28, 2008 Estimated Quantity of Release: Unknown Cause of Release: Unknown Source of Release (Dispenser/Piping/UST): Unknown Sizes and contents of UST system(s) from which the release occurred: Two 8,000-gallon gasoline USTs and one 4,000-gallon gasoline UST and associated dispensers TABLE OF CONTENTS 1.0 EXECUTIVE SUMMARY ............................................................................................................ 1  2.0 SUPPORTING INFORMATION AND CAP IMPLEMENTATION ......................................... 2  3.0 GROUNDWATER REMEDIATION ............................................................................................ 4  3.1 Background ..................................................................................................................... 4  3.2 System Operation and Maintenance, May-July 2017 ................................................... 5  4.0 CONCLUSIONS AND RECOMMENDATIONS ......................................................................... 7  5.0 REPORT LIMITATIONS .............................................................................................................. 7  TABLES Table 1 Site History Table 2 Public and Private Water Supply Well and Other Receptor Information Table 3 Historical Groundwater Sampling Results Table 4 Free Product Recovery Information Table 5 Monitored Natural Attenuation Parameters Table 6 SVE System Cumulative Recovery FIGURES Figure 1 Site Topographic Map Figure 2 Site Map Figure 3 Site Vicinity Map Figure 4 Remedial System Design APPENDICES Appendix A Laboratory Analytical Report Cajah’s Mountain Superette December 18, 2017 Corrective Action Performance Report Page 1 1.0 EXECUTIVE SUMMARY Cary Oil Company (Cary Oil) retained ATC Associates of North Carolina, P.C. (ATC) to prepare a Corrective Action Performance Report for the project site located at 1990 Connelly Springs Road in Lenoir, Caldwell County, North Carolina. Figure 1 shows the site and vicinity on part of a United States Geological Survey (USGS) site topographic map. A map showing site details is provided as Figure 2. This report documents three months of remedial system operation and maintenance. Groundwater impact at the site has historically been identified at concentrations exceeding Gross Contamination Levels (GCLs). Generally decreasing trends have been observed over time. However, according to groundwater analytical results obtained from a monitoring event performed in December 2016, contaminant concentrations increased, and benzene was reported in well MW-8 at a concentration above the GCL. The remedial systems were not operational during the December 2016 groundwater monitoring event and that may be the reason for observed increased dissolved impact. The remedial systems were restarted on July 10, 2017, and a subsequent groundwater monitoring event conducted on July 18 and 19, 2017, indicated stabilized or reduced contaminant concentrations. Petroleum hydrocarbons were detected above the associated 15A NCAC 2L .0202 Standards (2L Standards) in eight of the 11 sampled site monitoring wells in July 2017. Historical groundwater sampling results are provided in Table 3. Free product has historically been identified in site well MW-8 at a maximum thickness of 2.97 feet. Free product was not identified in site monitoring wells in July 2017. As outlined in the October 31, 2012, Corrective Action Plan (CAP), high vacuum extraction through the implementation of Aggressive Fluid/Vapor Recovery (AFVR) technology appeared to be the most feasible and cost effective option for recovering remaining free product from on-site well MW-8. AFVR events were conducted between March 2012 and December 2013 and recovered approximately 44 gallons of liquid phase product, 54.17 gallons of vaporized product, and 1,870 gallons of petroleum-contact water from well MW-8. Historical free product recovery information is summarized in Table 4. Adsorbent socks were installed and changed as necessary in well MW-8 beginning in February 2015 to recover remaining free product. The socks were removed in early July 2015, and the well has not indicated free product during subsequent groundwater monitoring events. Natural attenuation was determined in the CAP to be the most feasible and cost effective remedial option for reducing groundwater contaminant concentrations in the intermediate and deep aquifer zones. Historical Cajah’s Mountain Superette December 18, 2017 Corrective Action Performance Report Page 2 natural attenuation sampling indicates an environment conducive to potential bioremediation in the intermediate and deep aquifer zones. Generally, measured dissolved oxygen concentrations are consistently above anoxic and hypoxic conditions, indicating a potential for aerobic activity. Dissolved oxygen concentrations in wells IMW-1 and DMW-1 tend to be particularly high. Natural attenuation parameters are presented in Table 5. Petroleum compound concentrations had generally shown an increasing trend in downgradient, intermediate well IMW-1, until January 2016 when concentrations began decreasing. Some contaminant concentration rebounding was observed in well IMW-1 in December 2016, but the increases may have been due to off-site system downtime. The system was restarted on July 10, 2017, and a monitoring event conducted on July 18 and 19, 2017, generally indicated stabilized impact concentrations. Impact in this well will continue to be monitored and remedial system adjustments should be made as deemed necessary. Impact in on-site, deep well DMW-1 is generally decreasing with time. Contaminants of concern in other intermediate and deep wells remain minimal. The CAP identified air sparge/soil vapor extraction (AS/SVE) as the chosen corrective action technologies for shallow petroleum-impacted groundwater at the site. Air sparge and soil vapor extraction wells were installed at the site on December 30, 2013, through January 15, 2014. The on-site and off-site system installations were completed on January 13, 2014, through January 24, 2014. System startup activities were conducted on March 26, 2014. However, due to noise concerns, the off-site system was turned off until April 9, 2014, when the telemetry was programmed to operate the system from 8:00 am to 8:00 pm. Based on impact to vicinity water supply wells and historical free product and groundwater impact in site monitoring wells, the risk classification for the site has been designated as “High” and ranked H190D by the North Carolina Department of Environmental Quality (NCDEQ). Therefore, groundwater contamination must be remediated to concentrations which are equal to or less than the associated 2L Standards. 2.0 SUPPORTING INFORMATION AND CAP IMPLEMENTATION An underground storage tank (UST) system consisting of three tanks was formerly located on-site and was operated by Cary Oil from April 2005 until August 2008 when the UST system was removed. During UST removals, soil impact was identified and led to assessment requests from the North Carolina Department of Environment and Natural Resources (NCDENR; currently the NCDEQ). Cajah’s Mountain Superette December 18, 2017 Corrective Action Performance Report Page 3 The subject property is owned by Mary Lindsay and has one building that currently operates as a catering business known as Mooresridge Catering. The site formerly operated as a convenience store which included a UST system consisting of two 8,000-gallon gasoline USTs and one 4,000-gallon gasoline UST. Site history including on-site UST system information is summarized in Table 1. A site plan that indicates monitoring well locations and other site features is provided as Figure 2. The perennial surface water body identified in the closest proximity to the site is Stafford Creek located approximately 2,000 feet to the southwest of the site. A branch of Little Gunpowder Creek lies approximately 2,500 feet to the east of the site. The Caldwell County Geographic Information System database identified surface water bodies towards the east and west at distances of 700 and 500 feet from the site, respectively; however, these surface water bodies were not identified during field activities. Surface cover at the site consists mostly of asphalt on the east side of the property and grass and gravel on the west side of the property. The site lies in the Inner Piedmont in an area characterized by inter-fingered biotite gneiss, biotite schist, and mica schist with some other minor rock types that are heavily metamorphosed and structurally complex. The shallow subsurface contains overburden of soil, saprolite, and partially weathered rock (PWR) that derive from in-place weathering. Findings from the Comprehensive Site Assessment (CSA) suggest that most of the unconsolidated subsurface materials exhibit high permeability for the Piedmont and probably can best be described as saprolite or PWR. During assessment activities, rock was encountered at decreasing depths with distance from the site towards the east, with depths ranging from 85 feet below ground surface (bgs) at on-site well DMW-3 to 20 feet bgs at downgradient well MW-21. Depth to groundwater in the site monitoring wells ranged from approximately 23 to 35 feet below top of casing (TOC) during the July 2017 groundwater sampling event. Based on the recent groundwater level measurements and calculation of groundwater elevations, groundwater flows generally towards the southeast across the site. Baton Water Corporation and the Town of Lenoir supply public water in the site vicinity. Twenty-one (21) private water supply wells have been identified within approximately 1,500 feet of the site. Water supply well information for the area is summarized in Table 2, and supply well locations relative to the source area are depicted on Figure 3. Between 2008 and 2012, site assessment, AFVR events for free product recovery, and a CAP with pilot Cajah’s Mountain Superette December 18, 2017 Corrective Action Performance Report Page 4 testing were conducted related to the Cajah’s Mountain Superette release. Free product recovery efforts in the form of AFVR events, conducted between 2012 and 2013 recovered approximately 44 gallons of liquid phase product, 54.17 gallons of vaporized product, and 1,870 gallons of petroleum-contact water from well MW-8. Historical free product recovery information is summarized in Table 4. Adsorbent socks were installed and changed as necessary in well MW-8 between February 2015 and July 2015, and the well has not indicated free product during subsequent groundwater monitoring events. Based on results of the CAP and pilot testing, ATC found that AS and SVE technologies appeared to be the most feasible and cost effective remedial options for reducing groundwater contaminant concentrations in the shallow aquifer, and monitored natural attenuation was chosen for groundwater in the intermediate and deep zones. The AS/SVE wells were installed from December 30, 2013, to January 15, 2014. Depths of the air sparge wells ranged from 50 feet to 95 feet bgs, depending on zones of groundwater impact and depth of bedrock. Wells SVE-2 through SVE-7 and SVE-10 through SVE-14 were installed to depths of 34 feet or 35 feet bgs, depending on vicinity groundwater levels. Wells SVE-8 and SVE-9 were installed to depths of 26 feet bgs due to the elevated water table encountered behind the on-site building. Vapor extraction well SVE-1 was installed to a depth of 35 feet bgs on August 22, 2012, for the pilot study. The systems were installed during the period of December 2013 through January 2014. The on-site and off- site air sparge systems consist of six and eight air sparge wells, respectively, rotary claw air compressors, and schedule 80 PVC piping for transferring compressed air from the remediation systems to the air sparge wells. The on-site and off-site vapor extraction systems consist of nine and five vapor extraction wells, respectively, regenerative vacuum blowers, condensate collection vessels, and schedule 40 PVC piping for transferring extracted vapors from the vapor extraction wells to the remediation systems. A system design drawing is included as Figure 4. 3.0 GROUNDWATER REMEDIATION 3.1 Background System startup activities were conducted on March 26, 2014. However, due to noise concerns, the off-site system was turned off until April 9, 2014, when the telemetry could be programmed to operate the system from 8:00 am to 8:00 pm. Efforts have been made to reduce excessive noise that originates from the building but minimal reductions have been observed. Cajah’s Mountain Superette December 18, 2017 Corrective Action Performance Report Page 5 Air sparge wells AS-1 through AS-3 were left off, by means of closed system manifold valves, until free product was sufficiently recovered from the area. Following a reduction in measurable product at the site, sparge wells AS-1 through AS-3 were started in October 2015. Off-site wells AS-10 and AS-11 were shut down on April 13, 2016, and wells AS-9 and AS-12 were shut down on April 28, 2016, to provide more sparge pressure to the west side of the off-site property where higher dissolved contaminant concentrations exist. On-site system downtime has historically often been attributable to high temperature alarms which shut the system down during summer months, and power losses following storms. Off-site system downtime in 2014 occurred due to bad motor windings on the SVE blower which shut the system down. The off-site SVE blower was replaced under warranty by the system fabricator on October 15, 2014. Electrical issues (power outages, phase losses, and an indicated electrical fault) occurred at both the on-site and off-site systems in 2015. The systems were ultimately shut down manually by ATC as a safety precaution. The issue was identified to be melted high voltage fuses in each system which led the systems to run on one phase and then shut down. A small fire at the on-site catering business building occurred in August 2015, which Duke Energy attributed to insufficiently sized wires for the load. The wires were subsequently changed by Duke Energy. The combined issues are potentially related to a general electrical issue in the area, possibly caused by recent electrical storms. High voltage fuses on the on-site and off-site SVE blowers were replaced in October 2015 and the systems were re-started. Due to frequent shutdowns, the off-site SVE blower vacuum was reduced in 2016 as it was determined the operating capacity of the unit could not be fully achieved in the actual operating conditions. That is to say, the potential capacity of the blower is assumed under ideal conditions which are rarely achieved in an environmental, non-climate controlled setting. 3.2 System Operation and Maintenance, May-July 2017 System operation and maintenance was conducted twice per month from May to July 2017 to check system components and perform routine maintenance. Efforts are made to combine site visits with visits conducted at another Cary Oil site in the vicinity, Tilley’s Superette. On-site system run-time was approximately 89% from May to July 2017. System downtime was due to a phase fault from storms in the area during the Cajah’s Mountain Superette December 18, 2017 Corrective Action Performance Report Page 6 reporting period. Vacuum readings for each well point at the on-site SVE manifold were set at approximately 38 inches of water. Pressure readings for each well point at the on-site AS manifold were set at approximately 10 pounds per square inch (psi). The off-site system was not operational from December 2016 to July 10, 2017, due to a power fault which resulted in burned SVE motor wires. Additionally, a local motor repair shop assessed the blower motor and identified the following: one endbell needed to be bushed and the motor needed new bearings, lip seal, and filter media. Repairs were completed in June 2017 and the blower was re- installed at the site. Upon off-site system restart, a grinding noise was heard at the SVE blower. The motor repair shop assessed the problem and shaved the fan blades to prevent them from rubbing together. The system was fully restarted on July 10, 2017. During off-site system operation in July 2017, vacuum readings for each well point were set at approximately 22 inches of water. Pressure readings for each well point at the off-site AS manifold were set at approximately six psi. Off-site wells AS-9, AS-10, and AS-11 were left off to provide more sparge pressure near well IMW-1 and to the west side of the off-site property where higher dissolved contaminant concentrations exist. SVE influent air samples are collected on a quarterly basis during system operation to identify the efficiency of the SVE systems and assist with system optimization efforts. An SVE influent air sample was collected from the on-site system on June 20, 2017, and was submitted to Prism Laboratories, Inc. for analysis by EPA Method 18. The laboratory analytical report is provided in Appendix A. A sample was not collected from the off-site system following the July 2017 restart. Table 6 shows SVE cumulative recovery calculations based on system influent sampling data. Based on laboratory analytical results from quarterly influent air sampling, approximately 1,466 and 41.53 pounds of total BTEX have been recovered by the on-site and off-site SVE systems, respectively, since startup. The on-site and off-site system influent total BTEX concentrations upon initial startup and sampling in April 2014 were 413 mg/m3 and 0.64 mg/m3, respectively. The influent total BTEX concentrations during the most recent sampling were 208 mg/m3 and 42.4 mg/m3 for the on-site and off-site systems. Free product has historically been identified in on-site well MW-8 at a maximum thickness of 2.97 feet. Following multiple AFVR events and adsorbent sock changeouts, the well has not indicated free product since 2015. Groundwater contamination above NCDEQ 2L Standards is generally located in front of the on-site building in the vicinity of the former UST system and migrates downgradient to the east-southeast across Connelly Springs Road towards well IMW-1. Contaminant concentrations in the source area and downgradient generally indicate a decreasing trend with time. Cajah’s Mountain Superette December 18, 2017 Corrective Action Performance Report Page 7 4.0 CONCLUSIONS AND RECOMMENDATIONS The AS/SVE systems were started at the site in March and April 2014, and dissolved contaminant concentrations generally indicate a decreasing trend since system startup. Groundwater contaminant increases are generally observed during system downtime. Free product was not observed in gauged wells in July 2017. Impact concentrations in intermediate and deep wells appear generally stable or are decreasing. ATC recommends continued AS/SVE system operation and maintenance (O&M) visits and site groundwater monitoring at the Cajah’s Mountain Superette site. System O&M visits should continue to be conducted twice per month and continued efforts to optimize system efficacy should be implemented. Quarterly SVE effluent air sampling is recommended during scheduled O&M visits. ATC recommends groundwater monitoring events be conducted on a semi-annual basis during winter and summer months. 5.0 REPORT LIMITATIONS This investigation is intended to be a non-biased assessment of on-site environmental conditions proximate to the location of the former and/or current UST system. Subsurface investigative and remedial methodologies were performed in general accordance with applicable state and federal regulatory requirements. The information presented in this report is based upon site-specific observations, generally accepted geological and environmental consulting practices, and analytical results for environmental samples collected at the time of the field investigation was performed. The data presented in this report are believed to represent subsurface conditions at the facility; however, data may not be completely representative of subsurface conditions at every location. ATC assumes no liability arising from environmental impact to, or from, the site, regardless of the date of impact occurrence or findings. TABLES Table 1 Site History Cajah's Mountain Superette 1990 Connelly Springs Road Lenoir, North Carolina Facility ID Number 0-004593 Incident Number: 28649 Zip Telephone Number 27511 (919) 462-3194 Zip Telephone Number 27511 (919) 462-3194 1 Gasoline None 4,000 Fiberglass 24' x 64" Fiberglass Reinforced Plastic Early 1980s Removed 8/14/08 Yes 2 Gasoline None 8,000 Fiberglass 8' x 21.4" Fiberglass Reinforced Plastic Early 1980s Removed 8/14/08 Yes 3 Gasoline None 8,000 Fiberglass 8' x 21.4" Fiberglass Reinforced Plastic Early 1980s Removed 8/14/08 Yes UST ID Number Current/Last Contents Previous Contents Capacity (gallons) Release confirmed during 8/14/08 excavation Tank Dimensions Description of Associated Piping and Pumps Date Tank Installed Status of Tank Was Release Associated With UST System? Date of Release Description of Release 28649 Gasoline 8/14/08 Incident Number Material Released Construction Details 0-004593 Name of Owner Dates of Ownership (m/dd/yy) to (m/dd/yy) UST ID Number(s) Facility ID Number 4/2005 to 8/14/2008 Name of Operator Street Address Dates of Operation (m/dd/yy) to (m/dd/yy) Cary Oil Company Cary NC 110 Mackenan Drive, Suite 300 City State UST ID Number(s) Facility ID Number 1, 2, and 3 0-004593 Street Address 110 Mackenan Drive, Suite 300 Cary Oil Company City State Cary NC 4/2005 to 8/14/2008 1, 2, and 3 Table 2 Public and Private Water Supply Well and Other Receptor Information Cajah's Mountain Superette 1990 Connelly Springs Road Lenoir, North Carolina Facility ID Number 0-004593 Incident Number: 28649 PW-1 Jimmie & Louise Beane / 1511 Bradshaw Terrace, Lenoir, NC 28645 1511 Bradshaw Terrace Lenoir 828-728-9368 Not in use Unknown Unknown 400 Downgradient Well not operational and property provided municipal water by Baton Water Corporation PW-2 CitiMortgage, Inc. / 1000 Technology Drive, O'Fallon, MO 63368 1433 Brandon Road Lenoir NA In use for potable water by next- door Price & Shell Unknown Unknown 450 Downgradient Well services more than one residence (Price & Shell) PW-3 Henry & Linda Johnson / 1535 Bradshaw Terrace, Lenoir, NC 28645 1535 Bradshaw Terrace Lenoir 828-728-5256 Not in use Unknown Unknown 775 Downgradient Not accessible - According to Mr. Johnson, well has been filled over the years with sticks and rocks, and water is not accessible PW-4 Clifford & Jeanie Stewart / 319 Welcome Ave., Greenville, SC 29611 1554 Bradshaw Terrace Lenoir NA Not in use Unknown Unknown 1,100 Downgradient PW-5 Poarch Dixie Land Tate Azor / 1490 Land Street, Lenoir, NC 28645 1497 Land Street Lenoir NA Not in use Approx. 40-45' Unknown 1,000 Sidegradient PW-6 Ryan & Shirley Rozzelle / 186 Mountain Oak Lane, Hickory, NC 28601 1418 Brandon Road Lenoir 828-495-3456 Unknown Unknown Unknown 850 Sidegradient Current well use unknown; Property provided municipal water by Baton Water Corporation PW-7 Helen Sullivan / 904 Second St. NE, Apt. 234, Hickory, NC 28601 Justin Lane (No address number) Lenoir 828-728-2757 Not in use Unknown Unknown 1,200 Sidegradient Well operational but not in use and property provided municipal water by Baton Water Corporation PW-8 Brandon Apartments (Keith and Patricia Williams) / 1415 N. Catwaba Church Avenue, Lenoir, NC 28645 3715 Panda Lane Lenoir 828-728-9167 Not in use Unknown Unknown 1,000 Downgradient Well not operational and property provided municipal water by Baton Water Corporation PW-9 Randy & Joyce Kestner / 4593 Horseshoe Bend Road, Hudson, NC 28638 3725 Happy Horse Lane Lenoir NA In use for potable water Unknown Unknown 1,100 Downgradient PW-10 Berry Kaylor / 3965 Greenwood Drive, Lenoir, NC 28645 3965 Greenwood Drive Lenoir 828-728-6946 Not in use Unknown Unknown 1,475 Sidegradient PW-11 Sherri Barnwell / 1499 Union Grove Road, Lenoir, NC 28645 1499 Union Grove Road Lenoir 828-728-3412 Not in use Unknown Unknown 1,300 Sidegradient Well not operational and property provided municipal water by Baton Water Corporation PW-12 Roger & Penny Triplett / 1740 Taylorsville Road SE, Lenoir, NC 28645 1512 Union Grove Road Lenoir NA Not in use Unknown Unknown 1,100 Sidegradient Property provided municipal water by Baton Water Corporation PW-13 William Rudicil / 1520 Union Grove Road, Lenoir, NC 28645 1520 Union Grove Road Lenoir NA Not in use Unknown Unknown 1,190 Sidegradient Property provided municipal water by Baton Water Corporation PW-14 Karen Sanders / 1522 Union Grove Road, Lenoir, NC 28645 1522 Union Grove Road Lenoir 828-726-1420 Not in use Unknown Unknown 1,210 Sidegradient PW-15 Arnold & Wanda Correll / 1528 Bradshaw Terrace, Lenoir, NC 28645 1528 Bradshaw Terrace Lenoir 828-728-7497 In use for outdoor/irrigation water Approx. 90 Unknown 525 Downgradient Well depth estimated by Mr. Correll; Property provided municipal water by Baton Water Corporation; Well only supplies water to outside spigots; Well not operational during winter PW-16 Theohary & Linda Smargian / PO Box 967, Hudson, NC 28638 1518 Bradshaw Terrace Lenoir NA Not in use Approx. 176* Unknown 400 Downgradient Well not operational and property provided municipal water by Baton Water Corporation PW-17 Douglas & Katherine Hawkins / 1980 Connelly Springs Road, Lenoir, NC 28645 1980 Connelly Springs Road Lenoir NA Not in use Unknown Unknown 150 Sidegradient Well installed in 1961; Mary Lindsay (subject property owner) is POA; well is beneath house and not accessible PW-18 Jimmie & Louise Beane** / 1511 Bradshaw Terrace, Lenoir, NC 28645 1514 Bradshaw Terrace Lenoir NA Not in use Unknown Unknown 240 Downgradient Well not operational and property provided municipal water by Baton Water Corporation PW-20 Cajah's Mt Park LLC (Steve Hamby) / PO Box 1114, Hudson, NC 28638 0 Connellly Springs Road (Cajah's Mountain Mobile Home Park)Lenoir NA Not In use Unknown Unknown 325 Sidegradient No access to well, well reportedly not operational, and property provided municipal water by Baton Water Corporation PW-21 Paula Fetherbay c/o Paula St. Clair / 1975 Connelly Springs Road, Lenoir, NC 28645 1975 Connelly Springs Road Lenoir NA In use for potable water Unknown Unknown 375 Sidegradient PW-22 Daniel Ace / 3733 Happy Horse Lane, Lenoir, NC 28645 3733 Happy Horse Lane Lenoir NA Reportedly, in use for potable water Unknown Unknown 1,100 Downgradient N/A East N/A N/A Surface water 700 Downgradient Stream was not identified on USGS topographic map, but was depicted on Caldwell County Geographic Information website, and could not be located during field activities. N/A West N/A N/A Surface water 500 Downgradient Stream was not identified on USGS topographic map, but was depicted on Caldwell County Geographic Information website. * On 7/26/10, due to difficulty encountered gauging depth of the two foot diameter well with an o/w interface meter, it was estimated that depth of PW-16 was approximately 176 ft bgs, as the meter appeared to reach bottom at that depth. ** residential property is currently leased; The Beanes are the owner for the residential property NA = Not Available Potable Well ID Well Depth (ft bgs) Receptor ID Location Contact Property Owner Contact Information Property Address City Phone Number Well Screen Interval (ft) Well Use Comment Approx. distance from source area of release (ft) Up/Down/ or Crossgradient* Approx. distance from source area of release (ft) Up/Down/Crossgradient/Ot her Comment Unnamed intermittent stream Unnamed intermittent stream Description Phone Number Usage Historical Groundwater Sampling Results Cajah's Mountain Superette 1990 Connelly Springs Road Lenoir, North Carolina Facility ID Number 0-004593 Incident Number: 28649 C5-C8 Aliphatics Carbon Fraction Clas C9-C18 Aliphatics Carbon Fraction Clas C9-C22 Aromatics Carbon Fraction Clas C 5 - C 8 C9 - C 1 2 C 9 - C 1 0 1 , 2 , 4 - T r i m e t h y l b e n z e n e 1 , 3 , 5 - T r i m e t h y l b e n z e n e B r o m o d i c h l o r o m e t h a n e B r o m o f o r m C h l o r o f o r m C h l o r o m e t h a n e D i b r o m o c h l o r o m e t h a n e D i b r o m o m e t h a n e E t h y l e n e D i b r o m i d e ( E D B ) I s o p r o p y l E t h e r I s o p r o p y l b e n z e n e M e t h y l t e r t b u t y l e t h e r ( M T B E ) n - B u t y l b e n z e n e n - P r o p y l b e n z e n e 1 , 2 , - D i c h l o r o e t h a n e T r i c h l o r o e t h y l e n e ( T C E ) T e t r a c h l o r o e t h y l e n e ( P C E ) p - I s o p r o p y l t o l u e n e s e c - B u t y l b e n z e n e S t y r e n e N a p h t h a l e n e B e n z e n e T o l u e n e E t h y l b e n z e n e T o t a l X y l e n e s T o t a l B T E X E t h y l e n e D i b r o m i d e ( E D B ) L e a d 12/10/2008 180 1.6 42 3.1 1.6 0.65 <0.1 11 3.3 <0.1 <0.1 *<0.022 0.24 0.34 65 0.4 0.63 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 10 2.5 1.2 3.3 17.0 <0.022 110 11/17/2009 1,300 35 61 2.9 2.1 <0.1 <0.1 13 <0.1 <0.1 <0.1 *<0.022 <0.1 0.46 18 0.7 0.83 <0.2 <0.1 <0.2 0.53 <0.1 <0.1 <0.1 17 5.1 0.75 9.5 32.4 <0.022 149 2/3/2012 1,180 488 137 19.1 7.6 <0.50 <0.50 5.2 <1.0 <0.50 <0.50 *<0.020 <0.50 2.2 3.7 1.6 5.2 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 6.1 26.6 18.1 6.9 41.0 92.6 <0.020 36.6 8/22/2012 1,570 125 135 3.4 5.4 <0.12 <0.12 7.0 <0.20 <0.10 NA *0.020 0.22 J 3.5 6.1 1.4 6.4 <0.16 <0.18 <0.14 0.50 1.5 <0.10 <0.10 49.2 13.9 2.5 26.8 92.4 0.020 20.0 1/23/2014 549 <50.0 <50.0 1.5 1.7 <0.50 <0.50 8.1 <1.0 <0.50 <0.50 *<0.020 <0.50 1.1 0.75 0.53 0.96 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 11.4 0.54 <0.50 5.3 17.2 <0.020 10.0 7/18/2014 785 542 117 16.3 8.8 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 0.62 5.5 5.0 2.9 6.0 <0.50 <0.50 <0.50 NA 2.4 <0.50 <2.0 37.4 4.7 2.8 44.0 88.9 <0.020 47.0 1/14/2015 163 131 <50.0 <0.50 0.57 <0.50 <0.50 9.4 <1.0 <0.50 <0.50 *<0.020 <0.50 1.1 0.77 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 0.53 <0.50 <2.0 8.2 <0.50 <0.50 3.6 11.8 <0.020 37.4 7/22/2015 NA NA NA 0.98 1.40 <0.50 <0.50 8.5 <1.0 <0.50 <0.50 *<0.020 <0.50 0.93 0.81 <0.50 0.45 J <0.50 <0.50 <0.50 NA 0.49 J <0.50 <2.0 6.9 <0.50 <0.50 3.9 10.8 <0.020 6.8 1/20/2016 NA NA NA <0.50 <0.50 0.27 J <0.50 14.8 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 43.4 7/20/2016 NA NA NA 1.9 3.7 <0.50 <0.50 4.4 <1.0 <0.50 <0.50 <0.50 <0.50 0.78 5.8 <0.50 0.42 J <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 8.1 14.1 9.0 28.2 59.4 NA 20.5 12/29/2016 NA NA NA 19.1 4.0 <0.50 <0.50 3.5 <1.0 <0.50 <0.50 <0.50 <0.50 2.4 3.0 <0.50 1.6 <0.50 <0.50 <0.50 NA 0.25 J 0.44 J <2.0 12.9 11.8 33.9 204.8 263.4 NA 22.2 7/19/2017 NA NA NA 0.69 0.51 <0.50 <0.50 9.3 <0.50 <0.50 <0.50 <0.50 <0.50 0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 0.46 J 0.61 <0.50 <0.50 8.9 9.51 NA 49 3/13/2009 605 540 <100 29.3 10.7 1.8 <0.1 16.2 <1.0 <0.1 <0.1 *<0.02 2.8 1.7 72.1 1.1 3.7 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 151 80.8 11.6 116.1 360 <0.02 22.7 11/17/2009 2,600 460 660 110 38 <0.1 <0.1 16 <0.1 <0.1 <0.1 *<0.023 <0.1 3.9 340 <0.1 6.3 0.74 <0.1 <0.2 3.2 <0.1 <0.1 3.8 630 170 16 320 1,136 <0.023 22.4 2/3/2012 1,980 1,450 213 79.1 28.3 0.74 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 6.1 5.7 135 <0.50 10.9 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 3.7 336 79.3 32.7 233 681 <0.020 31.5 8/22/2012 3,660 1,180 1,180 126 53.2 <2.3 <2.4 14.1 <3.9 <2.0 NA *0.042 15.3 4.4 J 389 <2.0 7.4 J <3.3 <3.6 <2.7 <2.0 <2.0 <2.0 7.2 J 939 89.7 18.3 447 1,494 0.042 29.4 1/24/2014 2,020 445 <250 52.0 18.9 <1.0 <1.0 <1.0 <2.0 <1.0 <1.0 *<0.020 8.1 1.6 222 <1.0 1.3 <1.0 <1.0 <1.0 NA <1.0 <1.0 5.9 272 20.7 2.5 135.3 430.5 <0.020 <5.0 7/17/2014 2,350 696 <250 19.7 23.1 <1.2 <1.2 <1.2 <2.5 <1.2 <1.2 *<0.020 17.3 2.8 444 <1.2 2.2 <1.2 <1.2 <1.2 NA <1.2 <1.2 14.2 499 19.7 5.1 187.4 711.2 <0.020 11.7 1/14/2015 613 345 94.2 <2.5 16.8 <2.5 <2.5 5.7 <5.0 <2.5 <2.5 *<0.020 10.0 <2.5 274 <2.5 <2.5 <2.5 <2.5 <2.5 <2.5 <2.5 <2.5 14.1 345 10.9 3.9 68.9 428.7 <0.020 15.8 7/22/2015 NA NA NA 3.3 2.1 <1.2 <1.2 3.4 <2.5 <1.2 <1.2 *<0.020 7.1 1.4 197 <1.2 0.74 J 0.73 J <1.2 <1.2 NA <1.2 <1.2 7.1 143 2.4 1.4 12.8 159.6 <0.020 8.9 1/20/2016 NA NA NA 0.88 0.35 J <0.50 <0.50 2.7 <1.0 <0.50 <0.50 <0.50 0.62 0.58 12.6 <0.50 <0.50 <0.50 <0.50 <0.50 NA 0.26 J <0.50 <2.0 16.1 <0.50 <0.50 2.6 18.7 NA 61.8 7/20/2016 NA NA NA 0.34 J <0.50 <0.50 <0.50 5.1 <1.0 <0.50 <0.50 <0.50 <0.50 0.46 J 4.4 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 6.9 <0.50 <0.50 1.35 J 8.25 J NA 37.1 12/28/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 2.1 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 3.2 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 15.6 7/19/2017 NA NA NA <0.50 <0.50 <0.50 <0.50 6.2 <0.5 <0.50 <0.50 <0.50 <0.50 <0.50 2.0 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.5 3.8 <0.50 <0.50 0.46 J 4.26 NA 130 3/13/2009 <100 <100 <100 <0.50 <0.50 <0.50 <0.1 0.68 <1.0 <0.1 <0.1 *<0.02 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 ND <0.02 19.5 11/17/2009 <30 <10 <35 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 *<0.022 <0.1 <0.1 <0.2 <0.1 <0.1 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.1 ND <0.022 165 2/3/2012 <50.0 <50.0 <50.0 <0.50 <0.50 2.5 <0.50 11.9 <1.0 0.71 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 161 8/23/2012 <35 <35 <35 <0.10 <0.10 2.3 0.12 17.1 <0.20 0.27 J NA *<0.0091 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0091 100 1/23/2014 <50.0 <50.0 <50.0 <0.50 <0.50 1.4 <0.50 18.2 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 148 7/18/2014 <50.0 <50.0 <50.0 <0.50 <0.50 2.1 <0.50 22.7 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 174 1/14/2015 <50.0 <50.0 <50.0 <0.50 <0.50 1.5 <0.50 22.6 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 108 7/22/2015 NA NA NA <0.50 <0.50 0.97 <0.50 17.5 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 51.9 3/13/2009 <100 <100 <100 <0.50 <0.50 <0.50 <0.1 <0.50 <1.0 <0.1 <0.1 *<0.02 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 0.60 <0.50 <0.50 0.6 <0.02 25.9 11/17/2009 <30 <10 <35 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 *<0.022 <0.1 <0.1 <0.2 <0.1 <0.1 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 <0.1 0.5 <0.2 0.41 1.0 <0.022 185 2/3/2012 <50.0 <50.0 <50.0 <0.50 <0.50 1.2 <0.50 6.0 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 61.9 8/22/2012 94.8 J <35 <35 <0.10 <0.10 1.7 <0.12 8.5 <0.20 0.36 J NA *<0.0097 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0097 47.9 1/23/2014 <50.0 <50.0 <50.0 <0.50 <0.50 0.58 <0.50 11.6 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 31.4 7/18/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 17.7 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 17.5 1/14/2015 <50.0 <50.0 <50.0 <0.50 <0.50 0.59 <0.50 14.8 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 13.2 7/22/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 7.7 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 26.7 11/17/2009 800 50 130 12 3.7 <0.1 <0.1 7.7 <0.1 <0.1 <0.1 *<0.022 <0.1 0.87 1.7 <0.1 1.4 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 1.1 35 88 9.9 61 193.9 <0.022 <10 2/3/2012 156 155 <50.0 4.7 1.0 <0.50 <0.50 1.4 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 4.2 <0.50 3.8 1.3 8.3 13.4 <0.020 35.0 8/22/2012 146 <35 <35 <0.10 <0.10 <0.12 <0.12 0.73 <0.20 <0.10 NA *<0.0095 <0.11 0.18 J <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 0.36 J <0.13 <0.15 0.63 J 0.99 <0.0095 <5.0 1/24/2014 131 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 32.9 7/18/2014 55.2 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 9.2 1/14/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 1.3 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 18.9 7/22/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 1.2 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 79.4 1/20/2016 NA NA NA <0.50 0.87 <0.50 <0.50 0.58 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 0.39 J 6.5 1.9 5.18 J 13.97 J NA 36.8 7/20/2016 NA NA NA 4.7 6.5 <0.50 <0.50 0.68 <1.0 <0.50 <0.50 <0.50 <0.50 1.7 <0.50 <0.50 0.41 J <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 1.2 3.3 4.1 103.0 111.6 NA 13.6 12/29/2016 NA NA NA 27.1 15.8 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 4.4 <0.50 <0.50 1.4 <0.50 <0.50 <0.50 NA 0.37 J <0.50 <2.0 6.1 1.2 <0.50 291.8 299.1 NA 3.0 J 7/19/2017 NA NA NA <0.50 <0.50 <0.50 <0.50 0.59 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 ND NA 12 MW-1 MW-2 MW-5 MW-4 Table 3 EPA METHOD 6010 DATE SAMPLED EPA METHOD 504.1 EPA METHOD 6200B (Target analytes reported above method detection limits) MADEP VPH SAMPLE I.D. MW-3 Page 1 of 7 Historical Groundwater Sampling Results Cajah's Mountain Superette 1990 Connelly Springs Road Lenoir, North Carolina Facility ID Number 0-004593 Incident Number: 28649 C5-C8 Aliphatics Carbon Fraction Clas C9-C18 Aliphatics Carbon Fraction Clas C9-C22 Aromatics Carbon Fraction Clas C 5 - C 8 C9 - C 1 2 C 9 - C 1 0 1 , 2 , 4 - T r i m e t h y l b e n z e n e 1 , 3 , 5 - T r i m e t h y l b e n z e n e B r o m o d i c h l o r o m e t h a n e B r o m o f o r m C h l o r o f o r m C h l o r o m e t h a n e D i b r o m o c h l o r o m e t h a n e D i b r o m o m e t h a n e E t h y l e n e D i b r o m i d e ( E D B ) I s o p r o p y l E t h e r I s o p r o p y l b e n z e n e M e t h y l t e r t b u t y l e t h e r ( M T B E ) n - B u t y l b e n z e n e n - P r o p y l b e n z e n e 1 , 2 , - D i c h l o r o e t h a n e T r i c h l o r o e t h y l e n e ( T C E ) T e t r a c h l o r o e t h y l e n e ( P C E ) p - I s o p r o p y l t o l u e n e s e c - B u t y l b e n z e n e S t y r e n e N a p h t h a l e n e B e n z e n e T o l u e n e E t h y l b e n z e n e T o t a l X y l e n e s T o t a l B T E X E t h y l e n e D i b r o m i d e ( E D B ) L e a d Table 3 EPA METHOD 6010 DATE SAMPLED EPA METHOD 504.1 EPA METHOD 6200B (Target analytes reported above method detection limits) MADEP VPH SAMPLE I.D. 11/17/2009 1,200 990 410 23 4 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 *<0.023 3 3.7 130 0.79 7.2 0.34 <0.1 <0.2 1.9 0.9 <0.1 1.2 370 180 39 168 757 <0.023 45.2 2/2/2012 790 479 69.3 13.3 4.9 <0.50 <0.50 2.5 <1.0 <0.50 <0.50 *<0.020 <0.50 1.6 5.2 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 112 36.2 13.8 61.7 223.7 <0.020 92.3 8/22/2012 1,060 331 320 20.8 9.2 <0.59 <0.59 2.0 J <0.98 <0.51 NA *0.062 2.4 J 2.6 4.9 0.69 J 4.9 <0.82 <0.90 <0.69 0.63 J 1.2 J <0.50 2.0 J 226 77.1 24.9 122.1 450.1 0.062 18.1 1/23/2014 282 54.0 <50.0 3.6 1.5 <0.50 <0.50 2.4 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 1.0 <0.50 0.57 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 21.1 5.7 3.0 12.2 42.0 <0.020 41.2 7/17/2014 1/13/2015 7/22/2015 1/19/2016 7/19/2016 12/28/2016 11/17/2009 4,200 550 1,000 100 31 <0.1 <0.1 12 <0.1 <0.1 <0.1 *<0.023 12 7.4 290 3.2 9.3 1.4 <0.1 <0.2 2.6 <0.1 0.58 5.4 920 890 78 520 2,408 <0.023 <10 2/2/2012 1,840 1,840 428 88.7 31.0 <0.50 <0.50 15.0 <1.0 <0.50 <0.50 *<0.020 4.0 5.9 95.0 <0.50 8.0 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 4.1 252 131 15.4 291.6 690 <0.020 52.5 8/22/2012 2,250 784 753 110 32.1 <1.2 <1.2 11.7 <2.0 <1.0 NA *0.058 9.4 5.8 196 2.9 J 10.9 <1.6 <1.8 <1.4 1.3 J 2.0 J <1.0 4.3 J 463 275 43.5 418 1,199.5 0.058 <5.0 1/23/2014 3,790 1,880 <500 195 64.3 <5.0 <5.0 <5.0 <10.0 <5.0 <5.0 *0.052 11.4 12.6 170 <5.0 26.7 <5.0 <5.0 <5.0 NA <5.0 <5.0 <20.0 811 952 132 814 2,709 0.052 73.2 7/18/2014 3,140 1,800 <500 148 47.3 <5.0 <5.0 <5.0 <10.0 <5.0 <5.0 *0.085 6.1 9.4 68.1 <5.0 19.9 <5.0 <5.0 <5.0 NA <5.0 <5.0 <20.0 520 1,040 137 720 2,417 0.085 19.2 1/14/2015 2,930 2,610 <2,500 179 54.7 <5.0 <5.0 <5.0 <10.0 <5.0 <5.0 *<0.020 9.8 10.9 112 <5.0 23.2 <5.0 <5.0 <5.0 <5.0 <5.0 <5.0 <20.0 650 934 126 734 2,444 <0.020 216 7/22/2015 NA NA NA 101 39.9 <2.5 <2.5 4.6 <5.0 <2.5 <2.5 *0.085 9.8 7.8 134 <2.5 14.2 1.8 J <2.5 <2.5 NA 2.7 <2.5 7.4 J 434 401 59.4 387 1,281 0.085 23.5 1/20/2016 NA NA NA 34.2 14.7 <1.2 <1.2 4.0 <2.5 <1.2 <1.2 <1.2 5.9 3.8 125 <1.2 3.0 0.70 J <1.2 <1.2 NA 1.5 <1.2 7.5 276 17.2 4.3 89.2 386.7 NA 38.7 7/20/2016 NA NA NA 71.4 <1.0 <1.0 <1.0 <1.0 <2.0 <1.0 <1.0 <1.0 12.2 4.1 132 <1.0 6.5 1.2 <1.0 <1.0 NA <1.0 <1.0 13.5 235 152 38.6 266 691.6 NA 67.3 12/29/2016 NA NA NA 54.8 18.9 <1.0 <1.0 <1.0 <2.0 <1.0 <1.0 <1.0 12.1 1.8 244 <1.0 1.9 1.4 <1.0 <1.0 NA <1.0 <1.0 27.1 77.7 37.2 16.1 139.9 270.9 NA 21.5 7/19/2017 NA NA NA 3.8 2.4 <0.50 <0.50 1.9 <0.50 <0.50 <0.50 <0.50 0.85 <0.50 24 <0.50 0.68 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 0.66 1.1 6.2 2.0 11.2 20.5 NA 30 11/17/2009 31,000 4,100 8,700 580 130 <5 <0.1 <5 <5 <0.1 <0.1 *2.8 <5 25 <10 <5 61 39 27 27 <5 <5 29 130 1,900 17,000 900 4,600 24,400 2.8 <10 2/2/2012 8/22/2012 1/20/2014 7/17/2014 1/13/2015 7/22/2015 NA NA NA 4,130 2,480 <12.5 <12.5 <12.5 <25.0 <12.5 <12.5 *20.0 <12.5 335 77.2 434 1,220 <12.5 <12.5 <12.5 NA <12.5 83.3 2,330 6,810 36,100 4,160 19,240 66,310 20.0 8.9 1/20/2016 NA NA NA 5,330 1,290 <125 <125 <125 <250 <125 <125 <125 <125 189 <125 <125 626 <125 <125 <125 NA <125 <125 1,320 1,800 21,500 3,040 19,530 45,870 NA 54.1 7/20/2016 NA NA NA 5,350 1,500 <62.5 <62.5 <62.5 <125 <62.5 <62.5 <62.5 <62.5 204 208 259 708 <62.5 <62.5 <62.5 NA <62.5 55.8 J 1,280 4,950 24,600 2,610 15,440 47,600 NA 48.7 12/29/2016 NA NA NA 3,590 852 <100 <100 <100 <200 <100 <100 <100 <100 137 208 <100 425 <100 <100 <100 NA <100 63.1 J 1,000 7,310 36,400 2,750 16,320 62,780 NA 6.7 7/19/2017 NA NA NA 3,900 1000 <250 <250 <250 <250 <250 <250 <250 <250 <250 <250 <250 490 <250 <250 <250 <250 <250 <250 950 2,900 25,000 2,700 15,000 45,600 NA 36 7/28/2010 <30 <35 <5 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 *<0.021 <0.1 <0.2 <0.2 <0.1 <0.1 <0.1 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 ND <0.021 23.7 2/2/2012 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.019 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 1.6 <0.50 1.1 2.7 <0.019 6.4 8/22/2012 784 186 218 <0.10 <0.10 <0.10 <0.10 <0.10 <0.11 <0.10 NA *<0.0094 <0.10 <0.10 <0.10 <0.10 <0.10 <0.10 <0.10 <0.10 <0.10 <0.10 <0.10 <0.15 <0.10 0.26 J <0.10 <0.22 0.26 <0.0094 <5.0 1/22/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 31.5 7/17/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 50.0 1/14/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 56.7 7/22/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 15.4 7/28/2010 <30 <35 <5 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 *<0.021 <0.1 <0.2 <0.2 <0.1 <0.1 <0.1 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 0.12 1.4 <0.1 0.29 1.8 <0.021 <10 2/2/2012 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 0.83 <0.50 <1.5 0.83 <0.020 4.9 J 8/23/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0095 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0095 20.2 1/22/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 21.3 7/17/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 1/14/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 17.3 7/22/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 9.0 Not Sampled Due To Presence Of Free Product MW-9 MW-7 MW-8 Not Sampled Due to Mud/Sediment in Well MW-6 Not Sampled Due to Mud/Sediment in Well Not Sampled Due to Mud/Sediment in Well Not Sampled Due to Mud in Well Not Sampled Due to Mud in Well Not Sampled Due to Presence of Free Product MW-10 Not Sampled Due to Mud/Sediment in Well Not Sampled Due to Presence of Free Product Not Sampled Due To Presence Of Free Product Not Sampled Due To Presence Of Free Product Page 2 of 7 Historical Groundwater Sampling Results Cajah's Mountain Superette 1990 Connelly Springs Road Lenoir, North Carolina Facility ID Number 0-004593 Incident Number: 28649 C5-C8 Aliphatics Carbon Fraction Clas C9-C18 Aliphatics Carbon Fraction Clas C9-C22 Aromatics Carbon Fraction Clas C 5 - C 8 C9 - C 1 2 C 9 - C 1 0 1 , 2 , 4 - T r i m e t h y l b e n z e n e 1 , 3 , 5 - T r i m e t h y l b e n z e n e B r o m o d i c h l o r o m e t h a n e B r o m o f o r m C h l o r o f o r m C h l o r o m e t h a n e D i b r o m o c h l o r o m e t h a n e D i b r o m o m e t h a n e E t h y l e n e D i b r o m i d e ( E D B ) I s o p r o p y l E t h e r I s o p r o p y l b e n z e n e M e t h y l t e r t b u t y l e t h e r ( M T B E ) n - B u t y l b e n z e n e n - P r o p y l b e n z e n e 1 , 2 , - D i c h l o r o e t h a n e T r i c h l o r o e t h y l e n e ( T C E ) T e t r a c h l o r o e t h y l e n e ( P C E ) p - I s o p r o p y l t o l u e n e s e c - B u t y l b e n z e n e S t y r e n e N a p h t h a l e n e B e n z e n e T o l u e n e E t h y l b e n z e n e T o t a l X y l e n e s T o t a l B T E X E t h y l e n e D i b r o m i d e ( E D B ) L e a d Table 3 EPA METHOD 6010 DATE SAMPLED EPA METHOD 504.1 EPA METHOD 6200B (Target analytes reported above method detection limits) MADEP VPH SAMPLE I.D. 7/28/2010 75,000 5,700 24,000 1,800 520 <50 <0.1 <50 <50 <0.1 <0.1 *3.1 190 110 5,600 <50 270 <100 <50 <100 <50 <50 84 700 15,000 37,000 2,800 14,100 68,900 3.1 19.3 2/2/2012 56,300 68,400 <10,000 2,090 492 <0.50 <0.50 <0.50 <1.0 0.73 <0.50 *4.1 151 116 2,590 <0.50 273 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 565 9,890 27,100 2,980 15,290 55,260 4.1 18.1 8/23/2012 17,700 8,370 4,730 2,150 528 <120 <120 <160 <200 <100 NA *2.4 131 J <100 3,210 <100 309 J <160 <180 <140 <100 <100 <100 616 8,720 31,700 3,140 17,310 60,870 2.4 19.5 1/22/2014 71,500 47,800 5,070 2,130 489 <125 <125 <125 <250 <125 <125 *2.7 <125 <125 1,960 <125 265 <125 <125 <125 NA <125 <125 538 7,860 30,300 2,650 14,460 55,270 2.7 55.7 7/17/2014 54,100 33,200 <5,000 1,540 360 <5.0 <5.0 <5.0 <10.0 <5.0 <5.0 *0.93 57.6 69.4 1,210 <5.0 187 <5.0 <5.0 <5.0 NA <5.0 44.4 510 5,350 19,300 1,900 10,410 36,960 0.93 39.7 1/13/2015 54,700 59,600 <10,000 2,860 644 <100 <100 <100 <200 <100 <100 *2.5 <100 124 1,400 <100 361 <100 <100 <100 <100 <100 <100 739 6,650 28,100 3,200 17,760 55,710 2.5 48.5 7/21/2015 NA NA NA 2,270 568 <125 <125 <125 <250 <125 <125 *2.4 83.9 J 103 J 1,870 <125 307 <125 <125 <125 NA <125 67.8 J 728 5,630 26,000 2,960 15,150 49,740 2.4 14.9 1/20/2016 NA NA NA 2,530 594 <125 <125 <125 <250 <125 <125 <125 94.8 J 105 J 2,510 <125 322 <125 <125 <125 NA <125 <125 642 5,450 23,900 2,920 16,260 48,530 NA 54.8 7/19/2016 NA NA NA 851 201 <20.0 <20.0 <20.0 <40.0 <20.0 <20.0 <20.0 <20.0 34.1 138 <20.0 105 <20.0 <20.0 <20.0 NA <20.0 13.4 J 229 693 4,110 686 3,870 9,359 NA 23.2 12/28/2016 NA NA NA 2,360 539 <100 <100 <100 <200 <100 <100 <100 <100 93.5 J 864 <100 307 <100 <100 <100 NA <100 <100 605 3,400 20,400 2,540 13,750 40,090 NA 7.4 7/18/2017 NA NA NA 2,300 600 <100 <100 <100 <100 <100 <100 <100 <100 100 520 <100 300 <100 <100 <100 <100 <100 <100 490 2,100 16,000 2,400 12,500 33,000 NA 16 7/28/2010 <30 <35 <5 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 *<0.021 <0.1 <0.2 <0.2 <0.1 <0.1 <0.1 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 2.7 2.7 <0.021 15.2 2/2/2012 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <4.0 8/23/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0094 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0094 11.8 1/20/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 11.0 7/17/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 0.96 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 58.0 1/13/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *0.10 0.58 <0.50 46.0 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND 0.10 437 7/21/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *0.23 3.5 <0.50 207 <0.50 <0.50 1.1 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND 0.23 45.7 1/19/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 3.2 <0.50 188 <0.50 <0.50 0.68 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 29.3 7/19/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 6.4 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 50.5 12/28/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 10.2 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 9.7 2/2/2012 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 4.5 J 8/24/2012 163 50.8 J <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0096 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0096 <5.0 1/21/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 7/16/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 5.9 1/13/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 12.8 7/21/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 5.5 2/2/2012 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 4.3 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 11.4 8/23/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0092 <0.11 <0.10 1.7 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0092 14.5 1/20/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 21.1 7/17/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.021 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.021 12.4 1/13/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 117 7/21/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 2.9 <0.50 33.5 <0.50 <0.50 0.68 <0.50 <0.50 NA <0.50 <0.50 <2.0 1.1 <0.50 <0.50 <1.5 ND <0.020 7.7 1/19/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 4.1 <0.50 122 <0.50 <0.50 1.0 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 40.7 7/19/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 1.6 <0.50 14.2 <0.50 <0.50 0.29 J <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 92.6 12/28/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 1.1 <0.50 9.3 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 4.0 J 7/18/2017 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 2.3 <0.50 5.6 <0.50 <0.50 0.45 J <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 ND NA 17 2/2/2012 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 8/23/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0095 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0095 <5.0 1/20/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 7/16/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 1/13/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 7/21/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 2/2/2012 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 10.6 8/24/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0096 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0096 41.7 1/21/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 152 7/16/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.021 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.021 98.0 1/13/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 233 7/21/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.021 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.021 30.7 MW-13 MW-11 MW-14 MW-15 MW-16 MW-12 Page 3 of 7 Historical Groundwater Sampling Results Cajah's Mountain Superette 1990 Connelly Springs Road Lenoir, North Carolina Facility ID Number 0-004593 Incident Number: 28649 C5-C8 Aliphatics Carbon Fraction Clas C9-C18 Aliphatics Carbon Fraction Clas C9-C22 Aromatics Carbon Fraction Clas C 5 - C 8 C9 - C 1 2 C 9 - C 1 0 1 , 2 , 4 - T r i m e t h y l b e n z e n e 1 , 3 , 5 - T r i m e t h y l b e n z e n e B r o m o d i c h l o r o m e t h a n e B r o m o f o r m C h l o r o f o r m C h l o r o m e t h a n e D i b r o m o c h l o r o m e t h a n e D i b r o m o m e t h a n e E t h y l e n e D i b r o m i d e ( E D B ) I s o p r o p y l E t h e r I s o p r o p y l b e n z e n e M e t h y l t e r t b u t y l e t h e r ( M T B E ) n - B u t y l b e n z e n e n - P r o p y l b e n z e n e 1 , 2 , - D i c h l o r o e t h a n e T r i c h l o r o e t h y l e n e ( T C E ) T e t r a c h l o r o e t h y l e n e ( P C E ) p - I s o p r o p y l t o l u e n e s e c - B u t y l b e n z e n e S t y r e n e N a p h t h a l e n e B e n z e n e T o l u e n e E t h y l b e n z e n e T o t a l X y l e n e s T o t a l B T E X E t h y l e n e D i b r o m i d e ( E D B ) L e a d Table 3 EPA METHOD 6010 DATE SAMPLED EPA METHOD 504.1 EPA METHOD 6200B (Target analytes reported above method detection limits) MADEP VPH SAMPLE I.D. 2/2/2012 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 8.0 8/24/2012 78.4 J <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0095 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0095 16.3 1/21/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 95.6 7/16/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.021 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.021 91.4 1/13/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 139 7/21/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 0.33 J <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 21.7 2/2/2012 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 0.60 <0.50 <1.5 0.60 <0.020 28.2 8/23/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0093 0.39 J <0.10 1.2 <0.10 <0.11 <0.16 <0.18 <0.14 0.72 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0093 42.6 1/20/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 2.1 <0.50 1.7 <0.50 <0.50 0.81 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 79.3 7/16/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 1.7 <0.50 <0.50 0.63 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 50.9 1/13/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *0.023 2.0 <0.50 1.0 <0.50 <0.50 1.2 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND 0.023 109 7/21/2015 1/19/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 0.33 J <1.0 <0.50 <0.50 <0.50 2.2 <0.50 2.8 <0.50 <0.50 1.3 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 14.4 7/19/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 0.62 <0.50 <0.50 0.60 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 54.9 12/28/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 1.1 <0.50 1.2 <0.50 <0.50 1.6 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 2.8 J 7/18/2017 NA NA NA <0.50 <0.50 <0.50 <0.50 1.1 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 0.48 J <0.50 <0.50 1.2 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 ND NA 37 2/2/2012 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <20.0 8/23/2012 <35 <35 41.6 J <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0093 <0.11 <0.10 0.30 J <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0093 25.3 1/20/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.019 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.019 139 7/16/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.021 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.021 54.5 1/13/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.021 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.021 112 7/21/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <100 2/2/2012 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 15.6 8/23/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 0.21 J <0.20 <0.10 NA *<0.0097 0.14 J <0.10 0.38 J <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0097 8.2 1/21/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 41.7 7/16/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.021 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.021 26.8 1/13/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 64.3 7/21/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.021 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.021 24.4 2/2/2012 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 3.9 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <4.0 8/24/2012 60.8 J <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0095 <0.11 <0.10 2.5 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0095 <5.0 1/21/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 7/16/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 1/13/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 7/21/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 3.4 J 4/3/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *0.024 1.7 <0.10 47.4 <0.10 <0.11 0.64 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND 0.024 29.9 8/23/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0097 0.80 <0.10 24.0 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0097 7.5 1/22/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 8.9 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 7/17/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 *<0.020 <0.50 <0.50 1.6 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 66.0 1/13/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 2.3 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 109 7/21/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 0.49 J <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 7.2 1/19/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 0.32 J <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 21.4 J 7/19/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 0.41 J <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 56.3 12/28/2016 7/18/2017 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 0.54 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 ND NA 29 MW-21 MW-19 MW-20 Not Sampled - Aboveground Pool Obstructing Well Not Sampled - Could Not Find MW-18 MW-22 MW-17 Page 4 of 7 Historical Groundwater Sampling Results Cajah's Mountain Superette 1990 Connelly Springs Road Lenoir, North Carolina Facility ID Number 0-004593 Incident Number: 28649 C5-C8 Aliphatics Carbon Fraction Clas C9-C18 Aliphatics Carbon Fraction Clas C9-C22 Aromatics Carbon Fraction Clas C 5 - C 8 C9 - C 1 2 C 9 - C 1 0 1 , 2 , 4 - T r i m e t h y l b e n z e n e 1 , 3 , 5 - T r i m e t h y l b e n z e n e B r o m o d i c h l o r o m e t h a n e B r o m o f o r m C h l o r o f o r m C h l o r o m e t h a n e D i b r o m o c h l o r o m e t h a n e D i b r o m o m e t h a n e E t h y l e n e D i b r o m i d e ( E D B ) I s o p r o p y l E t h e r I s o p r o p y l b e n z e n e M e t h y l t e r t b u t y l e t h e r ( M T B E ) n - B u t y l b e n z e n e n - P r o p y l b e n z e n e 1 , 2 , - D i c h l o r o e t h a n e T r i c h l o r o e t h y l e n e ( T C E ) T e t r a c h l o r o e t h y l e n e ( P C E ) p - I s o p r o p y l t o l u e n e s e c - B u t y l b e n z e n e S t y r e n e N a p h t h a l e n e B e n z e n e T o l u e n e E t h y l b e n z e n e T o t a l X y l e n e s T o t a l B T E X E t h y l e n e D i b r o m i d e ( E D B ) L e a d Table 3 EPA METHOD 6010 DATE SAMPLED EPA METHOD 504.1 EPA METHOD 6200B (Target analytes reported above method detection limits) MADEP VPH SAMPLE I.D. 2/2/2012 309 406 <50.0 25.0 <0.50 0.67 <0.50 1.1 <1.0 0.74 <0.50 *0.42 16.5 2.6 84.6 <0.50 3.1 3.6 <0.50 <0.50 <0.50 <0.50 <0.50 10.8 260 71.1 21.8 215 567.9 0.42 <4.0 8/23/2012 2,300 865 477 76.3 <2.0 <2.3 <2.4 <3.2 <3.9 <2.0 NA *1.1 51.9 7.3 J 251 <2.0 11.6 12.3 <3.6 <2.7 <2.0 <2.0 <2.0 31.3 967 266 82.1 638 1,953.1 1.1 <5.0 1/22/2014 3,060 2,060 <1,000 110 <5.0 <5.0 <5.0 <5.0 <10.0 <5.0 <5.0 *1.5 61.0 8.9 247 <5.0 12.2 16.5 <5.0 <5.0 NA <5.0 <5.0 42.3 1,470 65.2 85.8 796 2,417.0 1.5 <5.0 7/17/2014 4,160 2,360 <1,250 112 9.8 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *1.5 74.9 11.5 292 1.8 15.1 21.3 <0.50 <0.50 bn <0.50 <0.50 53.1 1,360 78.5 118 785 2,341.5 1.5 <5.0 1/13/2015 5,250 5,210 <5,000 104 8.6 <5.0 <5.0 <5.0 <10.0 <5.0 <5.0 *1.4 57.8 9.4 282 <5.0 12.4 16.3 <5.0 <5.0 <5.0 <5.0 <5.0 47.4 1,360 23.4 88.5 783 2,254.9 1.4 <5.0 7/21/2015 NA NA NA 71.1 6.6 <5.0 <5.0 <5.0 14.1 <5.0 <5.0 *1.6 54.3 9.8 311 <5.0 12.0 17.8 <5.0 <5.0 NA <5.0 <5.0 47.2 1,550 17.6 78.0 691 2,336.6 1.6 2.5 J 1/19/2016 NA NA NA 1.4 1.0 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 11.8 0.86 61.6 <0.50 <0.50 3.2 <0.50 <0.50 NA <0.50 <0.50 4.8 144 0.44 J 0.80 17.0 162.24 J NA 9.1 7/19/2016 NA NA NA 1.7 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 0.25 J 23.6 0.63 150 <0.50 0.56 6.1 <0.50 <0.50 NA <0.50 <0.50 6.0 155 <0.50 4.2 12.1 171.3 NA 15.4 12/28/2016 NA NA NA 38.5 7.1 <2.0 <2.0 <2.0 <4.0 <2.0 <2.0 <2.0 60.4 2.1 429 <2.0 2.1 17.2 <2.0 <2.0 NA <2.0 <2.0 15.5 405 10.0 12.1 253.1 680.2 NA 5.4 7/18/2017 NA NA NA 4.2 3.1 <2.5 <2.5 <2.5 <2.5 <2.5 <2.5 <2.5 43 3.1 260 <2.5 2.4 J 28 <2.5 <2.5 <2.5 <2.5 <2.5 14 520 <2.5 6.0 22.1 548.1 NA 24 4/3/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *0.0096 J 0.91 <0.10 1.2 <0.10 <0.11 <0.12 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND 0.0096 J <5.0 8/23/2012 61.0 J <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0095 0.42 J <0.10 0.60 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0095 <5.0 1/22/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 7/17/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 1/13/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 7/22/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 0.65 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 1/19/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 0.55 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA <5.0 7/19/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 0.51 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA <5.0 12/28/2016 11/17/2009 1,300 180 230 41 <0.1 <0.1 <0.1 7.9 <0.1 <0.1 <0.1 *<0.022 2.3 2.6 450 1.2 3.2 <0.2 <0.1 <0.2 2.1 <0.1 <0.1 3.4 140 0.41 3 21.8 165.6 <0.022 <10 2/3/2012 1,510 502 90 31.1 <0.50 <0.50 <0.50 15.7 <1.0 <0.50 <0.50 *0.023 2.7 2.8 490 1.6 2.1 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 3.7 134 0.61 1.0 54.2 189.8 0.023 11.7 8/22/2012 757 160 181 11.9 <1.0 <1.2 <1.2 7.9 <2.0 <1.0 NA *0.026 2.1 J 1.1 J 349 <1.0 <1.1 <1.6 <1.8 <1.4 <1.0 <1.0 <1.0 1.5 J 57.9 11.8 <1.5 28.3 98.0 0.026 <5.0 1/23/2014 251 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 4.1 <1.0 <0.50 <0.50 *<0.020 1.2 <0.50 325 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 8.8 7/17/2014 273 <50.0 <50.0 <0.50 <0.50 1.1 <0.50 16.4 <1.0 <0.50 <0.50 *<0.020 1.8 <0.50 448 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 1/14/2015 123 <50.0 <50.0 <1.0 <1.0 <1.0 <1.0 10.3 <2.0 <1.0 <1.0 *<0.020 1.4 <1.0 174 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <1.0 <4.0 <1.0 <1.0 <1.0 <3.0 ND <0.020 9.7 7/22/2015 NA NA NA <0.50 <0.50 0.88 <0.50 12.9 <1.0 <0.50 <0.50 *<0.020 1.4 <0.50 118 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 8.0 1/20/2016 NA NA NA <0.50 <0.50 0.67 <0.50 10.9 <1.0 <0.50 <0.50 <0.50 1.3 <0.50 101 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 8.7 7/20/2016 NA NA NA <0.50 <0.50 0.83 <0.50 11.3 <1.0 <0.50 <0.50 <0.50 0.84 <0.50 44.5 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 0.60 <0.50 <0.50 <1.5 0.60 NA 12.9 12/29/2016 NA NA NA 0.34 J <0.50 0.88 <0.50 12.7 <1.0 <0.50 <0.50 <0.50 0.52 <0.50 51.0 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 1.3 <0.50 <0.50 0.28 J 1.58 NA 7.1 7/19/2017 NA NA NA <0.50 <0.50 0.96 <0.50 12 <0.50 <0.50 <0.50 <0.50 0.68 <0.50 36 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 ND NA 26 7/28/2010 <30 <35 <5 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 *<0.021 <0.1 <0.2 <0.2 <0.1 <0.1 <0.1 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 1.4 2 <0.1 3.1 6.5 <0.021 <10 2/2/2012 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 1.3 6.9 0.77 3.7 12.7 <0.020 <4.0 8/22/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 0.28 J <0.10 NA *<0.0096 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0096 <5.0 1/22/2014 399 <50.0 <50.0 0.62 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 5.5 <0.50 <0.50 3.84 3.84 <0.020 <5.0 7/17/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 <0.020 10.0 1/14/2015 85.8 74.8 <50.0 3.5 0.69 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *0.028 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 39.1 9.7 1.9 25.6 76.3 0.028 5.8 7/22/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 1/20/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA <5.0 7/20/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 4.4 J 12/28/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA <5.0 2/3/2012 <50.0 69.9 <50.0 0.69 <0.50 <0.50 <0.50 0.66 <1.0 <0.50 <0.50 *<0.021 <0.50 <0.50 25.8 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 1.7 1.5 <0.50 2.4 5.6 <0.021 4.2 J 8/22/2012 58.4 J <35 <35 0.17 J <0.10 <0.12 <0.12 <0.16 1.4 <0.10 NA *<0.0095 0.22 J <0.10 33.2 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 0.52 0.46 J <0.15 0.26 J 1.24 <0.0095 <5.0 1/23/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 27.1 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.30 <0.50 <1.5 ND <0.020 <5.0 7/17/2014 <50.0 <50.0 <50.0 0.55 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 25.1 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 1.0 1.0 <0.020 <5.0 1/14/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 7/22/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 0.41 J <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 0.56 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 1/20/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA <5.0 7/20/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 4.6 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA <5.0 12/29/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 6.4 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA <5.0 IMW-2 DMW-2 DMW-3 IMW-1 DMW-1 Page 5 of 7 Historical Groundwater Sampling Results Cajah's Mountain Superette 1990 Connelly Springs Road Lenoir, North Carolina Facility ID Number 0-004593 Incident Number: 28649 C5-C8 Aliphatics Carbon Fraction Clas C9-C18 Aliphatics Carbon Fraction Clas C9-C22 Aromatics Carbon Fraction Clas C 5 - C 8 C9 - C 1 2 C 9 - C 1 0 1 , 2 , 4 - T r i m e t h y l b e n z e n e 1 , 3 , 5 - T r i m e t h y l b e n z e n e B r o m o d i c h l o r o m e t h a n e B r o m o f o r m C h l o r o f o r m C h l o r o m e t h a n e D i b r o m o c h l o r o m e t h a n e D i b r o m o m e t h a n e E t h y l e n e D i b r o m i d e ( E D B ) I s o p r o p y l E t h e r I s o p r o p y l b e n z e n e M e t h y l t e r t b u t y l e t h e r ( M T B E ) n - B u t y l b e n z e n e n - P r o p y l b e n z e n e 1 , 2 , - D i c h l o r o e t h a n e T r i c h l o r o e t h y l e n e ( T C E ) T e t r a c h l o r o e t h y l e n e ( P C E ) p - I s o p r o p y l t o l u e n e s e c - B u t y l b e n z e n e S t y r e n e N a p h t h a l e n e B e n z e n e T o l u e n e E t h y l b e n z e n e T o t a l X y l e n e s T o t a l B T E X E t h y l e n e D i b r o m i d e ( E D B ) L e a d Table 3 EPA METHOD 6010 DATE SAMPLED EPA METHOD 504.1 EPA METHOD 6200B (Target analytes reported above method detection limits) MADEP VPH SAMPLE I.D. 2/2/2012 <50.0 116 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <4.0 8/23/2012 47.4 J <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 1.4 <0.10 NA *<0.0094 <0.11 <0.10 0.18 J <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 0.16 J 0.23 J 0.22 J <0.15 <0.30 0.45 <0.0094 <5.0 1/21/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 2.4 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 7/17/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 1/13/2015 <50.0 <50.0 <50.0 1.5 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 0.64 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 6.3 5.0 <0.50 7.2 18.50 <0.020 <5.0 7/21/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 0.39 J <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 1/19/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 0.78 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 0.57 <0.50 <0.50 0.28 J 0.85 J NA <5.0 7/19/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 0.40 J <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 12.4 12/28/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 0.32 J <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA <5.0 4/3/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0095 0.18 J <0.10 3.1 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 0.58 <0.13 <0.15 <0.30 0.58 <0.0095 <5.0 8/23/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 0.52 <0.10 NA *<0.0095 0.26 J <0.10 5.2 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 0.79 <0.13 <0.15 <0.30 0.79 <0.0095 <5.0 1/22/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 7/17/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 0.55 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 1/13/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 <5.0 7/21/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 3.4 J 1/19/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 0.28 J <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA <5.0 7/19/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 0.30 J <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA 13.7 12/28/2016 7/26/2010 NA NA NA <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.1 <0.1 *<0.023 <0.1 <0.2 <0.2 <0.1 <0.1 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 0.84 0.12 <0.1 <0.1 2.7 2.8 <0.023 NA 5/5/2011 <30 <40 <10 <0.1 <0.1 <0.1 <0.1 <0.1 0.97 <0.1 <0.1 *<0.021 <0.5 <0.2 <0.2 <0.1 <0.1 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 ND <0.021 NA 8/29/2012 39.6 J <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0093 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0093 NA 1/20/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND NA NA 7/26/2010 NA NA NA <0.1 <0.1 <0.1 <0.1 0.31 <0.2 <0.1 <0.1 *<0.021 <0.1 <0.2 6 <0.1 <0.1 0.12 <0.1 <0.2 <10 <0.1 <0.1 0.34 0.12 <0.1 <0.1 <0.1 0.12 <0.021 NA 5/5/2011 <30 <40 <10 <0.1 <0.1 <0.1 <0.1 0.22 1.5 <0.1 <0.1 *<0.02 <0.5 <0.2 2.5 <0.1 <0.1 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 ND <0.02 NA 8/24/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 1.6 <0.20 <0.10 NA *<0.0096 <0.11 <0.10 3.7 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0096 NA 1/24/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 3.4 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 7/16/2014 1/15/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 3.4 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 7/22/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 3.0 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 1/20/2016 8/29/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0093 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0093 NA 1/15/2015 7/22/2015 8/29/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0093 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0093 NA 1/15/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 7/22/2015 5/5/2011 <30 <40 <10 <0.1 <0.1 <0.1 <0.1 0.4 0.33 <0.1 <0.1 *<0.022 <0.5 <0.2 <0.2 <0.1 <0.1 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 ND <0.022 NA 8/24/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 0.44 J <0.20 <0.10 NA *<0.0096 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0096 NA 1/24/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 7/16/2014 1/15/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 7/22/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 0.34 J <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA DMW-5 DMW-4 PW-1 Not Sampled - No One Home, No Access PW-4 PW-5 Not Sampled - No One Home, No Access Not Sampled - Well House Partialy Collapsed and Multiple Hazards to Access Sample PortPW-2 Not Sampled - No One Home, No Access Not Sampled - No One Home, No Access Not Sampled - No One Home, No Access Not Sampled - Could Not Find PW-6 Page 6 of 7 Historical Groundwater Sampling Results Cajah's Mountain Superette 1990 Connelly Springs Road Lenoir, North Carolina Facility ID Number 0-004593 Incident Number: 28649 C5-C8 Aliphatics Carbon Fraction Clas C9-C18 Aliphatics Carbon Fraction Clas C9-C22 Aromatics Carbon Fraction Clas C 5 - C 8 C9 - C 1 2 C 9 - C 1 0 1 , 2 , 4 - T r i m e t h y l b e n z e n e 1 , 3 , 5 - T r i m e t h y l b e n z e n e B r o m o d i c h l o r o m e t h a n e B r o m o f o r m C h l o r o f o r m C h l o r o m e t h a n e D i b r o m o c h l o r o m e t h a n e D i b r o m o m e t h a n e E t h y l e n e D i b r o m i d e ( E D B ) I s o p r o p y l E t h e r I s o p r o p y l b e n z e n e M e t h y l t e r t b u t y l e t h e r ( M T B E ) n - B u t y l b e n z e n e n - P r o p y l b e n z e n e 1 , 2 , - D i c h l o r o e t h a n e T r i c h l o r o e t h y l e n e ( T C E ) T e t r a c h l o r o e t h y l e n e ( P C E ) p - I s o p r o p y l t o l u e n e s e c - B u t y l b e n z e n e S t y r e n e N a p h t h a l e n e B e n z e n e T o l u e n e E t h y l b e n z e n e T o t a l X y l e n e s T o t a l B T E X E t h y l e n e D i b r o m i d e ( E D B ) L e a d Table 3 EPA METHOD 6010 DATE SAMPLED EPA METHOD 504.1 EPA METHOD 6200B (Target analytes reported above method detection limits) MADEP VPH SAMPLE I.D. PW-7 5/5/2011 <30 <40 <10 <0.1 <0.1 4.2 3.5 3.2 0.19 7.2 0.1 *<0.021 <0.5 <0.2 <0.2 <0.1 <0.1 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 ND <0.021 NA 5/5/2011 <30 <40 <10 <0.1 <0.1 <0.1 <0.1 <0.1 0.93 <0.1 <0.1 *<0.022 <0.5 <0.2 0.64 <0.1 <0.1 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 ND <0.022 NA 8/24/2012 42.9 J <35 <35 <0.10 <0.10 <0.12 <0.12 0.20 J <0.20 <0.10 NA *<0.0096 0.30 J <0.10 0.40 J <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0096 NA 1/24/2014 7/18/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 1/15/2015 7/22/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 1/20/2016 PW-10 1/15/2015 PW-11 8/29/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0093 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0093 NA 8/29/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 0.54 <0.20 <0.10 NA *<0.0095 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0095 NA 1/15/2015 7/22/2015 1/15/2015 7/22/2015 PW-14 1/15/2015 11/17/2009 <30 <10 <35 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 *<0.022 <0.1 <0.1 <0.2 <0.1 <0.1 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.1 ND <0.022 NA 7/26/2010 NA NA NA <0.1 <0.1 <0.1 <0.1 1.3 <0.1 <0.1 <0.1 *<0.022 <0.1 <0.1 <0.2 <0.1 <0.1 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 1.2 <0.1 <0.1 <0.2 <0.1 ND <0.022 NA 5/5/2011 <30 <40 <10 <0.1 <0.1 <0.1 <0.1 1.2 0.78 <0.1 <0.1 *<0.022 <0.5 <0.2 0.25 <0.1 <0.1 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 ND <0.022 NA 7/18/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 1/15/2015 7/22/2015 11/17/2009 440 80 220 9.6 2.2 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 *NA <0.1 0.5 <0.1 <0.1 1.1 <0.1 <0.1 <0.2 <0.1 <0.1 0.46 2.7 12 170 16 81 ND NA NA 7/26/2010 NA NA NA <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 *<0.021 <0.1 <0.1 <0.2 <0.1 <0.1 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 1.4 4.3 <0.2 3.9 ND <0.021 NA 5/5/2011 <30 <40 <10 <0.1 <0.1 <0.1 <0.1 0.21 0.3 <0.1 <0.1 *<0.022 <0.5 <0.2 <0.2 <0.1 <0.1 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 ND <0.022 NA 8/29/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0094 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0094 NA 1/20/2016 7/26/2010 NA NA NA <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 *<0.022 <0.1 <0.1 <0.2 <0.1 <0.1 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.1 ND <0.022 NA 8/29/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0096 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0096 NA 1/20/2016 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.50 ND NA NA 5/5/2011 <30 <40 <10 <0.1 <0.1 <0.1 <0.1 0.10 1.7 <0.1 <0.1 *<0.023 <0.5 <0.2 <0.2 <0.1 <0.1 <0.2 <0.1 <0.2 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 ND <0.023 NA 8/24/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0097 <0.11 <0.10 <0.13 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0097 NA 1/27/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 7/18/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 1/15/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 7/22/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 2/2/2012 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 0.90 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 8/24/2012 <35 <35 <35 <0.10 <0.10 <0.12 <0.12 <0.16 <0.20 <0.10 NA *<0.0095 <0.11 <0.10 0.85 <0.10 <0.11 <0.16 <0.18 <0.14 <0.10 <0.10 <0.10 <0.10 <0.13 <0.13 <0.15 <0.30 ND <0.0095 NA 1/24/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 7/18/2014 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 1/15/2015 <50.0 <50.0 <50.0 <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 7/22/2015 NA NA NA <0.50 <0.50 <0.50 <0.50 <0.50 <1.0 <0.50 <0.50 *<0.020 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 <0.50 NA <0.50 <0.50 <2.0 <0.50 <0.50 <0.50 <1.5 ND <0.020 NA 1/20/2016 400 700 200 400 400 0.6 4 70 3 0.4 NE 0.02 70 70 20 70 70 0.4 3 0.7 25 70 70 6 1 600 600 500 N/A 0.02 15 NE NE NE 28,500 25,000 NE 4000 70,000 3,000 400 NE 50 70,000 25,000 20,000 6,900 30,000 400 3,000 700 11,700 8,500 70,000 6,000 5,000 260,000 84,500 85,500 N/A 50 15,000 1. All measurements are in micrograms per liter (ug/L)9. Analytical table indicates target analyte concentrations reported above method detection limit 2. NC 2L GW Standard = Title 15A NCAC 2L .0202 Groundwater Standard. (Amended Effective April 16, 2012 10. NA = Not Analyzed for specified paramete 3. "<" or ND = Not detected above method detection limit or laboratory reporting limi 11. N/A = Not Applicabl 4. GCL = Gross Contaminant Level established by NCDEQ 12. J = Estimated value below the laboratory reporting limit but above the method detection limi 5. Target analyte concentrations detected above 2L Groundwater Standards are bolded 6. Target analyte concentrations detected above GCLs are bolded and italicize 7. NE = Not Established. 14. * = Value reported under EPA Method 504.1 GCLs NC 2L GW Standards 8. VPH = Volatile Petroleum Hydrocarbons: C5-C8 and C9-C18 aliphatic chains, and C9-C22 aromatic chain Not Sampled - No One Home and Outside Water Turned Off Not Sampled - No One Home, No Access Not Sampled - No One Home, No Access Not Sampled - No One Home, No Access Not Sampled; Outside Spigots Winterized and No One Home PW-21 PW-9 Not Sampled - No One Home, No Access PW-16 Not Sampled - No One Home, No Access PW-22 PW-13 PW-18 Not Sampled - No One Home, No Access Not Sampled - Well Not Operational During Winter Not Sampled - No One Home, No Access Not Sampled - No One Home, No Access 13. Methylene chloride, a known laboratory contaminant, was reported at 0.2 ug/L for water collected from PW-16 on July 26, 2010; and at 0.51 ug/L for water collecte from PW-7 on May 5, 2011. PW-15 Not Sampled - Owner Refused Access Not Sampled - Owner Refused Access PW-12 Page 7 of 7 Table 4 Free Product Recovery Information Cajah's Mountain Superette 1990 Connelly Springs Road Lenoir, North Carolina Facility ID Number 0-004593 Incident Number 28649 Date Well ID Free Product Recovery Method Product Thickness Before Recovery (Feet) Product Thickness After Recovery (Feet) Amount of Vaporized Product (Gallons) Amount of Liquid (Water and Product) (Gallons) Amount of Liquid Product (Gallons) Total Amount of Product Recovered (Gallons) 3/28/2012 MW-8 AFVR 2.15 0.01 6.76 226 44 50.76 6/28/2012 MW-8 AFVR 0.48 0.00 6.07 231 0.00 6.07 9/28/2012 MW-8 AFVR 0.26 0.00 8.68 231 0.00 8.68 12/13/2012 MW-8 AFVR 0.69 0.00 12.79 226 0.00 12.79 3/14/2013 MW-8 AFVR 0.31 0.00 5.34 231 0.00 5.34 7/24/2013 MW-8 AFVR 0.94 0.00 2.97 189 0.00 2.97 9/16/2013 MW-8 AFVR 0.61 0.00 5.34 270 0.00 5.34 12/18/2013 MW-8 AFVR 1.12 0.00 6.22 310 0.00 6.22 AFVR = Aggressive Fluid/Vapor Recovery 12/13/2012 3/14/2013 7/24/2013 9/16/2013 12/18/2013 78.30 83.64 86.61 91.95 98.17 12.79 5.34 2.97 5.34 6.22 56.83 9/28/2012 8.68 65.51 Date of Recovery Event Total Volume of Free Product Recovered from Site During Current Recovery Event (Gallons) Cumulative Total Volume Recovered to Date from All Recovery Events (Gallons) 3/28/2012 50.76 50.76 6/28/2012 6.07 Table 5 Monitored Natural Attenuation Parameters Cajah's Mountain Superette 1990 Connelly Springs Road Lenoir, North Carolina Facility ID Number 0-004593 Incident Number 28649 Sample I.D.Date Sampled Dissolved Oxygen Nitrate Manganese Ferrous Iron Sulfate Methane 8/23/2012 3.22 0.17 0.832 <0.10 <2.0 0.00501 1/22/2014 5.87 0.038 2.12 <0.50 <2.0 0.0091 7/17/2014 6.08 0.040 1.88 <0.50 <2.0 0.0088 1/13/2015 2.93 0.080 1.99 0.87 <2.0 0.0077 7/21/2015 2.05 0.066 2.89 1.2 1.6 J 0.0090 J 1/19/2016 1.49 0.34 0.964 <0.50 1.4 J 0.0027 J 7/19/2016 5.01 NA NA NA NA NA 12/28/2016 8.54 NA NA NA NA NA 7/18/2017 9.23 NA NA NA NA NA 8/23/2012 3.56 <0.10 0.0994 0.34 2.0 0.00427 1/22/2014 7.22 0.023 0.0086 <0.50 3.6 <0.0066 7/17/2014 4.05 <0.020 0.0091 <0.50 3.9 <0.0066 1/13/2015 3.05 0.069 <0.0050 <0.50 5.8 <0.0066 7/22/2015 5.48 0.017 J 0.0486 <0.50 3.8 0.0021 J 1/19/2016 3.39 0.053 0.0206 <0.50 7.4 0.0019 J 7/19/2016 6.10 NA NA NA NA NA 12/28/2016 8/22/2012 3.09 0.80 0.214 0.33 6.3 0.00517 1/23/2014 10.11 1.2 0.188 <0.50 5.9 <0.0066 7/17/2014 12.17 1.2 0.253 <0.50 <2.0 <0.0066 1/14/2015 5.49 1.3 0.405 1.0 <2.0 <0.0066 7/22/2015 5.70 1.1 0.444 <0.50 1.5 J <0.0100 1/20/2016 2.26 1.1 0.290 <0.50 1.5 J 0.0015 J 7/20/2016 5.40 NA NA NA NA NA 12/28/2016 4.33 NA NA NA NA NA 7/19/2017 9.11 NA NA NA NA NA 8/22/2012 1.31 <0.10 0.510 0.48 <2.0 0.0237 1/22/2014 1.09 0.061 0.399 <0.50 <2.0 0.512 7/17/2014 11.37 0.057 0.586 <0.50 14.4 0.288 1/14/2015 1.99 0.23 0.509 0.80 9.2 1.58 7/22/2015 1.31 0.58 0.371 <0.50 7.5 0.0020 J 1/20/2016 1.35 <0.020 0.363 <0.50 1.8 J 4.49 7/20/2016 4.52 NA NA NA NA NA 12/28/2016 2.17 NA NA NA NA NA 8/22/2012 2.30 <1.0 <0.015 <0.10 <20 0.00180 1/23/2014 4.98 <0.020 <0.0050 <0.50 5.1 <0.0066 7/17/2014 3.32 <0.020 <0.0050 <0.50 12.6 0.01470 1/14/2015 5.06 0.48 0.0203 <0.50 6.2 <0.0066 7/22/2015 2.02 <0.020 0.0199 <0.50 11.3 0.0020 J 1/20/2016 1.91 0.21 0.0165 <0.50 5.8 0.0019 J 7/20/2016 4.69 NA NA NA NA NA 12/29/2016 1.95 NA NA NA NA NA 8/23/2012 1.67 <2.5 0.0171 <0.10 <50 0.0047 1/21/2014 4.52 <0.020 0.0150 <0.50 10 0.0206 7/17/2014 7.24 <0.020 0.0071 <0.50 9.9 0.0652 1/13/2015 2.45 <0.020 <0.0050 <0.50 10.4 0.0330 7/21/2015 1.91 <0.020 0.0156 0.70 9.5 <0.0100 1/19/2016 1.41 <0.020 0.0205 <0.50 15.2 0.0352 7/19/2016 4.31 NA NA NA NA NA 12/28/2016 1.82 NA NA NA NA NA 8/23/2012 1.65 0.11 0.0532 0.52 7.6 0.00126 1/22/2014 4.77 <0.020 0.0206 0.83 8.0 <0.0066 7/17/2014 3.59 0.022 0.0161 <0.50 6.6 <0.0066 1/13/2015 3.16 0.095 0.0059 <0.50 5.9 <0.0066 7/21/2015 2.63 0.050 0.0478 <0.50 5.4 0.0015 J 1/19/2016 1.63 0.089 0.0176 <0.50 6.0 0.0017 J 7/19/2016 7.82 NA NA NA NA NA 12/28/2016 1. All concentrations are in milligrams per liter (mg/L). 2. "<" = Not detected above laboratory reporting limit. 3. Dissolved oxygen readings collected in the field with water quality equipment. 4. Values in bold indicate levels greater than the laboratory reporting limit. 5. NA = Not Analyzed. IMW-1 DMW-1 IMW-2 Not Sampled - Could Not Find DMW-5 Not Sampled - Could Not Find DMW-2 DMW-3 DMW-4 Date Cross-Sectional Area of Pipe Conversion Factor3 Days of Operation Cumulative Recovery (ft2) (lb-m3/mg-ft3)(lb/hr) (lb/day) (days) (lbs) 04/04/14* 0.08700 1,116 97.09 413 0.00000006243 0.1502 3.60 9.00 32.44 07/10/14 0.08700 1,116 97.09 6.04 0.00000006243 0.0022 0.05 97.00 37.56 10/27/14 0.08700 714 62.12 281.0 0.00000006243 0.0654 1.57 109.0 208.6 03/04/15 0.08700 719 62.55 313.0 0.00000006243 0.0733 1.760 128.0 433.9 06/18/15* 0.08700 763 66.38 26.30 0.00000006243 0.0065 0.1569 106.0 450.5 10/29/15 0.08700 603 52.46 275.0 0.00000006243 0.05404 1.2970 32.00 492.0 12/15/15 0.08700 647 56.29 476.0 0.00000006243 0.10036 2.4087 47.00 605.2 03/31/16 0.08700 588 51.16 178.8 0.00000006243 0.03426 0.8223 107.0 693.2 06/27/16 0.08700 1,269 110.4 162.7 0.00000006243 0.06728 1.615 44.00 764.3 09/29/16 0.08700 596 51.9 181.0 0.00000006243 0.03516 0.844 106.0 853.7 12/14/16 0.08700 383 33.3 199.2 0.00000006243 0.02486 0.597 76.0 899.1 03/14/17 0.08700 2,020 175.7 290.0 0.00000006243 0.19090 4.582 90.0 1,311.4 06/20/17 0.08700 973 84.7 208.0 0.00000006243 0.06595 1.583 98.0 1,466.5 04/04/14* 0.08700 626 54.46 0.64 0.00000006243 0.0001 0.003 9.00 0.02820 07/10/14 10/27/14 0.08700 575 50.03 0.45 0.00000006243 0.0001 0.002 87.00 0.2043 03/04/15 0.08700 523 45.50 0.00 0.00000006243 0.0000 0.000 128.0 0.2043 06/18/15* 0.08700 731 63.60 0.00 0.00000006243 0.0000 0.000 106.0 0.2043 10/29/15 0.08700 528 45.94 0.00 0.00000006243 0.0000 0.000 55.00 0.2043 12/15/15 0.08700 368 32.02 0.00 0.00000006243 0.0000 0.000 47.00 0.2043 03/31/16 0.08700 645 56.12 0.00 0.00000006243 0.0000 0.000 107.0 0.2043 06/27/16 0.08700 720 62.64 0.00 0.00000006243 0.0000 0.000 54.00 0.2043 10/31/16 0.08700 523 45.50 0.00 0.00000006243 0.0000 0.000 53.00 0.2043 12/14/16 0.08700 2,832 246.38 42.4 0.00000006243 0.0391 0.939 44.00 41.5268 06/20/17 Notes: Table 6 SVE System Cumulative Recovery Cajah's Mountain Superette 1990 Connelly Springs Road Lenoir, North Carolina No Sample Collected; System Down 4. Mass removal rate = (air flow rate) x (total BTEX) x (conversion factor) x (60 min/hr or 1,440 min/day) 2. Total BTEX concentrations in effluent air are based on EPA Method 18 laboratory data 3. Conversion factor to convert units of concentration from m /m3 to lb/ft3 Facility ID Number 0-004593 Incident Number 28649 Effluent Velocity (ft/min) Air Flow Rate1 (ft3/min) Total BTEX2 (mg/m3) Mass Removal Rate4 1. Air flow rate = (cross-sectional area) x (effluent velocity) On-Site System Off-Site System No Sample Collected; System Down FIGURES SITE PR O J E C T N O . NO T E S : DA T E TI T L E SC A L E RE V . B Y PR E P . B Y CA D F I L E DC S A I D SITE HAMBY/CAJAH'SMT PARK TRIPLETT HAMBY/CAJAH' MT PARK WILLIAMS/BRANDON APARTMENTS PRICE CHURCH SHELL CHURCH PR O J E C T N O . NO T E S : DA T E TI T L E SC A L E RE V . B Y PR E P . B Y CA D F I L E PW-21 PW-20 PW-22 PW-8 PR O J E C T N O . NO T E S : DA T E TI T L E SC A L E RE V . B Y PR E P . B Y CA D F I L E PR O J E C T N O . NO T E S : DA T E TI T L E SC A L E RE V . B Y PR E P . B Y CA D F I L E APPENDIX A LABORATORY ANALYTICAL REPORT